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Single-blind testing of a regional, continuous monitoring system for finding methane leaks from oil and gas operations Caroline Alden 1,2 , Sean Coburn 2 , Robert Wright 2 , Esther Baumann 3 , Kevin Cossel 3 , Colm Sweeney 4 , Anna Karion 3 , Alex


  1. Single-blind testing of a regional, continuous monitoring system for finding methane leaks from oil and gas operations Caroline Alden 1,2 , Sean Coburn 2 , Robert Wright 2 , Esther Baumann 3 , Kevin Cossel 3 , Colm Sweeney 4 , Anna Karion 3 , Alex Rybchuk 2 , Kuldeep Prasad 3 , Ian Coddington 3 , Gregory Rieker 2 1 Cooperative Institute for Research in Environmental Sciences, 2 University of Colorado, 3 National Institute of Standards and Technology, 4 National Oceanic and Atmospheric Administration

  2. Outline • Approach to methane monitoring • METEC oil & gas test site • Single-blind test results • Regional, continuous methane leak monitoring 2

  3. Approach to methane leak detection • Locate mobile spectrometer in a central location Coburn, Alden et al. Optica, 5 (2018) Alden, Coburn et al. AMT , 11 (2018) 3

  4. Approach to methane leak detection • Locate mobile spectrometer in a central location • Deploy retroreflective mirrors in field Coburn, Alden et al. Optica, 5 (2018) Alden, Coburn et al. AMT , 11 (2018) 4

  5. Approach to methane leak detection • Locate mobile spectrometer in a central location • Deploy retroreflective mirrors in field • Sequentially measure atmospheric CH 4 along open paths 1+ km Coburn, Alden et al. Optica, 5 (2018) Alden, Coburn et al. AMT , 11 (2018) 5

  6. Approach to methane leak detection • Locate mobile spectrometer in a central location • Deploy retroreflective mirrors in field • Sequentially measure atmospheric CH 4 along open paths • Determine species concentration • < 5 ppb CH 4 precision over 1+ km paths in 2 mins • Handles multi-species absorption interference Water measured directly  dry-air mole fractions • • High stability over time, little to no instrument drift Coburn, Alden et al. Optica, 5 (2018) Alden, Coburn et al. AMT , 11 (2018) 6

  7. Approach to methane leak detection • Locate mobile spectrometer in a central location • Deploy retroreflective mirrors in field • Sequentially measure atmospheric CH 4 along open paths • Determine species concentration, track variability through time Dry [CH 4 ] Dry [CO 2 ] [H 2 O] Coburn, Alden et al. Optica, 5 (2018) Alden, Coburn et al. AMT , 11 (2018) 7

  8. Approach to methane leak detection • Locate mobile spectrometer in a central location • Deploy retroreflective mirrors in field • Sequentially measure atmospheric CH 4 along open paths • Determine species concentration, track variability through time, couple with atmospheric modeling and inversions Dry [CH 4 ] Dry [CO 2 ] [H 2 O] Coburn, Alden et al. Optica, 5 (2018) Alden, Coburn et al. AMT , 11 (2018) 8

  9. METEC oil & gas test site Fort Collins, Colorado METEC (Methane Emissions Technology Evaluation Center) “Hollywood well set”: CU Mobile Lab decommissioned equipment plumbed with controlled leaks Alden, Coburn et al,. In Prep 9

  10. METEC oil & gas test site Fort Collins, Colorado METEC (Methane Emissions Technology Evaluation Center) Spectrometer located >1 km away to the SW Alden, Coburn et al,. In Prep 10

  11. METEC oil & gas test site Pad A Detection: is there a leak? Attribution: where is the leak? Quantification: how big is the leak? Pad B Pad C Alden, Coburn et al,. In Prep 11

  12. Single-blind test results: Detection Pad A ✓ Pad A: 6/6 leaks detected at pad A ✓ Pad B: 6/6 leaks detected at pad B Pad C: ✓ 5/5 leaks detected at pad C 1/1 false detection avoided Pad B Pad C Alden, Coburn et al,. In Prep 12

