Cited by 39CO2 Sequestration and Geologic InteractionsGroundwater and Isotope GeochemistryAtmospheric and Environmental Gas Dynamics

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Technical note: In situ measurement of flux and isotopic composition of CO 2 released during oxidative weathering of sedimentary rocks

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Abstract

Oxidative weathering of sedimentary rocks can release carbon dioxide (CO 2 ) to the atmosphere and is an important natural CO 2 emission. Two mechanisms operate – the oxidation of sedimentary organic matter and the dissolution of carbonate minerals by sulfuric acid. It has proved difficult to directly measure the rates at which CO 2 is emitted in response to these weathering processes in the field, with previous work generally using methods which track the dissolved products of these reactions in rivers. Here we design a chamber method to measure CO 2 production during the oxidative weathering of shale bedrock, which can be applied in erosive environments where rocks are exposed frequently to the atmosphere. The chamber is drilled directly into the rock face and has a high surface-area-to-volume ratio which benefits measurement of CO 2 fluxes. It is a relatively low-cost method and provides a long-lived chamber (several months or more). To partition the measured CO 2 fluxes and the source of CO 2 , we use zeolite molecular sieves to trap CO 2 “actively” (over several hours) or “passively” (over a period of months). The approaches produce comparable results, with the trapped CO 2 having a radiocarbon activity (fraction modern, Fm) ranging from Fm = 0.05 to Fm = 0.06 and demonstrating relatively little contamination from local atmospheric CO 2 (Fm = 1.01). We use stable carbon isotopes of the trapped CO 2 to partition between an organic and inorganic carbon source. The measured fluxes of rock-derived organic matter oxidation (171 ± 5 mgC m −2 day −1 ) and carbonate dissolution by sulfuric acid (534±16 mgC m −2 day −1 ) from a single chamber were high when compared to the annual flux estimates derived from using dissolved river chemistry in rivers around the world. The high oxidative weathering fluxes are consistent with the high erosion rate of the study region. We propose that our in situ method has the potential to be more widely deployed to directly measure CO 2 fluxes during the oxidative weathering of sedimentary rocks, allowing for the spatial and temporal variability in these fluxes to be determined.

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Figure 1 A: Schematic diagram of the closed-loop monitoring-sampling system connected to the natural weathering chamber. Gas flow pathways are controlled by opening and closing the clips. Clips removed from the bypass allow pCO2 in the chamber to be monitored (IRGA stands for Infra-Red Gas Analyzer), thus measuring CO2 flux and ensuring that enough CO2 accumulated in the 5 chamber for 14 C analysis. To remove CO2 from the line before connecting to the chamber, clips are moved from the CO2 scrub (soda lime). When connected to the chamber, the CO2 scrub can be used to lower the CO2 concentration before flux measurement. To collect CO2 in the chamber for isotope analyses, clips are removed from the zeolite molecular sieve cartridge. B: Pictures showing the chamber design. Top picture is chamber (H6), diameter 2.9cm, drilled in the rock on a cleared surface, with white PVC tubing inserted at the outlet. Bottom picture shows the rubber stopper fitted in the PVC tubing. Two glass tubes go through the rubber 10 stopper and are fitted with Tygon tubing, sealed with the red clips, and the exterior of the chamber is sealed with outdoor sealant. C: View of the field site showing two chambers (top chamber is H6 and lower chamber is H4). The lower chamber is connected to the closed-loop system and is being monitored for flux measurement. The two large grey PVC tubes attached to the rock on the right of the chambers are cases in which zeolite molecular sieves are installed and left for months when connected to the chamber for passive CO2 trapping. 15
