Proposed Revision to. Allegheny County s Portion Of The Pennsylvania State Implementation Plan. for the

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1 Proposed Revision to Allegheny County s Portion Of The Pennsylvania State Implementation Plan for the Attainment and Maintenance of the National Ambient Air Quality Standards-- Removal of the Summertime Low Reid Vapor Pressure Gasoline Volatility Requirements from the Allegheny County Health Department Rules and Regulations Article XXI, Air Pollution Control Part E, Subpart 9, 215.9, Source Emission and Operating Standards- Transportation Sources-Gasoline Volatility, and Part G, , Methods-Gasoline Volatility and RFG; And the Supporting Noninterference Demonstration Under Section 11(l) of the Clean Air Act Revision Tracking No. 89 1

2 Local Executive Summary Article XXI Regulation Changes for Gasoline Volatility Regulations (State Implementation Plan (SIP) Revision 89) The ACHD Air Quality Program is proposing to update its regulations regarding Gasoline Volatility to pave the way for the eventual removal of the regulations from Article XXI. The proposed revision to Article XXI, 215.9, Gasoline Volatility, will add a single paragraph stating that the regulation will no longer be applicable in Allegheny County once the U.S. EPA approves a proposed SIP change based on the accompanying Non-Interference Demonstration substantiating that there will be no interference to the continued meeting of the 8-Hr Ozone NAAQS due to the removal of the requirement to sell only low RVP gasoline in Allegheny County during the ozone season. A similar change will be made to , Gasoline Volatility and RFG, which regulates the sampling and testing of gasoline required by These regulation revisions are in response to similar actions already taken by the PA DEP in response to Pennsylvania Act 5 of 214, which required action on the part of DEP to remove the state gasoline volatility regulations from the State Implementation Plan. While Act 5 of 214 does not require ACHD to remove its gasoline volatility regulations from Article XXI, the County is doing so. The information in this submittal demonstrates that there will be no adverse impact on the health of the citizens of this County due to this action. ACHD will submit this revision package to the U.S. EPA as an amendment to the County s portion of the Pennsylvania State Implementation Plan. 2

3 Table of Contents 1. Preface to the State Implementation Plan Revision Request 2. Proposed Changes to Article XXI Rules and Regulations: 215.9, Gasoline Volatility , Gasoline Volatility and RFG (regards sampling and testing) 3. Technical Support Document 4. Non-Interference Demonstration Appendices of the NID Appendix B of the NID Appendix C of the NID Appendix D of the NID Appendix E of the NID Appendix F of the NID Appendix G of the NID Appendix H of the NID 5. Documentation of Public Hearing and Certifications (All LATER ) (Required for SIP change.) Public hearing notice Transmittals of hearing notice to EPA & PA DEP Proof of publication of notice of hearing Certification of hearing Summary of Comments and responses Certifications of approval and adoption 3

4 1. Preface to the State Implementation Plan Revision Request Allegheny County is requesting that EPA amend the Allegheny County portion of Pennsylvania s approved State Implementation Plan (SIP) (4 C.F.R. part 52, subpart NN) to remove Article XXI, Part E, Subpart 9, 215.9, Source Emission and Operating Standards- Transportation Sources-Gasoline Volatility, and Article XXI, Part G, , Methods-Gasoline Volatility and RFG, as enforceable applicable SIP measures for Allegheny County, Pennsylvania. Additionally, Allegheny County notes that testing requirements of include references to the Allegheny County Source Testing Manual which is included in 4 C.F.R. part 52, subpart NN under 52.22(e), Identification of Plan - EPA-approved nonregulatory and quasi-regulatory material. Allegheny County requests that references to these requirements be removed from that portion of the SIP, as well. To support this SIP revision request, the ACHD Air Quality Program is: Revising its Gasoline Volatility regulations by adding paragraphs to Article XXI, 215.9, and , stating that these sections are no longer applicable upon the effective date of U.S. EPA s approval of the removal, suspension, or replacement of these sections as part of the Allegheny County portion of the SIP. See Section 2, below. Providing the background of this SIP revision request and its interaction with that of the similar SIP revision submitted by PA DEP to remove its gasoline volatility regulations. See Section 3, below. Providing a Non-Interference Demonstration demonstrating that repeal of Allegheny County s gasoline volatility regulations will not interfere with the attainment or maintenance of a NAAQS or any other applicable requirement of the CAA. See Section 4, below. ACHD notes that as of the time of preparation of this SIP revision, the PA DEP s SIP Revision Request/Non- Interference Demonstration has received the Direct Final approval of the U.S. EPA. See 83 FR 2791, June 15, 218. Pending the receipt of no adverse comments, the PA DEP s SIP revision related to 25 Pa.Code Chapter 126, Subchapter C, will be effective August 14,

5 2. Proposed Gasoline Volatility Regulations Revisions Deletions are shown with strikethroughs. Additions are shown in larger font, bolded, and underlined. PART E- Source Emission and Operating Standards GASOLINE VOLATILITY {This section added by May 7, 1998 amendment, effective May 15, 1998; Paragraph e renumbered, paragraphs c & d renumbered and amended August 12, 1999, effective September 1, Paragraph b.3 added mm/dd/218, effective mm/dd/218.} a. Applicability. This Section applies to gasoline which is sold or transferred into or within Allegheny County during the period May 1 through September 15, 1998, and continuing during the same period every year thereafter. b. Compliant Fuel Requirements. 1. No refiner, importer, distributor, reseller, or carrier may: A.. Sell, exchange or supply gasoline that is not a compliant fuel during the period described in Subsection (a). B. Blend, mix, store or transport or allow blending, mixing, storing or transporting of compliant fuel with noncompliant fuel during the period described in Subsection (a). 2. No retailer or wholesale purchaser-consumer may sell, exchange, or supply gasoline that is not a compliant fuel during the period June 1 through September 15, 1998, and continuing during the same period every year thereafter. 3. This Section will no longer be applicable upon the effective date of approval by the EPA of the removal, suspension or replacement of this Section as part of Allegheny County s portion of the Pennsylvania SIP. c. Record keeping and reporting. 1. Beginning with the terminal owner or operator who sells or transfers gasoline intended for use in Allegheny County during the period described in 215.9(a), each time the physical custody of or title to a shipment of gasoline changes hands other than when gasoline is sold or transferred for use in motor vehicles at a retail outlet or wholesale purchaser-consumer s facility, the transferor shall provide to the transferee a copy of the record described in this subsection. Said record shall legibly and conspicuously contain, at a minimum, the following information: (A) (B) (C) (D) (E) The date of the sale or transfer. The name and address of the transferor. The name and address of the transferee. The location of the gasoline at the time of transfer. The volume of gasoline which is being sold or transferred. 5

6 (F) A statement or grade code certifying that the gasoline has an RVP of 7.8 pounds per square inch or less per gallon. 2. Any person who transports, stores, or sells compliant fuel that is intended for use in Allegheny County during the period described in 215.9(a) shall segregate the compliant fuel from noncompliant fuel and the documentation described in c(1) shall accompany the compliant fuel at all times. 3. Each person in the gasoline distribution network shall maintain records containing the compliance information listed in c(1). These records shall be retained for at least 2 years from the date of the sale or transfer of compliant fuel. All records shall be kept on-site at each point in the distribution network, except for retail outlets. Retail outlets shall retain records on-site for at least the current compliance period (June 1 through September 15). The remaining records may be kept off-site, but they must be made available to the Department within 48 hours upon request. d. Labeling. During the period from June 1 to September 15 each year, and at all times when dispensing of clean fuels is required under this section, all retail gasoline dispensing facilities shall prominently display on each gasoline pump a label with the following statements and conditions: 1. Cleaner Gas, and JUNE 1 - SEPT 15". 2. RVP. 3. The letters RVP shall be a minimum of 5/16 inches in height; all other letters and numbers shall be a minimum of 1/4 inches in height. 4. The letters RVP shall be printed in green and all the other letters shall be printed in black. The label background shall be white. e. Sampling and test methods. Sampling and testing for the volatility of gasoline shall be performed according to the applicable procedures established PART G - Methods GASOLINE VOLATILITY and RFG {This section added by May 7, 1998 amendment, effective May 15, Subsection c added mm/dd/218, effective mm/dd/218} a. Volatility. Any sampling or testing of gasoline required by Section shall be performed according to the following methods as specified in Chapter 61 of the Allegheny County Source Testing Manual: 1. Sampling of gasoline for the purpose of determining compliance with shall be conducted in accordance with 4 CFR Part 8, Appendix D (relating to sampling procedures for fuel volatility). 2. Testing of gasoline for purposes of determining compliance with shall be conducted in accordance with 4 CFR Part 8, Appendix E (relating to test for determining the RVP of gasoline and gasoline-oxygenate blend). b. RFG. RFG shall be certified and tested in accordance with the requirements listed in 4 CFR Part 8 Subpart D (relating to reformulated gasoline) as specified in Chapter 61 of the Allegheny County Source Testing Manual. c. This Section will no longer be applicable upon the effective date of approval by the EPA of the removal, suspension or replacement of this Section as part of Allegheny County s portion of the Pennsylvania SIP. 6

7 3. Technical Support Document 3A. Background and History of the State and Local Low RVP Gasoline Regulations 25 Pa. Code Chapter 126, Subchapter C, Gasoline Volatility Requirements, applies to gasoline which is sold or transferred into or within the Pittsburgh-Beaver Valley Area between May 1 and September 15 of each year. More specifically, refiners, importers, distributors, resellers, terminal owners and operators, and carriers may not sell, exchange or supply gasoline that does not have a Reid vapor pressure (RVP) of 7.8 pounds per square inch or less (low RVP gasoline) in the Pittsburgh-Beaver Valley Area between May 1 and September 15 of each year. The PBV area includes Allegheny, Armstrong, Beaver, Butler, Fayette, Washington and Westmoreland counties. Gasoline vapors include volatile organic compound () emissions. s are a precursor to the formation of ground-level ozone air pollution and fine particulate matter (PM2.5), both hazards to public health and welfare. Gasoline formulated with an RVP of 7.8 psi or less has lower emissions than gasoline formulated at higher RVP levels. 25 Pa Code Chapter 126, Subchapter C was promulgated November 1, These requirements were approved by the EPA at 63 FR (June 8, 1998), effective July 23, 1998, as a revision to the Commonwealth s SIP and codified at 4 CFR Part 52, Subpart NN (relating to Pennsylvania). Thus, Chapter 126, Subchapter C is a Federally-enforceable control measure to attain and maintain the 1-hour Ozone National Ambient Air Quality Standards (NAAQS) in the Pittsburgh-Beaver Valley Area to protect the public health and welfare. Shortly thereafter, Allegheny County promulgated similar gasoline volatility requirements at Article XXI, Sections and These requirements were approved by the EPA at 66 FR (April 17, 21), effective June 18, 21, as a revision to the Allegheny County portion of the Pennsylvania SIP and codified at 4 CFR Part 52, Subpart NN. 3B. Changes to PA Air Pollution Control Act requiring the repeal of the state gasoline volatility rules and the Pennsylvania State s submittal of a PA SIP Revision Request In 214, Pennsylvania placed into law P.L. 674, No. 5, (Act 5), which amended the Pennsylvania Air Pollution Control Act (35 P.S ) to add section 4(18.3) (35 P.S. 44(18.3). The new provision required the PA Department of Environmental Protection to seek an amendment of the PA SIP and eventual repeal of the gasoline volatility rules: [W]ithin sixty (6) days of the effective date of this clause, initiate the process of amending the State implementation plan. Upon approval of a revision which demonstrates continued compliance with Federal national ambient air quality standards through utilization of commensurate emission reductions by the Environmental Protection Agency, the board [Environmental Quality Board] shall promulgate regulations to repeal the provisions of 25 Pa. Code Ch. 126 Subch. C (relating to gasoline volatility requirements). 7

8 3C. Stated Reason for Pennsylvania Act 5 requiring repeal of the low RVP gasoline regulations Act 5, and thereby the newly added Section 4(18.3) of the APCA, became effective May 14, 214. It was designed to address the price differential between low RVP gasoline and conventional gasoline in the Pittsburgh-Beaver Valley Area, cited by the legislative sponsors as being as much as a 1 to 15 cents per gallon price differential between the two fuels. See 48 Pa.B (April 7, 218). 3D. Pennsylvania s need to demonstrate non-interference and EPA s SIP Revision Requirements To repeal its gasoline volatility regulations, which are a part of its SIP, the state of Pennsylvania is required to ensure that the removal of Chapter 126, Subchapter C from the SIP complies with section 11(l) of the Clean Air Act ((42 U.S.C. 741(l)) (Non-Interference Clause). Likewise, the EPA may approve a SIP revision if, among other things, the SIP revision satisfies Section 11(l). That provision states that the EPA Administrator: shall not approve a revision of a plan if the revision would interfere with any applicable requirement concerning attainment and reasonable further progress (as defined in section 751 of this title), or any other applicable requirement of this act. In June 25, EPA provided draft guidance to states on how EPA intends to exercise its discretion in implementing CAA provisions related to the Section 11(l) requirements (25 EPA draft guidance) 1. The demonstration EPA describes in the 25 EPA draft guidance is known as a noninterference demonstration. 1 U.S. EPA Demonstrating Noninterference Under Section 11(l) of the Clean Air Act when Revising a State Implementation Plan Draft Guidance June 8,

9 3E. PA DEP implements Act 5 of 214 To implement Act 5 of 214, the Pennsylvania Department of Environmental Protection has prepared, held public comment upon (48 Pa. Bulletin 1481, March 1, 218), and submitted a SIP revision submittal that includes: A Non-Interference Demonstration to show continued compliance with the applicable NAAQS and protection of the public health and welfare through the use of commensurate emission reductions to offset the slight increases in emissions of and oxides of nitrogen (NOx) that will likely result in the near term from removing the low Reid Vapor Pressure regulations as a federally enforceable control measure from the SIP. This is a technical demonstration that repeal of Pennsylvania s gasoline volatility regulations for the Pittsburgh-Beaver Valley Area (which includes Allegheny County), codified at 25 Pa. Code Chapter 126, Subchapter C, will not interfere with the attainment or maintenance of a NAAQS or any other applicable requirement of the CAA. Consistent with the 25 EPA draft guidance on noninterference demonstrations, Pennsylvania is offsetting the potential emissions increases from repeal and removal of the gasoline volatility regulations from Pennsylvania s approved SIP with previously unclaimed emissions reductions already achieved by the Commonwealth in the PBV Area. These emission reductions consist of: (1) emissions benefit gained from Pennsylvania s adoption of volatile organic compound () limits on the use or application of adhesives, sealants, primers and solvents (25 Pa. Code ); and (2) previously unclaimed creditable emissions reductions associated with the permanent closure of a large stationary source of emissions of oxides of nitrogen (NOx) in the PBV Area (namely, Guardian Industries, in Allegheny County). It is noted that the NID includes a statement (on Page 2) that it supports an eventual repeal by ACHD of the Allegheny County summertime low volatility gasoline requirement. A request to remove the gasoline volatility requirements from 25 Pa. Code Chapter 126, Subchapter C, from the Pennsylvania SIP, as well as revised regulatory language that will make the state regulation no longer applicable once the EPA approves the SIP revision. (Once this first round of changes is made, the DEP intends to come back at a later date and process the regulatory changes needed to entirely remove Chapter 126, Subchapter C from the regulations.) 9

10 3F. Impact on the Allegheny County portion of the Pennsylvania SIP and ACHD Article XXI The previous discussion regarded the impact of the Pennsylvania State Act 5 and the consequent PA DEP changes to its regulations and the changes to the Pennsylvania SIP called for in 48 Pa. Bulletin 1481, March 1, 218. The following discussion regards the impact of those things on the Allegheny County air regulations and the related Allegheny County portion of the PA SIP. As a preface to that discussion, ACHD makes these remarks: 1. The language of Pennsylvania Act 5 of 214 is specifically directed at the repeal of 25 Pa. Code Ch. 126 Subch C. 2. Article XXI, Section governs the gasoline volatility requirements in Allegheny County, and is not directly affected by the Act 5 requirements. 3. While the ACHD intends to follow suit and repeal its low RVP gasoline regulations, it is with the realization that it is not required to do so under the provisions of Section 12 of the PA Air Pollution Control Act granting political subdivisions authority to enact ordinances not less stringent than the provisions of the Act. 4. ACHD recognizes the detailed technical analysis prepared by the PA DEP in the form of the PA NID of 48 Pa. Bulletin 1481 as accurate for the PBV area including Allegheny County, and intends for the calculations of that document to serve as the required NID for ACHD s SIP revision for repeal of, and removal of the low RVP requirements from the ACHD portion of the PA SIP. 5. ACHD believes it is necessary that portions of the PA NID, specifically Section 4, be annotated to include appropriate citations of the governing Article XXI regulations for the portion of the seven county Pittsburgh-Beaver Valley Area that is Allegheny County. Those annotations will be described in the Non-Interference Demonstration section, below along with other details specific to Allegheny County s NID. 1

11 3G. What ACHD is requesting as a SIP Revision The ACHD is requesting that EPA amend the Allegheny County portion of the Pennsylvania approved SIP (4 C.F.R. part 52, subpart NN) to remove the following regulations as enforceable applicable SIP measures for Allegheny County, Pennsylvania: Article XXI, Part E, Subpart 9, 215.9, Source Emission and Operating Standards- Transportation Sources-Gasoline Volatility, and Article XXI, Part G, , Methods-Gasoline Volatility and RFG. The ACHD is also herewith submitting revisions to these gasoline volatility regulations to read as shown in Section (2), above. These revisions call for Article XXI, and , to be no longer applicable upon the effective date of approval by the U.S. EPA of the removal, suspension, or replacement of these sections as part of the Allegheny County portion of the Pennsylvania State Implementation Plan (SIP). Note: Should EPA approve this SIP revision submittal, ACHD may, at some time in the future, revise Article XXI again, at such time to completely remove these two sections from the Article XXI. The complete removal of the Sections and could not be undertaken in this current SIP revision because, as described in 48 Pa.B.1934 (April 7, 218), prior to a recent decision by EPA Region 5 regarding Ohio s repeal of its low RVP gasoline volatility regulation, it was the policy of the EPA not to approve the removal of a regulation from a state s SIP unless the regulation had first been repealed at the state level and then submitted as a revision to the state s SIP. In Ohio, rather than repealing its low RVP gasoline volatility regulation, Ohio amended its regulation to make it no longer effective upon approval by EPA Region 5 of a SIP revision removing the provisions from Ohio s SIP. The PA DEP discussed this decision with EPA Region 3 and, with the concurrence of EPA Region 3, used Ohio s approach in DEP finalform rulemaking. The ACHD is likewise compelled to take the Ohio approach. As was the case for the state of Pennsylvania, to make it possible for EPA approval of these revisions to the Allegheny County portion of the PA SIP, the ACHD is required to ensure that the removal of and from the SIP complies with section 11(l) of the Clean Air Act (CAA), the Non- Interference Clause. Restating from above, the Non-Interference Clause prohibits the EPA Administrator from approving a SIP revision if the revision would interfere with any applicable requirement concerning the attainment of a National Ambient Air Quality Standard (NAAQS) or reasonable further progress in attaining a NAAQS, or any other applicable requirement of the CAA. To meet its own CAA Section 11(l) requirements, the ACHD is including as its Non-Interference Demonstration in Part 4 of this SIP submittal (below), the same NID including Appendices B through H, developed by the PA DEP and proposed by 48 Pa. Bulletin 1481 of March 1, 218, with the qualifications noted below. 11

12 4. SECTION 11(l) NONINTERFERENCE DEMONSTRATION Allegheny County s use of the Pennsylvania Department of Environmental Protection s Noninterference Demonstration As described above, because Allegheny County is one of seven counties that comprise the Pittsburgh-Beaver Valley Area, when the PA Department of Environmental Protection (PA DEP) prepared its non-interference demonstration (NID) for the purposes of removing its gasoline volatility requirements codified at 25 Pa. Code, Chapter 126, Subchapter C from the PA SIP, its analysis included Allegheny County. For example, emissions from sources located and operating in Allegheny County were included in the calculations made by the State for its demonstration. In order for Allegheny County to demonstrate non-interference for the removal of its own gasoline volatility regulations, and because the PA DEP s NID encompasses Allegheny County in its analysis, in the following pages of this Section 4 the ACHD is restating the language of Section 4 of the PA DEP s NID, which has already been submitted to the U.S. EPA as a SIP revision, and where it is necessary for the ACHD to modify the PA DEP NID in order to tailor the NID to specific Allegheny County concerns or attributes, the modifications will be noted in accordance with the text box below Overview of the Noninterference Demonstration Section 11(l) of the Clean Air Act contains the noninterference clause. This clause states that the EPA Administrator, shall not approve a revision of a plan if the revision would interfere with any applicable requirement concerning attainment and reasonable further progress (as defined in section 751 of this title), or any other applicable requirement of this act. (42 U.S.C. 741(l)) Additions made by ACHD are shown underlined. Deletions made by ACHD are shown with strikethroughs. In June 25, EPA provided states with draft guidance on how EPA intends to exercise its discretion in implementing CAA provisions and EPA regulations related to the Section 11(l) requirements (25 EPA draft guidance). 2 The draft document provides guidance for states on how they can demonstrate noninterference of SIP revisions with 2 U.S. EPA Demonstrating Noninterference Under Section 11(l) of the Clean Air Act when Revising a State Implementation Plan Draft Guidance June 8,

13 CAA provisions, especially related to area attainment, maintenance and reasonable further progress. The 25 EPA draft guidance, by its own terms, does not impose binding, enforceable requirements on a state; the EPA and states retain the discretion to adopt approaches on a case-by-case basis that differ from the guidance, as appropriate. According to the Department s analysis below, repealing and removing the gasoline volatility requirements for the Pittsburgh-Beaver Valley Area from Pennsylvania s SIP is estimated to cause a slight increase in emissions of volatile organic compounds (s) and NOx. The NAAQS for which there could be impacts are primarily the ozone and PM2.5 NAAQS, given that emissions of s and NOx both contribute to the formation of ozone and particulate matter. 3 It is important to note, however, that the original intent of adopting the gasoline volatility regulations was to reduce emissions from highway vehicles. As is shown in the Department s this noninterference demonstration, the removal of the requirements from the SIP and repeal of the Pennsylvania and Allegheny County rules rule will slightly reduce total emissions from the highway vehicle sector due to improvements in highway vehicle evaporative and exhaust emissions controls using higher RVP gasoline. The bulk of the estimated increases in emissions for the Pittsburgh-Beaver Valley Area resulting from the repeal are from the nonroad, or off-highway, vehicle sector. As the Department PA DEP seeks to repeal 25 Pa. Code Chapter 126, Subchapter C, and ACHD seeks to repeal Article XXI, and , and have EPA remove these this discretionary control measures from Pennsylvania s EPA-approved SIP, the ACHD, using the analysis performed by the Department PA DEP, which DEP has already submitted to the EPA for the overall seven county Pittsburgh-Beaver Valley Area, must demonstrate that removal of ACHD s gasoline volatility regulations will not interfere with the area s Allegheny County s attainment and maintenance of any NAAQS for which a measure remains in the SIP. To do this, the 25 EPA draft guidance provides an option for demonstrating noninterference through the substitution of lost emissions benefit from a removed measure with equivalent or greater reductions of the same pollutant from another measure previously not included in the SIP for the area. In addition, the Department it must be demonstrated that the removal of the control measure from the SIP does not interfere with other applicable CAA requirements (such as the regional haze requirements under sections 169A and 169B of the CAA, 42 U.S.C and 7492 (relating to visibility protection for Federal class I areas; and visibility)). 3 NO x is composed of Nitric Oxide (NO) and Nitrogen Dioxide (NO 2). The EPA has established a NAAQS for ambient NO 2 concentrations, however, the slight increases in NO x would only have a minor, secondary effect on ambient concentrations of NO 2. All counties in PA have been in attainment of the NO 2 standard since its establishment in

14 Pennsylvania s noninterference demonstration for the repeal of the low RVP gasoline volatility requirements contained in 25 Pa. Code Chapter 126, Subchapter C from the Commonwealth s approved SIP is based on the substitution option described in section 5 of the 25 EPA draft guidance. So too is ACHD s noninterference demonstration for the repeal of the low RVP gasoline volatility requirements contained in Article XXI, and from the PA SIP. Allegheny County is offsetting the emissions increases expected from the repeal and removal of Article XXI, and from the Allegheny County portion of the Pennsylvania SIP, as Pennsylvania did in is offsetting the emissions increases expected from the repeal and removal of Chapter 126, Subchapter C from the Commonwealth s approved SIP, with equivalent or greater reductions realized from two sectors: (1) Allegheny County s regulations relating to the use and application of adhesives, and adhesive primers (Article XXI, , Control of Emissions from Miscellaneous Industrial Adhesives) in conjunction with Pennsylvania s regulations relating to the use and application of adhesives, sealants, primers and solvents (25 Pa. Code ) (the adhesives rule); 4 and (2) surplus creditable emission reductions from the permanent shutdown of a major source of NOx in the Pittsburgh-Beaver Valley Area. In this SIP revision, the Department ACHD demonstrates, using the analysis developed by PADEP, that in 218 and 223 Pennsylvania, Allegheny County has compensating emission reductions for the slight emissions increases, and that the repeal and removal of Article XXI, and , and the corresponding Chapter 126, Subchapter C, from the Commonwealth s approved SIP will not interfere with any applicable requirement concerning attainment of a NAAQS, reasonable further progress, or any other applicable requirement of the CAA. This demonstration shows that overall NOx, and PM2.5 emissions from all sectors in the seven-county Pittsburgh-Beaver Valley Area are expected to continually decline through 223 when compared to the latest 214 National Emissions Inventory (NEI). 4 Although 25 Pa. Code is currently included in Pennsylvania s EPA-approved SIP as a discretionary SIP measure for Pennsylvania (4 C.F.R. part 52, subpart NN, 52.22(c)), the Department PA DEP has not claimed SIP credit from 25 Pa. Code in any Pittsburgh-Beaver Valley area attainment or maintenance plan relating to any NAAQS. ACHD also states that it has not claimed SIP credit from Article XXI, in any Allegheny County area attainment or maintenance plan relating to any NAAQS, though both regulations would seem to have figured in the areas ability to monitor attainment for the Hr Ozone NAAQS and affect the Final Designation Recommendations. 14

15 The 25 EPA draft guidance also specifies that substitution measures used for a noninterference demonstration should be quantifiable, permanent, surplus, enforceable and contemporaneous (when a substitute is a new measure). The Department PA DEP explains in its this SIP revision, and the ACHD restates here, how this noninterference demonstration meets EPA s guidance for these recommended substitution criteria. Lastly, the Pittsburgh-Beaver Valley Area is monitoring attainment for both the 28 and 215 ozone NAAQS. Numerical offset of estimated emissions from the repeal of the low RVP gasoline volatility requirements, as recommended in EPA draft guidance, demonstrates that the area will continue to attain and maintain the ozone NAAQS. Ambient air monitors in the Pittsburgh-Beaver Valley Area currently show attainment of the 215 ozone NAAQS for the years 214 through 216. This information was included in the Department s PA DEP s April 11, 217, revised submittal to EPA of its original October 3, 216, Final Designation Recommendations for the 215 Eight-Hour Ozone National Ambient Air Quality Standards, in which the Department PA DEP recommended the Pittsburgh-Beaver Valley Area be designated attainment of the 215 ozone NAAQS. EPA agreed with that recommendation and designated the area as attainment/unclassifiable (82 FR 54232, November 16, 217). Recent ozone modeling performed by EPA for 223 is also presented to further support Pennsylvania s, as well as Allegheny County s, demonstration. See Appendix H. Given both the Department s PA DEP s and the ACHD s use of the substitution option for noninterference demonstrations consistent with EPA guidance and Pennsylvania s and Allegheny County s current and projected monitored attainment, this SIP revision meets the CAA noninterference requirements. While this the PA DEP s demonstration includes included Allegheny County, and was based upon the state s gasoline volatility regulations of 25 Pa. Code Chapter 126, Subchapter C, that regulation is not applicable in Allegheny County, As described, the ACHD has its own regulation for summertime low volatility gasoline. This regulation is identical to the state regulation and is contained in the SIP for ACHD. 5 Therefore, the emission reductions related to Allegheny County calculated throughout the PA DEP noninterference demonstration were the result of the low RVP gasoline requirements of Article XXI, and ACHD is also pursuing a repeal of the Allegheny County gasoline volatility requirements regulation. The ACHD regulation is not more stringent than the Pennsylvania regulation. The repeal of the ACHD regulation will be submitted to EPA separately as a SIP revision. However, this noninterference demonstration, which includes an analysis that includes Allegheny County, will also likely serve as ACHD s required noninterference demonstration for its regulation repeal. 5 Allegheny County Health Department s Air Quality program was approved by the Department PA DEP on October 3, 1998 under Section 12 of the Air Pollution Control Act (APCA), 35 P.S

16 Estimated Changes in Emissions from RVP 7.8 to RVP 1 Summer Gasoline EPA approval of this the PA DEP s SIP revision will make the Pennsylvania RVP gasoline volatility requirements for the Pittsburgh-Beaver Valley Area no longer applicable. 6 EPA approval of this SIP revision will make the Allegheny County RVP gasoline volatility requirements for Allegheny County portion of the PBV Area no longer applicable. The less stringent federal RVP requirements in 4 C.F.R (relating to controls and prohibitions on gasoline volatility) will apply; it allows 9. pounds per square inch (psi) RVP in general and 1. psi RVP for gasoline blended with ethanol. Accordingly, with a repeal of the summertime gasoline volatility requirement requirements, emissions of NOx and are expected to increase slightly overall in the area. Highway vehicles are estimated to show a slight increase in NOx and slight decreases in both and PM2.5. Nonroad vehicles are expected to show an increase in emissions due to the increase in gasoline RVP. Both highway and nonroad sources are expected to be affected the most by the RVP change. emissions from certain point and area sources, such as aboveground gasoline storage tanks and portable fuel containers, may also increase. The point and area source emissions increases, however, are expected to be negligible. Both NOx and are considered precursors of PM2.5 formation and thus could contribute slightly to PM2.5 emissions; however, direct PM2.5 emissions are expected to decrease slightly from the highway vehicle sector. This interaction is discussed below in more detail in Section 2.D. Emissions of SO2 and lead from highway sources are directly related to the fuel sulfur and lead content, which are not affected by a change in gasoline RVP. For that reason, no changes are expected in SO2 or lead emissions as a result of the change in gasoline RVP. 6 For purposes of this the PA DEP s SIP revision, the Department s repeal of 25 Pa. Code Chapter 126, Subchapter C is the inclusion of a new subsection (d) to the existing requirements contained at of Subchapter C. The new subsection, promulgated April 7, 218, at 48 Pa.B. 1932, reads: This Subchapter will no longer be applicable to the Pittsburgh-Beaver Valley Area upon the effective date of approval by the Environmental Protection Agency of the removal, suspension or replacement of this Subchapter as a part of the Commonwealth s State Implementation Plan. The effective date of EPA approval of this the PA DEP s noninterference demonstration SIP revision will be the date on which Chapter 126, Subchapter C no longer applies to the Pittsburgh- Beaver Valley Area. At that point, the Pittsburgh-Beaver Valley Area will revert to federal gasoline volatility rules contained in 4 C.F.R. Part 8 (relating to regulation of fuels and fuel additives). For the purposes of this SIP revision, ACHD s repeal of Article XXI, and is the inclusion of new paragraphs c.3 and new subsection c, as described in Section 2, above. 16

17 The Department PA DEP has estimated lost and compensating emission reductions in 218, and assumed the use of 1. RVP gasoline. The noninterference demonstration in this SIP revision examines estimated changes in projected emissions reductions for 218 and a future year of 223, assuming future RVP in gasoline of 1. psi, in comparison to a baseline year of 214. Information regarding the Commonwealth s repeal of Chapter 126, Subchapter C is included in Appendix A of the PA DEP s Technical Appendices. The documents in Appendix A are were attached by the PA DEP for informational purposes only, and not for approval by EPA as part of this their SIP revision. ACHD is not including Appendix A in this SIP submittal. The following sections provide more detail on how the emissions were estimated for each source category. Highway Highway vehicle (onroad) emissions were estimated for the Pittsburgh-Beaver Valley Area by Michael Baker Corp., using the MOtor Vehicle Emission Simulator (MOVES) model version 214a (MOVES DB ). 7 Pennsylvania 216 highway vehicle registration, 216 traffic volume and speed data, and county-specific vehicle fleet projection estimates were employed for emissions estimates for 218 and 223. County-level highway vehicle emissions for 214 were taken from the NEI 214 version 1. 8 The MOVES default summertime gasoline formulation for the area assumes a fuel RVP of 7.8 psi with no 1. psi allowance for ethanol blending for 214. To estimate the impact of the fuel RVP change, the MOVES model was modified to reflect a future fuel RVP of 1. psi for 218 and 223 with all other inputs kept the same. 9 The RVP parameter was changed from the default value of 7.8 psi to 1. psi for the months May through September. 1 For both 218 and 223, the resulting emissions from the RVP 7.8 scenario were subtracted from the RVP 1. scenario to yield the estimated benefit (for a negative number) or impact (for a positive number). 7 See, 8 See, 9 Federal summertime gasoline RVP rules require a maximum fuel RVP of 9. psi, though gasoline fuels blended with 1% ethanol are allowed an additional 1. psi RVP allowance. As nearly all gasoline sold in the Pittsburgh- Beaver Valley area is already blended with 1% ethanol, the Department PA DEP is assuming a summertime fuel RVP maximum of 1. psi for the months May through September. 1 The MOVES Fuels Wizard was used to modify the modeling parameters. This application within MOVES allows users to modify fuel parameters for the modeled fuel. Modeled fuel parameters are included in the Technical Appendices. 17

18 Table 1 below summarizes the changes in highway vehicle emissions given a change in fuel RVP from 7.8 psi to 1. psi. It is important to note that the estimate of changes in highway vehicle emissions indicates that the increase in summertime fuel RVP will provide an overall reduction from the sector. While this seems counterintuitive, in aggregate, increases in evaporative loss and permeation emissions in the projected highway vehicle fleet are offset by exhaust reductions realized by improved engine fuel control and timing systems in newer model year vehicles. Over time, as the vehicle fleet is gradually replaced with newer and lower-emitting vehicles with exhaust emissions less sensitive to fuel RVP, the exhaust reductions overtake the evaporative increases and, therefore, provide a net reduction benefit in onroad vehicles in both 218 and 223. Additional details on the Department s PA DEP s highway vehicle emissions estimation procedure, including discussion of the net benefit realized in the highway fleet, are included in Section Appendix B of the Technical Appendices. Table 1 - Summary of Pittsburgh Beaver Valley Area Estimated Highway Emissions by Year and Fuel RVP Scenario Scenario RVP 7.8 RVP 1 Reduction (-) or Increase (+) Tons per Day Tons per Year 214 Tons per Day NOx Tons per Year PM 2.5 NOx PM 2.5 NOx PM 2.5 Tons Per year Tons per Day Highway Emissions Tons per Year Tons per Day , , , , , , n/a n/a n/a n/a n/a 25. 9, , , , Tons per Year Tons Per year Tons per Day Tons per Year Tons per Day Tons per Year Tons Per year Change from RVP 7.8 (tons) Change from RVP7.8 (%) -.7% -.5%.6%.3% -.3% -1.3% -.7%.3%.1% -.5% Nonroad Nonroad emissions were estimated using the MOVES NONROAD model version 214a. 11 The 214 NEI version 1 emissions inventory data were used to provide a baseline emissions year. National default county-based data was used to model nonroad emissions for each of the seven Pittsburgh-Beaver Valley Area counties for 218 and 223. The model was run for both 218 and 223 assuming the default summertime 7.8 RVP requirement, without a 1. psi RVP allowance for ethanol blending, for the summertime fuel season of May through September. Similar to the highway vehicle modeling, the NONROAD model in MOVES was used to modify the default fuel RVP 7.8 psi to RVP 1. psi for the subject summertime months (May through September) to estimate the effects of the fuel RVP change. The NONROAD model was configured to generate both weekday and weekend daily emissions for each month of the year and aggregated by Source 11 See, 18

19 Classification Code 12 by county. Emissions estimates are presented for only as no nonroad equipment emissions effects for NOx or PM2.5 were observed in the model. For both 218 and 223, the resulting emissions from the RVP 7.8 scenario were subtracted from the RVP 1. scenario to yield the estimated benefit (for a negative number) or impact (for a positive number). Table 2 below summarizes the changes in nonroad vehicle and equipment emissions given a change in fuel RVP from 7.8 psi to 1. psi. Additional details on the Department s PA DEP s nonroad vehicle emissions estimation procedure is included in Appendix C of the Technical Appendices. Table 2 - Summary of Pittsburgh Beaver Valley Area Estimated Nonroad Emissions by Year and Fuel RVP Scenario 214 Tons per Year Nonroad Emissions Tons per Day Tons per Year Tons per Day Tons per Year RVP RVP 1 n/a Reduction (-) or Increase (+) % change 3% 3% 3% 3% Area/Point Sources Changes in fuel RVP do not only affect highway and nonroad vehicle emissions. Certain area (nonpoint) and point sources that move, store and transfer gasoline (in other words, parts of the gasoline distribution system) may also have emissions increases. These sources can include gasoline plants and terminals, pipelines, service stations, tank trucks, underground storage tanks, and portable fuel containers (gas cans). Estimating emissions changes from these source categories with a change in fuel RVP can be challenging. EPA and states use emissions factors to estimate emissions from these sources that are specific to the type of fuel distribution activity that occurs. These factors are used for both area and point sources. 12 The EPA uses Source Classification Codes to classify different types of activities that generate emissions. Each Source Classification Code represents a unique source category-specific process or function that emits air pollutants. See, 19

20 Area source emissions factors for gasoline distribution are largely developed based on nationwide studies conducted by and for EPA. Current gasoline distribution emissions factors used for the 214 NEI are based on statewide fuel usage and sales apportioned to counties. Each county s assumed apportioned use of gasoline is multiplied by an emissions factor. This value reflects the total assumed emissions from the source category for the county. However, some sources (for example, bulk gasoline terminals and plants) are of sufficient size to be included in the point source inventory. The emissions for these facilities can be estimated using stationary source emissions methods. EPA s inventory development methodology requires that specific point source emissions from these facilities be subtracted from the general area source estimates to avoid double counting. According to the EPA 217 NEI estimation methodology, emissions factors for area sources were developed assuming a national fuel RVP of 1.4 psi. This reflected the weighted average fuel RVP of gasoline throughput in 199 with data supplemented in These assumptions were and still are used for area source emissions estimates in Pennsylvania. Given both the technical difficulty in reevaluating these factors, and the factors underlying annual and seasonal RVP assumptions that are now similar to expected RVP values following the repeal of Chapter 126, Subchapter C, the Department PA DEP is assuming no change in estimated area emissions as a result of the rule repeal, and following the repeal of Article XXI, and , ACHD is assuming no change in estimated area emissions as a result of the ACHD rule repeal. Stationary sources for gasoline distribution rely on emissions factors contained in EPA s AP-42 compendium of air emissions factors. These factors are further employed in EPA s TANKS model. Stationary sources are encouraged to use the TANKS model to estimate emissions for large aboveground storage tanks prevalent at gasoline bulk terminals and plants as the model uses the AP-42 emissions factors directly. This model reflects the many variables that influence emissions for individual tanks in addition to fuel RVP. These include tank dimensions, monthly fuel throughputs, product temperature, air temperature, tank color, and others. These calculations are submitted by the source operators to the Department PA DEP or the ACHD as part of the annual emissions statement and certification program and are reflected in the Department s PA DEP s and ACHD s air emissions inventory inventories. The stationary source inventory uses a Source Classification Code system to identify emissions from specific source categories in each county of Pennsylvania. From the 214 NEI, existing stationary sources in the seven counties for the applicable point source categories can be obtained. For this demonstration, the Department PA DEP has assumed that these sources will experience an increase in emissions similar to what is estimated for nonroad sources a 3% increase from 214 emissions in both 218 and

21 Table 3 - Summary of Estimated Point Source Increases Due to RVP Change Point Source Category 214 NEI (tpy) Point Terminals Point Bulk Plants 74.9 Tank Trucks in Transit 1.4 Service Station Unloading Point Emissions for RVP 217 3% of 214 Point Emissions 7 tpy for RVP increase.2 tpd Details on the area and point source emissions estimation methodologies are contained in Appendix D of the Technical Appendices. Summary of Expected Change in Emissions Table 4 summarizes the estimated emissions projected for both 218 and 223 assuming a fuel RVP of 1. psi in 218 and 223. Table 4 - Summary of Pittsburgh Beaver Valley Estimated Emissions Changes for 218 and 223 with RVP NOx PM2.5 tpy tpsd tpy tpsd tpy Highway Nonroad Point/Area 7.2 Total RVP Repeal NOx PM2.5 tpy tpsd tpy tpsd tpy Highway Nonroad Point/Area 7.2 Total RVP Repeal Note: Negative values denote a decrease (reduction) in emissions As a result of switching from a 7.8 to 1. psi RVP limit for summertime gasoline in the Pittsburgh-Beaver Valley Area, the Department PA DEP expects area-wide emissions to increase slightly in 218 and increase slightly less by 223. Emissions of NOx are expected to increase slightly in the highway sector in 218 and to a much smaller degree in 223. Emissions of direct PM2.5 are expected to decrease in 218 and decrease slightly more by 223. The following section describes how Pennsylvania, and the ACHD, offsets offset the and NOx increases with substitute measures. 21

22 Uncredited Emissions Benefits Available for Substitution The compensating emission reductions needed to demonstrate that Pennsylvania s repeal of its summertime RVP 7.8 gasoline volatility regulations for the Pittsburgh-Beaver Valley Area, and Allegheny County s repeal of its corresponding regulations, will not interfere with maintenance or attainment of a NAAQS, or with any other applicable requirement of the CAA, can be found in previously unclaimed emission reductions from two areas: (1) Overcontrol of contained in Pennsylvania s adhesives rule (25 Pa. Code ) and in Allegheny County s adhesives rule (Article XXI, ) and, (2) Unclaimed creditable emissions reductions associated with the permanent closure in 215 of a large stationary source of NOx in the Pittsburgh-Beaver Valley Area. Consistent with the 25 EPA draft guidance, these two measures are quantifiable, permanent, surplus, enforceable and contemporaneous, as applicable. The applicability of these conditions is discussed below for each measure. Adhesives Rule Emission Reductions The following section highlights the development, adoption and estimation of emissions benefits from Pennsylvania s adhesives rule codified at 25 Pa. Code , and Allegheny County s adhesives rule of Article XXI, Background The Commonwealth s adhesives rule was promulgated on December 24, 21. This regulation adopted requirements and emission limits consistent with those of the 26 Ozone Transport Commission (OTC) adhesives and sealants model rule for the use and application of 37 categories of products for which emissions were previously unregulated in Pennsylvania. The adhesives rule became effective December 25, 21, and contains no end date. 4 Pa.B Consequently, the emission reductions from the adhesives rule are permanent. ACHD s adhesives rule was effective June 8, 213. This regulation adopted requirements and emission limits consistent with the 28 Control Techniques Guidelines for Miscellaneous Industrial Adhesives, EPA-453/R

23 On June 25, 215, EPA incorporated the Pennsylvania adhesives rule, 25 Pa. Code , into the Pennsylvania SIP to fulfill Pennsylvania s CAA requirement to adopt statewide reasonably available control technology (RACT) for sources covered by EPA s control technique guidelines (CTG) for adhesives, sealants, primers and solvents (8 FR 36482, June 25, 215). This renders the regulation federally enforceable, in addition to it already being enforceable as state law upon its effective date. On January 2, 216, EPA incorporated the Allegheny County adhesives rule, Article XXI , into the Allegheny County portion of the Pennsylvania SIP (81 FR 2991, 1/2/216). This rendered the regulation federally enforceable. The Pennsylvania NID states that tthe emission reductions from the their rule are surplus. Although the rule was incorporated into the Pennsylvania SIP as a regulation, Pennsylvania did not include the potential emission reductions from the rule for any plan or demonstration for the 1997 or 28 ozone NAAQS or for the 26 PM2.5 NAAQS for the Pittsburgh-Beaver Valley Area. Allegheny County s rule has also been incorporated into the SIP. The Technical Support Document of the SIP submittal indicates that the regulation was added to meet the EPA mandate requiring CTGs to become regulations, written by Local and State Air Pollution Control Agencies. As shown in the Emissions Quantification section below, the emission reductions from the adhesives rule are also quantifiable. The ambient air quality in the Pittsburgh-Beaver Valley Area already meets the 215 and earlier ozone NAAQS, as is demonstrated by EPA s designation of the area as attainment/unclassifiable for the 215 NAAQS. Recent EPA ozone modeling for 223 shows attainment in the Pittsburgh-Beaver Valley Area of both the 28 and 215 ozone NAAQS. The Department PA DEP is using the quantifiable, surplus, permanent and enforceable emissions reductions available from Pennsylvania s adhesives rule in 25 Pa. Code to offset the expected emissions increases associated with a repeal and removal of 25 Pa. Code Chapter 126, Subchapter C from the Commonwealth s approved SIP. ACHD notes that the portion of the quantifiable and enforceable emissions reductions attributable to Allegheny County sources are available as a result of Allegheny County s adhesives rule, Article XXI , to offset the expected emissions increase associated with a repeal and removal of Article XXI and from the SIP. 23

24 Emissions Quantification In Pennsylvania s adhesives rule, the Department PA DEP used emission reduction estimates generated by the OTC in support of the OTC s model rule that estimated additional emissions reduction for 29 that could be realized through a state s adoption of the requirements and emission limits in the OTC model rule. The emissions reduction potential of the OTC model rule was based on initial studies performed by the California Air Resources Board (CARB) in support of CARB s adhesives regulation, upon which the OTC based its model rule. The 26 OTC model rule analysis provided county-level estimates for expected reductions from area and point sources that would be subject to the rule. For this its noninterference demonstration SIP revision and similar to the methodology used for Pennsylvania s adhesives rulemaking, the Department PA DEP has taken the summer ozone season daily reduction estimates of the OTC, by county, for the seven counties in the Pittsburgh-Beaver Valley Area and calculated a per capita daily reduction. Using current 217 population data and projection planning assumptions from PennDOT for the seven counties, the per capita emissions reduction factor (expressed as pounds reduction per person) was multiplied by the projected county population for 214, 218 and 223 and the results were converted to tons reduction per day by county. The sum of the county daily values multiplied by 365 days per year yields Pennsylvania s estimate of the annual reductions realized from the adhesives rule. 13 These values represent the total projected additional reductions available for annual offset from the source categories. The tons-per-day values also demonstrate that the area s summer day emissions rates will not be increased as an effect of the repeal and removal of Pennsylvania s RVP 7.8 rule from the SIP. For ACHD s noninterference demonstration SIP, ACHD is relying upon the calculations made by PA DEP as described above, with the underlying assumption that the Allegheny County adhesives rule, Article XXI , has similar emission limitations. Comparing the two regulations, they are different in scope. The Pennsylvania rule at 25 Pa. Code applies to control of emissions from the use or application of adhesives, sealants, primers and solvents, whereas the Allegheny County rule applies to owners of miscellaneous industrial adhesive application processes. Comparing Table V of 25 Pa. Code (not to be confused with Table 5 of this document, below) to Table , the former includes limitations for sealants, whereas Table does not. Further investigation reveals that the reason is that ACHD based its regulation on the Control Techniques Guidelines for Miscellaneous Industrial Adhesives EPA- 453/R-8-5 September 28, while as the Pennsylvania NID notes, the DEP regulation was based on the OTC Model Rule. ACHD has reviewed the limitations related to the adhesives listed in the tables and found them to be very 13 Current emissions estimation methods for area source adhesives assume no seasonality with emissions. Emissions rates are assumed to be constant from the adhesives sources independent of season. For this reason, annual reduction estimates are estimated by multiplying the daily reduction rate by 365 days per year. 24

25 similar. ACHD s regulation might be more stringent with respect to adhesives since Table contains limits on three categories not found in Table V of The OTC model rule tons-per-summer-day reduction estimates used for Pennsylvania s adhesives rulemaking were based on estimates assuming a three-month (91-day) ozone season (June through August). By comparison, the OTC county-by-county reduction estimates were modified to reflect the longer May through September (151-day) low RVP fuel season. The comparison has the effect of normalizing comparative daily adhesives rule emission reductions with the estimated daily increases for the entire 151-day May through September season in which RVP is currently regulated in gasoline. Table 5 summarizes the daily and annual emissions benefit available for offset in the Pittsburgh-Beaver Valley Area from Pennsylvania s adoption of the adhesives rule, and being used in this the PA DEP s SIP revision. ACHD notes that, with regard to the overall emission reductions determined in the Pennsylvania analysis to be due to an adhesives rule, the portion due to activities in Allegheny County results from application of ACHD adhesives rule found at Article XXI, Underlying data and the supporting calculations for the adhesives rule emissions benefit estimate are provided in Appendix E of the Technical Appendices. Table 5 - Summary of Pennsylvania Adhesives Rule Emission Reduction Estimates for 214, 218 and 223 Emissions Factor (EF) Calculation PA Adhesive Rule Reductions OTC Adhesives Rule Reductions (29) Tons per Tons per Year Day 1, P-BV Area Population 2,355,432 Tons reduction emissions factor (Tons/person) 4.96E E-6 Tons reduced divided by 29 area population Annual / Daily Reduction Estimates using EF and Population Year P-BV Area Population 2,358,96 2,346,571 2,338,2 Tons per Year Tons per Day Population Projections Reduction 25

26 Permanent Facility Closure NOx and PM2.5 Emission Reductions To offset the estimated increase in NOx emissions expected as a result of the repeal and removal from the SIP of Chapter 126, Subchapter C, and the repeal and removal of Article XXI, and from the Allegheny County portion of the Pennsylvania SIP, DEP and ACHD, respectively, is are using surplus emissions reductions realized by the permanent closure of Guardian Industries Corporation, a large glass manufacturing facility located in Jefferson Hills, Allegheny County (Facility ID ). Guardian Industries permanently ceased operations at the Jefferson Hills facility in August 215. Guardian Industries did not request that the potential creditable emissions reductions from the facility s closure be preserved in the inventory within one year of closure as required in 25 Pa. Code Chapter 127, Subchapter E (relating to new source review), (2)(i) (relating to creditable emissions decrease or ERC generation and creation). ACHD notes that the actual regulations to be followed by Guardian, a source located in Allegheny County, would be Article XXI, (relating to new source review) and c (relating to reporting requirements for emission offset registration). Therefore, as Guardian Industries did not make such a request and more than two years have passed since the closure, Guardian Industries cannot claim the creditable emissions reductions as new source review (NSR) emissions reduction credits (ERC) under (2) nor the corresponding ACHD regulation at Article XXI, c. Additionally, PA DEP states in its NID that the creditable emissions reductions have not been used to meet past or current SIP, attainment demonstration, emissions limitation or compliance plan requirements in Pennsylvania. This makes the credits surplus to Pennsylvania s existing NSR program. 14 ACHD notes that the Attainment Demonstration for the Allegheny, PA SO2 Nonattainment Area 21 Standards SIP includes the Guardian shutdown in the discussion of Control Strategy, and Reasonable Further Progress, and included Guardian emissions in the modeling demonstration. The shutdown of Guardian was also included in the future case modeling for the 212 PM2.5 NAAQS Attainment Demonstration for Allegheny County, PA. 14 The Department s PA DEP s NSR program at 25 Pa. Code Chapter 127, Subchapter E was originally adopted by the Commonwealth on January 14, DEP submitted a SIP revision on February 4, 1994, to incorporate the program into the Pennsylvania SIP. EPA gave limited approval for the program through its final rulemaking action on the SIP revision on December 9, 1997 (62 FR 64724, December 9, 1997). Full EPA approval for the program in the Pittsburgh-Beaver Valley Area was given on October 19, 21 (66 FR 5394), and was effective on November 18, 21. In February 217, the EPA found that Pennsylvania failed to submit a required SIP revision to satisfy certain requirements for the 28 ozone NAAQS that apply to nonattainment areas and/or states in the Ozone Transport Region. Specifically, Pennsylvania did not submit implementation plan revisions for the implementation of a Nonattainment New Source Review (NNSR) program. (82 FR 9158, February 3, 217). On November 3, 217, the Department PA DEP submitted a SIP revision to EPA to meet those requirements. On December 14, 217, the EPA issued a letter to the Department PA DEP stating the Department s PA DEP s submittal was administratively and technically complete and under review. 26

27 The previously unclaimed emissions reductions realized by the permanent closure of the Guardian Industries facility are permanent. The source has been permanently removed, the facility has been shut down, and plan approvals installation permits and operating permits are no longer valid. Any new source created by Guardian Industries at the same location in Allegheny County would be subject to permitting provisions as a new source under Pennsylvania s Allegheny County s EPA-approved NSR regulations. The emissions reductions are enforceable as they have been permanently removed from the inventory. The Department s PA DEP s existing procedures and authority to approve creditable emissions reductions and ERCs under 25 Pa. Code Chapter 127, Subchapter E, and take enforcement action on violations of those regulations ensures the enforceability of the emissions reductions. By nature of EPA s incorporation of 25 Pa. Code Chapter 127, Subchapter E in the Pennsylvania SIP, the reductions are also federally enforceable. The ACHD notes that because the Guardian Industries plant was located in Allegheny County, it is the regulations of Article XXI, 212.8, which are applicable and also included in the SIP and also federally enforceable. The creditable emissions reductions are quantifiable. The Department PA DEP applied requirements contained in Pennsylvania s creditable emissions decrease provisions for the NSR program (specifically, 25 Pa. Code a (relating to applicability determination) regarding ERC calculation lookback periods and baseline credit determination and regarding creditable emissions decrease generation and creation). ACHD notes that the requirements applied by the PA DEP analysis to Guardian Industries facility would have been ACHD Article XXI, a.1 and b.3.A, which incorporate by reference 25 Pa. Code a and Additional information regarding the offset calculation for creditable emissions reduction from the permanent shutdown of Guardian Industries Corp. can be found in Appendix F of the Technical Appendices. 27

28 Table 6 summarizes the creditable emissions reductions available for offset from the facility closure. Table 6 - Summary of Creditable Emissions Reductions from the Shutdown of Guardian Industries Guardian Industries Annual Emissions (tons) (end Pollutant 7/31) NOx PM Permanent Offsets for 24 Month Annual Average (8/1/13-7/31/15) Pollutant tons per year tons per day NOx PM n/a 28

29 Summary of Previously Uncredited Emissions Benefits from Substitute Measures Table 7 summarizes the previously uncredited emissions benefits the Department PA DEP is using used from the substitute measures to offset expected emissions increases associated with the repeal and removal of the Pittsburgh-Beaver Valley Area summertime low RVP gasoline volatility requirements from the Pennsylvania SIP. The Pennsylvania SIP includes the portion that relates to Allegheny County gasoline volatility regulations at and Table 7 - Summary of All Uncredited Emissions Benefits Available for Use to Offset Increases NOx PM tpy tpsd tpy tpsd tpy OTC Adhesives Rule n/a n/a n/a Source Shutdown Total NOx PM tpy tpsd tpy tpsd tpy OTC Adhesives Rule n/a n/a n/a Source Shutdown Total These emission benefits more than offset the emission increases expected from repeal and removal of 25 Pa. Code Chapter 126, Subchapter C from Pennsylvania s approved SIP and from repeal and removal of Article XXI, and from the Allegheny County portion of the Pennsylvania SIP. 29

30 Demonstration of Noninterference with Attainment and Maintenance of NAAQS Consistent with the options described in the 25 EPA draft guidance on noninterference demonstrations, Pennsylvania is electing elected to offset the predicted emissions increases from the repeal of Pennsylvania s low RVP gasoline volatility requirements (25 Pa. Code Chapter 126, Subchapter C) with surplus reductions available from Pennsylvania s adhesives rule (25 Pa. Code Chapter 129, ) and a permanent facility shutdown in the Pittsburgh-Beaver Valley. While at the same time, Allegheny County is electing to offset the predicted emissions increase from the repeal of Allegheny County s low RVP gasoline volatility requirements (Article XXI, and ) with surplus reductions available from Allegheny County s adhesives rule (Article XXI, ) and the permanent facility shutdown in Allegheny County, part of the Pittsburgh-Beaver Valley ozone nonattainment area. Table 8 summarizes the Pittsburgh-Beaver Valley Area emissions increases estimated due to Pennsylvania s and Allegheny County s repeal (including EPA s removal from the SIP) of the Pittsburgh-Beaver Valley low volatility fuel regulation regulations compared to the estimated surplus emissions reductions. The Department PA DEP is electing elected to make an upward adjustment to the total emissions requiring offset of 25 percent of the estimated emissions increases associated with the repeal of 25 Pa. Code Chapter 126, Subchapter C and Article XXI, and This is done to account for uncertainty in the emissions estimation methods. Allegheny County concurs with the use of a 25% adjustment. 3

31 Table 8 - Area Summary of Increases Anticipated and Offsets Available for Noninterference Demonstration Change in Emissions from RVP Rule Repeal Emissions Adjustment Total Emissions Requiring Offset Creditable Reductions Available for Offset 218 Sector Total estimated change in emissions Tons per Year Tons per Day Tons per Year Tons per Day PM 2.5 Tons per Year Highway Nonroad Point/Area % of total estimated emissions increase Estimated emissions changes plus adjustment n/a n/a Adhesives Rule Permanent Shutdown Total Available Offsets Creditable Reductions After Required Emissions Offset NOx Change in Emissions from RVP Rule Repeal Emissions Adjustment Total Emissions Requiring Offset Creditable Reductions Available for Offset 223 Sector Total estimated change in emissions Tons per Year Tons per Day Tons per Year Tons per Day PM 2.5 Tons per Year Highway Nonroad Point/Area % of total estimated emissions increase Estimated emissions changes plus adjustment n/a n/a Adhesives Rule Permanent Shutdown Total Available Offsets 1173 Creditable Reductions After Required Emissions Offset Note: Negative values denote a decrease (reduction) in emissions NOx

32 The above table demonstrates that the surplus emissions reductions from the adhesives rule and the permanent facility shutdown are significantly higher than the estimated increases expected with the repeal of the low volatility gasoline rule rules repeal. The Department PA DEP desires desired to retain the balance of the creditable emissions reductions not used to offset the estimated emissions increase and 25% allowance, for potential future use by the Department PA DEP or ACHD for future SIP planning purposes. The following sections describe how the repeal and removal from the SIP of Chapter 126, Subchapter C, and Article XXI, and , with the inclusion of the substitute measures identified in this SIP revision, will not interfere with the attainment or maintenance of any NAAQS or other applicable requirements under the CAA. Ozone As emissions of and NOx contribute to ground-level ozone formation, noninterference with the ozone NAAQS is demonstrated through the appropriate offset of estimated emissions increases with previously unclaimed permanent reductions. By using the 214 NEI as a baseline year, projected emissions of and NOx from all sectors (namely highway, nonroad, point and area source sectors) continue to decline for the entire area, either with or without emissions offsets. An examination of recent air emissions inventory projections performed through the Mid-Atlantic Regional Air Management Association, Inc. (MARAMA) to support regional ozone photochemical modeling demonstrates the continued emissions decline for the Pittsburgh-Beaver Valley Area. The projections are summarized in Table 9. The complete data, including documentation of the methodology used to project the emissions to future years, are included in Appendix G of the Technical Appendices. Table 9 - Summary of 214 NEI and MARAMA 218 and 223 Projected NOx and Inventory by Sector 32

