Methane and carbon dioxide emissions and nitrogen turnover during liquid manure storage
Animal slurry stored in-house and outside is a significant source of atmospheric methane (CH₄). The CH₄ source strength of stored slurry is greatly affected by temperature. To improve emission calculations on a global scale there is a need for knowledge about the relationship between production of C...
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description | Animal slurry stored in-house and outside is a significant source of atmospheric methane (CH₄). The CH₄ source strength of stored slurry is greatly affected by temperature. To improve emission calculations on a global scale there is a need for knowledge about the relationship between production of CH₄ in slurry and temperature. In this study, the filling of slurry channels was reproduced in the laboratory by gradually filling 1 m-high PVC vessels during 9 days followed by incubation for 100-200 days. A preliminary test showed that little CH₄ was produced from animal slurry during 10 days of incubation at 20°C, if no inoculum (slurry incubated anaerobically at the test temperature for 1.5-2 months) was present. However, the addition of 7.6% inoculum supported an immediate production of CH₄. Vessels amended with inoculum and gradually filled with cattle or pig slurry were then incubated at 10, 15 and 20°C. Methane production from stored pig and cattle slurry was not significant at temperatures below 15°C, where CO₂ was the main product of decomposition processes. In contrast, the anaerobic production of CH₄ was high and significant relative to the production of CO₂ at 20°C. Peak emissions of CH₄ averaging 0.012 and 0.02 g C h-¹ kg-¹ volatile solids (VS) were reached within about 10 days at 10 and 15°C, respectively. At 20°C, the emission of CH₄ from pig slurry was about 0.01 g C h-¹ kg-¹ for 10 days, and thereafter emissions increased to about 0.10 g C h-¹ kg-¹ VS. For cattle slurry a peak emission of 0.08 g C h-¹ kg-¹ VS was measured after 180 days. Degradation of organic nitrogen (N) in cattle slurry was related to the reduction of organic material as reflected in CO₂ and CH₄ emission. The mineralization of organic N during storage represented 10-80% of organic N in cattle slurry, and 40-80% of the organic N in pig slurry. |
doi_str_mv | 10.1007/s10705-006-9072-4 |
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The CH₄ source strength of stored slurry is greatly affected by temperature. To improve emission calculations on a global scale there is a need for knowledge about the relationship between production of CH₄ in slurry and temperature. In this study, the filling of slurry channels was reproduced in the laboratory by gradually filling 1 m-high PVC vessels during 9 days followed by incubation for 100-200 days. A preliminary test showed that little CH₄ was produced from animal slurry during 10 days of incubation at 20°C, if no inoculum (slurry incubated anaerobically at the test temperature for 1.5-2 months) was present. However, the addition of 7.6% inoculum supported an immediate production of CH₄. Vessels amended with inoculum and gradually filled with cattle or pig slurry were then incubated at 10, 15 and 20°C. Methane production from stored pig and cattle slurry was not significant at temperatures below 15°C, where CO₂ was the main product of decomposition processes. In contrast, the anaerobic production of CH₄ was high and significant relative to the production of CO₂ at 20°C. Peak emissions of CH₄ averaging 0.012 and 0.02 g C h-¹ kg-¹ volatile solids (VS) were reached within about 10 days at 10 and 15°C, respectively. At 20°C, the emission of CH₄ from pig slurry was about 0.01 g C h-¹ kg-¹ for 10 days, and thereafter emissions increased to about 0.10 g C h-¹ kg-¹ VS. For cattle slurry a peak emission of 0.08 g C h-¹ kg-¹ VS was measured after 180 days. Degradation of organic nitrogen (N) in cattle slurry was related to the reduction of organic material as reflected in CO₂ and CH₄ emission. The mineralization of organic N during storage represented 10-80% of organic N in cattle slurry, and 40-80% of the organic N in pig slurry.