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Swine Effluent Irrigation Rate and Timing Effects on Bermudagrass Growth, Nitrogen and Phosphorus Utilization, and Residual Soil Nitrogen
Maximizing utilization of effluent nutrients by forage grasses requires a better understanding of irrigation rate and timing effects. This study was conducted in 1998 and 1999 on a Vaiden silty clay (very-fine, smectitic, thermic Aquic Dystrudert) soil to determine the effects of swine lagoon efflue...
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Published in: | Journal of environmental quality 2003-03, Vol.32 (2), p.681-686 |
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description | Maximizing utilization of effluent nutrients by forage grasses requires a better understanding of irrigation rate and timing effects. This study was conducted in 1998 and 1999 on a Vaiden silty clay (very-fine, smectitic, thermic Aquic Dystrudert) soil to determine the effects of swine lagoon effluent irrigation rate and timing on bermudagrass [Cynodon dactylon (L.) Pers.] growth, nitrogen (N) and phosphorus (P) recovery, and postseason soil profile NO3− –N. Treatments consisted of swine effluent irrigation at the rates of 0, 5, 10, 15, and 20 ha-cm. Two additional treatments included 2.5 ha-cm applied on 1 September and 1 October in addition to a base summer rate of 10 ha-cm. In both years for early to mid-season irrigation, bermudagrass dry matter yield quadratically increased with increasing swine effluent irrigation rates. Averaged across years, effluent irrigation in October resulted in 30% less dry matter than in September. For late-season irrigation, apparent N recovery averaged 59% less and P recovery averaged 46% less with a delay in irrigation from 1 September to 1 October. The greatest quantity of soil NO3− –N was associated with both the greatest effluent rate and October irrigation treatments. Minimal yield benefit was obtained when effluent was applied at rates greater than 10 ha-cm during the summer months. Late-season irrigation, especially after 1 October for areas with similar climatic conditions, should be avoided to maximize synchronization of nutrient availability with maximum growth rates to minimize potential offsite movement of residual soil N and P. |
doi_str_mv | 10.2134/jeq2003.0681 |
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This study was conducted in 1998 and 1999 on a Vaiden silty clay (very-fine, smectitic, thermic Aquic Dystrudert) soil to determine the effects of swine lagoon effluent irrigation rate and timing on bermudagrass [Cynodon dactylon (L.) Pers.] growth, nitrogen (N) and phosphorus (P) recovery, and postseason soil profile NO3− –N. Treatments consisted of swine effluent irrigation at the rates of 0, 5, 10, 15, and 20 ha-cm. Two additional treatments included 2.5 ha-cm applied on 1 September and 1 October in addition to a base summer rate of 10 ha-cm. In both years for early to mid-season irrigation, bermudagrass dry matter yield quadratically increased with increasing swine effluent irrigation rates. Averaged across years, effluent irrigation in October resulted in 30% less dry matter than in September. For late-season irrigation, apparent N recovery averaged 59% less and P recovery averaged 46% less with a delay in irrigation from 1 September to 1 October. The greatest quantity of soil NO3− –N was associated with both the greatest effluent rate and October irrigation treatments. Minimal yield benefit was obtained when effluent was applied at rates greater than 10 ha-cm during the summer months. Late-season irrigation, especially after 1 October for areas with similar climatic conditions, should be avoided to maximize synchronization of nutrient availability with maximum growth rates to minimize potential offsite movement of residual soil N and P.