investigation of ch4 leaks from the natural gas distribution ......3. methods investigation of ch 4...

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3. METHODS Investigation of CH 4 leaks from the Natural Gas Distribution System in the Houston Area N.P. Sanchez 1 , C. Zheng 2 , W. Ye 2 , B. Czader 1 , A.K. Gluszek 2 , A.J. Hudzikowski 2 , D. Cohan 1 , R.J. Griffin 1 , F.KTittel 2 ¹Department of Civil and Environmental Engineering, Rice University, Houston, TX ²Department of Electrical and Computer Engineering, Rice University, Houston, TX 1. MOTIVATION Oil and natural gas (NG) operations are the main known source of CH 4 emissions to the atmosphere [1] CH 4 is a greenhouse gas with GWP of 34 (100-yr horizon), which contributes to background ozone pollution CH 4 emissions can occur during pre- production, production and distribution stages in the NG system CH 4 leak rates as high as 2.5-6 % have been recently estimated from the NG distribution system in some urban centers in the US [2] Specific studies on potential leaks from the NG distribution system in the Houston area and their impact on emissions benefits of NG use are needed 4. RESULTS (Cont.) 5. CONCLUSIONS AND NEXT STEPS CH 4 concentration peaks observed across Houston showed a predominant thermogenic origin as demonstrated by C 2 H 6 /CH 4 enhancement ratios CH 4 peak events related with thermogenic sources were generally below 3 ppmv, corresponding to atmospheric background enhancements of ~ 600 ppbv CH 4 concentration peaks related with biogenic sources exhibited maximum ambient background enhancement levels of ~ 1,100 ppbv Detailed analysis of meteorological data (wind speed and direction) will be conducted for more precise identification of specific CH 4 sources in the Houston area 7. ACKNOWLEDGEMENTS We acknowledge financial support from a National Science Foundation (NSF) ERC MIRTHE award, the Shell Center for Sustainability at Rice University and two DOE ARPA-E awards. 6. REFERENCES [1] EPA. https://www.epa.gov/ghgemissions/overview-greenhouse- gases#methane [2] Wennberg, P.O., et al. Environmental Science and Technology, 2012, 46, 9282-9289 [3] Ye, W., et al. Mid-infrared dual-gas sensor for simultaneous detection of methane and ethane using a single continuous-wave interband cascade laser. Optics Express, 2016, 24 (15) 16973-16985 [4] Czader, B., et al. Mapping the spatial distribution of methane in Houston, Texas. 15 th CMAS Conference, 2015 3. METHODS (Cont.) Fig. 1 CH 4 and C 2 H 6 selected absorption lines 4. RESULTS + Field tests + Spatial variation of CH 4 & C 2 H 6 mixing ratios 2. APPROACH 1. A long path absorption spectroscopy – based sensor employing a 3.337 μm CW- DFB ICL for simultaneous detection of CH 4 and C 2 H 6 at 2999.06 and 2996.88 cm -1 , respectively was developed [3] 2. Zones classified with expected high, medium and low probability of CH 4 leaks (based on age infrastructure and NG usage density) were selected for sampling in the Houston area [4] 3. The CH 4 /C 2 H 6 sensor system was deployed in a medium size vehicle and mobile-mode monitoring of trace gas concentration levels in the selected sampling zones was conducted during summer 2016 10 1 10 2 10 3 10 -5 10 -4 10 -3 10 -2 2.1 ppmv 0 ppmv 11.7 ppbv @ 5.3 s 0.70 ppbv @ 5.3 s CH 4 Allan Deviation(ppbv) C 2 H 6 19.3 ppbv @ 5.3 s 10 1 10 2 10 3 10 -1 10 0 30 ppbv 0 ppbv 0.64 ppbv @ 5.3 s Allan Deviation(ppbv) Averaging Time τ (s) + CH 4 /C 2 H 6 sensor Fig. 2 CH 4 /C 2 H 6 sensor architecture and current sensor unit employed in the Houston field tests during summer 2016 Fig 3. Allan Deviation analysis for the CH 4 /C 2 H 6 sensor system + Selection of sampling zones A 2 x 2 sampling criteria matrix was generated Pre 1980:old infrastructure (pipeline materials installed were considered) High NG usage: >1500 housing units with NG/sq. mile Two sampling areas under each high/medium/low leak probability category were selected Fig. 4 Sampling criteria matrix Fig. 5 Selected sampling locations in the Houston area Fig. 6 Sensor unit with weather station, power supply, pressure and temperature control systems deployed in a vehicle at different locations in the Houston area during summer 2016 + CH 4 peaks & source discrimination Biogenic origin Thermogenic source 38 CH 4 peaks were observed during field tests CH 4 atmospheric background level ranged between 2.1 and 2.3 ppmv in the sampling zones Maximum observed enhancement in CH 4 concentration was ~1100 ppbv Fig. 9 CH 4 peaks observed in zones with expected high and medium probability of CH 4 leaks (H2 & MA2) in south and west central Houston, respectively Fig. 10 C1-C2 slope and Keeling-like analysis of C 2 H 6 /CH 4 enhancement in CH 4 peaks in Fig. 9 Fig. 11 Source distribution of the CH 4 peaks observed during the field tests conducted in the Houston area during summer 2016. Fig. 7 Observed CH 4 & C 2 H 6 mixing ratios in zones with high (H1), medium (MA2) and low (L1) expected probability of leaks (H1-north central, MA2- west central and L1-north Houston) H2 MA2 Fig. 8 Spatial distribution of CH 4 & C 2 H 6 in the Houston area

