Mitigation of greenhouse gas emissions by anaerobic digestion of cattle slurry

Abstract Biogas treatment of animal manures is an upcoming technology because it is a way of producing renewable energy (biogas). However, little is known about effects of this management strategy on greenhouse gas (GHG) emissions during fermentation, storage, and field application of the substrates compared to untreated slurries. In this study, we compared cattle slurry and cattle slurry with potato starch as additive during the process of fermentation, during storage and after field application. The addition of potato starch strongly enhanced CH 4 production from 4230 l CH 4 m −3 to 8625 l CH 4 m −3 in the fermenter at a hydraulic retention time (HRT) of 29 days. Extending the HRT to 56 days had only a small effect on the CH 4 production. Methane emissions from stored slurry depended on storage temperature and were highest from unfermented slurry followed by the slurry/starch mixture. Gas emissions from untreated and fermented slurry during storage were further analyzed in a pilot-scale experiment with different levels of covering such as straw cover, a wooden lid and no cover. Emissions of greenhouse gases (CH 4 , N 2 O, NH 3 ) were in the range of 14.3–17.1 kg CO 2 eq. m −3 during winter (100 day storage period) and 40.5–90.5 kg CO 2 eq. m −3 during summer (140 day storage period). A straw cover reduced NH 3 losses, but not overall GHG emissions, whereas a solid cover reduced CH 4 and NH 3 emissions. After field application, there were no significant differences between slurry types in GHG emissions (4.15–8.12 kg CO 2 eq. m −3  a −1 ). GHG emissions from slurry stores were more important than emissions after field application. Co-digestion of slurry with additives such as starch has a large potential to substitute fossil energy by biogas. On a biogas plant, slurry stores should be covered gas-tight in order to eliminate GHG emissions and collect CH 4 for electricity production.

[1]  J. Clemens,et al.  Application technique and slurry co-fermentation effects on ammonia, nitrous oxide, and methane emissions after spreading: II. Greenhouse gas emissions. , 2002, Journal of environmental quality.

[2]  Søren Husted,et al.  Seasonal variation in methane emission from stored slurry and solid manures , 1994 .

[3]  P. L'Hermite,et al.  Odour and Ammonia Emissions from Livestock Farming , 2003 .

[4]  M. Kaupenjohann,et al.  In situ measurement of ammonia emissions from organic fertilizers in plot experiments , 1998 .

[5]  F. Beese,et al.  Laboratory estimates of trace gas emissions following surface application and injection of cattle slurry. , 2000 .

[6]  S. Sommer,et al.  Nitrous oxide and methane emissions from pig slurry amended soils , 1996 .

[7]  Carolien Kroeze,et al.  Closing the global atmospheric N2O budget: nitrous oxide emissions through the agricultural nitrogen cycle. (OECD/IPCC/IEA Phase II Development of IPCC Guidelines for National Greenhouse Gas Inventories). , 1997 .

[8]  G. Velthof,et al.  Nitrous oxide fluxes from grassland in the Netherlands: I. Statistical analysis of flux‐chamber measurements , 1995 .

[9]  CHRISTIAN-D. SCHÖNWIESE J.T. Houghton, L.G. Meira Filho, B.A. Callander, N. Harris, A. Kattenberg, and K. Maskell (eds.): Climate Change 1995, The Science of Climate Change , 1997 .

[10]  J. R. Simpson,et al.  Dynamics of Ammonia Volatilization during Furrow Irrigation of Maize , 1982 .

[11]  G. Watts,et al.  Climate Change 1995 , 1998 .

[12]  J. Clemens,et al.  The effect of biological oxygen demand of cattle slurry and soil moisture on nitrous oxide emissions , 2001, Nutrient Cycling in Agroecosystems.

[13]  Liane Hüther Entwicklung analytischer Methoden und Untersuchung von Einflußfaktoren auf Ammoniak-, Methan- und Distickstoffmonoxidemissionen aus Flüssig- und Festmist , 1999 .

[14]  Sven G. Sommer,et al.  Greenhouse Gas Emission from Stored Livestock Slurry , 2000 .

[15]  J. Clemens,et al.  Ammonia and nitrous oxide emissions after landspreading of slurry as influenced by application technique and dry matter-reduction. II. Short term nitrous oxide emissions , 1997 .

[16]  J. Clemens,et al.  Application technique and slurry co-fermentation effects on ammonia, nitrous oxide, and methane emissions after spreading: I. Ammonia volatilization. , 2002, Journal of environmental quality.

[17]  M. Kreuzer,et al.  Methane Emissions of Differently Fed Dairy Cows and Corresponding Methane and Nitrogen Emissions from their Manure during Storage , 2002, Environmental monitoring and assessment.

[18]  Søren O. Petersen,et al.  Nitrous Oxide Emissions from Manure and Inorganic Fertilizers Applied to Spring Barley , 1999 .

[19]  J. Clemens,et al.  NH3 and N2O Emissions after Landspreading of Slurry as Influenced by Application Technique and Dry Matter-Reduction. I. NH3 Emissions , 1997 .