Figure 1 A: Schematic diagram of the closed-loop monitoring-sampling system connected to the natural weathering chamber. Gas flow pathways are controlled by opening and closing the clips. Clips removed from the bypass allow pCO2 in the chamber to be monitored (IRGA stands for Infra-Red Gas Analyzer), thus measuring CO2 flux and ensuring that enough CO2 accumulated in the 5 chamber for 14 C analysis. To remove CO2 from the line before connecting to the chamber, clips are moved from the CO2 scrub (soda lime). When connected to the chamber, the CO2 scrub can be used to lower the CO2 concentration before flux measurement. To collect CO2 in the chamber for isotope analyses, clips are removed from the zeolite molecular sieve cartridge. B: Pictures showing the chamber design. Top picture is chamber (H6), diameter 2.9cm, drilled in the rock on a cleared surface, with white PVC tubing inserted at the outlet. Bottom picture shows the rubber stopper fitted in the PVC tubing. Two glass tubes go through the rubber 10 stopper and are fitted with Tygon tubing, sealed with the red clips, and the exterior of the chamber is sealed with outdoor sealant. C: View of the field site showing two chambers (top chamber is H6 and lower chamber is H4). The lower chamber is connected to the closed-loop system and is being monitored for flux measurement. The two large grey PVC tubes attached to the rock on the right of the chambers are cases in which zeolite molecular sieves are installed and left for months when connected to the chamber for passive CO2 trapping. 15CC-BY · From the PDF
Image 2
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Figure 2 An example of the monitoring of the CO2 accumulating in a chamber. The orange curve is the partial pressure of CO2 (pCO2, in parts per million volume) through time in chamber H6 on 27/03/2017. A: The CO2 sampling-monitoring system is not connected to the chamber. Atmospheric CO2 has been removed from the system (pCO2 = 0 ppm) using the CO2 scrub cartridge. B: The closed-loop monitoring system has been connected to the chamber. pCO2 increases to reach a maximum value of ~5100 ppm, 5 then drops and equilibrates to ~3500ppm. This pattern reflects the increase in the total volume (by the volume of the CO2 samplingmonitoring system) which decreases pCO2 and requires some time for the pCO2 to equilibrate. We determined that when connected to the chamber, the maximum value of pCO2 read is 0.94 the actual pCO2 in the chamber. C: The CO2 in the chamber is lowered (scrubbed with the CO2 scrub, or trapped with the zeolite molecular sieve) to near atmospheric pCO2. D: residual CO2 that in the chamber homogenized with the rest of the total volume 'artificially' increasing pCO2 quickly. E: pCO2 in chamber is monitored, 10 reflecting the flux of CO2 from the rock surface to the chamber.
Figure 2 An example of the monitoring of the CO2 accumulating in a chamber. The orange curve is the partial pressure of CO2 (pCO2, in parts per million volume) through time in chamber H6 on 27/03/2017. A: The CO2 sampling-monitoring system is not connected to the chamber. Atmospheric CO2 has been removed from the system (pCO2 = 0 ppm) using the CO2 scrub cartridge. B: The closed-loop monitoring system has been connected to the chamber. pCO2 increases to reach a maximum value of ~5100 ppm, 5 then drops and equilibrates to ~3500ppm. This pattern reflects the increase in the total volume (by the volume of the CO2 samplingmonitoring system) which decreases pCO2 and requires some time for the pCO2 to equilibrate. We determined that when connected to the chamber, the maximum value of pCO2 read is 0.94 the actual pCO2 in the chamber. C: The CO2 in the chamber is lowered (scrubbed with the CO2 scrub, or trapped with the zeolite molecular sieve) to near atmospheric pCO2. D: residual CO2 that in the chamber homogenized with the rest of the total volume 'artificially' increasing pCO2 quickly. E: pCO2 in chamber is monitored, 10 reflecting the flux of CO2 from the rock surface to the chamber.CC-BY · From the PDF
Image 4
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Image 5
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Figure 4 A: Zeolite molecular sieve connected to a chamber for passive CO2 trapping. The zeolite molecular sieve is encased in the grey PVC tubing and connected for months to the chamber using a white connector. B: Zeolite molecular sieve ready to be disconnected from chamber. The red clips are positioned so that they seal both the zeolite molecular sieve and the chamber.
