Initial Sand Mine and Processing Plant Particulate Levels. Crispin Pierce PhD University of Wisconsin-Eau Claire 20 January 2013

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Transcription:

Initial Sand Mine and Processing Plant Particulate Levels Crispin Pierce PhD University of Wisconsin-Eau Claire 20 January 2013

Sampling Instruments: DustTrak Aerosol Monitor DustTrak model 8520 aerosol monitor, zero-calibrated, flow rate set to 1.7 L/min, PM 2.5, PM 10 or cyclone respirable size filter used. Samples of 1-5 minutes were collected.

Instrument specifications: Sensitivity: Sensor type:... 90 light scattering, laser diode Range:... 0.001 100 mg/m3 (calibrated to respirable fraction of standard ISO 12103-1, A1 test dust) Resolution:... ±0.1 % of reading or ±0.001 mg/m3, whichever is greater Zero stability:... ±0.001 mg/m3 over 24 hours using 10-second time-constant Particle size range:... 0.1 approximate 10 μm (Upper limit is dependent on flow rate) Flow rate range:... 1.4 2.4 L/min. Temperature coefficient:.. +0.001 mg/m3 per C (for variations from temperature at which DUSTTRAK monitor was zeroed) Instrument Temperature Range: Operating range:... 0 C to 50 C (32 F to 120 F) Storage range:... -20 C to 60 C (-4 F to 140 F) Time Constant: Range:... Adjustable from 1 to 60 seconds Data Logging: Data points:... >31,000 (21 days logging every minute) Logging interval:... Adjustable from 1 second to 1 hour

Sample Siting Protocol EPA Sample siting protocol: Title 40: Protection of Environment, PART 58-AMBIENT AIR QUALITY SURVEILLANCE, Subpart G-Federal Monitoring, Appendix E to Part 58-Probe and Monitoring Path Siting Criteria for Ambient Air Quality Monitoring (http://www.gpo.gov/fdsys/pkg/cfr-2007-title40- vol5/pdf/cfr-2007-title40-vol5-part58-appe.pdf). Protocol dictates the following: Height from ground to probe between 2-7 meters. Distance between probe and any horizontal or vertical supporting structure must be > 2 meters. Distance between probe and dripline of nearest tree must be > 10 meters.

Results: DustTrak Aerosol Monitor 30-31 July 2011 EOG Construction Sampling: The five-minute DustTrak mass samples found that respirable aerosols upwind were 22 and 17 (average = 19.5) µg/m3 and downwind were 27 and 15 (average = 21) µg/m3. Site average = 20.2 µg/m3.

11-12 November 2011 EOG Beginning of Plant Operation Sampling: The five-minute DustTrak particulate mass samples found that respirable aerosols upwind were 11 and 35 (average = 23) µg/m3 and downwind were 14 and 32 (average = 23) µg/m3. Site average = 23 µg/m3.

17 Dec. 2012 EOG Plant Open But No Operations: 16 PM2.5 one-minute samples had an average of 13.1 µg/m3 (range 6-23 µg/m3). 28 Dec. 2012 Superior Silica Sands Plant Operating (Snowing): 10 PM2.5 samples had an average of 6.2 µg/m3 (range 4-8 µg/m3).

2 Jan. 2013 EOG Plant Operating: 16 PM2.5 samples had an average of 41.3 µg/m3 (range 33-57 µg/m3). 16 PM10 samples had an average of 47.1 µg/m3 (range 35-112 µg/m3). 9 Jan. 2013 Fairmount Mine (Menomonie) Minimal Activity (High Winds): 11 PM2.5 samples had an average of 6.9 µg/m3 (range 4-14 µg/m3). 11 PM10 samples had an average of 11 µg/m3 (range 4-33 µg/m3).

PM2.5 Levels May be the Best Indicator of Public Health Risk A 1995 American Cancer Society study, 2002 follow-up, and published 2012 study of six cities found that each 10-microgram percubic-meter increase in long-term average PM2.5 concentration was associated with, a 4-14% increased risk of death from all natural causes, a 6-26% increased risk of death from cardiopulmonary/cardiovascular disease, and an 8-37% increased risk of death from lung cancer. References: http://toxicology.usu.edu/endnote/1132.pdf, http://dx.doi.org/10.1289/ehp.1104660

Measured Levels of PM2.5/4 Increased from EOG Plant Construction Through Full Operation Our 1- to 5-minute multiple snapshot samples found the following: Measured values of PM 2.5 or PM 4 increased across sampling dates between 30-31 July 2011 and 2 January 2013. Measured values during full operation were above the EPA annual and 24-hour PM2.5 standards.

