Influence of Water Quality and Coapplied Agrochemicals on Efficacy of Glyphosate
Experiments were conducted in 2008, 2009, and 2010 to determine the influence of water source as carrier and other agrochemicals on glyphosate efficacy and physicochemical compatibility. Glyphosate efficacy was not affected by most water sources, when compared with deionized water, although response...
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creator | Chahal, Gurinderbir S Jordan, David L Burton, James D Danehower, David York, Alan C Eure, Peter M Clewis, Bart |
description | Experiments were conducted in 2008, 2009, and 2010 to determine the influence of water source as carrier and other agrochemicals on glyphosate efficacy and physicochemical compatibility. Glyphosate efficacy was not affected by most water sources, when compared with deionized water, although response was not consistent across all weed species, including cereal rye, common lambsquarters, common ragweed, goosegrass, Italian ryegrass, large crabgrass, Palmer amaranth, tall morningglory, and wheat. Control by glyphosate was not negatively affected when coapplied with cloransulam-methyl, dicamba, flumioxazin, pyrithiobac-sodium, thifensulfuron-methyl plus tribenuron-methyl, trifloxysulfuron-sodium, and 2,4-D but was affected by acifluorfen and glufosinate. Calcium, manganese, and zinc solutions consistently reduced weed control by glyphosate, whereas boron seldom affected efficacy. Compared with deionized water, Italian ryegrass control was affected by water sources when applied at seedling and jointing stages more so than at tillering and heading growth stages. Calcium, manganese, and zinc reduced control regardless of growth stage. Precipitates were not produced when glyphosate was applied with the water sources or fertilizer solutions. However, transient precipitates developed when glyphosate was coapplied with cloransulam-methyl, flumioxazin, thifensulfuron-methyl plus tribenuron-methyl, and trifloxysulfuron-sodium but not when coapplied with acifluorfen, dicamba, glufosinate, pyrithiobac-sodium, and 2,4-D. Solution pH ranged from 4.11 to 5.60 after glyphosate was added, regardless of solution pH before glyphosate addition. Nomenclature: 2,4-D; acifluorfen; boron; calcium; cloransulam-methyl; dicamba; flumioxazin; glufosinate; glyphosate; manganese; pyrithiobac-sodium; thifensulfuron-methyl plus tribenuron-methyl; trifloxysulfuron-sodium; zinc; cereal rye, Secale cereale L.; common lambsquarters, Chenopodium album L.; common ragweed, Ambrosia artemisiifolia L.; goosegrass, Eleusine indica (L.) Gaertn.; Italian ryegrass, Lolium perenne L. ssp. multiflorum (Lam.) Husnot.; large crabgrass, Digitaria sanguinalis (L.) Scop.; Palmer amaranth, Amaranthus palmeri (L.) S. Wats.; tall morningglory, Ipomoea purpurea (L.) Roth; wheat, Triticum aestivum L. |
doi_str_mv | 10.1614/WT-D-11-00060.1 |
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Glyphosate efficacy was not affected by most water sources, when compared with deionized water, although response was not consistent across all weed species, including cereal rye, common lambsquarters, common ragweed, goosegrass, Italian ryegrass, large crabgrass, Palmer amaranth, tall morningglory, and wheat. Control by glyphosate was not negatively affected when coapplied with cloransulam-methyl, dicamba, flumioxazin, pyrithiobac-sodium, thifensulfuron-methyl plus tribenuron-methyl, trifloxysulfuron-sodium, and 2,4-D but was affected by acifluorfen and glufosinate. Calcium, manganese, and zinc solutions consistently reduced weed control by glyphosate, whereas boron seldom affected efficacy. Compared with deionized water, Italian ryegrass control was affected by water sources