</description><identifier>ISSN: 0047-2425</identifier><identifier>ISSN: 1537-2537</identifier><identifier>EISSN: 1537-2537</identifier><identifier>DOI: 10.2134/jeq2003.0681</identifier><identifier>PMID: 12708693</identifier><identifier>CODEN: JEVQAA</identifier><language>eng</language><publisher>Madison, WI: Crop Science Society of America</publisher><subject>Agricultural and forest climatology and meteorology. Irrigation. Drainage ; Agriculture ; Agronomy. Soil science and plant productions ; Animals ; Biological and medical sciences ; Climatic conditions ; Cynodon - growth & development ; Dry matter ; Effluents ; Fundamental and applied biological sciences. Psychology ; General agronomy. Plant production ; Impaired water use ; Irrigation. Drainage ; Lagoons ; Manure ; Nitrogen ; Nitrogen - analysis ; Nitrogen - metabolism ; Nutrient availability ; Other nutrients. Amendments. Solid and liquid wastes. Sludges and slurries ; Phosphorus - analysis ; Phosphorus - metabolism ; Residual soils ; Seasons ; Soil Pollutants - analysis ; Soil Pollutants - metabolism ; Soil profiles ; Soil-plant relationships. Soil fertility. Fertilization. Amendments ; Summer ; Swine ; Waste Disposal, Fluid ; Wastewater irrigation ; Water Supply</subject><ispartof>Journal of environmental quality, 2003-03, Vol.32 (2), p.681-686</ispartof><rights>2003 INIST-CNRS</rights><rights>Copyright American Society of Agronomy Mar/Apr 2003</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c460t-e15b6bb934cead8c1b62d70e3c30a132cde689ab9c28d7798ceb5713cb569cdb3</citedby></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,776,780,27903,27904</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=14611973$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/12708693$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Adeli, A</creatorcontrib><creatorcontrib>Varco, J.J</creatorcontrib><creatorcontrib>Rowe, D.E</creatorcontrib><title>Swine Effluent Irrigation Rate and Timing Effects on Bermudagrass Growth, Nitrogen and Phosphorus Utilization, and Residual Soil Nitrogen</title><title>Journal of environmental quality</title><addtitle>J Environ Qual</addtitle><description>Maximizing utilization of effluent nutrients by forage grasses requires a better understanding of irrigation rate and timing effects. This study was conducted in 1998 and 1999 on a Vaiden silty clay (very-fine, smectitic, thermic Aquic Dystrudert) soil to determine the effects of swine lagoon effluent irrigation rate and timing on bermudagrass [Cynodon dactylon (L.) Pers.] growth, nitrogen (N) and phosphorus (P) recovery, and postseason soil profile NO3− –N. Treatments consisted of swine effluent irrigation at the rates of 0, 5, 10, 15, and 20 ha-cm. Two additional treatments included 2.5 ha-cm applied on 1 September and 1 October in addition to a base summer rate of 10 ha-cm. In both years for early to mid-season irrigation, bermudagrass dry matter yield quadratically increased with increasing swine effluent irrigation rates. Averaged across years, effluent irrigation in October resulted in 30% less dry matter than in September. For late-season irrigation, apparent N recovery averaged 59% less and P recovery averaged 46% less with a delay in irrigation from 1 September to 1 October. The greatest quantity of soil NO3− –N was associated with both the greatest effluent rate and October irrigation treatments. Minimal yield benefit was obtained when effluent was applied at rates greater than 10 ha-cm during the summer months. Late-season irrigation, especially after 1 October for areas with similar climatic conditions, should be avoided to maximize synchronization of nutrient availability with maximum growth rates to minimize potential offsite movement of residual soil N and P.