ESTCP Research on Optimization of Vapor Intrusion Mitigation Systems in Large Military Buildings

Similar documents
Empirical Data: Challenges and Future Directions

Lessons from Petroleum Hydrocarbon and Chlorinated Solvent Sites Extensively Monitored for Vapor Intrusion

An Integrated Model for Design of Soil Vapour Intrusion Mitigation Systems

New Models to Support Vapor Intrusion Mitigation Design

Case Studies of Innovative Use of Tracers, Indicators and Field GC/MS for Assessing the Vapor Intrusion Pathway

Examples of Data Collection Strategies and Methods

Presenter Bios. Finding Practical Solutions for the Chlorinated Vapor Intrusion Pathway: Helping RCRA Facilities Meet Significant Challenges

Updated J&E Model VIAModel.xls

Case Study of Modeled and Observed TCE Attenuation from Groundwater to Indoor Air. Christopher G. Lawless Johnson Wright, Inc.

Installation of Liquid Boot a spray applied membrane to reduce vapor intrusion of chlorinated solvents and radon

Vapor Intrusion Attenuation Factors Based On Long Term Monitoring Data

Evaluation of Spatial and Temporal Variability in VOC Concentrations at Vapor Intrusion Investigation Sites.

2. Appendix Y: Vapor Intrusion Modeling Requirements (Appendix to Statewide health standard VI guidance in the Technical Guidance Manual)

Vapor Intrusion Mitigation Methods & Strategies

U.S. EPA s Vapor Intrusion Database: Preliminary Evaluation of Attenuation Factors

PVI Risk Pathway: Sampling Considerations

UNDERSTANDING THE ROLE OF SEWER PREFERENTIAL PATHWAYS IN VAPOR INTRUSION. Thomas McHugh, Ph.D., D.A.B.T. Lila Beckley, P.G.

A Comparison of BioVapor and Johnson and Ettinger Model Predictions to Field Data for Multiple Sites

Oregon Guidance for Assessing and Remediating Vapor Intrusion in Buildings

MEMO. Kris Hinskey

Well Hydraulics. The time required to reach steady state depends on S(torativity) T(ransmissivity) BC(boundary conditions) and Q(pumping rate).

ATTACHMENT 12: CDISCO Description and Sensitivity to Input Parameters

Sustainability; in Residential, Commercial and Industrial Buildings

Proposed Changes to EPA s Spreadsheet Version of Johnson & Ettinger Model (and some new spreadsheet tools)

A REVIEW OF VAPOR INTRUSION GUIDANCE BY STATE

Leaky Aquifers. log s drawdown. log time. will the red observation well look more like?.. A infinite aquifer. D none of the above

Soil Vapor Intrusion Training In The New Economy*

Soil Vapor Installation

Modeling the Vapor Intrusion Pathway: Revisions to the MCP GW-2 Groundwater Standards

Is this the maturation Phase of Vapor Intrusion Investigations?

Best management practices for vapor investigation and building mitigation decisions

U. S. Army Corps of Engineers Soil Vapor Extraction Subsurface Performance Checklist

Indoor Air Quality Testing at the Middle River Complex. Indoor Air Quality Testing at the Middle River Complex. For More Information

Indoor Radon as an Option for Sustainable On going Screening/Monitoring of Short Term Risks from Low/Episodic Chlorinated Vapor Intrusion

Presented to the AEHS 26th Annual International Conference San Diego, California March 23, 2016 SANITARY SEWER CONTAMINANT MIGRATION STUDY

Vapor Intrusion Issues

PA Vapor Intrusion Guidance

Exclusion Distance Criteria for Assessing Potential Vapour Intrusion at Petroleum Hydrocarbon Sites

VAPOR INTRUSION FROM REGULATORY, TECHNICAL,

DESIGNING COMMERCIAL SUB-SLAB DEPRESSURIZATION SYSTEMS

Vapor Intrusion Assessment A Comparative Analysis of Subsurface Vapor Sampling Methods

Distribution Restriction Statement

Air Barrier Requirements for Low-Slope Roof Assemblies Myths vs. Facts

Ground-Water Flow to Wells Introduction. Drawdown Caused by a Pumping Well

Use of Crawl Space Sampling Data and Other Lines of Evidence for Evaluating Vapor Intrusion

RADON MITIGATION IN BLOCKS OF FLATS

HYDRO GEO CHEM, INC. PNEUMATIC TESTING AND RECOMMENDED CHANGES AT THE SUNSHINE CANYON LANDFILL SYLMAR, CALIFORNIA. Environmental Science & Technology

SUB-SLAB DEPRESSURIZATION SYSTEM DESIGN AND INSTALLATION

Soil Gas Analytical Methods (Overview, TAGA, Forensics)

Measuring Up. Tools for High Performance Building Performance. RESNET 2008 San Diego, CA February 20, 2008 Bill Spohn. Bill Spohn, testo, inc.