33 Complimenting the projected continued overall NOx and emissions decline, monitored levels of ozone in the area s ambient air continue to demonstrate compliance with the NAAQS. Additionally, EPA recently classified the seven counties of the Pittsburgh-Beaver Valley Area as attainment/unclassifiable for the 215 ozone NAAQS, based on certified ambient air monitoring data for 214 through 216. Lastly, recent preliminary photochemical modeling performed by EPA to support interstate ozone transport modeling shows all Pennsylvania counties will meet or exceed the 28 ozone standard and that all seven counties in the Pittsburgh-Beaver Valley Area will have design values at or below the 215 ozone NAAQS in While this modeling demonstration did not account for a repeal of Chapter 126, Subchapter C, nor for a repeal of Article XXI, and , it does demonstrate that with appropriate emissions offsets, the area will maintain compliance with both the 28 and 215 ozone NAAQS. Additional information on the EPA modeling analysis is included in Section H of the Technical Appendices. In summary, as the Department analysis has demonstrated that emissions increases of NOx and realized by the repeal of and removal from the SIP of 25 Pa. Code Chapter 126, Subchapter C and Article XXI, and , will be offset by quantified surplus, permanent and enforceable creditable emissions reductions and, therefore, no increase in NOx and emissions will occur in the area. Because no net increase in NOx or is anticipated, there will be no interference with the continued attainment or maintenance of either the 28 or 215 ozone NAAQS. Additionally, with no net increase in emissions, there is no demonstrated interference with any other applicable CAA requirement. Fine Particulate Matter (PM2.5) Allegheny County is designated as nonattainment of the 212 annual PM2.5 NAAQS, and the Liberty-Clairton area is designated nonattainment of the hour PM2.5 NAAQS. EPA redesignated the area it had designated as the Pittsburgh-Beaver Valley nonattainment area for the 26 PM2.5 standard to attainment of the standard and approved a maintenance plan on October 2, 215 (8 FR 59624, October 2, 215). The increase in summertime gasoline RVP from 7.8 psi to 1. psi is not expected to increase direct PM2.5 emissions in any affected sector. 15 This analysis used 216 data and incorporated recent 217 emissions reductions from Pennsylvania EGUs because of new Pennsylvania required RACT controls. The data and methodology for this modeling is available at ozone. 33

34 NOx and emissions are precursors to PM2.5 formation. NOx and emissions from the repeal and removal of Chapter 126, Subchapter C and Article XXI, and , are being offset by the permanent shutdown of Guardian Industries and the use of the surplus reductions available from the Pennsylvania adhesives rule (25 Pa. Code Chapter 129, ) and the Allegheny County adhesives rule (Article XXI, ). With no increase in emissions of PM2.5 precursors, additional PM2.5 is not formed and, therefore, does not interfere with attainment or maintenance of the PM2.5 NAAQS or any other CAA applicable requirement (including regional haze requirements). Additionally, the credited shutdown will permanently reduce direct PM2.5 emissions in Allegheny County by approximately 21 tons per year. Ammonia and SO2 emissions are also precursors of PM2.5, but emissions from neither are expected to increase from any sector as a result of the repeal and removal from the Pennsylvania SIP of Chapter 126, Subchapter C and removal from the Allegheny County portion of the Pennsylvania SIP of Article XXI, and Given the above offset of PM2.5 precursors and the overcontrol of direct PM2.5 emissions, the repeal and removal of the summertime low volatility gasoline rule rules from Pennsylvania s SIP and Allegheny County s portion of the PA SIP, will not interfere with Allegheny County s ability to achieve the 212 PM2.5 NAAQS, Liberty-Clairton area s ability to continue to attain the hour PM2.5 NAAQS, or the ability of the area designated as the Pittsburgh-Beaver Valley area for the hour PM2.5 NAAQS to continue to attain and maintain the NAAQS. Sulfur Dioxide (SO2) Portions of Allegheny and Beaver Counties are currently designated as nonattainment areas for the 21 SO2 NAAQS. Emissions of SO2 from fuels are directly related to the fuel s sulfur content during combustion. Fuel sulfur content does not affect RVP nor do changes in RVP affect SO2 emissions. Gasoline fuel sulfur content limits are regulated by the EPA and will not change as a result of the repeal and removal from Pennsylvania s SIP of Chapter 126, Subchapter C or the repeal and removal from the Allegheny County portion of the PA SIP of Article XXI, and Therefore, repeal and removal of the requirements from Pennsylvania s SIP will not interfere with attainment or maintenance of the SO2 NAAQS, or any other applicable requirement of the CAA pertaining to the SO2 NAAQS. In October 217, the Department PA DEP submitted 21 SO2 NAAQS attainment demonstration SIP revisions to EPA for the Beaver and Allegheny 34

35 County 16 nonattainment areas, based on dispersion modeling that shows 218 compliance with the SO2 NAAQS. As the repeal and removal of Chapter 126, Subchapter C from Pennsylvania s SIP and Article XXI, and from Allegheny County s portion of the Pennsylvania SIP, will not affect SO2 emissions from the SO2 sources identified in those SIP revisions, the repeal and removal of the requirements from Pennsylvania s SIP, including Allegheny Counties portion of the PA SIP, will not interfere with the attainment demonstration SIP revisions for these counties. Lead (Pb) One area within the seven-county Pittsburgh-Beaver Valley Area is currently designated as nonattainment for the 28 lead NAAQS. The Lower Beaver Valley nonattainment area for the 28 lead NAAQS is located in southern Beaver County and is associated with the operations surrounding Horsehead Corporation s processing of zinc ores at its former Monaca, Pennsylvania facility. This facility ceased operations in spring of 214. The structures have been demolished and the site converted to provide the land for the construction of a new polyethylene plant that will have few to no lead emissions. Lead emissions from gasoline are directly related to the lead content contained in the gasoline. EPA sets and enforces the maximum content levels of lead in gasoline. Changes in summertime fuel RVP will not affect lead emissions and therefore the repeal of Chapter 126, Subchapter C and Article XXI and and removal of the requirements from Pennsylvania s approved SIP will not interfere with attainment or maintenance of the 28 lead NAAQS, nor with any other applicable requirement of the CAA related to the lead NAAQS. Carbon Monoxide (CO) All seven counties in the Pittsburgh-Beaver Valley Area are in attainment of the 1971 CO NAAQS. A portion of the area is under a maintenance plan (see page 8). [EPA originally designated a portion of Pittsburgh as a nonattainment area for the 1971 CO NAAQS (43 FR 4513, September 12, 1978), but redesignated the area as attainment and approved a 1-year maintenance plan on January 1, 23 (67 FR 68521). EPA approved a maintenance plan for a second 1-year period effective May 27, 214 (79 FR 1754, March 27, 214).] Changes in summertime fuel RVP will not increase emissions of CO and, therefore, repeal and removal from the SIP of Chapter 126, Subchapter C and Article XXI and will not interfere with attainment, maintenance or any other applicable requirement of the CAA regarding the CO NAAQS. 16 The Department PA DEP submitted the SO 2 attainment demonstration SIP revision for the Allegheny County nonattainment area on behalf of the ACHD. 35

36 CONCLUSION Nitrogen Dioxide (NO2) Emissions of NO2 comprise a subset of total NOx emissions. All counties in the Pittsburgh-Beaver Valley Area are meeting the 1971 NO2 NAAQS. The area has no nonattainment areas or areas subject to a maintenance plan for the NO2 NAAQS. As total estimated NOx emission increases expected from repeal of Chapter 126, Subchapter C and Article XXI and are being offset by the surplus NOx emission reductions realized from the Guardian Industries permanent shutdown, repeal and removal of the requirements from Pennsylvania s approved SIP, including the Allegheny County portion of the PA SIP, will not interfere with the counties continued compliance with the NO2 NAAQS or with any other applicable requirement of the CAA relating to the NO2 NAAQS. Given the technical noninterference demonstration provided in this SIP revision, including the Technical Appendices, Pennsylvania DEP the Allegheny County Health Department respectfully requests that EPA remove 25 Pa. Code Chapter 126, Subchapter C Article XXI and as an enforceable control measure from the Allegheny County portion of the Pennsylvania SIP codified at 4 C.F.R. part 52, subpart NN. Upon EPA approval of this SIP revision, the requirements of 25 Pa. Code Chapter 126, Subchapter C Article XXI and will no longer be applicable in Allegheny County, a subset of the seven-county Pittsburgh-Beaver Valley Area. This SIP revision must meet the requirements for a public comment process set forth in Section 11(a)(2) of the CAA, 4 C.F.R (d) and Section 7.5 of the Air Pollution Control Act, 35 P.S On March 1, 218, the Department provided notice of a 3-day public comment period and the opportunity for a hearing on this Proposed State Implementation Plan Revision to Remove Pittsburgh-Beaver Valley Area Summertime Low Reid Vapor Pressure Gasoline Volatility Requirements from Pennsylvania s State Implementation Plan; and Supporting Noninterference Demonstration Under Section 11(l) of the Clean Air Act. (48 Pa.B. 1481). As no member of the public requested to testify at the hearing prior to the 12 p.m. April 4, 218 deadline indicated in the public notice, the Department cancelled the April 9, 218 hearing through an announcement on the Department s website, consistent with the March 1, 218 Pennsylvania Bulletin notice. The Department s ecomment system remained open for receipt of public comments on the SIP revision from March 1 through April 9, 218. The Department received no public comments during this period. The Commonwealth s verification of public notice is included in Appendix I. 36

37 APPENDICES B through H of the Non-Interference Demonstration Notes on the Pennsylvania NID Appendices Appendices A through I of the PA NID SIP submittal were reviewed by ACHD to decide which, if any, need to be annotated in any way to make them applicable for Allegheny County s use in its NID. Below are the determinations of that review. Appendix A PA DEP submitted it as For Info Only because it contains mostly rulemaking documents. ACHD does not need to include this Appendix in the ACHD NID SIP. Appendix B there is no content that requires changing to permit this appendix to be submitted as part of the Allegheny County SIP revision. ACHD notes erroneous references to sub appendices as Appendix D s. Appendix C there is no content that requires changing to permit this appendix to be submitted as part of the Allegheny County SIP revision. Appendix D there is no content that requires changing to permit this appendix to be submitted as part of the Allegheny County SIP revision. Review of Appendix E. Adhesives Rule Estimation Supports Pages 15 to 17 of NID body. Appendix E provides the method of calculating emission reductions attributable to the Adhesives rule. They take the OTC model rule reductions from 29, divide it by the 29 population to get an emission factor and then just multiply that by the population for the other years. The general tables are the same as those in the NID body. It is not possible to make any kind of statements attempting to separate the analysis just for Allegheny County. Allegheny County must accept the whole demonstration showing attainment for the entire seven county region. Review of Appendix F. Shutdown estimation. Calculates the emission reductions from the Guardian plant based on the emission inventories of a 24-month period over ACHD notes that since Guardian was located in Allegheny County, these emissions would have been first reported to Allegheny County. Review of Appendix G. Inventory. Produces Table 9. There is nothing that needs to be altered. Review of Appendix H, 223 Attainment Modeling Shows EPA projected 223 Ozone design values and that they are below the 215 Ozone std. Nothing needs to be altered. Review of Appendix I, Public Notification. not necessary to incorporate into ACHD s plan revision. Appendices B through H may be added to the ACHD NID SIP submittal. 37

38 APPENDIX B to ACHD Non-Interference Demonstration is Appendix B to PA DEP NID as follows:

39 APPENDIX B MOVES Documentation Bureau of Air Quality Department of Environmental Protection

40 Technical Appendix B - Onroad Emissions Technical Support Document TECHNICAL APPENDIX B1 Proposed State Implementation Plan Revision to Remove Pittsburgh Beaver Valley Area Summertime Low Reid Vapor Pressure Gasoline Volatility Requirements and Supporting Noninterference Demonstration Under Section 11(l) of the Clean Air Act Technical Support Document Mobile Source Highway Emissions Inventory Executive Summary Prepared for: Mobile Sources Section, Bureau of Air Quality Pennsylvania Department of Environmental Protection Prepared by: Michael Baker International February 218 B - 1

41 Technical Appendix B - Onroad Emissions Technical Support Document Mobile Source Emissions Inventory Executive Summary February 218 Exhibit of Contents SUMMARY... B-3 EMISSIONS INVENTORY... B-3 ANALYSIS METHODOLOGY... B-4 DATA SOURCES AND ANALYSIS TOOLS... B-6 ANALYSIS TOOLS... B-6 TRAFFIC DATA SOURCE/FLEET DATA INPUTS... B-7 TRAFFIC GROWTH ASSUMPTIONS... B-8 VEHICLE POPULATION GROWTH ASSUMPTIONS... B-8 I/M AND FUEL PARAMETERS... B-9 METEOROLOGY DATA... B1 VEHICLE TECHNOLOGY PROGRAMS... B-1 RESOURCES... B-12 List of Exhibits EXHIBIT 1: SUMMARY OF APPENDICES... B-3 EXHIBIT 2: MOTOR VEHICLE EMISSIONS USING MOVES214A... B-4 EXHIBIT 3: SUMMARY OF ANALYSIS TOOLS... B-6 EXHIBIT 4: PPSUITE PROCESS... B-7 B - 2

42 Technical Appendix B - Onroad Emissions Technical Support Document SUMMARY This technical appendix supports the Proposed State Implementation Plan Revision to Remove Pittsburgh Beaver Valley Area Summertime Low Reid Vapor Pressure Gasoline Volatility Requirements and Supporting Noninterference Demonstration Under Section 11(l) of the Clean Air Act. The nonattainment area included in the analyses consists of: Allegheny County, Armstrong County, Beaver County, Butler County, Fayette County, Washington County, and Westmoreland County. To meet emission inventory requirements of section 172(c)(3) of the Clean Air Act, a regional mobile source highway inventory has been prepared for the and NOx emissions. Emissions are estimated for summer weekday and annual conditions for the 218 and 223 analysis years. Appendix D has been provided to summarize the methodology and analysis results for the motor vehicle emissions inventory using MOVES214a. To complement this executive summary, attachments have been provided with additional detail regarding the analysis methodology, the MOVES input parameters, and the output vehicle miles of travel (VMT) and emission results for the region. These include: Exhibit 1: Summary of Appendices Appendix Title Description D-1 Explanation of Methodology Provides a detailed summary of the methodology used to calculate the VMT and emissions. D-2 Provides July weekday and annual emission exhibits by Ozone (, NOx) county, road type, source type and process categories in Emission Results 218 and 223 for each analysis scenario. D-3 MOVES Sample Input File Provides examples of the MOVES input files. Emissions Inventory A summary of the motor vehicle emissions for the Pittsburgh-Beaver Valley area nonattainment area is provided in Exhibit 2. The emission estimates for all pollutants have been developed using the MOVES214a emission model and latest planning assumptions. Emissions have been estimated for the 218 and 223 analysis years for the following analysis scenarios: RVP 7.8: used for the existing low RVP program scenario RVP 8.7: used for the no RVP program scenario assuming no RVP waiver RVP 1: used for the no RVP program scenario assuming 1 psi RVP waiver B - 3

43 Technical Appendix B - Onroad Emissions Technical Support Document Exhibit 2: Motor Vehicle Emissions Using MOVES214a Fuel Scenario Total Emissions for the Pittsburgh-Beaver Valley Area July Weekday (Tons/Day) Annual (Tons/Year) NOx NOx NOx NOx RVP 7.8 (Low RVP Program) , ,42.8 6, , RVP , ,42.4 6, , RVP , , ,64. 1, Assuming No RVP Waiver (RVP 8.7 RVP7.8) Assuming 1 psi RVP Waiver (RVP 1 RVP7.8) Low-RVP Program Benefits Positive numbers represent reductions in emissions; negative numbers represent increases in emissions. Analysis Methodology Guidance documents from EPA were used to develop the base and future year emissions inventories for the region. They include: Policy Guidance on the Use of MOVES214 for State Implementation Plan Development, Transportation Conformity, and Other Purposes, US EPA Office of Transportation and Air Quality, EPA-42-B-14-8, July 214. Instructions for Using LEV and NLEV Inputs for MOVES214, US EPA Office of Transportation and Air Quality, EPA-42-B-14-6a, October 214. MOVES214a User Guide, US EPA Office of Transportation and Air Quality, EPA-42- B-15-95, November 215. MOVES214 and MOVES214a Technical Guidance: Using MOVES to Prepare Emission Inventories for State Implementation Plans and Transportation Conformity, US EPA Office of Transportation and Air Quality, EPA-42-B-15-93, November 215. The highway mobile source emission inventory was developed using available travel data and EPA s MOVES214a emission model. The methodologies used to produce the emission data conform to the recommendations provided in EPA s Technical Guidance. A mix of local data and national default (internal to MOVES214a) data has been used for this submission. Local data has been used for the primary data items that have a significant impact on emissions. These include: Vehicle miles of travel (VMT) by vehicle type Average speed distribution Vehicle type mixes Source type population (for light-duty vehicles) Vehicle age distribution Hourly distributions Meteorology data B - 4

44 Technical Appendix B - Onroad Emissions Technical Support Document Inspection/Maintenance program Fuel supply Most local data inputs to the analysis process reflect the latest planning assumptions based on 214 data obtained from the Pennsylvania Department of Transportation (PennDOT), the Bureau of Motor Vehicles, and other local/national sources. Available more recent data was used for control strategies (e.g. Inspection- Maintenance programs), vehicle age distributions and fuel characteristics. The analysis methodology is consistent with past statewide inventory efforts including the 214 National Emissions Inventory (NEI) submission. This includes the use of custom post processing software to calculate hourly speeds and prepare key traffic input files to the MOVES214a emission model. A detailed methodology is provided in Appendix D-1. The following sections address the key input data sources and analysis tools used for the emissions inventory. B - 5

45 Technical Appendix B - Onroad Emissions Technical Support Document DATA SOURCES AND ANALYSIS TOOLS This section provides a summary of the key input data and analysis tools used for producing the emissions inventory. The key elements to the modeling protocol are described in the sections below. A more detailed description of the analysis process and tools is provided in the methodology reports in Appendix D-1 through D-3. Analysis Tools The mobile vehicle emissions inventory analysis utilizes several key software/programs for producing the county emissions totals. These tools are outlined in Exhibit 3. Exhibit 3: Summary of Analysis Tools Tool MOVES214a PPSUITE CENTRAL Purpose Produces emission rates for each ozone precursor, and NOx. Processes the highway data; Calculates hourly congested speeds for each state roadway segment; Prepares MOVES214a input files; Processes MOVES214a output files into a summary report. Provides a batch menu driven process to execute PPSUITE, MOVES214a and other MYSQL steps. The inventory reflects the highway mobile source emission estimations using EPA s MOVES214a emission model released in November 216. The MOVES214a model includes the Tier 3 vehicle/fuel standards and updates to the impact of ethanol fuel blends compared to its predecessor MOVES21b. MOVES214a has been integrated with local traffic, vehicle fleet, environmental, fuel, and control strategy data to estimate emissions. PPSUITE represents an enhanced version of the Post Processor for Air Quality (PPAQ) software system that has been used for previous inventory and conformity submissions in Pennsylvania. The software has undergone significant revisions to ensure consistency with the MOVES214a. PPSUITE was used to calculate hourly congested speeds for each roadway link, apply vehicle type fractions, aggregate VMT, prepare MOVES214a traffic-related input files and process MOVES214a outputs. The PPSUITE software and process methodologies are consistent with that used for state inventories and transportation conformity analyses throughout Pennsylvania. Exhibit 4 summarizes the key functions of PPSUITE. CENTRAL is a menu-driven software platform that executes the PPSUITE and MOVES214a processes in batch mode. The software allows users to execute runs for a variety of input options and integrates custom MYSQL steps into the process. CENTRAL provides important quality control and assurance steps including file naming and storage automation. B - 6

46 Technical Appendix B - Onroad Emissions Technical Support Document Exhibit 4: PPSUITE Process Traffic Data Source/Fleet Data Inputs Traffic Volume Data: The PennDOT Roadway Management System (RMS) data serves as the primary highway data source for the county and functional class VMT estimates. The data source is used to provide a snapshot of the regional roadway system and traffic volumes in 214 (consistent with past triennial updates of traffic data). The 214 data is also integrated with traffic signal locations. The data includes the average annual daily traffic (AADT) volumes for all state roadways in Pennsylvania. To account for additional local roadway VMT and to ensure consistency with reported Highway Performance Monitoring System (HPMS) VMT totals, the VMT totals estimated from PennDOT s RMS are adjusted to match the annual 214 HPMS VMT totals, as reported to FHWA. Seasonal Adjustments: Within MOVES, annual VMT is split to monthly sub-totals and then to weekdays and weekends using seasonal factors. The monthly seasonal factors are developed from data contained in the document, 214 Pennsylvania Traffic Data, prepared by PennDOT s Bureau of Planning and Research (BPR). The seasonal and daily factors provided in this document are based on statistical analyses of 214 traffic counts taken at permanent and in-pavement ATR (automatic traffic recorder) locations throughout the state. Congested Speeds: Based on the average annual daily traffic, a single set of hourly speed distributions are estimated by the PPSUITE post processing system and input to MOVES. To disaggregate the daily RMS volumes to hourly volumes, auto and truck hourly pattern data from PennDOT s 214 Pennsylvania Traffic Data report is used to determine the temporal variations in traffic volumes. B - 7

47 Technical Appendix B - Onroad Emissions Technical Support Document Vehicle Population: Vehicle population is a key input that has an important impact on start and evaporative emissions. MOVES214a requires the number of vehicles by 13 source types to determine evaporative emissions. Pennsylvania 214 vehicle registration data (consistent with past triennial updates of traffic data) was used to estimate vehicle population for light-duty vehicles, school buses and transit buses for each county. The data was split to source types using MOVES default population data. For all other heavyduty vehicles, PPSUITE calculates vehicle population based on the analysis year VMT for each source type and default MOVES214a ratios of VMT and source type population (e.g. the number of miles per vehicle by source type). VMT by Source Type: The total VMT is disaggregated to the 13 MOVES source types. For this inventory, the vehicle mix was calculated for each county and functional class grouping utilizing a combination of: 214 RMS truck percentages 214 school bus registration data 214 PennDOT transit data EPA s MOVES default distribution of VMT by source type was used to determine the remaining source type VMT percentages. The development of vehicle type pattern data input to the MOVES214a software is described in more detail in Appendix D-1. Vehicle Age Distribution: Vehicle age distributions are required to be input by 13 source types. The distributions reflect the percentage of vehicles in the fleet up to 31 years old. A 214 registration download from PennDOT s Bureau of Motor Vehicles Registration Database have been used to estimate age distributions for this inventory. Due to insufficient data, only data for light-duty vehicles are used as local inputs; and, heavy-duty vehicles use the MOVES214a national default age distribution. The registration data download is based on MOBILE6.2 vehicle categories. The data was converted to source types using the EPA convertor spreadsheets provided with the MOVES emission model. Traffic Growth Assumptions Traffic growth forecasting plays a pivotal role in estimating future year emissions for the region. There are many uncertainties affecting projections of traffic growth including the current economic conditions, potential fuel prices, the impacts of natural gas industry activities in many counties throughout the state, and the future growth in population and employment. Growth rates for this emissions inventory were based on an assessment of available data sources including PennDOT s BPR growth rate forecasting system based on a PennDOT study originally completed in 25 and documented in the report, Statistical Evaluation of Projected Traffic Growth, Traffic Growth Forecasting System: Final Report, March 14, 25. As part of that study, a statewide traffic growth forecasting system was developed that incorporates traffic data from PennDOT s Traffic Information System and socioeconomic forecasts. That forecasting system is maintained by the PennDOT BPR and is updated on a periodic basis. This system was updated in September of 215 to develop new statistical relationships between historic VMT growth (thru 214) and population. The forecast population was estimated from the Woods and Poole data 21 State Profile. The results of the study have been shared between PennDOT, PaDEP and other Interagency Consultation Group members, including the Pennsylvania Transportation - Air Quality Work Group (which also includes EPA, FHWA, and representatives from larger MPOs within the state). Vehicle Population Growth Assumptions Vehicle population growth forecasting plays an important key role in determining emissions for future years for the region. For this inventory, vehicle population was forecasted considering the growth from three different sources: B - 8

48 Technical Appendix B - Onroad Emissions Technical Support Document Household growth Population Growth VMT Growth The household and population data were obtained from the PennDOT study documented in the report as discussed above, Statistical Evaluation of Projected Traffic Growth, Traffic Growth Forecasting System: Final Report, March 14, 25. The forecast household and population were estimated from the Woods and Poole data 215 State Profile. The final growth rate was calculated assuming the highest growth rate of household and population data but then limiting it to the VMT growth rate. This methodology has been used for past conformity analyses and has been accepted using the interagency consultation process (Pennsylvania Air Quality Workgroup). I/M and Fuel Parameters I/M Program: The inspection maintenance (I/M) program inputs to the MOVES model are based on past and current programs within each county (all Pennsylvania I/M programs are based on county boundaries). All analysis years include Pennsylvania s statewide program. The default I/M program parameters included in MOVES model were examined for each county and necessary changes made to the defaults to match the actual local program. In order to assure that emission controls are working properly, vehicle inspection and maintenance (I/M) programs have been adopted in some nonattainment areas. These programs have the added benefit of improving the fuel efficiency of vehicles. The Pennsylvania inspection and maintenance (I/M) program was upgraded and expanded throughout the state with a phase-in period starting in September 23 and fully implemented by June 24. The program requirements vary by region (five regions) and include on-board diagnostics (OBD) technology that uses the vehicle s computer for model years 1996 and newer to identify potential engine and exhaust system problems that could affect emissions. The program, named PAOBDII, is implemented by region, as follows: Philadelphia Region - Bucks, Chester, Delaware, Montgomery and Philadelphia Counties Pittsburgh Region - Allegheny, Beaver, Washington and Westmoreland Counties South Central and Lehigh Valley Region - Berks, Cumberland, Dauphin, Lancaster, Lebanon, Lehigh, Northampton and York Counties North Region - Blair, Cambria, Centre, Erie, Lackawanna, Luzerne, Lycoming, and Mercer Counties The OBDII program is implemented in Philadelphia and Pittsburgh along with tailpipe (idle in Pittsburgh and idle and ASM in Philadelphia) and gas cap tests. Tests in other regions include: Subject vehicles registered in the South Central and Lehigh Valley counties receive the visual, OBD and gas cap tests. Subject vehicles registered in the North region receive a gas cap test and visual inspection. Subject vehicles registered in the other 42 counties (67 total counties) receive a visual inspection as part of the annual safety inspection. Fuel Assumptions: The MOVES214a default data assumptions have been reviewed and updated based on available local volumetric fuel property information. The gasohol market penetration was updated but MOVES214a default data was used for the remaining parameters. Fuel Wizard was used to update the B - 9

49 Technical Appendix B - Onroad Emissions Technical Support Document RVP and other default fuel properties per EPA MOVES214a User Guide and Technical Guidance. Key input assumptions included: The RVP assumptions for summer months: Using RVP 7.8 for the existing low RVP program scenario Using RVP 8.7 for the no RVP program scenario assuming no RVP waiver Using RVP 1 for the no RVP program scenario assuming 1 psi waiver 95.7% market share of 1% ethanol and 4.3% market share of 85% ethanol used throughout the year for analysis year 218, and 91.6% market share of 1% ethanol and 8.4% market share of 85% ethanol used throughout the year for analysis year 223 (based on MOVES214a defaults). Meteorology Data Updated weather information has been obtained from WeatherBank, Inc. ( The 1-year ( ) average minimum and maximum monthly temperature and relative humidity values were obtained for each of the 1 airport locations in Pennsylvania. The MOVES214a model requires temperature and relative humidity data for each hour of the day and for all the 12 months for the annual analysis. EPA s data converters were used to convert minimum and maximum daily temperatures to an hourly temperature profile that could be input to MOVES214a. These assumptions are consistent with the 214 NEI inventory submission. Vehicle Technology Programs Federal Programs Current federal vehicle emissions control and fuel programs are incorporated into the MOVES214a software. In addition to the National Program standards covering model year vehicles through 216 as included in MOVES21, MOVES214a incorporates three new federal emissions standard rules not included in MOVES21: Heavy duty greenhouse gas standards (promulgated September 211, 76 FR 5716) began phasing in with the 214 model year, and will result in lower heavy duty energy consumption rates and some reduction in criteria pollutant emissions. Light duty greenhouse gas standards (promulgated October 212, 77 FR 62623) will begin phasing in with the 217 model year, and will result in decreased energy consumption rates and decreased refueling emissions. Tier 3 vehicle and fuel standards (promulgated April 214, 79 FR 23414) will begin phasing in with the 217 model year, and will reduce both tailpipe and evaporative emissions from light duty cars and trucks, and some heavy duty vehicles, for, NOx, CO and PM. Modifications of default emission rates are required to reflect the early implementation of the National Low Emission Vehicle Program (NLEV) program in Pennsylvania. To reflect these impacts, EPA has released instructions and input files that can be used to model these impacts. This inventory utilized the October 214 version of the files ( B - 1

50 Technical Appendix B - Onroad Emissions Technical Support Document State Programs The Pennsylvania Clean Vehicles (PCV) Program, adopted in 1998, incorporated the California Low Emission Vehicle Program (CA LEV) by reference, although it allowed automakers to comply with the NLEV program as an alternative to this Pennsylvania program until MY 26. Beginning with MY 28, new passenger cars and light-duty trucks with a gross vehicle weight rating (GVWR) of 8,5 pounds or less that are sold or leased and titled in Pennsylvania must be certified by the California Air Resources Board (CARB) or be certified for sale in all 5 states. For this program, a new vehicle is a qualified vehicle with an odometer reading less than 7,5 miles. PaDEP and PennDOT worked with the automobile manufacturers, dealers and other interested business partners and finalized procedures for complying with these new requirements. DEP focuses its outreach effort with the manufacturers and dealers regarding what vehicles can be offered for sale and how to certify that the vehicles are compliant. PennDOT s role is to ensure licensing and registration records include these certifications of compliance or that the vehicle owner qualifies for an exemption to the requirements. In all cases, DEP will use information obtained during PennDOT s title and registration process to oversee and audit, as needed, certain vehicle title transactions to determine compliance to the program. The impacts of this program are modeled for all analysis years beyond 28 using the same instructions and tools as downloaded for the early NLEV analysis. EPA provided input database to reflect the LEV I, LEV II, and LEV III California standards. Modifications to those database was made to reflect a 28 start date for Pennsylvania. B - 11

51 Technical Appendix B - Onroad Emissions Technical Support Document RESOURCES 214 Pennsylvania Traffic Data, PennDOT Bureau of Planning and Research. Modeling Page within EPA s Office of Mobile Sources Website ( contains a downloadable model, MOVES users guide and other information. Policy Guidance on the Use of MOVES214 for State Implementation Plan Development, Transportation Conformity, and Other Purposes, US EPA Office of Transportation and Air Quality, EPA-42-B-14-8, July 214. Instructions for Using LEV and NLEV Inputs for MOVES214, US EPA Office of Transportation and Air Quality, EPA-42-B-14-6a, October 214. MOVES214a User Guide, US EPA Office of Transportation and Air Quality, EPA-42-B-15-95, November 215. MOVES214 and MOVES214a Technical Guidance: Using MOVES to Prepare Emission Inventories for State Implementation Plans and Transportation Conformity, US EPA Office of Transportation and Air Quality, EPA-42-B-15-93, November 215. Metrological Data from Weather Bank, Inc., B - 12

52 Technical Appendix B - Onroad Emissions Technical Support Document APPENDIX B2 Explanation of Methodology B - 13

53 Technical Appendix B - Onroad Emissions Technical Support Document Explanation of Methodology February 218 TABLE OF CONTENTS INTRODUCTION... 1 OVERVIEW OF EMISSIONS INVENTORIES... 1 HIGHWAY VEHICLE EMISSION INVENTORIES... 1 WHERE DOES PENNSYLVANIA OBTAIN ITS DATA?... 4 SUMMARY OF MOVES INPUTS... 4 VEHICLE MILES OF TRAVEL (VMT)... 5 ADJUSTMENTS TO ROADWAY DATA... 7 VEHICLE TYPE PROCESSING... 8 VEHICLE FLEET AND POPULATION DATA... 9 ENVIRONMENTAL, FUEL AND TECHNOLOGY ASSUMPTIONS... 1 SPEED/EMISSION ESTIMATION PROCEDURE VOLUME/VMT DEVELOPMENT SPEED/DELAY DETERMINATION HPMS AND VMT ADJUSTMENTS MOVES EMISSIONS RUN RESOURCES HIGHWAY VEHICLE INVENTORY GLOSSARY List of Exhibits EXHIBIT 1: SUMMARY OF PPSUITE PROCESS... 3 EXHIBIT 2: MOVES LOCAL DATA INPUT SUMMARY... 4 EXHIBIT 3: PENNDOT URBAN/RURAL AND FUNCTIONAL CLASS CODES... 6 EXHIBIT 4: MOVES SOURCE TYPES AND HPMS VEHICLE GROUPS... 9 EXHIBIT 5: PPSUITE SPEED / EMISSION ESTIMATION PROCEDURE B - 14

54 Technical Appendix B - Onroad Emissions Technical Support Document INTRODUCTION The purpose of this document is to explain how the Pennsylvania Department of Environmental Protection (Department) estimates emissions from highway vehicles for inclusion in its emission inventories and State Implementation Plans. Overview of Emissions Inventories The Department s inventories generally categorize emissions into four categories: Highway vehicles. Point sources (major industrial, commercial and utility sources). Non-point sources (smaller industrial/commercial sources, consumer products). Nonroad mobile sources (including construction and agricultural equipment, lawn and garden equipment). An evaluation of emissions from point, area, and mobile sources is needed to develop a complete inventory needed for a maintenance demonstration plan. This documentation addresses the mobile source activity and emissions for base and future years used to support such a demonstration. Of all of the sources of air pollution, only the emissions of some stationary sources are measured directly and continuously through instrumentation. Emissions from all other sources must be modeled based on available local data, including those from highway vehicles. In their very simplest form, estimates of emissions follow the following pattern: Emission rate x activity level = emissions per time period (usually day or year) Most emission rates have been developed by the U.S. Environmental Protection Agency (EPA), in cooperation with industry and states, and are compiled and documented into key references or emission models. These include Compilation of Air Pollution Emission Factors (AP-42), the Motor Vehicle Emission Simulator (MOVES) model, and the NONROAD model. Adding up the products of the emission rates and activity levels for all sources of a given pollutant constitutes the emission inventory for that pollutant. Highway Vehicle Emission Inventories Highway vehicles contribute significantly to air pollution, particularly to ground-level ozone, which is the most persistent air pollutant in Pennsylvania. Ground-level ozone is not emitted directly to the atmosphere, but is formed by photochemical reactions between volatile organic compounds (s) and oxides of nitrogen (NOx) in the presence of sunlight. The long, hot, humid days of summer are particularly conducive to ozone formation, so ozone levels are of concern primarily during the months of May through September. Both s and NOx are emitted from highway vehicles. Pennsylvania s ozone-related emission inventory efforts focus on these two types of pollutants. Obviously, direct measurement of emission levels from all vehicles in use is impossible. In comparison to highway vehicles, estimating residential heating emissions is a fairly simple calculation because there is a constant emission rate and a fairly simple measure of activity. However, for highway vehicles estimating the emission rate and activity levels of all vehicles on the road during a typical summer day is a complicated endeavor. Appendix B2 B - 15

55 Technical Appendix B - Onroad Emissions Technical Support Document If every vehicle emitted the same amount of pollution all the time, one could simply multiply those emission standards (emission rate in grams of pollution per mile) times the vehicle miles traveled (VMT) to estimate total emissions. But emission rates from all vehicles vary over the entire range of conditions under which they operate. These variables include air temperature, speed, traffic conditions, operating mode and fuel characteristics. The inventory must also account for non-exhaust or evaporative emissions. In addition, the fleet is composed of several generations and types of vehicles with different emission control technologies. This requires the estimation algorithm include the composition of the fleet (vehicle ages and types). In order to estimate both the rate at which emissions are being generated and to calculate vehicle miles traveled (activity level), Pennsylvania examines its road network and fleet to estimate vehicle activity. For ozone-related inventories, this is done for a typical summer weekday. For carbon monoxide (CO) and particulate matter (PM) emission inventories, this may be done for a typical winter weekday, summer weekday and/or annual conditions. Not only must this be done for a baseline year, but it must also be projected into the future. This process involves a large quantity of data and is extremely complex. Computer models have been developed to perform these calculations by simulating the travel of vehicles on the Commonwealth s roadway system. The models also generate emissions rates (also called emission factors) for different vehicle types for area-specific conditions, and then combine them in summary form. The area-specific conditions include vehicle and highway data, plus control measure characteristics and future year projections of all variables. The key models used to generate this mobile source emissions inventory are: MOVES: EPA s MOVES214a model, released in November 216, was used for this mobile source inventory as approved by EPA. The MOVES model provides a more robust estimate of emissions as compared to its predecessor MOBILE6.2. MOVES calculates average in-use fleet emissions for each of thirteen categories of vehicles under various conditions affecting in-use emission levels (e.g., ambient temperatures, average traffic speeds, gasoline volatility) as specified by the model user. MOVES can be used to estimate national, state, and county level inventories of criteria air pollutants, precursors, greenhouse gas emissions, and some mobile source air toxics from highway vehicles. Additionally, MOVES can make projections for energy consumption (total, petroleum-based, and fossilbased). PPSUITE: For the Department s highway emissions inventory, a post processor named PPSUITE (formerly named PPAQ - Post Processor for Air Quality) is used, which consists of a set of programs that perform the following functions: Analyzes highway operating conditions. Calculates highway speeds. Compiles vehicle miles of travel (VMT) and vehicle type mix data. Prepares MOVES runs and processes MOVES outputs. PPSUITE is a widely used and accepted tool for estimating speeds and processing emissions rates. The software is based upon accepted transportation engineering methodologies. For example, PPSUITE uses speed and delay estimation procedures based on planning methods provided in the Highway Capacity Manual, a report prepared by the Transportation Research Board (TRB) summarizing current knowledge and analysis techniques for capacity and level-of-service analyses of the transportation system. Appendix B2 B - 16

56 Technical Appendix B - Onroad Emissions Technical Support Document The PPSUITE process is integral to producing key input files to the MOVES emission model. Exhibit 1 summarizes the key functions of PPSUITE and the traffic-related input files prepared for the MOVES County Data Manager (CDM). Exhibit 1: Summary of PPSUITE Process The following sections summarize the key data and methodologies used to produce the mobile source emissions inventory. This includes a summary of local data sources and a step-by-step review of the speed calculation process. The emission data and process has been developed according to recommendations provided by EPA in key policy and technical guidance as provided below: Policy Guidance on the Use of MOVES214 for State Implementation Plan Development, Transportation Conformity, and Other Purposes, US EPA Office of Transportation and Air Quality, EPA-42-B-14-8, July 214. Instructions for Using LEV and NLEV Inputs for MOVES214, US EPA Office of Transportation and Air Quality, EPA-42-B-14-6a, October 214. MOVES214a User Guide, US EPA Office of Transportation and Air Quality, EPA-42- B-15-95, November 215. MOVES214 and MOVES214a Technical Guidance: Using MOVES to Prepare Emission Inventories for State Implementation Plans and Transportation Conformity, US EPA Office of Transportation and Air Quality, EPA-42-B-15-93, November 215. The process has focused on developing an emissions inventory using the available tools and data to its fullest extent. This includes the use of available local data for items that have a significant impact on emissions and applying a robust calculation process to estimate hourly traffic speeds. Appendix B2 B - 17

57 Technical Appendix B - Onroad Emissions Technical Support Document WHERE DOES PENNSYLVANIA OBTAIN ITS DATA? Summary of MOVES Inputs A large number of inputs to MOVES are needed to fully account for the numerous vehicle and environmental parameters that affect emissions. These include traffic flow characteristics (as determined from the PPSUITE software), vehicle descriptions, fuel parameters, inspection/maintenance program parameters, and environmental variables. MOVES includes a default national database of meteorology, vehicle fleet, vehicle activity, fuel, and emission control program data for every county; but EPA cannot certify that the default data is the most current or best available information for any specific area. As a result, local data is recommended for use for analyses supporting state implementation plans (SIPs). A mix of local and default data is used for this inventory. Local data sources are used for all inputs that have a significant impact on calculated emission rates. Exhibit 2 summarizes Pennsylvania-specific inputs assembled and used for this inventory. These data items are discussed in the following sections. Exhibit 2: MOVES Local Data Input Summary Traffic Vehicle Fuel Inspection Environmental Data Descriptions Parameters Maintenance Variables Vehicle Type Vehicle Type RVP Start Year Hourly VMT Mix Model Years Temperatures Vehicle Vehicle Age Sulfur Test Standards, Population Distribution Level Source Types, Humidity Frequency VMT Average Speeds Ethanol Stringency, Fractions (PPSUITE) Volume Waiver Rate, (PPSUITE) Compliance Road Type Hourly Refueling Distribution Distributions Controls (PPSUITE) Ramp Fraction (PPSUITE) Emission Rates Appendix B2 B - 18

58 Technical Appendix B - Onroad Emissions Technical Support Document Vehicle Miles of Travel (VMT) The VMT input to emissions calculations for Pennsylvania is based on information from the Roadway Management System (RMS) maintained by the Pennsylvania Department of Transportation s (PennDOT s) Bureau of Planning and Research (BPR). PennDOT obtains this information from periodic visual and electronic traffic counts. RMS data is dynamic, since it is continually reviewed and updated from new traffic counts and field visits conducted by PennDOT. Information on roadways included in the National Highway System is reviewed at least annually, while information on other roadways is reviewed at least biennially. On a triennial basis, a current snapshot of the RMS database is taken and downloaded to provide an upto-date record of the Commonwealth s highway system for estimating emissions. This emissions inventory is based on the most current snapshot of the RMS data. The RMS database contains all state highways, including the Pennsylvania Turnpike, divided into segments approximately.5 miles in length. These segments are usually divided at important intersections or locations where there is a change in the physical characteristics of the roadway (e.g. the number of lanes changes). There are approximately 12, state highway segments for the 67 Pennsylvania counties contained in the RMS. Each of these segments contains an abundance of descriptive data, but only the following information is extracted for emission calculations: Lanes. Distances. Volumes representing Average Annual Daily Traffic (AADT). Truck percentages. PennDOT urban/rural classifications. PennDOT functional class codes. Number of signals (based on linkage to PennDOT GIS signal location data). RMS volumes and distances are used in calculating highway VMT totals for each county. As discussed in the next section, adjustments are needed to convert the volumes to an average summer weekday, winter weekday, and monthly day. In addition, the traffic volumes must be forecast to support future year emission inventories. Lane values and traffic signals are an important input for determining the congestion and speeds for individual highway segments. Truck percentages are used in the speed determination process and are used to split volumes to individual vehicle types used by the MOVES software. Road segments are classified by function, as well as whether it is located in an urban, small urban or rural area, as indicated below in Exhibit 3. The PennDOT urban/rural (UR) and functional classes (FC) are important indicators of the type and function of each roadway segment. The variables provide insights into other characteristics not contained in the RMS data that are used for speed and emission calculations. Appendix B2 B - 19

59 Technical Appendix B - Onroad Emissions Technical Support Document Exhibit 3: PennDOT Urban/Rural and Functional Class Codes Urban/Rural Code 1=Rural 2=Small Urban 3=Urban Functional Class Rural Functional Classes Used Urban Functional Classes Used For Rural Areas For Small Urban and Urban Areas =Rural Freeway 11=Urban Freeway 2=Rural Other Principal Arterial 12=Urban Expressway 6=Rural Minor Arterial 14=Urban Principal Arterial 7=Rural Major Collector 16=Urban Minor Arterial 8=Rural Minor Collector 17=Urban Collector 9=Rural Local 19=Urban Local Additional Network Information: The PPSUITE software system allows for many additional variables other than those available in the RMS database. Using these variables improves the ability of the Department to incorporate real roadway conditions into its estimates. The variables include information regarding free-flow speeds and capacities, signal characteristics and other physical roadway features that can affect a roadway s calculated congested speed. This data can be determined from lookup tables based on a roadway segment s urban/rural code and functional class. Much of the lookup table data was developed from information contained in the Highway Capacity Manual, PennDOT information on speeds and signal densities, and other engineering judgment. MOVES Traffic Inputs: The PPSUITE software uses RMS traffic data to prepare key inputs to the MOVES emission model including: VMT. Travel speeds. Road type distributions. Ramp fractions. VMT is the primary traffic input that affects emission results. The roadway segment distances and traffic volumes are used to prepare estimates of VMT. PPSUITE performs these calculations and outputs the MOVES annual VMT input file to the CDM. In MOVES, typical drive cycles and associated operating conditions vary by the type of roadway. MOVES defines five different road types as follows: 1 Off-Network. 2 Rural Restricted Access. 3 Rural Unrestricted Access. 4 Urban Restricted Access. 5 Urban Unrestricted Access. The off-network road type includes emissions from vehicle starts, extended idle activity, and evaporative emissions. Off-network activity in MOVES is primarily determined by the Source Type Population input, as discussed in a following section. The remaining distribution among road types is determined by equating the PennDOT functional class with each MOVES road type as follows: Appendix B2 B - 2

60 Technical Appendix B - Onroad Emissions Technical Support Document MOVES Road Type (2) = PennDOT Functional Class (1). MOVES Road Type (3) = PennDOT Functional Class (2,6,7,8,9). MOVES Road Type (4) = PennDOT Functional Class (11,12). MOVES Road Type (5) = PennDOT Functional Class (14,16,17,19). For this inventory, the MOVES road type distribution file is automatically generated by PPSUITE using the defined equivalencies. Since ramps are not directly represented within the RMS database information, it is assumed that 8% of the Freeway VHT is Ramp VHT. This is consistent with the recommendations provided in EPA s technical guidance. Adjustments to Roadway Data Before the RMS data can be used by PPSUITE for speed and emission calculations, several adjustments and additions must be made to the roadway data. These adjustments are summarized below. HPMS Adjustments: According to EPA guidance, baseline inventory VMT computed from the RMS highway segment volumes must be adjusted to be consistent with Highway Performance Monitoring System (HPMS) VMT totals. The HPMS VMT reported for Pennsylvania is a subsystem of the RMS established to meet the data reporting requirements of the Federal Highway Administration (FHWA) and to serve as PennDOT s official source of highway information. Although it has some limitations, the HPMS system is currently in use in all 5 states and is being improved under FHWA direction. Although the HPMS VMT and the roadway data used for an inventory emissions analysis are both based on data from the RMS system, differences do exist between them and include the following. First, the HPMS and inventory roadway data are snapshots of the RMS data taken at different times. Since the RMS is dynamic, changing constantly due to new data, differences will result between the data used for calculating HPMS VMT totals and the inventory data used for an emissions analysis. Second, since the RMS does not contain many of the local roadways, local road estimates of HPMS VMT are obtained through alternative procedures developed by PennDOT. To account for such differences, adjustment factors are calculated and used to adjust the inventory roadway data to the reported HPMS VMT totals submitted to FHWA. The VMT contained in the HPMS reports are considered to represent average annual daily traffic (AADT). Adjustment factors are calculated which adjust the base year RMS download VMT to the reported HPMS totals for that year. These factors are developed for each county and functional class combination and are also applied to all future year runs. Adjustments for the higher functional classes (e.g. Freeway, Arterials - major routes) are close to 1. since HPMS VMT is derived from RMS information, and the only difference in the data is that the snapshot for the emission calculations is taken at a different time than for the HPMS. Lower classes (e.g. local roads) require greater adjustment since a large part of the local system is not under state jurisdiction and is not in the RMS database. There is, of course, a significant amount of local road mileage in the state. It is assumed that those local streets that are in RMS are representative of all local streets in their area with respect to volume and speed, so that roadway mileage adjustment is appropriate. Seasonal Adjustments to Volumes: The RMS contains AADT volumes that are an average of all days in the year, including weekends and holidays. An ozone emission analysis, however, is based on a typical July or summer weekday. PM and CO analyses require volumes representing a typical summer weekday, winter weekday and/or annual average daily conditions (needed for producing annual totals). Therefore, Appendix B2 B - 21

61 Technical Appendix B - Onroad Emissions Technical Support Document the RMS volumes must be seasonally adjusted. Seasonal factors were developed for each functional class and urban/rural code based on yearly count information prepared by PennDOT s BPR. These factors are applied to the existing RMS AADT volumes to produce the July volumes. The same factors are also used to develop the MOVES daily and monthly VMT fraction files. Hourly Adjustments: Speeds and emissions vary considerably depending on the time of day. Therefore, it is important to estimate the pattern by which roadway volume varies by hour of the day. The 24-hour pattern data provides PPSUITE with information used to split the daily roadway segment volumes to each of the 24 hours in a day. Pattern data is in the form of a percentage of the daily volumes for each hour. Distributions are provided for each county and functional class grouping. This data is developed from 24-hour count data compiled by PennDOT s BPR, according to the process in the agencies annual traffic data reports. The same factors are also used to develop the MOVES hourly fraction file. Traffic Volume Forecasts: Traffic growth forecasting plays a pivotal role in estimating future year emissions for the region. There are many uncertainties affecting projections of traffic growth, including the current economic conditions, potential fuel prices, the impacts of Marcellus Shale activities in many counties throughout the state, and the future growth in population and employment. Growth rates for the Department s emissions inventories are based on an assessment of available data sources which include: PennDOT BPR growth rate forecasting system. Regional travel model, if available. Estimates of Marcellus Shale related activity growth, if applicable. All SIP mobile source highway inventories include the review and assessment of county-specific growth rates from a PennDOT study originally completed in 25 and documented in the report, Statistical Evaluation of Projected Traffic Growth, Traffic Growth Forecasting System: Final Report, March 14, 25. As part of that study, a statewide traffic growth forecasting system was developed that incorporates traffic data from PennDOT s Traffic Information System and socioeconomic forecasts. That forecasting system is maintained by the PennDOT BPR and is updated on a periodic basis to develop new statistical relationships between historic VMT growth and population and updated demographic forecasts from Woods and Poole, Inc. The growth rates from the PennDOT BPR forecasting system are evaluated against other available data including travel model growth and other insights. Vehicle Type Processing Emission rates within MOVES vary significantly by the type of vehicle. The MOVES model produces emissions and rates by thirteen MOVES vehicle source types. However, VMT is input to MOVES by six HPMS vehicle groups. Exhibit 4 summarizes the distinction between each classification scheme. The process used for this inventory includes a method to disaggregate the RMS traffic volumes to the thirteen source types and then to recombine the estimates to the six HPMS vehicle classes. Vehicle type pattern data is used by PPSUITE to divide the hourly roadway segment volumes to the thirteen MOVES source types. Similar to the 24-hour pattern data, this data contains percentage splits to each source type for every hour of the day. The vehicle type pattern data for this inventory is developed from several sources of information: PennDOT truck percentages from the RMS database. Hourly distributions for trucks and total traffic compiled by PennDOT s BPR. Transit data from PennDOT and the National Transit Database. School bus registration data from PennDOT s Bureau of Motor Vehicles Registration Database. Appendix B2 B - 22

62 Technical Appendix B - Onroad Emissions Technical Support Document Exhibit 4: MOVES Source Types and HPMS Vehicle Groups SOURCE TYPES HPMS Class Groups 11 Motorcycle 1 Motorcycle 21 Passenger Car 25 Light Duty Vehicles 31 Passenger Truck 4 Buses 32 Light Commercial Truck 5 Single Unit Trucks 41 Intercity Bus 6 Combination Trucks 42 Transit Bus 43 School bus 51 Refuse Truck 52 Single Unit Short-haul Truck 53 Single Unit Long-haul Truck 54 Motor Home 61 Combination Short-haul Truck 62 Combination Long-haul Truck The vehicle type pattern data is developed for each county and functional class combination. First, RMS truck percentages are averaged for all roadways within a county and functional class grouping. Using this percentage data, the total roadway volume for any segment is divided to auto and truck vehicle type categories. The transit data and school bus data is used to further disaggregate trucks, resulting in four vehicle groups (light-duty, school, transit, and other heavy-duty). From these groups, MOVES default Pennsylvania county VMT distributions by source type are used to divide the four groups into each of the MOVES source types. PennDOT hourly distributions for trucks and total traffic are used to create source type percentage breakdowns for each hour of the day. Vehicle Type Capacity Analysis Factors: Vehicle type percentages are provided to the capacity analysis section of PPSUITE to adjust the speeds in response to trucks. That is, a given number of larger trucks take up more roadway space than a given number of cars, and this is accounted for in the speed estimation process by adjusting capacity using information from the Highway Capacity Manual. Vehicle Fleet and Population Data The information on the vehicle fleet including the number and age of vehicles has a significant impact on forecasted start and evaporative emissions within MOVES. The MOVES Model requires the population of vehicles by the thirteen source type categories. Pennsylvania county vehicle registration data is used to estimate vehicle population for light-duty vehicles, school buses and transit buses. The data is split to source types using MOVES214a default Pennsylvania county population data. Other heavy-duty vehicle population values are based on VMT for each source type using the vehicle mix and pattern data discussed previously. The PPSUITE software automatically applies default MOVES214a ratios of VMT and source type population (e.g. the number of miles per vehicle by source type) to the local VMT estimates to produce vehicle population for heavy duty trucks. Vehicle population is forecast based on projected household and population growth from Woods and Poole Inc. for each Pennsylvania county. The growth rate methodology includes: Choosing the highest growth rate between population and households. Limiting growth as to not exceed the VMT growth assumptions. Appendix B2 B - 23

63 Technical Appendix B - Onroad Emissions Technical Support Document Vehicle Age: Vehicle age distributions are input to MOVES for each county by the thirteen source types. The distributions reflect the percentage of vehicles in the fleet up to 31 years old. The most recent available registration download from PennDOT s Bureau of Motor Vehicles Registration Database has been used for the inventory. Due to insufficient data, only information for light-duty vehicles are used as local inputs; and, heavy-duty vehicles use the MOVES214a national default age distribution. The registration data download is based on MOBILE6.2 vehicle categories. As a result, the data was converted to source types using the EPA convertor spreadsheets provided with the MOVES model. Environmental, Fuel and Technology Assumptions Information on environmental, fuel, vehicle technology and other control strategy assumptions were determined based on a review of MOVES214a default information by the PaDEP. Fuel Parameters: The same vehicle will produce different emissions using a different type of gasoline. Fuel control strategies can be powerful emission reduction mechanisms. The MOVES214a default fuel formulation and fuel supply data were reviewed and updated based on available local volumetric fuel property information. Fuel Wizard was used to update the default fuel property for gasoline and gasolineethanol blends per EPA MOVES214a User Guide and Technical Guidance. The gasohol market penetration and RVP values were updated but MOVES214a default data was used for the remaining parameters. Refueling Emissions: MOVES also allows users to calculate refueling emissions, the emissions created when vehicles are refueled at service stations. Pennsylvania includes refueling emissions in its area source inventory and not in its highway vehicle inventory. Refueling emissions are not included in the highway emissions inventory. Vehicle Emission Inspection/Maintenance (I/M) Parameters: MOVES allows users to vary inputs depending on the I/M program in place for the area. The inputs include: Program start year and first and last model years subject to the program Waiver and compliance rates and stringency level Program type (test-only, test-and-repair, etc.) and effectiveness Frequency of inspection (annual, biennial) and vehicle type coverage Test type (idle, loaded, etc.) The MOVES default Pennsylvania assumptions were reviewed and modifications were made per actual program parameters. Environmental Variables: Ambient temperature and humidity are known to have a significant impact on most pollutant processes for on-road vehicles. In MOVES214a, temperature and humidity affect emissions through three mechanisms: 1) direct effect via a temperature adjustment on emission rates; 2) direct effect via a humidity correction factor for NOx; 3) indirect effect via an air conditioning adjustment for which temperature and relative humidity are used to populate a heat index which in turn is used to calculate the fraction of vehicle fleet with air conditioning turned on. Hourly temperatures have been compiled for each county based on information from WeatherBank, Inc. to specify temperatures from nine airports within the state. Ozone analysis temperature and humidity values were determined using the procedures documented in EPA s technical guidance. Minimum and maximum temperatures for each month were converted to hourly temperatures using EPA convertors supplied with the MOVES model. A summary of the MOVES related inputs used for the inventory and future year estimates are attached with the submission. Appendix B2 B - 24

64 Technical Appendix B - Onroad Emissions Technical Support Document SPEED/EMISSION ESTIMATION PROCEDURE The previous sections have summarized the input data used for computing speeds and emissions for Pennsylvania. This section explains how PPSUITE and MOVES uses that input data to produce emission estimates. Exhibit 5 summarizes PPSUITE s analysis procedure used for each of the RMS highway segments in the state. Producing an emissions inventory with PPSUITE requires a process of disaggregation and aggregation. Data is available and used on a very small scale -- individual ½ mile roadway segments 24 hours of the day. This data needs to be processed individually to determine the distribution of vehicle hours of travel (VHT) by speed and then aggregated by vehicle class to determine input VMT to the MOVES emission model. Volume/VMT Development Before speeds can be calculated and MOVES run, volumes acquired from RMS must be adjusted and disaggregated. Such adjustments include factoring to future years, seasonal adjustments, and disaggregating daily volumes to each hour of the day and to each of the thirteen MOVES source types. Determine Future Year Volumes: The RMS database contains up-to-date current year volumes. However, to conduct a future year analysis, these volumes must be factored to the year being analyzed. Growth factors have been prepared for each county and functional class grouping. These growth factors are applied to the base year RMS volumes to obtain future year estimates that can be utilized by PPSUITE. For this base year inventory, forecasting was not required. Example: A typical freeway link in the RMS database is I-8 segment 25 in Luzerne County, Pennsylvania. This link has an urban/rural code=1 which indicates the link is in a rural area, and a functional class=1 indicating a rural freeway. The average annual daily traffic (AADT) from the RMS database for this link in 28 is 12,77 vehicles/day. Growth factors have been developed to factor the 28 volume to future years. For example, to factor the 28 volume to the year 214, a growth factor of would yield: 214 volume = 12,77 vehicles/day x = 15,483 vehicles/day Appendix B2 B - 25

65 Technical Appendix B - Onroad Emissions Technical Support Document Exhibit 5: PPSUITE Speed / Emission Estimation Procedure Data From PPSUITE Input Files PPSUITE Analysis Process Data from Roadway Source (RMS) The Following is Performed For Each RMS Roadway Segment Percent Pattern Distributions Expand to 24 hourly volumes RMS AWDT Adjusted Volumes Apply VMT Adjustments (V/C thresholds for spreading) Adjust Volumes for Peak Spreading Vehicle Type Patterns Disaggregate to Vehicle Type RMS Truck Percentages Transit Data School Bus Data Speed/Capacity Lookup Table Calculate Link & Signal Capacities Calculate Link Calculate Midblock Speed Approach Delay Roadway Attributes (Lanes, FC code, UR code) Apply Post Speed VMT Adjustments Prepare MOVES CDM Files VHT by Annual Road Type Source Type Hourly Ramp Speed Bin VMT Fractions Population Fractions Fractions Per VMT <Default> <Trucks> Off-line File Preparation Vehicle Age Distribution Hourly Temps/Humidity I/M / Fuel Parameters Source Type Population Month/Day VMT Fractions Run MOVES Importer to convert county input data into MYSQL data format Run MOVES Appendix B2 B - 26

