Effect of dietary protein concentration on ammonia and greenhouse gas emitting potential of dairy manure

Two experiments were conducted to investigate the effect of dietary crude protein concentration on ammonia (NH3) and greenhouse gas (GHG; nitrous oxide, methane, and carbon dioxide) emissions from fresh dairy cow manure incubated in a controlled environment (experiment 1) and from manure-amended soi...

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Veröffentlicht in:Journal of dairy science 2012-04, Vol.95 (4), p.1930-1941
Hauptverfasser: Lee, C., Hristov, A.N., Dell, C.J., Feyereisen, G.W., Kaye, J., Beegle, D.
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container_end_page 1941
container_issue 4
container_start_page 1930
container_title Journal of dairy science
container_volume 95
creator Lee, C.
Hristov, A.N.
Dell, C.J.
Feyereisen, G.W.
Kaye, J.
Beegle, D.
description Two experiments were conducted to investigate the effect of dietary crude protein concentration on ammonia (NH3) and greenhouse gas (GHG; nitrous oxide, methane, and carbon dioxide) emissions from fresh dairy cow manure incubated in a controlled environment (experiment 1) and from manure-amended soil (experiment 2). Manure was prepared from feces and urine collected from lactating Holstein cows fed diets with 16.7% (DM basis; HCP) or 14.8% CP (LCP). High-CP manure had higher N content and proportion of NH3- and urea-N in total manure N than LCP manure (DM basis: 4.4 vs. 2.8% and 51.4 vs. 30.5%, respectively). In experiment 1, NH3 emitting potential (EP) was greater for HCP compared with LCP manure (9.20 vs. 4.88mg/m2 per min, respectively). The 122-h cumulative NH3 emission tended to be decreased 47% (P=0.09) using LCP compared with HCP manure. The EP and cumulative emissions of GHG were not different between HCP and LCP manure. In experiment 2, urine and feces from cows fed LCP or HCP diets were mixed and immediately applied to lysimeters (61×61×61cm; Hagerstown silt loam; fine, mixed, mesic Typic Hapludalf) at 277kg of N/ha application rate. The average NH3 EP (1.53 vs. 1.03mg/m2 per min, respectively) and the area under the EP curve were greater for lysimeters amended with HCP than with LCP manure. The largest difference in the NH3 EP occurred approximately 24h after manure application (approximately 3.5 times greater for HCP than LCP manure). The 100-h cumulative NH3 emission was 98% greater for HCP compared with LCP manure (7,415 vs. 3,745mg/m2, respectively). The EP of methane was increased and that of carbon dioxide tended to be increased by LCP compared with HCP manure. The cumulative methane emission was not different between treatments, whereas the cumulative carbon dioxide emission was increased with manure from the LCP diet. Nitrous oxide emissions were low in this experiment and did not differ between treatments. In the conditions of these experiments, fresh manure from dairy cows fed a LCP diet had substantially lower NH3 EP, compared with manure from cows fed a HCP diet. The LCP manure increased soil methane EP due to a larger mass of manure added to meet plant N requirements compared with HCP manure. These results represent effects of dietary protein on NH3 and GHG EP of manure in controlled laboratory conditions and do not account for environmental factors affecting gaseous emissions from manure on the farm.