Figure 4 A: Zeolite molecular sieve connected to a chamber for passive CO2 trapping. The zeolite molecular sieve is encased in the grey PVC tubing and connected for months to the chamber using a white connector. B: Zeolite molecular sieve ready to be disconnected from chamber. The red clips are positioned so that they seal both the zeolite molecular sieve and the chamber.CC-BY · From the PDF
Image 7
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Research works printed but not linked: 45

  1. Bardgett, R. D., Richter, A., Bol, R., Garnett, M. H., Bäumler, R., Xu, X., Lopez-Capel, E., Manning, D. A. C., Hobbs, P. J., Hartley, I. R., and Wanek, W.: Heterotrophic microbial communities use ancient carbon following glacial retreat, Biol. Lett., 3, 487–490, 10.1098/rsbl.2007.0242, 2007. · DOI
  2. Berner, E. K. and Berner, R. A.: Global environment: Water, air, and geochemical cycles, Princeton University Press, 488 pp., 2012. · DOI
  3. Berner, R. A. and Canfield, D. E.: A new model for atmospheric oxygen over Phanerozoic time, Am. J. Sci., 289, 333–361, 10.2475/ajs.289.4.333, 1989. · DOI
  4. Bertoni, G., Ciuchini, C., and Tappa, R.: Measurement of long-term average carbon dioxide concentrations using passive diffusion sampling, Atmos. Environ., 38, 1625–1630, 10.1016/j.atmosenv.2003.12.010, 2004. · DOI
  5. Billett, M. F., Garnett, M. H., and Hardie, S. M. L.: A Direct Method to Measure 14CO2 Lost by Evasion from Surface Waters, Radiocarbon, 48, 61–68, 10.1017/S0033822200035396, 2006. · DOI
  6. Blair, N. E., Leithold, E. L., Ford, S. T., Peeler, K. A., Holmes, J. C., and Perkey, D. W.: The persistence of memory: the fate of ancient sedimentary organic carbon in a modern sedimentary system, Geochim. Cosmochim. Ac., 67, 63–73, 10.1016/S0016-7037(02)01043-8, 2003. · DOI
  7. Borges, A. V., Delille, B., Schiettecatte, L.-S., Gazeau, F., Abril, G., and Frankignoulle, M.: Gas transfer velocities of CO2 in three European estuaries (Randers Fjord, Scheldt, and Thames), Limnol. Oceanogr., 49, 1630–1641, 10.4319/lo.2004.49.5.1630, 2004. · DOI
  8. Bouchez, J., Beyssac, O., Galy, V., Gaillardet, J., France-Lanord, C., Maurice, L., and Moreira-Turcq, P.: Oxidation of petrogenic organic carbon in the Amazon floodplain as a source of atmospheric CO2, Geology, 38, 255–258, 10.1130/G30608.1, 2010. · DOI
  9. Calmels, D., Gaillardet, J., Brenot, A., and France-Lanord, C.: Sustained sulfide oxidation by physical erosion processes in the Mackenzie River basin: Climatic perspectives, Geology, 35, 1003–1006, 10.1130/G24132A.1, 2007. · DOI
  10. Calmels, D., Galy, A., Hovius, N., Bickle, M., West, A. J., Chen, M.-C., and Chapman, H.: Contribution of deep groundwater to the weathering budget in a rapidly eroding mountain belt, Taiwan, Earth Planet. Sc. Lett., 303, 48–58, 10.1016/j.epsl.2010.12.032, 2011. · DOI
  11. Cras, A., Marc, V., and Travi, Y.: Hydrological behaviour of sub-Mediterranean alpine headwater streams in a badlands environment, J. Hydrol., 339, 130–144, 10.1016/j.jhydrol.2007.03.004, 2007. · DOI