</description><identifier>ISSN: 1385-1314</identifier><identifier>EISSN: 1573-0867</identifier><identifier>DOI: 10.1007/s10705-006-9072-4</identifier><language>eng</language><publisher>Dordrecht: Dordrecht : Kluwer Academic Publishers</publisher><subject>ambient temperature ; anaerobic conditions ; Anaerobic processes ; Animal wastes ; biodegradation ; Bovidae ; Carbon dioxide ; Carbon dioxide emissions ; Cattle ; Cattle manure ; composting ; gas emissions ; greenhouse gases ; Inoculum ; Liquid manure ; mathematical models ; Methane ; Mineralization ; Nitrogen ; nitrogen turnover ; Organic nitrogen ; Pig manure ; Slurries ; storage ; Swine ; Temperature ; Temperature effects ; Vessels ; volatile compounds ; Volatile solids ; waste lagoons</subject><ispartof>Nutrient cycling in agroecosystems, 2007-05, Vol.78 (1), p.27-36</ispartof><rights>Springer Science+Business Media B.V. 2006.</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c328t-9663881a53fb43c7c2f3a70b37435f150b570144aa9ade16c970d4e164d23d853</citedby><cites>FETCH-LOGICAL-c328t-9663881a53fb43c7c2f3a70b37435f150b570144aa9ade16c970d4e164d23d853</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,776,780,27903,27904</link.rule.ids></links><search><creatorcontrib>Sommer, Sven G</creatorcontrib><creatorcontrib>Petersen, Søren O</creatorcontrib><creatorcontrib>Sørensen, Peter</creatorcontrib><creatorcontrib>Poulsen, Hanne D</creatorcontrib><creatorcontrib>Møller, Henrik B</creatorcontrib><title>Methane and carbon dioxide emissions and nitrogen turnover during liquid manure storage</title><title>Nutrient cycling in agroecosystems</title><description>Animal slurry stored in-house and outside is a significant source of atmospheric methane (CH₄). The CH₄ source strength of stored slurry is greatly affected by temperature. To improve emission calculations on a global scale there is a need for knowledge about the relationship between production of CH₄ in slurry and temperature. In this study, the filling of slurry channels was reproduced in the laboratory by gradually filling 1 m-high PVC vessels during 9 days followed by incubation for 100-200 days. A preliminary test showed that little CH₄ was produced from animal slurry during 10 days of incubation at 20°C, if no inoculum (slurry incubated anaerobically at the test temperature for 1.5-2 months) was present. However, the addition of 7.6% inoculum supported an immediate production of CH₄. Vessels amended with inoculum and gradually filled with cattle or pig slurry were then incubated at 10, 15 and 20°C. Methane production from stored pig and cattle slurry was not significant at temperatures below 15°C, where CO₂ was the main product of decomposition processes. In contrast, the anaerobic production of CH₄ was high and significant relative to the production of CO₂ at 20°C. Peak emissions of CH₄ averaging 0.012 and 0.02 g C h-¹ kg-¹ volatile solids (VS) were reached within about 10 days at 10 and 15°C, respectively. At 20°C, the emission of CH₄ from pig slurry was about 0.01 g C h-¹ kg-¹ for 10 days, and thereafter emissions increased to about 0.10 g C h-¹ kg-¹ VS. For cattle slurry a peak emission of 0.08 g C h-¹ kg-¹ VS was measured after 180 days. Degradation of organic nitrogen (N) in cattle slurry was related to the reduction of organic material as reflected in CO₂ and CH₄ emission. The mineralization of organic N during storage represented 10-80% of organic N in cattle slurry, and 40-80% of the organic N in pig slurry.