66 Technical Appendix B - Onroad Emissions Technical Support Document Seasonal Adjustments: PPSUITE takes the input daily volumes from RMS (which represents annual average daily traffic (AADT)) and seasonally adjusts the volumes to an average weekday in July. This adjustment utilizes factors developed for each functional class and urban/rural code. VMT can then be calculated for each link using the adjusted weekday volumes. Example: Again, assume the rural freeway link: I-8 segment 25 in Luzerne County, Pennsylvania. The AADT for this link in 28 is 12,77 vehicles/day. Seasonal factors have been developed for urban/rural code and functional class combinations. For an urban/rural code=1 and a functional class=1, the factor to convert from AADT to an average weekday in July is = Average Weekday July Volume = 12,77 x 1.15 = 13,889 vehicles/day. Total VMT (daily) for this link is calculated as volume x distance. The distance of this link as obtained from RMS is.296 miles. 28 VMT = 13,889 vehicles/day x.296 miles = 4,111 vehicle-miles / day. Disaggregation to 24 Hours: After seasonally adjusting the link volume, the volume is split to each hour of the day. This allows for more accurate speed calculations (effects of congested hours) and allows PPSUITE to prepare the hourly VMT and speeds for input to the MOVES model. Example: To support speed calculations and emission estimates by time of day, the July weekday volume is disaggregated to 24 hourly volumes. Temporal patterns were previously developed from PennDOT count data and input to PPSUITE. For the I-8 rural freeway link with morning peak volumes similar to evening peak hours (neutral), the following temporal pattern is applied: Percent of Daily Hour of Day 17 Using the I-8 segment, typical hourly volumes which result include: 8-9 a.m. 6.% x (4,111 vehicle miles/.296mi.) = 833 vehicles/hour (vph) 12-1 p.m. 5.% x (4,111 vehicle.miles/.296mi.) = 694 vph 5-6 p.m. 6.3% x (4,111 vehicle miles/.296mi.) = 875 vph Appendix B2 B - 27

67 Technical Appendix B - Onroad Emissions Technical Support Document After dividing the daily volumes to each hour of the day, PPSUITE identifies hours that are unreasonably congested. For those hours, PPSUITE then spreads a portion of the volume to other hours within the same peak period, thereby approximating the peak spreading that normally occurs in such over-capacity conditions. Disaggregation to Vehicle Type: EPA requires VMT estimates to be prepared by source type, reflecting specific local characteristics. As a result, for Pennsylvania s emission inventory runs, the hourly volumes are disaggregated to the thirteen MOVES source types based on count data assembled by PennDOT in combination with MOVES defaults. Example: Disaggregation of the total I-8 VMT to the various source types would include the following: Total Volume 8-9 am = 833 vph Source Type Volume 8-9 am: Motorcycle 11.5% 4 vph Passenger Car % 456 vph Passenger Truck % 232 vph Light Commercial Truck % 78 vph Intercity Bus 41.1% 1 vph Transit Bus 42.1% 1 vph School bus 43.1% 1 vph Refuse Truck 51.% vph Single Unit Short-haul Truck % 19 vph Single Unit Long-haul Truck 53.3% 2 vph Motor Home 54.1% 1 vph Combination Short-haul Truck % 16 vph Combination Long-haul Truck % 22 vph Speed/Delay Determination EPA recognizes that the estimation of vehicle speeds is a difficult and complex process. Because emissions are so sensitive to speeds, it recommends special attention be given to developing reasonable and consistent speed estimates; it also recommends that VMT be disaggregated into subsets that have roughly equal speed, with separate emission factors for each subset. At a minimum, speeds should be estimated separately by road type. The computational framework used for this analysis meets and exceeds that recommendation. Speeds are individually calculated for each roadway segment and hour and include the delays encountered at signals. Rather than accumulating the roadway segments into a particular road type and calculating an average speed, each individual link hourly speed is represented in the MOVES vehicle hours of travel (VHT) by speed bin file. This MOVES input file allows the specification of a distribution of hourly speeds. For example, if 5% of a county s arterial VHT operates at 5 mph during the AM peak hour and the remaining 95% operates at 65 mph, this can be represented in the MOVES speed input file. For the model runs, distributions of speeds are input to MOVES by road type and source type by each hour of the day; VMT and VHT is accumulated by the same groupings for the application of the emission factors to produce resulting emission totals. Appendix B2 B - 28

68 Technical Appendix B - Onroad Emissions Technical Support Document To calculate speeds, PPSUITE first obtains initial capacities (how much volume the roadway can serve before heavy congestion) and free-flow speeds (speeds assuming no congestion) from the speed/capacity lookup data. As described in previous sections, this data contains default roadway information indexed by the urban/rural code and functional class. For areas with known characteristics, values can be directly coded to the RMS database and the speed/capacity data can be overridden. However, for most areas where known information is not available, the speed/capacity lookups provide valuable default information regarding speeds, capacities, signal characteristics, and other capacity adjustment information used for calculating congested delays and speeds. An effort has been made to enhance the RMS data with traffic signal locations using other GIS signal data available from PennDOT s Bureau of Highway Safety and Traffic Engineering. Example: The speed/capacity lookup table is used to obtain important data used for link speed calculations. For the I-8 link with an urban/rural code = 1 (rural) and a functional class = 1 (freeway), the lookup table provides information including the following: freeflow speed = 65 mph capacity = 18 vph per lane number of signals = (per RMS linkage to GIS traffic signal locations) This information is used along with the physical characteristics of the roadway to calculate the delay (including congestion) to travel this link during each hour of the day: For example: The I-8 link is calculated to have a travel time, including delay of seconds for the 8-9am hour. Total travel time, in vehicle hours, for the 8-9am hour is calculated as: VHT (8-9am) = seconds x 833vph / 36 sec/hr = 4.12 vehicle hours. The result of this process is an estimated average travel time for each hour of the day for each highway segment. The average time can be multiplied by the volume to produce vehicle hours of travel (VHT). HPMS and VMT Adjustments Volumes must also be adjusted to account for differences with the HPMS VMT totals, as described previously. VMT adjustment factors are provided as input to PPSUITE, and are applied to each of the roadway segment volumes. These factors were developed from the latest HPMS download (conducted triennially); however, they are also applied to any future year runs. The VMT added or subtracted to the RMS database assumes the speeds calculated using the original volumes for each roadway segment for each hour of the day. Appendix B2 B - 29

69 Technical Appendix B - Onroad Emissions Technical Support Document Example: Using the Luzerne County I-8 rural freeway link example, the daily assigned volume is adjusted to account for reconciliation with the HPMS VMT. RMS VMT (in AADT) for Luzerne County rural freeways totals 962,559 vehicle miles in 28. HPMS VMT (in AADT) as supplied by PennDOT and reported to FHWA totals to 99,88 vehicle miles for the rural freeways. A factor is developed by dividing the HPMS VMT by the RMS VMT: HPMS adjustment factor for Luzerne County rural freeways = 99,88 / 962,559 = This factor is held constant in all future years. As an example, this adjustment is made to the I-8 freeway link VMT for the 8-9am hour after speed calculations are made, and produces the final July weekday VMT for this hour used for Ozone runs. I-8 Link VMT (8-9am) = 833vph x.296 miles x 1.29 = 254 vehicle miles/hour. MOVES Emissions Run After computing speeds and aggregating VMT and VHT, PPSUITE prepares traffic-related inputs needed to run EPA s MOVES software, which is used to estimate emission factors in grams of pollutant per vehicle mile and to produce total emissions based on input VMT to the model. The process uses MOVES214a, the latest officially released emissions model that was obtained directly from EPA. The MOVES inputs prepared by PPSUITE include the following: Vehicle Type VMT. Vehicle Population. VMT fractions. Average speed distributions. Road Type Distribution. Ramp Fractions. These files are text formatted files with a.csv extension. The files are provided as inputs within the MOVES county data importer. In addition the remaining MOVES input data including temperatures, I/M programs, fuel and vehicle ages are prepared manually outside of the PPSUITE process. The MOVES county importer is run in batch mode. This program converts all data files into the MYSQL formats used by the MOVES model. At that point a MOVES run specification file (.mrs) is created which specifies options and key data locations for the run. MOVES is then executed in batch mode. MOVES can be executed using either the inventory or rate-based approaches. For this highway emissions inventory, MOVES is applied using the inventory-based approach. Under this method, actual VMT and population are provided as inputs to the model; MOVES is responsible for producing the total emissions for the region. Under the rate-based approach, MOVES would produce emission factors, after which PPSUITE would apply the emission factors to the link data and calculate total regional emissions. Appendix B2 B - 3

70 Technical Appendix B - Onroad Emissions Technical Support Document RESOURCES MOVES model Modeling Page within EPA s Office of Mobile Sources Website ( contains a downloadable model, MOVES users guide and other information. Policy Guidance on the Use of MOVES214 for State Implementation Plan Development, Transportation Conformity, and Other Purposes, US EPA Office of Transportation and Air Quality, EPA-42-B-14-8, July 214. MOVES214a User Guide, US EPA Office of Transportation and Air Quality, EPA-42-B-15-95, November 215. Instructions for Using LEV and NLEV Inputs for MOVES214, US EPA Office of Transportation and Air Quality, EPA-42-B-14-6a, October 214. MOVES214 and MOVES214a Technical Guidance: Using MOVES to Prepare Emission Inventories for State Implementation Plans and Transportation Conformity, US EPA Office of Transportation and Air Quality, EPA-42-B-15-93, November 215. Traffic Engineering Highway Capacity Manual, Transportation Research Board, presents current knowledge and techniques for analyzing the transportation system. 214 Pennsylvania Traffic Data, PennDOT Bureau of Planning and Research. Appendix B2 B - 31

71 Technical Appendix B - Onroad Emissions Technical Support Document Highway Vehicle Inventory Glossary AADT: Average Annual Daily Traffic, average of ALL days. AWDT: Average Weekday Daily Traffic. Basic emission rates: MOBILE emission rates based on the applicable Federal emission standards and the emission control technologies characterizing the fleet in various model years. Emission rate or factor: Expresses the amount of pollution emitted per unit of activity. For highway vehicles, usually in grams of pollutant emitted per mile driven. FC: Functional code, applied in data management to road segments to identify their type (freeway, local, etc.). Fuel volatility: The ability of fuel components to evaporate, thus entering the atmosphere as pollution. Fuel volatility is usually measured as Reid Vapor Pressure (RVP) in pounds per square inch. The lower the RVP, the less volatile the fuel. Growth factor: Factor used to convert volumes to future years. HPMS: Highway Performance Monitoring System, PENNDOT s official source of highway information and a subset of RMS. I/M: Vehicle emissions inspection/maintenance programs ensure that vehicle emission controls are in good working order throughout the life of the vehicle. The programs require vehicles to be tested for emissions. Most vehicles that do not pass must be repaired. MOBILE: The model EPA has developed and which Pennsylvania uses to estimate emissions from highway vehicles. MOVES: The latest model EPA has developed with which Pennsylvania uses to estimate emissions from highway vehicles. Pattern data: Extrapolations of traffic patterns (such as how traffic volume on road segment types varies by time of day, or what kinds of vehicles tend to use a road segment type) from segments with observed data to similar segments. PPSUITE: Post-Processor for Air Quality, a set of programs that estimate speeds and processes MOBILE emission rates. RMS: Roadway Management System, a database maintained by PENNDOT from traffic counts and field visits. Segment (also referred to as link): Division of roadway in the PENNDOT Roadway Management System. Usually represents.5 mile segments of roadway. UR: Urban/rural code, applied in data management to identify whether a road segment is urban, small urban or rural. Appendix B2 B - 32

72 Technical Appendix B - Onroad Emissions Technical Support Document VHT: Vehicle hours traveled. VMT: Vehicle miles traveled. In modeling terms, it is the simulated traffic volumes times link length. Vehicle Type: One of eight types, distinguished primarily by fuel type and/or weight, used in MOBILE modeling. Source Type: One of thirteen types, distinguished primarily by weight, used in MOVES modeling. Road Type: Functional code, applied in data management to road segments to identify their type (rural/urban highways, rural/urban arterials, etc.) County Data Manager: User interface developed to simplify importing specific local data for a single county or a user-defined custom domain without requiring direct interaction with the underlying MySQL database. Appendix B2 B - 33

73 Technical Appendix B - Onroad Emissions Technical Support Document APPENDIX B-3 Pittsburgh-Beaver Valley Area Emission Summary Tables Appendix B July Weekday Emissions Existing Scenario Emission Summary Emission Summary by Road Type Emission Summary by Source Type Emission Summary by Process Appendix B July Weekday Emissions RVP 8.7 Scenario Emission Summary Emission Summary by Road Type Emission Summary by Source Type Emission Summary by Process Appendix B July Weekday Emissions RVP 1 Scenario Emission Summary Emission Summary by Road Type Emission Summary by Source Type Emission Summary by Process Appendix B July Weekday Emissions Existing Scenario Emission Summary Emission Summary by Road Type Emission Summary by Source Type Emission Summary by Process Appendix B July Weekday Emissions RVP 8.7 Scenario Emission Summary Emission Summary by Road Type Emission Summary by Source Type Emission Summary by Process Appendix B July Weekday Emissions RVP 1 Scenario Emission Summary Emission Summary by Road Type Emission Summary by Source Type Emission Summary by Process B - 34

74 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Annual Emissions Existing Scenario Emission Summary Emission Summary by Road Type Emission Summary by Source Type Emission Summary by Process Appendix B Annual Emissions EVP 8.7 Scenario Emission Summary Emission Summary by Road Type Emission Summary by Source Type Emission Summary by Process Appendix B Annual Emissions RVP 1 Scenario Emission Summary Emission Summary by Road Type Emission Summary by Source Type Emission Summary by Process Appendix B Annual Emissions Existing Scenario Emission Summary Emission Summary by Road Type Emission Summary by Source Type Emission Summary by Process Appendix B Annual Emissions RVP 8.7 Scenario Emission Summary Emission Summary by Road Type Emission Summary by Source Type Emission Summary by Process Appendix B Annual Emissions RVP 1 Scenario Emission Summary Emission Summary by Road Type Emission Summary by Source Type Emission Summary by Process B - 35

75 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary Summer Weekday (Tons/Day) Scenario: Existing (RVP 7.8) County VMT Speed (mph) NOx Allegheny 26,564, Armstrong 1,774, Beaver 4,236, Butler 6,, Fayette 2,974, Washington 6,864, Westmoreland 1,132, SPC MPO 58,547, Appendix B-3 B - 36

76 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Road Type Summer Weekday (Tons/Day) Scenario: Existing (RVP 7.8) County Road Type VMT Speed (mph) Allegheny Off-Network Rural Restricted Access N/A Rural Unrestricted Access 29, Urban Restricted Access 7,334, Urban Unrestricted Access 19,19, Total 26,564, County Road Type VMT Speed (mph) Armstrong Off-Network Rural Restricted Access N/A Rural Unrestricted Access 1,34, Urban Restricted Access 221, Urban Unrestricted Access 518, Total 1,774, County Road Type VMT Speed (mph) Beaver Off-Network Rural Restricted Access 184, Rural Unrestricted Access 867, Urban Restricted Access 722, Urban Unrestricted Access 2,461, Total 4,236, County Road Type VMT Speed (mph) Butler Off-Network Rural Restricted Access 896, Rural Unrestricted Access 2,134, Urban Restricted Access 74, Urban Unrestricted Access 2,229, Total 6,, County Road Type VMT Speed (mph) Fayette Off-Network Rural Restricted Access N/A Rural Unrestricted Access 1,477, Urban Restricted Access 445, Urban Unrestricted Access 1,51, Total 2,974, County Road Type VMT Speed (mph) Washington Off-Network Rural Restricted Access 1,843, Rural Unrestricted Access 1,534, Urban Restricted Access 1,469, Urban Unrestricted Access 2,17, Total 6,864, County Road Type VMT Speed (mph) Westmoreland Off-Network Rural Restricted Access 721, Rural Unrestricted Access 2,45, Urban Restricted Access 2,57, Urban Unrestricted Access 4,796, Total 1,132, Appendix B-3 B - 37

77 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Source Type Summer Weekday (Tons/Day) Scenario: Existing (RVP 7.8) County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Allegheny Motorcycle 172,235.6% %.12.6% Passenger Car 13,491, % % % Passenger Truck 8,93, % % % Light Commercial Truck 2,242, % % % Intercity Bus 3,778.%.%.4.2% Transit Bus 125,749.5%.6.6%.77 4.% School Bus 49,111.2%.4.3% % Refuse Truck 26,747.1%.1.1%.13.7% Single Unit Short-haul Truck 553, %.3 2.7% % Single Unit Long-haul Truck 3,337.1%.1.1%.7.4% Motor Home 21,85.1%.3.3%.6.3% Combination Short-haul Truck 213,712.8%.5.5% % Combination Long-haul Truck 729, % % % Total 26,564, 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Armstrong Motorcycle 11,278.6%.3 3.3%.1.6% Passenger Car 883, % % % Passenger Truck 582, % % % Light Commercial Truck 146, % % % Intercity Bus 186.%.%.1% Transit Bus 1,247.6%.5%.6 4.% School Bus 7,945.4%.1.7%.3 2.3% Refuse Truck 2,239.1%.1%.1.7% Single Unit Short-haul Truck 46, %.2 2.6%.9 6.2% Single Unit Long-haul Truck 2,519.1%.1%.1.3% Motor Home 1,761.1%.3%.3% Combination Short-haul Truck 17,861 1.%.5%.8 5.4% Combination Long-haul Truck 6, %.2 1.9% % Total 1,774,534 1.%.91 1.% % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Beaver Motorcycle 27,222.6%.7 3.9%.2.6% Passenger Car 2,132,36 5.3% % % Passenger Truck 1,47, % % % Light Commercial Truck 354, % % % Intercity Bus 551.%.%.1.2% Transit Bus 9,876.2%.3%.6 1.8% School Bus 5,142.1%.2%.2.7% Refuse Truck 5,1.1%.1%.2.7% Single Unit Short-haul Truck 15, %.6 3.1% % Single Unit Long-haul Truck 5,788.1%.1%.1.4% Motor Home 4,6.1%.1.3%.1.4% Combination Short-haul Truck 4,688 1.%.1.5%.2 5.9% Combination Long-haul Truck 138, %.7 4.2% % Total 4,236,297 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Butler Motorcycle 37,856.6%.9 3.2%.3.5% Passenger Car 2,965, % % % Passenger Truck 1,956, % % % Light Commercial Truck 492, % % % Intercity Bus 848.%.%.1.1% Transit Bus 11,617.2%.1.2%.7 1.2% School Bus 6,826.1%.2%.3.5% Refuse Truck 8,957.1%.1%.4.7% Single Unit Short-haul Truck 185, %.9 3.2% % Single Unit Long-haul Truck 1,183.2%.1%.2.4% Motor Home 7,76.1%.1.3%.2.4% Combination Short-haul Truck 71,68 1.2%.2.5% % Combination Long-haul Truck 244,87 4.1% % % Total 6,,841 1.% % % Appendix B-3 B - 38

78 Technical Appendix B - Onroad Emissions Technical Support Document County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Fayette Motorcycle 19,93.6%.5 3.2%.2.6% Passenger Car 1,495, % % % Passenger Truck 986, % % % Light Commercial Truck 248, % % % Intercity Bus 266.%.%.1% Transit Bus 7,55.3%.2%.4 1.8% School Bus 2,889.1%.1%.1.5% Refuse Truck 3,68.1%.1%.2.7% Single Unit Short-haul Truck 74, %.4 2.3% % Single Unit Long-haul Truck 4,127.1%.1%.1.3% Motor Home 2,852.1%.2%.1.3% Combination Short-haul Truck 28,895 1.%.1.4% % Combination Long-haul Truck 98,7 3.3%.3 1.7% % Total 2,974,27 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Washington Motorcycle 42,438.6%.9 3.4%.3.5% Passenger Car 3,324, % % % Passenger Truck 2,193, % % % Light Commercial Truck 552, %.3 11.% % Intercity Bus 3,87.%.1%.3.4% Transit Bus 3,44.%.1%.2.3% School Bus 19,2.3%.1.4%.9 1.3% Refuse Truck 12,316.2%.1%.6.8% Single Unit Short-haul Truck 254, % % % Single Unit Long-haul Truck 13,989.2%.1.2%.3.4% Motor Home 9,716.1%.1.5%.3.4% Combination Short-haul Truck 98,45 1.4%.2.7% % Combination Long-haul Truck 336, % % % Total 6,864,553 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Westmoreland Motorcycle 62,777.6% %.5.5% Passenger Car 4,917, % %.8 8.3% Passenger Truck 3,245, % % % Light Commercial Truck 817,55 8.1% % % Intercity Bus 1,866.%.%.2.2% Transit Bus 14,35.1%.1.2%.9.9% School Bus 5,449.1%.1%.3.3% Refuse Truck 18,162.2%.1%.8.9% Single Unit Short-haul Truck 375, % % % Single Unit Long-haul Truck 2,581.2%.1.2%.4.4% Motor Home 14,35.1%.2.5%.4.4% Combination Short-haul Truck 144, %.3.8%.67 7.% Combination Long-haul Truck 495,24 4.9% % % Total 1,132,824 1.% % % Appendix B-3 B - 39

79 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Process Summer Weekday (Tons/Day) Scenario: Existing (RVP 7.8) County Process Emissions Pct. Emissions Pct. Allegheny Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.4.3%.1.% Crankcase Start Exhaust.6.5%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Armstrong Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation.8 9.2%.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks.1 1.7%.% Crankcase Running Exhaust.3%.% Crankcase Start Exhaust.1.6%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total.91 1.% % County Process Emissions Pct. Emissions Pct. Beaver Running Exhaust % % Start Exhaust %.7 21.% Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.1.3%.% Crankcase Start Exhaust.1.5%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.3 1.7% % Auxiliary Power Exhaust.1%.1% Total % % County Process Emissions Pct. Emissions Pct. Butler Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks.29 1.%.% Crankcase Running Exhaust.1.3%.% Crankcase Start Exhaust.2.6%.% Crankcase Extended Idle Exhaust.1%.% Extended Idle Exhaust % % Auxiliary Power Exhaust.1.2%.2.3% Total % % Appendix B-3 B - 4

80 Technical Appendix B - Onroad Emissions Technical Support Document County Process Emissions Pct. Emissions Pct. Fayette Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.3%.% Crankcase Start Exhaust.1.6%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Washington Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.1.4%.% Crankcase Start Exhaust.1.5%.% Crankcase Extended Idle Exhaust.1.2%.% Extended Idle Exhaust.3 11.% % Auxiliary Power Exhaust.1.4%.4.5% Total % % County Process Emissions Pct. Emissions Pct. Westmoreland Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation.4 9.7%.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.2.4%.% Crankcase Start Exhaust.2.5%.% Crankcase Extended Idle Exhaust.1%.% Extended Idle Exhaust.2 4.8% % Auxiliary Power Exhaust.1.2%.3.3% Total % % Appendix B-3 B - 41

81 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary Summer Weekday (Tons/Day) Scenario: RVP 8.7 County VMT Speed (mph) NOx Allegheny 26,564, Armstrong 1,774, Beaver 4,236, Butler 6,, Fayette 2,974, Washington 6,864, Westmoreland 1,132, SPC MPO 58,547, Appendix B-3 B - 42

82 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Road Type Summer Weekday (Tons/Day) Scenario: RVP 8.7 County Road Type VMT Speed (mph) Allegheny Off-Network Rural Restricted Access N/A Rural Unrestricted Access 29, Urban Restricted Access 7,334, Urban Unrestricted Access 19,19, Total 26,564, County Road Type VMT Speed (mph) Armstrong Off-Network Rural Restricted Access N/A Rural Unrestricted Access 1,34, Urban Restricted Access 221, Urban Unrestricted Access 518, Total 1,774, County Road Type VMT Speed (mph) Beaver Off-Network Rural Restricted Access 184, Rural Unrestricted Access 867, Urban Restricted Access 722, Urban Unrestricted Access 2,461, Total 4,236, County Road Type VMT Speed (mph) Butler Off-Network Rural Restricted Access 896, Rural Unrestricted Access 2,134, Urban Restricted Access 74, Urban Unrestricted Access 2,229, Total 6,, County Road Type VMT Speed (mph) Fayette Off-Network Rural Restricted Access N/A Rural Unrestricted Access 1,477, Urban Restricted Access 445, Urban Unrestricted Access 1,51, Total 2,974, County Road Type VMT Speed (mph) Washington Off-Network Rural Restricted Access 1,843, Rural Unrestricted Access 1,534, Urban Restricted Access 1,469, Urban Unrestricted Access 2,17, Total 6,864, County Road Type VMT Speed (mph) Westmoreland Off-Network Rural Restricted Access 721, Rural Unrestricted Access 2,45, Urban Restricted Access 2,57, Urban Unrestricted Access 4,796, Total 1,132, Appendix B-3 B - 43

83 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Source Type Summer Weekday (Tons/Day) Scenario: RVP 8.7 County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Allegheny Motorcycle 172,235.6% %.12.6% Passenger Car 13,491, % % % Passenger Truck 8,93, % % % Light Commercial Truck 2,242, % % % Intercity Bus 3,778.%.%.4.2% Transit Bus 125,749.5%.6.6%.77 4.% School Bus 49,111.2%.4.3% % Refuse Truck 26,747.1%.1.1%.13.7% Single Unit Short-haul Truck 553, %.3 2.7% % Single Unit Long-haul Truck 3,337.1%.1.1%.7.4% Motor Home 21,85.1%.3.3%.6.3% Combination Short-haul Truck 213,712.8%.5.5% % Combination Long-haul Truck 729, % % % Total 26,564, 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Armstrong Motorcycle 11,278.6%.3 3.4%.1.6% Passenger Car 883, % % % Passenger Truck 582, % % % Light Commercial Truck 146, % % % Intercity Bus 186.%.%.1% Transit Bus 1,247.6%.5%.6 4.% School Bus 7,945.4%.1.7%.3 2.3% Refuse Truck 2,239.1%.1%.1.7% Single Unit Short-haul Truck 46, %.2 2.6%.9 6.2% Single Unit Long-haul Truck 2,519.1%.1%.1.3% Motor Home 1,761.1%.3%.3% Combination Short-haul Truck 17,861 1.%.5%.8 5.4% Combination Long-haul Truck 6, %.2 1.9% % Total 1,774,534 1.%.91 1.% % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Beaver Motorcycle 27,222.6%.7 4.%.2.6% Passenger Car 2,132,36 5.3% % % Passenger Truck 1,47, % % % Light Commercial Truck 354, % % % Intercity Bus 551.%.%.1.2% Transit Bus 9,876.2%.3%.6 1.8% School Bus 5,142.1%.2%.2.7% Refuse Truck 5,1.1%.1%.2.7% Single Unit Short-haul Truck 15, %.6 3.1% % Single Unit Long-haul Truck 5,788.1%.1%.1.4% Motor Home 4,6.1%.1.3%.1.4% Combination Short-haul Truck 4,688 1.%.1.5%.2 5.8% Combination Long-haul Truck 138, %.7 4.2% % Total 4,236,297 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Butler Motorcycle 37,856.6%.9 3.3%.3.5% Passenger Car 2,965, % % % Passenger Truck 1,956, % % % Light Commercial Truck 492, % % % Intercity Bus 848.%.%.1.1% Transit Bus 11,617.2%.1.2%.7 1.2% School Bus 6,826.1%.2%.3.5% Refuse Truck 8,957.1%.1%.4.7% Single Unit Short-haul Truck 185, %.9 3.2% % Single Unit Long-haul Truck 1,183.2%.1%.2.4% Motor Home 7,76.1%.1.3%.2.4% Combination Short-haul Truck 71,68 1.2%.2.5% % Combination Long-haul Truck 244,87 4.1% % % Total 6,,841 1.% % % Appendix B-3 B - 44

84 Technical Appendix B - Onroad Emissions Technical Support Document County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Fayette Motorcycle 19,93.6%.6 3.4%.2.6% Passenger Car 1,495, % % % Passenger Truck 986, % % % Light Commercial Truck 248, % % % Intercity Bus 266.%.%.1% Transit Bus 7,55.3%.2%.4 1.8% School Bus 2,889.1%.1%.1.5% Refuse Truck 3,68.1%.1%.2.7% Single Unit Short-haul Truck 74, %.4 2.3% % Single Unit Long-haul Truck 4,127.1%.1%.1.3% Motor Home 2,852.1%.2%.1.3% Combination Short-haul Truck 28,895 1.%.1.4% % Combination Long-haul Truck 98,7 3.3%.3 1.7% % Total 2,974,27 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Washington Motorcycle 42,438.6%.1 3.5%.3.5% Passenger Car 3,324, % % % Passenger Truck 2,193, % % % Light Commercial Truck 552, %.3 1.9% % Intercity Bus 3,87.%.1%.3.4% Transit Bus 3,44.%.1%.2.3% School Bus 19,2.3%.1.4%.9 1.2% Refuse Truck 12,316.2%.1%.6.8% Single Unit Short-haul Truck 254, % % % Single Unit Long-haul Truck 13,989.2%.1.2%.3.4% Motor Home 9,716.1%.1.5%.3.4% Combination Short-haul Truck 98,45 1.4%.2.7% % Combination Long-haul Truck 336, % % % Total 6,864,553 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Westmoreland Motorcycle 62,777.6% %.5.5% Passenger Car 4,917, % %.8 8.3% Passenger Truck 3,245, % % % Light Commercial Truck 817,55 8.1% % % Intercity Bus 1,866.%.%.2.2% Transit Bus 14,35.1%.1.2%.9.9% School Bus 5,449.1%.1%.3.3% Refuse Truck 18,162.2%.1%.8.9% Single Unit Short-haul Truck 375, % % % Single Unit Long-haul Truck 2,581.2%.1.2%.4.4% Motor Home 14,35.1%.2.5%.4.4% Combination Short-haul Truck 144, %.3.8% % Combination Long-haul Truck 495,24 4.9% % % Total 1,132,824 1.% % % Appendix B-3 B - 45

85 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Process Summer Weekday (Tons/Day) Scenario: RVP 8.7 County Process Emissions Pct. Emissions Pct. Allegheny Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.4.3%.1.% Crankcase Start Exhaust.6.5%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Armstrong Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation.8 9.3%.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks.1 1.7%.% Crankcase Running Exhaust.3%.% Crankcase Start Exhaust.1.6%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total.91 1.% % County Process Emissions Pct. Emissions Pct. Beaver Running Exhaust % % Start Exhaust.72 4.%.7 21.% Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.1.3%.% Crankcase Start Exhaust.1.5%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.3 1.7% % Auxiliary Power Exhaust.1%.1% Total % % County Process Emissions Pct. Emissions Pct. Butler Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.1.3%.% Crankcase Start Exhaust.2.5%.% Crankcase Extended Idle Exhaust.1%.% Extended Idle Exhaust % % Auxiliary Power Exhaust.1.2%.2.3% Total % % Appendix B-3 B - 46

86 Technical Appendix B - Onroad Emissions Technical Support Document County Process Emissions Pct. Emissions Pct. Fayette Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.3%.% Crankcase Start Exhaust.1.6%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Washington Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.1.4%.% Crankcase Start Exhaust.1.5%.% Crankcase Extended Idle Exhaust.1.2%.% Extended Idle Exhaust.3 11.% % Auxiliary Power Exhaust.1.4%.4.5% Total % % County Process Emissions Pct. Emissions Pct. Westmoreland Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation.4 9.7%.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.2.4%.% Crankcase Start Exhaust.2.5%.% Crankcase Extended Idle Exhaust.1%.% Extended Idle Exhaust.2 4.8% % Auxiliary Power Exhaust.1.2%.3.3% Total % % Appendix B-3 B - 47

87 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary Summer Weekday (Tons/Day) Scenario: RVP 1 County VMT Speed (mph) NOx Allegheny 26,564, Armstrong 1,774, Beaver 4,236, Butler 6,, Fayette 2,974, Washington 6,864, Westmoreland 1,132, SPC MPO 58,547, Appendix B-3 B - 48

88 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Road Type Summer Weekday (Tons/Day) Scenario: RVP 1 County Road Type VMT Speed (mph) Allegheny Off-Network Rural Restricted Access N/A Rural Unrestricted Access 29, Urban Restricted Access 7,334, Urban Unrestricted Access 19,19, Total 26,564, County Road Type VMT Speed (mph) Armstrong Off-Network Rural Restricted Access N/A Rural Unrestricted Access 1,34, Urban Restricted Access 221, Urban Unrestricted Access 518, Total 1,774, County Road Type VMT Speed (mph) Beaver Off-Network Rural Restricted Access 184, Rural Unrestricted Access 867, Urban Restricted Access 722, Urban Unrestricted Access 2,461, Total 4,236, County Road Type VMT Speed (mph) Butler Off-Network Rural Restricted Access 896, Rural Unrestricted Access 2,134, Urban Restricted Access 74, Urban Unrestricted Access 2,229, Total 6,, County Road Type VMT Speed (mph) Fayette Off-Network Rural Restricted Access N/A Rural Unrestricted Access 1,477, Urban Restricted Access 445, Urban Unrestricted Access 1,51, Total 2,974, County Road Type VMT Speed (mph) Washington Off-Network Rural Restricted Access 1,843, Rural Unrestricted Access 1,534, Urban Restricted Access 1,469, Urban Unrestricted Access 2,17, Total 6,864, County Road Type VMT Speed (mph) Westmoreland Off-Network Rural Restricted Access 721, Rural Unrestricted Access 2,45, Urban Restricted Access 2,57, Urban Unrestricted Access 4,796, Total 1,132, Appendix B-3 B - 49

89 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Source Type Summer Weekday (Tons/Day) Scenario: RVP 1 County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Allegheny Motorcycle 172,235.6% %.12.6% Passenger Car 13,491, % % % Passenger Truck 8,93, % % % Light Commercial Truck 2,242, % % % Intercity Bus 3,778.%.%.4.2% Transit Bus 125,749.5%.6.6%.77 4.% School Bus 49,111.2%.4.3% % Refuse Truck 26,747.1%.1.1%.13.7% Single Unit Short-haul Truck 553, %.3 2.7% % Single Unit Long-haul Truck 3,337.1%.1.1%.7.4% Motor Home 21,85.1%.3.3%.6.3% Combination Short-haul Truck 213,712.8%.5.5% % Combination Long-haul Truck 729, % % % Total 26,564, 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Armstrong Motorcycle 11,278.6%.3 3.6%.1.6% Passenger Car 883, % % % Passenger Truck 582, % % % Light Commercial Truck 146, % % % Intercity Bus 186.%.%.1% Transit Bus 1,247.6%.5%.6 4.% School Bus 7,945.4%.1.7%.3 2.3% Refuse Truck 2,239.1%.1%.1.7% Single Unit Short-haul Truck 46, %.2 2.5%.9 6.2% Single Unit Long-haul Truck 2,519.1%.1%.1.3% Motor Home 1,761.1%.3%.3% Combination Short-haul Truck 17,861 1.%.5%.8 5.4% Combination Long-haul Truck 6, %.2 2.% % Total 1,774,534 1.%.9 1.% % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Beaver Motorcycle 27,222.6%.8 4.3%.2.6% Passenger Car 2,132,36 5.3% % % Passenger Truck 1,47, % % % Light Commercial Truck 354, % % % Intercity Bus 551.%.%.1.2% Transit Bus 9,876.2%.3%.6 1.7% School Bus 5,142.1%.2%.2.7% Refuse Truck 5,1.1%.1%.2.7% Single Unit Short-haul Truck 15, %.5 3.1% % Single Unit Long-haul Truck 5,788.1%.1%.1.4% Motor Home 4,6.1%.1.3%.1.4% Combination Short-haul Truck 4,688 1.%.1.5%.2 5.8% Combination Long-haul Truck 138, %.7 4.2% % Total 4,236,297 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Butler Motorcycle 37,856.6%.1 3.5%.3.5% Passenger Car 2,965, % % % Passenger Truck 1,956, % % % Light Commercial Truck 492, % % % Intercity Bus 848.%.%.1.1% Transit Bus 11,617.2%.1.2%.7 1.2% School Bus 6,826.1%.2%.3.5% Refuse Truck 8,957.1%.1%.4.7% Single Unit Short-haul Truck 185, %.9 3.2% % Single Unit Long-haul Truck 1,183.2%.1%.2.4% Motor Home 7,76.1%.1.4%.2.4% Combination Short-haul Truck 71,68 1.2%.2.5% % Combination Long-haul Truck 244,87 4.1% % % Total 6,,841 1.% % % Appendix B-3 B - 5

90 Technical Appendix B - Onroad Emissions Technical Support Document County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Fayette Motorcycle 19,93.6%.6 3.6%.2.6% Passenger Car 1,495, % % % Passenger Truck 986, % % % Light Commercial Truck 248, % % % Intercity Bus 266.%.%.1% Transit Bus 7,55.3%.2%.4 1.8% School Bus 2,889.1%.1%.1.5% Refuse Truck 3,68.1%.1%.2.7% Single Unit Short-haul Truck 74, %.4 2.3% % Single Unit Long-haul Truck 4,127.1%.1%.1.3% Motor Home 2,852.1%.2%.1.3% Combination Short-haul Truck 28,895 1.%.1.4% % Combination Long-haul Truck 98,7 3.3%.3 1.7% % Total 2,974,27 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Washington Motorcycle 42,438.6%.1 3.7%.3.5% Passenger Car 3,324, % % % Passenger Truck 2,193, % % % Light Commercial Truck 552, %.3 1.9% % Intercity Bus 3,87.%.1%.3.4% Transit Bus 3,44.%.1%.2.3% School Bus 19,2.3%.1.4%.9 1.2% Refuse Truck 12,316.2%.1%.6.8% Single Unit Short-haul Truck 254, % % % Single Unit Long-haul Truck 13,989.2%.1.2%.3.4% Motor Home 9,716.1%.1.5%.3.4% Combination Short-haul Truck 98,45 1.4%.2.8% % Combination Long-haul Truck 336, % % % Total 6,864,553 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Westmoreland Motorcycle 62,777.6%.16 4.%.5.5% Passenger Car 4,917, % % % Passenger Truck 3,245, % % % Light Commercial Truck 817,55 8.1% %.7 7.2% Intercity Bus 1,866.%.%.2.2% Transit Bus 14,35.1%.1.2%.9.9% School Bus 5,449.1%.1%.3.3% Refuse Truck 18,162.2%.1%.8.9% Single Unit Short-haul Truck 375, % % % Single Unit Long-haul Truck 2,581.2%.1.2%.4.4% Motor Home 14,35.1%.2.5%.4.4% Combination Short-haul Truck 144, %.3.8% % Combination Long-haul Truck 495,24 4.9% % % Total 1,132,824 1.% % % Appendix B-3 B - 51

91 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Process Summer Weekday (Tons/Day) Scenario: RVP 1 County Process Emissions Pct. Emissions Pct. Allegheny Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.4.3%.1.% Crankcase Start Exhaust.6.5%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Armstrong Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation.8 9.3%.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks.1 1.7%.% Crankcase Running Exhaust.3%.% Crankcase Start Exhaust.1.6%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total.9 1.% % County Process Emissions Pct. Emissions Pct. Beaver Running Exhaust % % Start Exhaust.7 39.% % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.1.3%.% Crankcase Start Exhaust.1.5%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.3 1.7% % Auxiliary Power Exhaust.1%.1% Total % % County Process Emissions Pct. Emissions Pct. Butler Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.1.3%.% Crankcase Start Exhaust.1.5%.% Crankcase Extended Idle Exhaust.1%.% Extended Idle Exhaust % % Auxiliary Power Exhaust.1.2%.2.3% Total % % Appendix B-3 B - 52

92 Technical Appendix B - Onroad Emissions Technical Support Document County Process Emissions Pct. Emissions Pct. Fayette Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.3%.% Crankcase Start Exhaust.1.6%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Washington Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.1.4%.% Crankcase Start Exhaust.1.4%.% Crankcase Extended Idle Exhaust.1.2%.% Extended Idle Exhaust % % Auxiliary Power Exhaust.1.4%.4.5% Total % % County Process Emissions Pct. Emissions Pct. Westmoreland Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation.4 9.7%.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.2.4%.% Crankcase Start Exhaust.2.5%.% Crankcase Extended Idle Exhaust.1%.% Extended Idle Exhaust.2 4.8% % Auxiliary Power Exhaust.1.2%.3.3% Total % % Appendix B-3 B - 53

93 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary Summer Weekday (Tons/Day) Scenario: Existing (RVP 7.8) County VMT Speed (mph) NOx Allegheny 27,71, Armstrong 1,819, Beaver 4,336, Butler 6,41, Fayette 3,31, Washington 7,331, Westmoreland 1,51, SPC MPO 6,511, Appendix B-3 B - 54

94 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Road Type Summer Weekday (Tons/Day) Scenario: Existing (RVP 7.8) County Road Type VMT Speed (mph) Allegheny Off-Network Rural Restricted Access N/A Rural Unrestricted Access 215, Urban Restricted Access 7,828, Urban Unrestricted Access 19,28, Total 27,71, County Road Type VMT Speed (mph) Armstrong Off-Network Rural Restricted Access N/A Rural Unrestricted Access 1,63, Urban Restricted Access 236, Urban Unrestricted Access 52, Total 1,819, County Road Type VMT Speed (mph) Beaver Off-Network Rural Restricted Access 212, Rural Unrestricted Access 89, Urban Restricted Access 77, Urban Unrestricted Access 2,462, Total 4,336, County Road Type VMT Speed (mph) Butler Off-Network Rural Restricted Access 1,42, Rural Unrestricted Access 2,224, Urban Restricted Access 815, Urban Unrestricted Access 2,328, Total 6,41, County Road Type VMT Speed (mph) Fayette Off-Network Rural Restricted Access N/A Rural Unrestricted Access 1,512, Urban Restricted Access 475, Urban Unrestricted Access 1,43, Total 3,31, County Road Type VMT Speed (mph) Washington Off-Network Rural Restricted Access 2,129, Rural Unrestricted Access 1,585, Urban Restricted Access 1,585, Urban Unrestricted Access 2,3, Total 7,331, County Road Type VMT Speed (mph) Westmoreland Off-Network Rural Restricted Access 83, Rural Unrestricted Access 2,14, Urban Restricted Access 2,742, Urban Unrestricted Access 4,832, Total 1,51, Appendix B-3 B - 55

95 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Source Type Summer Weekday (Tons/Day) Scenario: Existing (RVP 7.8) County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Allegheny Motorcycle 175,386.6% % % Passenger Car 13,738, % % % Passenger Truck 9,66, % % % Light Commercial Truck 2,283, % % % Intercity Bus 3,628.%.%.2.2% Transit Bus 13,77.5%.4.5% % School Bus 5,157.2%.2.3% % Refuse Truck 27,592.1%.%.7.6% Single Unit Short-haul Truck 57, % % % Single Unit Long-haul Truck 31,288.1%.1.1%.4.4% Motor Home 21,735.1%.2.2%.4.4% Combination Short-haul Truck 22,29.8%.3.3% % Combination Long-haul Truck 752, % % % Total 27,71,741 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Armstrong Motorcycle 11,562.6%.3 4.5%.1 1.% Passenger Car 95, % % % Passenger Truck 597, % % % Light Commercial Truck 15, % %.8 9.2% Intercity Bus 189.%.%.1% Transit Bus 1,569.6%.4%.3 4.1% School Bus 8,98.4%.5%.2 2.5% Refuse Truck 2,276.1%.%.1.6% Single Unit Short-haul Truck 47, %.1 2.1%.5 6.1% Single Unit Long-haul Truck 2,586.1%.1%.3% Motor Home 1,814.1%.2%.4% Combination Short-haul Truck 18,33 1.%.3%.4 4.9% Combination Long-haul Truck 62, %.1 1.6% % Total 1,819,657 1.%.63 1.%.86 1.% County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Beaver Motorcycle 27,83.6%.7 5.3%.2 1.% Passenger Car 2,18, % % % Passenger Truck 1,438, % % % Light Commercial Truck 362,49 8.4% % % Intercity Bus 568.%.%.2% Transit Bus 1,282.2%.2%.3 1.8% School Bus 5,28.1%.2%.1.8% Refuse Truck 5,284.1%.1%.1.6% Single Unit Short-haul Truck 19, %.3 2.5% % Single Unit Long-haul Truck 6,1.1%.1%.1.4% Motor Home 4,171.1%.3%.1.4% Combination Short-haul Truck 42,296 1.%.4%.1 5.2% Combination Long-haul Truck 144, %.5 4.4% % Total 4,336,535 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Butler Motorcycle 4,348.6%.9 4.3%.3.8% Passenger Car 3,16, % %.35 9.% Passenger Truck 2,85, % % % Light Commercial Truck 525, % % % Intercity Bus 942.%.%.1.1% Transit Bus 12,681.2%.2%.4 1.1% School Bus 7,368.1%.1%.2.5% Refuse Truck 9,773.2%.1%.2.6% Single Unit Short-haul Truck 22, %.5 2.6% % Single Unit Long-haul Truck 11,124.2%.1%.1.3% Motor Home 7,727.1%.1.3%.1.3% Combination Short-haul Truck 78, %.1.4% % Combination Long-haul Truck 267, %.2 9.5% % Total 6,41,221 1.% % % Appendix B-3 B - 56

96 Technical Appendix B - Onroad Emissions Technical Support Document County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Fayette Motorcycle 19,468.6%.5 4.3%.2 1.1% Passenger Car 1,525,4 5.3% % % Passenger Truck 1,6, % % % Light Commercial Truck 253, % % % Intercity Bus 295.%.%.1% Transit Bus 7,694.3%.2%.3 1.8% School Bus 2,92.1%.1%.1.5% Refuse Truck 3,688.1%.%.1.6% Single Unit Short-haul Truck 76, %.2 1.7%.8 5.9% Single Unit Long-haul Truck 4,157.1%.1%.3% Motor Home 2,91.1%.2%.3% Combination Short-haul Truck 29,445 1.%.3%.7 4.7% Combination Long-haul Truck 1,41 3.3%.2 1.3% % Total 3,31,981 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Washington Motorcycle 45,17.6%.9 4.6%.4.7% Passenger Car 3,538, % % % Passenger Truck 2,334, % % % Light Commercial Truck 588,212 8.%.2 1.1% % Intercity Bus 3,65.%.1%.2.4% Transit Bus 3,925.1%.1%.1.3% School Bus 2,573.3%.1.4%.6 1.2% Refuse Truck 13,52.2%.1%.3.6% Single Unit Short-haul Truck 279, %.7 3.6% % Single Unit Long-haul Truck 15,335.2%.1%.2.3% Motor Home 1,659.1%.1.4%.2.4% Combination Short-haul Truck 18,38 1.5%.1.5% % Combination Long-haul Truck 368,877 5.% % % Total 7,331,35 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Westmoreland Motorcycle 64,918.6%.14 5.%.5.8% Passenger Car 5,85, % %.48 8.% Passenger Truck 3,355, % % % Light Commercial Truck 845,359 8.% % % Intercity Bus 2,86.%.%.1.2% Transit Bus 14,878.1%.1%.5.9% School Bus 5,76.1%.1%.2.3% Refuse Truck 19,297.2%.1%.4.7% Single Unit Short-haul Truck 399,32 3.8% % % Single Unit Long-haul Truck 21,98.2%.1%.2.4% Motor Home 15,222.1%.1.4%.3.4% Combination Short-haul Truck 154,25 1.5%.2.5% % Combination Long-haul Truck 526,666 5.% % % Total 1,51,77 1.% % % Appendix B-3 B - 57

97 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Process Summer Weekday (Tons/Day) Scenario: Existing (RVP 7.8) County Process Emissions Pct. Emissions Pct. Allegheny Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.2.2%.% Crankcase Start Exhaust.4.6%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Armstrong Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation.5 8.2%.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.2%.% Crankcase Start Exhaust.6%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total.63 1.%.86 1.% County Process Emissions Pct. Emissions Pct. Beaver Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation.11 9.%.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.2%.% Crankcase Start Exhaust.1.5%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.3 2.3% % Auxiliary Power Exhaust.1%.1.3% Total % % County Process Emissions Pct. Emissions Pct. Butler Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.2%.% Crankcase Start Exhaust.1.5%.% Crankcase Extended Idle Exhaust.1%.% Extended Idle Exhaust.15 7.% % Auxiliary Power Exhaust.1.4%.3.9% Total % % Appendix B-3 B - 58

98 Technical Appendix B - Onroad Emissions Technical Support Document County Process Emissions Pct. Emissions Pct. Fayette Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.2%.% Crankcase Start Exhaust.1.6%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Washington Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.1.3%.% Crankcase Start Exhaust.1.4%.% Crankcase Extended Idle Exhaust.2%.% Extended Idle Exhaust % % Auxiliary Power Exhaust.2.9%.6 1.2% Total % % County Process Emissions Pct. Emissions Pct. Westmoreland Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.1.2%.% Crankcase Start Exhaust.1.5%.% Crankcase Extended Idle Exhaust.1%.% Extended Idle Exhaust % % Auxiliary Power Exhaust.1.4%.4.7% Total % % Appendix B-3 B - 59

99 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary Summer Weekday (Tons/Day) Scenario: RVP 8.7 County VMT Speed (mph) NOx Allegheny 27,71, Armstrong 1,819, Beaver 4,336, Butler 6,41, Fayette 3,31, Washington 7,331, Westmoreland 1,51, SPC MPO 6,511, Appendix B-3 B - 6

100 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Road Type Summer Weekday (Tons/Day) Scenario: RVP 8.7 County Road Type VMT Speed (mph) Allegheny Off-Network Rural Restricted Access N/A Rural Unrestricted Access 215, Urban Restricted Access 7,828, Urban Unrestricted Access 19,28, Total 27,71, County Road Type VMT Speed (mph) Armstrong Off-Network Rural Restricted Access N/A Rural Unrestricted Access 1,63, Urban Restricted Access 236, Urban Unrestricted Access 52, Total 1,819, County Road Type VMT Speed (mph) Beaver Off-Network Rural Restricted Access 212, Rural Unrestricted Access 89, Urban Restricted Access 77, Urban Unrestricted Access 2,462, Total 4,336, County Road Type VMT Speed (mph) Butler Off-Network Rural Restricted Access 1,42, Rural Unrestricted Access 2,224, Urban Restricted Access 815, Urban Unrestricted Access 2,328, Total 6,41, County Road Type VMT Speed (mph) Fayette Off-Network Rural Restricted Access N/A Rural Unrestricted Access 1,512, Urban Restricted Access 475, Urban Unrestricted Access 1,43, Total 3,31, County Road Type VMT Speed (mph) Washington Off-Network Rural Restricted Access 2,129, Rural Unrestricted Access 1,585, Urban Restricted Access 1,585, Urban Unrestricted Access 2,3, Total 7,331, County Road Type VMT Speed (mph) Westmoreland Off-Network Rural Restricted Access 83, Rural Unrestricted Access 2,14, Urban Restricted Access 2,742, Urban Unrestricted Access 4,832, Total 1,51, Appendix B-3 B - 61

101 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Source Type Summer Weekday (Tons/Day) Scenario: RVP 8.7 County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Allegheny Motorcycle 175,386.6% % % Passenger Car 13,738, % % % Passenger Truck 9,66, % % % Light Commercial Truck 2,283, % % % Intercity Bus 3,628.%.%.2.2% Transit Bus 13,77.5%.4.5% % School Bus 5,157.2%.2.3% % Refuse Truck 27,592.1%.%.7.6% Single Unit Short-haul Truck 57, % %.7 6.3% Single Unit Long-haul Truck 31,288.1%.1.1%.4.4% Motor Home 21,735.1%.2.2%.4.4% Combination Short-haul Truck 22,29.8%.3.3% % Combination Long-haul Truck 752, % % % Total 27,71,741 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Armstrong Motorcycle 11,562.6%.3 4.6%.1 1.% Passenger Car 95, % % % Passenger Truck 597, % % % Light Commercial Truck 15, % %.8 9.2% Intercity Bus 189.%.%.1% Transit Bus 1,569.6%.4%.3 4.% School Bus 8,98.4%.5%.2 2.5% Refuse Truck 2,276.1%.%.1.6% Single Unit Short-haul Truck 47, %.1 2.%.5 6.1% Single Unit Long-haul Truck 2,586.1%.1%.3% Motor Home 1,814.1%.2%.4% Combination Short-haul Truck 18,33 1.%.3%.4 4.9% Combination Long-haul Truck 62, %.1 1.6% % Total 1,819,657 1.%.63 1.%.86 1.% County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Beaver Motorcycle 27,83.6%.7 5.5%.2 1.% Passenger Car 2,18, % % % Passenger Truck 1,438, % % % Light Commercial Truck 362,49 8.4% % % Intercity Bus 568.%.%.2% Transit Bus 1,282.2%.2%.3 1.8% School Bus 5,28.1%.2%.1.8% Refuse Truck 5,284.1%.1%.1.6% Single Unit Short-haul Truck 19, %.3 2.5% % Single Unit Long-haul Truck 6,1.1%.1%.1.4% Motor Home 4,171.1%.3%.1.4% Combination Short-haul Truck 42,296 1.%.4%.1 5.2% Combination Long-haul Truck 144, %.5 4.4% % Total 4,336,535 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Butler Motorcycle 4,348.6%.9 4.4%.3.8% Passenger Car 3,16, % %.35 9.% Passenger Truck 2,85, % % % Light Commercial Truck 525, % % % Intercity Bus 942.%.%.1.1% Transit Bus 12,681.2%.2%.4 1.1% School Bus 7,368.1%.1%.2.5% Refuse Truck 9,773.2%.1%.2.6% Single Unit Short-haul Truck 22, %.5 2.6% % Single Unit Long-haul Truck 11,124.2%.1%.1.3% Motor Home 7,727.1%.1.3%.1.3% Combination Short-haul Truck 78, %.1.4% % Combination Long-haul Truck 267, %.2 9.6% % Total 6,41,221 1.% % % Appendix B-3 B - 62

102 Technical Appendix B - Onroad Emissions Technical Support Document County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Fayette Motorcycle 19,468.6%.6 4.5%.2 1.1% Passenger Car 1,525,4 5.3% % % Passenger Truck 1,6, % % % Light Commercial Truck 253, % % % Intercity Bus 295.%.%.1% Transit Bus 7,694.3%.2%.3 1.8% School Bus 2,92.1%.1%.1.5% Refuse Truck 3,688.1%.%.1.6% Single Unit Short-haul Truck 76, %.2 1.7%.9 5.9% Single Unit Long-haul Truck 4,157.1%.1%.3% Motor Home 2,91.1%.2%.3% Combination Short-haul Truck 29,445 1.%.3%.7 4.7% Combination Long-haul Truck 1,41 3.3%.2 1.3% % Total 3,31,981 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Washington Motorcycle 45,17.6%.9 4.7%.4.7% Passenger Car 3,538, % % % Passenger Truck 2,334, % % % Light Commercial Truck 588,212 8.%.2 1.% % Intercity Bus 3,65.%.1%.2.4% Transit Bus 3,925.1%.1%.1.3% School Bus 2,573.3%.1.4%.6 1.2% Refuse Truck 13,52.2%.1%.3.6% Single Unit Short-haul Truck 279, %.7 3.6% % Single Unit Long-haul Truck 15,335.2%.1%.2.3% Motor Home 1,659.1%.1.4%.2.4% Combination Short-haul Truck 18,38 1.5%.1.5% % Combination Long-haul Truck 368,877 5.% % % Total 7,331,35 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Westmoreland Motorcycle 64,918.6% %.5.8% Passenger Car 5,85, % %.48 8.% Passenger Truck 3,355, % % % Light Commercial Truck 845,359 8.% % % Intercity Bus 2,86.%.%.1.2% Transit Bus 14,878.1%.1%.5.9% School Bus 5,76.1%.1%.2.3% Refuse Truck 19,297.2%.1%.4.7% Single Unit Short-haul Truck 399,32 3.8% % % Single Unit Long-haul Truck 21,98.2%.1%.3.4% Motor Home 15,222.1%.1.4%.3.4% Combination Short-haul Truck 154,25 1.5%.2.5% % Combination Long-haul Truck 526,666 5.% % % Total 1,51,77 1.% % % Appendix B-3 B - 63

103 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Process Summer Weekday (Tons/Day) Scenario: RVP 8.7 County Process Emissions Pct. Emissions Pct. Allegheny Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.2.2%.% Crankcase Start Exhaust.4.5%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Armstrong Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation.5 8.3%.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.2%.% Crankcase Start Exhaust.6%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total.63 1.%.86 1.% County Process Emissions Pct. Emissions Pct. Beaver Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.2%.% Crankcase Start Exhaust.1.5%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.3 2.3% % Auxiliary Power Exhaust.1%.1.3% Total % % County Process Emissions Pct. Emissions Pct. Butler Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.2%.% Crankcase Start Exhaust.1.5%.% Crankcase Extended Idle Exhaust.1%.% Extended Idle Exhaust % % Auxiliary Power Exhaust.1.4%.3.9% Total % % Appendix B-3 B - 64

104 Technical Appendix B - Onroad Emissions Technical Support Document County Process Emissions Pct. Emissions Pct. Fayette Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.2%.% Crankcase Start Exhaust.1.6%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Washington Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks.3 15.%.% Crankcase Running Exhaust.1.3%.% Crankcase Start Exhaust.1.4%.% Crankcase Extended Idle Exhaust.2%.% Extended Idle Exhaust % % Auxiliary Power Exhaust.2.9%.6 1.2% Total % % County Process Emissions Pct. Emissions Pct. Westmoreland Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.1.2%.% Crankcase Start Exhaust.1.5%.% Crankcase Extended Idle Exhaust.1%.% Extended Idle Exhaust % % Auxiliary Power Exhaust.1.4%.4.7% Total % % Appendix B-3 B - 65

105 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary Summer Weekday (Tons/Day) Scenario: RVP 1 County VMT Speed (mph) NOx Allegheny 27,71, Armstrong 1,819, Beaver 4,336, Butler 6,41, Fayette 3,31, Washington 7,331, Westmoreland 1,51, SPC MPO 6,511, Appendix B-3 B - 66

106 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Road Type Summer Weekday (Tons/Day) Scenario: RVP 1 County Road Type VMT Speed (mph) Allegheny Off-Network Rural Restricted Access N/A Rural Unrestricted Access 215, Urban Restricted Access 7,828, Urban Unrestricted Access 19,28, Total 27,71, County Road Type VMT Speed (mph) Armstrong Off-Network Rural Restricted Access N/A Rural Unrestricted Access 1,63, Urban Restricted Access 236, Urban Unrestricted Access 52, Total 1,819, County Road Type VMT Speed (mph) Beaver Off-Network Rural Restricted Access 212, Rural Unrestricted Access 89, Urban Restricted Access 77, Urban Unrestricted Access 2,462, Total 4,336, County Road Type VMT Speed (mph) Butler Off-Network Rural Restricted Access 1,42, Rural Unrestricted Access 2,224, Urban Restricted Access 815, Urban Unrestricted Access 2,328, Total 6,41, County Road Type VMT Speed (mph) Fayette Off-Network Rural Restricted Access N/A Rural Unrestricted Access 1,512, Urban Restricted Access 475, Urban Unrestricted Access 1,43, Total 3,31, County Road Type VMT Speed (mph) Washington Off-Network Rural Restricted Access 2,129, Rural Unrestricted Access 1,585, Urban Restricted Access 1,585, Urban Unrestricted Access 2,3, Total 7,331, County Road Type VMT Speed (mph) Westmoreland Off-Network Rural Restricted Access 83, Rural Unrestricted Access 2,14, Urban Restricted Access 2,742, Urban Unrestricted Access 4,832, Total 1,51, Appendix B-3 B - 67