when applied at seedling and jointing stages more so than at tillering and heading growth stages. Calcium, manganese, and zinc reduced control regardless of growth stage. Precipitates were not produced when glyphosate was applied with the water sources or fertilizer solutions. However, transient precipitates developed when glyphosate was coapplied with cloransulam-methyl, flumioxazin, thifensulfuron-methyl plus tribenuron-methyl, and trifloxysulfuron-sodium but not when coapplied with acifluorfen, dicamba, glufosinate, pyrithiobac-sodium, and 2,4-D. Solution pH ranged from 4.11 to 5.60 after glyphosate was added, regardless of solution pH before glyphosate addition. Nomenclature: 2,4-D; acifluorfen; boron; calcium; cloransulam-methyl; dicamba; flumioxazin; glufosinate; glyphosate; manganese; pyrithiobac-sodium; thifensulfuron-methyl plus tribenuron-methyl; trifloxysulfuron-sodium; zinc; cereal rye, Secale cereale L.; common lambsquarters, Chenopodium album L.; common ragweed, Ambrosia artemisiifolia L.; goosegrass, Eleusine indica (L.) Gaertn.; Italian ryegrass, Lolium perenne L. ssp. multiflorum (Lam.) Husnot.; large crabgrass, Digitaria sanguinalis (L.) Scop.; Palmer amaranth, Amaranthus palmeri (L.) S. Wats.; tall morningglory, Ipomoea purpurea (L.) Roth; wheat, Triticum aestivum L.</description><identifier>ISSN: 0890-037X</identifier><identifier>EISSN: 1550-2740</identifier><identifier>DOI: 10.1614/WT-D-11-00060.1</identifier><language>eng</language><publisher>810 East 10th St., Lawrence, KS 66044-7050: Weed Science Society of America</publisher><subject>Agrochemical compatibility ; Agrochemicals ; Boron ; Calcium ; Coastal plains ; Cost control ; fertilizer solutions ; Fertilizers ; Freshwater ; Herbicides ; Magnesium ; Manganese ; Seedlings ; Sodium ; solution pH ; Triticum aestivum ; Water quality ; water sources ; Water treatment ; Weed control ; WEED MANAGEMENT — MAJOR CROPS ; Weeds ; Zinc</subject><ispartof>Weed technology, 2012-04, Vol.26 (2), p.167-176</ispartof><rights>Weed Science Society of America</rights><rights>Copyright 2012 Weed Science Society of America</rights><rights>Copyright Allen Press Publishing Services Apr-Jun 2012</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-b362t-8a3e404bc4ef03fda9557ee078bda7b1c178cafacf19166ac6c46dce54f337d03</citedby><cites>FETCH-LOGICAL-b362t-8a3e404bc4ef03fda9557ee078bda7b1c178cafacf19166ac6c46dce54f337d03</cites></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://www.jstor.org/stable/pdf/23264282$$EPDF$$P50$$Gjstor$$H</linktopdf><linktohtml>$$Uhttps://www.jstor.org/stable/23264282$$EHTML$$P50$$Gjstor$$H</linktohtml><link.rule.ids>314,780,784,803,27924,27925,58017,58250</link.rule.ids></links><search><creatorcontrib>Chahal, Gurinderbir S</creatorcontrib><creatorcontrib>Jordan, David L</creatorcontrib><creatorcontrib>Burton, James D</creatorcontrib><creatorcontrib>Danehower, David</creatorcontrib><creatorcontrib>York, Alan C</creatorcontrib><creatorcontrib>Eure, Peter M</creatorcontrib><creatorcontrib>Clewis, Bart</creatorcontrib><title>Influence of Water Quality and Coapplied Agrochemicals on Efficacy of Glyphosate</title><title>Weed technology</title><description>Experiments were conducted in 2008, 2009, and 2010 to determine the influence of water source as carrier and other agrochemicals on glyphosate efficacy and physicochemical compatibility. Glyphosate efficacy was not affected by most water sources, when compared with deionized water, although response was not consistent across all weed species, including cereal rye, common lambsquarters, common ragweed, goosegrass, Italian ryegrass, large crabgrass, Palmer amaranth, tall morningglory, and wheat. Control by glyphosate was not negatively affected