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Near surface gas monitoring at the CO2 Field Lab, Norway Sarah Hannis1, Dave Jones1, Andy Barkwith1, Bob Lister1, Frederick Gal2, Stefano Graziani3, Stan Beaubien3 and David Widory2, 4 and the CO2FieldLab team 1. British Geological Survey 2. Bureau de Recherches Géologiques et Minières 3. Università di Roma "La Sapienza 4. Now at Université du Québec à Montréal/Geotop www.sintef.no/projectweb/co2fieldlab/
 
Introduction to the CO2 Field Lab 
 
Surface gas methods 
 
Results 
 
Conclusions 
 
General lessons 
Outline 
2
CO2FieldLab 
Svalbard 
Gardermoen 
Svelvik 
BERGEN 
OSLO
Site characterization
5 
Site layout 
20m
CO2 injection – 1.8 tonnes in 124 hours 
6 
7th Sept 
(~ 5 days of injection) 
12th Sept
 
Continuous 
 
5 Soil gas locations (1 Rn, CO2 + C/O isotopes) 
 
4 CO2 flux chambers 
 
1 Eddy covariance 
 
1 Weather station 
 
Periodic surveys 
 
Regular grids of field soil gas and flux measurements 
 
Repeat field (and field lab) soil gas at fixed sites (~20) 
 
Open path laser (static and mobile) 
 
Other 
 
Water chemistry 
 
Geophysics (GPR, ERT, seismic, resistivity and sonic logging) 
Surface gas methods 
7
Continuous monitoring 
C and O isotopes Rn and CO2 
Injection wellhead 
toe 
Cabin 
CO2 concentration 
EC 
Flux
Periodic surveys: Mobile methods 
10 m grid 
5m grid 
2m grid 
Soil gas (CO2, Rn) concentration, surface gas flux 
Atmospheric CO2 concentration
10 
Cabin 
Periodic surveys: Static methods 
Soil gas field sampling probes (BGS) 
field & lab gas sampling (BRGM) 
( , GPR, resistivity, sonic logging ) 
( , water chemistry) 
( , cross-hole ERT)
6-7/9/11 (Baseline, Mobile Survey 3) 
Baseline survey 
Soil Gas CO2 concentration (%) at 50cm depth 
Soil Gas CO2 flux (gm-2d-1) at surface 
Soil Gas Radon concentration (Bq l-1) at 50cm depth 
5 6 7 8 9 10 11 12 13 14 15 
Injection start (10am) 
Injection stop (2pm)
8/9/11 (Mobile Surveys 4 & 5) 
4FNN & 5FNN 
5 6 7 8 9 10 11 12 13 14 15 
Injection start (10am) 
Injection stop (2pm) 
Soil Gas CO2 concentration (%) at 50cm depth 
Soil Gas CO2 flux (g m-2 d-1) at surface
5 6 7 8 9 10 11 12 13 14 15 
Injection start (10am) 
Injection stop (2pm) 
4FNN & 5FNN 
10/9/11 (Mobile Surveys (9 & 10) 
Soil Gas CO2 concentration (%) at 50cm depth 
Soil Gas CO2 flux (g m-2 d-1) at surface
5 6 7 8 9 10 11 12 13 14 15 
Injection start (10am) 
Injection stop (2pm) 
12/9/11 (Mobile Surveys 13,14,15) 
Soil Gas CO2 concentration (%) at 50cm depth 
Soil Gas CO2 flux (g m-2 d-1) at surface
13/9/11 (Mobile Surveys 16,17,18) 
Soil Gas CO2 concentration (%) at 50cm depth 
Soil Gas CO2 flux (g m-2 d-1) at surface 
5 6 7 8 9 10 11 12 13 14 15 
Injection start (10am) 
Injection stop (2pm)
16 
toe 
Injection well head 
Soil gas post injection
Continuous CO2 flux monitoring 
17
Atmospheric monitoring 
18 
Eddy covariance footprints (% probability) 
Mobile open path laser 9/9/11 (CO2 ppm)
19 
Isotope monitoring
 
Surface seepage very clear above low baseline values 
 
Not in expected area directly above injection point 
 
Seepage in central area only apparent in isotope data 
 
Initial seep related to pathway near injection well 
 
Later seeps to the N approximately updip (tortuous paths) 
 
Maximum flux (2 kg m-2 d-1) and size (m to tens of m) c.f. to natural CO2 seeps 
 
Measured CO2 flux < 5% of injected CO2 (underestimate) 
 
Atmospheric monitoring compromised by leakage at injection wellhead (and other CO2 sources) 
Conclusions 
20
 
Hard to predict where migration and seepage will occur 
 
Where in relation to wellhead or fault? 
 