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Manure was prepared from feces and urine collected from lactating Holstein cows fed diets with 16.7% (DM basis; HCP) or 14.8% CP (LCP). High-CP manure had higher N content and proportion of NH3- and urea-N in total manure N than LCP manure (DM basis: 4.4 vs. 2.8% and 51.4 vs. 30.5%, respectively). In experiment 1, NH3 emitting potential (EP) was greater for HCP compared with LCP manure (9.20 vs. 4.88mg/m2 per min, respectively). The 122-h cumulative NH3 emission tended to be decreased 47% (P=0.09) using LCP compared with HCP manure. The EP and cumulative emissions of GHG were not different between HCP and LCP manure. In experiment 2, urine and feces from cows fed LCP or HCP diets were mixed and immediately applied to lysimeters (61×61×61cm; Hagerstown silt loam; fine, mixed, mesic Typic Hapludalf) at 277kg of N/ha application rate. 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The LCP manure increased soil methane EP due to a larger mass of manure added to meet plant N requirements compared with HCP manure. These results represent effects of dietary protein on NH3 and GHG EP of manure in controlled laboratory conditions and do not account for environmental factors affecting gaseous emissions from manure on the farm.</description><identifier>ISSN: 0022-0302</identifier><identifier>EISSN: 1525-3198</identifier><identifier>DOI: 10.3168/jds.2010-4141</identifier><identifier>PMID: 22459840</identifier><identifier>CODEN: JDSCAE</identifier><language>eng</language><publisher>New York, NY: Elsevier Inc</publisher><subject>ammonia ; Ammonia - analysis ; Animal productions ; Animals ; application rate ; Biological and medical sciences ; carbon dioxide ; Carbon Dioxide - analysis ; Cattle - metabolism ; crude protein ; dairy cows ; dairy manure ; dietary protein ; Dietary Proteins - administration &amp; dosage ; Environment, Controlled ; environmental factors ; feces ; Female ; Food industries ; Fundamental and applied biological sciences. Psychology ; Greenhouse Effect ; greenhouse gas ; greenhouse gas emissions ; greenhouse gases ; Hapludalfs ; Holstein ; Lactation ; lysimeters ; Manure - analysis ; manure spreading ; methane ; Methane - analysis ; methane production ; Milk and cheese industries. Ice creams ; nitrous oxide ; Nitrous Oxide - analysis ; silt ; Soil ; Terrestrial animal productions ; urea nitrogen ; urine ; Vertebrates</subject><ispartof>Journal of dairy science, 2012-04, Vol.95 (4), p.1930-1941</ispartof><rights>2012 American Dairy Science Association</rights><rights>2015 INIST-CNRS</rights><rights>Copyright © 2012 American Dairy Science Association. Published by Elsevier Inc. 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Manure was prepared from feces and urine collected from lactating Holstein cows fed diets with 16.7% (DM basis; HCP) or 14.8% CP (LCP). High-CP manure had higher N content and proportion of NH3- and urea-N in total manure N than LCP manure (DM basis: 4.4 vs. 2.8% and 51.4 vs. 30.5%, respectively). In experiment 1, NH3 emitting potential (EP) was greater for HCP compared with LCP manure (9.20 vs. 4.88mg/m2 per min, respectively). The 122-h cumulative NH3 emission tended to be decreased 47% (P=0.09) using LCP compared with HCP manure. The EP and cumulative emissions of GHG were not different between HCP and LCP manure. In experiment 2, urine and feces from cows fed LCP or HCP diets were mixed and immediately applied to lysimeters (61×61×61cm; Hagerstown silt loam; fine, mixed, mesic Typic Hapludalf) at 277kg of N/ha application rate. The average NH3 EP (1.53 vs. 1.03mg/m2 per min, respectively) and the area under the EP curve were greater for lysimeters amended with HCP than with LCP manure. The largest difference in the NH3 EP occurred approximately 24h after manure application (approximately 3.5 times greater for HCP than LCP manure). The 100-h cumulative NH3 emission was 98% greater for HCP compared with LCP manure (7,415 vs. 3,745mg/m2, respectively). The EP of methane was increased and that of carbon dioxide tended to be increased by LCP compared with HCP manure. The cumulative methane emission was not different between treatments, whereas the cumulative carbon dioxide emission was increased with manure from the LCP diet. Nitrous oxide emissions were low in this experiment and did not differ between treatments. In the conditions of these experiments, fresh manure from dairy cows fed a LCP diet had substantially lower NH3 EP, compared with manure from cows fed a HCP diet. The LCP manure increased soil methane EP due to a larger mass of manure added to meet plant N requirements compared with HCP manure. These results represent effects of dietary protein on NH3 and GHG EP of manure in controlled laboratory conditions and do not account for environmental factors affecting gaseous emissions from manure on the farm.