when coapplied with cloransulam-methyl, dicamba, flumioxazin, pyrithiobac-sodium, thifensulfuron-methyl plus tribenuron-methyl, trifloxysulfuron-sodium, and 2,4-D but was affected by acifluorfen and glufosinate. Calcium, manganese, and zinc solutions consistently reduced weed control by glyphosate, whereas boron seldom affected efficacy. Compared with deionized water, Italian ryegrass control was affected by water sources when applied at seedling and jointing stages more so than at tillering and heading growth stages. Calcium, manganese, and zinc reduced control regardless of growth stage. Precipitates were not produced when glyphosate was applied with the water sources or fertilizer solutions. However, transient precipitates developed when glyphosate was coapplied with cloransulam-methyl, flumioxazin, thifensulfuron-methyl plus tribenuron-methyl, and trifloxysulfuron-sodium but not when coapplied with acifluorfen, dicamba, glufosinate, pyrithiobac-sodium, and 2,4-D. Solution pH ranged from 4.11 to 5.60 after glyphosate was added, regardless of solution pH before glyphosate addition. Nomenclature: 2,4-D; acifluorfen; boron; calcium; cloransulam-methyl; dicamba; flumioxazin; glufosinate; glyphosate; manganese; pyrithiobac-sodium; thifensulfuron-methyl plus tribenuron-methyl; trifloxysulfuron-sodium; zinc; cereal rye, Secale cereale L.; common lambsquarters, Chenopodium album L.; common ragweed, Ambrosia artemisiifolia L.; goosegrass, Eleusine indica (L.) Gaertn.; Italian ryegrass, Lolium perenne L. ssp. multiflorum (Lam.) Husnot.; large crabgrass, Digitaria sanguinalis (L.) Scop.; Palmer amaranth, Amaranthus palmeri (L.) S. Wats.; tall morningglory, Ipomoea purpurea (L.) Roth; wheat, Triticum aestivum L.</description><subject>Agrochemical compatibility</subject><subject>Agrochemicals</subject><subject>Boron</subject><subject>Calcium</subject><subject>Coastal plains</subject><subject>Cost control</subject><subject>fertilizer solutions</subject><subject>Fertilizers</subject><subject>Freshwater</subject><subject>Herbicides</subject><subject>Magnesium</subject><subject>Manganese</subject><subject>Seedlings</subject><subject>Sodium</subject><subject>solution pH</subject><subject>Triticum aestivum</subject><subject>Water quality</subject><subject>water sources</subject><subject>Water treatment</subject><subject>Weed control</subject><subject>WEED MANAGEMENT — MAJOR CROPS</subject><subject>Weeds</subject><subject>Zinc</subject><issn>0890-037X</issn><issn>1550-2740</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2012</creationdate><recordtype>article</recordtype><sourceid>8G5</sourceid><sourceid>ABUWG</sourceid><sourceid>AFKRA</sourceid><sourceid>AZQEC</sourceid><sourceid>BENPR</sourceid><sourceid>CCPQU</sourceid><sourceid>DWQXO</sourceid><sourceid>GNUQQ</sourceid><sourceid>GUQSH</sourceid><sourceid>M2O</sourceid><recordid>eNqFkEFr3DAQhUVoIdsk55wKhl56UTNjyZJ8DJs0DQSSwobNTciy1PXitVzJPuy_j7Zbcsglpxnmfe8xPEIuEX6gQH61XtEbikgBQOTTCVlgVQEtJYdPZAGqBgpMvpySLyltAVCUJSzI0_3g-9kN1hXBF2szuVj8nk3fTfvCDG2xDGYc-861xfWfGOzG7Tpr-lSEobj1Pu92fzDe9ftxE1K2n5PPPgPu4v88I88_b1fLX_Th8e5-ef1AGybKiSrDHAfeWO48MN-auqqkcyBV0xrZoEWprPHGeqxRCGOF5aK1ruKeMdkCOyPfj7ljDH9nlya965J1fW8GF-akUSlVyxo5y-i3d-g2zHHI32kEBlBzpmSmro6UjSGl6LweY7czcZ8hfWhYr1f6RiPqfw1rzI6vR8c2TSG-4SUrBS9VmXV61JsuhMF9mPcKBDWGGw</recordid><startdate>20120401</startdate><enddate>20120401</enddate><creator>Chahal, Gurinderbir S</creator><creator>Jordan, David L</creator><creator>Burton, James D</creator><creator>Danehower, David</creator><creator>York, Alan C</creator><creator>Eure, Peter M</creator><creator>Clewis, Bart</creator><general>Weed Science Society of America</general><general>Cambridge University Press</general><scope>AAYXX</scope><scope>CITATION</scope><scope>3V.