Siting of fixed monitoring, therefore, difficult 
 
Mobile monitoring more flexible/successful 
 
Small vents will be hard to identify 
 
Signs of low-level seepage from isotopes only 
 
If this was widespread could have implications 
 
Ideally would have allowed site longer to re-equilibrate after drilling and had longer term baselines 
Lessons/implications 
21
Thank you for your attention Acknowledgements 
www.sintef.no/CO2FieldLab 
For financial support: 
 
CLIMIT via Gassnova SF (NO) 
 
DGCIS, Direction générale de la compétitivité, de l'industrie et des services (FR) 
 
NERC/BGS (UK) 
 
Svelviksand AS 
 
Eyvind Aker and Marion Børreson at NGI 
 
Hurum kommune 
 
Per Aagard at University of Oslo
 
Jones, D. G., Barkwith, A. K. A. P., Hannis, S., Lister, T. R., Gal, F., Graziani, S., Beaubien, S. and Widory, D. (2014). Monitoring of near surface gas seepage from a shallow injection experiment at the CO2 Field Lab, Norway. International Journal of Greenhouse Gas Control, 28, 300-317. doi: http://dx.doi.org/10.1016/j.ijggc.2014.06.021 
 
Denchik, N., Pezard, P. A., Neyens, D., Lofi, J., Gal, F., Girard, J.-F. and Levannier, A. (2014). Near-surface CO2 leak detection monitoring from downhole electrical resistivity at the CO2 Field Laboratory, Svelvik Ridge (Norway). International Journal of Greenhouse Gas Control, 28, 275-282. doi: http://dx.doi.org/10.1016/j.ijggc.2014.06.033 
 
Barrio, M., Bakk, A., Grimstad, A.-A., Querendez, E., Jones, D. G., Kuras, O., Gal, F., Girard, J.F., Pezard, P., Depraz, L., Baudin, E., Børreson, M.H. and Sønneland, L. (2014). CO2 Migration Monitoring Methodology in the Shallow Subsurface: Lessons Learned From the CO2 Field Lab Project. Energy Procedia, 51, 65–74. doi: http://dx.doi.org/10.1016/j.egypro.2014.07.008 
Recent publications 
23
Extra slides 
24
Instrumentation (0-20 m) 
Downhole: 
 
4 ALERT wells (6-m) - BGS 
 
IR Laser Spectrometer (BRGM) 1 well C/O isotopes in CO2 
 
Water/ gas sampling (BRGM) 
 
Schlumberger WestBay multipacker completion 
 
Hydrochemical monitoring (pressure, fluid sampling) (CNRS) 
 
Crosshole GPR (BRGM) 
 
Induction & sonic logging (CNRS) 
 
Downhole electrical observatory (Imageau) 
 
PVC cased hole for repeat logging during injection 
 
induction & sonic logging (CNRS) 
 
Crosshole GPR (BRGM) Surface: 
 
Numerous fixed and mobile instruments (soil & atmosphere) measuring flux, concentration (CO2, O2, CH4, Rn).
Instrumentation at (near) surface 
26 
Tool 
Depth 
Deployment 
Mode 
GAS 
Gas monitor station 
c. 1 m 
Fixed 
Continuous 
Flux station 
Surface 
Fixed 
Continuous 
Eddy covariance 
Surface 
Fixed 
Continuous 
Fixed probes 
c. 1 m 
Fixed 
Intermittent 
Mobile laser 
Surface 
Mobile 
Intermittent 
Soil gas 
0-1 m 
Point (not fixed) 
Intermittent 
Flux 
Surface 
Point (not fixed) 
Intermittent 
*Licor or FTIR 
1m 
Fixed 
Continuous 
Radon/ CO2 monitoring probes 
0.8m 
Fixed 
Continuous 
CO2, O2and CH4 monitoring 
1m 
Fixed/ mobile 
Intermittent 
Portable GC 
Surface 
Fixed 
Intermittent 
*Aerodyne isotopic analyser 
1m 
Fixed 
Continuous 
WATER 
*Perisaltic pumps 
Surface 
Fixed 
Intermittent 
*Idronaut probe 
Surface 
Fixed 
Intermittent 
*Precision balance 
Surface 
Fixed 
intermittent 
* Tubing connected to ALERT boreholes