Manufactured Gas Plant Site Management - Program 50

Quantitative Passive Diffusion-Adsorptive Sampling Techniques for Vapor Intrusion Assessment

Soil Gas Sampling for Vapor Intrusion Assessments: Key Issues

Vapor Intrusion Risk Pathway: Updates & Hot topics

Effective Stress Design For Floodwalls on Deep Foundations

Analysis of the Cromwell, Minnesota Well 4 (593593) Aquifer Test CONDUCTED ON MAY 24, 2017 CONFINED QUATERNARY GLACIAL-FLUVIAL SAND AQUIFER

(,,,) = ( )exp ( + C(x,y,z,t) = the concentration of the contaminant at location x, y, z from the source at time t.

August Vapor Intrusion Guidance FAQs

Effects of Alternate Petroleum Hydrocarbon Sources in the Vadose Zone on the Vapor Intrusion Pathway beneath a Residential Community

POROSITY, SPECIFIC YIELD & SPECIFIC RETENTION. Physical properties of

Vapor Barriers Under Concrete Slabs Guidance for Selection and Location

About 900 total tests (that we know of)

Soil Vapor Extraction System Optimization, Transition, and Closure Guidance

Comparison of purge and no-purge sampling strategies for deep groundwater

When R-Value Doesn t Measure Up

Continuous Simulation Modeling of Stormwater Ponds, Lakes, & Wetlands: A BUILT-IN APPLICATION OF PONDS 3.2

Techna-Duc. Advantages. Features and Benefits. LEED Eligible Product

Drying of Concrete TDS 183

Administrative Building Cooling Tower. University of Tennessee Chattanooga

Vapor Intrusion Regulatory Guidance and IRIS Updates with Mitigation Case Studies. Richard J. Rago Haley & Aldrich 20 June 2012

Hydrology. Jürg M. Matter Lamont-Doherty Earth Observatory, The Earth Institute at Columbia University. May 9, 2008

Vapor Intrusion: How, Why, Where, When

CEE 452/652. Week 12, Lecture 1 Cyclones. Dr. Dave DuBois Division of Atmospheric Sciences, Desert Research Institute

Risk Assessment & Generic Assessment Criteria for Groundwater Vapours

A Stakeholder s Guide to New Construction at Vapor Intrusion Sites By Lenny Siegel December, 2016

Green Remediation at. LUST Technical Workshop Stephen G. Reuter New Mexico Environment Department

Groundwater Risk Assessment

Health Assessment Section

Using CFD to Wring Out Energy Efficiency in Laboratory Settings

Using 222 Rn/ 220 Rn versus 226 Ra/ 232 Th activity ratio and CO 2 concentration in soil gas to trace advective fluxes

Evergreen Project Implementation Plan Instructions Low Income Housing Tax Credit Program

SOURCES OF WATER SUPPLY GROUND WATER HYDRAULICS

Subsurface Fire Identification, Assessment, and Mitigation (A Presentation of Selected Case Studies)

ENERGY PERFORMANCE R-VALUE: PART 2, EXAMPLES OF INTEGRATED METHODOLOGY FOR EVALUATION OF ENERGY EQUIVALENT R-VALUE FOR BUILDING ENCLOSURES;

Of Building Science: From Control Layers to High Performance Enclosures

Radon mitigation in Slovenia

Vapor Intrusion: A State s Perspective

Notes. Lesson overview. This lesson discusses how radon enters a home, where people can be exposed to unhealthy levels.

Chapter 2: Foundation

Municipal Water Experts Celebrated our 50 th Anniversary National Service Capability Part of a Global Group of Suez Companies Focused on Asset

EPA S 2015 vapor intrusion guides What do they mean for your facility?

