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Considerations in Evaluation of Potential Exposures to Emissions from Unconventional Oil and Gas Exploration Lindsey Jones, MS Toxicology Division Texas Commission on Environmental Quality
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Page 1: Considerations in Evaluation of Potential Exposures to ...

Considerations in Evaluation of Potential Exposures to Emissions from

Unconventional Oil and Gas Exploration

Lindsey Jones, MSToxicology DivisionTexas Commission on Environmental Quality

Page 2: Considerations in Evaluation of Potential Exposures to ...

Number of Producing Gas and Gas Condensate Wells, 1990-2016

0

100,000

200,000

300,000

400,000

500,000

600,000

Other 29 States Texas Pennsylvania Oklahoma West Virginia Colorado OffshoreSource: US Energy Information Administration, 2017

Page 3: Considerations in Evaluation of Potential Exposures to ...

Production in the Barnett Shale Area, 2000-2017

0

500

1000

1500

2000

2500

3000

3500

4000

4500

0

5000

10000

15000

20000

25000

30000

35000

Perm

its Is

sued

Prod

uctio

n

Barnett Shale Condensate Production (barrels/day) Barnett Shale Oil Production (barrels/day)

Barnett Shale Total Natural Gas Production (million cubic ft/day) Drilling Permits IssuedImage: http://industrialhousingsolutions.com/about/oilfield-locations/oilfield-housing-for-barnett-shale/

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Research Question

Are ambient air concentrations of pollutants at levels that could negatively impact public health or the environment in areas of high oil and natural gas activity? Not included in this question Traffic, noise, light (local jurisdictions) Indoor air quality or personal exposure Water (considered separately) Indirect impacts

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Potential Pollutants

Volatile Organic Compounds (VOCs)Modified TO-15 suite of 84 VOCs (grab, 30-minute, or 24-hour discrete canister samples) Suite of 46 VOCs (1-hour continuous sampling using autoGCs)

Carbonyls (aldehydes) TO-11 suite of 18 carbonyls (1-hour or 24-hour discrete cartridge samples)

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Exposure Considerations

Constituents and concentrations

Distance to receptor Emission source is sometimes very close to residences

Length of exposure

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Typical Timelines

Site selection, pad site preparation

4-6 weeks

Drilling2-4 weeks

Fracturing3-5 days

ProductionDecades

Page 8: Considerations in Evaluation of Potential Exposures to ...

Investigative Strategy

Qualitative Sampling and Surveys Pro: Highly mobile, provides data closer to both sources and residents Con: Unspeciated data not useful for health effect evaluations

Quantitative Sampling Pro: Provides insight into pollutant concentrations and variability over

time Con: Not easily movable, expensive

Special Emission Inventory Pro: Provides insight into likely sources Con: Data collection takes time and relies on calculations

Page 9: Considerations in Evaluation of Potential Exposures to ...

Qualitative Data Collection

Handheld instrumentsOver 4000 surveys on the ground Almost all used a survey VOC monitor Over 90 investigations used a handheld H2S monitor

Infrared ImagingOver 3000 investigations used a handheld IR camera Thousands of images collected during flyovers in 2005 and 2007

Page 10: Considerations in Evaluation of Potential Exposures to ...

Quantitative Data Collection

Field SamplingOver 1700 individual canister samples 52 carbonyl samples Collected distance and source information

http://www.tceq.texas.gov/airquality/barnettshale

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Quantitative Data Collection

Mobile Monitoring Eight multi-day trips in 2009 and 2010 Discrete and real-time sampling for VOCs, NOx, sulfur compounds, carbonyls

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Quantitative Data Collection

Fixed-site monitors 2009 – 6 monitoring sites 2 autoGCs 6 canister samplers (2 collocated with autoGCs) 2 carbonyl samplers

2017 – 26 monitoring sites 15 autoGCs 13 canister samplers (2 collocated with

autoGCs) 2 carbonyl samplers

Image available at: https://www.tceq.texas.gov/airquality/barnettshale/bshale-maps

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Results to Date

Nearly all of the issues documented arose from human or mechanical failures.