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Near Surface Gas Monitoring and CO2 Flux Measurements in Norway

  • 1. Near surface gas monitoring at the CO2 Field Lab, Norway Sarah Hannis1, Dave Jones1, Andy Barkwith1, Bob Lister1, Frederick Gal2, Stefano Graziani3, Stan Beaubien3 and David Widory2, 4 and the CO2FieldLab team 1. British Geological Survey 2. Bureau de Recherches Géologiques et Minières 3. Università di Roma "La Sapienza 4. Now at Université du Québec à Montréal/Geotop www.sintef.no/projectweb/co2fieldlab/
  • 2.  Introduction to the CO2 Field Lab  Surface gas methods  Results  Conclusions  General lessons Outline 2
  • 3. CO2FieldLab Svalbard Gardermoen Svelvik BERGEN OSLO
  • 6. CO2 injection – 1.8 tonnes in 124 hours 6 7th Sept (~ 5 days of injection) 12th Sept
  • 7.  Continuous  5 Soil gas locations (1 Rn, CO2 + C/O isotopes)  4 CO2 flux chambers  1 Eddy covariance  1 Weather station  Periodic surveys  Regular grids of field soil gas and flux measurements  Repeat field (and field lab) soil gas at fixed sites (~20)  Open path laser (static and mobile)  Other  Water chemistry  Geophysics (GPR, ERT, seismic, resistivity and sonic logging) Surface gas methods 7
  • 8. Continuous monitoring C and O isotopes Rn and CO2 Injection wellhead toe Cabin CO2 concentration EC Flux
  • 9. Periodic surveys: Mobile methods 10 m grid 5m grid 2m grid Soil gas (CO2, Rn) concentration, surface gas flux Atmospheric CO2 concentration
  • 10. 10 Cabin Periodic surveys: Static methods Soil gas field sampling probes (BGS) field & lab gas sampling (BRGM) ( , GPR, resistivity, sonic logging ) ( , water chemistry) ( , cross-hole ERT)
  • 11. 6-7/9/11 (Baseline, Mobile Survey 3) Baseline survey Soil Gas CO2 concentration (%) at 50cm depth Soil Gas CO2 flux (gm-2d-1) at surface Soil Gas Radon concentration (Bq l-1) at 50cm depth 5 6 7 8 9 10 11 12 13 14 15 Injection start (10am) Injection stop (2pm)
  • 12. 8/9/11 (Mobile Surveys 4 & 5) 4FNN & 5FNN 5 6 7 8 9 10 11 12 13 14 15 Injection start (10am) Injection stop (2pm) Soil Gas CO2 concentration (%) at 50cm depth Soil Gas CO2 flux (g m-2 d-1) at surface
  • 13. 5 6 7 8 9 10 11 12 13 14 15 Injection start (10am) Injection stop (2pm) 4FNN & 5FNN 10/9/11 (Mobile Surveys (9 & 10) Soil Gas CO2 concentration (%) at 50cm depth Soil Gas CO2 flux (g m-2 d-1) at surface
  • 14. 5 6 7 8 9 10 11 12 13 14 15 Injection start (10am) Injection stop (2pm) 12/9/11 (Mobile Surveys 13,14,15) Soil Gas CO2 concentration (%) at 50cm depth Soil Gas CO2 flux (g m-2 d-1) at surface
  • 15. 13/9/11 (Mobile Surveys 16,17,18) Soil Gas CO2 concentration (%) at 50cm depth Soil Gas CO2 flux (g m-2 d-1) at surface 5 6 7 8 9 10 11 12 13 14 15 Injection start (10am) Injection stop (2pm)
  • 16. 16 toe Injection well head Soil gas post injection
  • 17. Continuous CO2 flux monitoring 17
  • 18. Atmospheric monitoring 18 Eddy covariance footprints (% probability) Mobile open path laser 9/9/11 (CO2 ppm)
  • 20.  Surface seepage very clear above low baseline values  Not in expected area directly above injection point  Seepage in central area only apparent in isotope data  Initial seep related to pathway near injection well  Later seeps to the N approximately updip (tortuous paths)  Maximum flux (2 kg m-2 d-1) and size (m to tens of m) c.f. to natural CO2 seeps  Measured CO2 flux < 5% of injected CO2 (underestimate)  Atmospheric monitoring compromised by leakage at injection wellhead (and other CO2 sources) Conclusions 20
