INPUTS OF COPPER‐BASED CROP PROTECTANTS TO COASTAL CREEKS FROM PASTICULTURE RUNOFF
Identifieur interne : 000B89 ( Istex/Corpus ); précédent : 000B88; suivant : 000B90INPUTS OF COPPER‐BASED CROP PROTECTANTS TO COASTAL CREEKS FROM PASTICULTURE RUNOFF
Auteurs : Andrea M. Dietrich ; Daniel L. Gallagher ; Kathryn A. KlawiterSource :
- JAWRA Journal of the American Water Resources Association [ 1093-474X ] ; 2001-04.
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Abstract
ABSTRACT: Inputs of copper‐based crop protectants from tomato fields grown under plastic mulch agriculture (plasticulture) to an estuarine creek were investigated. Copper was measured in runoff from diverse land‐uses including conventional agriculture, plasticulture, residences, and natural areas. Water column and sediment copper concentrations were measured in plasticulture and control (nonagriculture) watersheds. Copper concentrations in plasticulture‐impacted creeks exceeded background levels episodically. High concentrations occurred during or immediately after runoff‐producing rains. Concentrations of 263 μg/L total copper and 126 μg/L dissolved copper were measured in a tidal creek affected by plasticulture; concentrations exceeded the shellfish LC50 values and the water quality criteria of 2.9 μg/L dissolved copper. Control watersheds indicated background water column levels of ≤ 4 μg/L dissolved copper with similar copper levels during periods with and without rain. The copper concentrations in tomato plasticulture field runoff itself contained up to 238 μg/L dissolved copper. Copper concentrations in runoff from other land‐uses were less than 5 μg/L dissolved copper. Creek sediment samples adjacent to a plasticulture field contained significantly higher copper concentrations than sediments taken from nonplasticulture watersheds.
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DOI: 10.1111/j.1752-1688.2001.tb00968.x
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Copper was measured in runoff from diverse land‐uses including conventional agriculture, plasticulture, residences, and natural areas. Water column and sediment copper concentrations were measured in plasticulture and control (nonagriculture) watersheds. Copper concentrations in plasticulture‐impacted creeks exceeded background levels episodically. High concentrations occurred during or immediately after runoff‐producing rains. Concentrations of 263 μg/L total copper and 126 μg/L dissolved copper were measured in a tidal creek affected by plasticulture; concentrations exceeded the shellfish LC50 values and the water quality criteria of 2.9 μg/L dissolved copper. Control watersheds indicated background water column levels of ≤ 4 μg/L dissolved copper with similar copper levels during periods with and without rain. The copper concentrations in tomato plasticulture field runoff itself contained up to 238 μg/L dissolved copper. Copper concentrations in runoff from other land‐uses were less than 5 μg/L dissolved copper. Creek sediment samples adjacent to a plasticulture field contained significantly higher copper concentrations than sediments taken from nonplasticulture watersheds.</div></front></TEI><istex><corpusName>wiley</corpusName><author><json:item><name>Andrea M. Dietrich</name></json:item><json:item><name>Daniel L. Gallagher</name></json:item><json:item><name>Kathryn A. 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Copper was measured in runoff from diverse land‐uses including conventional agriculture, plasticulture, residences, and natural areas. Water column and sediment copper concentrations were measured in plasticulture and control (nonagriculture) watersheds. Copper concentrations in plasticulture‐impacted creeks exceeded background levels episodically. High concentrations occurred during or immediately after runoff‐producing rains. Concentrations of 263 μg/L total copper and 126 μg/L dissolved copper were measured in a tidal creek affected by plasticulture; concentrations exceeded the shellfish LC50 values and the water quality criteria of 2.9 μg/L dissolved copper. Control watersheds indicated background water column levels of ≤ 4 μg/L dissolved copper with similar copper levels during periods with and without rain. The copper concentrations in tomato plasticulture field runoff itself contained up to 238 μg/L dissolved copper. Copper concentrations in runoff from other land‐uses were less than 5 μg/L dissolved copper. 