November 8, 2016 International Petroleum Environmental Conference. Tim Nickels Pastor, Behling & Wheeler, LLC

Using the PPM2 Portable Trace Moisture Transmitter

Green Energy Guild Molecular Gate Technology. Digester Gas Treatment for Energy Production / Pipeline Gas Production from WWTP Digester Gas

ROUX ASSOCIATES, INC. Environmental Consulting & Management

Increasing Availability of Continuous and Real-Time VOC Monitoring Technologies for VI Assessment

Dayton Bar Association

*** IN THE PUMPING WELL

Empirical Data to Evaluate the Occurrence of Sub-slab O 2 Depletion Shadow at Petroleum Hydrocarbon- Impacted Vapor Intrusion Sites

Transcription:

ESTCP Research on Optimization of Vapor Intrusion Mitigation Systems in Large Military Buildings Todd McAlary, Ph.D., P.Eng., P.G., CUT Principal and Practice Leader Vapor Intrusion Services Geosyntec Consultants, Inc. USEPA Vapor Intrusion Workshop at the AEHS Conference San Diego, CA, 23 March 2015

Research Goals Improve energy efficiency of mitigation system Develop new design and diagnostic tools Demonstrate and validate Scientific review Regulatory acceptance Publish protocols 2

Case Study: Building 205, Raritan, NJ 160 ft Suction point 400 ft Building area = 67,000 ft 2 Area per vent pipe = 2,480 ft 2 Radius = 28 ft 3

SSD System (2005) 9 HS-2000 High Suction Fans Connected to 3 suction points each Total system flow ~500 scfm 4

Mass Flux Conceptualization Extracted Flux Ideally, F 2 ~ F 1 and F 3 = C IA x Q build F 3 < IASL x Q build Upward Diffusive Flux Capillary Fringe Groundwater Flow

Subsurface Conceptualization Key Variables: Flow, vacuum, permeability, thickness, porosity Hantush-Jacob Leaky Aquifer Model (1955) 6

Vent-Pipe Monitoring Data Thermal anemometer flow rate in scfm 30-day Waterloo Membrane Sampler - VOC concentrations in µg/m³ 1 hour Durridge RAD 7 - Radon concentrations in Bq/m 3 Area with TCE vapors near SSSL 7

8 Extracted Mass Flux Fan ID Fan Q (scfm) Fan Q (m 3 /min) TCE Conc. (ug/m 3 ) Mass Flux (g/d) Proportion of MF HSF-01 30.41 0.861 100 0.124 27% HSF-02 26.54 0.751 58 0.063 14% HSF-03 30.52 0.864 100 0.124 27% HSF-04 46.45 1.315 49 0.093 20% HSF-05 63.50 1.797 9.3 0.024 5% HSF-06 72.40 2.049 3.4 0.010 2% HSF-07 72.35 2.048 2 0.006 1% HSF-08 73.04 2.067 3.4 0.010 2% HSF-09 73.35 2.076 1.4 0.004 1% Average [TCE] less than industrial IASL Total MF (g/d) 0.458 How Much Mass Flux poses a problem? C IA = MF/Q build Q build = V x AER Threshold MF = 2.6 g/d 8

9 Pneumatic Testing: Specific Capacity Measure flow (Q) and vacuum (ΔP) at each vent-pipe (<2 min) Q/ΔP = Specific capacity (depends on permeability) Specific Capacity (scfm/in.h 2 O) ~30X range in values across 27 vent-pipes

Pneumatic Testing: Static ΔP vs r Measure steady vacuum at sub-slab probes, takes <30 minutes Area with ΔP > 6 Pa (ASTM Spec) Subfloor Vacuum in Pascals Note: this is with only Fan #3 running do we need 9 fans? 10

Vacuum inches of water Pneumatic Testing: Transient ΔP vs t Conducted tests at 11 locations near fans 1, 3, 5, 7 and 9 0.0 0 500 1,000 1,500 2,000 2,500 3,000 3,500 4,000 4,500-0.2-0.4-0.6 recovery drawdown -0.8 Slower than average response (~1-hr) because of low permeability -1.0-1.2-1.4-1.6 time (s) 11

12 Pneumatic Analysis: Hantush-Jacob T r/b The fit between measured vacuum and the Hantush-Jacob Model (blue curve) is usually nearly perfect