107 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Source Type Summer Weekday (Tons/Day) Scenario: RVP 1 County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Allegheny Motorcycle 175,386.6%.48 6.% % Passenger Car 13,738, % % % Passenger Truck 9,66, % % % Light Commercial Truck 2,283, % % % Intercity Bus 3,628.%.%.2.2% Transit Bus 13,77.5%.4.5% % School Bus 5,157.2%.2.3% % Refuse Truck 27,592.1%.%.7.6% Single Unit Short-haul Truck 57, %.16 2.%.7 6.3% Single Unit Long-haul Truck 31,288.1%.1.1%.4.4% Motor Home 21,735.1%.2.2%.4.4% Combination Short-haul Truck 22,29.8%.3.3% % Combination Long-haul Truck 752, % % % Total 27,71,741 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Armstrong Motorcycle 11,562.6%.3 4.9%.1 1.% Passenger Car 95, % % % Passenger Truck 597, %.3 48.% % Light Commercial Truck 15, % %.8 9.2% Intercity Bus 189.%.%.1% Transit Bus 1,569.6%.5%.3 4.% School Bus 8,98.4%.6%.2 2.5% Refuse Truck 2,276.1%.%.1.6% Single Unit Short-haul Truck 47, %.1 2.%.5 6.1% Single Unit Long-haul Truck 2,586.1%.1%.3% Motor Home 1,814.1%.2%.4% Combination Short-haul Truck 18,33 1.%.3%.4 4.8% Combination Long-haul Truck 62, %.1 1.6% % Total 1,819,657 1.%.62 1.%.86 1.% County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Beaver Motorcycle 27,83.6%.7 5.8%.2 1.% Passenger Car 2,18, % % % Passenger Truck 1,438, % % % Light Commercial Truck 362,49 8.4% % % Intercity Bus 568.%.%.2% Transit Bus 1,282.2%.2%.3 1.8% School Bus 5,28.1%.2%.1.8% Refuse Truck 5,284.1%.1%.1.6% Single Unit Short-haul Truck 19, %.3 2.5% % Single Unit Long-haul Truck 6,1.1%.1%.1.4% Motor Home 4,171.1%.3%.1.4% Combination Short-haul Truck 42,296 1.%.4%.1 5.2% Combination Long-haul Truck 144, %.5 4.5% % Total 4,336,535 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Butler Motorcycle 4,348.6%.1 4.7%.3.8% Passenger Car 3,16, % %.35 9.% Passenger Truck 2,85, % % % Light Commercial Truck 525, % % % Intercity Bus 942.%.%.1.1% Transit Bus 12,681.2%.2%.4 1.1% School Bus 7,368.1%.1%.2.5% Refuse Truck 9,773.2%.1%.2.6% Single Unit Short-haul Truck 22, %.5 2.6% % Single Unit Long-haul Truck 11,124.2%.1%.1.3% Motor Home 7,727.1%.1.3%.1.3% Combination Short-haul Truck 78, %.1.4% % Combination Long-haul Truck 267, %.2 9.6% % Total 6,41,221 1.% % % Appendix B-3 B - 68

108 Technical Appendix B - Onroad Emissions Technical Support Document County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Fayette Motorcycle 19,468.6%.6 4.8%.2 1.1% Passenger Car 1,525,4 5.3% % % Passenger Truck 1,6, % % % Light Commercial Truck 253, % % % Intercity Bus 295.%.%.1% Transit Bus 7,694.3%.2%.3 1.7% School Bus 2,92.1%.1%.1.5% Refuse Truck 3,688.1%.%.1.6% Single Unit Short-haul Truck 76, %.2 1.7%.9 5.9% Single Unit Long-haul Truck 4,157.1%.1%.3% Motor Home 2,91.1%.2%.3% Combination Short-haul Truck 29,445 1.%.3%.7 4.7% Combination Long-haul Truck 1,41 3.3%.2 1.3% % Total 3,31,981 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Washington Motorcycle 45,17.6%.1 5.%.4.7% Passenger Car 3,538, % % % Passenger Truck 2,334, % % % Light Commercial Truck 588,212 8.%.2 1.% % Intercity Bus 3,65.%.1%.2.4% Transit Bus 3,925.1%.1%.1.3% School Bus 2,573.3%.1.4%.6 1.2% Refuse Truck 13,52.2%.1%.3.6% Single Unit Short-haul Truck 279, %.7 3.6% % Single Unit Long-haul Truck 15,335.2%.1%.2.3% Motor Home 1,659.1%.1.4%.2.4% Combination Short-haul Truck 18,38 1.5%.1.5% % Combination Long-haul Truck 368,877 5.% % % Total 7,331,35 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Westmoreland Motorcycle 64,918.6% %.5.8% Passenger Car 5,85, % % % Passenger Truck 3,355, % % % Light Commercial Truck 845,359 8.% % % Intercity Bus 2,86.%.%.1.2% Transit Bus 14,878.1%.1%.5.9% School Bus 5,76.1%.1%.2.3% Refuse Truck 19,297.2%.1%.4.7% Single Unit Short-haul Truck 399,32 3.8%.1 3.6% % Single Unit Long-haul Truck 21,98.2%.1%.3.4% Motor Home 15,222.1%.1.4%.3.4% Combination Short-haul Truck 154,25 1.5%.2.5% % Combination Long-haul Truck 526,666 5.% % % Total 1,51,77 1.% % % Appendix B-3 B - 69

109 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Process Summer Weekday (Tons/Day) Scenario: RVP 1 County Process Emissions Pct. Emissions Pct. Allegheny Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.2.2%.% Crankcase Start Exhaust.4.5%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Armstrong Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation.5 8.3%.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.2%.% Crankcase Start Exhaust.6%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total.62 1.%.86 1.% County Process Emissions Pct. Emissions Pct. Beaver Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.2%.% Crankcase Start Exhaust.1.5%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.3 2.3% % Auxiliary Power Exhaust.1%.1.3% Total % % County Process Emissions Pct. Emissions Pct. Butler Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.2%.% Crankcase Start Exhaust.1.5%.% Crankcase Extended Idle Exhaust.1%.% Extended Idle Exhaust % % Auxiliary Power Exhaust.1.5%.3.9% Total % % Appendix B-3 B - 7

110 Technical Appendix B - Onroad Emissions Technical Support Document County Process Emissions Pct. Emissions Pct. Fayette Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.2%.% Crankcase Start Exhaust.1.6%.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Washington Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.3%.% Crankcase Start Exhaust.1.4%.% Crankcase Extended Idle Exhaust.2%.% Extended Idle Exhaust % % Auxiliary Power Exhaust.2.9%.6 1.2% Total % % County Process Emissions Pct. Emissions Pct. Westmoreland Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.1.2%.% Crankcase Start Exhaust.1.5%.% Crankcase Extended Idle Exhaust.1%.% Extended Idle Exhaust % % Auxiliary Power Exhaust.1.4%.4.7% Total % % Appendix B-3 B - 71

111 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary Annual (Tons/Year) Scenario: Existing (RVP 7.8) County VMT Speed (mph) NOx Allegheny 8,256,245, ,1.32 6, Armstrong 569,613, Beaver 1,33,487, , Butler 1,898,524, ,1.62 2,56.51 Fayette 952,747, Washington 2,159,687, , Westmoreland 3,185,821, , ,399.7 SPC MPO 18,353,126,378-9, ,42.8 Appendix B-3 B - 72

112 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Road Type Annual (Tons/Year) Scenario: Existing (RVP 7.8) County Road Type VMT Speed (mph) Allegheny Off-Network - - 3, , Rural Restricted Access N/A Rural Unrestricted Access 69,59, Urban Restricted Access 2,36,118, , Urban Unrestricted Access 5,827,67, , Total 8,256,245,17 4,1.32 6, County Road Type VMT Speed (mph) Armstrong Off-Network Rural Restricted Access N/A Rural Unrestricted Access 338,946, Urban Restricted Access 71,213, Urban Unrestricted Access 159,453, Total 569,613, County Road Type VMT Speed (mph) Beaver Off-Network Rural Restricted Access 56,887, Rural Unrestricted Access 286,76, Urban Restricted Access 232,416, Urban Unrestricted Access 755,16, Total 1,33,487, , County Road Type VMT Speed (mph) Butler Off-Network Rural Restricted Access 276,464, Rural Unrestricted Access 7,188, Urban Restricted Access 238,187, Urban Unrestricted Access 683,684, Total 1,898,524,94 1,1.62 2,56.51 County Road Type VMT Speed (mph) Fayette Off-Network Rural Restricted Access N/A Rural Unrestricted Access 483,332, Urban Restricted Access 143,459, Urban Unrestricted Access 325,954, Total 952,747, County Road Type VMT Speed (mph) Washington Off-Network Rural Restricted Access 568,172, Rural Unrestricted Access 55,333, Urban Restricted Access 472,996, Urban Unrestricted Access 613,184, Total 2,159,687, , County Road Type VMT Speed (mph) Westmoreland Off-Network - - 1, Rural Restricted Access 222,288, Rural Unrestricted Access 669,33, Urban Restricted Access 826,966, Urban Unrestricted Access 1,467,236, Total 3,185,821,677 1, ,399.7 Appendix B-3 B - 73

113 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Source Type Annual (Tons/Year) Scenario: Existing (RVP 7.8) County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Allegheny Motorcycle 53,486,52.6% % % Passenger Car 4,189,816, % 1, % % Passenger Truck 2,764,958, % 1, % 2, % Light Commercial Truck 696,512, % % % Intercity Bus 1,15,389.%.59.% 1.6.2% Transit Bus 39,594,293.5% 21..5% % School Bus 15,463,424.2% % % Refuse Truck 8,422,29.1% % % Single Unit Short-haul Truck 174,28,62 2.1% % % Single Unit Long-haul Truck 9,546,15.1% % % Motor Home 6,633,525.1% 9.8.2% % Combination Short-haul Truck 67,231,12.8% % % Combination Long-haul Truck 229,537, % % 1, % Total 8,256,245,17 1.% 4, % 6, % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Armstrong Motorcycle 3,617,712.6% % % Passenger Car 283,391, % % % Passenger Truck 187,14, % % % Light Commercial Truck 47,11,95 8.3% % % Intercity Bus 6,149.%.3.%.59.1% Transit Bus 3,318,139.6% % % School Bus 2,572,73.5% % % Refuse Truck 726,176.1%.21.1% % Single Unit Short-haul Truck 14,934, % % % Single Unit Long-haul Truck 821,285.1%.36.1% % Motor Home 569,267.1%.72.2% % Combination Short-haul Truck 5,764,162 1.% % % Combination Long-haul Truck 19,712, % % % Total 569,613,8 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Beaver Motorcycle 8,546,391.6% % % Passenger Car 669,47,66 5.3% % % Passenger Truck 441,87, % % % Light Commercial Truck 111,29, % % % Intercity Bus 152,439.%.9.% % Transit Bus 3,124,226.2% % % School Bus 1,626,711.1% 1.6.2% % Refuse Truck 1,611,422.1%.49.1% % Single Unit Short-haul Truck 33,183, % % % Single Unit Long-haul Truck 1,818,84.1%.83.1% % Motor Home 1,263,818.1% % % Combination Short-haul Truck 12,87,74 1.% % % Combination Long-haul Truck 43,783, % % % Total 1,33,487,46 1.% % 1, % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Butler Motorcycle 11,973,898.6% % % Passenger Car 937,963, % % % Passenger Truck 618,982, % % % Light Commercial Truck 155,927, % % % Intercity Bus 231,877.%.12.% % Transit Bus 3,76,636.2% % % School Bus 2,177,948.1% % % Refuse Truck 2,838,64.1%.79.1% % Single Unit Short-haul Truck 58,873,3 3.1% % % Single Unit Long-haul Truck 3,228,727.2% % % Motor Home 2,243,182.1% % % Combination Short-haul Truck 22,738, % % % Combination Long-haul Truck 77,638, % % % Total 1,898,524,94 1.% 1, % 2, % Appendix B-3 B - 74

114 Technical Appendix B - Onroad Emissions Technical Support Document County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Fayette Motorcycle 6,111,48.6% % % Passenger Car 478,73, % % % Passenger Truck 315,925, % % % Light Commercial Truck 79,584, % % % Intercity Bus 86,227.%.5.%.85.1% Transit Bus 2,446,35.3% % % School Bus 936,97.1%.99.2% % Refuse Truck 1,18,84.1%.35.1% % Single Unit Short-haul Truck 24,24, % % % Single Unit Long-haul Truck 1,329,753.1%.58.1% % Motor Home 921,77.1% % % Combination Short-haul Truck 9,345,62 1.% % % Combination Long-haul Truck 31,944, % % % Total 952,747,111 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Washington Motorcycle 13,349,512.6% % % Passenger Car 1,45,722, % % % Passenger Truck 69,89, % % % Light Commercial Truck 173,844,7 8.% % % Intercity Bus 853,83.%.42.% % Transit Bus 945,41.%.45.% % School Bus 6,31,623.3% % % Refuse Truck 3,882,34.2% 1.4.1% % Single Unit Short-haul Truck 8,35, % % % Single Unit Long-haul Truck 4,41,779.2% % % Motor Home 3,6,446.1% % 1.7.4% Combination Short-haul Truck 31,24,26 1.4% % % Combination Long-haul Truck 15,96, % % 1, % Total 2,159,687,57 1.% % 2, % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Westmoreland Motorcycle 19,72,474.6% % % Passenger Car 1,544,781, % % % Passenger Truck 1,19,44, % % % Light Commercial Truck 256,85, % % % Intercity Bus 53,219.%.28.% % Transit Bus 4,487,146.1% % % School Bus 1,741,961.1% % % Refuse Truck 5,743,921.2% % % Single Unit Short-haul Truck 118,859, % % % Single Unit Long-haul Truck 6,514,549.2% % % Motor Home 4,529,7.1% % % Combination Short-haul Truck 45,899, % % % Combination Long-haul Truck 156,766, % % 1, % Total 3,185,821,677 1.% 1, % 3, % Appendix B-3 B - 75

115 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Process Annual (Tons/Year) Scenario: Existing (RVP 7.8) County Process Emissions Pct. Emissions Pct. Allegheny Running Exhaust % 5, % Start Exhaust 2, % 1, % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust % 1.98.% Crankcase Start Exhaust %.8.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total 4, % 6, % County Process Emissions Pct. Emissions Pct. Armstrong Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.86.3%.16.% Crankcase Start Exhaust %.1.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Beaver Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.34.% Crankcase Start Exhaust %.1.% Crankcase Extended Idle Exhaust.19.%.2.% Extended Idle Exhaust % % Auxiliary Power Exhaust.34.1% % Total % 1, % County Process Emissions Pct. Emissions Pct. Butler Running Exhaust % 1, % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.57.% Crankcase Start Exhaust %.2.% Crankcase Extended Idle Exhaust.97.1%.1.% Extended Idle Exhaust % % Auxiliary Power Exhaust % % Total 1, % 2, % Appendix B-3 B - 76

116 Technical Appendix B - Onroad Emissions Technical Support Document County Process Emissions Pct. Emissions Pct. Fayette Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.24.% Crankcase Start Exhaust %.1.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Washington Running Exhaust % 1, % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.77.% Crankcase Start Exhaust 6.3.6%.2.% Crankcase Extended Idle Exhaust %.2.% Extended Idle Exhaust % % Auxiliary Power Exhaust % % Total % 2, % County Process Emissions Pct. Emissions Pct. Westmoreland Running Exhaust % 2, % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust % 1.11.% Crankcase Start Exhaust %.3.% Crankcase Extended Idle Exhaust %.13.% Extended Idle Exhaust % % Auxiliary Power Exhaust % % Total 1, % 3, % Appendix B-3 B - 77

117 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary Annual (Tons/Year) Scenario: RVP 8.7 County VMT Speed (mph) NOx Allegheny 8,256,245, , , Armstrong 569,613, Beaver 1,33,487, ,18.58 Butler 1,898,524, ,7.9 2,58.41 Fayette 952,747, Washington 2,159,687, ,585.6 Westmoreland 3,185,821, , ,42.63 SPC MPO 18,353,126,378-9, ,42.4 Appendix B-3 B - 78

118 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Road Type Annual (Tons/Year) Scenario: RVP 8.7 County Road Type VMT Speed (mph) Allegheny Off-Network - - 3, ,717.1 Rural Restricted Access N/A Rural Unrestricted Access 69,59, Urban Restricted Access 2,36,118, , Urban Unrestricted Access 5,827,67, , Total 8,256,245,17 3, , County Road Type VMT Speed (mph) Armstrong Off-Network Rural Restricted Access N/A Rural Unrestricted Access 338,946, Urban Restricted Access 71,213, Urban Unrestricted Access 159,453, Total 569,613, County Road Type VMT Speed (mph) Beaver Off-Network Rural Restricted Access 56,887, Rural Unrestricted Access 286,76, Urban Restricted Access 232,416, Urban Unrestricted Access 755,16, Total 1,33,487, ,18.58 County Road Type VMT Speed (mph) Butler Off-Network Rural Restricted Access 276,464, Rural Unrestricted Access 7,188, Urban Restricted Access 238,187, Urban Unrestricted Access 683,684, Total 1,898,524,94 1,7.9 2,58.41 County Road Type VMT Speed (mph) Fayette Off-Network Rural Restricted Access N/A Rural Unrestricted Access 483,332, Urban Restricted Access 143,459, Urban Unrestricted Access 325,954, Total 952,747, County Road Type VMT Speed (mph) Washington Off-Network Rural Restricted Access 568,172, Rural Unrestricted Access 55,333, Urban Restricted Access 472,996, Urban Unrestricted Access 613,184, Total 2,159,687, ,585.6 County Road Type VMT Speed (mph) Westmoreland Off-Network - - 1, Rural Restricted Access 222,288, Rural Unrestricted Access 669,33, Urban Restricted Access 826,966, Urban Unrestricted Access 1,467,236, Total 3,185,821,677 1, ,42.63 Appendix B-3 B - 79

119 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Source Type Annual (Tons/Year) Scenario: RVP 8.7 County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Allegheny Motorcycle 53,486,52.6% % % Passenger Car 4,189,816, % 1, % % Passenger Truck 2,764,958, % 1, % 2, % Light Commercial Truck 696,512, % % % Intercity Bus 1,15,389.%.59.% 1.6.2% Transit Bus 39,594,293.5% 21..5% % School Bus 15,463,424.2% % % Refuse Truck 8,422,29.1% % % Single Unit Short-haul Truck 174,28,62 2.1% % % Single Unit Long-haul Truck 9,546,15.1% % % Motor Home 6,633,525.1% 9.7.2% % Combination Short-haul Truck 67,231,12.8% % % Combination Long-haul Truck 229,537, % % 1, % Total 8,256,245,17 1.% 3, % 6, % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Armstrong Motorcycle 3,617,712.6% % % Passenger Car 283,391, % % % Passenger Truck 187,14, % % % Light Commercial Truck 47,11,95 8.3% % % Intercity Bus 6,149.%.3.%.59.1% Transit Bus 3,318,139.6% % % School Bus 2,572,73.5% % % Refuse Truck 726,176.1%.21.1% % Single Unit Short-haul Truck 14,934, % % % Single Unit Long-haul Truck 821,285.1%.36.1% % Motor Home 569,267.1%.72.2% % Combination Short-haul Truck 5,764,162 1.% % % Combination Long-haul Truck 19,712, % % % Total 569,613,8 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Beaver Motorcycle 8,546,391.6% % % Passenger Car 669,47,66 5.3% % % Passenger Truck 441,87, % % % Light Commercial Truck 111,29, % % % Intercity Bus 152,439.%.9.% % Transit Bus 3,124,226.2% % % School Bus 1,626,711.1% 1.6.2% % Refuse Truck 1,611,422.1%.49.1% 8.4.7% Single Unit Short-haul Truck 33,183, % % % Single Unit Long-haul Truck 1,818,84.1%.83.1% % Motor Home 1,263,818.1% % % Combination Short-haul Truck 12,87,74 1.% % % Combination Long-haul Truck 43,783, % % % Total 1,33,487,46 1.% % 1, % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Butler Motorcycle 11,973,898.6% % % Passenger Car 937,963, % % % Passenger Truck 618,982, % % % Light Commercial Truck 155,927, % % % Intercity Bus 231,877.%.12.% % Transit Bus 3,76,636.2% % % School Bus 2,177,948.1% % % Refuse Truck 2,838,64.1%.79.1% % Single Unit Short-haul Truck 58,873,3 3.1% % % Single Unit Long-haul Truck 3,228,727.2% % % Motor Home 2,243,182.1% % % Combination Short-haul Truck 22,738, % % % Combination Long-haul Truck 77,638, % % % Total 1,898,524,94 1.% 1,7.9 1.% 2, % Appendix B-3 B - 8

120 Technical Appendix B - Onroad Emissions Technical Support Document County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Fayette Motorcycle 6,111,48.6% % % Passenger Car 478,73, % % % Passenger Truck 315,925, % % % Light Commercial Truck 79,584, % % % Intercity Bus 86,227.%.5.%.85.1% Transit Bus 2,446,35.3% % % School Bus 936,97.1%.99.2% % Refuse Truck 1,18,84.1%.35.1% % Single Unit Short-haul Truck 24,24, % % % Single Unit Long-haul Truck 1,329,753.1%.58.1% % Motor Home 921,77.1% % % Combination Short-haul Truck 9,345,62 1.% % % Combination Long-haul Truck 31,944, % % % Total 952,747,111 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Washington Motorcycle 13,349,512.6% % % Passenger Car 1,45,722, % % % Passenger Truck 69,89, % % % Light Commercial Truck 173,844,7 8.% % % Intercity Bus 853,83.%.42.% % Transit Bus 945,41.%.45.% % School Bus 6,31,623.3% % % Refuse Truck 3,882,34.2% 1.4.1% % Single Unit Short-haul Truck 8,35, % % % Single Unit Long-haul Truck 4,41,779.2% % % Motor Home 3,6,446.1% % 1.8.4% Combination Short-haul Truck 31,24,26 1.4% % % Combination Long-haul Truck 15,96, % % 1, % Total 2,159,687,57 1.% % 2, % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Westmoreland Motorcycle 19,72,474.6% % % Passenger Car 1,544,781, % % % Passenger Truck 1,19,44, % % % Light Commercial Truck 256,85, % % % Intercity Bus 53,219.%.28.% % Transit Bus 4,487,146.1% % % School Bus 1,741,961.1% % % Refuse Truck 5,743,921.2% % % Single Unit Short-haul Truck 118,859, % % % Single Unit Long-haul Truck 6,514,549.2% % % Motor Home 4,529,7.1% % % Combination Short-haul Truck 45,899, % % % Combination Long-haul Truck 156,766, % % 1, % Total 3,185,821,677 1.% 1, % 3, % Appendix B-3 B - 81

121 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Process Annual (Tons/Year) Scenario: RVP 8.7 County Process Emissions Pct. Emissions Pct. Allegheny Running Exhaust % 5, % Start Exhaust 2, % 1, % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust % 1.98.% Crankcase Start Exhaust %.8.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total 3, % 6, % County Process Emissions Pct. Emissions Pct. Armstrong Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.85.3%.16.% Crankcase Start Exhaust %.1.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Beaver Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.34.% Crankcase Start Exhaust %.1.% Crankcase Extended Idle Exhaust.19.%.2.% Extended Idle Exhaust % % Auxiliary Power Exhaust.34.1% % Total % 1, % County Process Emissions Pct. Emissions Pct. Butler Running Exhaust % 1, % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.57.% Crankcase Start Exhaust %.2.% Crankcase Extended Idle Exhaust.97.1%.1.% Extended Idle Exhaust % % Auxiliary Power Exhaust % % Total 1,7.9 1.% 2, % Appendix B-3 B - 82

122 Technical Appendix B - Onroad Emissions Technical Support Document County Process Emissions Pct. Emissions Pct. Fayette Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.24.% Crankcase Start Exhaust %.1.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Washington Running Exhaust % 1, % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.77.% Crankcase Start Exhaust %.2.% Crankcase Extended Idle Exhaust %.2.% Extended Idle Exhaust % % Auxiliary Power Exhaust % % Total % 2, % County Process Emissions Pct. Emissions Pct. Westmoreland Running Exhaust % 2, % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust % 1.11.% Crankcase Start Exhaust %.3.% Crankcase Extended Idle Exhaust %.13.% Extended Idle Exhaust % % Auxiliary Power Exhaust % % Total 1, % 3, % Appendix B-3 B - 83

123 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary Annual (Tons/Year) Scenario: RVP 1 County VMT Speed (mph) NOx Allegheny 8,256,245, , , Armstrong 569,613, Beaver 1,33,487, , Butler 1,898,524, ,5.95 2,61.22 Fayette 952,747, Washington 2,159,687, , Westmoreland 3,185,821, , ,46.94 SPC MPO 18,353,126,378-9, , Appendix B-3 B - 84

124 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Road Type Annual (Tons/Year) Scenario: RVP 1 County Road Type VMT Speed (mph) Allegheny Off-Network - - 3, ,72.2 Rural Restricted Access N/A Rural Unrestricted Access 69,59, Urban Restricted Access 2,36,118, ,843.9 Urban Unrestricted Access 5,827,67, , Total 8,256,245,17 3, , County Road Type VMT Speed (mph) Armstrong Off-Network Rural Restricted Access N/A Rural Unrestricted Access 338,946, Urban Restricted Access 71,213, Urban Unrestricted Access 159,453, Total 569,613, County Road Type VMT Speed (mph) Beaver Off-Network Rural Restricted Access 56,887, Rural Unrestricted Access 286,76, Urban Restricted Access 232,416, Urban Unrestricted Access 755,16, Total 1,33,487, , County Road Type VMT Speed (mph) Butler Off-Network Rural Restricted Access 276,464, Rural Unrestricted Access 7,188, Urban Restricted Access 238,187, Urban Unrestricted Access 683,684, Total 1,898,524,94 1,5.95 2,61.22 County Road Type VMT Speed (mph) Fayette Off-Network Rural Restricted Access N/A Rural Unrestricted Access 483,332, Urban Restricted Access 143,459, Urban Unrestricted Access 325,954, Total 952,747, County Road Type VMT Speed (mph) Washington Off-Network Rural Restricted Access 568,172, Rural Unrestricted Access 55,333, Urban Restricted Access 472,996, Urban Unrestricted Access 613,184, Total 2,159,687, , County Road Type VMT Speed (mph) Westmoreland Off-Network - - 1, Rural Restricted Access 222,288, Rural Unrestricted Access 669,33, Urban Restricted Access 826,966, Urban Unrestricted Access 1,467,236, Total 3,185,821,677 1, ,46.94 Appendix B-3 B - 85

125 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Source Type Annual (Tons/Year) Scenario: RVP 1 County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Allegheny Motorcycle 53,486,52.6% % % Passenger Car 4,189,816, % 1, % % Passenger Truck 2,764,958, % 1, % 2, % Light Commercial Truck 696,512, % % % Intercity Bus 1,15,389.%.59.% 1.6.2% Transit Bus 39,594,293.5% 21..5% % School Bus 15,463,424.2% % % Refuse Truck 8,422,29.1% % % Single Unit Short-haul Truck 174,28,62 2.1% % % Single Unit Long-haul Truck 9,546,15.1% % % Motor Home 6,633,525.1% 9.1.2% % Combination Short-haul Truck 67,231,12.8% % % Combination Long-haul Truck 229,537, % % 1, % Total 8,256,245,17 1.% 3, % 6, % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Armstrong Motorcycle 3,617,712.6% % % Passenger Car 283,391, % % % Passenger Truck 187,14, % % % Light Commercial Truck 47,11,95 8.3% % % Intercity Bus 6,149.%.3.%.59.1% Transit Bus 3,318,139.6% % % School Bus 2,572,73.5% % % Refuse Truck 726,176.1%.21.1% % Single Unit Short-haul Truck 14,934, % % % Single Unit Long-haul Truck 821,285.1%.36.1% % Motor Home 569,267.1%.73.2% % Combination Short-haul Truck 5,764,162 1.% % % Combination Long-haul Truck 19,712, % % % Total 569,613,8 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Beaver Motorcycle 8,546,391.6% % % Passenger Car 669,47,66 5.3% % % Passenger Truck 441,87, % % % Light Commercial Truck 111,29, % % % Intercity Bus 152,439.%.9.% % Transit Bus 3,124,226.2% % % School Bus 1,626,711.1% 1.6.2% % Refuse Truck 1,611,422.1%.49.1% 8.4.7% Single Unit Short-haul Truck 33,183, % % % Single Unit Long-haul Truck 1,818,84.1%.83.1% % Motor Home 1,263,818.1% 1.7.3% % Combination Short-haul Truck 12,87,74 1.% % % Combination Long-haul Truck 43,783, % % % Total 1,33,487,46 1.% % 1, % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Butler Motorcycle 11,973,898.6% % % Passenger Car 937,963, % % % Passenger Truck 618,982, % % % Light Commercial Truck 155,927, % % % Intercity Bus 231,877.%.12.% % Transit Bus 3,76,636.2% % % School Bus 2,177,948.1% % % Refuse Truck 2,838,64.1%.79.1% % Single Unit Short-haul Truck 58,873,3 3.1% % % Single Unit Long-haul Truck 3,228,727.2% % % Motor Home 2,243,182.1% % % Combination Short-haul Truck 22,738, % % % Combination Long-haul Truck 77,638, % % % Total 1,898,524,94 1.% 1, % 2, % Appendix B-3 B - 86

126 Technical Appendix B - Onroad Emissions Technical Support Document County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Fayette Motorcycle 6,111,48.6% % % Passenger Car 478,73, % % % Passenger Truck 315,925, % % % Light Commercial Truck 79,584, % % % Intercity Bus 86,227.%.5.%.85.1% Transit Bus 2,446,35.3% % % School Bus 936,97.1%.99.2% % Refuse Truck 1,18,84.1%.35.1% % Single Unit Short-haul Truck 24,24, % % % Single Unit Long-haul Truck 1,329,753.1%.58.1% % Motor Home 921,77.1% % % Combination Short-haul Truck 9,345,62 1.% % % Combination Long-haul Truck 31,944, % % % Total 952,747,111 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Washington Motorcycle 13,349,512.6% % % Passenger Car 1,45,722, % % % Passenger Truck 69,89, % % % Light Commercial Truck 173,844,7 8.% % % Intercity Bus 853,83.%.42.% % Transit Bus 945,41.%.45.% % School Bus 6,31,623.3% % % Refuse Truck 3,882,34.2% 1.4.1% % Single Unit Short-haul Truck 8,35, % % % Single Unit Long-haul Truck 4,41,779.2% % % Motor Home 3,6,446.1% % 1.1.4% Combination Short-haul Truck 31,24,26 1.4% % % Combination Long-haul Truck 15,96, % % 1, % Total 2,159,687,57 1.% % 2, % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Westmoreland Motorcycle 19,72,474.6% % % Passenger Car 1,544,781, % % % Passenger Truck 1,19,44, % % % Light Commercial Truck 256,85, % % % Intercity Bus 53,219.%.28.% % Transit Bus 4,487,146.1% % % School Bus 1,741,961.1% % % Refuse Truck 5,743,921.2% % % Single Unit Short-haul Truck 118,859, % % % Single Unit Long-haul Truck 6,514,549.2% % % Motor Home 4,529,7.1% % % Combination Short-haul Truck 45,899, % % % Combination Long-haul Truck 156,766, % % 1, % Total 3,185,821,677 1.% 1, % 3, % Appendix B-3 B - 87

127 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Process Annual (Tons/Year) Scenario: RVP 1 County Process Emissions Pct. Emissions Pct. Allegheny Running Exhaust % 5, % Start Exhaust 2, % 1, % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust % 1.98.% Crankcase Start Exhaust %.8.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total 3, % 6, % County Process Emissions Pct. Emissions Pct. Armstrong Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.85.3%.16.% Crankcase Start Exhaust %.1.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Beaver Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.34.% Crankcase Start Exhaust %.1.% Crankcase Extended Idle Exhaust.19.%.2.% Extended Idle Exhaust % % Auxiliary Power Exhaust.34.1% % Total % 1, % County Process Emissions Pct. Emissions Pct. Butler Running Exhaust % 1, % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.57.% Crankcase Start Exhaust %.2.% Crankcase Extended Idle Exhaust.97.1%.1.% Extended Idle Exhaust % % Auxiliary Power Exhaust % % Total 1, % 2, % Appendix B-3 B - 88

128 Technical Appendix B - Onroad Emissions Technical Support Document County Process Emissions Pct. Emissions Pct. Fayette Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.24.% Crankcase Start Exhaust 4.8.8%.1.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Washington Running Exhaust % 1, % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.77.% Crankcase Start Exhaust 6.2.6%.2.% Crankcase Extended Idle Exhaust %.2.% Extended Idle Exhaust % % Auxiliary Power Exhaust % % Total % 2, % County Process Emissions Pct. Emissions Pct. Westmoreland Running Exhaust % 2, % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust % 1.11.% Crankcase Start Exhaust %.3.% Crankcase Extended Idle Exhaust %.13.% Extended Idle Exhaust % % Auxiliary Power Exhaust % % Total 1, % 3, % Appendix B-3 B - 89

129 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary Annual (Tons/Year) Scenario: Existing (RVP 7.8) County VMT Speed (mph) NOx Allegheny 8,419,778, , , Armstrong 584,28, Beaver 1,362,549, Butler 2,27,468, ,38.98 Fayette 971,67, Washington 2,35,999, , Westmoreland 3,35,748, , ,154.8 SPC MPO 18,977,36,478-6, , Appendix B-3 B - 9

130 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Road Type Annual (Tons/Year) Scenario: Existing (RVP 7.8) County Road Type VMT Speed (mph) Allegheny Off-Network - - 2, ,17.43 Rural Restricted Access N/A Rural Unrestricted Access 7,868, Urban Restricted Access 2,518,97, ,8.4 Urban Unrestricted Access 5,829,939, , Total 8,419,778,958 2, , County Road Type VMT Speed (mph) Armstrong Off-Network Rural Restricted Access N/A Rural Unrestricted Access 348,234, Urban Restricted Access 76,1, Urban Unrestricted Access 159,962, Total 584,28, County Road Type VMT Speed (mph) Beaver Off-Network Rural Restricted Access 65,512, Rural Unrestricted Access 293,437, Urban Restricted Access 248,6, Urban Unrestricted Access 755,539, Total 1,362,549, County Road Type VMT Speed (mph) Butler Off-Network Rural Restricted Access 321,289, Rural Unrestricted Access 729,759, Urban Restricted Access 262,484, Urban Unrestricted Access 713,935, Total 2,27,468, ,38.98 County Road Type VMT Speed (mph) Fayette Off-Network Rural Restricted Access N/A Rural Unrestricted Access 494,88, Urban Restricted Access 153,115, Urban Unrestricted Access 323,683, Total 971,67, County Road Type VMT Speed (mph) Washington Off-Network Rural Restricted Access 656,398, Rural Unrestricted Access 522,14, Urban Restricted Access 51,292, Urban Unrestricted Access 617,23, Total 2,35,999, , County Road Type VMT Speed (mph) Westmoreland Off-Network Rural Restricted Access 256,74, Rural Unrestricted Access 688,657, Urban Restricted Access 882,655, Urban Unrestricted Access 1,478,36, Total 3,35,748,27 1, ,154.8 Appendix B-3 B - 91

131 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Source Type Annual (Tons/Year) Scenario: Existing (RVP 7.8) County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Allegheny Motorcycle 54,52,339.6% % % Passenger Car 4,269,453,99 5.7% % % Passenger Truck 2,817,397, % 1, % 1, % Light Commercial Truck 79,746,57 8.4% % % Intercity Bus 979,15.%.36.% 6.1.2% Transit Bus 4,952,282.5% % % School Bus 15,79,965.2% % % Refuse Truck 8,68,539.1% 1.3.% % Single Unit Short-haul Truck 179,55,7 2.1% % % Single Unit Long-haul Truck 9,841,525.1% % % Motor Home 6,841,554.1% % % Combination Short-haul Truck 69,34,778.8% % % Combination Long-haul Truck 236,747, % % % Total 8,419,778,958 1.% 2, % 3, % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Armstrong Motorcycle 3,78,355.6% % % Passenger Car 29,493, % % % Passenger Truck 191,695, % % % Light Commercial Truck 48,293, % % % Intercity Bus 61,58.%.2.%.36.1% Transit Bus 3,441,987.6% 1.7.5% % School Bus 2,637,318.5% % % Refuse Truck 74,83.1%.1.% % Single Unit Short-haul Truck 15,422, % % % Single Unit Long-haul Truck 841,313.1%.18.1% 1.4.3% Motor Home 587,567.1%.46.2% % Combination Short-haul Truck 5,949,96 1.%.75.3% % Combination Long-haul Truck 2,334, % % % Total 584,28,243 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Beaver Motorcycle 8,741,814.6% % % Passenger Car 684,793, % % % Passenger Truck 451,893, % % % Light Commercial Truck 113,836, % % % Intercity Bus 157,216.%.6.%.97.1% Transit Bus 3,252,523.2% 1.2.2% % School Bus 1,67,243.1% 1.2.2% % Refuse Truck 1,66,281.1%.24.1% % Single Unit Short-haul Truck 34,512, % % % Single Unit Long-haul Truck 1,886,788.1%.42.1% % Motor Home 1,315,427.1% 1.8.2% % Combination Short-haul Truck 13,323,532 1.% % % Combination Long-haul Truck 45,55, % % % Total 1,362,549,823 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Butler Motorcycle 12,762,195.6% % % Passenger Car 999,732, % % % Passenger Truck 659,72, % % % Light Commercial Truck 166,188, % % % Intercity Bus 26,261.%.9.% % Transit Bus 4,43,694.2% % % School Bus 2,349,561.1% % % Refuse Truck 3,96,146.2%.41.1% % Single Unit Short-haul Truck 64,92, % % % Single Unit Long-haul Truck 3,56,94.2%.72.1% 4.3.3% Motor Home 2,442,893.1% % % Combination Short-haul Truck 24,753, % % % Combination Long-haul Truck 84,519, % % % Total 2,27,468,329 1.% % 1, % Appendix B-3 B - 92

132 Technical Appendix B - Onroad Emissions Technical Support Document County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Fayette Motorcycle 6,232,527.6% % % Passenger Car 488,227, % % % Passenger Truck 322,182, % % % Light Commercial Truck 81,157, % % % Intercity Bus 8,133.%.3.%.47.1% Transit Bus 2,54,152.3%.81.2% % School Bus 944,43.1%.66.1% 2.8.5% Refuse Truck 1,189,222.1%.17.% % Single Unit Short-haul Truck 24,693, % % % Single Unit Long-haul Truck 1,353,68.1%.29.1% % Motor Home 941,628.1%.74.2% % Combination Short-haul Truck 9,527,3 1.% % % Combination Long-haul Truck 32,573, % % % Total 971,67,628 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Washington Motorcycle 14,27,693.6% % % Passenger Car 1,112,968, % % % Passenger Truck 734,438,8 31.8% % % Light Commercial Truck 185,14,54 8.% % % Intercity Bus 1,12,288.%.31.% % Transit Bus 1,12,232.%.3.% % School Bus 6,74,171.3% % % Refuse Truck 4,261,653.2%.55.1% % Single Unit Short-haul Truck 88,1, % % % Single Unit Long-haul Truck 4,818,12.2%.98.1% % Motor Home 3,354,151.1% % % Combination Short-haul Truck 34,9, % % % Combination Long-haul Truck 116,62,47 5.% % % Total 2,35,999,29 1.% % 1, % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Westmoreland Motorcycle 2,4,23.6% % % Passenger Car 1,598,61, % % % Passenger Truck 1,54,549, % % % Light Commercial Truck 265,652,42 8.% % % Intercity Bus 576,453.%.19.% % Transit Bus 4,77,314.1% % % School Bus 1,829,592.1% 1.8.1% % Refuse Truck 6,11,929.2%.81.1% % Single Unit Short-haul Truck 126,453,86 3.8% % % Single Unit Long-haul Truck 6,931,71.2% % % Motor Home 4,818,742.1% % % Combination Short-haul Truck 48,838, % % % Combination Long-haul Truck 166,763,759 5.% % % Total 3,35,748,27 1.% 1, % 2, % Appendix B-3 B - 93

133 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Process Annual (Tons/Year) Scenario: Existing (RVP 7.8) County Process Emissions Pct. Emissions Pct. Allegheny Running Exhaust % 2, % Start Exhaust 1, % 1, % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.88.% Crankcase Start Exhaust %.5.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total 2, % 3, % County Process Emissions Pct. Emissions Pct. Armstrong Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.41.2%.7.% Crankcase Start Exhaust %.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Beaver Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.82.2%.15.% Crankcase Start Exhaust 3.3.7%.1.% Crankcase Extended Idle Exhaust.11.%.1.% Extended Idle Exhaust % % Auxiliary Power Exhaust.56.1% % Total % % County Process Emissions Pct. Emissions Pct. Butler Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.27.% Crankcase Start Exhaust %.1.% Crankcase Extended Idle Exhaust.55.1%.6.% Extended Idle Exhaust % % Auxiliary Power Exhaust % % Total % 1, % Appendix B-3 B - 94

134 Technical Appendix B - Onroad Emissions Technical Support Document County Process Emissions Pct. Emissions Pct. Fayette Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.62.1%.11.% Crankcase Start Exhaust %.1.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Washington Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.36.% Crankcase Start Exhaust %.1.% Crankcase Extended Idle Exhaust 1.4.1%.11.% Extended Idle Exhaust % % Auxiliary Power Exhaust % % Total % 1, % County Process Emissions Pct. Emissions Pct. Westmoreland Running Exhaust % 1, % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.5.% Crankcase Start Exhaust %.2.% Crankcase Extended Idle Exhaust.68.1%.7.% Extended Idle Exhaust % % Auxiliary Power Exhaust % % Total 1, % 2, % Appendix B-3 B - 95

135 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary Annual (Tons/Year) Scenario: RVP 8.7 County VMT Speed (mph) NOx Allegheny 8,419,778, , ,95.6 Armstrong 584,28, Beaver 1,362,549, Butler 2,27,468, , Fayette 971,67, Washington 2,35,999, , Westmoreland 3,35,748, , , SPC MPO 18,977,36,478-6, , Appendix B-3 B - 96

136 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Road Type Annual (Tons/Year) Scenario: RVP 8.7 County Road Type VMT Speed (mph) Allegheny Off-Network - - 2, ,17.74 Rural Restricted Access N/A Rural Unrestricted Access 7,868, Urban Restricted Access 2,518,97, ,8.64 Urban Unrestricted Access 5,829,939, , Total 8,419,778,958 2, ,95.6 County Road Type VMT Speed (mph) Armstrong Off-Network Rural Restricted Access N/A Rural Unrestricted Access 348,234, Urban Restricted Access 76,1, Urban Unrestricted Access 159,962, Total 584,28, County Road Type VMT Speed (mph) Beaver Off-Network Rural Restricted Access 65,512, Rural Unrestricted Access 293,437, Urban Restricted Access 248,6, Urban Unrestricted Access 755,539, Total 1,362,549, County Road Type VMT Speed (mph) Butler Off-Network Rural Restricted Access 321,289, Rural Unrestricted Access 729,759, Urban Restricted Access 262,484, Urban Unrestricted Access 713,935, Total 2,27,468, , County Road Type VMT Speed (mph) Fayette Off-Network Rural Restricted Access N/A Rural Unrestricted Access 494,88, Urban Restricted Access 153,115, Urban Unrestricted Access 323,683, Total 971,67, County Road Type VMT Speed (mph) Washington Off-Network Rural Restricted Access 656,398, Rural Unrestricted Access 522,14, Urban Restricted Access 51,292, Urban Unrestricted Access 617,23, Total 2,35,999, , County Road Type VMT Speed (mph) Westmoreland Off-Network Rural Restricted Access 256,74, Rural Unrestricted Access 688,657, Urban Restricted Access 882,655, Urban Unrestricted Access 1,478,36, Total 3,35,748,27 1, , Appendix B-3 B - 97

137 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Source Type Annual (Tons/Year) Scenario: RVP 8.7 County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Allegheny Motorcycle 54,52,339.6% % % Passenger Car 4,269,453,99 5.7% % % Passenger Truck 2,817,397, % 1, % 1, % Light Commercial Truck 79,746,57 8.4% % % Intercity Bus 979,15.%.36.% 6.1.2% Transit Bus 4,952,282.5% % % School Bus 15,79,965.2% % % Refuse Truck 8,68,539.1% 1.3.% % Single Unit Short-haul Truck 179,55,7 2.1% % % Single Unit Long-haul Truck 9,841,525.1% % % Motor Home 6,841,554.1% 5.7.2% % Combination Short-haul Truck 69,34,778.8% % % Combination Long-haul Truck 236,747, % % % Total 8,419,778,958 1.% 2, % 3, % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Armstrong Motorcycle 3,78,355.6% % % Passenger Car 29,493, % % % Passenger Truck 191,695, % % % Light Commercial Truck 48,293, % % % Intercity Bus 61,58.%.2.%.36.1% Transit Bus 3,441,987.6% 1.6.5% % School Bus 2,637,318.5% % % Refuse Truck 74,83.1%.1.% % Single Unit Short-haul Truck 15,422, % % % Single Unit Long-haul Truck 841,313.1%.18.1% 1.4.3% Motor Home 587,567.1%.46.2% % Combination Short-haul Truck 5,949,96 1.%.75.3% % Combination Long-haul Truck 2,334, % % % Total 584,28,243 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Beaver Motorcycle 8,741,814.6% % % Passenger Car 684,793, % % % Passenger Truck 451,893, % % % Light Commercial Truck 113,836, % % % Intercity Bus 157,216.%.6.%.97.1% Transit Bus 3,252,523.2% 1.2.2% % School Bus 1,67,243.1% 1.2.2% % Refuse Truck 1,66,281.1%.24.1% % Single Unit Short-haul Truck 34,512, % % % Single Unit Long-haul Truck 1,886,788.1%.42.1% % Motor Home 1,315,427.1% 1.7.2% % Combination Short-haul Truck 13,323,532 1.% % % Combination Long-haul Truck 45,55, % % % Total 1,362,549,823 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Butler Motorcycle 12,762,195.6% % % Passenger Car 999,732, % % % Passenger Truck 659,72, % % % Light Commercial Truck 166,188, % % % Intercity Bus 26,261.%.9.% % Transit Bus 4,43,694.2% % % School Bus 2,349,561.1% % % Refuse Truck 3,96,146.2%.41.1% % Single Unit Short-haul Truck 64,92, % % % Single Unit Long-haul Truck 3,56,94.2%.72.1% 4.3.3% Motor Home 2,442,893.1% % % Combination Short-haul Truck 24,753, % % % Combination Long-haul Truck 84,519, % % % Total 2,27,468,329 1.% % 1, % Appendix B-3 B - 98

138 Technical Appendix B - Onroad Emissions Technical Support Document County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Fayette Motorcycle 6,232,527.6% % % Passenger Car 488,227, % % % Passenger Truck 322,182, % % % Light Commercial Truck 81,157, % % % Intercity Bus 8,133.%.3.%.47.1% Transit Bus 2,54,152.3%.81.2% % School Bus 944,43.1%.66.1% 2.8.5% Refuse Truck 1,189,222.1%.17.% % Single Unit Short-haul Truck 24,693, % % % Single Unit Long-haul Truck 1,353,68.1%.29.1% % Motor Home 941,628.1%.74.2% % Combination Short-haul Truck 9,527,3 1.% % % Combination Long-haul Truck 32,573, % % % Total 971,67,628 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Washington Motorcycle 14,27,693.6% % % Passenger Car 1,112,968, % % % Passenger Truck 734,438,8 31.8% % % Light Commercial Truck 185,14,54 8.% % % Intercity Bus 1,12,288.%.31.% % Transit Bus 1,12,232.%.3.% % School Bus 6,74,171.3% % % Refuse Truck 4,261,653.2%.55.1% % Single Unit Short-haul Truck 88,1, % % % Single Unit Long-haul Truck 4,818,12.2%.98.1% % Motor Home 3,354,151.1% % % Combination Short-haul Truck 34,9, % % % Combination Long-haul Truck 116,62,47 5.% % % Total 2,35,999,29 1.% % 1, % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Westmoreland Motorcycle 2,4,23.6% % % Passenger Car 1,598,61, % % % Passenger Truck 1,54,549, % % % Light Commercial Truck 265,652,42 8.% % % Intercity Bus 576,453.%.19.% % Transit Bus 4,77,314.1% % % School Bus 1,829,592.1% 1.8.1% % Refuse Truck 6,11,929.2%.81.1% % Single Unit Short-haul Truck 126,453,86 3.8% % % Single Unit Long-haul Truck 6,931,71.2% % % Motor Home 4,818,742.1% % % Combination Short-haul Truck 48,838, % % % Combination Long-haul Truck 166,763,759 5.% % % Total 3,35,748,27 1.% 1, % 2, % Appendix B-3 B - 99

139 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Process Annual (Tons/Year) Scenario: RVP 8.7 County Process Emissions Pct. Emissions Pct. Allegheny Running Exhaust % 2, % Start Exhaust 1, % 1, % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.88.% Crankcase Start Exhaust %.5.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total 2, % 3, % County Process Emissions Pct. Emissions Pct. Armstrong Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.41.2%.7.% Crankcase Start Exhaust %.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Beaver Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.81.2%.15.% Crankcase Start Exhaust %.1.% Crankcase Extended Idle Exhaust.11.%.1.% Extended Idle Exhaust % % Auxiliary Power Exhaust.56.1% % Total % % County Process Emissions Pct. Emissions Pct. Butler Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.27.% Crankcase Start Exhaust 5.8.7%.1.% Crankcase Extended Idle Exhaust.55.1%.6.% Extended Idle Exhaust % % Auxiliary Power Exhaust % % Total % 1, % Appendix B-3 B - 1

140 Technical Appendix B - Onroad Emissions Technical Support Document County Process Emissions Pct. Emissions Pct. Fayette Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.61.1%.11.% Crankcase Start Exhaust %.1.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Washington Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.36.% Crankcase Start Exhaust %.1.% Crankcase Extended Idle Exhaust 1.4.1%.11.% Extended Idle Exhaust % % Auxiliary Power Exhaust % % Total % 1, % County Process Emissions Pct. Emissions Pct. Westmoreland Running Exhaust % 1, % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.5.% Crankcase Start Exhaust %.2.% Crankcase Extended Idle Exhaust.68.1%.7.% Extended Idle Exhaust % % Auxiliary Power Exhaust % % Total 1, % 2, % Appendix B-3 B - 11

141 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary Annual (Tons/Year) Scenario: RVP 1 County VMT Speed (mph) NOx Allegheny 8,419,778, , , Armstrong 584,28, Beaver 1,362,549, Butler 2,27,468, , Fayette 971,67, Washington 2,35,999, , Westmoreland 3,35,748, ,56.2 2, SPC MPO 18,977,36,478-6,64. 1, Appendix B-3 B - 12

142 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Road Type Annual (Tons/Year) Scenario: RVP 1 County Road Type VMT Speed (mph) Allegheny Off-Network - - 2, , Rural Restricted Access N/A Rural Unrestricted Access 7,868, Urban Restricted Access 2,518,97, ,81.53 Urban Unrestricted Access 5,829,939, , Total 8,419,778,958 2, , County Road Type VMT Speed (mph) Armstrong Off-Network Rural Restricted Access N/A Rural Unrestricted Access 348,234, Urban Restricted Access 76,1, Urban Unrestricted Access 159,962, Total 584,28, County Road Type VMT Speed (mph) Beaver Off-Network Rural Restricted Access 65,512, Rural Unrestricted Access 293,437, Urban Restricted Access 248,6, Urban Unrestricted Access 755,539, Total 1,362,549, County Road Type VMT Speed (mph) Butler Off-Network Rural Restricted Access 321,289, Rural Unrestricted Access 729,759, Urban Restricted Access 262,484, Urban Unrestricted Access 713,935, Total 2,27,468, , County Road Type VMT Speed (mph) Fayette Off-Network Rural Restricted Access N/A Rural Unrestricted Access 494,88, Urban Restricted Access 153,115, Urban Unrestricted Access 323,683, Total 971,67, County Road Type VMT Speed (mph) Washington Off-Network Rural Restricted Access 656,398, Rural Unrestricted Access 522,14, Urban Restricted Access 51,292, Urban Unrestricted Access 617,23, Total 2,35,999, , County Road Type VMT Speed (mph) Westmoreland Off-Network Rural Restricted Access 256,74, Rural Unrestricted Access 688,657, Urban Restricted Access 882,655, Urban Unrestricted Access 1,478,36, Total 3,35,748,27 1,56.2 2, Appendix B-3 B - 13

143 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Source Type Annual (Tons/Year) Scenario: RVP 1 County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Allegheny Motorcycle 54,52,339.6% % % Passenger Car 4,269,453,99 5.7% % % Passenger Truck 2,817,397, % 1, % 1, % Light Commercial Truck 79,746,57 8.4% % % Intercity Bus 979,15.%.36.% 6.1.2% Transit Bus 4,952,282.5% % % School Bus 15,79,965.2% % % Refuse Truck 8,68,539.1% 1.3.% % Single Unit Short-haul Truck 179,55,7 2.1% % % Single Unit Long-haul Truck 9,841,525.1% % % Motor Home 6,841,554.1% % % Combination Short-haul Truck 69,34,778.8% % % Combination Long-haul Truck 236,747, % % % Total 8,419,778,958 1.% 2, % 3, % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Armstrong Motorcycle 3,78,355.6% % % Passenger Car 29,493, % % % Passenger Truck 191,695, % % % Light Commercial Truck 48,293, % % % Intercity Bus 61,58.%.2.%.36.1% Transit Bus 3,441,987.6% 1.6.5% % School Bus 2,637,318.5% % % Refuse Truck 74,83.1%.1.% % Single Unit Short-haul Truck 15,422, % % % Single Unit Long-haul Truck 841,313.1%.18.1% 1.4.3% Motor Home 587,567.1%.46.2% % Combination Short-haul Truck 5,949,96 1.%.75.3% % Combination Long-haul Truck 2,334, % % % Total 584,28,243 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Beaver Motorcycle 8,741,814.6% % % Passenger Car 684,793, % % % Passenger Truck 451,893, % % % Light Commercial Truck 113,836, % % % Intercity Bus 157,216.%.6.%.97.1% Transit Bus 3,252,523.2% 1.1.2% % School Bus 1,67,243.1% 1.2.2% % Refuse Truck 1,66,281.1%.24.1% % Single Unit Short-haul Truck 34,512, % % % Single Unit Long-haul Truck 1,886,788.1%.42.1% % Motor Home 1,315,427.1% 1.7.2% % Combination Short-haul Truck 13,323,532 1.% % % Combination Long-haul Truck 45,55, % % % Total 1,362,549,823 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Butler Motorcycle 12,762,195.6% % % Passenger Car 999,732, % % % Passenger Truck 659,72, % % % Light Commercial Truck 166,188, % % % Intercity Bus 26,261.%.9.% % Transit Bus 4,43,694.2% % % School Bus 2,349,561.1% % % Refuse Truck 3,96,146.2%.41.1% % Single Unit Short-haul Truck 64,92, % % % Single Unit Long-haul Truck 3,56,94.2%.72.1% % Motor Home 2,442,893.1% % % Combination Short-haul Truck 24,753, % % % Combination Long-haul Truck 84,519, % % % Total 2,27,468,329 1.% % 1, % Appendix B-3 B - 14

144 Technical Appendix B - Onroad Emissions Technical Support Document County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Fayette Motorcycle 6,232,527.6% % % Passenger Car 488,227, % % % Passenger Truck 322,182, % % % Light Commercial Truck 81,157, % % % Intercity Bus 8,133.%.3.%.47.1% Transit Bus 2,54,152.3%.81.2% % School Bus 944,43.1%.66.1% 2.8.5% Refuse Truck 1,189,222.1%.17.% % Single Unit Short-haul Truck 24,693, % % % Single Unit Long-haul Truck 1,353,68.1%.29.1% % Motor Home 941,628.1%.74.2% % Combination Short-haul Truck 9,527,3 1.% % % Combination Long-haul Truck 32,573, % % % Total 971,67,628 1.% % % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Washington Motorcycle 14,27,693.6% % % Passenger Car 1,112,968, % % % Passenger Truck 734,438,8 31.8% % % Light Commercial Truck 185,14,54 8.% % % Intercity Bus 1,12,288.%.31.% % Transit Bus 1,12,232.%.3.% % School Bus 6,74,171.3% % % Refuse Truck 4,261,653.2%.55.1% % Single Unit Short-haul Truck 88,1, % % % Single Unit Long-haul Truck 4,818,12.2%.98.1% % Motor Home 3,354,151.1% % % Combination Short-haul Truck 34,9, % % % Combination Long-haul Truck 116,62,47 5.% % % Total 2,35,999,29 1.% % 1, % County Sourcetype VMT Miles Pct. Emissions Pct. Emissions Pct. Westmoreland Motorcycle 2,4,23.6% % % Passenger Car 1,598,61, % % % Passenger Truck 1,54,549, % % % Light Commercial Truck 265,652,42 8.% % % Intercity Bus 576,453.%.19.% % Transit Bus 4,77,314.1% % % School Bus 1,829,592.1% 1.8.1% % Refuse Truck 6,11,929.2%.81.1% % Single Unit Short-haul Truck 126,453,86 3.8% % % Single Unit Long-haul Truck 6,931,71.2% % % Motor Home 4,818,742.1% % % Combination Short-haul Truck 48,838, % % % Combination Long-haul Truck 166,763,759 5.% % % Total 3,35,748,27 1.% 1, % 2, % Appendix B-3 B - 15

145 Technical Appendix B - Onroad Emissions Technical Support Document Appendix B Pittsburgh-Beaver Valley Area Emission Summary by Process Annual (Tons/Year) Scenario: RVP 1 County Process Emissions Pct. Emissions Pct. Allegheny Running Exhaust % 2, % Start Exhaust 1, % 1, % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust 5.8.2%.88.% Crankcase Start Exhaust %.5.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total 2, % 3, % County Process Emissions Pct. Emissions Pct. Armstrong Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.41.2%.7.% Crankcase Start Exhaust %.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Beaver Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.81.2%.15.% Crankcase Start Exhaust %.1.% Crankcase Extended Idle Exhaust.11.%.1.% Extended Idle Exhaust % % Auxiliary Power Exhaust.56.1% % Total % % County Process Emissions Pct. Emissions Pct. Butler Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.27.% Crankcase Start Exhaust 5.2.7%.1.% Crankcase Extended Idle Exhaust.55.1%.6.% Extended Idle Exhaust % % Auxiliary Power Exhaust % % Total % 1, % Appendix B-3 B - 16

146 Technical Appendix B - Onroad Emissions Technical Support Document County Process Emissions Pct. Emissions Pct. Fayette Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust.61.1%.11.% Crankcase Start Exhaust 3.5.8%.1.% Crankcase Extended Idle Exhaust.%.% Extended Idle Exhaust.%.% Auxiliary Power Exhaust.%.% Total % % County Process Emissions Pct. Emissions Pct. Washington Running Exhaust % % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.36.% Crankcase Start Exhaust %.1.% Crankcase Extended Idle Exhaust 1.4.1%.11.% Extended Idle Exhaust % % Auxiliary Power Exhaust % % Total % 1, % County Process Emissions Pct. Emissions Pct. Westmoreland Running Exhaust % 1, % Start Exhaust % % Brakewear.%.% Tirewear.%.% Evap Permeation %.% Evap Fuel Vapor Venting %.% Evap Fuel Leaks %.% Crankcase Running Exhaust %.5.% Crankcase Start Exhaust %.2.% Crankcase Extended Idle Exhaust.68.1%.7.% Extended Idle Exhaust % % Auxiliary Power Exhaust % % Total 1, % 2, % Appendix B-3 B - 17