  • 21.  Hard to predict where migration and seepage will occur  Where in relation to wellhead or fault?  Siting of fixed monitoring, therefore, difficult  Mobile monitoring more flexible/successful  Small vents will be hard to identify  Signs of low-level seepage from isotopes only  If this was widespread could have implications  Ideally would have allowed site longer to re-equilibrate after drilling and had longer term baselines Lessons/implications 21
  • 22. Thank you for your attention Acknowledgements www.sintef.no/CO2FieldLab For financial support:  CLIMIT via Gassnova SF (NO)  DGCIS, Direction générale de la compétitivité, de l'industrie et des services (FR)  NERC/BGS (UK)  Svelviksand AS  Eyvind Aker and Marion Børreson at NGI  Hurum kommune  Per Aagard at University of Oslo
  • 23.  Jones, D. G., Barkwith, A. K. A. P., Hannis, S., Lister, T. R., Gal, F., Graziani, S., Beaubien, S. and Widory, D. (2014). Monitoring of near surface gas seepage from a shallow injection experiment at the CO2 Field Lab, Norway. International Journal of Greenhouse Gas Control, 28, 300-317. doi: http://dx.doi.org/10.1016/j.ijggc.2014.06.021  Denchik, N., Pezard, P. A., Neyens, D., Lofi, J., Gal, F., Girard, J.-F. and Levannier, A. (2014). Near-surface CO2 leak detection monitoring from downhole electrical resistivity at the CO2 Field Laboratory, Svelvik Ridge (Norway). International Journal of Greenhouse Gas Control, 28, 275-282. doi: http://dx.doi.org/10.1016/j.ijggc.2014.06.033  Barrio, M., Bakk, A., Grimstad, A.-A., Querendez, E., Jones, D. G., Kuras, O., Gal, F., Girard, J.F., Pezard, P., Depraz, L., Baudin, E., Børreson, M.H. and Sønneland, L. (2014). CO2 Migration Monitoring Methodology in the Shallow Subsurface: Lessons Learned From the CO2 Field Lab Project. Energy Procedia, 51, 65–74. doi: http://dx.doi.org/10.1016/j.egypro.2014.07.008 Recent publications 23
  • 25. Instrumentation (0-20 m) Downhole:  4 ALERT wells (6-m) - BGS  IR Laser Spectrometer (BRGM) 1 well C/O isotopes in CO2  Water/ gas sampling (BRGM)  Schlumberger WestBay multipacker completion  Hydrochemical monitoring (pressure, fluid sampling) (CNRS)  Crosshole GPR (BRGM)  Induction & sonic logging (CNRS)  Downhole electrical observatory (Imageau)  PVC cased hole for repeat logging during injection  induction & sonic logging (CNRS)  Crosshole GPR (BRGM) Surface:  Numerous fixed and mobile instruments (soil & atmosphere) measuring flux, concentration (CO2, O2, CH4, Rn).
  • 26. Instrumentation at (near) surface 26 Tool Depth Deployment Mode GAS Gas monitor station c. 1 m Fixed Continuous Flux station Surface Fixed Continuous Eddy covariance Surface Fixed Continuous Fixed probes c. 1 m Fixed Intermittent Mobile laser Surface Mobile Intermittent Soil gas 0-1 m Point (not fixed) Intermittent Flux Surface Point (not fixed) Intermittent *Licor or FTIR 1m Fixed Continuous Radon/ CO2 monitoring probes 0.8m Fixed Continuous CO2, O2and CH4 monitoring 1m Fixed/ mobile Intermittent Portable GC Surface Fixed Intermittent *Aerodyne isotopic analyser 1m Fixed Continuous WATER *Perisaltic pumps Surface Fixed Intermittent *Idronaut probe Surface Fixed Intermittent *Precision balance Surface Fixed intermittent * Tubing connected to ALERT boreholes