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Page 1: Investigation of CH4 leaks from the Natural Gas Distribution ......3. METHODS Investigation of CH 4 leaks from the Natural Gas Distribution System in the Houston Area N.P. Sanchez1,

3. METHODS

Investigation of CH4 leaks from the Natural Gas Distribution System in the Houston Area

N.P. Sanchez1, C. Zheng2, W. Ye2, B. Czader1, A.K. Gluszek2, A.J. Hudzikowski2, D. Cohan1, R.J. Griffin1, F.KTittel2

¹Department of Civil and Environmental Engineering, Rice University, Houston, TX ²Department of Electrical and Computer Engineering, Rice University, Houston, TX

1. MOTIVATION • Oil and natural gas (NG) operations are the

main known source of CH4 emissions to the atmosphere [1]

• CH4 is a greenhouse gas with GWP of 34

(100-yr horizon), which contributes to background ozone pollution

• CH4 emissions can occur during pre-production, production and distribution stages in the NG system

• CH4 leak rates as high as 2.5-6 % have been recently estimated from the NG distribution system in some urban centers in the US [2]

• Specific studies on potential leaks from the NG distribution system in the Houston area and their impact on emissions benefits of NG use are needed

4. RESULTS (Cont.)

5. CONCLUSIONS AND NEXT STEPS • CH4 concentration peaks observed across Houston showed a

predominant thermogenic origin as demonstrated by C2H6/CH4 enhancement ratios

• CH4 peak events related with thermogenic sources were generally below 3 ppmv, corresponding to atmospheric background enhancements of ~ 600 ppbv

• CH4 concentration peaks related with biogenic sources exhibited

maximum ambient background enhancement levels of ~ 1,100 ppbv

• Detailed analysis of meteorological data (wind speed and direction) will be conducted for more precise identification of specific CH4 sources in the Houston area

7. ACKNOWLEDGEMENTS We acknowledge financial support from a National Science Foundation (NSF) ERC MIRTHE award, the Shell Center for Sustainability at Rice University and two DOE ARPA-E awards.

6. REFERENCES [1] EPA. https://www.epa.gov/ghgemissions/overview-greenhouse-gases#methane [2] Wennberg, P.O., et al. Environmental Science and Technology, 2012, 46, 9282-9289 [3] Ye, W., et al. Mid-infrared dual-gas sensor for simultaneous detection of methane and ethane using a single continuous-wave interband cascade laser. Optics Express, 2016, 24 (15) 16973-16985 [4] Czader, B., et al. Mapping the spatial distribution of methane in Houston, Texas. 15th CMAS Conference, 2015

3. METHODS (Cont.)

Fig. 1 CH4 and C2H6 selected absorption lines

4. RESULTS

+ Field tests

+ Spatial variation of CH4 & C2H6 mixing ratios

2. APPROACH

1. A long path absorption spectroscopy –based sensor employing a 3.337 µm CW-DFB ICL for simultaneous detection of CH4 and C2H6 at 2999.06 and 2996.88 cm-1, respectively was developed [3]

2. Zones classified with expected high, medium and low probability of CH4 leaks (based on age infrastructure and NG usage density) were selected for sampling in the Houston area [4]

3. The CH4/C2H6 sensor system was deployed in a medium size vehicle and mobile-mode monitoring of trace gas concentration levels in the selected sampling zones was conducted during summer 2016

101 102 10310-5

10-4

10-3

10-2

2.1 ppmv 0 ppmv

11.7 ppbv @ 5.3 s

0.70 ppbv @ 5.3 s

CH4

Alla

n De

viatio

n(pp

bv)

C2H6

19.3 ppbv @ 5.3 s

101 102 103

10-1

100

30 ppbv 0 ppbv

0.64 ppbv @ 5.3 s

Alla

n De

viatio

n(pp

bv)

Averaging Time τ(s)

+ CH4/C2H6 sensor

Fig. 2 CH4/C2H6 sensor architecture and current sensor unit employed in the Houston field tests during summer 2016

Fig 3. Allan Deviation analysis for the CH4 /C2H6 sensor system

+ Selection of sampling zones

• A 2 x 2 sampling criteria matrix was generated

• Pre 1980:old infrastructure (pipeline materials installed were considered)

• High NG usage: >1500 housing units with NG/sq. mile

• Two sampling areas under each high/medium/low leak probability category were selected

Fig. 4 Sampling criteria matrix

Fig. 5 Selected sampling locations in the Houston area

Fig. 6 Sensor unit with weather station, power supply, pressure and temperature control systems deployed in a vehicle at different locations in the Houston area during summer 2016

+ CH4 peaks & source discrimination

Biogenic origin

Thermogenic source

• 38 CH4 peaks were observed during field tests

• CH4 atmospheric background level ranged between 2.1 and 2.3 ppmv in the sampling zones

• Maximum observed enhancement in CH4

concentration was ~1100 ppbv

Fig. 9 CH4 peaks observed in zones with expected high and medium probability of CH4 leaks (H2 & MA2) in south and west central Houston, respectively Fig. 10 C1-C2 slope and

Keeling-like analysis of C2H6/CH4 enhancement in CH4 peaks in Fig. 9

Fig. 11 Source distribution of the CH4 peaks observed during the field tests conducted in the Houston area during summer 2016.

Fig. 7 Observed CH4 & C2H6 mixing ratios in zones with high (H1), medium (MA2) and low (L1) expected probability of leaks (H1-north central, MA2-west central and L1-north Houston)

H2

MA2

Fig. 8 Spatial distribution of CH4 & C2H6 in the Houston area