</description><subject>ammonia</subject><subject>Ammonia - analysis</subject><subject>Animal productions</subject><subject>Animals</subject><subject>application rate</subject><subject>Biological and medical sciences</subject><subject>carbon dioxide</subject><subject>Carbon Dioxide - analysis</subject><subject>Cattle - metabolism</subject><subject>crude protein</subject><subject>dairy cows</subject><subject>dairy manure</subject><subject>dietary protein</subject><subject>Dietary Proteins - administration &amp; dosage</subject><subject>Environment, Controlled</subject><subject>environmental factors</subject><subject>feces</subject><subject>Female</subject><subject>Food industries</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>Greenhouse Effect</subject><subject>greenhouse gas</subject><subject>greenhouse gas emissions</subject><subject>greenhouse gases</subject><subject>Hapludalfs</subject><subject>Holstein</subject><subject>Lactation</subject><subject>lysimeters</subject><subject>Manure - analysis</subject><subject>manure spreading</subject><subject>methane</subject><subject>Methane - analysis</subject><subject>methane production</subject><subject>Milk and cheese industries. Ice creams</subject><subject>nitrous oxide</subject><subject>Nitrous Oxide - analysis</subject><subject>silt</subject><subject>Soil</subject><subject>Terrestrial animal productions</subject><subject>urea nitrogen</subject><subject>urine</subject><subject>Vertebrates</subject><issn>0022-0302</issn><issn>1525-3198</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2012</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNp1kc9vFCEUx4mxsWv16FW5GE_T8nOGOZqm_kiaeGh7Jgw8tjQzzAqsif-9b91VTyYkhPDh-x6fR8gbzi4l783VU6iXgnHWKa74M7LhWuhO8tE8JxvGhOiYZOKcvKz1CY9cMP2CnAuh9GgU25DHmxjBN7pGGhI0V37SXVkbpEz9mj3kVlxLa6a43LKsOTnqcqDbApAf130FunWVwpJaS3lLd_g2t-Tm34kuYd7i8r7AK3IW3Vzh9Wm_IA-fbu6vv3S33z5_vf5423klZetACm-U5iKOahgHJUD5Kbg4xSiB60mowL3kU2DeDML3eD_qYQp6HEyv-CAvyIdjLn7j-x5qs0uqHubZZcB27dhLZUbGNJLdkfRlrbVAtLuSFjRgObMHtxbd2oNbe3CL_NtT8n5aIPyl_8hE4P0JcNW7ORaXfar_ON0rwYxB7t2Ri261bluQebjDOprhhAYzKiSGIwFo6keCYqtPgOMIqeC0bFjTf5r8Bb-rno4</recordid><startdate>20120401</startdate><enddate>20120401</enddate><creator>Lee, C.</creator><creator>Hristov, A.N.</creator><creator>Dell, C.J.</creator><creator>Feyereisen, G.W.</creator><creator>Kaye, J.</creator><creator>Beegle, D.</creator><general>Elsevier Inc</general><general>Elsevier</general><scope>6I.</scope><scope>AAFTH</scope><scope>FBQ</scope><scope>IQODW</scope><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7X8</scope></search><sort><creationdate>20120401</creationdate><title>Effect of dietary protein concentration on ammonia and greenhouse gas emitting potential of dairy manure</title><author>Lee, C. ; Hristov, A.N. ; Dell, C.J. ; Feyereisen, G.W. ; Kaye, J. ; Beegle, D.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c433t-e32c84512f9479742e4cbdafbff3e15b24d1c31bd0c872c62e4957bd597864173</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2012</creationdate><topic>ammonia</topic><topic>Ammonia - analysis</topic><topic>Animal productions</topic><topic>Animals</topic><topic>application rate</topic><topic>Biological and medical sciences</topic><topic>carbon dioxide</topic><topic>Carbon Dioxide - analysis</topic><topic>Cattle - metabolism</topic><topic>crude protein</topic><topic>dairy cows</topic><topic>dairy manure</topic><topic>dietary protein</topic><topic>Dietary Proteins - administration &amp; dosage</topic><topic>Environment, Controlled</topic><topic>environmental factors</topic><topic>feces</topic><topic>Female</topic><topic>Food industries</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>Greenhouse Effect</topic><topic>greenhouse gas</topic><topic>greenhouse gas emissions</topic><topic>greenhouse gases</topic><topic>Hapludalfs</topic><topic>Holstein</topic><topic>Lactation</topic><topic>lysimeters</topic><topic>Manure - analysis</topic><topic>manure spreading</topic><topic>methane</topic><topic>Methane - analysis</topic><topic>methane production</topic><topic>Milk and cheese industries. Ice creams</topic><topic>nitrous oxide</topic><topic>Nitrous Oxide - analysis</topic><topic>silt</topic><topic>Soil</topic><topic>Terrestrial animal productions</topic><topic>urea nitrogen</topic><topic>urine</topic><topic>Vertebrates</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Lee, C.</creatorcontrib><creatorcontrib>Hristov, A.N.</creatorcontrib><creatorcontrib>Dell, C.J.