147 Technical Appendix B - Onroad Emissions Technical Support Document APPENDIX B-4 Pittsburgh-Beaver Valley Area MOVES Sample Input Files B - 18

148 Technical Appendix B - Onroad Emissions Technical Support Document July Weekday MOVES Run Specification File Settings Existing Scenario (RVP 7.8) Sample xml file format <moves> <importer mode="county" > <filters> <geographicselections> <geographicselection type="county" key="423" description="pennsylvania - Allegheny County"/> </geographicselections> <timespan> <year key="218"/> <month id="7"/> <day id="2"/> <day id="5"/> <beginhour id="1"/> <endhour id="24"/> <aggregateby key="hour"/> </timespan> <onroadvehicleselections> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="42" sourcetypename="transit Bus"/> B-4 B - 19

149 Technical Appendix B - Onroad Emissions Technical Support Document <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="42" sourcetypename="transit Bus"/> </onroadvehicleselections> <offroadvehicleselections> </offroadvehicleselections> <offroadvehiclesccs> </offroadvehiclesccs> <roadtypes> <roadtype roadtypeid="1" roadtypename="off-network"/> <roadtype roadtypeid="2" roadtypename="rural Restricted Access"/> <roadtype roadtypeid="3" roadtypename="rural Unrestricted Access"/> <roadtype roadtypeid="4" roadtypename="urban Restricted Access"/> <roadtype roadtypeid="5" roadtypename="urban Unrestricted Access"/> </roadtypes> </filters> <databaseselection servername="localhost" databasename="423_218_7_5_m214a_pgh_existing_mi"/> <agedistribution> <description><![cdata[]]></description> <parts> <sourcetypeagedistribution> <filename>c:\pamoves14a\movesinputs\agedistribution\moves214\14reg_repcty\218\4219_218_sourcetypeagedistribution.csv</filename> </sourcetypeagedistribution> </parts> </agedistribution> <avgspeeddistribution> <description><![cdata[]]></description> <parts> <avgspeeddistribution> <filename>c:\pamoves14a\out\218_m214a_pgh_existing\\423_218_7_5_m214a_pgh_existing\cdm\avgspeeddistribution.csv</filename> </avgspeeddistribution> </parts> </avgspeeddistribution> <imcoverage> <description><![cdata[]]></description> <parts> <imcoverage> <filename>c:\pamoves14a\movesinputs\im\moves214a\42_218_imcoverage.csv</filename> </imcoverage> </parts> </imcoverage> <fuel> <description><![cdata[]]></description> <parts> <FuelSupply> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\!pgh_rvp_inv\pa_pgh_fuelsupply_14a_218_223_7.csv</filename> </FuelSupply> <FuelFormulation> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\!pgh_rvp_inv\pa_pgh_fuelformulation_14a_218_223_7_rvp78.csv</filename> </FuelFormulation> <FuelUsageFraction> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\movesdefaults\42_fuelusagefraction_14a.csv</filename> </FuelUsageFraction> <AVFT> <filename></filename> Appendix B-4 B - 11

150 Technical Appendix B - Onroad Emissions Technical Support Document </AVFT> </parts> </fuel> <zonemonthhour> <description><![cdata[]]></description> <parts> <zonemonthhour> <filename>c:\pamoves14a\movesinputs\meteorology\214\423_214_met.csv</filename> </zonemonthhour> </parts> </zonemonthhour> <roadtypedistribution> <description><![cdata[]]></description> <parts> <roadtypedistribution> <filename>c:\pamoves14a\out\218_m214a_pgh_existing\\423_218_7_5_m214a_pgh_existing\cdm\roadtypedistribution.csv</filename> </roadtypedistribution> </parts> </roadtypedistribution> <sourcetypepopulation> <description><![cdata[]]></description> <parts> <sourcetypeyear> <filename>c:\pamoves14a\out\218_m214a_pgh_existing\\423_218_7_5_m214a_pgh_existing\cdm\sourcetypepopulation.csv</filename> </sourcetypeyear> </parts> </sourcetypepopulation> <rampfraction> <description><![cdata[]]></description> <parts> <roadtype> <filename>c:\pamoves14a\movesinputs\rampfraction\rampfraction_defaults.csv</filename> </roadtype> </parts> </rampfraction> <vehicletypevmt> <description><![cdata[]]></description> <parts> <hpmsvtypeyear> <filename>c:\pamoves14a\out\218_m214a_pgh_existing\\423_218_7_5_m214a_pgh_existing\cdm\hpmsvtypeyear.csv</filename> </hpmsvtypeyear> <monthvmtfraction> <filename>c:\pamoves14a\out\218_m214a_pgh_existing\\423_218_7_5_m214a_pgh_existing\cdm\notused\monthvmtfraction_m21ab_import.csv</filename> </monthvmtfraction> <dayvmtfraction> <filename>c:\pamoves14a\movesinputs\monthdayhourfractions\highgrw\218_dayfraction\423_218_dayvmtfraction.csv</filename> </dayvmtfraction> <hourvmtfraction> <filename>c:\pamoves14a\out\218_m214a_pgh_existing\\423_218_7_5_m214a_pgh_existing\cdm\hourvmtfraction.csv</filename> </hourvmtfraction> </parts> </vehicletypevmt> <starts> <description><![cdata[]]></description> <parts> <startsperday> <filename></filename> </startsperday> <startshourfraction> <filename></filename> </startshourfraction> <startssourcetypefraction> B-4 B - 111

151 Technical Appendix B - Onroad Emissions Technical Support Document <filename></filename> </startssourcetypefraction> <startsmonthadjust> <filename></filename> </startsmonthadjust> <importstartsopmodedistribution> <filename></filename> </importstartsopmodedistribution> <Starts> <filename></filename> </Starts> </parts> </starts> <hotelling> <description><![cdata[]]></description> <parts> <hotellingactivitydistribution> <filename></filename> </hotellingactivitydistribution> <hotellinghours> <filename></filename> </hotellinghours> </parts> </hotelling> <onroadretrofit> <description><![cdata[]]></description> <parts> <onroadretrofit> <filename></filename> </onroadretrofit> </parts> </onroadretrofit> </moves> <generic> <description><![cdata[]]></description> <parts> <anytable> <tablename>regioncounty</tablename> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\movesdefaults\42_regioncounty_moves214adefaults.csv</filename> </anytable> </parts> </generic> </importer> Sample mrs file format <runspec version="moves214a "> <description><![cdata[moves214a RunSpec Created by CENTRAL4 Scenario: ALLE 218 JULWKD M214a_PGH_Existing Emission Inventory with user's data]]></description> <models> <model value="onroad"/> </models> <modelscale value="inv"/> <modeldomain value="single"/> <geographicselections> <geographicselection type="county" key="423" description="pennsylvania - Allegheny County"/> </geographicselections> <timespan> <year key="218"/> <month id="7"/> <day id="5"/> <beginhour id="1"/> B-4 B - 112

152 Technical Appendix B - Onroad Emissions Technical Support Document <endhour id="24"/> <aggregateby key="hour"/> </timespan> <onroadvehicleselections> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> </onroadvehicleselections> <offroadvehicleselections> </offroadvehicleselections> <offroadvehiclesccs> </offroadvehiclesccs> <roadtypes separateramps="false"> <roadtype roadtypeid="1" roadtypename="off-network" modelcombination="m1"/> <roadtype roadtypeid="2" roadtypename="rural Restricted Access" modelcombination="m1"/> <roadtype roadtypeid="3" roadtypename="rural Unrestricted Access" modelcombination="m1"/> <roadtype roadtypeid="4" roadtypename="urban Restricted Access" modelcombination="m1"/> <roadtype roadtypeid="5" roadtypename="urban Unrestricted Access" modelcombination="m1"/> </roadtypes> B-4 B - 113

153 Technical Appendix B - Onroad Emissions Technical Support Document <pollutantprocessassociations> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen (NOx)" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="12" processname="evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="13" processname="evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="12" processname="evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="13" processname="evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="12" processname="evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="13" processname="evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="11" processname="evap Permeation"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="11" processname="evap Permeation"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="11" processname="evap Permeation"/> </pollutantprocessassociations> <databaseselections> <databaseselection servername="localhost" databasename="moves214_early_nlev" description=""/> <databaseselection servername="localhost" databasename="moves214_calevii8" description=""/> </databaseselections> <inputdatabase servername="" databasename="" description=""/> <uncertaintyparameters uncertaintymodeenabled="false" numberofrunspersimulation="" numberofsimulations=""/> <geographicoutputdetail description="county"/> <outputemissionsbreakdownselection> <modelyear selected="false"/> <fueltype selected="false"/> <fuelsubtype selected="false"/> <emissionprocess selected="true"/> <onroadoffroad selected="true"/> <roadtype selected="true"/> <sourceusetype selected="true"/> <movesvehicletype selected="false"/> <onroadscc selected="false"/> <offroadscc selected="false"/> <estimateuncertainty selected="false" numberofiterations="2" keepsampleddata="false" keepiterations="false"/> <sector selected="false"/> <engtechid selected="false"/> <hpclass selected="false"/> </outputemissionsbreakdownselection> <outputdatabase servername="localhost" databasename="423_218_7_5_m214a_pgh_existing_mo" description=""/>> <outputtimestep value="hour"/> <outputvmtdata value="true"/> <outputsho value="true"/> <outputsh value="true"/> <outputshp value="true"/> B-4 B - 114

154 Technical Appendix B - Onroad Emissions Technical Support Document <outputshidling value="true"/> <outputstarts value="true"/> <outputpopulation value="true"/> <scaleinputdatabase servername="localhost" databasename="423_218_7_5_m214a_pgh_existing_mi" description=""/> <pmsize value=""/> <outputfactors> <timefactors selected="true" units="hours"/> <distancefactors selected="false" units="miles"/> <massfactors selected="false" units="grams" energyunits="million BTU"/> </outputfactors> <savedata> </savedata> <donotexecute> </donotexecute> <generatordatabase shouldsave="false" servername="" databasename="" description=""/> <donotperformfinalaggregation selected="false"/> <lookuptableflags scenarioid="" truncateoutput="false" truncateactivity="false"/> <internalcontrolstrategies> <internalcontrolstrategy classname="gov.epa.otaq.moves.master.implementation.ghg.internalcontrolstrategies.rateofprogress.rateofprogressstrategy"><![cdata[ useparameters No ]]></internalcontrolstrategy> </internalcontrolstrategies> </runspec> B-4 B - 115

155 Technical Appendix B - Onroad Emissions Technical Support Document July Weekday MOVES Run Specification File Settings RVP 8.7 Scenario Sample xml file format <moves> <importer mode="county" > <filters> <geographicselections> <geographicselection type="county" key="423" description="pennsylvania - Allegheny County"/> </geographicselections> <timespan> <year key="218"/> <month id="7"/> <day id="2"/> <day id="5"/> <beginhour id="1"/> <endhour id="24"/> <aggregateby key="hour"/> </timespan> <onroadvehicleselections> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> B-4 B - 116

156 Technical Appendix B - Onroad Emissions Technical Support Document <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="42" sourcetypename="transit Bus"/> </onroadvehicleselections> <offroadvehicleselections> </offroadvehicleselections> <offroadvehiclesccs> </offroadvehiclesccs> <roadtypes> <roadtype roadtypeid="1" roadtypename="off-network"/> <roadtype roadtypeid="2" roadtypename="rural Restricted Access"/> <roadtype roadtypeid="3" roadtypename="rural Unrestricted Access"/> <roadtype roadtypeid="4" roadtypename="urban Restricted Access"/> <roadtype roadtypeid="5" roadtypename="urban Unrestricted Access"/> </roadtypes> </filters> <databaseselection servername="localhost" databasename="423_218_7_5_m214a_pgh_rvp87_mi"/> <agedistribution> <description><![cdata[]]></description> <parts> <sourcetypeagedistribution> <filename>c:\pamoves14a\movesinputs\agedistribution\moves214\14reg_repcty\218\4219_218_sourcetypeagedistribution.csv</filename> </sourcetypeagedistribution> </parts> </agedistribution> <avgspeeddistribution> <description><![cdata[]]></description> <parts> <avgspeeddistribution> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp87\\423_218_7_5_m214a_pgh_rvp87\cdm\avgspeeddistribution.csv</filename> </avgspeeddistribution> </parts> </avgspeeddistribution> <imcoverage> <description><![cdata[]]></description> <parts> <imcoverage> <filename>c:\pamoves14a\movesinputs\im\moves214a\42_218_imcoverage.csv</filename> </imcoverage> </parts> </imcoverage> <fuel> <description><![cdata[]]></description> <parts> <FuelSupply> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\!pgh_rvp_inv\pa_pgh_fuelsupply_14a_218_223_7.csv</filename> </FuelSupply> <FuelFormulation> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\!pgh_rvp_inv\pgh_fuelformulation_14a_218_223_7_rvp87.csv</filename> </FuelFormulation> <FuelUsageFraction> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\movesdefaults\42_fuelusagefraction_14a.csv</filename> </FuelUsageFraction> B-4 B - 117

157 Technical Appendix B - Onroad Emissions Technical Support Document <AVFT> <filename></filename> </AVFT> </parts> </fuel> <zonemonthhour> <description><![cdata[]]></description> <parts> <zonemonthhour> <filename>c:\pamoves14a\movesinputs\meteorology\214\423_214_met.csv</filename> </zonemonthhour> </parts> </zonemonthhour> <roadtypedistribution> <description><![cdata[]]></description> <parts> <roadtypedistribution> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp87\\423_218_7_5_m214a_pgh_rvp87\cdm\roadtypedistribution.csv</filename> </roadtypedistribution> </parts> </roadtypedistribution> <sourcetypepopulation> <description><![cdata[]]></description> <parts> <sourcetypeyear> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp87\\423_218_7_5_m214a_pgh_rvp87\cdm\sourcetypepopulation.csv</filename> </sourcetypeyear> </parts> </sourcetypepopulation> <rampfraction> <description><![cdata[]]></description> <parts> <roadtype> <filename>c:\pamoves14a\movesinputs\rampfraction\rampfraction_defaults.csv</filename> </roadtype> </parts> </rampfraction> <vehicletypevmt> <description><![cdata[]]></description> <parts> <hpmsvtypeyear> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp87\\423_218_7_5_m214a_pgh_rvp87\cdm\hpmsvtypeyear.csv</filename> </hpmsvtypeyear> <monthvmtfraction> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp87\\423_218_7_5_m214a_pgh_rvp87\cdm\notused\monthvmtfraction_m21ab_import.csv</filename> </monthvmtfraction> <dayvmtfraction> <filename>c:\pamoves14a\movesinputs\monthdayhourfractions\highgrw\218_dayfraction\423_218_dayvmtfraction.csv</filename> </dayvmtfraction> <hourvmtfraction> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp87\\423_218_7_5_m214a_pgh_rvp87\cdm\hourvmtfraction.csv</filename> </hourvmtfraction> </parts> </vehicletypevmt> <starts> <description><![cdata[]]></description> <parts> <startsperday> <filename></filename> </startsperday> <startshourfraction> <filename></filename> B-4 B - 118

158 Technical Appendix B - Onroad Emissions Technical Support Document </startshourfraction> <startssourcetypefraction> <filename></filename> </startssourcetypefraction> <startsmonthadjust> <filename></filename> </startsmonthadjust> <importstartsopmodedistribution> <filename></filename> </importstartsopmodedistribution> <Starts> <filename></filename> </Starts> </parts> </starts> <hotelling> <description><![cdata[]]></description> <parts> <hotellingactivitydistribution> <filename></filename> </hotellingactivitydistribution> <hotellinghours> <filename></filename> </hotellinghours> </parts> </hotelling> <onroadretrofit> <description><![cdata[]]></description> <parts> <onroadretrofit> <filename></filename> </onroadretrofit> </parts> </onroadretrofit> </moves> <generic> <description><![cdata[]]></description> <parts> <anytable> <tablename>regioncounty</tablename> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\movesdefaults\42_regioncounty_moves214adefaults.csv</filename> </anytable> </parts> </generic> </importer> Sample mrs file format <runspec version="moves214a "> <description><![cdata[moves214a RunSpec Created by CENTRAL4 Scenario: ALLE 218 JULWKD M214a_PGH_RVP87 Emission Inventory with user's data]]></description> <models> <model value="onroad"/> </models> <modelscale value="inv"/> <modeldomain value="single"/> <geographicselections> <geographicselection type="county" key="423" description="pennsylvania - Allegheny County"/> </geographicselections> <timespan> B-4 B - 119

159 Technical Appendix B - Onroad Emissions Technical Support Document <year key="218"/> <month id="7"/> <day id="5"/> <beginhour id="1"/> <endhour id="24"/> <aggregateby key="hour"/> </timespan> <onroadvehicleselections> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> </onroadvehicleselections> <offroadvehicleselections> </offroadvehicleselections> <offroadvehiclesccs> </offroadvehiclesccs> <roadtypes separateramps="false"> <roadtype roadtypeid="1" roadtypename="off-network" modelcombination="m1"/> B-4 B - 12

160 Technical Appendix B - Onroad Emissions Technical Support Document <roadtype roadtypeid="2" roadtypename="rural Restricted Access" modelcombination="m1"/> <roadtype roadtypeid="3" roadtypename="rural Unrestricted Access" modelcombination="m1"/> <roadtype roadtypeid="4" roadtypename="urban Restricted Access" modelcombination="m1"/> <roadtype roadtypeid="5" roadtypename="urban Unrestricted Access" modelcombination="m1"/> </roadtypes> <pollutantprocessassociations> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen (NOx)" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="12" processname="evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="13" processname="evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="12" processname="evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="13" processname="evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="12" processname="evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="13" processname="evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="11" processname="evap Permeation"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="11" processname="evap Permeation"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="11" processname="evap Permeation"/> </pollutantprocessassociations> <databaseselections> <databaseselection servername="localhost" databasename="moves214_early_nlev" description=""/> <databaseselection servername="localhost" databasename="moves214_calevii8" description=""/> </databaseselections> <inputdatabase servername="" databasename="" description=""/> <uncertaintyparameters uncertaintymodeenabled="false" numberofrunspersimulation="" numberofsimulations=""/> <geographicoutputdetail description="county"/> <outputemissionsbreakdownselection> <modelyear selected="false"/> <fueltype selected="false"/> <fuelsubtype selected="false"/> <emissionprocess selected="true"/> <onroadoffroad selected="true"/> <roadtype selected="true"/> <sourceusetype selected="true"/> <movesvehicletype selected="false"/> <onroadscc selected="false"/> <offroadscc selected="false"/> <estimateuncertainty selected="false" numberofiterations="2" keepsampleddata="false" keepiterations="false"/> <sector selected="false"/> <engtechid selected="false"/> <hpclass selected="false"/> B-4 B - 121

161 Technical Appendix B - Onroad Emissions Technical Support Document </outputemissionsbreakdownselection> <outputdatabase servername="localhost" databasename="423_218_7_5_m214a_pgh_rvp87_mo" description=""/>> <outputtimestep value="hour"/> <outputvmtdata value="true"/> <outputsho value="true"/> <outputsh value="true"/> <outputshp value="true"/> <outputshidling value="true"/> <outputstarts value="true"/> <outputpopulation value="true"/> <scaleinputdatabase servername="localhost" databasename="423_218_7_5_m214a_pgh_rvp87_mi" description=""/> <pmsize value=""/> <outputfactors> <timefactors selected="true" units="hours"/> <distancefactors selected="false" units="miles"/> <massfactors selected="false" units="grams" energyunits="million BTU"/> </outputfactors> <savedata> </savedata> <donotexecute> </donotexecute> <generatordatabase shouldsave="false" servername="" databasename="" description=""/> <donotperformfinalaggregation selected="false"/> <lookuptableflags scenarioid="" truncateoutput="false" truncateactivity="false"/> <internalcontrolstrategies> <internalcontrolstrategy classname="gov.epa.otaq.moves.master.implementation.ghg.internalcontrolstrategies.rateofprogress.rateofprogressstrategy"><![cdata[ useparameters No ]]></internalcontrolstrategy> </internalcontrolstrategies> </runspec> B-4 B - 122

162 Technical Appendix B - Onroad Emissions Technical Support Document July Weekday MOVES Run Specification File Settings RVP 1 Scenario Sample xml file format <moves> <importer mode="county" > <filters> <geographicselections> <geographicselection type="county" key="423" description="pennsylvania - Allegheny County"/> </geographicselections> <timespan> <year key="218"/> <month id="7"/> <day id="2"/> <day id="5"/> <beginhour id="1"/> <endhour id="24"/> <aggregateby key="hour"/> </timespan> <onroadvehicleselections> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> B-4 B - 123

163 Technical Appendix B - Onroad Emissions Technical Support Document <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="42" sourcetypename="transit Bus"/> </onroadvehicleselections> <offroadvehicleselections> </offroadvehicleselections> <offroadvehiclesccs> </offroadvehiclesccs> <roadtypes> <roadtype roadtypeid="1" roadtypename="off-network"/> <roadtype roadtypeid="2" roadtypename="rural Restricted Access"/> <roadtype roadtypeid="3" roadtypename="rural Unrestricted Access"/> <roadtype roadtypeid="4" roadtypename="urban Restricted Access"/> <roadtype roadtypeid="5" roadtypename="urban Unrestricted Access"/> </roadtypes> </filters> <databaseselection servername="localhost" databasename="423_218_7_5_m214a_pgh_rvp1_mi"/> <agedistribution> <description><![cdata[]]></description> <parts> <sourcetypeagedistribution> <filename>c:\pamoves14a\movesinputs\agedistribution\moves214\14reg_repcty\218\4219_218_sourcetypeagedistribution.csv</filename> </sourcetypeagedistribution> </parts> </agedistribution> <avgspeeddistribution> <description><![cdata[]]></description> <parts> <avgspeeddistribution> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp1\\423_218_7_5_m214a_pgh_rvp1\cdm\avgspeeddistribution.csv</filename> </avgspeeddistribution> </parts> </avgspeeddistribution> <imcoverage> <description><![cdata[]]></description> <parts> <imcoverage> <filename>c:\pamoves14a\movesinputs\im\moves214a\42_218_imcoverage.csv</filename> </imcoverage> </parts> </imcoverage> <fuel> <description><![cdata[]]></description> <parts> <FuelSupply> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\!pgh_rvp_inv\pa_pgh_fuelsupply_14a_218_223_7.csv</filename> </FuelSupply> <FuelFormulation> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\!pgh_rvp_inv\pgh_fuelformulation_14a_218_223_7_rvp1.csv</filename> </FuelFormulation> <FuelUsageFraction> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\movesdefaults\42_fuelusagefraction_14a.csv</filename> </FuelUsageFraction> B-4 B - 124

164 Technical Appendix B - Onroad Emissions Technical Support Document <AVFT> <filename></filename> </AVFT> </parts> </fuel> <zonemonthhour> <description><![cdata[]]></description> <parts> <zonemonthhour> <filename>c:\pamoves14a\movesinputs\meteorology\214\423_214_met.csv</filename> </zonemonthhour> </parts> </zonemonthhour> <roadtypedistribution> <description><![cdata[]]></description> <parts> <roadtypedistribution> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp1\\423_218_7_5_m214a_pgh_rvp1\cdm\roadtypedistribution.csv</filename> </roadtypedistribution> </parts> </roadtypedistribution> <sourcetypepopulation> <description><![cdata[]]></description> <parts> <sourcetypeyear> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp1\\423_218_7_5_m214a_pgh_rvp1\cdm\sourcetypepopulation.csv</filename> </sourcetypeyear> </parts> </sourcetypepopulation> <rampfraction> <description><![cdata[]]></description> <parts> <roadtype> <filename>c:\pamoves14a\movesinputs\rampfraction\rampfraction_defaults.csv</filename> </roadtype> </parts> </rampfraction> <vehicletypevmt> <description><![cdata[]]></description> <parts> <hpmsvtypeyear> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp1\\423_218_7_5_m214a_pgh_rvp1\cdm\hpmsvtypeyear.csv</filename> </hpmsvtypeyear> <monthvmtfraction> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp1\\423_218_7_5_m214a_pgh_rvp1\cdm\notused\monthvmtfraction_m21ab_import.csv</filename> </monthvmtfraction> <dayvmtfraction> <filename>c:\pamoves14a\movesinputs\monthdayhourfractions\highgrw\218_dayfraction\423_218_dayvmtfraction.csv</filename> </dayvmtfraction> <hourvmtfraction> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp1\\423_218_7_5_m214a_pgh_rvp1\cdm\hourvmtfraction.csv</filename> </hourvmtfraction> </parts> </vehicletypevmt> <starts> <description><![cdata[]]></description> <parts> <startsperday> <filename></filename> </startsperday> <startshourfraction> <filename></filename> B-4 B - 125

165 Technical Appendix B - Onroad Emissions Technical Support Document </startshourfraction> <startssourcetypefraction> <filename></filename> </startssourcetypefraction> <startsmonthadjust> <filename></filename> </startsmonthadjust> <importstartsopmodedistribution> <filename></filename> </importstartsopmodedistribution> <Starts> <filename></filename> </Starts> </parts> </starts> <hotelling> <description><![cdata[]]></description> <parts> <hotellingactivitydistribution> <filename></filename> </hotellingactivitydistribution> <hotellinghours> <filename></filename> </hotellinghours> </parts> </hotelling> <onroadretrofit> <description><![cdata[]]></description> <parts> <onroadretrofit> <filename></filename> </onroadretrofit> </parts> </onroadretrofit> </moves> <generic> <description><![cdata[]]></description> <parts> <anytable> <tablename>regioncounty</tablename> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\movesdefaults\42_regioncounty_moves214adefaults.csv</filename> </anytable> </parts> </generic> </importer> Sample mrs file format <runspec version="moves214a "> <description><![cdata[moves214a RunSpec Created by CENTRAL4 Scenario: ALLE 218 JULWKD M214a_PGH_RVP1 Emission Inventory with user's data]]></description> <models> <model value="onroad"/> </models> <modelscale value="inv"/> <modeldomain value="single"/> <geographicselections> <geographicselection type="county" key="423" description="pennsylvania - Allegheny County"/> </geographicselections> <timespan> B-4 B - 126

166 Technical Appendix B - Onroad Emissions Technical Support Document <year key="218"/> <month id="7"/> <day id="5"/> <beginhour id="1"/> <endhour id="24"/> <aggregateby key="hour"/> </timespan> <onroadvehicleselections> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> </onroadvehicleselections> <offroadvehicleselections> </offroadvehicleselections> <offroadvehiclesccs> </offroadvehiclesccs> <roadtypes separateramps="false"> <roadtype roadtypeid="1" roadtypename="off-network" modelcombination="m1"/> B-4 B - 127

167 Technical Appendix B - Onroad Emissions Technical Support Document <roadtype roadtypeid="2" roadtypename="rural Restricted Access" modelcombination="m1"/> <roadtype roadtypeid="3" roadtypename="rural Unrestricted Access" modelcombination="m1"/> <roadtype roadtypeid="4" roadtypename="urban Restricted Access" modelcombination="m1"/> <roadtype roadtypeid="5" roadtypename="urban Unrestricted Access" modelcombination="m1"/> </roadtypes> <pollutantprocessassociations> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen (NOx)" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="12" processname="evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="13" processname="evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="12" processname="evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="13" processname="evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="12" processname="evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="13" processname="evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="11" processname="evap Permeation"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="11" processname="evap Permeation"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="11" processname="evap Permeation"/> </pollutantprocessassociations> <databaseselections> <databaseselection servername="localhost" databasename="moves214_early_nlev" description=""/> <databaseselection servername="localhost" databasename="moves214_calevii8" description=""/> </databaseselections> <inputdatabase servername="" databasename="" description=""/> <uncertaintyparameters uncertaintymodeenabled="false" numberofrunspersimulation="" numberofsimulations=""/> <geographicoutputdetail description="county"/> <outputemissionsbreakdownselection> <modelyear selected="false"/> <fueltype selected="false"/> <fuelsubtype selected="false"/> <emissionprocess selected="true"/> <onroadoffroad selected="true"/> <roadtype selected="true"/> <sourceusetype selected="true"/> <movesvehicletype selected="false"/> <onroadscc selected="false"/> <offroadscc selected="false"/> <estimateuncertainty selected="false" numberofiterations="2" keepsampleddata="false" keepiterations="false"/> <sector selected="false"/> <engtechid selected="false"/> <hpclass selected="false"/> B-4 B - 128

168 Technical Appendix B - Onroad Emissions Technical Support Document </outputemissionsbreakdownselection> <outputdatabase servername="localhost" databasename="423_218_7_5_m214a_pgh_rvp1_mo" description=""/>> <outputtimestep value="hour"/> <outputvmtdata value="true"/> <outputsho value="true"/> <outputsh value="true"/> <outputshp value="true"/> <outputshidling value="true"/> <outputstarts value="true"/> <outputpopulation value="true"/> <scaleinputdatabase servername="localhost" databasename="423_218_7_5_m214a_pgh_rvp1_mi" description=""/> <pmsize value=""/> <outputfactors> <timefactors selected="true" units="hours"/> <distancefactors selected="false" units="miles"/> <massfactors selected="false" units="grams" energyunits="million BTU"/> </outputfactors> <savedata> </savedata> <donotexecute> </donotexecute> <generatordatabase shouldsave="false" servername="" databasename="" description=""/> <donotperformfinalaggregation selected="false"/> <lookuptableflags scenarioid="" truncateoutput="false" truncateactivity="false"/> <internalcontrolstrategies> <internalcontrolstrategy classname="gov.epa.otaq.moves.master.implementation.ghg.internalcontrolstrategies.rateofprogress.rateofprogressstrategy"><![cdata[ useparameters No ]]></internalcontrolstrategy> </internalcontrolstrategies> </runspec> B-4 B - 129

169 Technical Appendix B - Onroad Emissions Technical Support Document Annual MOVES Run Specification File Settings Existing Scenario (RVP 7.8) Sample xml file format <moves> <importer mode="county" > <filters> <geographicselections> <geographicselection type="county" key="423" description="pennsylvania - Allegheny County"/> </geographicselections> <timespan> <year key="218"/> <month id=""/> <day id="2"/> <day id="5"/> <beginhour id="1"/> <endhour id="24"/> <aggregateby key="hour"/> </timespan> <onroadvehicleselections> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="42" sourcetypename="transit Bus"/> B-4 B - 13

170 Technical Appendix B - Onroad Emissions Technical Support Document <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="42" sourcetypename="transit Bus"/> </onroadvehicleselections> <offroadvehicleselections> </offroadvehicleselections> <offroadvehiclesccs> </offroadvehiclesccs> <roadtypes> <roadtype roadtypeid="1" roadtypename="off-network"/> <roadtype roadtypeid="2" roadtypename="rural Restricted Access"/> <roadtype roadtypeid="3" roadtypename="rural Unrestricted Access"/> <roadtype roadtypeid="4" roadtypename="urban Restricted Access"/> <roadtype roadtypeid="5" roadtypename="urban Unrestricted Access"/> </roadtypes> </filters> <databaseselection servername="localhost" databasename="423_218 5_M214a_PGH_Existing_SCC_mi"/> <agedistribution> <description><![cdata[]]></description> <parts> <sourcetypeagedistribution> <filename>c:\pamoves14a\movesinputs\agedistribution\moves214\14reg_repcty\218\4219_218_sourcetypeagedistribution.csv</filename> </sourcetypeagedistribution> </parts> </agedistribution> <avgspeeddistribution> <description><![cdata[]]></description> <parts> <avgspeeddistribution> <filename>c:\pamoves14a\out\218_m214a_pgh_existing_ann_scc\\423_218 5_M214a_PGH_Existing_SCC\CDM\avgSpeedDistribution.csv</filename> </avgspeeddistribution> </parts> </avgspeeddistribution> <imcoverage> <description><![cdata[]]></description> <parts> <imcoverage> <filename>c:\pamoves14a\movesinputs\im\moves214a\42_218_imcoverage.csv</filename> </imcoverage> </parts> </imcoverage> <fuel> <description><![cdata[]]></description> <parts> <FuelSupply> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\!pgh_rvp_inv\pa_pgh_fuelsupply_14a_218_223_.csv</filename> </FuelSupply> <FuelFormulation> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\!pgh_rvp_inv\pa_pgh_fuelformulation_14a_218_223 RVP78.csv</filename> </FuelFormulation> <FuelUsageFraction> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\movesdefaults\42_fuelusagefraction_14a.csv</filename> </FuelUsageFraction> <AVFT> B-4 B - 131

171 Technical Appendix B - Onroad Emissions Technical Support Document <filename></filename> </AVFT> </parts> </fuel> <zonemonthhour> <description><![cdata[]]></description> <parts> <zonemonthhour> <filename>c:\pamoves14a\movesinputs\meteorology\214\423_214_met.csv</filename> </zonemonthhour> </parts> </zonemonthhour> <roadtypedistribution> <description><![cdata[]]></description> <parts> <roadtypedistribution> <filename>c:\pamoves14a\out\218_m214a_pgh_existing_ann_scc\\423_218 5_M214a_PGH_Existing_SCC\CDM\roadTypeDistribution.csv</filename> </roadtypedistribution> </parts> </roadtypedistribution> <sourcetypepopulation> <description><![cdata[]]></description> <parts> <sourcetypeyear> <filename>c:\pamoves14a\out\218_m214a_pgh_existing_ann_scc\\423_218 5_M214a_PGH_Existing_SCC\CDM\SourceTypePopulation.csv</filename> </sourcetypeyear> </parts> </sourcetypepopulation> <rampfraction> <description><![cdata[]]></description> <parts> <roadtype> <filename>c:\pamoves14a\movesinputs\rampfraction\rampfraction_defaults.csv</filename> </roadtype> </parts> </rampfraction> <vehicletypevmt> <description><![cdata[]]></description> <parts> <hpmsvtypeyear> <filename>c:\pamoves14a\out\218_m214a_pgh_existing_ann_scc\\423_218 5_M214a_PGH_Existing_SCC\CDM\hpmsVTypeYear.csv</filename> </hpmsvtypeyear> <monthvmtfraction> <filename>c:\pamoves14a\out\218_m214a_pgh_existing_ann_scc\\423_218 5_M214a_PGH_Existing_SCC\CDM\NotUsed\MonthVMTFraction_M21AB_Import.csv</filename> </monthvmtfraction> <dayvmtfraction> <filename>c:\pamoves14a\movesinputs\monthdayhourfractions\dayvmtfraction_avgday.csv</filename> </dayvmtfraction> <hourvmtfraction> <filename>c:\pamoves14a\out\218_m214a_pgh_existing_ann_scc\\423_218 5_M214a_PGH_Existing_SCC\CDM\hourvmtfraction.csv</filename> </hourvmtfraction> </parts> </vehicletypevmt> <starts> <description><![cdata[]]></description> <parts> <startsperday> <filename></filename> </startsperday> B-4 B - 132

172 Technical Appendix B - Onroad Emissions Technical Support Document <startshourfraction> <filename></filename> </startshourfraction> <startssourcetypefraction> <filename></filename> </startssourcetypefraction> <startsmonthadjust> <filename></filename> </startsmonthadjust> <importstartsopmodedistribution> <filename></filename> </importstartsopmodedistribution> <Starts> <filename></filename> </Starts> </parts> </starts> <hotelling> <description><![cdata[]]></description> <parts> <hotellingactivitydistribution> <filename></filename> </hotellingactivitydistribution> <hotellinghours> <filename></filename> </hotellinghours> </parts> </hotelling> <onroadretrofit> <description><![cdata[]]></description> <parts> <onroadretrofit> <filename></filename> </onroadretrofit> </parts> </onroadretrofit> </moves> <generic> <description><![cdata[]]></description> <parts> <anytable> <tablename>regioncounty</tablename> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\movesdefaults\42_regioncounty_moves214adefaults.csv</filename> </anytable> </parts> </generic> </importer> Sample mrs file format <runspec version="moves214a "> <description><![cdata[moves214a RunSpec Created by CENTRAL4 Scenario: ALLE 218 ANNAVG M214a_PGH_Existing_SCC Emission Inventory with user's data]]></description> <models> <model value="onroad"/> </models> <modelscale value="inv"/> <modeldomain value="single"/> <geographicselections> <geographicselection type="county" key="423" description="pennsylvania - Allegheny County"/> </geographicselections> <timespan> B-4 B - 133

173 Technical Appendix B - Onroad Emissions Technical Support Document <year key="218"/> <month id="1"/> <month id="2"/> <month id="3"/> <month id="4"/> <month id="5"/> <month id="6"/> <month id="7"/> <month id="8"/> <month id="9"/> <month id="1"/> <month id="11"/> <month id="12"/> <day id="5"/> <beginhour id="1"/> <endhour id="24"/> <aggregateby key="hour"/> </timespan> <onroadvehicleselections> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> B-4 B - 134

174 Technical Appendix B - Onroad Emissions Technical Support Document <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> </onroadvehicleselections> <offroadvehicleselections> </offroadvehicleselections> <offroadvehiclesccs> </offroadvehiclesccs> <roadtypes separateramps="false"> <roadtype roadtypeid="1" roadtypename="off-network" modelcombination="m1"/> <roadtype roadtypeid="2" roadtypename="rural Restricted Access" modelcombination="m1"/> <roadtype roadtypeid="3" roadtypename="rural Unrestricted Access" modelcombination="m1"/> <roadtype roadtypeid="4" roadtypename="urban Restricted Access" modelcombination="m1"/> <roadtype roadtypeid="5" roadtypename="urban Unrestricted Access" modelcombination="m1"/> </roadtypes> <pollutantprocessassociations> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen (NOx)" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="12" processname="evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="13" processname="evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="12" processname="evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="13" processname="evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="12" processname="evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="13" processname="evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="118" pollutantname="composite - NonECPM" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="118" pollutantname="composite - NonECPM" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="118" pollutantname="composite - NonECPM" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="118" pollutantname="composite - NonECPM" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="112" pollutantname="elemental Carbon" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="112" pollutantname="elemental Carbon" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="112" pollutantname="elemental Carbon" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="112" pollutantname="elemental Carbon" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="119" pollutantname="h2o (aerosol)" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="119" pollutantname="h2o (aerosol)" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="119" pollutantname="h2o (aerosol)" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="119" pollutantname="h2o (aerosol)" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="9" processname="extended Idle Exhaust"/> B-4 B - 135

175 Technical Appendix B - Onroad Emissions Technical Support Document <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="116" pollutantname="primary PM2.5 - Brakewear Particulate" processkey="9" processname="brakewear"/> <pollutantprocessassociation pollutantkey="117" pollutantname="primary PM2.5 - Tirewear Particulate" processkey="1" processname="tirewear"/> <pollutantprocessassociation pollutantkey="115" pollutantname="sulfate Particulate" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="115" pollutantname="sulfate Particulate" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="115" pollutantname="sulfate Particulate" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="115" pollutantname="sulfate Particulate" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="11" processname="evap Permeation"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="11" processname="evap Permeation"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="11" processname="evap Permeation"/> </pollutantprocessassociations> <databaseselections> <databaseselection servername="localhost" databasename="moves214_early_nlev" description=""/> <databaseselection servername="localhost" databasename="moves214_calevii8" description=""/> </databaseselections> <inputdatabase servername="" databasename="" description=""/> <uncertaintyparameters uncertaintymodeenabled="false" numberofrunspersimulation="" numberofsimulations=""/> <geographicoutputdetail description="county"/> <outputemissionsbreakdownselection> <modelyear selected="false"/> <fueltype selected="false"/> <fueltype selected="true"/> <fuelsubtype selected="false"/> <emissionprocess selected="true"/> <onroadoffroad selected="true"/> <roadtype selected="true"/> <roadtype selected="false"/> <sourceusetype selected="true"/> <sourceusetype selected="false"/> <movesvehicletype selected="false"/> <onroadscc selected="false"/> <onroadscc selected="true"/> <offroadscc selected="false"/> <estimateuncertainty selected="false" numberofiterations="2" keepsampleddata="false" keepiterations="false"/> <sector selected="false"/> <engtechid selected="false"/> <hpclass selected="false"/> </outputemissionsbreakdownselection> <outputdatabase servername="localhost" databasename="423_218 5_M214a_PGH_Existing_SCC_mo" description=""/>> <outputtimestep value="24-hour Day"/> <outputvmtdata value="true"/> <outputsho value="true"/> <outputsh value="true"/> <outputshp value="true"/> <outputshidling value="true"/> <outputstarts value="true"/> <outputpopulation value="true"/> <scaleinputdatabase servername="localhost" databasename="423_218 5_M214a_PGH_Existing_SCC_mi" description=""/> <pmsize value=""/> <outputfactors> <timefactors selected="true" units="hours"/> <distancefactors selected="false" units="miles"/> <massfactors selected="false" units="grams" energyunits="million BTU"/> </outputfactors> <savedata> </savedata> <donotexecute> </donotexecute> <generatordatabase shouldsave="false" servername="" databasename="" description=""/> <donotperformfinalaggregation selected="false"/> <lookuptableflags scenarioid="" truncateoutput="false" truncateactivity="false"/> <internalcontrolstrategies> <internalcontrolstrategy classname="gov.epa.otaq.moves.master.implementation.ghg.internalcontrolstrategies.rateofprogress.rateofprogressstrategy"><![cdata[ useparameters No ]]></internalcontrolstrategy> </internalcontrolstrategies> </runspec> B-4 B - 136

176 Technical Appendix B - Onroad Emissions Technical Support Document Annual MOVES Run Specification File Settings RVP 8.7 Scenario Sample xml file format <moves> <importer mode="county" > <filters> <geographicselections> <geographicselection type="county" key="423" description="pennsylvania - Allegheny County"/> </geographicselections> <timespan> <year key="218"/> <month id=""/> <day id="2"/> <day id="5"/> <beginhour id="1"/> <endhour id="24"/> <aggregateby key="hour"/> </timespan> <onroadvehicleselections> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> B-4 B - 137

177 Technical Appendix B - Onroad Emissions Technical Support Document <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="42" sourcetypename="transit Bus"/> </onroadvehicleselections> <offroadvehicleselections> </offroadvehicleselections> <offroadvehiclesccs> </offroadvehiclesccs> <roadtypes> <roadtype roadtypeid="1" roadtypename="off-network"/> <roadtype roadtypeid="2" roadtypename="rural Restricted Access"/> <roadtype roadtypeid="3" roadtypename="rural Unrestricted Access"/> <roadtype roadtypeid="4" roadtypename="urban Restricted Access"/> <roadtype roadtypeid="5" roadtypename="urban Unrestricted Access"/> </roadtypes> </filters> <databaseselection servername="localhost" databasename="423_218 5_M214a_PGH_RVP87_SCC_mi"/> <agedistribution> <description><![cdata[]]></description> <parts> <sourcetypeagedistribution> <filename>c:\pamoves14a\movesinputs\agedistribution\moves214\14reg_repcty\218\4219_218_sourcetypeagedistribution.csv</filename> </sourcetypeagedistribution> </parts> </agedistribution> <avgspeeddistribution> <description><![cdata[]]></description> <parts> <avgspeeddistribution> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp87_ann_scc\\423_218 5_M214a_PGH_RVP87_SCC\CDM\avgSpeedDistribution.csv</filename> </avgspeeddistribution> </parts> </avgspeeddistribution> <imcoverage> <description><![cdata[]]></description> <parts> <imcoverage> <filename>c:\pamoves14a\movesinputs\im\moves214a\42_218_imcoverage.csv</filename> </imcoverage> </parts> </imcoverage> <fuel> <description><![cdata[]]></description> <parts> <FuelSupply> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\!pgh_rvp_inv\pa_pgh_fuelsupply_14a_218_223_.csv</filename> </FuelSupply> <FuelFormulation> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\!pgh_rvp_inv\pgh_fuelformulation_14a_218_223 RVP87.csv</filename> </FuelFormulation> <FuelUsageFraction> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\movesdefaults\42_fuelusagefraction_14a.csv</filename> </FuelUsageFraction> B-4 B - 138

178 Technical Appendix B - Onroad Emissions Technical Support Document <AVFT> <filename></filename> </AVFT> </parts> </fuel> <zonemonthhour> <description><![cdata[]]></description> <parts> <zonemonthhour> <filename>c:\pamoves14a\movesinputs\meteorology\214\423_214_met.csv</filename> </zonemonthhour> </parts> </zonemonthhour> <roadtypedistribution> <description><![cdata[]]></description> <parts> <roadtypedistribution> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp87_ann_scc\\423_218 5_M214a_PGH_RVP87_SCC\CDM\roadTypeDistribution.csv</filename> </roadtypedistribution> </parts> </roadtypedistribution> <sourcetypepopulation> <description><![cdata[]]></description> <parts> <sourcetypeyear> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp87_ann_scc\\423_218 5_M214a_PGH_RVP87_SCC\CDM\SourceTypePopulation.csv</filename> </sourcetypeyear> </parts> </sourcetypepopulation> <rampfraction> <description><![cdata[]]></description> <parts> <roadtype> <filename>c:\pamoves14a\movesinputs\rampfraction\rampfraction_defaults.csv</filename> </roadtype> </parts> </rampfraction> <vehicletypevmt> <description><![cdata[]]></description> <parts> <hpmsvtypeyear> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp87_ann_scc\\423_218 5_M214a_PGH_RVP87_SCC\CDM\hpmsVTypeYear.csv</filename> </hpmsvtypeyear> <monthvmtfraction> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp87_ann_scc\\423_218 5_M214a_PGH_RVP87_SCC\CDM\NotUsed\MonthVMTFraction_M21AB_Import.csv</filename> </monthvmtfraction> <dayvmtfraction> <filename>c:\pamoves14a\movesinputs\monthdayhourfractions\dayvmtfraction_avgday.csv</filename> </dayvmtfraction> <hourvmtfraction> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp87_ann_scc\\423_218 5_M214a_PGH_RVP87_SCC\CDM\hourvmtfraction.csv</filename> </hourvmtfraction> </parts> </vehicletypevmt> <starts> <description><![cdata[]]></description> <parts> <startsperday> <filename></filename> </startsperday> <startshourfraction> <filename></filename> B-4 B - 139

179 Technical Appendix B - Onroad Emissions Technical Support Document </startshourfraction> <startssourcetypefraction> <filename></filename> </startssourcetypefraction> <startsmonthadjust> <filename></filename> </startsmonthadjust> <importstartsopmodedistribution> <filename></filename> </importstartsopmodedistribution> <Starts> <filename></filename> </Starts> </parts> </starts> <hotelling> <description><![cdata[]]></description> <parts> <hotellingactivitydistribution> <filename></filename> </hotellingactivitydistribution> <hotellinghours> <filename></filename> </hotellinghours> </parts> </hotelling> <onroadretrofit> <description><![cdata[]]></description> <parts> <onroadretrofit> <filename></filename> </onroadretrofit> </parts> </onroadretrofit> </moves> <generic> <description><![cdata[]]></description> <parts> <anytable> <tablename>regioncounty</tablename> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\movesdefaults\42_regioncounty_moves214adefaults.csv</filename> </anytable> </parts> </generic> </importer> Sample mrs file format <runspec version="moves214a "> <description><![cdata[moves214a RunSpec Created by CENTRAL4 Scenario: ALLE 218 ANNAVG M214a_PGH_RVP87_SCC Emission Inventory with user's data]]></description> <models> <model value="onroad"/> </models> <modelscale value="inv"/> <modeldomain value="single"/> <geographicselections> <geographicselection type="county" key="423" description="pennsylvania - Allegheny County"/> </geographicselections> <timespan> <year key="218"/> B-4 B - 14

180 Technical Appendix B - Onroad Emissions Technical Support Document <month id="1"/> <month id="2"/> <month id="3"/> <month id="4"/> <month id="5"/> <month id="6"/> <month id="7"/> <month id="8"/> <month id="9"/> <month id="1"/> <month id="11"/> <month id="12"/> <day id="5"/> <beginhour id="1"/> <endhour id="24"/> <aggregateby key="hour"/> </timespan> <onroadvehicleselections> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="54" sourcetypename="motor Home"/> B-4 B - 141

181 Technical Appendix B - Onroad Emissions Technical Support Document <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> </onroadvehicleselections> <offroadvehicleselections> </offroadvehicleselections> <offroadvehiclesccs> </offroadvehiclesccs> <roadtypes separateramps="false"> <roadtype roadtypeid="1" roadtypename="off-network" modelcombination="m1"/> <roadtype roadtypeid="2" roadtypename="rural Restricted Access" modelcombination="m1"/> <roadtype roadtypeid="3" roadtypename="rural Unrestricted Access" modelcombination="m1"/> <roadtype roadtypeid="4" roadtypename="urban Restricted Access" modelcombination="m1"/> <roadtype roadtypeid="5" roadtypename="urban Unrestricted Access" modelcombination="m1"/> </roadtypes> <pollutantprocessassociations> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen (NOx)" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="12" processname="evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="13" processname="evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="12" processname="evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="13" processname="evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="12" processname="evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="13" processname="evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="118" pollutantname="composite - NonECPM" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="118" pollutantname="composite - NonECPM" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="118" pollutantname="composite - NonECPM" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="118" pollutantname="composite - NonECPM" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="112" pollutantname="elemental Carbon" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="112" pollutantname="elemental Carbon" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="112" pollutantname="elemental Carbon" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="112" pollutantname="elemental Carbon" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="119" pollutantname="h2o (aerosol)" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="119" pollutantname="h2o (aerosol)" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="119" pollutantname="h2o (aerosol)" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="119" pollutantname="h2o (aerosol)" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="91" processname="auxiliary Power Exhaust"/> B-4 B - 142

182 Technical Appendix B - Onroad Emissions Technical Support Document <pollutantprocessassociation pollutantkey="116" pollutantname="primary PM2.5 - Brakewear Particulate" processkey="9" processname="brakewear"/> <pollutantprocessassociation pollutantkey="117" pollutantname="primary PM2.5 - Tirewear Particulate" processkey="1" processname="tirewear"/> <pollutantprocessassociation pollutantkey="115" pollutantname="sulfate Particulate" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="115" pollutantname="sulfate Particulate" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="115" pollutantname="sulfate Particulate" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="115" pollutantname="sulfate Particulate" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="11" processname="evap Permeation"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="11" processname="evap Permeation"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="11" processname="evap Permeation"/> </pollutantprocessassociations> <databaseselections> <databaseselection servername="localhost" databasename="moves214_early_nlev" description=""/> <databaseselection servername="localhost" databasename="moves214_calevii8" description=""/> </databaseselections> <inputdatabase servername="" databasename="" description=""/> <uncertaintyparameters uncertaintymodeenabled="false" numberofrunspersimulation="" numberofsimulations=""/> <geographicoutputdetail description="county"/> <outputemissionsbreakdownselection> <modelyear selected="false"/> <fueltype selected="false"/> <fueltype selected="true"/> <fuelsubtype selected="false"/> <emissionprocess selected="true"/> <onroadoffroad selected="true"/> <roadtype selected="true"/> <roadtype selected="false"/> <sourceusetype selected="true"/> <sourceusetype selected="false"/> <movesvehicletype selected="false"/> <onroadscc selected="false"/> <onroadscc selected="true"/> <offroadscc selected="false"/> <estimateuncertainty selected="false" numberofiterations="2" keepsampleddata="false" keepiterations="false"/> <sector selected="false"/> <engtechid selected="false"/> <hpclass selected="false"/> </outputemissionsbreakdownselection> <outputdatabase servername="localhost" databasename="423_218 5_M214a_PGH_RVP87_SCC_mo" description=""/>> <outputtimestep value="24-hour Day"/> <outputvmtdata value="true"/> <outputsho value="true"/> <outputsh value="true"/> <outputshp value="true"/> <outputshidling value="true"/> <outputstarts value="true"/> <outputpopulation value="true"/> <scaleinputdatabase servername="localhost" databasename="423_218 5_M214a_PGH_RVP87_SCC_mi" description=""/> <pmsize value=""/> <outputfactors> <timefactors selected="true" units="hours"/> <distancefactors selected="false" units="miles"/> <massfactors selected="false" units="grams" energyunits="million BTU"/> </outputfactors> <savedata> </savedata> <donotexecute> </donotexecute> <generatordatabase shouldsave="false" servername="" databasename="" description=""/> <donotperformfinalaggregation selected="false"/> <lookuptableflags scenarioid="" truncateoutput="false" truncateactivity="false"/> <internalcontrolstrategies> <internalcontrolstrategy classname="gov.epa.otaq.moves.master.implementation.ghg.internalcontrolstrategies.rateofprogress.rateofprogressstrategy"><![cdata[ useparameters No ]]></internalcontrolstrategy> </internalcontrolstrategies> </runspec> B-4 B - 143

183 Technical Appendix B - Onroad Emissions Technical Support Document Annual MOVES Run Specification File Settings RVP 1 Scenario Sample xml file format <moves> <importer mode="county" > <filters> <geographicselections> <geographicselection type="county" key="423" description="pennsylvania - Allegheny County"/> </geographicselections> <timespan> <year key="218"/> <month id=""/> <day id="2"/> <day id="5"/> <beginhour id="1"/> <endhour id="24"/> <aggregateby key="hour"/> </timespan> <onroadvehicleselections> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="42" sourcetypename="transit Bus"/> B-4 B - 144

184 Technical Appendix B - Onroad Emissions Technical Support Document <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="42" sourcetypename="transit Bus"/> </onroadvehicleselections> <offroadvehicleselections> </offroadvehicleselections> <offroadvehiclesccs> </offroadvehiclesccs> <roadtypes> <roadtype roadtypeid="1" roadtypename="off-network"/> <roadtype roadtypeid="2" roadtypename="rural Restricted Access"/> <roadtype roadtypeid="3" roadtypename="rural Unrestricted Access"/> <roadtype roadtypeid="4" roadtypename="urban Restricted Access"/> <roadtype roadtypeid="5" roadtypename="urban Unrestricted Access"/> </roadtypes> </filters> <databaseselection servername="localhost" databasename="423_218 5_M214a_PGH_RVP1_SCC_mi"/> <agedistribution> <description><![cdata[]]></description> <parts> <sourcetypeagedistribution> <filename>c:\pamoves14a\movesinputs\agedistribution\moves214\14reg_repcty\218\4219_218_sourcetypeagedistribution.csv</filename> </sourcetypeagedistribution> </parts> </agedistribution> <avgspeeddistribution> <description><![cdata[]]></description> <parts> <avgspeeddistribution> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp1_ann_scc\\423_218 5_M214a_PGH_RVP1_SCC\CDM\avgSpeedDistribution.csv</filename> </avgspeeddistribution> </parts> </avgspeeddistribution> <imcoverage> <description><![cdata[]]></description> <parts> <imcoverage> <filename>c:\pamoves14a\movesinputs\im\moves214a\42_218_imcoverage.csv</filename> </imcoverage> </parts> </imcoverage> <fuel> <description><![cdata[]]></description> <parts> <FuelSupply> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\!pgh_rvp_inv\pa_pgh_fuelsupply_14a_218_223_.csv</filename> </FuelSupply> <FuelFormulation> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\!pgh_rvp_inv\pgh_fuelformulation_14a_218_223 RVP1.csv</filename> </FuelFormulation> <FuelUsageFraction> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\movesdefaults\42_fuelusagefraction_14a.csv</filename> </FuelUsageFraction> <AVFT> <filename></filename> B-4 B - 145

185 Technical Appendix B - Onroad Emissions Technical Support Document </AVFT> </parts> </fuel> <zonemonthhour> <description><![cdata[]]></description> <parts> <zonemonthhour> <filename>c:\pamoves14a\movesinputs\meteorology\214\423_214_met.csv</filename> </zonemonthhour> </parts> </zonemonthhour> <roadtypedistribution> <description><![cdata[]]></description> <parts> <roadtypedistribution> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp1_ann_scc\\423_218 5_M214a_PGH_RVP1_SCC\CDM\roadTypeDistribution.csv</filename> </roadtypedistribution> </parts> </roadtypedistribution> <sourcetypepopulation> <description><![cdata[]]></description> <parts> <sourcetypeyear> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp1_ann_scc\\423_218 5_M214a_PGH_RVP1_SCC\CDM\SourceTypePopulation.csv</filename> </sourcetypeyear> </parts> </sourcetypepopulation> <rampfraction> <description><![cdata[]]></description> <parts> <roadtype> <filename>c:\pamoves14a\movesinputs\rampfraction\rampfraction_defaults.csv</filename> </roadtype> </parts> </rampfraction> <vehicletypevmt> <description><![cdata[]]></description> <parts> <hpmsvtypeyear> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp1_ann_scc\\423_218 5_M214a_PGH_RVP1_SCC\CDM\hpmsVTypeYear.csv</filename> </hpmsvtypeyear> <monthvmtfraction> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp1_ann_scc\\423_218 5_M214a_PGH_RVP1_SCC\CDM\NotUsed\MonthVMTFraction_M21AB_Import.csv</filename> </monthvmtfraction> <dayvmtfraction> <filename>c:\pamoves14a\movesinputs\monthdayhourfractions\dayvmtfraction_avgday.csv</filename> </dayvmtfraction> <hourvmtfraction> <filename>c:\pamoves14a\out\218_m214a_pgh_rvp1_ann_scc\\423_218 5_M214a_PGH_RVP1_SCC\CDM\hourvmtfraction.csv</filename> </hourvmtfraction> </parts> </vehicletypevmt> <starts> <description><![cdata[]]></description> <parts> <startsperday> <filename></filename> </startsperday> <startshourfraction> <filename></filename> </startshourfraction> <startssourcetypefraction> B-3 B - 146

186 Technical Appendix B - Onroad Emissions Technical Support Document <filename></filename> </startssourcetypefraction> <startsmonthadjust> <filename></filename> </startsmonthadjust> <importstartsopmodedistribution> <filename></filename> </importstartsopmodedistribution> <Starts> <filename></filename> </Starts> </parts> </starts> <hotelling> <description><![cdata[]]></description> <parts> <hotellingactivitydistribution> <filename></filename> </hotellingactivitydistribution> <hotellinghours> <filename></filename> </hotellinghours> </parts> </hotelling> <onroadretrofit> <description><![cdata[]]></description> <parts> <onroadretrofit> <filename></filename> </onroadretrofit> </parts> </onroadretrofit> </moves> <generic> <description><![cdata[]]></description> <parts> <anytable> <tablename>regioncounty</tablename> <filename>c:\pamoves14a\movesinputs\fuel\moves214a\movesdefaults\42_regioncounty_moves214adefaults.csv</filename> </anytable> </parts> </generic> </importer> Sample mrs file format <runspec version="moves214a "> <description><![cdata[moves214a RunSpec Created by CENTRAL4 Scenario: ALLE 218 ANNAVG M214a_PGH_RVP1_SCC Emission Inventory with user's data]]></description> <models> <model value="onroad"/> </models> <modelscale value="inv"/> <modeldomain value="single"/> <geographicselections> <geographicselection type="county" key="423" description="pennsylvania - Allegheny County"/> </geographicselections> <timespan> <year key="218"/> <month id="1"/> <month id="2"/> B-4 B - 147

