Methane emissions from oil and gas production sites and their storage tanks in West Virginia
A measurement campaign characterized methane and other emissions from 15 natural gas production sites. Sites were surveyed using optical gas imaging (OGI) cameras to identify fugitive and vented emissions, with the methane mass emission rate quantified using a full flow sampler. We present storage t...
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Published in | Atmospheric Environment: X Vol. 16; pp. 100193 - 11 |
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Main Authors | , , , , , , |
Format | Journal Article |
Language | English |
Published |
England
Elsevier Ltd
01.12.2022
Elsevier |
Subjects | |
Online Access | Get full text |
ISSN | 2590-1621 2590-1621 |
DOI | 10.1016/j.aeaoa.2022.100193 |
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Abstract | A measurement campaign characterized methane and other emissions from 15 natural gas production sites. Sites were surveyed using optical gas imaging (OGI) cameras to identify fugitive and vented emissions, with the methane mass emission rate quantified using a full flow sampler. We present storage tank emissions in context of all site emissions, followed by a detailed account of the former. In total, 224 well pad emission sources at 15 sites were quantified yielding a total emission rate of 57.5 ± 2.89 kg/hr for all sites. Site specific emissions ranged from 0.4 to 10.5 kg/hr with arithmetic and geometric means of 3.8 and 2.2 kg/hr, respectively. The two largest categories of emissions by mass were pneumatic devices (35 kg/hr or ∼61% of total) and tanks (14.3 kg/hr or ∼25% of total). Produced water and condensate tanks at all sites employed emissions control devices. Nevertheless, tanks may still lose gas via component leaks as observed in this study. The total number of tanks at all sites was 153. One site experienced a major malfunction and direct tank measurements were not conducted due to safety concerns and may have represented a super-emitter as found in other studies. The remaining sites had 143 tanks, which accounted for 42 emissions sources. Leaks on controlled tanks were associated with ERVs, PRVs, and thief hatches. Since measurements represented snapshots-in-time and could only be compared with modeled tank emission data, it was difficult to assess real capture efficiencies accurately. Our estimates suggest that capture efficiency ranged from 63 to 92% for controlled tanks.
•Fifteen shale gas sites were surveyed with OGI and CH4 mass emissions quantified.•Site specific CH4 emissions ranged from 0.4 to 10.5 kg/h.•The largest CH4 emitter categories by mass were PCs followed by tanks.•Tanks that deploy ECDS may still experience leaks that emit CH4 and other emissions.•Connecting multiple tanks via a common header may obfuscate causes of emissions. |
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AbstractList | A measurement campaign characterized methane and other emissions from 15 natural gas production sites. Sites were surveyed using optical gas imaging (OGI) cameras to identify fugitive and vented emissions, with the methane mass emission rate quantified using a full flow sampler. We present storage tank emissions in context of all site emissions, followed by a detailed account of the former. In total, 224 well pad emission sources at 15 sites were quantified yielding a total emission rate of 57.5 ± 2.89 kg/hr for all sites. Site specific emissions ranged from 0.4 to 10.5 kg/hr with arithmetic and geometric means of 3.8 and 2.2 kg/hr, respectively. The two largest categories of emissions by mass were pneumatic devices (35 kg/hr or ∼61% of total) and tanks (14.3 kg/hr or ∼25% of total). Produced water and condensate tanks at all sites employed emissions control devices. Nevertheless, tanks may still lose gas via component leaks as observed in this study. The total number of tanks at all sites was 153. One site experienced a major malfunction and direct tank measurements were not conducted due to safety concerns and may have represented a super-emitter as found in other studies. The remaining sites had 143 tanks, which accounted for 42 emissions sources. Leaks on controlled tanks were associated with ERVs, PRVs, and thief hatches. Since measurements represented snapshots-in-time and could only be compared with modeled tank emission data, it was difficult to assess real capture efficiencies accurately. Our estimates suggest that capture efficiency ranged from 63 to 92% for controlled tanks.
