Nitrogen Dynamics in Irrigated Forage Systems Fertilized with Liquid Dairy Manure
Optimal manure management that ensures adequate crop nutrition while avoiding pollution problems requires estimates of manure N availability. The present study was performed in the San Joaquin Valley (California) on three dairy forage production fields where liquid manure is applied together with fl...
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| Veröffentlicht in: | Agronomy journal 2012-07, Vol.104 (4), p.897-907 |
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| creator | Geisseler, Daniel Lazicki, Patricia A Pettygrove, G. Stuart Ludwig, Bernard Bachand, Philip A.M Horwath, William R |
| description | Optimal manure management that ensures adequate crop nutrition while avoiding pollution problems requires estimates of manure N availability. The present study was performed in the San Joaquin Valley (California) on three dairy forage production fields where liquid manure is applied together with flood irrigation water. The objective of this study was to determine the fate of manure N by combining field measurements with model simulations using the Root Zone Water Quality Model (RZWQM). The average annual N application to corn (Zea mays L.) and winter forage (oat [Avena sativa L.], triticale [× Triticosecale Wittmack], or Sudan grass [Sorghum bicolor (L.) Moench ssp. drummondii (Steud.) de Wet ex Davidse]) was 840 kg N ha-1, while 490 kg N ha-1 was removed with the harvested crops. The irrigation water input to corn ranged from 45 to 128 cm. The RZWQM described crop yield and N uptake well and accurately simulated the seasonal trends in soil moisture and mineral N content in the top 90 cm of the profile; however, the short-term changes and mineral N estimates for different soil layers were not accurate. For soil nutrient and water dynamics, site-specific calibration was an essential requirement. The model estimated that between 140 and 320 kg N ha-1 was leached in a 12-mo period and up to 80 kg N ha-1 was volatilized as NH3, while losses due to denitrification were insignificant in these sandy soils. Field data and model estimates highlight the potential for a more efficient water and N use in the forage systems studied. |
| doi_str_mv | 10.2134/agronj2011.0362 |
| format | Article |
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Stuart ; Ludwig, Bernard ; Bachand, Philip A.M ; Horwath, William R</creator><creatorcontrib>Geisseler, Daniel ; Lazicki, Patricia A ; Pettygrove, G. Stuart ; Ludwig, Bernard ; Bachand, Philip A.M ; Horwath, William R</creatorcontrib><description>Optimal manure management that ensures adequate crop nutrition while avoiding pollution problems requires estimates of manure N availability. The present study was performed in the San Joaquin Valley (California) on three dairy forage production fields where liquid manure is applied together with flood irrigation water. The objective of this study was to determine the fate of manure N by combining field measurements with model simulations using the Root Zone Water Quality Model (RZWQM). The average annual N application to corn (Zea mays L.) and winter forage (oat [Avena sativa L.], triticale [× Triticosecale Wittmack], or Sudan grass [Sorghum bicolor (L.) Moench ssp. drummondii (Steud.) de Wet ex Davidse]) was 840 kg N ha-1, while 490 kg N ha-1 was removed with the harvested crops. The irrigation water input to corn ranged from 45 to 128 cm. The RZWQM described crop yield and N uptake well and accurately simulated the seasonal trends in soil moisture and mineral N content in the top 90 cm of the profile; however, the short-term changes and mineral N estimates for different soil layers were not accurate. For soil nutrient and water dynamics, site-specific calibration was an essential requirement. The model estimated that between 140 and 320 kg N ha-1 was leached in a 12-mo period and up to 80 kg N ha-1 was volatilized as NH3, while losses due to denitrification were insignificant in these sandy soils. Field data and model estimates highlight the potential for a more efficient water and N use in the forage systems studied.