The Influence of Vegetation in Riparian Filterstrips on Coliform Bacteria: I. Movement and Survival in Water
Swine (Sus scrofa) wastewater was applied to three separate 4 m wide × 30 m long riparian filterstrips consisting of 20 m grass and 10 m forest, 10 m grass and 20 m forest, and 10 m grass and 20 m maidencane (Panicum hemitomon Schult.) in Southern Georgia during each season. Total and fecal coliform...
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description | Swine (Sus scrofa) wastewater was applied to three separate 4 m wide × 30 m long riparian filterstrips consisting of 20 m grass and 10 m forest, 10 m grass and 20 m forest, and 10 m grass and 20 m maidencane (Panicum hemitomon Schult.) in Southern Georgia during each season. Total and fecal coliform numbers in the applied wastewater pulse did not decline as water moved downslope regardless of vegetation type or season. The pulse of applied wastewater did not move beyond 15 m in any treatment in autumn or summer (dry seasons) and only moved beyond 7.5 m in the 20 m grass‐10 m forest treatment in the summer. Total and fecal coliform numbers in soil water and shallow ground water declined by approximately 10‐fold every 7 d for the first 14 d regardless of vegetative treatment or season. Soil temperature and soil moisture correlated with total coliform bacteria in both 1.5 m wells (r2 = 0.89) and 2.0 m wells (r2 = 0.89), and with fecal coliform bacteria in 1.5 (r2 = 0.82) and 2.0 m (r2 = 0.76) wells. Animal production operations may need to locate in warm‐dry climates so animal waste can be applied to lands to help ensure enteric bacteria input to surface and ground water will not occur. |
doi_str_mv | 10.2134/jeq2000.00472425002900040026x |
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Movement and Survival in Water</title><source>Wiley Online Library Journals Frontfile Complete</source><creator>Entry, James A. ; Hubbard, Robert K. ; Thies, Janice E. ; Fuhrmann, Jeffry J.</creator><creatorcontrib>Entry, James A. ; Hubbard, Robert K. ; Thies, Janice E. ; Fuhrmann, Jeffry J.</creatorcontrib><description>Swine (Sus scrofa) wastewater was applied to three separate 4 m wide × 30 m long riparian filterstrips consisting of 20 m grass and 10 m forest, 10 m grass and 20 m forest, and 10 m grass and 20 m maidencane (Panicum hemitomon Schult.) in Southern Georgia during each season. Total and fecal coliform numbers in the applied wastewater pulse did not decline as water moved downslope regardless of vegetation type or season. The pulse of applied wastewater did not move beyond 15 m in any treatment in autumn or summer (dry seasons) and only moved beyond 7.5 m in the 20 m grass‐10 m forest treatment in the summer. Total and fecal coliform numbers in soil water and shallow ground water declined by approximately 10‐fold every 7 d for the first 14 d regardless of vegetative treatment or season. Soil temperature and soil moisture correlated with total coliform bacteria in both 1.5 m wells (r2 = 0.89) and 2.0 m wells (r2 = 0.89), and with fecal coliform bacteria in 1.5 (r2 = 0.82) and 2.0 m (r2 = 0.76) wells. Animal production operations may need to locate in warm‐dry climates so animal waste can be applied to lands to help ensure enteric bacteria input to surface and ground water will not occur.</description><identifier>ISSN: 0047-2425</identifier><identifier>EISSN: 1537-2537</identifier><identifier>DOI: 10.2134/jeq2000.00472425002900040026x</identifier><identifier>CODEN: JEVQAA</identifier><language>eng</language><publisher>Madison, WI: American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America</publisher><subject>Agronomy. Soil science and plant productions ; Applied sciences ; Biological and medical sciences ; Continental surface waters ; Earth sciences ; Earth, ocean, space ; Engineering and environment geology. Geothermics ; Exact sciences and technology ; Fundamental and applied biological sciences. Psychology ; Groundwaters ; Natural water pollution ; Panicum hemitomon ; Pollution ; Pollution, environment geology ; Riparian vegetation ; Soil and water pollution ; Soil science ; Sus scrofa ; USA, Georgia ; Water treatment and pollution</subject><ispartof>Journal of environmental quality, 2000-07, Vol.29 (4), p.1206-1214</ispartof><rights>2000 American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America</rights><rights>2001 INIST-CNRS</rights><rights>Copyright American Society of Agronomy, Inc. 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Movement and Survival in Water</title><title>Journal of environmental quality</title><description>Swine (Sus scrofa) wastewater was applied to three separate 4 m wide × 30 m long riparian filterstrips consisting of 20 m grass and 10 m forest, 10 m grass and 20 m forest, and 10 m grass and 20 m maidencane (Panicum hemitomon Schult.) in Southern Georgia during each season. Total and fecal coliform numbers in the applied wastewater pulse did not decline as water moved downslope regardless of vegetation type or season. The pulse of applied wastewater did not move beyond 15 m in any treatment in autumn or summer (dry seasons) and only moved beyond 7.5 m in the 20 m grass‐10 m forest treatment in the summer. Total and fecal coliform numbers in soil water and shallow ground water declined by approximately 10‐fold every 7 d for the first 14 d regardless of vegetative treatment or season. Soil temperature and soil moisture correlated with total coliform bacteria in both 1.5 m wells (r2 = 0.89) and 2.0 m wells (r2 = 0.89), and with fecal coliform bacteria in 1.5 (r2 = 0.82) and 2.0 m (r2 = 0.76) wells. Animal production operations may need to locate in warm‐dry climates so animal waste can be applied to lands to help ensure enteric bacteria input to surface and ground water will not occur.