Vacuum versus distance: Velocity versus distance: Travel time for sub-slab gas from a given distance: Proportion of total flow originating below the floor: Bulk gas permeability of the floor and Qsoil: Qw Vacuum K0(r/B) 2 π T Qw 1 v( r) K 1(r/B) 2 π b n B Q( r) Q w K = T b B 2 r B Bonus Information K (r/b) 1 Q soil = K i A T = transmissivity [L 2 /t] B = leakance [L] Q w =volumetric flow rate from well (ft 3 /day) r = distance from extraction point (ft) b = thickness of fill layer (ft) n = fill layer porosity (ft 3 /ft 3 ) K 1 = Modified Bessel function of first order K 0 = Modified Bessel function of zero order K = bulk gas conductivity of the floor slab [L/t] b = floor slab thickness [L], easily measured i = pressure gradient across the floor slab A = Area of the building All of these calculations can be done in a spreadsheet (thanks Hantush and Jacob!) 13

Vacuum (Pa) Distance from Extraction Point (ft) 14 Vacuum vs Radial Distance Qw Vacuum K0(r/B) 2 π T

15 Sub-Slab Velocity: 1) Inter-well Tracer Test Inject helium into a sub-slab probe, then let it flow Monitor Helium in a nearby vent-pipe, get a breakthrough curve t 1 t 2 t 3

16 Sub-Slab Velocity: 1) Inter-well test results Travel time = 130 seconds from a radius of 6 ft Travel time = 44 seconds from a radius of 14 ft Travel time = 50 seconds from a radius of 14 ft These tests are quick, simple and very informative using low-cost equipment that is easily rented

17 Sub-Slab Velocity: 2) Helium Flood Reverse the flow on a vent-fan and match ΔP and Q Add helium (~2%v/v or so), monitor transport below the slab

18 Sub-Slab Velocity: 2) Helium Flood He injected at 2% v/v = 20,000 ppmv Average travel time = arrival of C/Co =0.5 =10,000 ppmv ~100 min at r = 43 ft Projected to about 360 min at a radius of 67 ft

Time to Reach Extraction Point (min) Sub-Slab Travel Time: Calibration Inter-well Test Helium Flood Distance from Extraction Point (ft) 19

20 Indoor Air Leakance: CO 2 Tracer Test 1) Add CO 2 to indoor air (~2,000 ppmv) 2) Turn on a Fan - measure CO 2 in exhaust CO 2 in Vent exhaust / CO 2 in indoor air = Fraction from Leakage Calculate the cost of lost indoor air

21 CO 2 sensors Special thanks to Prof. Jeffrey Siegel and his student Donna Vakalis Lesson Learned: Naturally-occurring (background) CO 2 can be high enough to confound the response Sometimes, that can be a good thing (see next slide)

Existing Sub-Floor O 2 and CO 2 Recent data collected below the slab of a different large building O 2 CO 2 Slight increase in O 2 with volume purged Slight decrease in CO 2 with volume purged Both trends are consistent with gradual leakage of air through the floor slab 22

Indoor Air Leakance: From H-J Analyses Portion of flow from indoor air via leakance Q( r) Q w r B K (r/b) 1 Portion of flow from below the floor 23

HVAC costs per year ~$50,000 for Building 205 SSD system flow is ~2% of total building flow leakance is ~35% Potential saving ~$400/yr Over a 30 year operating period up to $12,000 Electrical power draw ~$5,000/yr 9x reduction = $4,450/yr in savings Over a 30 year operating period - $134,000 in net savings Total potential savings up to $146,000 Cost Assessment (not bad for a weekend of field work) (could have saved $170K more if this approach had been used for the initial design) 24

Take-Home Messages We can do better than current standard practice (based on Radon research that is several decades old) Vacuum is not the only metric Several groundwater tools work well for soil gas too Thankfully much faster and less expensive There s still more to learn about non-idealities Preferential pathways Barriers Slab-on-clay It s all part of a bigger and better toolbox 25

Study Team Organization Individual Role Geosyntec Consultants, Inc. Todd McAlary Project Director/Principal Investigator Geosyntec Consultants, Inc. William Wertz Principal Investigator Geosyntec Consultants, Inc. Paul Nicholson Principal Investigator WPB Enterprises, Inc. Bill Brodhead Technical Reviewer Practitioner (Radon) United States EPA Henry Schuver Technical Reviewer EPA Geosyntec Consultants, Inc. Robert Ettinger Technical Reviewer Internal (VOCs) Arizona State University Paul Johnson Technical Reviewer Academic (VOCs) University of Minnesota William Angell Technical Reviewer Academic (Radon) University of Toronto Jeffrey Siegel Technical Reviewer - HVAC US Army Corps of Engineers Sandra Piettro FUDS Manager at Raritan Arsenal, NJ AFCEC Cornell Long DOD Liaison tmcalary@geosyntec.com 26