</description><identifier>ISSN: 0002-1962</identifier><identifier>EISSN: 1435-0645</identifier><identifier>DOI: 10.2134/agronj2011.0362</identifier><identifier>CODEN: AGJOAT</identifier><language>eng</language><publisher>Madison, WI: American Society of Agronomy</publisher><subject>Agronomy. Soil science and plant productions ; animal manure management ; Animal productions ; Avena sativa ; Biological and medical sciences ; crop yield ; crops ; dairy manure ; denitrification ; flood irrigation ; forage ; forage production ; Fundamental and applied biological sciences. Psychology ; Irrigation systems ; irrigation water ; liquid manure ; nitrogen ; nitrogen content ; nutrition ; oats ; pollution ; Root Zone Water Quality Model ; sandy soils ; simulation models ; soil water ; Sorghum bicolor subsp. drummondii ; Terrestrial animal productions ; triticale ; Triticosecale ; Vertebrates ; Zea mays</subject><ispartof>Agronomy journal, 2012-07, Vol.104 (4), p.897-907</ispartof><rights>Copyright © 2012 by the American Society of Agronomy, Inc.</rights><rights>2015 INIST-CNRS</rights><rights>Copyright American Society of Agronomy Jul 2012</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c3792-bd95139e19b40aa675f2087b5edfe70554a74faf199f3c79c4304b82058a291e3</citedby><cites>FETCH-LOGICAL-c3792-bd95139e19b40aa675f2087b5edfe70554a74faf199f3c79c4304b82058a291e3</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://onlinelibrary.wiley.com/doi/pdf/10.2134%2Fagronj2011.0362$$EPDF$$P50$$Gwiley$$H</linktopdf><linktohtml>$$Uhttps://onlinelibrary.wiley.com/doi/full/10.2134%2Fagronj2011.0362$$EHTML$$P50$$Gwiley$$H</linktohtml><link.rule.ids>314,776,780,1411,27901,27902,45550,45551</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=26176873$$DView record in Pascal Francis$$Hfree_for_read</backlink></links><search><creatorcontrib>Geisseler, Daniel</creatorcontrib><creatorcontrib>Lazicki, Patricia A</creatorcontrib><creatorcontrib>Pettygrove, G. Stuart</creatorcontrib><creatorcontrib>Ludwig, Bernard</creatorcontrib><creatorcontrib>Bachand, Philip A.M</creatorcontrib><creatorcontrib>Horwath, William R</creatorcontrib><title>Nitrogen Dynamics in Irrigated Forage Systems Fertilized with Liquid Dairy Manure</title><title>Agronomy journal</title><description>Optimal manure management that ensures adequate crop nutrition while avoiding pollution problems requires estimates of manure N availability. The present study was performed in the San Joaquin Valley (California) on three dairy forage production fields where liquid manure is applied together with flood irrigation water. The objective of this study was to determine the fate of manure N by combining field measurements with model simulations using the Root Zone Water Quality Model (RZWQM). The average annual N application to corn (Zea mays L.) and winter forage (oat [Avena sativa L.], triticale [× Triticosecale Wittmack], or Sudan grass [Sorghum bicolor (L.) Moench ssp. drummondii (Steud.) de Wet ex Davidse]) was 840 kg N ha-1, while 490 kg N ha-1 was removed with the harvested crops. The irrigation water input to corn ranged from 45 to 128 cm. The RZWQM described crop yield and N uptake well and accurately simulated the seasonal trends in soil moisture and mineral N content in the top 90 cm of the profile; however, the short-term changes and mineral N estimates for different soil layers were not accurate. For soil nutrient and water dynamics, site-specific calibration was an essential requirement. The model estimated that between 140 and 320 kg N ha-1 was leached in a 12-mo period and up to 80 kg N ha-1 was volatilized as NH3, while losses due to denitrification were insignificant in these sandy soils. Field data and model estimates highlight the potential for a more efficient water and N use in the forage systems studied.</description><subject>Agronomy. Soil science and plant productions</subject><subject>animal manure management</subject><subject>Animal productions</subject><subject>Avena sativa</subject><subject>Biological and medical sciences</subject><subject>crop yield</subject><subject>crops</subject><subject>dairy manure</subject><subject>denitrification</subject><subject>flood irrigation</subject><subject>forage</subject><subject>forage production</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>Irrigation systems</subject><subject>irrigation water</subject><subject>liquid manure</subject><subject>nitrogen</subject><subject>nitrogen content</subject><subject>nutrition</subject><subject>oats</subject><subject>pollution</subject><subject>Root Zone Water Quality Model</subject><subject>sandy soils</subject><subject>simulation models</subject><subject>soil water</subject><subject>Sorghum bicolor subsp. drummondii</subject><subject>Terrestrial animal productions</subject><subject>triticale</subject><subject>Triticosecale</subject><subject>Vertebrates</subject><subject>Zea