</description><subject>ambient temperature</subject><subject>anaerobic conditions</subject><subject>Anaerobic processes</subject><subject>Animal wastes</subject><subject>biodegradation</subject><subject>Bovidae</subject><subject>Carbon dioxide</subject><subject>Carbon dioxide emissions</subject><subject>Cattle</subject><subject>Cattle manure</subject><subject>composting</subject><subject>gas emissions</subject><subject>greenhouse gases</subject><subject>Inoculum</subject><subject>Liquid manure</subject><subject>mathematical models</subject><subject>Methane</subject><subject>Mineralization</subject><subject>Nitrogen</subject><subject>nitrogen turnover</subject><subject>Organic nitrogen</subject><subject>Pig manure</subject><subject>Slurries</subject><subject>storage</subject><subject>Swine</subject><subject>Temperature</subject><subject>Temperature effects</subject><subject>Vessels</subject><subject>volatile compounds</subject><subject>Volatile solids</subject><subject>waste lagoons</subject><issn>1385-1314</issn><issn>1573-0867</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2007</creationdate><recordtype>article</recordtype><sourceid>AFKRA</sourceid><sourceid>AZQEC</sourceid><sourceid>BENPR</sourceid><sourceid>CCPQU</sourceid><sourceid>DWQXO</sourceid><sourceid>GNUQQ</sourceid><recordid>eNpdkM1LAzEQxRdRsFb_AE8GBG-rM_nY7B6l-AUVD1o8hnSTrSlt0ia7ov-9qfXkaR7M7w3zXlGcI1wjgLxJCBJECVCVDUha8oNihEKyEupKHmbNalEiQ35cnKS0hOxhNR8V78-2_9DeEu0NaXWcB0-MC1_OWGLXLiUXfPpdetfHsLCe9EP04dNGYobo_IKs3HZwhqy1H6IlqQ9RL-xpcdTpVbJnf3NczO7v3iaP5fTl4WlyOy1bRuu-bKqK1TVqwbo5Z61sace0hDmTnIkOBcyFBORc60Ybi1XbSDA8C24oM7Vg4-Jqf3cTw3awqVf56dauVjlTGJLCpuJU4A68_AcuQw6Sf1OUiqamtMIqU7in2hhSirZTm-jWOn4rBLUrWu2LVrlotSta8ey52Hs6HZReRJfU7JUCsoxLigjsB1nUeWs</recordid><startdate>20070501</startdate><enddate>20070501</enddate><creator>Sommer, Sven G</creator><creator>Petersen, Søren O</creator><creator>Sørensen, Peter</creator><creator>Poulsen, Hanne D</creator><creator>Møller, Henrik B</creator><general>Dordrecht : Kluwer Academic Publishers</general><general>Springer Nature B.V</general><scope>FBQ</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>3V.</scope><scope>7X2</scope><scope>8FE</scope><scope>8FH</scope><scope>8FK</scope><scope>AEUYN</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BENPR</scope><scope>BHPHI</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>GNUQQ</scope><scope>HCIFZ</scope><scope>M0K</scope><scope>PATMY</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PYCSY</scope><scope>7ST</scope><scope>7U6</scope><scope>C1K</scope></search><sort><creationdate>20070501</creationdate><title>Methane and carbon dioxide emissions and nitrogen turnover during liquid manure storage</title><author>Sommer, Sven G ; Petersen, Søren O ; Sørensen, Peter ; Poulsen, Hanne D ; Møller, Henrik B</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c328t-9663881a53fb43c7c2f3a70b37435f150b570144aa9ade16c970d4e164d23d853</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2007</creationdate><topic>ambient temperature</topic><topic>anaerobic conditions</topic><topic>Anaerobic processes</topic><topic>Animal wastes</topic><topic>biodegradation</topic><topic>Bovidae</topic><topic>Carbon dioxide</topic><topic>Carbon dioxide emissions</topic><topic>Cattle</topic><topic>Cattle manure</topic><topic>composting</topic><topic>gas emissions</topic><topic>greenhouse gases</topic><topic>Inoculum</topic><topic>Liquid manure</topic><topic>mathematical models</topic><topic>Methane</topic><topic>Mineralization</topic><topic>Nitrogen</topic><topic>nitrogen turnover</topic><topic>Organic nitrogen</topic><topic>Pig manure</topic><topic>Slurries</topic><topic>storage</topic><topic>Swine</topic><topic>Temperature</topic><topic>Temperature effects</topic><topic>Vessels</topic><topic>volatile compounds</topic><topic>Volatile solids</topic><topic>waste lagoons</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Sommer, Sven G</creatorcontrib><creatorcontrib>Petersen, Søren O</creatorcontrib><creatorcontrib>Sørensen, Peter</creatorcontrib><creatorcontrib>Poulsen, Hanne D</creatorcontrib><creatorcontrib>Møller, Henrik B</creatorcontrib><collection>AGRIS</collection><collection>CrossRef</collection><collection>ProQuest Central (Corporate)</collection><collection>Agricultural Science Collection</collection><collection>ProQuest SciTech Collection</collection><collection>ProQuest Natural Science Collection</collection><collection>ProQuest Central (Alumni) (purchase pre-March 2016)</collection><collection>ProQuest One Sustainability</collection><collection>ProQuest Central UK/Ireland</collection><collection>Agricultural & Environmental Science