187 Technical Appendix B - Onroad Emissions Technical Support Document <month id="3"/> <month id="4"/> <month id="5"/> <month id="6"/> <month id="7"/> <month id="8"/> <month id="9"/> <month id="1"/> <month id="11"/> <month id="12"/> <day id="5"/> <beginhour id="1"/> <endhour id="24"/> <aggregateby key="hour"/> </timespan> <onroadvehicleselections> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="11" sourcetypename="motorcycle"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="21" sourcetypename="passenger Car"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="31" sourcetypename="passenger Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="32" sourcetypename="light Commercial Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="41" sourcetypename="intercity Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="42" sourcetypename="transit Bus"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="43" sourcetypename="school Bus"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="3" fueltypedesc="compressed Natural Gas (CNG)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="2" fueltypedesc="diesel Fuel" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="51" sourcetypename="refuse Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="52" sourcetypename="single Unit Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="53" sourcetypename="single Unit Long-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="54" sourcetypename="motor Home"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="61" sourcetypename="combination Short-haul Truck"/> <onroadvehicleselection fueltypeid="5" fueltypedesc="ethanol (E-85)" sourcetypeid="62" sourcetypename="combination Long-haul Truck"/> B-4 B - 148

188 Technical Appendix B - Onroad Emissions Technical Support Document </onroadvehicleselections> <offroadvehicleselections> </offroadvehicleselections> <offroadvehiclesccs> </offroadvehiclesccs> <roadtypes separateramps="false"> <roadtype roadtypeid="1" roadtypename="off-network" modelcombination="m1"/> <roadtype roadtypeid="2" roadtypename="rural Restricted Access" modelcombination="m1"/> <roadtype roadtypeid="3" roadtypename="rural Unrestricted Access" modelcombination="m1"/> <roadtype roadtypeid="4" roadtypename="urban Restricted Access" modelcombination="m1"/> <roadtype roadtypeid="5" roadtypename="urban Unrestricted Access" modelcombination="m1"/> </roadtypes> <pollutantprocessassociations> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen (NOx)" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="12" processname="evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="13" processname="evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="12" processname="evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="13" processname="evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="12" processname="evap Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="13" processname="evap Fuel Leaks"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="118" pollutantname="composite - NonECPM" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="118" pollutantname="composite - NonECPM" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="118" pollutantname="composite - NonECPM" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="118" pollutantname="composite - NonECPM" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="112" pollutantname="elemental Carbon" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="112" pollutantname="elemental Carbon" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="112" pollutantname="elemental Carbon" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="112" pollutantname="elemental Carbon" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="119" pollutantname="h2o (aerosol)" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="119" pollutantname="h2o (aerosol)" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="119" pollutantname="h2o (aerosol)" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="119" pollutantname="h2o (aerosol)" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="16" processname="crankcase Start Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="17" processname="crankcase Extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="116" pollutantname="primary PM2.5 - Brakewear Particulate" processkey="9" processname="brakewear"/> <pollutantprocessassociation pollutantkey="117" pollutantname="primary PM2.5 - Tirewear Particulate" processkey="1" processname="tirewear"/> B-4 B - 149

189 Technical Appendix B - Onroad Emissions Technical Support Document <pollutantprocessassociation pollutantkey="115" pollutantname="sulfate Particulate" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="115" pollutantname="sulfate Particulate" processkey="2" processname="start Exhaust"/> <pollutantprocessassociation pollutantkey="115" pollutantname="sulfate Particulate" processkey="9" processname="extended Idle Exhaust"/> <pollutantprocessassociation pollutantkey="115" pollutantname="sulfate Particulate" processkey="91" processname="auxiliary Power Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="11" processname="evap Permeation"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="11" processname="evap Permeation"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="11" processname="evap Permeation"/> </pollutantprocessassociations> <databaseselections> <databaseselection servername="localhost" databasename="moves214_early_nlev" description=""/> <databaseselection servername="localhost" databasename="moves214_calevii8" description=""/> </databaseselections> <inputdatabase servername="" databasename="" description=""/> <uncertaintyparameters uncertaintymodeenabled="false" numberofrunspersimulation="" numberofsimulations=""/> <geographicoutputdetail description="county"/> <outputemissionsbreakdownselection> <modelyear selected="false"/> <fueltype selected="false"/> <fueltype selected="true"/> <fuelsubtype selected="false"/> <emissionprocess selected="true"/> <onroadoffroad selected="true"/> <roadtype selected="true"/> <roadtype selected="false"/> <sourceusetype selected="true"/> <sourceusetype selected="false"/> <movesvehicletype selected="false"/> <onroadscc selected="false"/> <onroadscc selected="true"/> <offroadscc selected="false"/> <estimateuncertainty selected="false" numberofiterations="2" keepsampleddata="false" keepiterations="false"/> <sector selected="false"/> <engtechid selected="false"/> <hpclass selected="false"/> </outputemissionsbreakdownselection> <outputdatabase servername="localhost" databasename="423_218 5_M214a_PGH_RVP1_SCC_mo" description=""/>> <outputtimestep value="24-hour Day"/> <outputvmtdata value="true"/> <outputsho value="true"/> <outputsh value="true"/> <outputshp value="true"/> <outputshidling value="true"/> <outputstarts value="true"/> <outputpopulation value="true"/> <scaleinputdatabase servername="localhost" databasename="423_218 5_M214a_PGH_RVP1_SCC_mi" description=""/> <pmsize value=""/> <outputfactors> <timefactors selected="true" units="hours"/> <distancefactors selected="false" units="miles"/> <massfactors selected="false" units="grams" energyunits="million BTU"/> </outputfactors> <savedata> </savedata> <donotexecute> </donotexecute> <generatordatabase shouldsave="false" servername="" databasename="" description=""/> <donotperformfinalaggregation selected="false"/> <lookuptableflags scenarioid="" truncateoutput="false" truncateactivity="false"/> <internalcontrolstrategies> <internalcontrolstrategy classname="gov.epa.otaq.moves.master.implementation.ghg.internalcontrolstrategies.rateofprogress.rateofprogressstrategy"><![cdata[ useparameters No ]]></internalcontrolstrategy> </internalcontrolstrategies> </runspec> B-4 B - 15

190 APPENDIX C to ACHD Non-Interference Demonstration is Appendix C to PA DEP NID as follows:

191 APPENDIX C NONROAD Documentation Bureau of Air Quality Department of Environmental Protection

192 Technical Appendix C - NONROAD Documentation RVP 7.8 Scenario MOVES NONROAD Run Specifications for 218 and 223 Pittsburgh - Beaver Valley Area <runspec version="moves214a "> <description><![cdata[rvp 7.8, PBV all Counties; 218 & 223; all months; weekend, weekday, aggregate by day, by SCC & Sector]]></description> <models> <model value="nonroad"/> </models> <modelscale value="inv"/> <modeldomain value="national"/> <geographicselections> <geographicselection type="county" key="423" description="pennsylvania - Allegheny County"/> <geographicselection type="county" key="425" description="pennsylvania - Armstrong County"/> <geographicselection type="county" key="427" description="pennsylvania - Beaver County"/> <geographicselection type="county" key="4219" description="pennsylvania - Butler County"/> <geographicselection type="county" key="4251" description="pennsylvania - Fayette County"/> <geographicselection type="county" key="42125" description="pennsylvania - Washington County"/> <geographicselection type="county" key="42129" description="pennsylvania - Westmoreland County"/> </geographicselections> <timespan> <year key="218"/> <month id="1"/> <month id="2"/> <month id="3"/> <month id="4"/> <month id="5"/> <month id="6"/> <month id="7"/> <month id="8"/> <month id="9"/> <month id="1"/> <month id="11"/> <month id="12"/> <day id="2"/> <day id="5"/> <beginhour id=""/> <endhour id=""/> <aggregateby key="hour"/> </timespan> <onroadvehicleselections> </onroadvehicleselections> <offroadvehicleselections> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="5" sectorname="agriculture"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="8" sectorname="airport Support"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="6" sectorname="commercial"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="2" sectorname="construction"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="3" sectorname="industrial"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="4" sectorname="lawn/garden"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="7" sectorname="logging"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="1" sectorname="oil Field"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="11" sectorname="pleasure Craft"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="12" sectorname="railroad"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="1" sectorname="recreational"/> </offroadvehicleselections> <offroadvehiclesccs> </offroadvehiclesccs> <roadtypes separateramps="false"> <roadtype roadtypeid="1" roadtypename="nonroad" modelcombination="m2"/> </roadtypes> <pollutantprocessassociations> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="18" processname="refueling Displacement Vapor Loss"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="19" processname="refueling Spillage Loss"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="2" processname="evap Tank Permeation"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="21" processname="evap Hose Permeation"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="3" processname="diurnal Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="31" processname="hotsoak Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="32" processname="runningloss Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen (NOx)" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="18" processname="refueling Displacement Vapor Loss"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="19" processname="refueling Spillage Loss"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="2" processname="evap Tank Permeation"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="21" processname="evap Hose Permeation"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="3" processname="diurnal Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="31" processname="hotsoak Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="32" processname="runningloss Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="18" processname="refueling Displacement Vapor Loss"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="19" processname="refueling Spillage Loss"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="2" processname="evap Tank Permeation"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="21" processname="evap Hose Permeation"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="3" processname="diurnal Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="31" processname="hotsoak Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="32" processname="runningloss Fuel Vapor Venting"/> </pollutantprocessassociations> <databaseselections> Page 1

193 Technical Appendix C - NONROAD Documentation </databaseselections> <internalcontrolstrategies> <internalcontrolstrategy classname="gov.epa.otaq.moves.master.implementation.ghg.internalcontrolstrategies.rateofprogress.rateofprogressstrategy"><![cdata[ useparame No ]]></internalcontrolstrategy> </internalcontrolstrategies> <inputdatabase servername="" databasename="" description=""/> <uncertaintyparameters uncertaintymodeenabled="false" numberofrunspersimulation="" numberofsimulations=""/> <geographicoutputdetail description="county"/> <outputemissionsbreakdownselection> <modelyear selected="false"/> <fueltype selected="false"/> <fuelsubtype selected="false"/> <emissionprocess selected="false"/> <onroadoffroad selected="true"/> <roadtype selected="false"/> <sourceusetype selected="false"/> <movesvehicletype selected="false"/> <onroadscc selected="true"/> <estimateuncertainty selected="false" numberofiterations="2" keepsampleddata="false" keepiterations="false"/> <sector selected="true"/> <engtechid selected="false"/> <hpclass selected="false"/> <regclassid selected="false"/> </outputemissionsbreakdownselection> <outputdatabase servername="" databasename="nr_pbv_rvp7_8_218_223_out" description=""/> <outputtimestep value="24-hour Day"/> <outputvmtdata value="false"/> <outputsho value="false"/> <outputsh value="false"/> <outputshp value="false"/> <outputshidling value="false"/> <outputstarts value="false"/> <outputpopulation value="false"/> <scaleinputdatabase servername="" databasename="" description=""/> <pmsize value=""/> <outputfactors> <timefactors selected="true" units="days"/> <distancefactors selected="true" units="miles"/> <massfactors selected="true" units="grams" energyunits="joules"/> </outputfactors> <savedata> </savedata> <donotexecute> </donotexecute> <generatordatabase shouldsave="false" servername="" databasename="" description=""/> <donotperformfinalaggregation selected="false"/> <lookuptableflags scenarioid="" truncateoutput="true" truncateactivity="true" truncatebaserates="true"/> </runspec> Page 2

194 Technical Appendix C - NONROAD Documentation RVP 1. Scenario <runspec version="moves214a "> <description><![cdata[pbv RVP Repeal- All counties: 218, 223 RVP1 by SCC and Sector: Run 1 on nr_pbv_rvp1_218_223_a_out]]></description> <models> <model value="nonroad"/> </models> <modelscale value="inv"/> <modeldomain value="national"/> <geographicselections> <geographicselection type="county" key="423" description="pennsylvania - Allegheny County"/> <geographicselection type="county" key="425" description="pennsylvania - Armstrong County"/> <geographicselection type="county" key="427" description="pennsylvania - Beaver County"/> <geographicselection type="county" key="4219" description="pennsylvania - Butler County"/> <geographicselection type="county" key="4251" description="pennsylvania - Fayette County"/> <geographicselection type="county" key="42125" description="pennsylvania - Washington County"/> <geographicselection type="county" key="42129" description="pennsylvania - Westmoreland County"/> </geographicselections> <timespan> <year key="218"/> <year key="223"/> <month id="1"/> <month id="2"/> <month id="3"/> <month id="4"/> <month id="5"/> <month id="6"/> <month id="7"/> <month id="8"/> <month id="9"/> <month id="1"/> <month id="11"/> <month id="12"/> <day id="2"/> <day id="5"/> <beginhour id=""/> <endhour id=""/> <aggregateby key="hour"/> </timespan> <onroadvehicleselections> </onroadvehicleselections> <offroadvehicleselections> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="5" sectorname="agriculture"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="8" sectorname="airport Support"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="6" sectorname="commercial"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="2" sectorname="construction"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="3" sectorname="industrial"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="4" sectorname="lawn/garden"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="7" sectorname="logging"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="1" sectorname="oil Field"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="11" sectorname="pleasure Craft"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="12" sectorname="railroad"/> <offroadvehicleselection fueltypeid="1" fueltypedesc="gasoline" sectorid="1" sectorname="recreational"/> </offroadvehicleselections> <offroadvehiclesccs> </offroadvehiclesccs> <roadtypes separateramps="false"> <roadtype roadtypeid="1" roadtypename="nonroad" modelcombination="m2"/> </roadtypes> <pollutantprocessassociations> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="18" processname="refueling Displacement Vapor Loss"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="19" processname="refueling Spillage Loss"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="2" processname="evap Tank Permeation"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="21" processname="evap Hose Permeation"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="3" processname="diurnal Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="31" processname="hotsoak Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="79" pollutantname="non-methane Hydrocarbons" processkey="32" processname="runningloss Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="3" pollutantname="oxides of Nitrogen (NOx)" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="11" pollutantname="primary Exhaust PM2.5 - Total" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="31" pollutantname="sulfur Dioxide (SO2)" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="18" processname="refueling Displacement Vapor Loss"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="19" processname="refueling Spillage Loss"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="2" processname="evap Tank Permeation"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="21" processname="evap Hose Permeation"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="3" processname="diurnal Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="31" processname="hotsoak Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="1" pollutantname="total Gaseous Hydrocarbons" processkey="32" processname="runningloss Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="1" processname="running Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="15" processname="crankcase Running Exhaust"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="18" processname="refueling Displacement Vapor Loss"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="19" processname="refueling Spillage Loss"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="2" processname="evap Tank Permeation"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="21" processname="evap Hose Permeation"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="3" processname="diurnal Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="31" processname="hotsoak Fuel Vapor Venting"/> <pollutantprocessassociation pollutantkey="87" pollutantname="volatile Organic Compounds" processkey="32" processname="runningloss Fuel Vapor Venting"/> </pollutantprocessassociations> Page 3

195 Technical Appendix C - NONROAD Documentation <databaseselections> <databaseselection servername="localhost" databasename="nr_fuels_pbv_rvp_in" description=""/> </databaseselections> <internalcontrolstrategies> <internalcontrolstrategy classname="gov.epa.otaq.moves.master.implementation.ghg.internalcontrolstrategies.rateofprogress.rateofprogressstrategy"><![cdata[ useparame No ]]></internalcontrolstrategy> </internalcontrolstrategies> <inputdatabase servername="" databasename="" description=""/> <uncertaintyparameters uncertaintymodeenabled="false" numberofrunspersimulation="" numberofsimulations=""/> <geographicoutputdetail description="county"/> <outputemissionsbreakdownselection> <modelyear selected="false"/> <fueltype selected="false"/> <fuelsubtype selected="false"/> <emissionprocess selected="false"/> <onroadoffroad selected="true"/> <roadtype selected="false"/> <sourceusetype selected="false"/> <movesvehicletype selected="false"/> <onroadscc selected="true"/> <estimateuncertainty selected="false" numberofiterations="2" keepsampleddata="false" keepiterations="false"/> <sector selected="true"/> <engtechid selected="false"/> <hpclass selected="false"/> <regclassid selected="false"/> </outputemissionsbreakdownselection> <outputdatabase servername="" databasename="nr_pbv_rvp1_218_223_a_out" description=""/> <outputtimestep value="24-hour Day"/> <outputvmtdata value="false"/> <outputsho value="false"/> <outputsh value="false"/> <outputshp value="false"/> <outputshidling value="false"/> <outputstarts value="false"/> <outputpopulation value="false"/> <scaleinputdatabase servername="" databasename="" description=""/> <pmsize value=""/> <outputfactors> <timefactors selected="true" units="days"/> <distancefactors selected="true" units="miles"/> <massfactors selected="true" units="grams" energyunits="joules"/> </outputfactors> <savedata> </savedata> <donotexecute> </donotexecute> <generatordatabase shouldsave="false" servername="" databasename="" description=""/> <donotperformfinalaggregation selected="false"/> <lookuptableflags scenarioid="" truncateoutput="true" truncateactivity="true" truncatebaserates="true"/> </runspec> Page 4

196 Technical Appendix C - NONROAD Documentation NONROAD Model output was aggregated and the emissions changes estimated in the following manner: For each SCC, the average of each summer or winter month weekday or weekend emissions quantity was calculated for each county. The summer month daily emissions for the Pittsburgh Beaver Valley area are the average of the weekday or weekend emissions values for months 5,6,7,8 and 9 (May through September) and months 1,2,3,4,1,11 and 12 for winter. The average daily values are then multiplied by the number of weekdays or weekend days respectively in the given year (see Appendix Tables C1 and C2 for values). Annual totals in g/day for each SCC are summed for summer and winter seasons and converted to tons. Total estimated annual emissons from the RVP7.8 scenario (Total Summer + Total Winter Emissions) are subtracted from the RVP1 scenario to yield the annual emissions difference. Summer daily emissions are estimated by dividing the annual emissions difference by the number of summer days (note: there is no change in emissions in the winter months). 223 NONROAD Daily Emissions Summary by Fuel RVP Type, Season and Day RVP7.8 RVP1 Winter Summer Winter Summer P-BV Area Emissions P-BV Area Emissions P-BV Area Emissions P-BV Area Emissions SCC Weekday Weekend Total Annual Weekday Weekend Total Annual Weekday Weekend Total Annual Weekday Weekend Total Annual (g/day) (g/day) (g/yr) (g/day) (g/day) (g/yr) (g/day) (g/day) (g/yr) (g/day) (g/day) (g/yr) ,51 1,42,94 191,211,25 1,286,597 2,556,99 252,743,69 74,51 1,42,94 191,211,25 1,298,569 2,57, ,648,95 31, ,591 84,233,574 12,531 12,531 1,917,21 31, ,591 84,233,574 2,975 2,975 3,29, , ,95 58,62,648 4, ,386 77,569, , ,95 58,62, ,55 793,828 8,823,442 5,649 9,971 1,456,88 1,929 18,794 2,18,197 5,649 9,971 1,456,88 13,51 2,924 2,343,221 57,128 28,676 1,44,71 66,883 33,75 8,773,285 57,128 28,676 1,44,71 67,218 34,38 8,824,451 1, ,451 2,324 1,187 35,537 1, ,451 2,355 1,218 31,319 2,355 1, ,363 2,773 1, ,45 2,355 1, ,363 2,86 1, , , , , ,2 146,13 73,169 26,61,917 17,64 85,562 22,364, ,13 73,169 26,61,917 17,981 85,895 22,416, , , , , , , , , , , , ,171 8,937 17,261 2,394,169 17,455 33,419 3,373,81 8,937 17,261 2,394,169 18,292 34,32 3,53,63 34,17 21,34 6,464,65 65,44 4,957 8,935,5 34,17 21,34 6,464,65 65,712 41,158 8,973, ,24 452,223 62,276, , ,22 47,54, ,24 452,223 62,276,378 25, ,637 47,977,939 1,119,938 7, ,247,771 1,19, ,16 151,435,666 1,119,938 7, ,247,771 1,111,17 695, ,72,34 184, ,423 49,328,889 36, ,765 69,596, , ,423 49,328, ,5 76,24 72,172,975 41,36 251,247 76,81,486 77, ,399 15,185,422 41,36 251,247 76,81, , ,859 15,639, ,385 25,346 29,43, ,374 42,653 42,173, ,385 25,346 29,43, , ,668 46,55,296 41, ,228 76,61,997 77,11 482,333 15,153,841 41, ,228 76,61, , ,211 15,668, ,44 942, ,595,683 13,998 13,998 2,141, ,44 942, ,595,683 21,299 21,299 3,258, , , ,386,957 1,155 1, , , , ,386,957 1,747 1, , , , , , ,2 1, , ,2 1, ,418 4,158 2,248 7,318,819 4,185 2,492 5,281,778 4,158 2,248 7,318,819 4,771 21,32 5,369, , ,765 51,79, , ,794 37,114, , ,765 51,79, , ,796 37,454, , , , ,37 1, ,472 1, ,519 1, ,472 1, ,86 24,589 12,32 4,475,67 24,344 12,192 3,189,927 24,589 12,32 4,475,67 24,39 12,219 3,196,137 34,281 65,151 9,119,73 61, ,79 11,834,489 34,281 65,151 9,119,73 67, ,91 12,72, ,616 71,41 98,57,196 68,63 1,263, ,794, ,616 71,41 98,57,196 75,575 1,339,45 14,746, , ,431 3,747,54 197, ,431 38,536,51 113, ,431 3,747,54 22, ,682 39,315,999 5,439 9,675 1,47,267 1,473 17,768 1,923,38 5,439 9,675 1,47,267 11,42 18,76 2,65,833 2,464 1, ,89 2,755 1, ,127 2,464 1, ,89 2,826 1, , , , , ,627 6,384 3,266 1,166,315 7,239 3, ,76 6,384 3,266 1,166,315 7,461 4,13 989,817 4,399 2,244 83,331 4,92 2, ,94 4,399 2,244 83,331 5,7 2,79 671,768 1,523 5,589 1,934,752 12,348 6,934 1,651,57 1,523 5,589 1,934,752 13,394 7,972 1,81,665 Page 5

197 Technical Appendix C - NONROAD Documentation SCC Weekday (g/day) Weekend (g/day) Total Annual (g/yr) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) 4,584 2, ,99 5,182 2, ,976 4,584 2, ,99 5,38 2, , , , , ,673 7,898 4,47 1,443,364 8,89 4,67 1,174,57 7,898 4,47 1,443,364 9,212 4,986 1,223,488 3,191 1, ,27 3,811 2, ,965 3,191 1, ,27 4,29 2, ,841 18,163 9,226 3,314,24 2,214 1,44 2,662,724 18,163 9,226 3,314,24 2,72 1,915 2,736,768 1,358 5,886 1,927,65 13,119 8,24 1,79,925 1,358 5,886 1,927,65 15,335 1,414 2,129, , , , ,959 1, ,129 1, ,32 1, ,129 1, , , , , , , , , ,292 5,712 2,913 1,42,964 6,382 3, ,768 5,712 2,913 1,42,964 6,568 3,54 87,15 2,296 1,24 421,184 2,646 1, ,329 2,296 1,24 421,184 2,836 1, ,24 1, ,98 2,64 1, ,485 1, ,98 2,381 1,6 329, , , , ,637 1,917 1,5 351,721 1,916 1,63 255,633 1,917 1,5 351,721 2,89 1, , , , , , , , , ,953 2,326 1, ,234 2,226 1, ,69 2,326 1, ,234 2,38 1,213 34, , , , , , , , , , , , , ,218 71,748 1,893, ,3 1,361, ,452,96 383,218 71,748 1,893, ,943 1,451,41 154,39,65 211, ,692 4,85, , ,794 54,82, , ,692 4,85,316 42, ,995 55,78,96 33,943 64,25 9,,878 65, ,382 12,567,758 33,943 64,25 9,,878 71, ,527 13,44,752 12,683 75,578 22,878,44 226, ,8 3,95,265 12,683 75,578 22,878,44 229, ,94 31,372,858 2,759 5, ,687 5,375 1,84 1,29,616 2,759 5, ,687 5,673 1,422 1,76,98 5,651 3,544 1,71,586 1,627 6,674 1,452,33 5,651 3,544 1,71,586 1,777 6,78 1,472,973 3,476 5, ,388 6,96 11,554 1,266,99 3,476 5, ,388 8,486 13,158 1,53, ,257 82,27 24,887, , ,386 33,4, ,257 82,27 24,887, , ,115 34,16, ,98 258,58 36,168,463 31,935 31,935 4,886,64 135,98 258,58 36,168,463 5,135 5,135 7,67, ,43 15,6 45,396,915 2,675 2,675 49,3 239,43 15,6 45,396,915 4,15 4,15 635,12 51,692 87,456 13,14,468 13, ,168 18,691,747 51,692 87,456 13,14, , ,341 22,691,532 12,714 8,47 2,415,411 23,485 14,915 3,216,12 12,714 8,47 2,415,411 24,424 15,651 3,35,833 14,72 9,62 2,814,63 27,693 18,337 3,825,359 14,72 9,62 2,814,63 29,683 2,99 4,119,857 13,63 8,613 2,588,568 25,696 16,29 3,517,576 13,63 8,613 2,588,568 26,34 16,789 3,65, ,8 1,18,19 147,423,829 1,15,33 1,933,5 25,554, ,8 1,18,19 147,423,829 1,3,471 2,148,36 236,264, ,696 14,332 31,445,746 34, ,428 41,75, ,696 14,332 31,445, ,17 199,94 43,149,315 17,211 1,916 3,271,61 31,658 2,153 4,337,425 17,211 1,916 3,271,61 33,553 21,591 4,67, ,641 36,72 92,67,632 89, , ,987,1 484,641 36,72 92,67,632 93,47 596, ,65,17 23,776 4,292 6,31,475 47,252 77,595 8,564,663 23,776 4,292 6,31,475 59,157 9,189 1,416,459 21,687 15,561 4,23,138 42,392 31,169 5,992,18 21,687 15,561 4,23,138 51,325 39,829 7,346, , , , , , , , , , , , , , , , , ,618 1,875 1,97 35,817 3,583 2,17 486,23 1,875 1,97 35,817 4,82 2, ,234 6,564 3,69 1,214,28 12,612 7,24 1,691,683 6,564 3,69 1,214,28 12,99 7,578 1,749,355 Page 6

198 Technical Appendix C - NONROAD Documentation SCC Grand Total (g/day) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) ,21 1, , ,21 1, , ,2 1, , ,2 1,788 1,87 242, , , , ,72 88, ,36 149,122, , , ,9,321 88, ,36 149,122, ,925 61,112 13,753,79 218, ,97 39,924, , ,314 28,36,37 218, ,97 39,924, , ,824 3,114,694 92,52 46,741 16,796,311 88,539 45,922 11,671,35 92,52 46,741 16,796,311 92,36 48,973 12,222,12 213,14 17,696 38,858,995 23,622 14,461 26,791, ,14 17,696 38,858,995 21,291 19,481 27,738, , ,511 75,354,455 49, ,6 54,51,53 411, ,511 75,354, , ,81 59,194,795 15,24 7,788 2,783,676 14,632 7,76 1,933,995 15,24 7,788 2,783,676 15,174 8,239 2,16,477 3,629 1, ,47 3,672 2,28 489,46 3,629 1, ,47 3,924 2,25 526, , , , ,955 1,671 1, ,348 1,595 1, ,63 1,671 1, ,348 1,655 1, ,178 11,925 11,925 2,528,57 13,194 13,194 2,18,631 11,925 11,925 2,528,57 13,38 13,38 2,47,82 286,19 1,7,51 13,911, ,754 3,286, ,295,3 286,19 1,7,51 13,911, ,3 3,374, ,569,531 38,849 21,47 17,993, , ,885 43,367,244 38,849 21,47 17,993,311 13, ,54 43,957,461 61, ,87 17,959, ,87 43,814 37,471,642 61, ,87 17,959,797 25,28 466,743 42,94,39 1, ,918 1, ,859 1, ,918 1, ,835 11,117,34 12,946,848 2,466,646,622 14,256,25 19,343,177 2,45,31,44 11,117,34 12,946,848 2,466,646,622 15,171,739 2,268,649 2,545,54,111 Winter Weekday Winter Weekend 223 NONROAD Emissions Comparision for Fuel RVP Change RVP7.8 Summer Winter Total Weekday Summer Weekend Summer Total Winter Weekday Winter Weekend RVP1 Summer Winter Total Weekday Summer Weekend Summer Total Total tons per day Annual TPY (winter + summer totals) Change in Emissions (+ increase, - decrease) Annual TPY (Annual RVP1 - Annual RVP7.8) Tons per Summer Day (Annual TPY / 153 days) page 12, Table 2 Values 1 Ton = grams SCC Weekday (g/day) 218 NONROAD Daily Emissions Summary by Fuel RVP Type, Season and Day RVP7.8 RVP1 Winter Summer Winter Summer P-BV Area Emissions P-BV Area Emissions P-BV Area Emissions Weekend (g/day) Total Annual (g/yr) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) Weekday (g/day) P-BV Area Emissions Weekend Total Annual (g/day) (g/yr) 735,95 1,463,28 199,656,793 1,346,29 2,67, ,213, ,95 1,463,28 199,656,793 1,357,422 2,683, ,27, , ,961 11,8,628 15,46 15,46 2,365, , ,961 11,8,628 23,284 23,284 3,562, , , ,712,33 837,438 1,637, ,324, , , ,712,33 857,879 1,659, ,526,389 5,85 1,234 1,496,473 11,286 19,346 2,81,374 5,85 1,234 1,496,473 13,366 21,435 2,4,12 56,376 28,298 1,267,83 66,2 33,261 8,657,767 56,376 28,298 1,267,83 66,333 33,59 8,78,262 Page 7

199 Technical Appendix C - NONROAD Documentation SCC Weekday (g/day) Weekend (g/day) Total Annual (g/yr) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) 1, ,719 2,293 1,171 31,514 1, ,719 2,324 1,22 36,233 2,324 1, ,71 2,736 1, ,67 2,324 1, ,71 2,769 1, , , , , , ,26 72,26 26,251, ,394 84,435 22,7,63 144,26 72,26 26,251, ,73 84,764 22,121, , , , , , , , , , , , ,1 8,341 16,57 2,231,34 16,349 31,145 3,152,397 8,341 16,57 2,231,34 17,124 31,963 3,272,97 31,616 19,782 5,992,491 6,662 37,968 8,282,697 31,616 19,782 5,992,491 6,914 38,154 8,318, , ,21 57,73, , ,188 44,37, , ,21 57,73, , ,356 44,476,129 1,38, , ,784,11 1,28,32 643,536 14,42,479 1,38, , ,784,11 1,3, ,844 14,666, ,82 329,767 45,79, ,34 639,354 64,65,35 171,82 329,767 45,79,396 35, ,555 67,39, ,87 232,923 7,532, ,96 447,216 97,513, ,87 232,923 7,532, ,35 449,497 97,934,79 14,335 19,53 27,289,88 28, ,75 39,164,493 14,335 19,53 27,289,88 234,824 4,66 43,222, , ,97 7,514, , ,157 97,485, , ,97 7,514, , ,826 97,962, , , ,247,787 13,53 13,53 2,65, , , ,247,787 2,339 2,339 3,111, , , ,586,638 1,115 1,115 17, , , ,586,638 1,67 1,67 255, , , , , ,542 1, , ,542 1, ,137 36,252 18,278 6,66,959 36,276 18,499 4,768,6 36,252 18,278 6,66,959 36,86 18,986 4,847, , ,299 46,96, , ,322 33,613, , ,299 46,96, , ,132 33,921, , , , ,917 1, ,42 1, ,12 1, ,42 1, ,38 22,17 11,15 4,7,456 21,797 1,917 2,856,219 22,17 11,15 4,7,456 21,838 1,941 2,861,779 33,992 63,72 8,988,847 62,58 114,33 11,843,958 33,992 63,72 8,988,847 67,855 12,212 12,685, ,19 714,951 11,115, ,827 1,298, ,717, ,19 714,951 11,115,926 78,49 1,372, ,455,66 19, ,994 29,728,681 19, ,593 37,259,591 19, ,994 29,728, , ,671 38,13,275 6,849 12,57 1,764,563 13,427 22,47 2,449,428 6,849 12,57 1,764,563 14,49 23,399 2,6,115 2,472 1, ,36 2,766 1, ,581 2,472 1, ,36 2,839 1,55 375, , , , ,651 6,335 3,242 1,157,422 7,186 3,77 949,143 6,335 3,242 1,157,422 7,45 3, ,468 4,348 2, ,989 4,864 2, ,616 4,348 2, ,989 5,12 2, ,147 1,669 5,68 1,962,422 12,571 7,96 1,682,444 1,669 5,68 1,962,422 13,621 8,14 1,842,879 4,53 2, ,128 5,122 2, ,26 4,53 2, ,128 5,318 2,893 76, , , , ,21 7,924 4,61 1,448,84 8,923 4,69 1,178,932 7,924 4,61 1,448,84 9,251 5,12 1,228,823 3,346 1,87 616,981 4,4 2, ,25 3,346 1,87 616,981 4,428 2,735 62,95 17,924 9,15 3,27,732 19,949 1,33 2,627,779 17,924 9,15 3,27,732 2,43 1,772 2,7,867 11,337 6,499 2,113,135 14,615 9,298 2,2,196 11,337 6,499 2,113,135 16,92 11,597 2,354, , , , ,679 1, ,646 1, ,56 1, ,646 1, , , , , , , , , ,642 5,638 2,875 1,29,431 6,299 3,279 83,855 5,638 2,875 1,29,431 6,483 3, ,885 2,734 1,437 51,866 3,164 1, ,493 2,734 1,437 51,866 3,41 1, ,658 1,839 1,53 342,746 2,386 1, ,53 1,839 1,53 342,746 2,722 1, , , , , ,736 5,315 2, ,842 5,32 2,932 76,935 5,315 2, ,842 5,753 3, ,781 Page 8

200 Technical Appendix C - NONROAD Documentation SCC Weekday (g/day) Weekend (g/day) Total Annual (g/yr) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) 2,258 1, ,91 2,134 1,1 28,999 2,258 1, ,91 2,25 1, ,57 1, ,528 1, ,328 1, ,528 1,938 1,42 257,61 8,83 4,94 1,474,356 7,737 3,991 1,18,991 8,83 4,94 1,474,356 8,29 4,221 1,6, , , , , , , , , , , , , ,356 72,633 12,42,76 761,862 1,381, ,814, ,356 72,633 12,42,76 84,217 1,466, ,12, , ,19 37,163, ,889 23,658 5,139, , ,19 37,163, ,42 235,48 51,63,924 34,145 64,238 9,44,412 66,43 122,81 12,644,91 34,145 64,238 9,44,412 71, ,656 13,477, ,782 71,884 21,759, , ,968 29,414, ,782 71,884 21,759, , ,96 29,87,323 2,62 4, ,93 5,68 9,56 97,631 2,62 4, ,93 5,346 9,821 1,14,89 5,24 3, ,598 9,854 6,188 1,346,359 5,24 3, ,598 9,992 6,287 1,365,773 3,32 5, ,923 6,652 11,44 1,211,41 3,32 5, ,923 8,79 12,543 1,432, ,146 77,185 23,349, ,37 143,884 31,332, ,146 77,185 23,349, ,45 147,348 32,38,35 126,639 24,283 33,666,15 31,526 31,526 4,823, ,639 24,283 33,666,15 48,45 48,45 7,412, , ,15 42,91,634 2,636 2,636 43, , ,15 42,91,634 4,8 4,8 613,247 5,635 85,14 12,797,311 12,11 165,486 18,41,363 5,635 85,14 12,797, , ,143 22,189,72 11,811 7,476 2,243,886 21,818 13,857 2,987,845 11,811 7,476 2,243,886 22,688 14,54 3,112,747 15,391 1,18 2,95,271 29,321 19,772 4,65,996 15,391 1,18 2,95,271 31,255 21,493 4,352,457 13,228 8,361 2,512,369 24,911 15,799 3,41,428 13,228 8,361 2,512,369 25,481 16,268 3,493, , ,51 143,157,886 1,83,213 1,878,964 2,744, , ,51 143,157,886 1,267,472 2,81, ,727, ,931 96,927 29,213, ,29 178,773 38,744, ,931 96,927 29,213, , ,75 4,83,414 16,59 1,188 3,52,187 29,54 18,812 4,47,564 16,59 1,188 3,52,187 31,318 2,165 4,3, , ,542 85,414, , , ,173,26 449, ,542 85,414, , , ,423,792 25,644 43,249 6,492,824 51,525 83,823 9,34,437 25,644 43,249 6,492,824 63,325 96,265 11,138,57 23,527 16,936 4,592,292 46,411 34,35 6,57,157 23,527 16,936 4,592,292 55,253 42,938 7,911, , , , , , , , , , , ,83 1, , ,83 1, , , , , ,11 2,19 1, ,421 4,72 2,56 554,149 2,19 1, ,421 4,612 3,44 636,62 7,741 4,266 1,432,649 14,936 8,567 2,4,955 7,741 4,266 1,432,649 15,316 8,942 2,62, ,634 1, , ,634 1,8 1,224 25,87 1, ,282 2,55 1, ,344 1, ,282 2,253 1,364 35, , , , ,48 78, , ,961, ,81 49,52 111,594,353 78, , ,961, ,41 588, ,149,588 2,67 12,599 36,566, ,73 13,978 25,947,1 2,67 12,599 36,566,186 27, ,767 27,625,926 84,218 42,781 15,368,18 81,49 42,77 1,685,692 84,218 42,781 15,368,18 84,598 44,93 11,198,98 194,235 98,184 35,414,79 185,657 95,33 24,431,66 194,235 98,184 35,414,79 191,851 1,35 25,313,27 374, ,626 68,64,28 374,52 24,2 49,747,79 374, ,626 68,64,28 42,81 229,397 53,999,755 13,78 7,42 2,517,124 13,233 6,97 1,749,51 13,78 7,42 2,517,124 13,723 7,453 1,823,722 3,691 1, ,83 3,82 2, ,923 3,691 1, ,83 4,63 2, , , , , ,437 1,618 1, ,934 1,546 1, ,587 1,618 1, ,934 1,68 1,68 245,968 11,793 11,793 2,5,6 13,48 13,48 1,996,274 11,793 11,793 2,5,6 13,231 13,231 2,24,41 45,349 1,74,399 17,717,72 1,388,887 5,594, ,549,321 45,349 1,74,399 17,717,72 1,497,284 5,74, ,29,348 61, ,249 28,451,441 2,523 1,65,963 68,759,351 61, ,249 28,451,441 24,132 1,7, 69,33,439 Page 9

201 Technical Appendix C - NONROAD Documentation SCC Grand Total (g/day) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) Weekday (g/day) Weekend (g/day) Total Annual (g/yr) 75,94 175,718 21,957,35 28, ,8 45,919,73 75,94 175,718 21,957,35 25,25 568,779 52,279,68 1, ,335 1, ,349 1, ,335 1, ,711 11,132,9 14,19,917 2,533,26,322 14,893,16 22,732,99 2,623,596,483 11,132,9 14,19,917 2,533,26,322 15,794,431 23,644,522 2,761,951,985 Winter Weekday Winter Weekend RVP7.8 Summer Winter Total Weekday Summer Weekend Total tons per day NONROAD Emissions Comparision for Fuel RVP Change Summer Total Winter Weekday Winter Weekend RVP1 Summer Winter Total Weekday Summer Weekend Summer Total Annual TPY (winter + summer totals) Change in Emissions (+ increase, - decrease) Annual TPY (Annual RVP1 - Annual RVP7.8) Tons per Summer Day (Annual TPY / 153 days) page 12, Table 2 Values 1 Ton = grams Page 1

202 Technical Appendix C - NONROAD Documentation Year Table C1-218 and 223 Weekday / Weekend Distribution Month # Weekend Days (2) # Weekdays (5) Year Month # Weekend Days (2) # Weekdays (5) Table C2 - Winter / Summer Day Summary Winter Weekend Winter Weekday Summer Weekend Summer Weekday Summer Days Winter Weekend Winter Weekday Summer Weekend Summer Weekday Summer Days Year Category Count Page 11

203 APPENDIX D to ACHD Non-Interference Demonstration is Appendix D to PA DEP NID as follows:

204 APPENDIX D Area Point Documentation Bureau of Air Quality Department of Environmental Protection

205 Technical Appendix D - Area / Point Source Documentation 214 NEIv1 Emissions Inventory for Gasoline Distribution Point Sources Summary of Estimated Point Source Increases Due to RVP Change (Table 3 - pg 14) Note: Only Counties with affected sources are included Gasoline Distribution Point Source Gasoline Terminal Emissions by SCC and County (tpy) Category 214 NEI (tpy) SCC Allegheny Beaver Butler Westmoreland SCC Total (tpy) Point Terminals Point Bulk Plants Tank Trucks in Transit Service Station Unloading Point Emissions for RVP % of 214 Point Emissions for RVP 7 tpy increase.2 tpd County Total (tpy) Gasoline Bulk Plant Emissions by SCC and County (tpy) SCC Allegheny Beaver Butler Westmoreland SCC Total (tpy) County Total (tpy) Tank Trucks in Transit Emissions by SCC and County (tpy) SCC Allegheny Beaver Butler Westmoreland SCC Total (tpy) County Total (tpy) Service Station Unloading Emissions by SCC and County (tpy) SCC Allegheny Beaver Butler Westmoreland SCC Total (tpy) County Total (tpy).6.6 Page 1

206 APPENDIX E to ACHD Non-Interference Demonstration is Appendix E to PA DEP NID as follows:

207 APPENDIX E Adhesives Rule Estimation Bureau of Air Quality Department of Environmental Protection

208 Technical Appendix E - Adhesives Rule Emissions Benefit Estimation Adhesives Rule Emissions Benefit Estimation Supporting Data Step 1: OTC Adhesives Rule Reduction Summary (29) Table A PA Population and Population Projections 29 Area Source BOTW Reductions 29 Point Source BOTW 29 Adhesives Rule BOTW County Reductions Reductions (Area - Point) Allegheny 1,222,171 1,232,896 1,22,281 1,24,432 Annual (tpy) Armstrong 69,12 67,693 66,822 66,492 Summer Day (tpd) Beaver 17, , ,89 166,181 Adhesives rule 29 reductions for the Pittsburgh Beaver-Valley Area were taken from the OTC Adhesives Rule Technical Support Document for each of the seven counties. Point source reduction estimates were subtracted from total area source estimates consistent with the OTC reduction estimate and EPA emissions inventory methodologies. OTC data is summarized on page 2. Step 2: Emissions Factor (EF) Calculation for Post 29 Adhesive Rule BOTW Reductions Butler Fayette Washington Westmoreland Total P-B-V Total PA % of State Source: PA Dept. of Transportation; Woods & Poole , ,386 19, , ,45 134, ,14 132,99 27,571 28,175 29, ,72 365, , , ,34 2,355,432 2,358,96 2,346,571 2,338,2 12,666,858 12,793,767 12,936,93 13,179, % 18.43% 18.14% 17.74% OTC Adhesives Rule Reductions (29) 29 PBV Population Tons per Year Tons per Day notes 1, From Step 1 2,355,432 From Table A Tons reduction per capita (Tons/person) 4.96E E-6 Tons reduced divided by 29 area population Step 3: Multiply EF by Population to Estimate Annual / Daily Reduction Population Projections Reduction Estimates (Offsets) P-BV Area Population Year ,358,96 2,346,571 2,338,2 Tons per Year Tons per Day Page 1

209 Technical Appendix E - Adhesives Rule Emissions Benefit Estimation Summary of OTC Adhesive Rule 29 Reduction Benefits SOURCE: Identification and Evaluation of Candidate Control Measures: Final Technical Support Document; Ozone Transport Commission (OTC), February 28, 27 AREA SOURCE EMISSIONS ESTIMATES: SCC 2442 Adhesives and Sealants State County FIPS SCC 29 OTB/OTW Emissions 29 BOTW Emissions 29 BOTW Reductions Annual Summer Day from Inventory Summer Day Calculated 29 BOTW Incremental Control Annual Summer Day Calculated Annual Summer Day (tpy) (tpd) (tpd) Factor (tpy) (tpd) (tpy) (tpd) PA Allegheny ,8.1 Missing PA Armstrong Missing PA Beaver Missing PA Butler Missing PA Fayette Missing PA Washington Missing PA Westmoreland Missing Total: 1, OTB/OTW = "On The Books" / "On The Way" = Existing or Planned Federal Rule BOTW = "Beyond On The Way" = OTC Model Rule Emissions Reductions POINT SOURCE EMISSIONS ESTIMATES : SCC 4271 Adhesives and Sealants State County FIPS Site ID EU ID Proc ID SCC 29 OTB/OTW Emissions Summer Summer Day Annual Day from Calculated Inventory 29 BOTW Incremental 29 BOTW Emissions 29 BOTW Reductions Annual Summer Day Calculated Annual Summer Day Control Factor (tpy) (tpd) (tpd) (tpy) (tpd) (tpy) (tpd) PA Butler Missing PA Butler Missing PA Butler Missing PA Butler Missing PA Butler Missing PA Butler Missing PA Butler Missing PA Butler Missing PA Westmoreland Missing PA Westmoreland Missing Total: Plant Name CASTLE RUBBER LLC/EAST BUTLER BORO CASTLE RUBBER LLC/EAST BUTLER BORO CUE INC/CRANBERRY TWP PLT CUE INC/CRANBERRY TWP PLT CUE INC/CRANBERRY TWP PLT CUE INC/CRANBERRY TWP PLT CUE INC/CRANBERRY TWP PLT CUE INC/CRANBERRY TWP PLT CHESTNUT RIDGE FOAM /LATROBE PLT ADVANCE USA INC/NEW STANTON PLT Page 2

210 Technical Appendix E - Adhesives Rule Emissions Benefit Estimation OTC Adhesive Rule 29 Benefit Calculation Spreadsheet (Area Sources Filtered by PA County) COLUMN A,B,C D E F G H I J COLUMN DESCRIPTIONS State abbreviation, County Name, FIPS state/county code SCC-Source Classification Code 22 Annual Emissions (tons/year) as reported in MANEVU Version 3 and VISTAS BaseG Inventories 22 Summer Day (tons/day) from MANEVU Version 3 and VISTAS BaseG (Note: Missing indicates that summer day emissions are not reported in MANEVU/VISTAS) 22 Summer Day Emissions (tons/day) calculated using the following hierarchy: 1. If summer day emissions in inventory, use summer day emissions as reported in inventory (Column F) 2. If summer day emission not in inventory: a) if summer PCT in NIF EP file not=blank, multiply annual by NIF EP summer PCT/91 days b) if summer PCT in NIF EP file = blank, multiply annual by SMOKE summer PCT/91 days Summer season percentage from NIF Emission Process (EP) file Summer season percentage from SMOKE ((June_PCT+July_PCT+Aug_PCT)/Total_PCT) Blank SCC: xxx Indicates County in Pittsburgh - Beaver Valley Area COLUMN K L M N O P Q, R S, T COLUMN DESCRIPTIONS 29 Annual Emissions (tons/year) as reported in MANEVU Version 3 and VISTAS BaseG Inventories 29 Summer Day (tons/day) from MANEVU Version 3 and VISTAS BaseG (Note: Missing indicates that summer day emissions are not reported in MANEVU/VISTAS) 22 Summer Day Emissions (tons/day) calculated using the following hierarchy: 1. If summer day emissions in inventory, use summer day emissions as reported in inventory (Column F) 2. If summer day emission not in inventory: a) if summer PCT in NIF EP file not=blank, multiply annual by NIF EP summer PCT/91 days b) if summer PCT in NIF EP file = blank, multiply annual by SMOKE summer PCT/91 days Growth Factor 22 to 29 (used in MANEVU/VISTAS Emission Projections) Incremental Control Factor for 29 (used in MANEVU/VISTAS Emission Projections) Incremental Control Factor (percent reduction due to OTC 26 Control Measure) 29 BOTW Emissions (29 OTB/OTW x (1-29 BOTW control factor/1) 29 Emission Reduction (29 OTB/OTW Emissions - 29 BOTW Emissions) Adhesives and Sealants (Area) 22 Emissions 29 OTB/OTW Emissions 29 BOTW Emissions 29 BOTW Reductions Annual Summer Day from Inventory Summer Day Calculated Summer Season Percent Summer Season Percent Annual Summer Day from Inventory Summer Day Calculated Growth Factor 29 OTB/OTW Incremental Control Factor 29 BOTW Incremental Control Factor State County FIPS SCC (tpy) (tpd) (tpd) NIF EP SMOKE (tpy) (tpd) (tpd) 2 to 9 TOTAL_EFF (tpy) (tpd) (tpy) (tpd) PA Adams Missing Missing PA Allegheny Missing ,8.14 Missing PA Armstrong Missing Missing PA Beaver Missing Missing PA Bedford Missing Missing PA Berks Missing Missing PA Blair Missing Missing PA Bradford Missing Missing PA Butler Missing Missing PA Cambria Missing Missing PA Cameron Missing Missing PA Carbon Missing Missing PA Centre Missing Missing PA Chester Missing Missing PA Clarion Missing Missing PA Clearfield Missing Missing PA Clinton Missing Missing PA Columbia Missing Missing PA Crawford Missing Missing PA Cumberland Missing Missing PA Dauphin Missing Missing PA Delaware Missing Missing PA Elk Missing Missing PA Erie Missing Missing PA Fayette Missing Missing PA Forest Missing Missing PA Franklin Missing Missing PA Fulton Missing Missing PA Greene Missing Missing PA Huntingdon Missing Missing PA Indiana Missing Missing PA Jefferson Missing Missing PA Juniata Missing Missing PA Lackawanna Missing Missing PA Lancaster Missing Missing PA Lawrence Missing Missing PA Lebanon Missing Missing PA Lehigh Missing Missing PA Luzerne Missing Missing PA Lycoming Missing Missing PA McKean Missing Missing PA Mercer Missing Missing PA Mifflin Missing Missing PA Monroe Missing Missing PA Montgomery Missing ,9.12 Missing PA Montour Missing Missing PA Northampton Missing Missing Annual Summer Day Calculated Annual Summer Day Page 3

211 Technical Appendix E - Adhesives Rule Emissions Benefit Estimation Adhesives and Sealants (Area) 22 Emissions 29 OTB/OTW Emissions 29 BOTW Emissions 29 BOTW Reductions Annual Summer Day from Inventory Summer Day Calculated Summer Season Percent Summer Season Percent Annual Summer Day from Inventory Summer Day Calculated Growth Factor 29 OTB/OTW Incremental Control Factor 29 BOTW Incremental Control Factor State County FIPS SCC (tpy) (tpd) (tpd) NIF EP SMOKE (tpy) (tpd) (tpd) 2 to 9 TOTAL_EFF (tpy) (tpd) (tpy) (tpd) PA Northumberland Missing Missing PA Perry Missing Missing PA Philadelphia Missing ,3.78 Missing PA Pike Missing Missing PA Potter Missing Missing PA Schuylkill Missing Missing PA Snyder Missing Missing PA Somerset Missing Missing PA Sullivan Missing Missing PA Susquehanna Missing Missing PA Tioga Missing Missing PA Union Missing Missing PA Venango Missing Missing PA Warren Missing Missing PA Washington Missing Missing PA Wayne Missing Missing PA Westmoreland Missing Missing PA Wyoming Missing Missing PA York Missing Missing Annual Summer Day Calculated Annual Summer Day PA Total 8, , , , P-BV Area Total 1, , Page 4

212 Technical Appendix E - Adhesives Rule Emissions Benefit Estimation COLUMN A-F G H I J COLUMN DESCRIPTIONS State abbreviation, County Name, FIPS state/county code, Site ID, Emission Unit ID, Process ID SCC-Source Classification Code 22 Annual Emissions (tons/year) as reported in MANEVU Version 3 and VISTAS BaseG Inventories 22 Summer Day (tons/day) from MANEVU Version 3 and VISTAS BaseG (Note: Missing indicates that summer day emissions are not reported in MANEVU/VISTAS) 22 Summer Day Emissions (tons/day) calculated using the following hierarchy: 1. If summer day emissions in inventory, use summer day emissions as reported in inventory (Column F) 2. If summer day emission not in inventory: a) if summer PCT in NIF EP file not=blank, multiply annual by NIF EP summer PCT/91 days b) if summer PCT in NIF EP file = blank, multiply annual by SMOKE summer PCT/91 days OTC Adhesive Rule 29 Benefit Calculation Spreadsheet (Point Sources Filtered by PA County) COLUMN COLUMN DESCRIPTIONS O 29 Annual Emissions (tons/year) as reported in MANEVU Version 3 and VISTAS BaseG Inventories P 29 Summer Day (tons/day) from MANEVU Version 3 and VISTAS BaseG Q 22 Summer Day Emissions (tons/day) calculated using the following hierarchy: R Growth Factor 22 to 29 (used in MANEVU/VISTAS Emission Projections) S Total capture/control efficiency from NIF 29 CE file K L M N Summer season percentage from NIF Emission Process (EP) file Summer season percentage from SMOKE ((June_PCT+July_PCT+Aug_PCT)/Total_PCT) Total capture/control efficiency from NIF 22 CE file Blank O P Q, R S, T Incremental Control Factor for 29 (used in MANEVU/VISTAS Emission Projections) Incremental Control Factor (64.4% if uncontrolled, % if greater than 85% control system requirment) 29 BOTW Emissions (29 OTB/OTW x (1-29 BOTW incremental control factor/1) 29 Emission Reduction (29 OTB/OTW Emissions - 29 BOTW Emissions) Indicates County in Pittsburgh - Beaver Valley Area Adhesives and Sealants (Point) 22 Emissions 29 OTB/OTW Emissions 29 BOTW Emissions 29 BOTW Reductions 29 Summer Summer Summer Summer 29 BOTW Summer Day 22 Summer Day Growth OTB/OTW Summer Day Annual Day from Season Season Annual Day from Incremental Annual Annual Summer Day Calculated Control Calculated Factor Control Calculated Inventory Percent Percent Inventory Control Factor Factor State County FIPS Site ID EU ID Proc ID SCC (tpy) (tpd) (tpd) NIF EP SMOKE Efficiency (tpy) (tpd) (tpd) 2 to 9 TOTAL_EFF (tpy) (tpd) (tpy) (tpd) Plant Name PA Adams Missing Missing SCHINDLER ELEVATOR CORP/GETTYSBURG PA Berks Missing Missing PACKAGING GROUP/BOYERTOWN PRINTING PLT PA Berks Missing Missing PACKAGING GROUP/BOYERTOWN PRINTING PLT PA Blair Missing Missing HH BROWN SHOE CO/COVE SHOE MARTINSBURG PA Bucks Missing Missing ROGERS FOAM CORP/MORRISVILLE PA Butler Missing Missing CASTLE RUBBER LLC/EAST BUTLER BORO PA Butler Missing Missing CASTLE RUBBER LLC/EAST BUTLER BORO PA Butler Missing Missing CUE INC/CRANBERRY TWP PLT PA Butler Missing Missing CUE INC/CRANBERRY TWP PLT PA Butler Missing Missing CUE INC/CRANBERRY TWP PLT PA Butler Missing Missing CUE INC/CRANBERRY TWP PLT PA Butler Missing Missing CUE INC/CRANBERRY TWP PLT PA Butler Missing Missing CUE INC/CRANBERRY TWP PLT PA Clinton P Missing Missing XL ACQUISITION CORP/AVIS AMER HENRY ST PLT PA Clinton P Missing Missing XL ACQUISITION CORP/AVIS AMER HENRY ST PLT PA Crawford Missing Missing LORD CORP/SAEGERTOWN PA Crawford Missing Missing LORD CORP/MECH PROD DIV PA Crawford Missing Missing LORD CORP/MECH PROD DIV PA Crawford Missing Missing LORD CORP/MECH PROD DIV PA Crawford Missing Missing LORD CORP/MECH PROD DIV PA Delaware Missing Missing JEFFERSON SMURFIT CO/ASTON CONTAINER DIV PA Franklin Missing Missing ARMACLAD INC/QUINCY PLT PA Franklin Missing Missing ARMACLAD INC/QUINCY PLT PA Huntingdon Missing.15 Missing Missing AGY HUNTINGDON LLC/HUNTINGDON PA Huntingdon Missing 1 Missing Missing AGY HUNTINGDON LLC/HUNTINGDON PA Huntingdon Missing 8 Missing Missing OWENS CORNING/HUNTINGDON MAT PLANT PA Huntingdon Missing 3 Missing Missing OWENS CORNING/HUNTINGDON MAT PLANT PA Huntingdon Missing 8 Missing Missing OWENS CORNING/HUNTINGDON MAT PLANT PA Huntingdon Missing 7 Missing Missing OWENS CORNING/HUNTINGDON MAT PLANT PA Huntingdon Missing 2 Missing Missing OWENS CORNING/HUNTINGDON MAT PLANT PA Huntingdon Missing 7 Missing Missing OWENS CORNING/HUNTINGDON MAT PLANT PA Huntingdon Missing.2 Missing Missing OWENS CORNING/HUNTINGDON MAT PLANT PA Huntingdon Missing 8 Missing Missing OWENS CORNING/HUNTINGDON MAT PLANT PA Lackawanna Missing 2 Missing Missing MACTAC INC/SCRANTON FAC PA Lackawanna Missing Missing MACTAC INC/SCRANTON FAC PA Lancaster Missing Missing HOMETTE CORP/SKYLINE HOMES EPHRATA PA Lancaster Missing Missing HOMETTE CORP/SKYLINE HOMES LEOLA PA Lehigh Missing Missing ALLEN ORGAN CO/MACUNGIE PA Lehigh Missing Missing ALLEN ORGAN CO/MACUNGIE PA Lehigh Missing Missing ALLEN ORGAN CO/MACUNGIE PA Lehigh Missing Missing ALLEN ORGAN CO/MACUNGIE PA Lehigh Missing Missing ALLEN ORGAN CO/MACUNGIE PA Lehigh Missing Missing ALLEN ORGAN CO/MACUNGIE PA Lehigh Missing Missing ALLEN ORGAN CO/MACUNGIE PA Lycoming Missing Missing SPECIALIZED VEHICLES CORP/MONTGOMERY PLT PA Lycoming P Missing Missing JOHN SAVOY & SON INC/MONTOURSVILLE PLT PA Montgomery Missing Missing LOCKHEED MARTIN CORP/MISSILES & SPACE OPR PA Montgomery Missing Missing ATOFINA CHEM INC/KING OF PRUSSIA PA Montgomery Missing Missing ATOFINA CHEM INC/KING OF PRUSSIA PA Northumberland Missing Missing RESILITE SPORTS PROD/NORTHUMBERLAND PLT PA Northumberland Missing Missing RESILITE SPORTS PROD/NORTHUMBERLAND PLT PA Northumberland Missing Missing RESILITE SPORTS PROD/NORTHUMBERLAND PLT PA Northumberland Missing Missing FLEETWOOD MOTOR HOMES/MAIN PLT PA Northumberland A Missing Missing FLEETWOOD MOTOR HOMES/MAIN PLT PA Philadelphia Missing PERFECSEAL PA Philadelphia Missing SMURFIT-STONE CONTAINER CORPORATION PA Philadelphia Missing SMURFIT-STONE CONTAINER CORPORATION PA Philadelphia Missing SMURFIT-STONE CONTAINER CORPORATION PA Philadelphia Missing SMURFIT-STONE CONTAINER CORPORATION PA Philadelphia Missing SMURFIT-STONE CONTAINER CORPORATION PA Philadelphia Missing SMURFIT-STONE CONTAINER CORPORATION PA Philadelphia Missing SMURFIT-STONE CONTAINER CORPORATION PA Philadelphia Missing GEII INSPECTION & REPAIR SERVICES PA Snyder Missing Missing WOOD MODE INC/KREAMER PLT PA Snyder Missing Missing WOOD MODE INC/KREAMER PLT PA Union P Missing Missing RITZ CRAFT CORP/MIFFLINBURG PLT PA Westmoreland Missing Missing CHESTNUT RIDGE FOAM /LATROBE PLT PA Westmoreland Missing Missing ADVANCE USA INC/NEW STANTON PLT Page 5