</scope><scope>7X2</scope><scope>7XB</scope><scope>8FE</scope><scope>8FH</scope><scope>8FK</scope><scope>8G5</scope><scope>ABUWG</scope><scope>AFKRA</scope><scope>ATCPS</scope><scope>AZQEC</scope><scope>BBNVY</scope><scope>BENPR</scope><scope>BHPHI</scope><scope>CCPQU</scope><scope>DWQXO</scope><scope>GNUQQ</scope><scope>GUQSH</scope><scope>HCIFZ</scope><scope>LK8</scope><scope>M0K</scope><scope>M2O</scope><scope>M7P</scope><scope>MBDVC</scope><scope>PADUT</scope><scope>PQEST</scope><scope>PQQKQ</scope><scope>PQUKI</scope><scope>Q9U</scope><scope>7QH</scope><scope>7UA</scope><scope>C1K</scope><scope>F1W</scope><scope>H97</scope><scope>L.G</scope></search><sort><creationdate>20120401</creationdate><title>Influence of Water Quality and Coapplied Agrochemicals on Efficacy of Glyphosate</title><author>Chahal, Gurinderbir S ; Jordan, David L ; Burton, James D ; Danehower, David ; York, Alan C ; Eure, Peter M ; Clewis, Bart</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-b362t-8a3e404bc4ef03fda9557ee078bda7b1c178cafacf19166ac6c46dce54f337d03</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2012</creationdate><topic>Agrochemical compatibility</topic><topic>Agrochemicals</topic><topic>Boron</topic><topic>Calcium</topic><topic>Coastal plains</topic><topic>Cost control</topic><topic>fertilizer solutions</topic><topic>Fertilizers</topic><topic>Freshwater</topic><topic>Herbicides</topic><topic>Magnesium</topic><topic>Manganese</topic><topic>Seedlings</topic><topic>Sodium</topic><topic>solution pH</topic><topic>Triticum aestivum</topic><topic>Water quality</topic><topic>water sources</topic><topic>Water treatment</topic><topic>Weed control</topic><topic>WEED MANAGEMENT — MAJOR CROPS</topic><topic>Weeds</topic><topic>Zinc</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Chahal, Gurinderbir S</creatorcontrib><creatorcontrib>Jordan, David L</creatorcontrib><creatorcontrib>Burton, James D</creatorcontrib><creatorcontrib>Danehower, David</creatorcontrib><creatorcontrib>York, Alan C</creatorcontrib><creatorcontrib>Eure, Peter M</creatorcontrib><creatorcontrib>Clewis, Bart</creatorcontrib><collection>CrossRef</collection><collection>ProQuest Central (Corporate)</collection><collection>Agricultural Science Collection</collection><collection>ProQuest Central (purchase pre-March 2016)</collection><collection>ProQuest SciTech Collection</collection><collection>ProQuest Natural Science Collection</collection><collection>ProQuest Central (Alumni) (purchase pre-March 2016)</collection><collection>Research Library (Alumni Edition)</collection><collection>ProQuest Central (Alumni Edition)</collection><collection>ProQuest Central UK/Ireland</collection><collection>Agricultural & Environmental Science Collection</collection><collection>ProQuest Central Essentials</collection><collection>Biological Science Collection</collection><collection>ProQuest Central</collection><collection>Natural Science Collection</collection><collection>ProQuest One Community College</collection><collection>ProQuest Central Korea</collection><collection>ProQuest Central Student</collection><collection>Research Library Prep</collection><collection>SciTech Premium Collection</collection><collection>ProQuest Biological Science Collection</collection><collection>Agricultural Science Database</collection><collection>Research Library</collection><collection>Biological Science Database</collection><collection>Research Library (Corporate)</collection><collection>Research Library China</collection><collection>ProQuest One Academic Eastern Edition (DO NOT USE)</collection><collection>ProQuest One Academic</collection><collection>ProQuest One Academic UKI Edition</collection><collection>ProQuest