Collection</collection><collection>ProQuest Central Essentials</collection><collection>ProQuest Central</collection><collection>Natural Science Collection</collection><collection>ProQuest One Community College</collection><collection>ProQuest Central Korea</collection><collection>ProQuest Central Student</collection><collection>SciTech Premium Collection</collection><collection>Agricultural Science Database</collection><collection>Environmental Science Database</collection><collection>ProQuest One Academic Eastern Edition (DO NOT USE)</collection><collection>ProQuest One Academic</collection><collection>ProQuest One Academic UKI Edition</collection><collection>Environmental Science Collection</collection><collection>Environment Abstracts</collection><collection>Sustainability Science Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><jtitle>Nutrient cycling in agroecosystems</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Sommer, Sven G</au><au>Petersen, Søren O</au><au>Sørensen, Peter</au><au>Poulsen, Hanne D</au><au>Møller, Henrik B</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Methane and carbon dioxide emissions and nitrogen turnover during liquid manure storage</atitle><jtitle>Nutrient cycling in agroecosystems</jtitle><date>2007-05-01</date><risdate>2007</risdate><volume>78</volume><issue>1</issue><spage>27</spage><epage>36</epage><pages>27-36</pages><issn>1385-1314</issn><eissn>1573-0867</eissn><abstract>Animal slurry stored in-house and outside is a significant source of atmospheric methane (CH₄). The CH₄ source strength of stored slurry is greatly affected by temperature. To improve emission calculations on a global scale there is a need for knowledge about the relationship between production of CH₄ in slurry and temperature. In this study, the filling of slurry channels was reproduced in the laboratory by gradually filling 1 m-high PVC vessels during 9 days followed by incubation for 100-200 days. A preliminary test showed that little CH₄ was produced from animal slurry during 10 days of incubation at 20°C, if no inoculum (slurry incubated anaerobically at the test temperature for 1.5-2 months) was present. However, the addition of 7.6% inoculum supported an immediate production of CH₄. Vessels amended with inoculum and gradually filled with cattle or pig slurry were then incubated at 10, 15 and 20°C. Methane production from stored pig and cattle slurry was not significant at temperatures below 15°C, where CO₂ was the main product of decomposition processes. In contrast, the anaerobic production of CH₄ was high and significant relative to the production of CO₂ at 20°C. Peak emissions of CH₄ averaging 0.012 and 0.02 g C h-¹ kg-¹ volatile solids (VS) were reached within about 10 days at 10 and 15°C, respectively. At 20°C, the emission of CH₄ from pig slurry was about 0.01 g C h-¹ kg-¹ for 10 days, and thereafter emissions increased to about 0.10 g C h-¹ kg-¹ VS. For cattle slurry a peak emission of 0.08 g C h-¹ kg-¹ VS was measured after 180 days. Degradation of organic nitrogen (N) in cattle slurry was related to the reduction of organic material as reflected in CO₂ and CH₄ emission. The mineralization of organic N during storage represented 10-80% of organic N in cattle slurry, and 40-80% of the organic N in pig slurry.</abstract><cop>Dordrecht</cop><pub>Dordrecht : Kluwer Academic Publishers</pub><doi>10.1007/s10705-006-9072-4</doi><tpages>10</tpages></addata></record> |
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subjects | ambient temperature anaerobic conditions Anaerobic processes Animal wastes biodegradation Bovidae Carbon dioxide Carbon dioxide emissions Cattle Cattle manure composting gas emissions greenhouse gases Inoculum Liquid manure mathematical models Methane Mineralization Nitrogen nitrogen turnover Organic nitrogen Pig manure Slurries storage Swine Temperature Temperature effects Vessels volatile compounds Volatile solids waste lagoons |
title | Methane and carbon dioxide emissions and nitrogen turnover during liquid manure storage |
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