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Copper was measured in runoff from diverse land‐uses including conventional agriculture, plasticulture, residences, and natural areas. Water column and sediment copper concentrations were measured in plasticulture and control (nonagriculture) watersheds. Copper concentrations in plasticulture‐impacted creeks exceeded background levels episodically. High concentrations occurred during or immediately after runoff‐producing rains. Concentrations of 263 μg/L total copper and 126 μg/L dissolved copper were measured in a tidal creek affected by plasticulture; concentrations exceeded the shellfish LC50 values and the water quality criteria of 2.9 μg/L dissolved copper. Control watersheds indicated background water column levels of ≤ 4 μg/L dissolved copper with similar copper levels during periods with and without rain. The copper concentrations in tomato plasticulture field runoff itself contained up to 238 μg/L dissolved copper. Copper concentrations in runoff from other land‐uses were less than 5 μg/L dissolved copper. Creek sediment samples adjacent to a plasticulture field contained significantly higher copper concentrations than sediments taken from nonplasticulture watersheds.</p></abstract><textClass xml:lang="en"><keywords scheme="keyword"><list><head>keywords</head><item><term>runoff</term></item><item><term>copper</term></item><item><term>estuaries</term></item><item><term>pesticides</term></item><item><term>plasticulture</term></item><item><term>nonpoint source pollution</term></item></list></keywords></textClass></profileDesc><revisionDesc><change when="2001-04">Published</change></revisionDesc></teiHeader></istex:fulltextTEI><json:item><extension>txt</extension><original>false</original><mimetype>text/plain</mimetype><uri>https://api.istex.fr/document/54FDD63B248BEE3C316486E66A91D040E7D8B6E4/fulltext/txt</uri></json:item></fulltext><metadata><istex:metadataXml wicri:clean="Wiley, elements deleted: body"><istex:xmlDeclaration>version="1.0" encoding="UTF-8" standalone="yes"</istex:xmlDeclaration><istex:document><component version="2.0" type="serialArticle" xml:lang="en"><header><publicationMeta level="product"><publisherInfo><publisherName>Blackwell Publishing Ltd</publisherName><publisherLoc>Oxford, UK</publisherLoc></publisherInfo><doi origin="wiley" registered="yes">10.1111/(ISSN)1752-1688</doi><issn type="print">1093-474X</issn><issn type="electronic">1752-1688</issn><idGroup><id type="product" value="JAWR"></id><id type="publisherDivision" value="ST"></id></idGroup><titleGroup><title type="main" sort="JOURNAL OF AMERICAN WATER RESOURCES ASSOCIATION">JAWRA Journal of the American Water Resources Association</title></titleGroup></publicationMeta><publicationMeta level="part" position="04002"><doi origin="wiley">10.1111/jawr.2001.37.issue-2</doi><numberingGroup><numbering type="journalVolume" number="37">37</numbering><numbering type="journalIssue" number="2">2</numbering></numberingGroup><coverDate startDate="2001-04">April 2001</coverDate></publicationMeta><publicationMeta level="unit" type="article" position="0028100" status="forIssue"><doi origin="wiley">10.1111/j.1752-1688.2001.tb00968.x</doi><idGroup><id type="unit" value="JAWR281"></id></idGroup><countGroup><count type="pageTotal" number="13"></count></countGroup><eventGroup><event type="firstOnline" date="2007-06-08"></event><event type="publishedOnlineFinalForm" date="2007-06-08"></event><event type="xmlConverted" agent="Converter:BPG_TO_WML3G