•Fifteen shale gas sites were surveyed with OGI and CH4 mass emissions quantified.•Site specific CH4 emissions ranged from 0.4 to 10.5 kg/h.•The largest CH4 emitter categories by mass were PCs followed by tanks.•Tanks that deploy ECDS may still experience leaks that emit CH4 and other emissions.•Connecting multiple tanks via a common header may obfuscate causes of emissions. A measurement campaign characterized methane and other emissions from 15 natural gas production sites. Sites were surveyed using optical gas imaging (OGI) cameras to identify fugitive and vented emissions, with the methane mass emission rate quantified using a full flow sampler. We present storage tank emissions in context of all site emissions, followed by a detailed account of the former. In total, 224 well pad emission sources at 15 sites were quantified yielding a total emission rate of 57.5 ± 2.89 kg/hr for all sites. Site specific emissions ranged from 0.4 to 10.5 kg/hr with arithmetic and geometric means of 3.8 and 2.2 kg/hr, respectively. The two largest categories of emissions by mass were pneumatic devices (35 kg/hr or ~61% of total) and tanks (14.3 kg/hr or ~25% of total). Produced water and condensate tanks at all sites employed emissions control devices. Nevertheless, tanks may still lose gas via component leaks as observed in this study. The total number of tanks at all sites was 153. One site experienced a major malfunction and direct tank measurements were not conducted due to safety concerns and may have represented a super-emitter as found in other studies. The remaining sites had 143 tanks, which accounted for 42 emissions sources. Leaks on controlled tanks were associated with ERVs, PRVs, and thief hatches. Since measurements represented snapshots-in-time and could only be compared with modeled tank emission data, it was difficult to assess real capture efficiencies accurately. Our estimates suggest that capture efficiency ranged from 63 to 92% for controlled tanks. A measurement campaign characterized methane and other emissions from 15 natural gas production sites. Sites were surveyed using optical gas imaging (OGI) cameras to identify fugitive and vented emissions, with the methane mass emission rate quantified using a full flow sampler. We present storage tank emissions in context of all site emissions, followed by a detailed account of the former. In total, 224 well pad emission sources at 15 sites were quantified yielding a total emission rate of 57.5 ± 2.89 kg/hr for all sites. Site specific emissions ranged from 0.4 to 10.5 kg/hr with arithmetic and geometric means of 3.8 and 2.2 kg/hr, respectively. The two largest categories of emissions by mass were pneumatic devices (35 kg/hr or ~61% of total) and tanks (14.3 kg/hr or ~25% of total). Produced water and condensate tanks at all sites employed emissions control devices. Nevertheless, tanks may still lose gas via component leaks as observed in this study. The total number of tanks at all sites was 153. One site experienced a major malfunction and direct tank measurements were not conducted due to safety concerns and may have represented a super-emitter as found in other studies. The remaining sites had 143 tanks, which accounted for 42 emissions sources. Leaks on controlled tanks were associated with ERVs, PRVs, and thief hatches. Since measurements represented snapshots-in-time and could only be compared with modeled tank emission data, it was difficult to assess real capture efficiencies accurately. Our estimates suggest that capture efficiency ranged from 63 to 92% for controlled tanks.A measurement campaign characterized methane and other emissions from 15 natural gas production sites. Sites were surveyed using optical gas imaging (OGI) cameras to identify fugitive and vented emissions, with the methane mass emission rate quantified using a full flow sampler. We present storage tank emissions in context of all site emissions, followed by a detailed account of the former. In total, 224 well pad emission sources at 15 sites were quantified yielding a total emission rate of 57.5 ± 2.89 kg/hr for all sites. Site specific emissions ranged from 0.4 to 10.5 kg/hr with arithmetic and geometric means of 3.8 and 2.2 kg/hr, respectively. The two largest categories of emissions by mass were pneumatic devices (35 kg/hr or ~61% of total) and tanks (14.3 kg/hr or ~25% of total). Produced water and condensate tanks at all sites employed emissions control devices. Nevertheless, tanks may still lose gas via component leaks as observed in this study. The total number of tanks at all sites was 153. One site experienced a major malfunction and direct tank measurements were not conducted due to safety concerns and may have represented a super-emitter as found in other studies. The remaining sites had 143 tanks, which accounted for 