  12. Dalai, T. K., Singh, S. K., Trivedi, J. R., and Krishnaswami, S.: Dissolved rhenium in the Yamuna River System and the Ganga in the Himalaya: Role of black shale weathering on the budgets of Re, Os, and U in rivers and CO2 in the atmosphere, Geochim. Cosmochim. Ac., 66, 29–43, 10.1016/S0016-7037(01)00747-5, 2002. · DOI
  13. Das, A., Chung, C.-H., and You, C.-F.: Disproportionately high rates of sulfide oxidation from mountainous river basins of Taiwan orogeny: Sulfur isotope evidence, Geophys. Res. Lett., 39, L12404, 10.1029/2012GL051549, 2012. · DOI
  14. Davidson, G. R.: The stable isotopic composition and measurement of carbon in soil CO2, Geochim. Cosmochim. Ac., 59, 2485–2489, 10.1016/0016-7037(95)00143-3, 1995. · DOI
  15. Galy, A. and France-Lanord, C.: Weathering processes in the Ganges-Brahmaputra basin and the riverine alkalinity budget, Chem. Geol., 159, 31–60, 10.1016/S0009-2541(99)00033-9, 1999. · DOI
  16. Galy, V., Beyssac, O., France-Lanord, C., and Eglinton, T.: Recycling of Graphite During Himalayan Erosion: A Geological Stabilization of Carbon in the Crust, Science, 322, 943–945, 10.1126/science.1161408, 2008. · DOI
  17. Garnett, M. H. and Hardie, S. M. L.: Isotope (14C and 13C) analysis of deep peat CO2 using a passive sampling technique, Soil Biol. Biochem., 41, 2477–2483, 10.1016/j.soilbio.2009.09.004, 2009. · DOI
  18. Garnett, M. H. and Hartley, I. P.: A passive sampling method for radiocarbon analysis of atmospheric CO2 using molecular sieve, Atmos. Environ., 44, 877–883, 10.1016/j.atmosenv.2009.12.005, 2010. · DOI
  19. Garnett, M. H. and Murray, C.: Processing of CO2 Samples Collected Using Zeolite Molecular Sieve for 14C Analysis at the NERC Radiocarbon Facility (East Kilbride, UK), Radiocarbon, 55, 410–415, 10.1017/S0033822200057532, 2013. · DOI
  20. Garnett, M. H., Billett, M. F., Gulliver, P., and Dean, J. F.: A new field approach for the collection of samples for aquatic 14CO2 analysis using headspace equilibration and molecular sieve traps: the super headspace method, Ecohydrology, 9, 1630–1638, 10.1002/eco.1754, 2016. · DOI
  21. Garnett, M. H., Hartley, I. P., Hopkins, D. W., Sommerkorn, M., and Wookey, P. A.: A passive sampling method for radiocarbon analysis of soil respiration using molecular sieve, Soil Biol. Biochem., 41, 1450–1456, 10.1016/j.soilbio.2009.03.024, 2009. · DOI
  22. Graz, Y., Di-Giovanni, C., Copard, Y., Mathys, N., Cras, A., and Marc, V.: Annual fossil organic carbon delivery due to mechanical and chemical weathering of marly badlands areas, Earth Surf. Process. Land., 37, 1263–1271, 10.1002/esp.3232, 2012. · DOI
  23. Hahn, V., Högberg, P., and Buchmann, N.: 14C – A tool for separation of autotrophic and heterotrophic soil respiration, Glob. Chang. Biol., 12, 972–982, 10.1111/j.1365-2486.2006.001143.x, 2006. · DOI
  24. Hardie, S. L. M. L., Garnett, M. H. H., Fallick, A. E. E., Rowland, A. P. P., and Ostle, N. J. J.: Carbon dioxide capture using a zeolite molecular sieve sampling system for isotopic studies (13C and 14C) of respiration, Radiocarbon, 47, 441–451, 10.2458/azu_js_rc.v.2838, 2005. · DOI