version:2.3.2 mode:FullText source:HeaderRef result:HeaderRef" date="2010-03-06"></event><event type="xmlConverted" agent="Converter:WILEY_ML3G_TO_WILEY_ML3GV2 version:3.8.8" date="2014-01-28"></event><event type="xmlConverted" agent="Converter:WML3G_To_WML3G version:4.1.7 mode:FullText,remove_FC" date="2014-10-23"></event></eventGroup><numberingGroup><numbering type="pageFirst" number="281">281</numbering><numbering type="pageLast" number="293">293</numbering></numberingGroup><linkGroup><link type="toTypesetVersion" href="file:JAWR.JAWR281.pdf"></link></linkGroup></publicationMeta><contentMeta><countGroup><count type="referenceTotal" number="49"></count><count type="linksCrossRef" number="2"></count></countGroup><titleGroup><title type="main">INPUTS OF COPPER‐BASED CROP PROTECTANTS TO COASTAL CREEKS FROM PASTICULTURE RUNOFF<link href="#fn1"><sup>1</sup></link></title></titleGroup><creators><creator creatorRole="author" xml:id="cr1"><personName><givenNames>Andrea M.</givenNames><familyName>Dietrich</familyName></personName></creator><creator creatorRole="author" xml:id="cr2"><personName><givenNames>Daniel L.</givenNames><familyName>Gallagher</familyName></personName></creator><creator creatorRole="author" xml:id="cr3" noteRef="#fn2"><personName><givenNames>Kathryn A.</givenNames><familyName>Klawiter</familyName></personName></creator></creators><keywordGroup xml:lang="en"><keyword xml:id="k1">runoff</keyword><keyword xml:id="k2">copper</keyword><keyword xml:id="k3">estuaries</keyword><keyword xml:id="k4">pesticides</keyword><keyword xml:id="k5">plasticulture</keyword><keyword xml:id="k6">nonpoint source pollution</keyword></keywordGroup><abstractGroup><abstract type="main" xml:lang="en"><p><b>ABSTRACT: </b> Inputs of copper‐based crop protectants from tomato fields grown under plastic mulch agriculture (plasticulture) to an estuarine creek were investigated. Copper was measured in runoff from diverse land‐uses including conventional agriculture, plasticulture, residences, and natural areas. Water column and sediment copper concentrations were measured in plasticulture and control (nonagriculture) watersheds. Copper concentrations in plasticulture‐impacted creeks exceeded background levels episodically. High concentrations occurred during or immediately after runoff‐producing rains. Concentrations of 263 μg/L total copper and 126 μg/L dissolved copper were measured in a tidal creek affected by plasticulture; concentrations exceeded the shellfish LC<sub>50</sub> values and the water quality criteria of 2.9 μg/L dissolved copper. Control watersheds indicated background water column levels of ≤ 4 μg/L dissolved copper with similar copper levels during periods with and without rain. The copper concentrations in tomato plasticulture field runoff itself contained up to 238 μg/L dissolved copper. Copper concentrations in runoff from other land‐uses were less than 5 μg/L dissolved copper. Creek sediment samples adjacent to a plasticulture field contained significantly higher copper concentrations than sediments taken from nonplasticulture watersheds.</p></abstract></abstractGroup></contentMeta><noteGroup><note xml:id="fn1"><label>1</label><p>Paper No. 99037 of the <i>Journal of the American Water Resources Association.</i><b>Discussions are open until December 1, 2001.</b></p></note><note xml:id="fn2"><label>2</label><p>Respectively, Associate Professors, Civil and Environmental Engineering, Virginia Tech, Blacksburg, Virginia 24061–0246; and Environmental Scientist, ENSAT, 155510 Montanus Drive, Suite B, Culpeper, Virginia 22701 (E‐Mail/Dietrich: <email>andread@vt.edu</email>).</p></note></noteGroup></header></component></istex:document></istex:metadataXml><mods version="3.6"><titleInfo lang="en"><title>INPUTS OF COPPER‐BASED CROP PROTECTANTS TO COASTAL CREEKS FROM PASTICULTURE RUNOFF</title></titleInfo><titleInfo type="alternative" contentType="CDATA" lang="en"><title>INPUTS OF COPPER‐BASED CROP PROTECTANTS TO COASTAL CREEKS FROM PASTICULTURE RUNOFF1</title></titleInfo><name type="personal"><namePart type="given">Andrea M.