  13. Single-blind test results: Attribution Pad B SEPARATOR Pad A WELL ✓ Pad A: Sub-pad level sub-pad identified in 6 of 6 cases TANK ✓ Pad B: Component-level component identified in 6 of 6 cases Pad C Pad C: Component-level TANK component identified in 2 of 5 cases WELL SEPARATOR Orientation of pad C with respect to spectrometer made component-level detection difficult Alden, Coburn et al,. In Prep 13

  14. Single-blind test results: Quantification Pad B Test 10 SEPARATOR True leak 3.9 ± 2 scfh (0.7 kg/hr) leak from separator regulator WELL flange Leak estimate 3.5 ± 1 scfh (0.6 kg/hr) from separator house TANK pressure-reducing valve Beam 1 Beam 2 Beam 3 5-10 ppb enhancements measured over 3.7 hours Beam 1 Beam 2 Beam 3 Background estimate Alden, Coburn et al,. In Prep 14

  15. Single-blind test results: Quantification Device-level measurements suggest 90% of all emissions come from leaks > 135 scfh (2.5 kg/hr) ! Controlled rate (Blind Test) Estimated rate (Blind Test) Controlled rate (Ad Hoc, treated as blind) Estimated rate (Ad Hoc, treated as blind) Brandt et al., ES&T, 50 (2016) Alden, Coburn et al,. In Prep 15

  16. Regional, continuous methane leak monitoring Methane emissions from oil and gas intermittent, unpredictable, and heavy-tailed: a small fraction of sources cause most of the emissions (“super-emitters”) Continuous NOAA/GMD data Campaigns provide snapshots, provide nation-wide statistics reconciliation of emissions estimates Continuous monitoring of emissions across large areas Miller et al., 2013 PNAS Pétron et al., 2014 JGR “Missing Link” Continuous monitoring of many sites will provide critical, missing information about time variability of emissions and distributions of “super-emitters” 16

  17. Thank You Contact caroline.alden@colorado.edu Thank you to funding agencies DOE ARPA-E https://arpa-e.energy.gov/ DOE Office of Fossil Energy https://www.energy.gov/fe/office-fossil-energy For more information about METEC site energy.colostate.edu/metec 17

  18. Extra Slides 18

  19. Frequency Comb Spectroscopy Tooth spacing < 200 MHz (2 x 10 -3 nm) Intensity 0 frequency Spectral Bandwidth 179 – 187 THz (1600 – 1670 nm) chosen here for methane Equivalent to ~80,000 well-behaved continuous wave lasers 19

  20. Dual Frequency Comb Spectroscopy Two frequency comb lasers with slightly offset tooth spacing, give rise to a third comb in the radio frequency (rf) regime Absorption feature Optical Frequency (THz): Too fast to resolve on photodetector Radio Frequency (MHz): Resolvable by photodetector Rieker et al. Optica, 1 (2014) 20

  21. Dual Frequency Comb Spectroscopy Dry-air mole fractions CO 2 , CH 4 , H 2 O, HDO and 13 CO 2 • • Minimal to no instrument drift • Very high precision: < 5 ppb CH 4 over 1 km path in 2-5 minutes • Measurement of long, open paths through the atmosphere (up to several km) Absorption feature Optical Frequency (THz): Too fast to resolve on photodetector Radio Frequency (MHz): Resolvable by photodetector Rieker et al. Optica, 1 (2014) 21

  22. Dual Frequency Comb Spectroscopy f r f r E( ν ) Optical Frequency (THz) ∆ f r =f r - f r RF Frequency (MHz)

  23. Dual Frequency Comb Spectroscopy f r f r E( ν ) Optical Frequency (THz) ∆ f r =f r - f r RF Frequency (MHz)

  24. Frequency Comb Spectroscopy T=1 / f rep Passively Time domain Mode-locked Laser t >100,000 well-behaved Continuous Wave lasers f rep Frequency domain I ( f ) f o 0 f With noise, output moves around... but basic comb structure is preserved. Comb can only “translate” and “breathe” 24

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