</description><subject>Agricultural and forest climatology and meteorology. Irrigation. Drainage</subject><subject>Agriculture</subject><subject>Agronomy. Soil science and plant productions</subject><subject>Animals</subject><subject>Biological and medical sciences</subject><subject>Climatic conditions</subject><subject>Cynodon - growth & development</subject><subject>Dry matter</subject><subject>Effluents</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>General agronomy. Plant production</subject><subject>Impaired water use</subject><subject>Irrigation. Drainage</subject><subject>Lagoons</subject><subject>Manure</subject><subject>Nitrogen</subject><subject>Nitrogen - analysis</subject><subject>Nitrogen - metabolism</subject><subject>Nutrient availability</subject><subject>Other nutrients. Amendments. Solid and liquid wastes. Sludges and slurries</subject><subject>Phosphorus - analysis</subject><subject>Phosphorus - metabolism</subject><subject>Residual soils</subject><subject>Seasons</subject><subject>Soil Pollutants - analysis</subject><subject>Soil Pollutants - metabolism</subject><subject>Soil profiles</subject><subject>Soil-plant relationships. Soil fertility. Fertilization. Amendments</subject><subject>Summer</subject><subject>Swine</subject><subject>Waste Disposal, Fluid</subject><subject>Wastewater irrigation</subject><subject>Water Supply</subject><issn>0047-2425</issn><issn>1537-2537</issn><issn>1537-2537</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2003</creationdate><recordtype>article</recordtype><recordid>eNqF0c9v0zAUB3ALgVi3ceMMFtI4tcM_Ejs-smmMSRNM63qOHOeldZXEne1oGv8B_zVOGzGJCxfb0vu8Z1tfhN5Tcs4oz75s4ZERws-JKOgrNKM5lwuWltdoRkiWzhnLj9BxCFtCKCNSvEVHlElSCMVn6PfyyfaAr5qmHaCP-MZ7u9bRuh7f6whY9zV-sJ3t16MBEwNOpQvw3VDrtdch4GvvnuJmjn_Y6N0a-n3P3caF3cb5IeBVtK39tZ8539fuIdh60C1eOtv-bTtFbxrdBng37Sdo9e3q4fL74vbn9c3l19uFyQSJC6B5JapK8cyArgtDK8FqSYAbTjTlzNQgCqUrZVhRS6kKA1UuKTdVLpSpK36CPh_m7rx7HCDEsrPBQNvqHtwQSiqoZCTj_4eZEJQxluCnf-DWDb5PnyipklxxQlVC8wMy3oXgoSl33nbaP5eUlGOQ5RRkOQaZ-Idp5lB1UL_gKbkEziagg9Ft43VvbHhxmaDj5cl9PLhGuzIllsxqyQgdH5UXUuX8D-9zsHA</recordid><startdate>20030301</startdate><enddate>20030301</enddate><creator>Adeli, A</creator><creator>Varco, J.J</creator><creator>Rowe, D.E</creator><general>Crop Science Society of America</general><general>American Society of Agronomy</general><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>3V.</scope><scope>7ST</scope><scope>7T7</scope><scope>7TG</scope><scope>7X2</scope><scope>7X7</scope><scope>7XB</scope><scope>88E</scope><scope>88I</scope><scope>8AF</scope><scope>8AO</scope><scope>8C1</scope><scope>8FD</scope><scope>8FE</scope><scope>8FG</scope><scope>8FH</scope><scope>8FI</scope><scope>8FJ</scope><scope>8FK</scope><scope>8G5</scope><scope>ABJCF</scope><scope>ABUWG</scope><scope>AEUYN</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BEC</scope><scope>BENPR</scope><scope>BGLVJ</scope><scope>BHPHI</scope><scope>C1K</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>FR3</scope><scope>FYUFA</scope><scope>GHDGH</scope><scope>GNUQQ</scope><scope>GUQSH</scope><scope>HCIFZ</scope><scope>K9.</scope><scope>KL.</scope><scope>L6V</scope><scope>M0K</scope><scope>M0S</scope><scope>M1P</scope><scope>M2O</scope><scope>M2P</scope><scope>M7S</scope><scope>MBDVC</scope><scope>P64</scope><scope>PATMY</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>PTHSS</scope><scope>PYCSY</scope><scope>Q9U</scope><scope>S0X</scope><scope>SOI</scope><scope>7QH</scope><scope>7UA</scope></search><sort><creationdate>20030301</creationdate><title>Swine Effluent Irrigation Rate and Timing Effects on Bermudagrass Growth, Nitrogen and Phosphorus Utilization, and Residual Soil Nitrogen</title><author>Adeli, A ; Varco, J.J ; Rowe, D.E</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c460t-e15b6bb934cead8c1b62d70e3c30a132cde689ab9c28d7798ceb5713cb569cdb3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2003</creationdate><topic>Agricultural