  25. Hartley, I. P., Garnett, M. H., Sommerkorn, M., Hopkins, D. W., and Wookey, P. A.: The age of CO2 released from soils in contrasting ecosystems during the arctic winter, Soil Biol. Biochem., 63, 1–4, 10.1016/j.soilbio.2013.03.011, 2013. · DOI
  26. Hilton, R. G., Galy, A., Hovius, N., Horng, M. J., and Chen, H.: Efficient transport of fossil organic carbon to the ocean by steep mountain rivers: An orogenic carbon sequestration mechanism, Geology, 39, 71–74, 10.1130/G31352.1, 2011. · DOI
  27. Hilton, R. G., Gaillardet, J., Calmels, D., and Birck, J. L.: Geological respiration of a mountain belt revealed by the trace element rhenium, Earth Planet. Sc. Lett., 403, 27–36, 10.1016/j.epsl.2014.06.021, 2014. · DOI
  28. Hindshaw, R. S., Heaton, T. H. E., Boyd, E. S., Lindsay, M. R., and Tipper, E. T.: Influence of glaciation on mechanisms of mineral weathering in two high Arctic catchments, Chem. Geol., 420, 37–50, 10.1016/j.chemgeo.2015.11.004, 2016. · DOI
  29. Horan, K., Hilton, R. G., Selby, D., Ottley, C. J., Gröcke, D. R., Hicks, M., and Burton, K. W.: Mountain glaciation drives rapid oxidation of rock-bound organic carbon, Sci. Adv., 3, e1701107, 10.1126/sciadv.1701107, 2017. · DOI · Paper page
  30. Jaffe, L. A., Peucker-Ehrenbrink, B., and Petsch, S. T.: Mobility of rhenium, platinum group elements and organic carbon during black shale weathering, Earth Planet. Sc. Lett., 198, 339–353, 10.1016/S0012-821X(02)00526-5, 2002. · DOI
  31. Keller, C. K. and Bacon, D. H.: Soil respiration and georespiration distinguished by transport analyses of vadose CO2, 13CO2, and 14CO2, Global Biogeochem. Cy., 12, 361–372, 10.1029/98GB00742, 1998. · DOI
  32. Kutzbach, L., Schneider, J., Sachs, T., Giebels, M., Nykänen, H., Shurpali, N. J., Martikainen, P. J., Alm, J., and Wilmking, M.: CO2 flux determination by closed-chamber methods can be seriously biased by inappropriate application of linear regression, Biogeosciences, 4, 1005–1025, 10.5194/bg-4-1005-2007, 2007. · DOI
  33. Li, S. L., Calmels, D., Han, G., Gaillardet, J., and Liu, C. Q.: Sulfuric acid as an agent of carbonate weathering constrained by δ13C DIC: Examples from Southwest China, Earth Planet. Sc. Lett., 270, 189–199, 10.1016/j.epsl.2008.02.039, 2008. · DOI
  34. Maquaire, O., Ritzenthaler, A., Fabre, D., Ambroise, B., Thiery, Y., Truchet, E., Malet, J.-P., and Monnet, J.: Caractérisation des profils de formations superficielles par pénétrométrie dynamique à énergie variable?: application aux marnes noires de Draix (Alpes-de-Haute-Provence, France), Comptes Rendus Geosci., 334, 835–841, 10.1016/S1631-0713(02)01788-1, 2002. · DOI
  35. Mathys, N. and Klotz, S.: Draix: A field laboratory for research on hydrology and erosion in mountain areas, in: Proceedings of the 4th Canadian Conference on Geohazards: From Causes to Management, edited by: Locat, D.D., Perret, D., and Turmel, D., 594, 2008.