Central Basic</collection><collection>Aqualine</collection><collection>Water Resources Abstracts</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><jtitle>Weed technology</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Chahal, Gurinderbir S</au><au>Jordan, David L</au><au>Burton, James D</au><au>Danehower, David</au><au>York, Alan C</au><au>Eure, Peter M</au><au>Clewis, Bart</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Influence of Water Quality and Coapplied Agrochemicals on Efficacy of Glyphosate</atitle><jtitle>Weed technology</jtitle><date>2012-04-01</date><risdate>2012</risdate><volume>26</volume><issue>2</issue><spage>167</spage><epage>176</epage><pages>167-176</pages><issn>0890-037X</issn><eissn>1550-2740</eissn><abstract>Experiments were conducted in 2008, 2009, and 2010 to determine the influence of water source as carrier and other agrochemicals on glyphosate efficacy and physicochemical compatibility. Glyphosate efficacy was not affected by most water sources, when compared with deionized water, although response was not consistent across all weed species, including cereal rye, common lambsquarters, common ragweed, goosegrass, Italian ryegrass, large crabgrass, Palmer amaranth, tall morningglory, and wheat. Control by glyphosate was not negatively affected when coapplied with cloransulam-methyl, dicamba, flumioxazin, pyrithiobac-sodium, thifensulfuron-methyl plus tribenuron-methyl, trifloxysulfuron-sodium, and 2,4-D but was affected by acifluorfen and glufosinate. Calcium, manganese, and zinc solutions consistently reduced weed control by glyphosate, whereas boron seldom affected efficacy. Compared with deionized water, Italian ryegrass control was affected by water sources when applied at seedling and jointing stages more so than at tillering and heading growth stages. Calcium, manganese, and zinc reduced control regardless of growth stage. Precipitates were not produced when glyphosate was applied with the water sources or fertilizer solutions. However, transient precipitates developed when glyphosate was coapplied with cloransulam-methyl, flumioxazin, thifensulfuron-methyl plus tribenuron-methyl, and trifloxysulfuron-sodium but not when coapplied with acifluorfen, dicamba, glufosinate, pyrithiobac-sodium, and 2,4-D. Solution pH ranged from 4.11 to 5.60 after glyphosate was added, regardless of solution pH before glyphosate addition. Nomenclature: 2,4-D; acifluorfen; boron; calcium; cloransulam-methyl; dicamba; flumioxazin; glufosinate; glyphosate; manganese; pyrithiobac-sodium; thifensulfuron-methyl plus tribenuron-methyl; trifloxysulfuron-sodium; zinc; cereal rye, Secale cereale L.; common lambsquarters, Chenopodium album L.; common ragweed, Ambrosia artemisiifolia L.; goosegrass, Eleusine indica (L.) Gaertn.; Italian ryegrass, Lolium perenne L. ssp. multiflorum (Lam.) Husnot.; large crabgrass, Digitaria sanguinalis (L.) Scop.; Palmer amaranth, Amaranthus palmeri (L.) S. Wats.; tall morningglory, Ipomoea purpurea (L.) Roth; wheat, Triticum aestivum L.</abstract><cop>810 East 10th St., Lawrence, KS 66044-7050</cop><pub>Weed Science Society of America</pub><doi>10.1614/WT-D-11-00060.1</doi><tpages>10</tpages></addata></record> |
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subjects | Agrochemical compatibility Agrochemicals Boron Calcium Coastal plains Cost control fertilizer solutions Fertilizers Freshwater Herbicides Magnesium Manganese Seedlings Sodium solution pH Triticum aestivum Water quality water sources Water treatment Weed control WEED MANAGEMENT — MAJOR CROPS Weeds Zinc |
title | Influence of Water Quality and Coapplied Agrochemicals on Efficacy of Glyphosate |
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