</description><subject>Agronomy. Soil science and plant productions</subject><subject>Applied sciences</subject><subject>Biological and medical sciences</subject><subject>Continental surface waters</subject><subject>Earth sciences</subject><subject>Earth, ocean, space</subject><subject>Engineering and environment geology. Geothermics</subject><subject>Exact sciences and technology</subject><subject>Fundamental and applied biological sciences. Psychology</subject><subject>Groundwaters</subject><subject>Natural water pollution</subject><subject>Panicum hemitomon</subject><subject>Pollution</subject><subject>Pollution, environment geology</subject><subject>Riparian vegetation</subject><subject>Soil and water pollution</subject><subject>Soil science</subject><subject>Sus scrofa</subject><subject>USA, Georgia</subject><subject>Water treatment and pollution</subject><issn>0047-2425</issn><issn>1537-2537</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2000</creationdate><recordtype>article</recordtype><sourceid>8G5</sourceid><sourceid>BEC</sourceid><sourceid>BENPR</sourceid><sourceid>GUQSH</sourceid><sourceid>M2O</sourceid><recordid>eNqV0V9rFDEQAPBFFDyr3yEo-rbX_N1cBB_s0epJRdSqBR-WaXZWc-SSa7J72m_fLHf4oIIYSIYwv8wQpqqeMjrnTMjjNV5zSumcUqm55IpSbspdltj8vFPNmBK65uW4W80mU0_ofvUg5zWljFPdzCp_8R3JKvR-xGCRxJ58xm84wOBiIC6QD24LyUEgZ84PmPKQ3DaTkltG7_qYNuQEbEk4eE5Wc_I27nCDYSAQOvJxTDu3Az_V-QIFPazu9eAzPjrEo-rT2enF8nV9_u7VavnyvLaKi8t6YY2xSi8MNdh1gmFnrjqDDdhO6UaB5FSCZJ1daLUwVioAdQVC9Fw2aHsujqpn-7rbFK9HzEO7cdmi9xAwjrnllCkjGP0nZFLJppGqwMe_wXUcUyifaJnRwmjJZUEv9simmHPCvt0mt4F00zLaThNrDxNr_zqx8v7JoQlkC75PEKzLv4poI4zURX3dqx_O483_tWjfnL7n06bT-hNcilt75K7w</recordid><startdate>200007</startdate><enddate>200007</enddate><creator>Entry, James A.</creator><creator>Hubbard, Robert K.</creator><creator>Thies, Janice E.</creator><creator>Fuhrmann, Jeffry J.</creator><general>American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America</general><general>Crop Science Society of America</general><general>American Society of Agronomy</general><scope>IQODW</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>7QL</scope><scope>7TV</scope><scope>7UA</scope><scope>F1W</scope><scope>H97</scope><scope>L.G</scope></search><sort><creationdate>200007</creationdate><title>The Influence of Vegetation in Riparian Filterstrips on Coliform Bacteria: I. 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Movement and Survival in Water</atitle><jtitle>Journal of environmental quality</jtitle><date>2000-07</date><risdate>2000</risdate><volume>29</volume><issue>4</issue><spage>1206</spage><epage>1214</epage><pages>1206-1214</pages><issn>0047-2425</issn><eissn>1537-2537</eissn><coden>JEVQAA</coden><abstract>Swine (Sus scrofa) wastewater was applied to three separate 4 m wide × 30 m long riparian filterstrips consisting of 20 m grass and 10 m forest, 10 m grass and 20 m forest, and 10 m grass and 20 m maidencane (Panicum hemitomon Schult.) in Southern Georgia during each season. Total and fecal coliform numbers in the applied wastewater pulse did not decline as water moved downslope regardless of vegetation type or season. The pulse of applied wastewater did not move beyond 15 m in any treatment in autumn or summer (dry seasons) and only moved beyond 7.5 m in the 20 m grass‐10 m forest treatment in the summer. Total and fecal coliform numbers in soil water and shallow ground water declined by approximately 10‐fold every 7 d for the first 14 d regardless of vegetative treatment or season. Soil temperature and soil moisture correlated with total coliform bacteria in both 1.5 m wells (r2 = 0.89) and 2.0 m wells (r2 = 0.89), and with fecal coliform bacteria in 1.5 (r2 = 0.82) and 2.0 m (r2 = 0.76) wells. Animal production operations may need to locate in warm‐dry climates so animal waste can be applied to lands to help ensure enteric bacteria input to surface and ground water will not occur.</abstract><cop>Madison, WI</cop><pub>American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America</pub><doi>10.2134/jeq2000.00472425002900040026x</doi><tpages>9</tpages><oa>free_for_read</oa></addata></record> |
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source | Wiley Online Library Journals Frontfile Complete |
subjects | Agronomy. Soil science and plant productions Applied sciences Biological and medical sciences Continental surface waters Earth sciences Earth, ocean, space Engineering and environment geology. Geothermics Exact sciences and technology Fundamental and applied biological sciences. Psychology Groundwaters Natural water pollution Panicum hemitomon Pollution Pollution, environment geology Riparian vegetation Soil and water pollution Soil science Sus scrofa USA, Georgia Water treatment and pollution |
title | The Influence of Vegetation in Riparian Filterstrips on Coliform Bacteria: I. Movement and Survival in Water |
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