Encyclopedia of Analytical Chemistry 2017
DOI: 10.1002/9780470027318.a9603
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Analysis of Orphan and Difficult Herbicides and/or Pesticides

Abstract: This article reviews the main chromatography/mass spectrometry methods for the analysis of four main categories of herbicides and related pesticides including cationic charged herbicides (quaternary ammonium (quat) herbicides), anionic charged herbicides or organophosphorus herbicides (glyphosate (GLYP) and glufosinate (GLUF)), sulfonylurea herbicides that utilize liquid chromatography‐positive ion electrospray ionization‐tandem mass spectrometry (LC‐ESI+‐MS/MS), and phenoxyacid herbicides that have optimal ma… Show more

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Cited by 2 publications
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“…For the individual compounds, DIN and NIT were the top contributors, with discharges of 412 (CI = 271–603) and 271 (CI = 181–393) tons during the dry season and 176 (CI = 115–258) and 187 (CI = 132–263) tons during the wet season, respectively. IMI, ACE, and THIA were the most commonly used types of neonicotinoids in China. , However, their discharges turned out to be relatively small compared with those of DIN and NIT. The annual discharges of IMI, ACE, and THIA were 35.7 (CI = 28.8–45.2), 8.56 (CI = 6.29–11.6), and 32.0 (CI = 23.4–43.8) tons, respectively.…”
Section: Discussionmentioning
confidence: 99%
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“…For the individual compounds, DIN and NIT were the top contributors, with discharges of 412 (CI = 271–603) and 271 (CI = 181–393) tons during the dry season and 176 (CI = 115–258) and 187 (CI = 132–263) tons during the wet season, respectively. IMI, ACE, and THIA were the most commonly used types of neonicotinoids in China. , However, their discharges turned out to be relatively small compared with those of DIN and NIT. The annual discharges of IMI, ACE, and THIA were 35.7 (CI = 28.8–45.2), 8.56 (CI = 6.29–11.6), and 32.0 (CI = 23.4–43.8) tons, respectively.…”
Section: Discussionmentioning
confidence: 99%
“…In the present study, the neonicotinoid fluxes were established separately for the upper and midlower Yangtze River as follows (in units of tons) where L Upstream In , L Tributary In , L Nonpoint In , L Sewage In , L Sediment Release , and L Precipitation are the inputs from upstream, tributaries/lakes, nonpoint sources, sewage discharges, sediment release and precipitation, respectively, and L Downstream Out , L Water Use Out , L Photolysis , and L Evaporation Out are the losses from downstream, water use, photolysis process, and evaporation, respectively. When solving the equation, the following assumptions were made: (a) compared with runoff from agricultural areas into the rivers (nonpoint source), the sewage discharge from industrial production (point source) into the rivers is considered small for neonicotinoids; , (b) because neonicotinoids are a type of hydrophilic substance, it is difficult for them to absorb into sediment, which results in low concentrations in the sediments, ,, and thus, the release of neonicotinoids from sediments is expected to be very low; and (c) the exchange of neonicotinoids between water and air consists of precipitation and evaporation. According to previous studies, the concentration of neonicotinoid in the air was in the range from 1.0 to 4.0 pg/m 3 , , 6–7 orders of magnitude lower than that in the water found in this study.…”
Section: Methodsmentioning
confidence: 99%
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