Table 1.
Basin | Dates surveyed | Area surveyed (km2) | No. of detected plumes | Total airborne CH4 emissions (t h−1)* |
Sector contribution to point source total (%)† | Average no. of overpasses per source | Average source persistence (unitless) | Total area CH4 flux (t h−1)‡ |
Contribution of point sources to area flux (%) |
---|---|---|---|---|---|---|---|---|---|
San Joaquin Valley | July 8 to September 24, 2020 | 5,600 | 284 | 10.6 ± 3.3 | O: 65 W: 2 M: 33 C: 0 |
8.2 | 0.29 | 22.5 ± 3.3 | 47 |
San Joaquin Valley | November 9–23, 2020 | 5,600 | 111 | 5.56 ± 2.0 | O: 100 W: 0 M: 0 C: 0 |
6.2 | 0.28 | 22.2 ± 4.5 | 25 |
San Joaquin Valley | November 5–13, 2021 | 5,600 | 68 | 2.34 ± 3.3 | O: 93 W: 0 M: 7 C: 0 |
3.1 | 0.41 | 17.6 ± 2.4 | 13 |
Permian | September 22 to November 4, 2019 | 54,000 | 3025 | 246 ± 79 | O: 100 W: 0 M: 0 C: 0 |
7.7 | 0.26 | 415 ± 110 | 59 |
Permian | July 13–24, 2020 | 8,400 | 595 | 72.3 ± 20 | O: 100 W: 0 M: 0 C: 0% |
3.2 | 0.45 | 177 ± 59 | 41 |
Permian | July 26 to August 10, 2021 | 8,900 | 901 | 67.7 ± 19 | O: 100 W: 0 M: 0 C: 0 |
3.9 | 0.39 | 181 ± 40 | 38 |
Permian | October 3–17, 2021 | 8,900 | 765 | 74.1 ± 27 | O: 100 W: 0 M: 0 C: 0 |
4.0 | 0.38 | 111 ± 28 | 67 |
Uinta | July 26 to August 7, 2020 | 6,200 | 123 | 6.13 ± 2.8 | O: 100 W: 0 M: 0 C: 0 |
3.6 | 0.44 | 33.9 ± 5.5 | 18 |
Denver-Julesburg | July 12–22, 2021 | 4,800 | 92 | 4.98 ± 2.1 | O: 50 W: 6 M: 44 C: 0 |
4.5 | 0.34 | 21.1 ± 4.1 | 24 |
Denver-Julesburg | September 19–29, 2021 | 4,800 | 94 | 5.37 ± 1.7 | O: 79 W: 5 M: 16 C: 0 |
4.8 | 0.28 | 25.2 ± 6.8 | 21 |
Southwest Pennsylvania | May 13–21, 2021 | 10,300 | 136 | 63.8 ± 24 | O: 33 W: 1 M: 0 C: 66 |
3.1 | 0.60 | 109 ± 39 | 59 |
*Total airborne emissions calculated by aggregated persistence-averaged source emissions within each observing domain.
†O, O&G; W, waste management; M, wet manure management; C, coal.
‡Total area flux estimated through inversion of TROPOMI XCH4 (methods described in SI Appendix, Section S2).