213 Technical Appendix E - Adhesives Rule Emissions Benefit Estimation Adhesives and Sealants (Point) 22 Emissions 29 OTB/OTW Emissions 29 BOTW Emissions 29 BOTW Reductions 29 Summer Summer Summer Summer 29 BOTW Summer Day 22 Summer Day Growth OTB/OTW Summer Day Annual Day from Season Season Annual Day from Incremental Annual Annual Summer Day Calculated Control Calculated Factor Control Calculated Inventory Percent Percent Inventory Control Factor Factor State County FIPS Site ID EU ID Proc ID SCC (tpy) (tpd) (tpd) NIF EP SMOKE Efficiency (tpy) (tpd) (tpd) 2 to 9 TOTAL_EFF (tpy) (tpd) (tpy) (tpd) Plant Name PA York Missing Missing ADHESIVES RESEARCH INC/GLEN ROCK PA York Missing Missing ADHESIVES RESEARCH INC/GLEN ROCK PA York Missing Missing ADHESIVES RESEARCH INC/GLEN ROCK PA York Missing Missing ADHESIVES RESEARCH INC/GLEN ROCK PA York Missing Missing ADHESIVES RESEARCH INC/GLEN ROCK PA York Missing Missing ADHESIVES RESEARCH INC/GLEN ROCK PA York Missing Missing ADHESIVES RESEARCH INC/GLEN ROCK PA York Missing Missing ADHESIVES RESEARCH INC/GLEN ROCK PA York Missing Missing ADHESIVES RESEARCH INC/GLEN ROCK PA York Missing Missing ADHESIVES RESEARCH INC/GLEN ROCK PA York Missing Missing ADHESIVES RESEARCH INC/GLEN ROCK PA York Missing Missing ADHESIVES RESEARCH INC/GLEN ROCK PA York Missing Missing ADHESIVES RESEARCH INC/GLEN ROCK PA York Missing Missing ADHESIVES RESEARCH INC/GLEN ROCK PA York Missing Missing ADHESIVES RESEARCH INC/GLEN ROCK PA York Missing Missing ADHESIVES RESEARCH INC/GLEN ROCK PA York Missing Missing ADHESIVES RESEARCH INC/GLEN ROCK PA York Missing Missing ADHESIVES RESEARCH INC/GLEN ROCK PA York Missing Missing UNITED DEFENSE LTD P/YORK PA York Missing Missing TATE ACCESS FLOORS/RED LION PA York Missing Missing TATE ACCESS FLOORS/RED LION PA Total P-BV Area Total Page 6

214 APPENDIX F to ACHD Non-Interference Demonstration is Appendix F to PA DEP NID as follows:

215 APPENDIX F Shutdown Estimation Bureau of Air Quality Department of Environmental Protection

216 Guardian Industries Facility Shutdown Creditable Reduction Calculations Creditable reductions calculated from last 24 months of continuous facility operation. Annual reported emissions of, NOx and PM2.5 were apportioned to reported monthly facility raw material inputs (Source Id 11). Apportioned monthly emissions summed from 8/1/213 through 7/31/215 and divided by 2 for annual creditable reduction. Summer day reduction calculated by same method for months May through September. Annual Emissions as Reported to DEP. See attached Annual and Daily Creditable Reduction Calculations Firm/Plant Reports for 213, 214 and 215 NOx PM2.5 NOx PM2.5 Annual Reported Emissions (tons per year) month total Annual emissions (tons) Reduction Average Annual (24 mo. emissions / 2) (tons) Summer Day Reduction 24 Month May - Sept Emissions (tons) Daily summer emisions (1 summer mo. / 32 Day)(tons per day) NOx PM n/a n/a Reported Monthly Raw Material Throughputs (Source Id 11) and Monthly Apportioned Emissions Key: Selected month for 24 month averaging period Selected summer months in Bold Month Throughput Apportioned Emissions (tons) Apportioned Emissions (tons) Month Throughput NOx PM2.5 NOx PM2.5 1/1/213 7, /1/214 6, /1/213 6, /1/214 6, /1/213 6, /1/214 8, /1/213 6, /1/214 7, /1/213 7, /1/214 7, /1/213 7, /1/214 7, /1/213 7, /1/214 5, /1/213 6, /1/214 8, /1/213 6, /1/215 7, /1/213 6, /1/215 6, /1/213 5, /1/215 7, /1/213 6, /1/215 6, /1/214 7, /1/215 6, /1/214 6, /1/215 6, /1/214 6, /1/215 7, /1/214 8, /1/ Table 6 - Summary of Creditable Emissions Reductions from the Shutdown of Guardian Industries Guardian Industries Annual Emissions (tpd) 215 (end /31) Pollutant NOx PM Permanent Offsets for 24 Month Annual Average (8/1/13-7/31/15) Pollutant tpy tpd NOx PM n/a

217 Wednesday, November Pennsylvania Department of Environmental Protection Page 1 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Region: 7 SIC Code: Site Totals (Best Controlled) Criteria/Non-Criteria(Totals) District: 71 County: 2 Allegheny Municipality: 2826 Jefferson Hills Boro AFS-Id Number: CDS-Id Number: Date Totals Last Completed: 4/28/216 Contact Type Location Address Firm Plant Contact Responsible Official Contact Site Location Information 3211 Manufacturing - Flat Glass Street Address 1 Glass House Rd 1 Glass House Rd 1 Glass House Rd City State Zip Contact Name Phone Number Jefferson Hills Jefferson Hills Jefferson Hills NAICS Code: PA PA PA Flat Glass Manufacturing Gregg Eckstein John Buckner Map: Latitude: 4 deg, 15 min, 2 sec N UTM : Zone: 17 North: Elevation(Ft): Longitude: -79 deg, 54 min, 57. sec W East: CO: LEAD: : PM1: PM25: SOX: : Criteria/Hazardous: Non-Criteria: Total Stacks: 6 Site Comment Processes 22 Combustion Units 5 Incinerators Control Devices 1 NESHAPS: NSPS: PSD: Fuel Material Location Data

218 Wednesday, November Pennsylvania Department of Environmental Protection Page 2 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,74 1/1/215 1/31/215 7,59. Tons 2/1/215 2/28/215 6,118. Tons 3/1/215 3/31/215 7,14. Tons 4/1/215 4/3/215 6,714. Tons 5/1/215 5/31/215 6,979. Tons 6/1/215 6/3/215 6,818. Tons 7/1/215 7/31/215 7,43. Tons 8/1/215 8/31/ Tons 9/1/215 9/3/215. Tons 1/1/215 1/31/215. Tons 11/1/215 11/3/215. Tons 12/1/215 12/31/215. Tons 213 1,74 Total Throughput: 47,969. Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 11 RAW MATERIAL RECEIVING / HANDLING Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; RAW MATERIAL HANDLING (ALL TYPES OF GLASS) Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/215

219 Wednesday, November Pennsylvania Department of Environmental Protection Page 3 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 11 RAW MATERIAL RECEIVING / HANDLING Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant DEP EFFICIENCY OF CONTROL DEVICE

220 Wednesday, November Pennsylvania Department of Environmental Protection Page 4 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,112 1/1/215 1/31/ Tons 2/1/215 2/28/ Tons 3/1/215 3/31/ Tons 4/1/215 4/3/ Tons 5/1/215 5/31/ Tons 6/1/215 6/3/ Tons 7/1/215 7/31/ Tons 8/1/215 8/31/ Tons 9/1/215 9/3/215. Tons 1/1/215 1/31/215. Tons 11/1/215 11/3/215. Tons 12/1/215 12/1/215. Tons 213 5,112 Total Throughput: 23.4 Tons Average Thru/Hr.5 Exhaust Details ACFM: Stack Data Stack Id Name 12 RAW MATERIAL RECEIVING / HANDLING (HYDRATED LIME) Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; RAW MATERIAL HANDLING (ALL TYPES OF GLASS) Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/215

221 Wednesday, November Pennsylvania Department of Environmental Protection Page 5 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 12 RAW MATERIAL RECEIVING / HANDLING (HYDRATED LIME) Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

222 Wednesday, November Pennsylvania Department of Environmental Protection Page 6 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,112 1/1/215 1/31/ Tons 2/1/215 2/28/ Tons 3/1/215 3/31/ Tons 4/1/215 4/3/ Tons 5/1/215 5/31/ Tons 6/1/215 6/3/ Tons 7/1/215 7/31/ Tons 8/1/215 8/31/ Tons 9/1/215 9/3/215. Tons 1/1/215 1/31/215. Tons 11/1/215 11/3/215. Tons 12/1/215 12/1/215. Tons 213 5,112 Total Throughput: Tons Average Thru/Hr.3 Exhaust Details ACFM: Stack Data Stack Id Name 13 RAW MATERIAL RECEIVING / HANDLING (RECIRC LIME) Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; RAW MATERIAL HANDLING (ALL TYPES OF GLASS) Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/215

223 Wednesday, November Pennsylvania Department of Environmental Protection Page 7 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 13 RAW MATERIAL RECEIVING / HANDLING (RECIRC LIME) Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

224 Wednesday, November Pennsylvania Department of Environmental Protection Page 8 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/215 1/31/215. Tons 2/1/215 2/28/215. Tons 3/1/215 3/31/215. Tons 4/1/215 4/3/215. Tons 5/1/215 5/31/215. Tons 6/1/215 6/3/215. Tons 7/1/215 7/31/215. Tons 8/1/215 8/31/215. Tons 9/1/215 9/3/215. Tons 1/1/215 1/31/215. Tons 11/1/215 11/3/215. Tons 12/1/215 12/31/215. Tons 1 Total Throughput:. Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 14 GLASS MELT FURNACE / NON-METAL GLASS DI/ESP Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; FLAT GLASS: MELTING FURNACE Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S2 EP STACK (PRIMARY) , /1/215

225 Wednesday, November Pennsylvania Department of Environmental Protection Page 9 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 14 GLASS MELT FURNACE / NON-METAL GLASS DI/ESP Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Cobalt Compounds Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP

226 Wednesday, November Pennsylvania Department of Environmental Protection Page 1 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/215 1/31/215. Tons 2/1/215 2/28/215. Tons 3/1/215 3/31/215. Tons 4/1/215 4/3/215. Tons 5/1/215 5/31/215. Tons 6/1/215 6/3/215. Tons 7/1/215 7/31/215. Tons 8/1/215 8/31/215. Tons 9/1/215 9/3/215. Tons 1/1/215 1/31/215. Tons 11/1/215 11/3/215. Tons 12/1/215 12/31/215. Tons 1 Total Throughput:. Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 15 GLASS MELT FURNACE / NON-METAL NO DI/ESP Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; FLAT GLASS: MELTING FURNACE Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S1 FURNACE EJECTOR STACK , /1/215

227 Wednesday, November Pennsylvania Department of Environmental Protection Page 11 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 15 GLASS MELT FURNACE / NON-METAL NO DI/ESP Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Cobalt Compounds Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP

228 Wednesday, November Pennsylvania Department of Environmental Protection Page 12 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput /1/215 1/31/ Tons 2/1/215 2/28/215 1 Tons 3/1/215 3/31/ Tons 4/1/215 4/3/ Tons 5/1/215 5/31/ Tons 6/1/215 6/3/ Tons 7/1/215 7/31/ Tons 8/1/215 8/31/215. Tons 9/1/215 9/3/215. Tons 1/1/215 1/31/215. Tons 11/1/215 11/3/215. Tons 12/1/215 12/31/215. Tons 7 7 Total Throughput: 8 Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 16 GLASS MELT FURNACE / METAL GLASS NO DI/ESP Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; FLAT GLASS: MELTING FURNACE Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S1 FURNACE EJECTOR STACK , /1/215

229 Wednesday, November Pennsylvania Department of Environmental Protection Page 13 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 16 GLASS MELT FURNACE / METAL GLASS NO DI/ESP Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 SOX Denotes Best Value for Pollutant B RATED FACTOR B RATED FACTOR B RATED FACTOR B RATED FACTOR B RATED FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR

230 Wednesday, November Pennsylvania Department of Environmental Protection Page 14 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 16 GLASS MELT FURNACE / METAL GLASS Criteria: NON CRITERIA SOURCE NO DI/ESP Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Cadmium Chromium Lead Selenium Nitrous Oxide PM-CON Cobalt Compounds Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP

231 Wednesday, November Pennsylvania Department of Environmental Protection Page 15 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/215 1/31/215. Tons 2/1/215 2/28/215. Tons 3/1/215 3/31/215. Tons 4/1/215 4/3/215. Tons 5/1/215 5/31/215. Tons 6/1/215 6/3/215. Tons 7/1/215 7/31/215. Tons 8/1/215 8/31/215. Tons 9/1/215 9/3/215. Tons 1/1/215 1/31/215. Tons 11/1/215 11/3/215. Tons 12/1/215 12/31/215. Tons 1 Total Throughput:. Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 17 GLASS MELT FURNACE / NON-METAL (ESP ONLY OPR) Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; FLAT GLASS: MELTING FURNACE Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S2 EP STACK (PRIMARY) , /1/215

232 Wednesday, November Pennsylvania Department of Environmental Protection Page 16 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 17 GLASS MELT FURNACE / NON-METAL (ESP ONLY OPR) Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP

233 Wednesday, November Pennsylvania Department of Environmental Protection Page 17 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/215 1/31/215. Tons 2/1/215 2/28/215. Tons 3/1/215 3/31/215. Tons 4/1/215 4/3/215. Tons 5/1/215 5/31/215. Tons 6/1/215 6/3/215. Tons 7/1/215 7/31/215. Tons 8/1/215 8/31/215. Tons 9/1/215 9/3/215. Tons 1/1/215 1/31/215. Tons 11/1/215 11/3/215. Tons 12/1/215 12/31/215. Tons 1 Total Throughput:. Tons Average Thru/Hr Exhaust Details ACFM: Control Equipment Details 18 GLASS MELT FURNACE / METAL GLASS (ESP ONLY OPR Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr Category: SCC-Number Criteria: Material NON CRITERIA SOURCE INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; FLAT GLASS: MELTING FURNACE SCFM: % Moist: Temp-F: ID CD-1 Name Date Installed Type Code Pressure Drop METAL GLASS DI/ESP 41 Discharges To S2

234 Wednesday, November Pennsylvania Department of Environmental Protection Page 18 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 18 GLASS MELT FURNACE / METAL GLASS (ESP ONLY OPR Control Equipment Details Criteria: NON CRITERIA SOURCE ID Name Pollutant Control Pollutant PM1 Particulate Matter < 1 Microns PM25 Particulate Matter < 2.5 Microns Date Installed EFF(%) Type Code EFF Code A A Pressure Drop Discharges To EFF Description Rated efficiency: guaranteed minimum Rated efficiency: guaranteed minimum Stack Data Stack Id Name Source Totals (Best Controlled) Emission Data for SCC Factors SCC: Height Diameter Elevation Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S2 EP STACK (PRIMARY) , /1/215 CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds

235 Wednesday, November Pennsylvania Department of Environmental Protection Page 19 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 18 GLASS MELT FURNACE / METAL GLASS Criteria: NON CRITERIA SOURCE (ESP ONLY OPR Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Cadmium Chromium Lead Selenium Nitrous Oxide PM-CON Cobalt Compounds Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP

236 Wednesday, November Pennsylvania Department of Environmental Protection Page 2 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,112 1/1/215 1/31/215 2,998. Tons 2/1/215 2/28/215 2,754. Tons 3/1/215 3/31/215 3,68. Tons 4/1/215 4/3/215 2,925. Tons 5/1/215 5/31/215 3,16. Tons 6/1/215 6/3/215 2,877. Tons 7/1/215 7/31/215 3,155. Tons 8/1/215 8/31/ Tons 9/1/215 9/3/215. Tons 1/1/215 1/31/215. Tons 11/1/215 11/3/215. Tons 12/1/215 12/1/215. Tons 213 5,112 Total Throughput: 2,896. Tons Average Thru/Hr 4.9 Exhaust Details ACFM: Stack Data Stack Id Name 19 CULLET PROCESSING / CULLET CRUSHING Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; CULLET: CRUSHING/GRINDING Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/215

237 Wednesday, November Pennsylvania Department of Environmental Protection Page 21 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 19 CULLET PROCESSING / CULLET CRUSHING Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant AP-42 LATEST AVAILABLE AP-42 LATEST AVAILABLE

238 Wednesday, November Pennsylvania Department of Environmental Protection Page 22 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,112 1/1/215 1/31/215 3,732. Tons 2/1/215 2/28/215 3,428. Tons 3/1/215 3/31/215 3,841. Tons 4/1/215 4/3/215 3,64 Tons 5/1/215 5/31/215 3,755. Tons 6/1/215 6/3/215 3,582. Tons 7/1/215 7/31/215 3,927. Tons 8/1/215 8/31/ Tons 9/1/215 9/3/215. Tons 1/1/215 1/31/215. Tons 11/1/215 11/3/215. Tons 12/1/215 12/31/215. Tons 213 5,112 Total Throughput: 26,33. Tons Average Thru/Hr 5.9 Exhaust Details ACFM: Stack Data Stack Id Name 11 CULLET PROCESSING / CULLET HANDLING Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; RAW MATERIAL HANDLING (ALL TYPES OF GLASS) Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/215

239 Wednesday, November Pennsylvania Department of Environmental Protection Page 23 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 11 CULLET PROCESSING / CULLET HANDLING Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP

240 Wednesday, November Pennsylvania Department of Environmental Protection Page 24 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Exhaust Details ACFM: Stack Data Stack Id Name Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,112 1/1/215 1/31/215 3,732. 2/1/215 2/28/215 3,428. 3/1/215 3/31/215 3,841. 4/1/215 4/3/215 3,64 5/1/215 5/31/215 3,755. 6/1/215 6/3/215 3,582. 7/1/215 7/31/215 3,927. 8/1/215 8/31/ /1/215 9/3/215. 1/1/215 1/31/ /1/215 11/3/ /1/215 12/1/ ,112 Total Throughput: 26,33. Average Thru/Hr CULLET PROCESSING / CULLET PADS Criteria: Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; CULLET: CRUSHING/GRINDING Diameter Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/215 Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons

241 Wednesday, November Pennsylvania Department of Environmental Protection Page 25 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 111 CULLET PROCESSING / CULLET PADS Criteria: Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant AP-42 LATEST AVAILABLE AP-42 LATEST AVAILABLE

242 Wednesday, November Pennsylvania Department of Environmental Protection Page 26 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type PETROL./SOLVENT EVAPOR. ; PETRO-PROD. STORAGE (REFINERY) Exhaust Details ACFM: Stack Data Stack Id Name Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/215 1/31/215. 2/1/215 2/28/215. 3/1/215 3/31/215. 4/1/215 4/3/215. 5/1/215 5/31/215. 6/1/215 6/3/215. 7/1/215 7/31/215. 8/1/215 8/31/215. 9/1/215 9/3/215. 1/1/215 1/31/ /1/215 11/3/ /1/215 12/31/ Total Throughput:. Average Thru/Hr 112 STORAGE TANKS / STORAGE TANKS Criteria: Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number PETROL./SOLVENT EVAPOR. ; PETRO-PROD. STORAGE (REFINERY) ; VARIABLE VAPOR SPACE ; SPECIFY LIQUID: FILLING LOSS Diameter Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/215 Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal

243 Wednesday, November Pennsylvania Department of Environmental Protection Page 27 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 112 STORAGE TANKS / STORAGE TANKS Criteria: Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

244 Wednesday, November Pennsylvania Department of Environmental Protection Page 28 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Industrial Processes; Electrical Equipment; Light Bulb Manuf Exhaust Details ACFM: Stack Data Stack Id Name Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,112 1/1/215 1/31/215 1, 2/1/215 2/28/215 1,25 3/1/215 3/31/215 1, 4/1/215 4/3/215 1,25 5/1/215 5/31/215. 6/1/215 6/3/215 1,25 7/1/215 7/31/ /1/215 8/31/ /1/215 9/3/215. 1/1/215 1/31/ /1/215 11/3/ /1/215 12/31/ ,112 Total Throughput: 6,75 Average Thru/Hr GLASS/ROLL COATING / GLASS/ROLL COATING SO2 Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number Industrial Processes; Electrical Equipment; Light Bulb Manufacture; Light Bulb Glass to Socket Base Lubrication with SO2 Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/215 Lbs Lbs Lbs Lbs Lbs Lbs Lbs Lbs Lbs Lbs Lbs Lbs Lbs

245 Wednesday, November Pennsylvania Department of Environmental Protection Page 29 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 113 GLASS/ROLL COATING / GLASS/ROLL COATING SO2 Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant CO. MATERIAL BALANCE

246 Wednesday, November Pennsylvania Department of Environmental Protection Page 3 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type PETROL./SOLVENT EVAPOR. ; SURFACE COATING OPERATIONS ; S Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput /1/215 1/31/ Gal 2/1/215 2/28/ Gal 3/1/215 3/31/ Gal 4/1/215 4/3/ Gal 5/1/215 5/31/ Gal 6/1/215 6/3/ Gal 7/1/215 7/31/ Gal 8/1/215 8/31/215. Gal 9/1/215 9/3/215. Gal 1/1/215 1/31/215. Gal 11/1/215 11/3/215. Gal 12/1/215 12/31/215. Gal 8 85 Total Throughput: 7. Gal Average Thru/Hr.8 Exhaust Details ACFM: Stack Data Stack Id Name 114 PAINTING ACTIVITIES / PAINTING ACTIVITIES Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number PETROL./SOLVENT EVAPOR. ; SURFACE COATING OPERATIONS ; SURFACE COATING APPLICATION - GENERAL ; PAINT: SOLVENT-BASE Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/215

247 Wednesday, November Pennsylvania Department of Environmental Protection Page 31 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 114 PAINTING ACTIVITIES / PAINTING ACTIVITIES Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year U UNRATED FACTOR EPA SCC FACTOR Denotes Best Value for Pollutant CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant CO. MATERIAL BALANCE.12.12

248 Wednesday, November Pennsylvania Department of Environmental Protection Page 32 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Industrial Processes; Mineral Products; Asphalt Concrete; Tr Exhaust Details ACFM: Stack Data Stack Id Name Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/215 1/31/215. 2/1/215 2/28/215. 3/1/215 3/31/215. 4/1/215 4/3/215. 5/1/215 5/31/215. 6/1/215 6/3/215. 7/1/215 7/31/215. 8/1/215 8/31/215. 9/1/215 9/3/215. 1/1/215 1/31/ /1/215 11/3/ /1/215 12/31/ Total Throughput:. Average Thru/Hr 115 ASPHALT DRIVEWAY SEALER / ASPHALT DRIVEWAY SEALER Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number Industrial Processes; Mineral Products; Asphalt Concrete; Truck Load-out Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/215 Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons

249 Wednesday, November Pennsylvania Department of Environmental Protection Page 33 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 115 ASPHALT DRIVEWAY SEALER / ASPHALT DRIVEWAY SEALER Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

250 Wednesday, November Pennsylvania Department of Environmental Protection Page 34 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Propane Active. 91, Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/215 1/31/215. 2/1/215 2/28/215. 3/1/215 3/31/215. 4/1/215 4/3/215. 5/1/215 5/31/215. 6/1/215 6/3/215. 7/1/215 7/31/215. 8/1/215 8/31/215. 9/1/215 9/3/215. 1/1/215 1/31/ /1/215 11/3/ /1/215 12/31/ Total Throughput:. Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 116 FORK TRUCK, PROPANE / FORK TRUCK, PROPANE Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INTERNAL COMBUSTION ENGINES ; COMMERCIAL/INSTITUTIONAL ; LIQUIFIED PETROLEUM GAS (LPG) ; PROPANE: RECIPROCATING Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/215 Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal

251 Wednesday, November Pennsylvania Department of Environmental Protection Page 35 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 116 FORK TRUCK, PROPANE / FORK TRUCK, PROPANE Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE FUEL TYPE: Propane Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: FUEL TYPE: Propane Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant DEP STACK TEST

252 Wednesday, November Pennsylvania Department of Environmental Protection Page 36 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type PETROL./SOLVENT EVAPOR. ; SURFACE COATING OPERATIONS ; T Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,112 1/1/215 1/31/ Tons 2/1/215 2/28/ Tons 3/1/215 3/31/ Tons 4/1/215 4/3/ Tons 5/1/215 5/31/ Tons 6/1/215 6/3/ Tons 7/1/215 7/31/215.7 Tons 8/1/215 8/31/ Tons 9/1/215 9/3/215. Tons 1/1/215 1/31/215. Tons 11/1/215 11/3/215. Tons 12/1/215 12/31/215. Tons 213 5,112 Total Throughput: 5.98 Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 117 GLASS CUTTING/PACKAGING / CUTTING GLASS(SOLVENT) Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number PETROL./SOLVENT EVAPOR. ; SURFACE COATING OPERATIONS ; THINNING SOLVENTS - GENERAL ; MINERAL SPIRITS Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/215

253 Wednesday, November Pennsylvania Department of Environmental Protection Page 37 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 117 GLASS CUTTING/PACKAGING / CUTTING GLASS(SOLVENT) Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year NON CRITERIA SOURCE E RATED FACTOR EPA SCC FACTOR Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant CO. MATERIAL BALANCE

254 Wednesday, November Pennsylvania Department of Environmental Protection Page 38 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; FUGITIVE EMISS Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,112 1/1/215 1/31/215.6 Tons 2/1/215 2/28/215.6 Tons 3/1/215 3/31/215.6 Tons 4/1/215 4/3/215.6 Tons 5/1/215 5/31/215.6 Tons 6/1/215 6/3/215.6 Tons 7/1/215 7/31/215.6 Tons 8/1/215 8/31/215.6 Tons 9/1/215 9/3/215. Tons 1/1/215 1/31/215. Tons 11/1/215 11/3/215. Tons 12/1/215 12/31/215. Tons 213 5,112 Total Throughput: 4.8 Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 118 GLASS CUTTING/PACKAGING / G- CORE(GLASS SEPARATOR) Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; FUGITIVE EMISSIONS ; SPECIFY IN COMMENTS FIELD Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/215

255 Wednesday, November Pennsylvania Department of Environmental Protection Page 39 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 118 GLASS CUTTING/PACKAGING / G- CORE(GLASS SEPARATOR) Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

256 Wednesday, November Pennsylvania Department of Environmental Protection Page 4 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Diesel Fuel Active , Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/215 1/31/215. 2/1/215 2/28/215. 3/1/215 3/31/215. 4/1/215 4/3/215. 5/1/215 5/31/215. 6/1/215 6/3/215. 7/1/215 7/31/215. 8/1/215 8/31/215. 9/1/215 9/3/215. 1/1/215 1/31/ /1/215 11/3/ /1/215 12/31/ Total Throughput:. Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 119 SITE DEDICATED VEHICLES / DUMP/PAYLOADER EXHAUST Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INTERNAL COMBUSTION ENGINES ; INDUSTRIAL ; DISTILLATE OIL (DIESEL) ; RECIPROCATING: EXHAUST Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S6 ROAD FUGITIVES /1/215 Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal

257 Wednesday, November Pennsylvania Department of Environmental Protection Page 41 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 119 SITE DEDICATED VEHICLES / DUMP/PAYLOADER EXHAUST Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE FUEL TYPE: Diesel Fuel Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: FUEL TYPE: Diesel Fuel Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

258 Wednesday, November Pennsylvania Department of Environmental Protection Page 42 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; STONE QUARRYIN Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,112 1/1/215 1/31/ Miles 2/1/215 2/28/ Miles 3/1/215 3/31/ Miles 4/1/215 4/3/ Miles 5/1/215 5/31/ Miles 6/1/215 6/3/ Miles 7/1/215 7/31/ Miles 8/1/215 8/31/ Miles 9/1/215 9/3/215. Miles 1/1/215 1/31/215. Miles 11/1/215 11/3/215. Miles 12/1/215 12/31/215. Miles 213 5,112 Total Throughput: 2,385. Miles Average Thru/Hr.47 Exhaust Details ACFM: Stack Data Stack Id Name 12 SITE DEDICATED VEHICLES / PAVED ROADS Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; STONE QUARRYING - PROCESSING ; HAULING Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S6 ROAD FUGITIVES /1/215

259 Wednesday, November Pennsylvania Department of Environmental Protection Page 43 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 12 SITE DEDICATED VEHICLES / PAVED ROADS Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year PM1 U UNRATED FACTOR EPA SCC FACTOR Denotes Best Value for Pollutant CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

260 Wednesday, November Pennsylvania Department of Environmental Protection Page 44 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; STONE QUARRYIN Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,112 1/1/215 1/31/ Miles 2/1/215 2/28/ Miles 3/1/215 3/31/ Miles 4/1/215 4/3/ Miles 5/1/215 5/31/215.5 Miles 6/1/215 6/3/215.5 Miles 7/1/215 7/31/ Miles 8/1/215 8/31/215.5 Miles 9/1/215 9/3/215. Miles 1/1/215 1/31/215. Miles 11/1/215 11/3/215. Miles 12/1/215 12/31/215. Miles 213 5,112 Total Throughput: 2.75 Miles Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 121 SITE DEDICATED VEHICLES / UNPAVED ROADS Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; STONE QUARRYING - PROCESSING ; HAULING Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S6 ROAD FUGITIVES /1/215

261 Wednesday, November Pennsylvania Department of Environmental Protection Page 45 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 121 SITE DEDICATED VEHICLES / UNPAVED ROADS Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year PM1 U UNRATED FACTOR EPA SCC FACTOR Denotes Best Value for Pollutant CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

262 Wednesday, November Pennsylvania Department of Environmental Protection Page 46 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type PETROL./SOLVENT EVAPOR. ; SURFACE COATING OPERATIONS ; S Exhaust Details ACFM: Stack Data Stack Id Name Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,112 1/1/215 1/31/ /1/215 2/28/ /1/215 3/31/ /1/215 4/3/ /1/215 5/31/ /1/215 6/3/ /1/215 7/31/ /1/215 8/31/ /1/215 9/3/215. 1/1/215 1/31/ /1/215 11/3/ /1/215 12/31/ ,112 Total Throughput: 12.8 Average Thru/Hr 122 RTV SEALANT / RTV SEALANT Criteria: Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number PETROL./SOLVENT EVAPOR. ; SURFACE COATING OPERATIONS ; SURFACE COATING APPLICATION - GENERAL ; PAINT: SOLVENT-BASE Diameter Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/215 Gal Gal Gal Gal Gal Gal Gal Gal Gal Gal Gal Gal Gal

263 Wednesday, November Pennsylvania Department of Environmental Protection Page 47 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Process Unit: 122 RTV SEALANT / RTV SEALANT Criteria: Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year U UNRATED FACTOR EPA SCC FACTOR Denotes Best Value for Pollutant CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant CO. MATERIAL BALANCE 25 25

264 Wednesday, November Pennsylvania Department of Environmental Protection Page 48 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Combustion Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Natural Gas Active. 1,5 Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/215 1/31/215. MMCF 2/1/215 2/28/215. MMCF 3/1/215 3/31/215. MMCF 4/1/215 4/3/215. MMCF 5/1/215 5/31/215. MMCF 6/1/215 6/3/215. MMCF 7/1/215 7/31/215. MMCF 8/1/215 8/31/215. MMCF 9/1/215 9/3/215. MMCF 1/1/215 1/31/215. MMCF 11/1/215 11/3/215. MMCF 12/1/215 12/31/215. MMCF 1 Total Throughput:. MMCF Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 1 RAW MATERIAL RECEIVING / BATCH WATER HEATER-NG Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: Boiler Desc: SCC-Number EXTERNAL COMBUSTION BOILERS ; INDUSTRIAL ; NATURAL GAS ; < 1 MILLION BTU/HR Diameter Criteria: Material Elevation NON CRITERIA SOURCE Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S4 MISC COMBUSTION /1/215

265 Wednesday, November Pennsylvania Department of Environmental Protection Page 49 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Combustion Unit: 1 RAW MATERIAL RECEIVING / BATCH WATER HEATER-NG Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE FUEL TYPE: Natural Gas Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: FUEL TYPE: Natural Gas Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Hexane Denotes Best Value for Pollutant AP-42 LATEST AVAILABLE

266 Wednesday, November Pennsylvania Department of Environmental Protection Page 5 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Combustion Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,112 1/1/215 1/31/215 9,156. Tons 2/1/215 2/28/215 7,936. Tons 3/1/215 3/31/215 9,98. Tons 4/1/215 4/3/215 8,77. Tons 5/1/215 5/31/215 9,51. Tons 6/1/215 6/3/215 8,842. Tons 7/1/215 7/31/215 9,135. Tons 8/1/215 8/31/ Tons 9/1/215 9/3/215. Tons 1/1/215 1/31/215. Tons 11/1/215 11/3/215. Tons 12/1/215 12/31/215. Tons 213 5,112 Total Throughput: 62,215. Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 2 GLASS MELT FURNACE / METAL GLASS DI/ESP Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: Boiler Desc: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; FLAT GLASS: MELTING FURNACE Diameter Criteria: Material Elevation NON CRITERIA SOURCE Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S2 EP STACK (PRIMARY) , /1/215

267 Wednesday, November Pennsylvania Department of Environmental Protection Page 51 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Combustion Unit: 2 GLASS MELT FURNACE / METAL GLASS DI/ESP Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 SOX Denotes Best Value for Pollutant B RATED FACTOR B RATED FACTOR B RATED FACTOR B RATED FACTOR B RATED FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR

268 Wednesday, November Pennsylvania Department of Environmental Protection Page 52 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Combustion Unit: 2 GLASS MELT FURNACE / METAL GLASS Criteria: NON CRITERIA SOURCE DI/ESP Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Cadmium Chromium Lead Selenium Nitrous Oxide PM-CON Cobalt Compounds Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP ,

269 Wednesday, November Pennsylvania Department of Environmental Protection Page 53 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Combustion Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Natural Gas Active. 1,5 Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,112 1/1/215 1/31/215.2 MMCF 2/1/215 2/28/215.2 MMCF 3/1/215 3/31/215.2 MMCF 4/1/215 4/3/215.2 MMCF 5/1/215 5/31/215.2 MMCF 6/1/215 6/3/215.2 MMCF 7/1/215 7/31/215.2 MMCF 8/1/215 8/31/215.2 MMCF 9/1/215 9/3/215. MMCF 1/1/215 1/31/215. MMCF 11/1/215 11/3/215. MMCF 12/1/215 12/31/215. MMCF 213 5,112 Total Throughput: 1.6 MMCF Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 3 CULLET PROCESSING / CULLET HEATING-NG Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: Boiler Desc: SCC-Number EXTERNAL COMBUSTION BOILERS ; INDUSTRIAL ; NATURAL GAS ; < 1 MILLION BTU/HR Diameter Criteria: Material Elevation NON CRITERIA SOURCE Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/215

270 Wednesday, November Pennsylvania Department of Environmental Protection Page 54 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Combustion Unit: 3 CULLET PROCESSING / CULLET HEATING-NG Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE FUEL TYPE: Natural Gas Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 SOX Methane Ammonia Carbon Dioxide Nitrous Oxide Denotes Best Value for Pollutant A RATED FACTOR A RATED FACTOR C RATED FACTOR A RATED FACTOR D RATED FACTOR A RATED FACTOR C RATED FACTOR A RATED FACTOR A RATED FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR

271 Wednesday, November Pennsylvania Department of Environmental Protection Page 55 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Combustion Unit: 3 CULLET PROCESSING / CULLET Criteria: NON CRITERIA SOURCE HEATING-NG Emission Data for Company Estimates SCC: FUEL TYPE: Natural Gas Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Hexane Denotes Best Value for Pollutant

272 Wednesday, November Pennsylvania Department of Environmental Protection Page 56 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Combustion Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Liquid Petroleum Gas (Lpg) Active. 91, Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,112 1/1/215 1/31/215.3 Th Gal 2/1/215 2/28/215.3 Th Gal 3/1/215 3/31/215.3 Th Gal 4/1/215 4/3/215.3 Th Gal 5/1/215 5/31/215.3 Th Gal 6/1/215 6/3/215.3 Th Gal 7/1/215 7/31/215.3 Th Gal 8/1/215 8/31/215.3 Th Gal 9/1/215 9/3/215. Th Gal 1/1/215 1/31/215. Th Gal 11/1/215 11/3/215. Th Gal 12/1/215 12/31/215. Th Gal 213 5,112 Total Throughput:.24 Th Gal Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 4 PROPANE HEATERS / PROPANE HEATERS Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: Boiler Desc: SCC-Number EXTERNAL COMBUSTION BOILERS ; INDUSTRIAL ; LIQUIFIED PETROLEUM GAS (LPG) ; PROPANE Diameter Criteria: Material Elevation NON CRITERIA SOURCE Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S4 MISC COMBUSTION /1/215

273 Wednesday, November Pennsylvania Department of Environmental Protection Page 57 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Combustion Unit: 4 PROPANE HEATERS / PROPANE HEATERS Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE FUEL TYPE: Liquid Petroleum Gas (Lpg) Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 Methane Carbon Dioxide Denotes Best Value for Pollutant C RATED FACTOR C RATED FACTOR C RATED FACTOR E RATED FACTOR A RATED FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR

274 Wednesday, November Pennsylvania Department of Environmental Protection Page 58 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Combustion Unit: 4 PROPANE HEATERS / PROPANE Criteria: NON CRITERIA SOURCE HEATERS Emission Data for Company Estimates SCC: FUEL TYPE: Liquid Petroleum Gas (Lpg) Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

275 Wednesday, November Pennsylvania Department of Environmental Protection Page 59 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Combustion Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Natural Gas Active. 1,5 Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,112 1/1/215 1/31/ MMCF 2/1/215 2/28/ MMCF 3/1/215 3/31/ MMCF 4/1/215 4/3/ MMCF 5/1/215 5/31/ MMCF 6/1/215 6/3/ MMCF 7/1/215 7/31/ MMCF 8/1/215 8/31/ MMCF 9/1/215 9/3/215. MMCF 1/1/215 1/31/215. MMCF 11/1/215 11/3/215. MMCF 12/1/215 12/31/215. MMCF 213 5,112 Total Throughput: 54.8 MMCF Average Thru/Hr.1 Exhaust Details ACFM: Stack Data Stack Id Name 31 SPACE/WATER HEATERS, NG / SPACE/WATER HEATERS, NG Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: Boiler Desc: SCC-Number EXTERNAL COMBUSTION BOILERS ; INDUSTRIAL ; NATURAL GAS ; < 1 MILLION BTU/HR Diameter Criteria: Material Elevation NON CRITERIA SOURCE Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S4 MISC COMBUSTION /1/215

276 Wednesday, November Pennsylvania Department of Environmental Protection Page 6 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Combustion Unit: 31 SPACE/WATER HEATERS, NG / SPACE/WATER HEATERS, NG Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE FUEL TYPE: Natural Gas Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 SOX Methane Ammonia Carbon Dioxide Nitrous Oxide Denotes Best Value for Pollutant A RATED FACTOR A RATED FACTOR C RATED FACTOR A RATED FACTOR D RATED FACTOR A RATED FACTOR C RATED FACTOR A RATED FACTOR A RATED FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR , , , ,

277 Wednesday, November Pennsylvania Department of Environmental Protection Page 61 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 215 Firm/Plant Code: Primary Facility ID: Combustion Unit: 31 SPACE/WATER HEATERS, NG / Criteria: NON CRITERIA SOURCE SPACE/WATER HEATERS, NG Emission Data for Company Estimates SCC: FUEL TYPE: Natural Gas Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Hexane Denotes Best Value for Pollutant AP-42 LATEST AVAILABLE DEP EFFICIENCY OF CONTROL DEVICE DEP EFFICIENCY OF CONTROL DEVICE ,

278 Wednesday, November Pennsylvania Department of Environmental Protection Page 1 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Region: 7 SIC Code: Site Totals (Best Controlled) Criteria/Non-Criteria(Totals) District: 71 County: 2 Allegheny Municipality: 2826 Jefferson Hills Boro AFS-Id Number: CDS-Id Number: Date Totals Last Completed: 7/9/215 Contact Type Location Address Firm Plant Contact Responsible Official Contact Site Location Information 3211 Manufacturing - Flat Glass Street Address 1 Glass House Rd 1 Glass House Rd 1 Glass House Rd City State Zip Contact Name Phone Number Jefferson Hills Jefferson Hills Jefferson Hills NAICS Code: PA PA PA Flat Glass Manufacturing Gregg Eckstein John Buckner Map: Latitude: 4 deg, 15 min, 2 sec N UTM : Zone: 17 North: Elevation(Ft): Longitude: -79 deg, 54 min, 57. sec W East: CO: LEAD: : PM1: PM25: SOX: : Criteria/Hazardous: Non-Criteria: Total Stacks: 6 Site Comment Processes 22 Combustion Units 5 Incinerators Control Devices 1 NESHAPS: NSPS: PSD: Fuel Material Location Data

279 Wednesday, November Pennsylvania Department of Environmental Protection Page 2 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,92 1/1/214 1/31/214 7,33.65 Tons 2/1/214 2/28/214 6,384.1 Tons 3/1/214 3/31/214 6, Tons 4/1/214 4/3/214 8,3.81 Tons 5/1/214 5/31/214 6, Tons 6/1/214 6/3/214 6, Tons 7/1/214 7/31/214 8, Tons 8/1/214 8/31/214 7, Tons 9/1/214 9/3/214 7, Tons 1/1/214 1/31/214 7,6.41 Tons 11/1/214 11/3/214 5, Tons 12/1/214 12/31/214 8,344.6 Tons 365 2,92 Total Throughput: 87,16.28 Tons Average Thru/Hr 29.8 Exhaust Details ACFM: Stack Data Stack Id Name 11 RAW MATERIAL RECEIVING / HANDLING Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; RAW MATERIAL HANDLING (ALL TYPES OF GLASS) Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/214

280 Wednesday, November Pennsylvania Department of Environmental Protection Page 3 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 11 RAW MATERIAL RECEIVING / HANDLING Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

281 Wednesday, November Pennsylvania Department of Environmental Protection Page 4 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/214 1/31/ Tons 2/1/214 2/28/ Tons 3/1/214 3/31/ Tons 4/1/214 4/3/ Tons 5/1/214 5/31/ Tons 6/1/214 6/3/ Tons 7/1/214 7/31/ Tons 8/1/214 8/31/ Tons 9/1/214 9/3/ Tons 1/1/214 1/31/ Tons 11/1/214 11/3/ Tons 12/1/214 12/31/ Tons 365 8,76 Total Throughput: Tons Average Thru/Hr.5 Exhaust Details ACFM: Stack Data Stack Id Name 12 RAW MATERIAL RECEIVING / HANDLING (HYDRATED LIME) Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; RAW MATERIAL HANDLING (ALL TYPES OF GLASS) Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/214

282 Wednesday, November Pennsylvania Department of Environmental Protection Page 5 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 12 RAW MATERIAL RECEIVING / HANDLING (HYDRATED LIME) Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

283 Wednesday, November Pennsylvania Department of Environmental Protection Page 6 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/214 1/31/ Tons 2/1/214 2/28/ Tons 3/1/214 3/31/ Tons 4/1/214 4/3/ Tons 5/1/214 5/31/ Tons 6/1/214 6/3/ Tons 7/1/214 7/31/ Tons 8/1/214 8/31/ Tons 9/1/214 9/3/ Tons 1/1/214 1/31/ Tons 11/1/214 11/3/ Tons 12/1/214 12/31/ Tons 365 8,76 Total Throughput: Tons Average Thru/Hr.6 Exhaust Details ACFM: Stack Data Stack Id Name 13 RAW MATERIAL RECEIVING / HANDLING (RECIRC LIME) Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; RAW MATERIAL HANDLING (ALL TYPES OF GLASS) Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/214

284 Wednesday, November Pennsylvania Department of Environmental Protection Page 7 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 13 RAW MATERIAL RECEIVING / HANDLING (RECIRC LIME) Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

285 Wednesday, November Pennsylvania Department of Environmental Protection Page 8 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/214 1/31/214. Tons 2/1/214 2/28/214. Tons 3/1/214 3/31/214. Tons 4/1/214 4/3/214. Tons 5/1/214 5/31/214. Tons 6/1/214 6/3/214. Tons 7/1/214 7/31/214. Tons 8/1/214 8/31/214. Tons 9/1/214 9/3/214. Tons 1/1/214 1/31/214. Tons 11/1/214 11/3/214. Tons 12/1/214 12/31/214. Tons 1 Total Throughput:. Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 14 GLASS MELT FURNACE / NON-METAL GLASS DI/ESP Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; FLAT GLASS: MELTING FURNACE Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S2 EP STACK (PRIMARY) , /1/214

286 Wednesday, November Pennsylvania Department of Environmental Protection Page 9 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 14 GLASS MELT FURNACE / NON-METAL GLASS DI/ESP Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Cobalt Compounds Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP

287 Wednesday, November Pennsylvania Department of Environmental Protection Page 1 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/214 1/31/214. Tons 2/1/214 2/28/214. Tons 3/1/214 3/31/214. Tons 4/1/214 4/3/214. Tons 5/1/214 5/31/214. Tons 6/1/214 6/3/214. Tons 7/1/214 7/31/214. Tons 8/1/214 8/31/214. Tons 9/1/214 9/3/214. Tons 1/1/214 1/31/214. Tons 11/1/214 11/3/214. Tons 12/1/214 12/31/214. Tons 1 Total Throughput:. Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 15 GLASS MELT FURNACE / NON-METAL NO DI/ESP Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; FLAT GLASS: MELTING FURNACE Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S1 FURNACE EJECTOR STACK , /1/214

288 Wednesday, November Pennsylvania Department of Environmental Protection Page 11 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 15 GLASS MELT FURNACE / NON-METAL NO DI/ESP Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Cobalt Compounds Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP

289 Wednesday, November Pennsylvania Department of Environmental Protection Page 12 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput /1/214 1/31/ Tons 2/1/214 2/28/ Tons 3/1/214 3/31/ Tons 4/1/214 4/3/ Tons 5/1/214 5/31/ Tons 6/1/214 6/3/ Tons 7/1/214 7/31/ Tons 8/1/214 8/31/ Tons 9/1/214 9/3/214. Tons 1/1/214 1/31/214. Tons 11/1/214 11/3/214. Tons 12/1/214 12/31/ Tons Total Throughput: 1,615. Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 16 GLASS MELT FURNACE / METAL GLASS NO DI/ESP Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; FLAT GLASS: MELTING FURNACE Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S1 FURNACE EJECTOR STACK , /1/214

290 Wednesday, November Pennsylvania Department of Environmental Protection Page 13 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 16 GLASS MELT FURNACE / METAL GLASS NO DI/ESP Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 SOX Denotes Best Value for Pollutant B RATED FACTOR B RATED FACTOR B RATED FACTOR B RATED FACTOR B RATED FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR

291 Wednesday, November Pennsylvania Department of Environmental Protection Page 14 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 16 GLASS MELT FURNACE / METAL GLASS Criteria: NON CRITERIA SOURCE NO DI/ESP Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Cadmium Chromium Lead Selenium Nitrous Oxide PM-CON Cobalt Compounds Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP

292 Wednesday, November Pennsylvania Department of Environmental Protection Page 15 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/214 1/31/214. Tons 2/1/214 2/28/214. Tons 3/1/214 3/31/214. Tons 4/1/214 4/3/214. Tons 5/1/214 5/31/214. Tons 6/1/214 6/3/214. Tons 7/1/214 7/31/214. Tons 8/1/214 8/31/214. Tons 9/1/214 9/3/214. Tons 1/1/214 1/31/214. Tons 11/1/214 11/3/214. Tons 12/1/214 12/31/214. Tons 1 Total Throughput:. Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 17 GLASS MELT FURNACE / NON-METAL (ESP ONLY OPR) Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; FLAT GLASS: MELTING FURNACE Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S2 EP STACK (PRIMARY) , /1/214

293 Wednesday, November Pennsylvania Department of Environmental Protection Page 16 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 17 GLASS MELT FURNACE / NON-METAL (ESP ONLY OPR) Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP

294 Wednesday, November Pennsylvania Department of Environmental Protection Page 17 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput /1/214 1/31/214. Tons 2/1/214 2/28/214. Tons 3/1/214 3/31/214. Tons 4/1/214 4/3/214. Tons 5/1/214 5/31/214. Tons 6/1/214 6/3/214. Tons 7/1/214 7/31/214. Tons 8/1/214 8/31/214. Tons 9/1/214 9/3/214. Tons 1/1/214 1/31/ Tons 11/1/214 11/3/214. Tons 12/1/214 12/31/214. Tons 1 1 Total Throughput: 13. Tons Average Thru/Hr 13. Exhaust Details ACFM: Control Equipment Details 18 GLASS MELT FURNACE / METAL GLASS (ESP ONLY OPR Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr Category: SCC-Number Criteria: Material NON CRITERIA SOURCE INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; FLAT GLASS: MELTING FURNACE SCFM: % Moist: Temp-F: ID CD-1 Name Date Installed Type Code Pressure Drop METAL GLASS DI/ESP 41 Discharges To S2

295 Wednesday, November Pennsylvania Department of Environmental Protection Page 18 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 18 GLASS MELT FURNACE / METAL GLASS (ESP ONLY OPR Control Equipment Details Criteria: NON CRITERIA SOURCE ID Name Pollutant Control Pollutant PM1 Particulate Matter < 1 Microns PM25 Particulate Matter < 2.5 Microns Date Installed EFF(%) Type Code EFF Code A A Pressure Drop Discharges To EFF Description Rated efficiency: guaranteed minimum Rated efficiency: guaranteed minimum Stack Data Stack Id Name Source Totals (Best Controlled) Emission Data for SCC Factors SCC: Height Diameter Elevation Exhaust SCFM Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Temp (F) Moist (%) Flow (%) Flow Start Date S2 EP STACK (PRIMARY) , /1/214 CO PM1 SOX CO PM1 PM25 SOX Denotes Best Value for Pollutant Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds B RATED FACTOR B RATED FACTOR B RATED FACTOR B RATED FACTOR B RATED FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR

296 Wednesday, November Pennsylvania Department of Environmental Protection Page 19 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 18 GLASS MELT FURNACE / METAL GLASS Criteria: NON CRITERIA SOURCE (ESP ONLY OPR Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Cadmium Chromium Lead Selenium Nitrous Oxide PM-CON Cobalt Compounds Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP

297 Wednesday, November Pennsylvania Department of Environmental Protection Page 2 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/214 1/31/214 2,7 Tons 2/1/214 2/28/214 2,135. Tons 3/1/214 3/31/214 2,983. Tons 4/1/214 4/3/214 5,188. Tons 5/1/214 5/31/214 2,487. Tons 6/1/214 6/3/214 2,186. Tons 7/1/214 7/31/214 2,137. Tons 8/1/214 8/31/214 2,594. Tons 9/1/214 9/3/214 2,355. Tons 1/1/214 1/31/214 5,872. Tons 11/1/214 11/3/214 2,856. Tons 12/1/214 12/31/214 3,45. Tons 365 8,76 Total Throughput: 36,538. Tons Average Thru/Hr 4.17 Exhaust Details ACFM: Stack Data Stack Id Name 19 CULLET PROCESSING / CULLET CRUSHING Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; CULLET: CRUSHING/GRINDING Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/214

298 Wednesday, November Pennsylvania Department of Environmental Protection Page 21 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 19 CULLET PROCESSING / CULLET CRUSHING Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant AP-42 LATEST AVAILABLE AP-42 LATEST AVAILABLE

299 Wednesday, November Pennsylvania Department of Environmental Protection Page 22 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/214 1/31/214 4,95. Tons 2/1/214 2/28/214 3,7 Tons 3/1/214 3/31/214 3,442. Tons 4/1/214 4/3/214 3,182. Tons 5/1/214 5/31/214 3,788. Tons 6/1/214 6/3/214 3,837. Tons 7/1/214 7/31/214 3,84 Tons 8/1/214 8/31/214 3,738. Tons 9/1/214 9/3/214 3,452. Tons 1/1/214 1/31/214 3,746. Tons 11/1/214 11/3/214 4,259. Tons 12/1/214 12/31/214 4,42. Tons 365 8,76 Total Throughput: 45,481. Tons Average Thru/Hr 5.19 Exhaust Details ACFM: Stack Data Stack Id Name 11 CULLET PROCESSING / CULLET HANDLING Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; RAW MATERIAL HANDLING (ALL TYPES OF GLASS) Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/214

300 Wednesday, November Pennsylvania Department of Environmental Protection Page 23 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 11 CULLET PROCESSING / CULLET HANDLING Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP

301 Wednesday, November Pennsylvania Department of Environmental Protection Page 24 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Exhaust Details ACFM: Stack Data Stack Id Name Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/214 1/31/214 4,95. 2/1/214 2/28/214 3,7 3/1/214 3/31/214 3,442. 4/1/214 4/3/214 3,182. 5/1/214 5/31/214 3,788. 6/1/214 6/3/214 3,837. 7/1/214 7/31/214 3,84 8/1/214 8/31/214 3,738. 9/1/214 9/3/214 3,452. 1/1/214 1/31/214 3, /1/214 11/3/214 4, /1/214 12/31/214 4, ,76 Total Throughput: 45,481. Average Thru/Hr CULLET PROCESSING / CULLET PADS Criteria: Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; CULLET: CRUSHING/GRINDING Diameter Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/214 Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons

302 Wednesday, November Pennsylvania Department of Environmental Protection Page 25 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 111 CULLET PROCESSING / CULLET PADS Criteria: Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant AP-42 LATEST AVAILABLE AP-42 LATEST AVAILABLE

303 Wednesday, November Pennsylvania Department of Environmental Protection Page 26 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type PETROL./SOLVENT EVAPOR. ; PETRO-PROD. STORAGE (REFINERY) Exhaust Details ACFM: Stack Data Stack Id Name Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/214 1/31/214. 2/1/214 2/28/214. 3/1/214 3/31/214. 4/1/214 4/3/214. 5/1/214 5/31/214. 6/1/214 6/3/214. 7/1/214 7/31/214. 8/1/214 8/31/214. 9/1/214 9/3/214. 1/1/214 1/31/ /1/214 11/3/ /1/214 12/31/ Total Throughput:. Average Thru/Hr 112 STORAGE TANKS / STORAGE TANKS Criteria: Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number PETROL./SOLVENT EVAPOR. ; PETRO-PROD. STORAGE (REFINERY) ; VARIABLE VAPOR SPACE ; SPECIFY LIQUID: FILLING LOSS Diameter Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/214 Gal Gal Gal Gal Gal Gal Gal Gal Gal Gal Gal Gal Th Gal

304 Wednesday, November Pennsylvania Department of Environmental Protection Page 27 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 112 STORAGE TANKS / STORAGE TANKS Criteria: Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

305 Wednesday, November Pennsylvania Department of Environmental Protection Page 28 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Industrial Processes; Electrical Equipment; Light Bulb Manuf Exhaust Details ACFM: Stack Data Stack Id Name Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/214 1/31/214 1,25 2/1/214 2/28/214 5, 3/1/214 3/31/214 1,75 4/1/214 4/3/214 2,75 5/1/214 5/31/214 3,75 6/1/214 6/3/ /1/214 7/31/214 3, 8/1/214 8/31/214 2,75 9/1/214 9/3/214 2,75 1/1/214 1/31/214 2, 11/1/214 11/3/214 2,25 12/1/214 12/31/214 1, 365 8,76 Total Throughput: 29, Average Thru/Hr GLASS/ROLL COATING / GLASS/ROLL COATING SO2 Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number Industrial Processes; Electrical Equipment; Light Bulb Manufacture; Light Bulb Glass to Socket Base Lubrication with SO2 Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/214 Lbs Lbs Lbs Lbs Lbs Lbs Lbs Lbs Lbs Lbs Lbs Lbs Lbs

306 Wednesday, November Pennsylvania Department of Environmental Protection Page 29 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 113 GLASS/ROLL COATING / GLASS/ROLL COATING SO2 Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant CO. MATERIAL BALANCE

307 Wednesday, November Pennsylvania Department of Environmental Protection Page 3 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type PETROL./SOLVENT EVAPOR. ; SURFACE COATING OPERATIONS ; S Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput /1/214 1/31/ Gal 2/1/214 2/28/ Gal 3/1/214 3/31/ Gal 4/1/214 4/3/ Gal 5/1/214 5/31/ Gal 6/1/214 6/3/ Gal 7/1/214 7/31/ Gal 8/1/214 8/31/ Gal 9/1/214 9/3/ Gal 1/1/214 1/31/ Gal 11/1/214 11/3/ Gal 12/1/214 12/31/ Gal Total Throughput: 12. Gal Average Thru/Hr.8 Exhaust Details ACFM: Stack Data Stack Id Name 114 PAINTING ACTIVITIES / PAINTING ACTIVITIES Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number PETROL./SOLVENT EVAPOR. ; SURFACE COATING OPERATIONS ; SURFACE COATING APPLICATION - GENERAL ; PAINT: SOLVENT-BASE Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/214

308 Wednesday, November Pennsylvania Department of Environmental Protection Page 31 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 114 PAINTING ACTIVITIES / PAINTING ACTIVITIES Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year U UNRATED FACTOR EPA SCC FACTOR Denotes Best Value for Pollutant CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant CO. MATERIAL BALANCE

309 Wednesday, November Pennsylvania Department of Environmental Protection Page 32 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Industrial Processes; Mineral Products; Asphalt Concrete; Tr Exhaust Details ACFM: Stack Data Stack Id Name Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/214 1/31/214. 2/1/214 2/28/214. 3/1/214 3/31/214. 4/1/214 4/3/214. 5/1/214 5/31/214. 6/1/214 6/3/214. 7/1/214 7/31/214. 8/1/214 8/31/214. 9/1/214 9/3/214. 1/1/214 1/31/ /1/214 11/3/ /1/214 12/31/ Total Throughput:. Average Thru/Hr 115 ASPHALT DRIVEWAY SEALER / ASPHALT DRIVEWAY SEALER Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number Industrial Processes; Mineral Products; Asphalt Concrete; Truck Load-out Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/214 Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons

310 Wednesday, November Pennsylvania Department of Environmental Protection Page 33 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 115 ASPHALT DRIVEWAY SEALER / ASPHALT DRIVEWAY SEALER Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

311 Wednesday, November Pennsylvania Department of Environmental Protection Page 34 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Propane Active. 91, Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/214 1/31/214. 2/1/214 2/28/214. 3/1/214 3/31/214. 4/1/214 4/3/214. 5/1/214 5/31/214. 6/1/214 6/3/214. 7/1/214 7/31/214. 8/1/214 8/31/214. 9/1/214 9/3/214. 1/1/214 1/31/ /1/214 11/3/ /1/214 12/31/ Total Throughput:. Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 116 FORK TRUCK, PROPANE / FORK TRUCK, PROPANE Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INTERNAL COMBUSTION ENGINES ; COMMERCIAL/INSTITUTIONAL ; LIQUIFIED PETROLEUM GAS (LPG) ; PROPANE: RECIPROCATING Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/214 Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal

312 Wednesday, November Pennsylvania Department of Environmental Protection Page 35 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 116 FORK TRUCK, PROPANE / FORK TRUCK, PROPANE Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE FUEL TYPE: Propane Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: FUEL TYPE: Propane Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

313 Wednesday, November Pennsylvania Department of Environmental Protection Page 36 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type PETROL./SOLVENT EVAPOR. ; SURFACE COATING OPERATIONS ; T Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/214 1/31/214.7 Tons 2/1/214 2/28/214.7 Tons 3/1/214 3/31/ Tons 4/1/214 4/3/ Tons 5/1/214 5/31/214.7 Tons 6/1/214 6/3/ Tons 7/1/214 7/31/ Tons 8/1/214 8/31/ Tons 9/1/214 9/3/ Tons 1/1/214 1/31/ Tons 11/1/214 11/3/ Tons 12/1/214 12/31/ Tons 365 8,76 Total Throughput: 9.32 Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 117 GLASS CUTTING/PACKAGING / CUTTING GLASS(SOLVENT) Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number PETROL./SOLVENT EVAPOR. ; SURFACE COATING OPERATIONS ; THINNING SOLVENTS - GENERAL ; MINERAL SPIRITS Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/214

