In this study, we examined regional differences in CH4 emissions from O&G production sites in the Denver-Julesburg (DJB, Weld County, CO), Uintah (Uintah and Duchesne Counties, UT), and Marcellus (northeastern (NEPA)) basins. These three O&G production regions differ significantly in several key operational parameters. First, there are large variabilities in the total number and type of active O&G well pads (e.g., 1260 unconventional gas well pads (UNG) in NEPA versus 12000 mixed O&G well pads in the DJB). Second, regional O&G production and facility-specific O&G production rates vary widely among the three production regions. For example, in May 2015, approximately 1260 NEPA UNG well pad sites produced 6 times more natural gas than all 7700 O&G well pads in Uintah. Third, at the regional scale, average facility age (estimated from well spud dates) are highest in the Uintah (10.6 years old) and DJB (13 years old) and lowest among NEPA UNG sites (3.5 years old). Finally, measured average ethane/methane (C2H6/CH4) molar ratios in natural gas varied from a low 2% (NEPA) to a high 30% in the DJB.
Measurements of facility-level CH4 emission rates (CH4 FLER) in these three regions were performed at 103 active O&G production well pad sites in April to May 2015 (Uintah, n = 31, and DJB, n = 23) and May 2016 (NEPA, n = 49). Selection of sites were quasi-random, and were determined by downwind road access, local terrain and meteorology. Nevertheless, efforts were made to ensure that sites were selected from a distribution that adequately matched regional diversity in site production, facility age, and site operators. In all three regions, three top-down ground-based measurement techniques—i.e., dual tracer flux utilizing acetylene and nitrous oxide as atmospheric tracers, drive-by plume intercepts utilizing Gaussian plume inverse modeling, and stationary OTM (Other Test Methods)-33A approaches—were utilized. Measured CH4 FLER were scaled up to total populations of well pads in each region using a probabilistic modeling scheme that accounts for the contributions of high emitting sites and large episodic emissions based on empirical observations.
Measured mean CH4 FLER varied by four orders of magnitude, ranging from 0.01 ± 0.01 kg/h (Uintah) to 293 kg/h (NEPA), and from 0.001% to 42% proportional CH4 loss rates at the facility level. Overall, 72% to 83% of sampled sites in each region emitted less than 3 kg/h CH4 (average: 0.81 ± 0.89 kg/h), equivalent to 0.13% to 4.27% CH4 loss rates. However, the top 10% of measured well pad sites in each region contributed approximately 60% (Uintah, DJB) to 80% (NEPA) of respective cumulative CH4 emissions, underscoring the importance of “super emitters”. For all sites in the three regions, multilinear regression models incorporating oil/gas production rates, well count, facility age, and C2H6/CH4 molar ratios explained only 11% (p = 0.027) of the observed variability in mean CH4 FLER. However, preliminary results suggest that high mean CH4 FLER are likely to be observed at sites with high gas production rates in Marcellus (r2adj = 0.30, p < 0.05) and low C2H6/CH4 content in Uintah (C2H6/CH4 < 8%, r2adj = 0.25, p < 0.05). Regionally, preliminary analyses indicate total (basin-wide) CH4 emissions from active O&G production well pads are highest in the DJB and lowest in NEPA corresponding to regional proportional CH4 loss rates that are lowest in NEPA (<0.5%) and highest in the Uintah and DJB (<3%) during the measurement period. Detailed discussions on factors influencing estimated regional CH4 emissions, contributions of high emitting sites in each region, comparisons with recent top-down and bottom-up inventory estimates, and uncertainty assessments will be presented.