  36. Mathys, N., Brochot, S., Meunier, M., and Richard, D.: Erosion quantification in the small marly experimental catchments of Draix (Alpes de Haute Provence, France), Calibration of the ETC rainfall-runoff-erosion model, CATENA, 50, 527–548, 10.1016/S0341-8162(02)00122-4, 2003. · DOI
  37. Oostwoud Wijdenes, D. J. and Ergenzinger, P.: Erosion and sediment transport on steep marly hillslopes, Draix, Haute-Provence, France: an experimental field study, CATENA, 33, 179–200, 10.1016/S0341-8162(98)00076-9, 1998. · DOI
  38. Petsch, S. T.: Weathering of Organic Carbon, in: Treatise on Geochemistry, 12, 217–238, Elsevier, Amsterdam, 2014. · DOI
  39. Petsch, S. T., Eglinton, T. I., and Edwards, K. J.: 14C-Dead Living Biomass: Evidence for Microbial Assimilation of Ancient Organic Carbon During Shale Weathering, Science, 292, 1127–1131, 10.1126/science.1058332, 2001. · DOI
  40. Pirk, N., Mastepanov, M., Parmentier, F.-J. W., Lund, M., Crill, P., and Christensen, T. R.: Calculations of automatic chamber flux measurements of methane and carbon dioxide using short time series of concentrations, Biogeosciences, 13, 903–912, 10.5194/bg-13-903-2016, 2016. · DOI
  41. Spence, J. and Telmer, K.: The role of sulfur in chemical weathering and atmospheric CO2 fluxes: Evidence from major ions, δ13CDIC, and δ34SSO4 in rivers of the Canadian Cordillera, Geochim. Cosmochim. Ac, 69, 5441–5458, 10.1016/j.gca.2005.07.011, 2005. · DOI
  42. Stuiver, M. and Polach, H. A.: Discussion Reporting of 14C Data, Radiocarbon, 19, 355–363, 10.1017/S0033822200003672, 1977. · DOI · Paper page
  43. Sundquist, E. T. and Visser, K.: Geologic history of the carbon cycle, Biogeochemistry, 8, 425–472, 2005. · DOI
  44. Torres, M. A., West, A. J., and Li, G.: Sulphide oxidation and carbonate dissolution as a source of CO2 over geological timescales, Nature, 507, 346–349, 10.1038/nature13030, 2014. · DOI
  45. Travelletti, J., Sailhac, P., Malet, J.-P., Grandjean, G., and Ponton, J.: Hydrological response of weathered clay-shale slopes: water infiltration monitoring with time-lapse electrical resistivity tomography, Hydrol. Process., 26, 2106–2119, 10.1002/hyp.7983, 2012. · DOI

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Metadata

Authors
Soulet, G., Hilton, R. G., Garnett, M. H., Dellinger, M., Croissant, T., Ogrič, M., & Klotz, S.
Affiliations
  • Durham University (GB)
  • Institut National de Recherche en Sciences et Technologies pour l'Environnement et l'Agriculture (FR)
Corresponding author
Soulet, Guillaume
Venue
Biogeosciences
Published
2018-07-04
Volume
15
Issue
13
Pages
4087-4102
ISSN
  • 1726-4170 (ISSN-L)
  • 1726-4189
OpenAlex
W2768393184
Cited by
39
References
5
Citations by year
2026: 1 · 2025: 2 · 2024: 4 · 2023: 12 · 2022: 3 · 2021: 12 · 2020: 3 · 2019: 1 · 2018: 1
FWCI
2.13
Type
journal article
Language
en
Open access
Locations
  • Biogeosciences (publishedVersion, cc-by)
  • ENLIGHTEN (Jurnal Bimbingan dan Konseling Islam) (acceptedVersion, cc-by-sa)
  • Durham Research Online (Durham University) (acceptedVersion)
  • Durham Research Online (Durham University) (submittedVersion, cc-by)
  • HAL (submittedVersion)
  • DOAJ (DOAJ: Directory of Open Access Journals) (submittedVersion, cc-by-sa)
  • Cemadoc (Cemagref / IRSTEA) (submittedVersion)
  • Biogeosciences (European Geosciences Union) (submittedVersion, cc-by)
Funders
European Research Council
Topics
  • Physical Sciences › Environmental Science › Environmental Engineering › CO2 Sequestration and Geologic Interactions
  • Physical Sciences › Earth and Planetary Sciences › Geochemistry and Petrology › Groundwater and Isotope Geochemistry
  • Physical Sciences › Environmental Science › Global and Planetary Change › Atmospheric and Environmental Gas Dynamics
Keywords
oxidative weathering, CO2 flux, sedimentary rock, organic matter oxidation, carbonate dissolution, sulfuric acid, CO2 isotopic composition, carbon-14, zeolite molecular sieves, erosion, stable carbon isotopes

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Soulet, G., Hilton, R. G., Garnett, M. H., Dellinger, M., Croissant, T., Ogrič, M., & Klotz, S. (2018). Technical note: In situ measurement of flux and isotopic composition of CO 2 released during oxidative weathering of sedimentary rocks. Biogeosciences. https://doi.org/10.5194/bg-15-4087-2018