mays</subject><issn>0002-1962</issn><issn>1435-0645</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2012</creationdate><recordtype>article</recordtype><sourceid>8G5</sourceid><sourceid>BEC</sourceid><sourceid>BENPR</sourceid><sourceid>GUQSH</sourceid><sourceid>M2O</sourceid><recordid>eNqFkc1PAjEQxRujifhx9mgT43Gxn9vtyRARlKBEkfNmWFosgV1pl5D1r7cEokdPk8z83nvJG4SuKGkzysUdzH1VLhihtE14yo5QiwouE5IKeYxahBCWUJ2yU3QWwoJETAvaQm-vrvbV3JS425SwckXArsTP3rs51GaGe5WHucHjJtRmFXDP-Not3Xe8bF39iYduvXEz3AXnG_wC5cabC3RiYRnM5WGeo0nv8ePhKRmO-s8PnWFScKVZMp1pSbk2VE8FAUiVtIxkairNzBpFpBSghAVLtba8ULoQnIhpxojMgGlq-Dm62ft--Wq9MaHOF9XGlzEyp4QJKmiqdKTu9lThqxC8sfmXdyvwTYTyXW_5X2_5rreouD34QihgaT2UhQu_MpZSlWaKR-5-z23d0jT_2ead_oB1-u-j18Fud0i63jtYqHZ8TJmM41XGZ0mRZSn_AfJiidY</recordid><startdate>201207</startdate><enddate>201207</enddate><creator>Geisseler, Daniel</creator><creator>Lazicki, Patricia A</creator><creator>Pettygrove, G. 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Psychology</topic><topic>Irrigation systems</topic><topic>irrigation water</topic><topic>liquid manure</topic><topic>nitrogen</topic><topic>nitrogen content</topic><topic>nutrition</topic><topic>oats</topic><topic>pollution</topic><topic>Root Zone Water Quality Model</topic><topic>sandy soils</topic><topic>simulation models</topic><topic>soil water</topic><topic>Sorghum bicolor subsp. drummondii</topic><topic>Terrestrial animal productions</topic><topic>triticale</topic><topic>Triticosecale</topic><topic>Vertebrates</topic><topic>Zea mays</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Geisseler, Daniel</creatorcontrib><creatorcontrib>Lazicki, Patricia A</creatorcontrib><creatorcontrib>Pettygrove, G. 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Stuart</au><au>Ludwig, Bernard</au><au>Bachand, Philip A.M</au><au>Horwath, William R</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Nitrogen Dynamics in Irrigated Forage Systems Fertilized with Liquid Dairy Manure</atitle><jtitle>Agronomy journal</jtitle><date>2012-07</date><risdate>2012</risdate><volume>104</volume><issue>4</issue><spage>897</spage><epage>907</epage><pages>897-907</pages><issn>0002-1962</issn><eissn>1435-0645</eissn><coden>AGJOAT</coden><abstract>Optimal manure management that ensures adequate crop nutrition while avoiding pollution problems requires estimates of manure N availability. The present study was performed in the San Joaquin Valley (California) on three dairy forage production fields where liquid manure is applied together with flood irrigation water. The objective of this study was to determine the fate of manure N by combining field measurements with model simulations using the Root Zone Water Quality Model (RZWQM). The average annual N application to corn (Zea mays L.) and winter forage (oat [Avena sativa L.], triticale [× Triticosecale Wittmack], or Sudan grass [Sorghum bicolor (L.) Moench ssp. drummondii (Steud.) de Wet ex Davidse]) was 840 kg N ha-1, while 490 kg N ha-1 was removed with the harvested crops. The irrigation water input to corn ranged from 45 to 128 cm. The RZWQM described crop yield and N uptake well and accurately simulated the seasonal trends in soil moisture and mineral N content in the top 90 cm of the profile; however, the short-term changes and mineral N estimates for different soil layers were not accurate. For soil nutrient and water dynamics, site-specific calibration was an essential requirement. The model estimated that between 140 and 320 kg N ha-1 was leached in a 12-mo period and up to 80 kg N ha-1 was volatilized as NH3, while losses due to denitrification were insignificant in these sandy soils. Field data and model estimates highlight the potential for a more efficient water and N use in the forage systems studied.</abstract><cop>Madison, WI</cop><pub>American Society of Agronomy</pub><doi>10.2134/agronj2011.0362</doi><tpages>11</tpages></addata></record> |
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| subjects | Agronomy. Soil science and plant productions animal manure management Animal productions Avena sativa Biological and medical sciences crop yield crops dairy manure denitrification flood irrigation forage forage production Fundamental and applied biological sciences. Psychology Irrigation systems irrigation water liquid manure nitrogen nitrogen content nutrition oats pollution Root Zone Water Quality Model sandy soils simulation models soil water Sorghum bicolor subsp. drummondii Terrestrial animal productions triticale Triticosecale Vertebrates Zea mays |
| title | Nitrogen Dynamics in Irrigated Forage Systems Fertilized with Liquid Dairy Manure |
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