and forest climatology and meteorology. Irrigation. Drainage</topic><topic>Agriculture</topic><topic>Agronomy. Soil science and plant productions</topic><topic>Animals</topic><topic>Biological and medical sciences</topic><topic>Climatic conditions</topic><topic>Cynodon - growth & development</topic><topic>Dry matter</topic><topic>Effluents</topic><topic>Fundamental and applied biological sciences. Psychology</topic><topic>General agronomy. Plant production</topic><topic>Impaired water use</topic><topic>Irrigation. Drainage</topic><topic>Lagoons</topic><topic>Manure</topic><topic>Nitrogen</topic><topic>Nitrogen - analysis</topic><topic>Nitrogen - metabolism</topic><topic>Nutrient availability</topic><topic>Other nutrients. Amendments. Solid and liquid wastes. Sludges and slurries</topic><topic>Phosphorus - analysis</topic><topic>Phosphorus - metabolism</topic><topic>Residual soils</topic><topic>Seasons</topic><topic>Soil Pollutants - analysis</topic><topic>Soil Pollutants - metabolism</topic><topic>Soil profiles</topic><topic>Soil-plant relationships. Soil fertility. Fertilization. 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This study was conducted in 1998 and 1999 on a Vaiden silty clay (very-fine, smectitic, thermic Aquic Dystrudert) soil to determine the effects of swine lagoon effluent irrigation rate and timing on bermudagrass [Cynodon dactylon (L.) Pers.] growth, nitrogen (N) and phosphorus (P) recovery, and postseason soil profile NO3− –N. Treatments consisted of swine effluent irrigation at the rates of 0, 5, 10, 15, and 20 ha-cm. Two additional treatments included 2.5 ha-cm applied on 1 September and 1 October in addition to a base summer rate of 10 ha-cm. In both years for early to mid-season irrigation, bermudagrass dry matter yield quadratically increased with increasing swine effluent irrigation rates. Averaged across years, effluent irrigation in October resulted in 30% less dry matter than in September. For late-season irrigation, apparent N recovery averaged 59% less and P recovery averaged 46% less with a delay in irrigation from 1 September to 1 October. The greatest quantity of soil NO3− –N was associated with both the greatest effluent rate and October irrigation treatments. Minimal yield benefit was obtained when effluent was applied at rates greater than 10 ha-cm during the summer months. Late-season irrigation, especially after 1 October for areas with similar climatic conditions, should be avoided to maximize synchronization of nutrient availability with maximum growth rates to minimize potential offsite movement of residual soil N and P.</abstract><cop>Madison, WI</cop><pub>Crop Science Society of America</pub><pmid>12708693</pmid><doi>10.2134/jeq2003.0681</doi><tpages>6</tpages></addata></record> |
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subjects | Agricultural and forest climatology and meteorology. Irrigation. Drainage Agriculture Agronomy. Soil science and plant productions Animals Biological and medical sciences Climatic conditions Cynodon - growth & development Dry matter Effluents Fundamental and applied biological sciences. Psychology General agronomy. Plant production Impaired water use Irrigation. Drainage Lagoons Manure Nitrogen Nitrogen - analysis Nitrogen - metabolism Nutrient availability Other nutrients. Amendments. Solid and liquid wastes. Sludges and slurries Phosphorus - analysis Phosphorus - metabolism Residual soils Seasons Soil Pollutants - analysis Soil Pollutants - metabolism Soil profiles Soil-plant relationships. Soil fertility. Fertilization. Amendments Summer Swine Waste Disposal, Fluid Wastewater irrigation Water Supply |
title | Swine Effluent Irrigation Rate and Timing Effects on Bermudagrass Growth, Nitrogen and Phosphorus Utilization, and Residual Soil Nitrogen |
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