TY - JOUR
T1 - Exploring How to Use Groundwater Chemistry to Identify Migration of Methane near Shale Gas Wells in the Appalachian Basin
AU - Wen, Tao
AU - Woda, Josh
AU - Marcon, Virginia
AU - Niu, Xianzeng
AU - Li, Zhenhui
AU - Brantley, Susan L.
N1 - Funding Information:
Funding was derived from the National Science Foundation IIS-16-39150 to S.L.B. and Z.L. We thank Alison Herman, Marcus Guarnieri, and Li Li for technical support, Bruce Lindsey (U.S. Geological Survey), and Seth Pelepko and Stew Beattie (PA DEP) for access and help with data, Maurie Kelly and James Spayd (Penn State University) for help with data publishing and data storage. We would also like to thank the editor for handling this article and the constructive reviews of Zunli Lu and two other anonymous reviewers.
Publisher Copyright:
© 2019 American Chemical Society.
PY - 2019/8/6
Y1 - 2019/8/6
N2 - Methane (CH4) enters waters in hydrocarbon-rich basins because of natural processes and problems related to oil and gas wells. As a redox-active greenhouse gas, CH4 degrades water or emits to the atmosphere and contributes to climate change. To detect if methane migrated from hydrocarbon wells (i.e., anomalous methane), we examined 20â»751 methane-containing groundwaters from the Upper Appalachian Basin (AB). We looked for concentrations (mg/L) that indicated AB brine salts (chloride concentrations ([Cl]) > 30; [Ca]/[Na] < 0.52) to detect natural methane, and we looked for concentrations of redox-active species ([SO4] ≥ 6; [Fe] ≥ 0.3) to detect anomalous methane. These indicators highlight natural contamination by methane-containing brines or recent onset of microbial oxidation of methane coupled to iron-or sulfate-reduction. We hypothesized that only waters recently contaminated by methane still exhibit high iron and sulfate concentrations. Of the AB samples, 17 (0.08%) from 12 sites indicated potential contamination. All were located in areas with high densities of shale-gas or conventional oil/gas wells. In contrast, in southwestern Pennsylvania where brines are shallow and coal, oil, and gas all have been extracted extensively, no sites of recent methane migration were detectable. Such indicators may help screen for contamination in some areas even without predrill measurements.
AB - Methane (CH4) enters waters in hydrocarbon-rich basins because of natural processes and problems related to oil and gas wells. As a redox-active greenhouse gas, CH4 degrades water or emits to the atmosphere and contributes to climate change. To detect if methane migrated from hydrocarbon wells (i.e., anomalous methane), we examined 20â»751 methane-containing groundwaters from the Upper Appalachian Basin (AB). We looked for concentrations (mg/L) that indicated AB brine salts (chloride concentrations ([Cl]) > 30; [Ca]/[Na] < 0.52) to detect natural methane, and we looked for concentrations of redox-active species ([SO4] ≥ 6; [Fe] ≥ 0.3) to detect anomalous methane. These indicators highlight natural contamination by methane-containing brines or recent onset of microbial oxidation of methane coupled to iron-or sulfate-reduction. We hypothesized that only waters recently contaminated by methane still exhibit high iron and sulfate concentrations. Of the AB samples, 17 (0.08%) from 12 sites indicated potential contamination. All were located in areas with high densities of shale-gas or conventional oil/gas wells. In contrast, in southwestern Pennsylvania where brines are shallow and coal, oil, and gas all have been extracted extensively, no sites of recent methane migration were detectable. Such indicators may help screen for contamination in some areas even without predrill measurements.
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U2 - 10.1021/acs.est.9b02290
DO - 10.1021/acs.est.9b02290
M3 - Article
C2 - 31299147
AN - SCOPUS:85071064310
SN - 0013-936X
VL - 53
SP - 9317
EP - 9327
JO - Environmental Science & Technology
JF - Environmental Science & Technology
IS - 15
ER -