</namePart><namePart type="family">Dietrich</namePart><role><roleTerm type="text">author</roleTerm></role></name><name type="personal"><namePart type="given">Daniel L.</namePart><namePart type="family">Gallagher</namePart><role><roleTerm type="text">author</roleTerm></role></name><name type="personal"><namePart type="given">Kathryn A.</namePart><namePart type="family">Klawiter</namePart><role><roleTerm type="text">author</roleTerm></role></name><typeOfResource>text</typeOfResource><genre type="article" displayLabel="article"></genre><originInfo><publisher>Blackwell Publishing Ltd</publisher><place><placeTerm type="text">Oxford, UK</placeTerm></place><dateIssued encoding="w3cdtf">2001-04</dateIssued><copyrightDate encoding="w3cdtf">2001</copyrightDate></originInfo><language><languageTerm type="code" authority="rfc3066">en</languageTerm><languageTerm type="code" authority="iso639-2b">eng</languageTerm></language><physicalDescription><internetMediaType>text/html</internetMediaType><extent unit="references">49</extent></physicalDescription><abstract>ABSTRACT: Inputs of copper‐based crop protectants from tomato fields grown under plastic mulch agriculture (plasticulture) to an estuarine creek were investigated. Copper was measured in runoff from diverse land‐uses including conventional agriculture, plasticulture, residences, and natural areas. Water column and sediment copper concentrations were measured in plasticulture and control (nonagriculture) watersheds. Copper concentrations in plasticulture‐impacted creeks exceeded background levels episodically. High concentrations occurred during or immediately after runoff‐producing rains. Concentrations of 263 μg/L total copper and 126 μg/L dissolved copper were measured in a tidal creek affected by plasticulture; concentrations exceeded the shellfish LC50 values and the water quality criteria of 2.9 μg/L dissolved copper. Control watersheds indicated background water column levels of ≤ 4 μg/L dissolved copper with similar copper levels during periods with and without rain. The copper concentrations in tomato plasticulture field runoff itself contained up to 238 μg/L dissolved copper. Copper concentrations in runoff from other land‐uses were less than 5 μg/L dissolved copper. Creek sediment samples adjacent to a plasticulture field contained significantly higher copper concentrations than sediments taken from nonplasticulture watersheds.</abstract><note type="content">*Paper No. 99037 of the Journal of the American Water Resources Association.Discussions are open until December 1, 2001.</note><subject lang="en"><genre>keywords</genre><topic>runoff</topic><topic>copper</topic><topic>estuaries</topic><topic>pesticides</topic><topic>plasticulture</topic><topic>nonpoint source pollution</topic></subject><relatedItem type="host"><titleInfo><title>JAWRA Journal of the American Water Resources Association</title></titleInfo><genre type="journal">journal</genre><identifier type="ISSN">1093-474X</identifier><identifier type="eISSN">1752-1688</identifier><identifier type="DOI">10.1111/(ISSN)1752-1688</identifier><identifier type="PublisherID">JAWR</identifier><part><date>2001</date><detail type="volume"><caption>vol.</caption><number>37</number></detail><detail type="issue"><caption>no.</caption><number>2</number></detail><extent unit="pages"><start>281</start><end>293</end><total>13</total></extent></part></relatedItem><identifier type="istex">54FDD63B248BEE3C316486E66A91D040E7D8B6E4</identifier><identifier type="DOI">10.1111/j.1752-1688.2001.tb00968.x</identifier><identifier type="ArticleID">JAWR281</identifier><recordInfo><recordContentSource>WILEY</recordContentSource><recordOrigin>Blackwell Publishing Ltd</recordOrigin></recordInfo></mods></metadata><serie></serie></istex></record>Pour manipuler ce document sous Unix (Dilib)
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