314 Wednesday, November Pennsylvania Department of Environmental Protection Page 37 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 117 GLASS CUTTING/PACKAGING / CUTTING GLASS(SOLVENT) Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year NON CRITERIA SOURCE E RATED FACTOR EPA SCC FACTOR Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant CO. MATERIAL BALANCE

315 Wednesday, November Pennsylvania Department of Environmental Protection Page 38 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; FUGITIVE EMISS Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/214 1/31/214.6 Tons 2/1/214 2/28/214.6 Tons 3/1/214 3/31/214.6 Tons 4/1/214 4/3/214.6 Tons 5/1/214 5/31/214.6 Tons 6/1/214 6/3/214.6 Tons 7/1/214 7/31/214.6 Tons 8/1/214 8/31/214.6 Tons 9/1/214 9/3/214.6 Tons 1/1/214 1/31/214.6 Tons 11/1/214 11/3/214.6 Tons 12/1/214 12/31/214.6 Tons 365 8,76 Total Throughput: 7.2 Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 118 GLASS CUTTING/PACKAGING / G- CORE(GLASS SEPARATOR) Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; FUGITIVE EMISSIONS ; SPECIFY IN COMMENTS FIELD Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/214

316 Wednesday, November Pennsylvania Department of Environmental Protection Page 39 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 118 GLASS CUTTING/PACKAGING / G- CORE(GLASS SEPARATOR) Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

317 Wednesday, November Pennsylvania Department of Environmental Protection Page 4 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Diesel Fuel Active , Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/214 1/31/214. 2/1/214 2/28/214. 3/1/214 3/31/214. 4/1/214 4/3/214. 5/1/214 5/31/214. 6/1/214 6/3/214. 7/1/214 7/31/214. 8/1/214 8/31/214. 9/1/214 9/3/214. 1/1/214 1/31/ /1/214 11/3/ /1/214 12/31/ Total Throughput:. Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 119 SITE DEDICATED VEHICLES / DUMP/PAYLOADER EXHAUST Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INTERNAL COMBUSTION ENGINES ; INDUSTRIAL ; DISTILLATE OIL (DIESEL) ; RECIPROCATING: EXHAUST Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S6 ROAD FUGITIVES /1/214 Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal

318 Wednesday, November Pennsylvania Department of Environmental Protection Page 41 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 119 SITE DEDICATED VEHICLES / DUMP/PAYLOADER EXHAUST Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE FUEL TYPE: Diesel Fuel Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: FUEL TYPE: Diesel Fuel Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

319 Wednesday, November Pennsylvania Department of Environmental Protection Page 42 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; STONE QUARRYIN Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/214 1/31/ Miles 2/1/214 2/28/ Miles 3/1/214 3/31/ Miles 4/1/214 4/3/ Miles 5/1/214 5/31/ Miles 6/1/214 6/3/ Miles 7/1/214 7/31/ Miles 8/1/214 8/31/ Miles 9/1/214 9/3/ Miles 1/1/214 1/31/ Miles 11/1/214 11/3/ Miles 12/1/214 12/31/ Miles 365 8,76 Total Throughput: 4, Miles Average Thru/Hr.5 Exhaust Details ACFM: Stack Data Stack Id Name 12 SITE DEDICATED VEHICLES / PAVED ROADS Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; STONE QUARRYING - PROCESSING ; HAULING Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S6 ROAD FUGITIVES /1/214

320 Wednesday, November Pennsylvania Department of Environmental Protection Page 43 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 12 SITE DEDICATED VEHICLES / PAVED ROADS Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year PM1 U UNRATED FACTOR EPA SCC FACTOR Denotes Best Value for Pollutant CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

321 Wednesday, November Pennsylvania Department of Environmental Protection Page 44 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; STONE QUARRYIN Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/214 1/31/ Miles 2/1/214 2/28/ Miles 3/1/214 3/31/ Miles 4/1/214 4/3/ Miles 5/1/214 5/31/214.5 Miles 6/1/214 6/3/214.5 Miles 7/1/214 7/31/ Miles 8/1/214 8/31/214.5 Miles 9/1/214 9/3/214.5 Miles 1/1/214 1/31/ Miles 11/1/214 11/3/ Miles 12/1/214 12/31/ Miles 365 8,76 Total Throughput: 4. Miles Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 121 SITE DEDICATED VEHICLES / UNPAVED ROADS Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; STONE QUARRYING - PROCESSING ; HAULING Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S6 ROAD FUGITIVES /1/214

322 Wednesday, November Pennsylvania Department of Environmental Protection Page 45 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 121 SITE DEDICATED VEHICLES / UNPAVED ROADS Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year PM1 U UNRATED FACTOR EPA SCC FACTOR Denotes Best Value for Pollutant CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

323 Wednesday, November Pennsylvania Department of Environmental Protection Page 46 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type PETROL./SOLVENT EVAPOR. ; SURFACE COATING OPERATIONS ; S Exhaust Details ACFM: Stack Data Stack Id Name Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/214 1/31/ /1/214 2/28/ /1/214 3/31/ /1/214 4/3/ /1/214 5/31/ /1/214 6/3/ /1/214 7/31/ /1/214 8/31/ /1/214 9/3/ /1/214 1/31/ /1/214 11/3/ /1/214 12/31/ ,76 Total Throughput: 19.2 Average Thru/Hr 122 RTV SEALANT / RTV SEALANT Criteria: Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number PETROL./SOLVENT EVAPOR. ; SURFACE COATING OPERATIONS ; SURFACE COATING APPLICATION - GENERAL ; PAINT: SOLVENT-BASE Diameter Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/214 Gal Gal Gal Gal Gal Gal Gal Gal Gal Gal Gal Gal Gal

324 Wednesday, November Pennsylvania Department of Environmental Protection Page 47 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Process Unit: 122 RTV SEALANT / RTV SEALANT Criteria: Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year U UNRATED FACTOR EPA SCC FACTOR Denotes Best Value for Pollutant CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant CO. MATERIAL BALANCE 38 38

325 Wednesday, November Pennsylvania Department of Environmental Protection Page 48 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Combustion Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Natural Gas Active. 1,5 Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/214 1/31/214. MMCF 2/1/214 2/28/214. MMCF 3/1/214 3/31/214. MMCF 4/1/214 4/3/214. MMCF 5/1/214 5/31/214. MMCF 6/1/214 6/3/214. MMCF 7/1/214 7/31/214. MMCF 8/1/214 8/31/214. MMCF 9/1/214 9/3/214. MMCF 1/1/214 1/31/214. MMCF 11/1/214 11/3/214. MMCF 12/1/214 12/31/214. MMCF 1 Total Throughput:. MMCF Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 1 RAW MATERIAL RECEIVING / BATCH WATER HEATER-NG Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: Boiler Desc: SCC-Number EXTERNAL COMBUSTION BOILERS ; INDUSTRIAL ; NATURAL GAS ; < 1 MILLION BTU/HR Diameter Criteria: Material Elevation NON CRITERIA SOURCE Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S4 MISC COMBUSTION /1/214

326 Wednesday, November Pennsylvania Department of Environmental Protection Page 49 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Combustion Unit: 1 RAW MATERIAL RECEIVING / BATCH WATER HEATER-NG Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE FUEL TYPE: Natural Gas Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: FUEL TYPE: Natural Gas Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Hexane Denotes Best Value for Pollutant AP-42 LATEST AVAILABLE

327 Wednesday, November Pennsylvania Department of Environmental Protection Page 5 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Combustion Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/214 1/31/214 9,279. Tons 2/1/214 2/28/214 8,522. Tons 3/1/214 3/31/214 9,515. Tons 4/1/214 4/3/214 8,227. Tons 5/1/214 5/31/214 9,32 Tons 6/1/214 6/3/214 8,888. Tons 7/1/214 7/31/214 9,262. Tons 8/1/214 8/31/214 9,91. Tons 9/1/214 9/3/214 9,44 Tons 1/1/214 1/31/214 9,851. Tons 11/1/214 11/3/214 9,65. Tons 12/1/214 12/31/214 9,662. Tons 365 8,76 Total Throughput: 111,472. Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 2 GLASS MELT FURNACE / METAL GLASS DI/ESP Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: Boiler Desc: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; FLAT GLASS: MELTING FURNACE Diameter Criteria: Material Elevation NON CRITERIA SOURCE Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S2 EP STACK (PRIMARY) , /1/214

328 Wednesday, November Pennsylvania Department of Environmental Protection Page 51 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Combustion Unit: 2 GLASS MELT FURNACE / METAL GLASS DI/ESP Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 SOX Denotes Best Value for Pollutant B RATED FACTOR B RATED FACTOR B RATED FACTOR B RATED FACTOR B RATED FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR

329 Wednesday, November Pennsylvania Department of Environmental Protection Page 52 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Combustion Unit: 2 GLASS MELT FURNACE / METAL GLASS Criteria: NON CRITERIA SOURCE DI/ESP Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Cadmium Chromium Lead Selenium Nitrous Oxide PM-CON Cobalt Compounds Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP ,

330 Wednesday, November Pennsylvania Department of Environmental Protection Page 53 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Combustion Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Natural Gas Active. 1,5 Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/214 1/31/214.2 MMCF 2/1/214 2/28/214.2 MMCF 3/1/214 3/31/214.2 MMCF 4/1/214 4/3/214.2 MMCF 5/1/214 5/31/214.2 MMCF 6/1/214 6/3/214.2 MMCF 7/1/214 7/31/214.2 MMCF 8/1/214 8/31/214.2 MMCF 9/1/214 9/3/214.2 MMCF 1/1/214 1/31/214.2 MMCF 11/1/214 11/3/214.2 MMCF 12/1/214 12/31/214.2 MMCF 365 8,76 Total Throughput: 2.4 MMCF Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 3 CULLET PROCESSING / CULLET HEATING-NG Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: Boiler Desc: SCC-Number EXTERNAL COMBUSTION BOILERS ; INDUSTRIAL ; NATURAL GAS ; < 1 MILLION BTU/HR Diameter Criteria: Material Elevation NON CRITERIA SOURCE Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/214

331 Wednesday, November Pennsylvania Department of Environmental Protection Page 54 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Combustion Unit: 3 CULLET PROCESSING / CULLET HEATING-NG Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE FUEL TYPE: Natural Gas Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 SOX Methane Ammonia Carbon Dioxide Nitrous Oxide Denotes Best Value for Pollutant A RATED FACTOR A RATED FACTOR C RATED FACTOR A RATED FACTOR D RATED FACTOR A RATED FACTOR C RATED FACTOR A RATED FACTOR A RATED FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR

332 Wednesday, November Pennsylvania Department of Environmental Protection Page 55 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Combustion Unit: 3 CULLET PROCESSING / CULLET Criteria: NON CRITERIA SOURCE HEATING-NG Emission Data for Company Estimates SCC: FUEL TYPE: Natural Gas Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Hexane Denotes Best Value for Pollutant

333 Wednesday, November Pennsylvania Department of Environmental Protection Page 56 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Combustion Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Liquid Petroleum Gas (Lpg) Active. 91, Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/214 1/31/214.3 Th Gal 2/1/214 2/28/214.3 Th Gal 3/1/214 3/31/214.3 Th Gal 4/1/214 4/3/214.3 Th Gal 5/1/214 5/31/214.3 Th Gal 6/1/214 6/3/214.3 Th Gal 7/1/214 7/31/214.3 Th Gal 8/1/214 8/31/214.3 Th Gal 9/1/214 9/3/214.3 Th Gal 1/1/214 1/31/214.3 Th Gal 11/1/214 11/3/214.3 Th Gal 12/1/214 12/31/214.3 Th Gal 365 8,76 Total Throughput:.36 Th Gal Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 4 PROPANE HEATERS / PROPANE HEATERS Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: Boiler Desc: SCC-Number EXTERNAL COMBUSTION BOILERS ; INDUSTRIAL ; LIQUIFIED PETROLEUM GAS (LPG) ; PROPANE Diameter Criteria: Material Elevation NON CRITERIA SOURCE Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S4 MISC COMBUSTION /1/214

334 Wednesday, November Pennsylvania Department of Environmental Protection Page 57 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Combustion Unit: 4 PROPANE HEATERS / PROPANE HEATERS Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE FUEL TYPE: Liquid Petroleum Gas (Lpg) Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 Methane Carbon Dioxide Denotes Best Value for Pollutant C RATED FACTOR C RATED FACTOR C RATED FACTOR E RATED FACTOR A RATED FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR

335 Wednesday, November Pennsylvania Department of Environmental Protection Page 58 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Combustion Unit: 4 PROPANE HEATERS / PROPANE Criteria: NON CRITERIA SOURCE HEATERS Emission Data for Company Estimates SCC: FUEL TYPE: Liquid Petroleum Gas (Lpg) Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

336 Wednesday, November Pennsylvania Department of Environmental Protection Page 59 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Combustion Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Natural Gas Active. 1,5 Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/214 1/31/ MMCF 2/1/214 2/28/ MMCF 3/1/214 3/31/ MMCF 4/1/214 4/3/ MMCF 5/1/214 5/31/ MMCF 6/1/214 6/3/ MMCF 7/1/214 7/31/ MMCF 8/1/214 8/31/ MMCF 9/1/214 9/3/ MMCF 1/1/214 1/31/ MMCF 11/1/214 11/3/ MMCF 12/1/214 12/31/ MMCF 365 8,76 Total Throughput: 82.2 MMCF Average Thru/Hr.1 Exhaust Details ACFM: Stack Data Stack Id Name 31 SPACE/WATER HEATERS, NG / SPACE/WATER HEATERS, NG Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: Boiler Desc: SCC-Number EXTERNAL COMBUSTION BOILERS ; INDUSTRIAL ; NATURAL GAS ; < 1 MILLION BTU/HR Diameter Criteria: Material Elevation NON CRITERIA SOURCE Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S4 MISC COMBUSTION /1/214

337 Wednesday, November Pennsylvania Department of Environmental Protection Page 6 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Combustion Unit: 31 SPACE/WATER HEATERS, NG / SPACE/WATER HEATERS, NG Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE FUEL TYPE: Natural Gas Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 SOX Methane Ammonia Carbon Dioxide Nitrous Oxide Denotes Best Value for Pollutant A RATED FACTOR A RATED FACTOR C RATED FACTOR A RATED FACTOR D RATED FACTOR A RATED FACTOR C RATED FACTOR A RATED FACTOR A RATED FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR , , , ,

338 Wednesday, November Pennsylvania Department of Environmental Protection Page 61 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 214 Firm/Plant Code: Primary Facility ID: Combustion Unit: 31 SPACE/WATER HEATERS, NG / Criteria: NON CRITERIA SOURCE SPACE/WATER HEATERS, NG Emission Data for Company Estimates SCC: FUEL TYPE: Natural Gas Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Hexane Denotes Best Value for Pollutant AP-42 LATEST AVAILABLE ,

339 Wednesday, November Pennsylvania Department of Environmental Protection Page 1 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Region: 7 SIC Code: Site Totals (Best Controlled) Criteria/Non-Criteria(Totals) District: 71 County: 2 Allegheny Municipality: 2826 Jefferson Hills Boro AFS-Id Number: CDS-Id Number: Date Totals Last Completed: 6/3/214 Contact Type Location Address Firm Plant Contact Responsible Official Contact Site Location Information 3211 Manufacturing - Flat Glass Street Address 1 Glass House Rd 1 Glass House Rd 1 Glass House Rd City State Zip Contact Name Phone Number Jefferson Hills Jefferson Hills Jefferson Hills NAICS Code: PA PA PA Flat Glass Manufacturing Gregg Eckstein John Buckner Map: Latitude: 4 deg, 15 min, 2 sec N UTM : Zone: 17 North: Elevation(Ft): Longitude: -79 deg, 54 min, 57. sec W East: CO: LEAD: : PM1: PM25: SOX: : Criteria/Hazardous: Non-Criteria: Total Stacks: 6 Site Comment Processes 22 Combustion Units 5 Incinerators Control Devices 1 NESHAPS: NSPS: PSD: Fuel Material Location Data

340 Wednesday, November Pennsylvania Department of Environmental Protection Page 2 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,92 1/1/213 1/31/213 7,651. Tons 2/1/213 2/28/213 6,626. Tons 3/1/213 3/31/213 6,476. Tons 4/1/213 4/3/213 6,725. Tons 5/1/213 5/31/213 7,456. Tons 6/1/213 6/3/213 7,4 Tons 7/1/213 7/31/213 7,21. Tons 8/1/213 8/31/213 6,338. Tons 9/1/213 9/3/213 6,22 Tons 1/1/213 1/31/213 6,63 Tons 11/1/213 11/3/213 5,666. Tons 12/1/213 12/31/213 6,5 Tons 365 2,92 Total Throughput: 8,529. Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 11 RAW MATERIAL RECEIVING / HANDLING Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; RAW MATERIAL HANDLING (ALL TYPES OF GLASS) Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/213

341 Wednesday, November Pennsylvania Department of Environmental Protection Page 3 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 11 RAW MATERIAL RECEIVING / HANDLING Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

342 Wednesday, November Pennsylvania Department of Environmental Protection Page 4 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/213 1/31/ Tons 2/1/213 2/28/ Tons 3/1/213 3/31/ Tons 4/1/213 4/3/ Tons 5/1/213 5/31/ Tons 6/1/213 6/3/ Tons 7/1/213 7/31/ Tons 8/1/213 8/31/ Tons 9/1/213 9/3/ Tons 1/1/213 1/31/ Tons 11/1/213 11/3/ Tons 12/1/213 12/31/ Tons 365 8,76 Total Throughput: Tons Average Thru/Hr.4 Exhaust Details ACFM: Stack Data Stack Id Name 12 RAW MATERIAL RECEIVING / HANDLING (HYDRATED LIME) Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; RAW MATERIAL HANDLING (ALL TYPES OF GLASS) Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/213

343 Wednesday, November Pennsylvania Department of Environmental Protection Page 5 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 12 RAW MATERIAL RECEIVING / HANDLING (HYDRATED LIME) Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

344 Wednesday, November Pennsylvania Department of Environmental Protection Page 6 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/213 1/31/ Tons 2/1/213 2/28/ Tons 3/1/213 3/31/ Tons 4/1/213 4/3/ Tons 5/1/213 5/31/ Tons 6/1/213 6/3/ Tons 7/1/213 7/31/ Tons 8/1/213 8/31/ Tons 9/1/213 9/3/ Tons 1/1/213 1/31/ Tons 11/1/213 11/3/ Tons 12/1/213 12/31/ Tons 365 8,76 Total Throughput: Tons Average Thru/Hr.4 Exhaust Details ACFM: Stack Data Stack Id Name 13 RAW MATERIAL RECEIVING / HANDLING (RECIRC LIME) Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; RAW MATERIAL HANDLING (ALL TYPES OF GLASS) Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/213

345 Wednesday, November Pennsylvania Department of Environmental Protection Page 7 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 13 RAW MATERIAL RECEIVING / HANDLING (RECIRC LIME) Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

346 Wednesday, November Pennsylvania Department of Environmental Protection Page 8 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/213 1/31/213. Tons 2/1/213 2/28/213. Tons 3/1/213 3/31/213. Tons 4/1/213 4/3/213. Tons 5/1/213 5/31/213. Tons 6/1/213 6/3/213. Tons 7/1/213 7/31/213. Tons 8/1/213 8/31/213. Tons 9/1/213 9/3/213. Tons 1/1/213 1/31/213. Tons 11/1/213 11/3/213. Tons 12/1/213 12/31/213. Tons 1 Total Throughput:. Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 14 GLASS MELT FURNACE / NON-METAL GLASS DI/ESP Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; FLAT GLASS: MELTING FURNACE Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S2 EP STACK (PRIMARY) , /1/213

347 Wednesday, November Pennsylvania Department of Environmental Protection Page 9 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 14 GLASS MELT FURNACE / NON-METAL GLASS DI/ESP Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Cobalt Compounds Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP

348 Wednesday, November Pennsylvania Department of Environmental Protection Page 1 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/213 1/31/213. Tons 2/1/213 2/28/213. Tons 3/1/213 3/31/213. Tons 4/1/213 4/3/213. Tons 5/1/213 5/31/213. Tons 6/1/213 6/3/213. Tons 7/1/213 7/31/213. Tons 8/1/213 8/31/213. Tons 9/1/213 9/3/213. Tons 1/1/213 1/31/213. Tons 11/1/213 11/3/213. Tons 12/1/213 12/31/213. Tons 1 Total Throughput:. Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 15 GLASS MELT FURNACE / NON-METAL NO DI/ESP Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; FLAT GLASS: MELTING FURNACE Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S1 FURNACE EJECTOR STACK , /1/213

349 Wednesday, November Pennsylvania Department of Environmental Protection Page 11 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 15 GLASS MELT FURNACE / NON-METAL NO DI/ESP Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Cobalt Compounds Denotes Best Value for Pollutant

350 Wednesday, November Pennsylvania Department of Environmental Protection Page 12 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput /1/213 1/31/213. Tons 2/1/213 2/28/213. Tons 3/1/213 3/31/ Tons 4/1/213 4/3/ Tons 5/1/213 5/31/213. Tons 6/1/213 6/3/ Tons 7/1/213 7/31/213. Tons 8/1/213 8/31/213.2 Tons 9/1/213 9/3/ Tons 1/1/213 1/31/213. Tons 11/1/213 11/3/213. Tons 12/1/213 12/31/213. Tons 3 52 Total Throughput: 43.5 Tons Average Thru/Hr.83 Exhaust Details ACFM: Stack Data Stack Id Name 16 GLASS MELT FURNACE / METAL GLASS NO DI/ESP Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; FLAT GLASS: MELTING FURNACE Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S1 FURNACE EJECTOR STACK , /1/213

351 Wednesday, November Pennsylvania Department of Environmental Protection Page 13 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 16 GLASS MELT FURNACE / METAL GLASS NO DI/ESP Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 SOX Denotes Best Value for Pollutant B RATED FACTOR B RATED FACTOR B RATED FACTOR B RATED FACTOR B RATED FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR

352 Wednesday, November Pennsylvania Department of Environmental Protection Page 14 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 16 GLASS MELT FURNACE / METAL GLASS Criteria: NON CRITERIA SOURCE NO DI/ESP Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Cadmium Chromium Lead Selenium Nitrous Oxide PM-CON Cobalt Compounds Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP

353 Wednesday, November Pennsylvania Department of Environmental Protection Page 15 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/213 1/31/213. Tons 2/1/213 2/28/213. Tons 3/1/213 3/31/213. Tons 4/1/213 4/3/213. Tons 5/1/213 5/31/213. Tons 6/1/213 6/3/213. Tons 7/1/213 7/31/213. Tons 8/1/213 8/31/213. Tons 9/1/213 9/3/213. Tons 1/1/213 1/31/213. Tons 11/1/213 11/3/213. Tons 12/1/213 12/31/213. Tons 1 Total Throughput:. Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 17 GLASS MELT FURNACE / NON-METAL (ESP ONLY OPR) Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; FLAT GLASS: MELTING FURNACE Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S2 EP STACK (PRIMARY) , /1/213

354 Wednesday, November Pennsylvania Department of Environmental Protection Page 16 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 17 GLASS MELT FURNACE / NON-METAL (ESP ONLY OPR) Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP

355 Wednesday, November Pennsylvania Department of Environmental Protection Page 17 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput /1/213 1/31/213. Tons 2/1/213 2/28/213. Tons 3/1/213 3/31/213. Tons 4/1/213 4/3/213. Tons 5/1/213 5/31/213. Tons 6/1/213 6/3/ Tons 7/1/213 7/31/ Tons 8/1/213 8/31/213.2 Tons 9/1/213 9/3/ Tons 1/1/213 1/31/213. Tons 11/1/213 11/3/213. Tons 12/1/213 12/31/213. Tons Total Throughput: Tons Average Thru/Hr.5 Exhaust Details ACFM: Control Equipment Details 18 GLASS MELT FURNACE / METAL GLASS (ESP ONLY OPR Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr Category: SCC-Number Criteria: Material NON CRITERIA SOURCE INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; FLAT GLASS: MELTING FURNACE SCFM: % Moist: Temp-F: ID CD-1 Name Date Installed Type Code Pressure Drop METAL GLASS DI/ESP 41 Discharges To S2

356 Wednesday, November Pennsylvania Department of Environmental Protection Page 18 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 18 GLASS MELT FURNACE / METAL GLASS (ESP ONLY OPR Control Equipment Details Criteria: NON CRITERIA SOURCE ID Name Pollutant Control Pollutant PM1 Particulate Matter < 1 Microns PM25 Particulate Matter < 2.5 Microns Date Installed EFF(%) Type Code EFF Code A A Pressure Drop Discharges To EFF Description Rated efficiency: guaranteed minimum Rated efficiency: guaranteed minimum Stack Data Stack Id Name Source Totals (Best Controlled) Emission Data for SCC Factors SCC: Height Diameter Elevation Exhaust SCFM Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Temp (F) Moist (%) Flow (%) Flow Start Date S2 EP STACK (PRIMARY) , /1/213 CO PM1 SOX CO PM1 PM25 SOX Denotes Best Value for Pollutant Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds B RATED FACTOR B RATED FACTOR B RATED FACTOR B RATED FACTOR B RATED FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR

357 Wednesday, November Pennsylvania Department of Environmental Protection Page 19 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 18 GLASS MELT FURNACE / METAL GLASS Criteria: NON CRITERIA SOURCE (ESP ONLY OPR Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Cadmium Chromium Lead Selenium Nitrous Oxide PM-CON Cobalt Compounds Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP

358 Wednesday, November Pennsylvania Department of Environmental Protection Page 2 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/213 1/31/213 2,282. Tons 2/1/213 2/28/213 2,46 Tons 3/1/213 3/31/213 2,133. Tons 4/1/213 4/3/213 1,92 Tons 5/1/213 5/31/213 2,25 Tons 6/1/213 6/3/213 2,126. Tons 7/1/213 7/31/213 6,454. Tons 8/1/213 8/31/213 6,598. Tons 9/1/213 9/3/213 3,155. Tons 1/1/213 1/31/213 1,976. Tons 11/1/213 11/3/213 2,89 Tons 12/1/213 12/31/213 2,361. Tons 365 8,76 Total Throughput: 36,65. Tons Average Thru/Hr 4.18 Exhaust Details ACFM: Stack Data Stack Id Name 19 CULLET PROCESSING / CULLET CRUSHING Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; CULLET: CRUSHING/GRINDING Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/213

359 Wednesday, November Pennsylvania Department of Environmental Protection Page 21 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 19 CULLET PROCESSING / CULLET CRUSHING Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant AP-42 LATEST AVAILABLE AP-42 LATEST AVAILABLE

360 Wednesday, November Pennsylvania Department of Environmental Protection Page 22 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/213 1/31/213 4,868. Tons 2/1/213 2/28/213 4,2. Tons 3/1/213 3/31/213 4,34 Tons 4/1/213 4/3/213 4,288. Tons 5/1/213 5/31/213 4,153. Tons 6/1/213 6/3/213 3,646. Tons 7/1/213 7/31/213 3,76. Tons 8/1/213 8/31/213 4,67. Tons 9/1/213 9/3/213 3,917. Tons 1/1/213 1/31/213 3,938. Tons 11/1/213 11/3/213 3,58 Tons 12/1/213 12/31/213 4,44. Tons 365 8,76 Total Throughput: 48,549. Tons Average Thru/Hr 5.54 Exhaust Details ACFM: Stack Data Stack Id Name 11 CULLET PROCESSING / CULLET HANDLING Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; RAW MATERIAL HANDLING (ALL TYPES OF GLASS) Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/213

361 Wednesday, November Pennsylvania Department of Environmental Protection Page 23 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 11 CULLET PROCESSING / CULLET HANDLING Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP

362 Wednesday, November Pennsylvania Department of Environmental Protection Page 24 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Exhaust Details ACFM: Stack Data Stack Id Name Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/213 1/31/213 4,868. 2/1/213 2/28/213 4,2. 3/1/213 3/31/213 4,34 4/1/213 4/3/213 4,288. 5/1/213 5/31/213 4,153. 6/1/213 6/3/213 3,646. 7/1/213 7/31/213 3,76. 8/1/213 8/31/213 4,67. 9/1/213 9/3/213 3,917. 1/1/213 1/31/213 3, /1/213 11/3/213 3,58 12/1/213 12/31/213 4, ,76 Total Throughput: 48,549. Average Thru/Hr CULLET PROCESSING / CULLET PADS Criteria: Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; CULLET: CRUSHING/GRINDING Diameter Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/213 Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons

363 Wednesday, November Pennsylvania Department of Environmental Protection Page 25 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 111 CULLET PROCESSING / CULLET PADS Criteria: Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant AP-42 LATEST AVAILABLE AP-42 LATEST AVAILABLE

364 Wednesday, November Pennsylvania Department of Environmental Protection Page 26 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type PETROL./SOLVENT EVAPOR. ; PETRO-PROD. STORAGE (REFINERY) Exhaust Details ACFM: Stack Data Stack Id Name Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/213 1/31/213. 2/1/213 2/28/213. 3/1/213 3/31/213. 4/1/213 4/3/213. 5/1/213 5/31/213. 6/1/213 6/3/213. 7/1/213 7/31/213. 8/1/213 8/31/213. 9/1/213 9/3/213. 1/1/213 1/31/ /1/213 11/3/ /1/213 12/31/ Total Throughput:. Average Thru/Hr 112 STORAGE TANKS / STORAGE TANKS Criteria: Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number PETROL./SOLVENT EVAPOR. ; PETRO-PROD. STORAGE (REFINERY) ; VARIABLE VAPOR SPACE ; SPECIFY LIQUID: FILLING LOSS Diameter Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/213 Gal Gal Gal Gal Gal Gal Gal Gal Gal Gal Gal Gal Th Gal

365 Wednesday, November Pennsylvania Department of Environmental Protection Page 27 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 112 STORAGE TANKS / STORAGE TANKS Criteria: Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

366 Wednesday, November Pennsylvania Department of Environmental Protection Page 28 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Industrial Processes; Electrical Equipment; Light Bulb Manuf Exhaust Details ACFM: Stack Data Stack Id Name Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/213 1/31/213 4,75 2/1/213 2/28/213 3,75 3/1/213 3/31/213 4,25 4/1/213 4/3/213 4,75 5/1/213 5/31/213 2,25 6/1/213 6/3/213 3, 7/1/213 7/31/213 2,25 8/1/213 8/31/213 1,5 9/1/213 9/3/213 1,75 1/1/213 1/31/ /1/213 11/3/ /1/213 12/31/213 2, ,76 Total Throughput: 31,5 Average Thru/Hr GLASS/ROLL COATING / GLASS/ROLL COATING SO2 Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number Industrial Processes; Electrical Equipment; Light Bulb Manufacture; Light Bulb Glass to Socket Base Lubrication with SO2 Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/213 Lbs Lbs Lbs Lbs Lbs Lbs Lbs Lbs Lbs Lbs Lbs Lbs Lbs

367 Wednesday, November Pennsylvania Department of Environmental Protection Page 29 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 113 GLASS/ROLL COATING / GLASS/ROLL COATING SO2 Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant CO. MATERIAL BALANCE

368 Wednesday, November Pennsylvania Department of Environmental Protection Page 3 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type PETROL./SOLVENT EVAPOR. ; SURFACE COATING OPERATIONS ; S Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput /1/213 1/31/ Gal 2/1/213 2/28/213. Gal 3/1/213 3/31/ Gal 4/1/213 4/3/ Gal 5/1/213 5/31/213. Gal 6/1/213 6/3/213. Gal 7/1/213 7/31/ Gal 8/1/213 8/31/ Gal 9/1/213 9/3/ Gal 1/1/213 1/31/213. Gal 11/1/213 11/3/213. Gal 12/1/213 12/31/ Gal Total Throughput: 74.5 Gal Average Thru/Hr.5 Exhaust Details ACFM: Stack Data Stack Id Name 114 PAINTING ACTIVITIES / PAINTING ACTIVITIES Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number PETROL./SOLVENT EVAPOR. ; SURFACE COATING OPERATIONS ; SURFACE COATING APPLICATION - GENERAL ; PAINT: SOLVENT-BASE Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/213

369 Wednesday, November Pennsylvania Department of Environmental Protection Page 31 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 114 PAINTING ACTIVITIES / PAINTING ACTIVITIES Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year U UNRATED FACTOR EPA SCC FACTOR Denotes Best Value for Pollutant CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant CO. MATERIAL BALANCE

370 Wednesday, November Pennsylvania Department of Environmental Protection Page 32 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Industrial Processes; Mineral Products; Asphalt Concrete; Tr Exhaust Details ACFM: Stack Data Stack Id Name Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/213 1/31/213. 2/1/213 2/28/213. 3/1/213 3/31/213. 4/1/213 4/3/213. 5/1/213 5/31/213. 6/1/213 6/3/213. 7/1/213 7/31/213. 8/1/213 8/31/213. 9/1/213 9/3/213. 1/1/213 1/31/ /1/213 11/3/ /1/213 12/31/ Total Throughput:. Average Thru/Hr 115 ASPHALT DRIVEWAY SEALER / ASPHALT DRIVEWAY SEALER Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number Industrial Processes; Mineral Products; Asphalt Concrete; Truck Load-out Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/213 Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons Tons

371 Wednesday, November Pennsylvania Department of Environmental Protection Page 33 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 115 ASPHALT DRIVEWAY SEALER / ASPHALT DRIVEWAY SEALER Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

372 Wednesday, November Pennsylvania Department of Environmental Protection Page 34 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Propane Active. 2,516 Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/213 1/31/213. 2/1/213 2/28/213. 3/1/213 3/31/213. 4/1/213 4/3/213. 5/1/213 5/31/213. 6/1/213 6/3/213. 7/1/213 7/31/213. 8/1/213 8/31/213. 9/1/213 9/3/213. 1/1/213 1/31/ /1/213 11/3/ /1/213 12/31/ Total Throughput:. Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 116 FORK TRUCK, PROPANE / FORK TRUCK, PROPANE Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INTERNAL COMBUSTION ENGINES ; COMMERCIAL/INSTITUTIONAL ; LIQUIFIED PETROLEUM GAS (LPG) ; PROPANE: RECIPROCATING Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S6 ROAD FUGITIVES /1/213 Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal

373 Wednesday, November Pennsylvania Department of Environmental Protection Page 35 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 116 FORK TRUCK, PROPANE / FORK TRUCK, PROPANE Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE FUEL TYPE: Propane Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: FUEL TYPE: Propane Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

374 Wednesday, November Pennsylvania Department of Environmental Protection Page 36 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type PETROL./SOLVENT EVAPOR. ; SURFACE COATING OPERATIONS ; T Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/213 1/31/ Tons 2/1/213 2/28/ Tons 3/1/213 3/31/ Tons 4/1/213 4/3/ Tons 5/1/213 5/31/ Tons 6/1/213 6/3/ Tons 7/1/213 7/31/ Tons 8/1/213 8/31/213.7 Tons 9/1/213 9/3/ Tons 1/1/213 1/31/ Tons 11/1/213 11/3/ Tons 12/1/213 12/31/ Tons 365 8,76 Total Throughput: 1.27 Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 117 GLASS CUTTING/PACKAGING / CUTTING GLASS(SOLVENT) Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number PETROL./SOLVENT EVAPOR. ; SURFACE COATING OPERATIONS ; THINNING SOLVENTS - GENERAL ; MINERAL SPIRITS Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/213

375 Wednesday, November Pennsylvania Department of Environmental Protection Page 37 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 117 GLASS CUTTING/PACKAGING / CUTTING GLASS(SOLVENT) Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year E RATED FACTOR EPA SCC FACTOR Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant CO. MATERIAL BALANCE 1.274

376 Wednesday, November Pennsylvania Department of Environmental Protection Page 38 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; FUGITIVE EMISS Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/213 1/31/ Tons 2/1/213 2/28/ Tons 3/1/213 3/31/ Tons 4/1/213 4/3/ Tons 5/1/213 5/31/ Tons 6/1/213 6/3/ Tons 7/1/213 7/31/ Tons 8/1/213 8/31/ Tons 9/1/213 9/3/ Tons 1/1/213 1/31/ Tons 11/1/213 11/3/ Tons 12/1/213 12/31/ Tons 365 8,76 Total Throughput: 4.44 Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 118 GLASS CUTTING/PACKAGING / G- CORE(GLASS SEPARATOR) Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; FUGITIVE EMISSIONS ; SPECIFY IN COMMENTS FIELD Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/213

377 Wednesday, November Pennsylvania Department of Environmental Protection Page 39 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 118 GLASS CUTTING/PACKAGING / G- CORE(GLASS SEPARATOR) Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

378 Wednesday, November Pennsylvania Department of Environmental Protection Page 4 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Diesel Fuel Active. 129,5 Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/213 1/31/213. 2/1/213 2/28/213. 3/1/213 3/31/213. 4/1/213 4/3/213. 5/1/213 5/31/213. 6/1/213 6/3/213. 7/1/213 7/31/213. 8/1/213 8/31/213. 9/1/213 9/3/213. 1/1/213 1/31/ /1/213 11/3/ /1/213 12/31/ Total Throughput:. Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 119 SITE DEDICATED VEHICLES / DUMP/PAYLOADER EXHAUST Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INTERNAL COMBUSTION ENGINES ; INDUSTRIAL ; DISTILLATE OIL (DIESEL) ; RECIPROCATING: EXHAUST Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S6 ROAD FUGITIVES /1/213 Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal Th Gal

379 Wednesday, November Pennsylvania Department of Environmental Protection Page 41 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 119 SITE DEDICATED VEHICLES / DUMP/PAYLOADER EXHAUST Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE FUEL TYPE: Diesel Fuel Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: FUEL TYPE: Diesel Fuel Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

380 Wednesday, November Pennsylvania Department of Environmental Protection Page 42 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; STONE QUARRYIN Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/213 1/31/ Miles 2/1/213 2/28/ Miles 3/1/213 3/31/ Miles 4/1/213 4/3/ Miles 5/1/213 5/31/ Miles 6/1/213 6/3/ Miles 7/1/213 7/31/ Miles 8/1/213 8/31/ Miles 9/1/213 9/3/ Miles 1/1/213 1/31/ Miles 11/1/213 11/3/ Miles 12/1/213 12/31/ Miles 365 8,76 Total Throughput: 4, Miles Average Thru/Hr.49 Exhaust Details ACFM: Stack Data Stack Id Name 12 SITE DEDICATED VEHICLES / PAVED ROADS Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; STONE QUARRYING - PROCESSING ; HAULING Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S6 ROAD FUGITIVES /1/213

381 Wednesday, November Pennsylvania Department of Environmental Protection Page 43 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 12 SITE DEDICATED VEHICLES / PAVED ROADS Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year PM1 U UNRATED FACTOR EPA SCC FACTOR Denotes Best Value for Pollutant CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

382 Wednesday, November Pennsylvania Department of Environmental Protection Page 44 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; STONE QUARRYIN Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/213 1/31/ Miles 2/1/213 2/28/ Miles 3/1/213 3/31/ Miles 4/1/213 4/3/ Miles 5/1/213 5/31/213.5 Miles 6/1/213 6/3/213.5 Miles 7/1/213 7/31/ Miles 8/1/213 8/31/213.5 Miles 9/1/213 9/3/213.5 Miles 1/1/213 1/31/ Miles 11/1/213 11/3/ Miles 12/1/213 12/31/ Miles 365 8,76 Total Throughput: 4. Miles Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 121 SITE DEDICATED VEHICLES / UNPAVED ROADS Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; STONE QUARRYING - PROCESSING ; HAULING Diameter Criteria: Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S6 ROAD FUGITIVES /1/213

383 Wednesday, November Pennsylvania Department of Environmental Protection Page 45 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 121 SITE DEDICATED VEHICLES / UNPAVED ROADS Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year PM1 U UNRATED FACTOR EPA SCC FACTOR Denotes Best Value for Pollutant CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

384 Wednesday, November Pennsylvania Department of Environmental Protection Page 46 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type PETROL./SOLVENT EVAPOR. ; SURFACE COATING OPERATIONS ; S Exhaust Details ACFM: Stack Data Stack Id Name Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/213 1/31/ /1/213 2/28/ /1/213 3/31/ /1/213 4/3/ /1/213 5/31/ /1/213 6/3/ /1/213 7/31/ /1/213 8/31/ /1/213 9/3/ /1/213 1/31/ /1/213 11/3/ /1/213 12/31/ ,76 Total Throughput: Average Thru/Hr RTV SEALANT / RTV SEALANT Criteria: Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: SCC-Number PETROL./SOLVENT EVAPOR. ; SURFACE COATING OPERATIONS ; SURFACE COATING APPLICATION - GENERAL ; PAINT: SOLVENT-BASE Diameter Material NON CRITERIA SOURCE Elevation Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S5 MISC FUGITIVES /1/213 Gal Gal Gal Gal Gal Gal Gal Gal Gal Gal Gal Gal Gal

385 Wednesday, November Pennsylvania Department of Environmental Protection Page 47 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Process Unit: 122 RTV SEALANT / RTV SEALANT Criteria: Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year U UNRATED FACTOR EPA SCC FACTOR Denotes Best Value for Pollutant CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant CO. MATERIAL BALANCE

386 Wednesday, November Pennsylvania Department of Environmental Protection Page 48 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Combustion Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Natural Gas Active. 1,5 Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput. 1 1/1/213 1/31/213. MMCF 2/1/213 2/28/213. MMCF 3/1/213 3/31/213. MMCF 4/1/213 4/3/213. MMCF 5/1/213 5/31/213. MMCF 6/1/213 6/3/213. MMCF 7/1/213 7/31/213. MMCF 8/1/213 8/31/213. MMCF 9/1/213 9/3/213. MMCF 1/1/213 1/31/213. MMCF 11/1/213 11/3/213. MMCF 12/1/213 12/31/213. MMCF 1 Total Throughput:. MMCF Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 1 RAW MATERIAL RECEIVING / BATCH WATER HEATER-NG Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: Boiler Desc: SCC-Number EXTERNAL COMBUSTION BOILERS ; INDUSTRIAL ; NATURAL GAS ; < 1 MILLION BTU/HR Diameter Criteria: Material Elevation NON CRITERIA SOURCE Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S4 MISC COMBUSTION /1/213

387 Wednesday, November Pennsylvania Department of Environmental Protection Page 49 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Combustion Unit: 1 RAW MATERIAL RECEIVING / BATCH WATER HEATER-NG Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE FUEL TYPE: Natural Gas Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year Denotes Best Value for Pollutant Emission Data for Company Estimates SCC: FUEL TYPE: Natural Gas Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Hexane Denotes Best Value for Pollutant AP-42 LATEST AVAILABLE CO. STACK TEST APPROVED BY DEP

388 Wednesday, November Pennsylvania Department of Environmental Protection Page 5 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Combustion Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACT Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/213 1/31/213 1,56.64 Tons 2/1/213 2/28/213 8, Tons 3/1/213 3/31/213 9, Tons 4/1/213 4/3/213 9,57.98 Tons 5/1/213 5/31/213 9,91.9 Tons 6/1/213 6/3/213 9, Tons 7/1/213 7/31/213 9, Tons 8/1/213 8/31/213 9,13.7 Tons 9/1/213 9/3/213 8,891.7 Tons 1/1/213 1/31/213 8,91.9 Tons 11/1/213 11/3/213 7,435.9 Tons 12/1/213 12/31/213 9, Tons 365 8,76 Total Throughput: 11,711.2 Tons Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 2 GLASS MELT FURNACE / METAL GLASS DI/ESP Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Active. Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: Boiler Desc: SCC-Number INDUSTRIAL PROCESSES ; MINERAL PRODUCTS ; GLASS MANUFACTURE ; FLAT GLASS: MELTING FURNACE Diameter Criteria: Material Elevation NON CRITERIA SOURCE Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S2 EP STACK (PRIMARY) , /1/213

389 Wednesday, November Pennsylvania Department of Environmental Protection Page 51 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Combustion Unit: 2 GLASS MELT FURNACE / METAL GLASS DI/ESP Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 SOX Denotes Best Value for Pollutant B RATED FACTOR B RATED FACTOR B RATED FACTOR B RATED FACTOR B RATED FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR

390 Wednesday, November Pennsylvania Department of Environmental Protection Page 52 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Combustion Unit: 2 GLASS MELT FURNACE / METAL GLASS Criteria: NON CRITERIA SOURCE DI/ESP Emission Data for Company Estimates SCC: Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Cadmium Chromium Lead Selenium Nitrous Oxide PM-CON Cobalt Compounds Denotes Best Value for Pollutant CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP CO. STACK TEST APPROVED BY DEP ,

391 Wednesday, November Pennsylvania Department of Environmental Protection Page 53 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Combustion Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Natural Gas Active. 1,5 Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/213 1/31/213.2 MMCF 2/1/213 2/28/213.2 MMCF 3/1/213 3/31/213.2 MMCF 4/1/213 4/3/213.2 MMCF 5/1/213 5/31/213.2 MMCF 6/1/213 6/3/213.2 MMCF 7/1/213 7/31/213.2 MMCF 8/1/213 8/31/213.2 MMCF 9/1/213 9/3/213.2 MMCF 1/1/213 1/31/213.2 MMCF 11/1/213 11/3/213.2 MMCF 12/1/213 12/31/213.2 MMCF 365 8,76 Total Throughput: 2.4 MMCF Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 3 CULLET PROCESSING / CULLET HEATING-NG Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: Boiler Desc: SCC-Number EXTERNAL COMBUSTION BOILERS ; INDUSTRIAL ; NATURAL GAS ; < 1 MILLION BTU/HR Diameter Criteria: Material Elevation NON CRITERIA SOURCE Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S3 MATERIAL HANDLING /1/213

392 Wednesday, November Pennsylvania Department of Environmental Protection Page 54 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Combustion Unit: 3 CULLET PROCESSING / CULLET HEATING-NG Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE FUEL TYPE: Natural Gas Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 SOX Methane Ammonia Carbon Dioxide Nitrous Oxide Denotes Best Value for Pollutant A RATED FACTOR A RATED FACTOR C RATED FACTOR A RATED FACTOR D RATED FACTOR A RATED FACTOR C RATED FACTOR A RATED FACTOR A RATED FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR

393 Wednesday, November Pennsylvania Department of Environmental Protection Page 55 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Combustion Unit: 3 CULLET PROCESSING / CULLET Criteria: NON CRITERIA SOURCE HEATING-NG Emission Data for Company Estimates SCC: FUEL TYPE: Natural Gas Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Hexane Denotes Best Value for Pollutant AP-42 LATEST AVAILABLE AP-42 LATEST AVAILABLE CO. STACK TEST APPROVED BY DEP

394 Wednesday, November Pennsylvania Department of Environmental Protection Page 56 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Combustion Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Liquid Petroleum Gas (Lpg) Active. 2,516 Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/213 1/31/213.3 Th Gal 2/1/213 2/28/213.3 Th Gal 3/1/213 3/31/213.3 Th Gal 4/1/213 4/3/213.3 Th Gal 5/1/213 5/31/213.3 Th Gal 6/1/213 6/3/213.3 Th Gal 7/1/213 7/31/213.3 Th Gal 8/1/213 8/31/213.3 Th Gal 9/1/213 9/3/213.3 Th Gal 1/1/213 1/31/213.3 Th Gal 11/1/213 11/3/213.3 Th Gal 12/1/213 12/31/213.3 Th Gal 365 8,76 Total Throughput:.36 Th Gal Average Thru/Hr Exhaust Details ACFM: Stack Data Stack Id Name 4 PROPANE HEATERS / PROPANE HEATERS Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: Boiler Desc: SCC-Number EXTERNAL COMBUSTION BOILERS ; INDUSTRIAL ; LIQUIFIED PETROLEUM GAS (LPG) ; PROPANE Diameter Criteria: Material Elevation NON CRITERIA SOURCE Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S4 MISC COMBUSTION /1/213

395 Wednesday, November Pennsylvania Department of Environmental Protection Page 57 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Combustion Unit: 4 PROPANE HEATERS / PROPANE HEATERS Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE FUEL TYPE: Liquid Petroleum Gas (Lpg) Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 Methane Carbon Dioxide Denotes Best Value for Pollutant C RATED FACTOR C RATED FACTOR C RATED FACTOR E RATED FACTOR A RATED FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR

396 Wednesday, November Pennsylvania Department of Environmental Protection Page 58 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Combustion Unit: 4 PROPANE HEATERS / PROPANE Criteria: NON CRITERIA SOURCE HEATERS Emission Data for Company Estimates SCC: FUEL TYPE: Liquid Petroleum Gas (Lpg) Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Denotes Best Value for Pollutant

397 Wednesday, November Pennsylvania Department of Environmental Protection Page 59 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Combustion Unit: Rated Input (MMBTU/HR): Rated Output (MW): Sub Facility SCC Details Fuel Type Code NEDS SCC SCC Status Material Processed %Sulfur %Ash BTU Content Natural Gas Active. 1,5 Hours Operated and Periodic Throughput HR/Day Days/Year Total Hrs Start Date End Date Throughput ,76 1/1/213 1/31/ MMCF 2/1/213 2/28/ MMCF 3/1/213 3/31/ MMCF 4/1/213 4/3/ MMCF 5/1/213 5/31/ MMCF 6/1/213 6/3/ MMCF 7/1/213 7/31/ MMCF 8/1/213 8/31/ MMCF 9/1/213 9/3/ MMCF 1/1/213 1/31/ MMCF 11/1/213 11/3/ MMCF 12/1/213 12/31/ MMCF 365 8,76 Total Throughput: MMCF Average Thru/Hr.1 Exhaust Details ACFM: Stack Data Stack Id Name 31 SPACE/WATER HEATERS, NG / SPACE/WATER HEATERS, NG Maximum Thru/Hr SCFM: % Moist: Temp-F: Height Category: Boiler Desc: SCC-Number EXTERNAL COMBUSTION BOILERS ; INDUSTRIAL ; NATURAL GAS ; < 1 MILLION BTU/HR Diameter Criteria: Material Elevation NON CRITERIA SOURCE Exhaust SCFM Temp (F) Moist (%) Flow (%) Flow Start Date S4 MISC COMBUSTION /1/213

398 Wednesday, November Pennsylvania Department of Environmental Protection Page 6 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Combustion Unit: 31 SPACE/WATER HEATERS, NG / SPACE/WATER HEATERS, NG Source Totals (Best Controlled) Emission Data for SCC Factors SCC: CO PM1 PM25 SOX Carbon Monoxide Nitrogen Oxides Particulate Matter < 1 Microns Particulate Matter < 2.5 Microns Sulfur Oxides Volatile Organic Compounds Criteria: NON CRITERIA SOURCE FUEL TYPE: Natural Gas Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 SOX Methane Ammonia Carbon Dioxide Nitrous Oxide Denotes Best Value for Pollutant A RATED FACTOR A RATED FACTOR C RATED FACTOR A RATED FACTOR D RATED FACTOR A RATED FACTOR C RATED FACTOR A RATED FACTOR A RATED FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR EPA SCC FACTOR , , , ,

399 Wednesday, November Pennsylvania Department of Environmental Protection Page 61 Bureau of Air Quality Firm/Plant Report Firm/Plant Name: GUARDIAN IND CORP/JEFFERSON HILLS Emission Year: 213 Firm/Plant Code: Primary Facility ID: Combustion Unit: 31 SPACE/WATER HEATERS, NG / Criteria: NON CRITERIA SOURCE SPACE/WATER HEATERS, NG Emission Data for Company Estimates SCC: FUEL TYPE: Natural Gas Controlled Uncontrolled Pollutant Reliability Basis Lbs/Hr Tons/Year Lbs/Hr Tons/Year CO PM1 PM2.5 SOX Methane Ammonia Carbon Dioxide Lead Nitrous Oxide PM-CON Hexane Denotes Best Value for Pollutant AP-42 LATEST AVAILABLE AP-42 LATEST AVAILABLE CO. STACK TEST APPROVED BY DEP DEP EFFICIENCY OF CONTROL DEVICE CO. STACK TEST APPROVED BY DEP

400 APPENDIX G to ACHD Non-Interference Demonstration is Appendix G to PA DEP NID as follows:

401 APPENDIX G 214/218/223 Inventory Bureau of Air Quality Department of Environmental Protection

402 Technical Appendix G - 214/218/223 Inventory Documentation Summary of Emissions Inventory and Projections for Noninterference Demonstration 214 NEI v1 Summary State / County Data NOx (tpy) (tpy) FIPS State County Fires Nonpoint Nonroad Onroad Point Total Fires Nonpoint Nonroad Onroad Point Total 423 PA Allegheny 4 9,68 3,183 11,754 13,715 37, ,831 2,914 6,422 1,524 26, PA Armstrong 4 1, ,498 2, , , PA Beaver 4 2, ,934 2,166 24, , , , PA Butler 7 1, ,12 1,32 6, , , , PA Fayette 6 2, , , , , PA Washington 4 4, , , , , , PA Westmoreland 2 4, ,43 1,428 12, ,653 1,388 2, ,138 TOTAL 31 26,569 6,472 28,142 54, , ,816 7,221 14,134 4,11 88, Total (no fires) (tpy) 115, Total (no fires)(tpy) 88,272 Source: Filename: 214 v1 NEi emissions summaries without biogenics (excel spreadsheet) 218 (tons per year) 223 (tons per year) Sector Allegheny Armstrong Beaver Butler Fayette Washington Westmoreland 218 Total Allegheny Armstrong Beaver Butler Fayette Washington Westmoreland 223 Total AREA 1,954 3,995 1,573 3,42 3,919 4,837 6,97 34,416 1,413 4,25 1,525 3,36 3,828 4,88 6,13 34,16 NONROAD 2, ,241 6,424 2, ,158 5,981 ONROAD 3, ,24 7,567 2, ,578 POINT 1, ,985 1, ,4 EGU POINT 1, (nonegu) 3,867 1, ,784 Small EGU Grand Total (tpy) 18,888 4,849 3,123 5,82 5,133 6,164 9,152 52,392 17,63 4,99 2,856 4,789 4,811 6,126 8,881 49, NOx (tons per year) 223 NOx (tons per year) Sector Allegheny Armstrong Beaver Butler Fayette Washington Westmoreland 218 Total Allegheny Armstrong Beaver Butler Fayette Washington Westmoreland 223 Total AREA 4,567 6, ,479 3,715 4,336 6,41 28,5 4,37 6, ,251 3,145 3,121 5,51 24,16 NONROAD 2, ,956 1, ,73 ONROAD 5, , ,397 2,51 12,753 3, ,327 8,147 POINT 12,82 12,75 15,48 1, ,716 44,26 1,698 6,961 13,73 1, ,11 33,813 EGU 3,692 12,13 13, ,976 2,44 6,583 1, ,972 POINT 8, ,736 1, ,716 (nonegu) 14,319 8, ,672 1, ,46 13,111 Small EGU Grand Total (tpy) 24,758 2,421 17,227 4,439 5,155 6,892 1,894 89,786 2,632 13,654 14,41 3,571 4,254 5,62 8,555 7,139 Table 9 -Summary of 214 NEI and MARAMA 218 and 223 Projected NOx and Inventory by Sector (pg 21) Page 1

403 Technical Appendix G - 214/218/223 Inventory Documentation MARAMA Inventory Files for 218 and 223 Source: Emissions Modeling Framework (EMF) v 2.12 MARAMA 218 alpha inventory MARAMA 223 gamma inventory MARAMA_Alpha_218_ag_211NEIv2_NONPOINT_214118_11nov214_v_csv_v_14jan215_nf_v1 MARAMA_Alpha_218_refueling_211NEIv2_NONPOINT_214118_11nov214_v_csv_v_21jan215_nf_v1 MARAMA_Alpha_218_rwc_211NEIv2_NONPOINT_214118_11nov214_v_csv_v_21jan215_nf_v1 MARAMA_Alpha_218_afdust_211NEIv2_NONPOINT_214118_11nov214_v1 MARAMA_Alpha_218_agburn_monthly_211NEIv2_NONPOINT_214118_11nov214_v_csv_v_2jan215_nf_v1 MARAMA_Alpha_218_nonpt_211NEIv2_NONPOINT_214118_11nov214_v1_csv_v_21jan215_nf_v1 MARAMA_Alpha_218_np_oilgas_211NEIv2_NONPOINT_214118_11nov214_v_csv_v_21jan215_nf_v1 MARAMA_Alpha_218_pfc_211NEIv2_NONPOINT_214118_11nov214_v_csv_21jan215_nf_v1 AREA el_ag_MARAMA_211NEIv2_NONPOINT_214118_7sep216_v 223_NONPOINT_nonpt_12may el_MARAMA_from_afdust_211NEIv2_NONPOINT_214118_19sep216_v1 223el_MARAMA_from_EPA_211_afdust_no_precipadj_paved_unpaved_noNEIv2RPOstates_19sep216_v1 223el_MARAMA_from_refueling_211NEIv2_NONPOINT_214118_mar_13sep216_v1 MARAMA_223_from_pfc_211NEIv2_NONPOINT_214118_11nov214_v_14sep216_v 223el_rwc_MARAMA_211NEIv2_NONPOINT_214118_7sep216_v 223el_MARAMA_np_oilgas_211NEIv2_NONPOINT_214118_mar_14sep216_v1_MDPAVAWV 223en_np_oilgas_211NEIv2_NONPOINT_7aug217_v1 agburn_monthly_211neiv2_nonpoint_3dec215_v _nonroad_213829_3oct213_v2.csv NONROAD el_nonroad_ff1_NCD216627_5oct216_v3_part1 223el_nonroad_ff1_NCD216627_5oct216_v3_part eh_onroad_SMOKE_MOVES_MOVES214_no_speciated_pm_MARAMA ONROAD 223 MOVES214a_ONROAD_EPA223el_FF1 218 EGU OTC_218_ERTACEGUv23_15227_MENHVTMARICTNYNJDEPAMDDCVA.csv MARAMA_Alpha_218_MARAMA_Alpha_ptnonipm_211NEIv2_POINT_214913_revised_21417_8oct214_nf_v1_csv_23oct2 14_v_mar_v_1feb215_nf_v1 MARAMA_Alpha_218_othpt_offshore_oil_211NEIv2_POINT_214913_16sep214_v_csv_v_1feb215_v Point (nonipm) MARAMA_Alpha_218_pt_oilgas_211NEIv2_POINT_214913_17oct214_v2_csv_v_1feb215_nf_v1 MARAMA_Alpha_218_refueling_refueling_211NEIv2_POINT_214913_23sep214_v_csv_v_2feb215_nf_v1 MARAMA_Alpha_218_Ethanol_plants_211_OTAQ_17oct214_v6_csv_6nov214_v_v_1feb215_nf_v1 Biodiesel_Plants_218_ff1_11apr213_v Small EGU 217_POINT_PTNONERTAC_IPM_2jun216 POINT 223 EGU OTC_223_ERTACEGUv27_217918_MENHVTMARICTNYNJDEPAMDDCVA 223_POINT_PTNONIPM_29may217 othpt_offshore_oil_211neiv2_point_214913_16sep214_v.csv 223el_MARAMA_from_refueling_211NEIv2_POINT_214913_15sep216_v1 Biodiesel_Plants_218_ff1_11apr213_v.csv Point (nonipm) 223_MARAMA_new_sources_2jun _MARAMA_PT_offsets_217_4_25 223el_from_ethanol_plants_211NEIv2_POINT_ _2sep216_v 223en_MARAMA_pt_oilgas_211NEIv2_POINT_21aug217_v 223en_pt_oilgas_211NEIv2_POINT_21aug217_v2 Small EGU 22_POINT_PTNONERTAC_IPM_xxdec217 Page 2

404 APPENDIX H to ACHD Non-Interference Demonstration is Appendix H to PA DEP NID as follows:

405 APPENDIX H 223 Attainment Modeling Bureau of Air Quality Department of Environmental Protection