Measured EOG PM2.5/4 Increased During Operation 45 40 n=16 35 EPA PM2.5 24-hr limit PM Concentration (ug/m3) 30 25 20 15 10 n=4 n=4 n=16 EPA PM2.5 annual limit 5 0 EOG Construction (PM 4) EOG Beginning of Plant Operation (PM 4) EOG Plant Open But No Operations (PM 2.5) EOG Plant Operating (PM 2.5)

Measured PM10 Levels During Operation Were Higher than the DNR Model-Predicted Maximum Concentration and the EOG 24-Hour Measured Levels

UWEC Measured PM10 Higher Than DNR Predicted or EOG Measured 150 PM 10 EPA Standard 125 PM 10 (micrograms/m3) 100 75 50 25 0 DNR Predicted Max. Offsite EOG 24-hr Averages UWEC Offsite 1-min Samples

EOG PM10 Measurements are Unreliable Estimates of PM2.5 Measured PM10 values from EOG were compared to averages of the 24 hours of DNR Eau Claire regional PM2.5 values for the same days.

DNR PM 2.5 vs. EOG PM 10 Concentrations 30 25 PM Concentration (micrograms/m3) 20 15 10 EOG PM10 Eau Claire PM2.5 5 0 1/4/2012 2/23/2012 4/13/2012 6/2/2012 7/22/2012 9/10/2012

Measured Levels of PM2.5 at EOG, Superior Silica Sands (Auburn), and Fairmount Mine (Menomonie) Were 1.7-22 micrograms/m3 Higher Than Concurrent DNR Regional Levels Average measured PM2.5 levels were compared to listed Eau Claire DNR PM2.5 levels over the same hourly periods.

PM 2.5 Increases Over Background at Sand Plants 45 41.30 40 35 EPA 24-Hour PM 2.5 Standard 30 PM 2.5 (ug/m3) 25 20 19.5 DNR Eau Claire PM 2.5 (ug/m3) DustTrak PM 2.5 (ug/m3) 15 13.10 EPA Annual PM 2.5 Standard 10 5 9 4.5 6.20 6.9 0 12/17/12 EOG No wind or activity. 12/28/12 SSS Slight wind, frequent truck activity, snowing. 1/3/13 EOG Slight wind, regular truck & train activity. 0 1/9/13 Fairmount Strong wind, low truck activity.

Measurement and Enforcement of the Current EPA 12 micrograms/m3 PM2.5 Standard is Likely to Protect Against Silicosis Risk Measured 14.5% silica concentration in 41 respirable dust samples collected in Wisconsin by MSHA. State of California OEHHA reference concentration of 3 micrograms/m3 respirable crystalline silica. 12 micrograms/m3 PM2.5 x 14.5% = 1.74 micrograms/m3.

MSHA Sampling Results Date Location Job Contaminant Concentration (mg/m3) PEL (mg/m3, varies by %SiO2) %SiO2 SiO2 Concentration (mg/m3) Sand Mining/Processing Company 2/18/2009 M - Drying & Kiln/Dryer Roasting Operator 2/11/2009 M - Drying & Mechanic Roasting 12/16/2009 M - Dry Screening 11/8/2011 S - Active Production Dry Screen Plant Operator Washer Operator 6/6/2012 S - General Electrician 3/27/2012 Laboratory 3/27/2012 M - Washing & Screening Lab Technician Washer Operator 3/27/2012 S - General Electrician Quartz, respirable, >1% Qtz Quartz, respirable, >1% Qtz Quartz, respirable, >1% Qtz Quartz, respirable, >1% Qtz Quartz, respirable, >1% Qtz Quartz, respirable, >1% Qtz Quartz, respirable, >1% Qtz Quartz, respirable, >1% Qtz 0.34 0.28 33.7142857 0.114628571 A F Gelhar Co Inc 0.36 2.47 2.048583 0.007374899 Badger Mining Corporation 0.13 0.64 13.625 0.0177125 Badger Mining Corporation-Fairwater Plant 0.32 2.35 2.25531915 0.007217021 Barton Sand & Gravel Co 0.13 0.56 15.8571429 0.020614286 EOG Resources, Inc 0.23 0.4 23 0.0529 0.6 0.53 16.8679245 0.101207547 0.82 0.57 15.5438596 0.127459649 " MIN 1.24675325 MAX 39.6666667 AVERAGE 14.517322 s.d. 10.434715 " "

Snow, Wind and Degree of Plant Activity Appear to Influence Measured PM2.5 Levels

No Activity vs. Regular Activity

Questions? Crispin Pierce, PhD Associate Professor, University of Wisconsin- Eau Claire 715-836-5589 piercech@uwec.edu http://www.uwec.edu/conhs/programs/enp h/silica/silicaresearch1.htm