These items were quickly remedied and could have been avoided through increased diligence on the part of the operator.

Corrective actions amounted to little more than replacing worn gaskets, closing open hatches, and repairing stuck valves.

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** Not all monitors met 75% data completeness objective.

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Changes in Annual Average BTEX Concentrations at Stationary Canister Sites, 2006-2016

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Single Canisters

Over 1700 samples collected since 2009

<4% of collected canisters had exceedances of short-term health or odor comparison values

Repeat investigations showed concentrations below short-term comparison values

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Investigation Canisters with an Exceedance of a Health or Odor Value, 2009-2017

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Investigation Canisters with an Exceedance of a Health or Odor Value, 2009-2017

One on-site sample excluded

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Investigation Canisters with an Exceedance of a Health or Odor Value, 2009-2017

0.0%

0.2%

0.4%

0.6%

0.8%

1.0%Pe

rcen

tage

of

Sam

ples

Exc

eedi

ng a

n A

MC

V

43 3 3

21

One on-site sample excludedBlue – exceedance of health-based AMCVGreen – exceedance of odor-based AMCVPurple – exceedance of health and odor AMCVNumbers indicate the number of individual samples with an exceedance

*Using 2017 air monitoring comparison values (AMCVs)

Page 20: Considerations in Evaluation of Potential Exposures to ...

Sampling DistancesReceptors within 100 ft from Source, 2%

Receptors 100-300 ft from Source, 24%

Receptors 300-500 ft from Source, 16%

Receptors >500 ft

from Source,54%

Unidentified, 4%

Location of Canister Samples with a Short-Term AMCV Exceedance

108

480390

184275

17882

1

30

26

2

6

1

1

0

100

200

300

400

500

600

Num

ber o

f Sam

ples

Sampling Distance from Potential Source

Location of Discrete Cansiter Samples in Relation to Potential Sources in the Barnett Shale, 2009-2017

Samples with anExceedance of an AMCVSamples with NoExceedance of an AMCV

Page 21: Considerations in Evaluation of Potential Exposures to ...

Carbonyl Concentrations

None of the 52 sample concentrations was above a level of health concern Relatively consistent concentration independent of sampling location Formaldehyde, acetaldehyde, and acetone were the most abundant carbonyls detected Formaldehyde concentrations were typical for populated areas

Page 22: Considerations in Evaluation of Potential Exposures to ...

Barnett Shale Special Emissions Inventory-VOCs , 2009

0

1,000

2,000

3,000

4,000

5,000

6,000

7,000

Arc

her

Bosq

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lay

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anch

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ooke

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Dal

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Den

ton

East

land Ellis

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illH

ood

Jack

John

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Mon

tagu

ePa

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into

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Som

erve

llSt

ephe

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rran

tW

ise

Rep

orte

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issi

ons

(tpy

)

Water Tank

Vent

Turbine

Thermal Oxidizer

Separator

Oil Tank

Loading

Heater

Glycol Dehydrator

Fugitives

Frac Tank

Flare

Engine

Condensate Tank

Boiler

Amine Unit

Other

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Barnett Shale Special Emissions Inventory-VOCs , 2009

Condensate Tank39%

Fugitives25%

Oil Tank8%

Water Tank8%

Engine8%

Loading3%

Glycol Dehydrator2%

Vent2%

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Conclusions

Monitored ambient VOC, carbonyl, and H2S concentrations remain below a level of health concern

Using a multi-pronged approach to evaluating potential for exposure leads to a more complete picture of potential risk and helps to focus investigative efforts

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Moving Forward

Ensure transparency of our efforts through abundant and timely communication with all interested parties

Evaluate data from the existing ambient air quality monitoring network and samples collected during investigations

Maintain a frequent, routine investigative presence while also providing timely complaint response

Adjust as necessary

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Extras

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Wells and Ambient Air Quality Monitors


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