42 emissions sources. Leaks on controlled tanks were associated with ERVs, PRVs, and thief hatches. Since measurements represented snapshots-in-time and could only be compared with modeled tank emission data, it was difficult to assess real capture efficiencies accurately. Our estimates suggest that capture efficiency ranged from 63 to 92% for controlled tanks. A measurement campaign characterized methane and other emissions from 15 natural gas production sites. Sites were surveyed using optical gas imaging (OGI) cameras to identify fugitive and vented emissions, with the methane mass emission rate quantified using a full flow sampler. We present storage tank emissions in context of all site emissions, followed by a detailed account of the former. In total, 224 well pad emission sources at 15 sites were quantified yielding a total emission rate of 57.5 ± 2.89 kg/hr for all sites. Site specific emissions ranged from 0.4 to 10.5 kg/hr with arithmetic and geometric means of 3.8 and 2.2 kg/hr, respectively. The two largest categories of emissions by mass were pneumatic devices (35 kg/hr or ∼61% of total) and tanks (14.3 kg/hr or ∼25% of total). Produced water and condensate tanks at all sites employed emissions control devices. Nevertheless, tanks may still lose gas via component leaks as observed in this study. The total number of tanks at all sites was 153. One site experienced a major malfunction and direct tank measurements were not conducted due to safety concerns and may have represented a super-emitter as found in other studies. The remaining sites had 143 tanks, which accounted for 42 emissions sources. Leaks on controlled tanks were associated with ERVs, PRVs, and thief hatches. Since measurements represented snapshots-in-time and could only be compared with modeled tank emission data, it was difficult to assess real capture efficiencies accurately. Our estimates suggest that capture efficiency ranged from 63 to 92% for controlled tanks. |
ArticleNumber | 100193 |
Author | Clark, Nigel Footer, Tracey L. Heltzel, Robert Herndon, Scott Darzi, Mahdi Johnson, Derek Thoma, Eben D. |
AuthorAffiliation | c Aerodyne, 45 Manning Road, Billerica, MA, 01821, United States a West Virginia University, Mechanical & Aerospace Engineering, PO Box 6106, Morgantown, WV, 26506, United States d Center for Environmental Measurement and Modeling, Office of Research and Development, U.S. Environmental Protection Agency, Mail Code E343-02, Research Triangle Park, NC, 27711, United States b Eastern Research Group, Inc., 601 Keystone Park Drive, Suite 700, Morrisville, NC, 27560, United States |
AuthorAffiliation_xml | – name: c Aerodyne, 45 Manning Road, Billerica, MA, 01821, United States – name: a West Virginia University, Mechanical & Aerospace Engineering, PO Box 6106, Morgantown, WV, 26506, United States – name: b Eastern Research Group, Inc., 601 Keystone Park Drive, Suite 700, Morrisville, NC, 27560, United States – name: d Center for Environmental Measurement and Modeling, Office of Research and Development, U.S. Environmental Protection Agency, Mail Code E343-02, Research Triangle Park, NC, 27711, United States |
Author_xml | – sequence: 1 givenname: Derek orcidid: 0000-0002-3189-5711 surname: Johnson fullname: Johnson, Derek email: derek.johnson@mail.wvu.edu organization: West Virginia University, Mechanical & Aerospace Engineering, PO Box 6106, Morgantown, WV, 26506, United States – sequence: 2 givenname: Nigel surname: Clark fullname: Clark, Nigel organization: West Virginia University, Mechanical & Aerospace Engineering, PO Box 6106, Morgantown, WV, 26506, United States – sequence: 3 givenname: Robert surname: Heltzel fullname: Heltzel, Robert organization: West Virginia University, Mechanical & Aerospace Engineering, PO Box 6106, Morgantown, WV, 26506, United States – sequence: 4 givenname: Mahdi surname: Darzi fullname: Darzi, Mahdi organization: West Virginia University, Mechanical & Aerospace Engineering, PO Box 6106, Morgantown, WV, 26506, United States – sequence: 5 givenname: Tracey L. surname: Footer fullname: Footer, Tracey L. organization: Eastern Research Group, Inc., 601 Keystone Park Drive, Suite 700, Morrisville, NC, 27560, United States – sequence: 6 givenname: Scott surname: Herndon fullname: Herndon, Scott organization: Aerodyne, 45 Manning Road, Billerica, MA, 01821, United States – sequence: 7 givenname: Eben D. surname: Thoma fullname: Thoma, Eben D. organization: Center for Environmental Measurement and Modeling, Office of Research and Development, U.S. Environmental Protection Agency, Mail Code E343-02, Research Triangle Park, NC, 27711, United States |
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Keywords | Storage tanks Oil and natural gas production Greenhouse gases Methane emissions |
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