</creatorcontrib><creatorcontrib>Feyereisen, G.W.</creatorcontrib><creatorcontrib>Kaye, J.</creatorcontrib><creatorcontrib>Beegle, D.</creatorcontrib><collection>ScienceDirect Open Access Titles</collection><collection>Elsevier:ScienceDirect:Open Access</collection><collection>AGRIS</collection><collection>Pascal-Francis</collection><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>MEDLINE - Academic</collection><jtitle>Journal of dairy science</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Lee, C.</au><au>Hristov, A.N.</au><au>Dell, C.J.</au><au>Feyereisen, G.W.</au><au>Kaye, J.</au><au>Beegle, D.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Effect of dietary protein concentration on ammonia and greenhouse gas emitting potential of dairy manure</atitle><jtitle>Journal of dairy science</jtitle><addtitle>J Dairy Sci</addtitle><date>2012-04-01</date><risdate>2012</risdate><volume>95</volume><issue>4</issue><spage>1930</spage><epage>1941</epage><pages>1930-1941</pages><issn>0022-0302</issn><eissn>1525-3198</eissn><coden>JDSCAE</coden><abstract>Two experiments were conducted to investigate the effect of dietary crude protein concentration on ammonia (NH3) and greenhouse gas (GHG; nitrous oxide, methane, and carbon dioxide) emissions from fresh dairy cow manure incubated in a controlled environment (experiment 1) and from manure-amended soil (experiment 2). Manure was prepared from feces and urine collected from lactating Holstein cows fed diets with 16.7% (DM basis; HCP) or 14.8% CP (LCP). High-CP manure had higher N content and proportion of NH3- and urea-N in total manure N than LCP manure (DM basis: 4.4 vs. 2.8% and 51.4 vs. 30.5%, respectively). In experiment 1, NH3 emitting potential (EP) was greater for HCP compared with LCP manure (9.20 vs. 4.88mg/m2 per min, respectively). The 122-h cumulative NH3 emission tended to be decreased 47% (P=0.09) using LCP compared with HCP manure. The EP and cumulative emissions of GHG were not different between HCP and LCP manure. In experiment 2, urine and feces from cows fed LCP or HCP diets were mixed and immediately applied to lysimeters (61×61×61cm; Hagerstown silt loam; fine, mixed, mesic Typic Hapludalf) at 277kg of N/ha application rate. The average NH3 EP (1.53 vs. 1.03mg/m2 per min, respectively) and the area under the EP curve were greater for lysimeters amended with HCP than with LCP manure. The largest difference in the NH3 EP occurred approximately 24h after manure application (approximately 3.5 times greater for HCP than LCP manure). The 100-h cumulative NH3 emission was 98% greater for HCP compared with LCP manure (7,415 vs. 3,745mg/m2, respectively). The EP of methane was increased and that of carbon dioxide tended to be increased by LCP compared with HCP manure. The cumulative methane emission was not different between treatments, whereas the cumulative carbon dioxide emission was increased with manure from the LCP diet. Nitrous oxide emissions were low in this experiment and did not differ between treatments. In the conditions of these experiments, fresh manure from dairy cows fed a LCP diet had substantially lower NH3 EP, compared with manure from cows fed a HCP diet. The LCP manure increased soil methane EP due to a larger mass of manure added to meet plant N requirements compared with HCP manure. These results represent effects of dietary protein on NH3 and GHG EP of manure in controlled laboratory conditions and do not account for environmental factors affecting gaseous emissions from manure on the farm.</abstract><cop>New York, NY</cop><pub>Elsevier Inc</pub><pmid>22459840</pmid><doi>10.3168/jds.2010-4141</doi><tpages>12</tpages><oa>free_for_read</oa></addata></record>
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subjects ammonia
Ammonia - analysis
Animal productions
Animals
application rate
Biological and medical sciences
carbon dioxide
Carbon Dioxide - analysis
Cattle - metabolism
crude protein
dairy cows
dairy manure
dietary protein
Dietary Proteins - administration & dosage
Environment, Controlled
environmental factors
feces
Female
Food industries
Fundamental and applied biological sciences. Psychology
Greenhouse Effect
greenhouse gas
greenhouse gas emissions
greenhouse gases
Hapludalfs
Holstein
Lactation
lysimeters
Manure - analysis
manure spreading
methane
Methane - analysis
methane production
Milk and cheese industries. Ice creams
nitrous oxide
Nitrous Oxide - analysis
silt
Soil
Terrestrial animal productions
urea nitrogen
urine
Vertebrates
title Effect of dietary protein concentration on ammonia and greenhouse gas emitting potential of dairy manure
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