环境监测管理与技术
環境鑑測管理與技術
배경감측관리여기술
THE ADMINISTRATION AND TECHNIQUE OF ENVIRONMENTAL MONITORING
2015年
1期
42-45
,共4页
谭红%郭正元%周验旭%戴亮
譚紅%郭正元%週驗旭%戴亮
담홍%곽정원%주험욱%대량
稻瘟酰胺%咪鲜胺%气相色谱法%土壤%水质%水稻植株
稻瘟酰胺%咪鮮胺%氣相色譜法%土壤%水質%水稻植株
도온선알%미선알%기상색보법%토양%수질%수도식주
Fenoxanil%Prochloraz%Gas chromatography%Soils%Water quality%Rice plants
采用二氯甲烷萃取稻田水样品,土壤样品用丙酮-二氯甲烷(体积比为9∶1)混合溶液提取,二氯甲烷萃取,水稻植株样品用乙腈-二氯甲烷(体积比为9∶1)混合溶液直接萃取,用气相色谱法同时测定样品中稻瘟酰胺和咪鲜胺残留。该方法在0.0122 mg /L ~2.68 mg /L 范围内线性良好,稻田土壤、田水、水稻植株中稻瘟酰胺的检出限分别为2.75μg /kg、1.83μg /L、3.80μg /kg,咪鲜胺的检出限分别为3.55μg /kg、2.66μg /L、5.62μg /kg。空白稻田土壤、稻田水和水稻植株样品3个浓度水平的加标回收率为80.3%~104%,RSD 为3.0%~13.2%。
採用二氯甲烷萃取稻田水樣品,土壤樣品用丙酮-二氯甲烷(體積比為9∶1)混閤溶液提取,二氯甲烷萃取,水稻植株樣品用乙腈-二氯甲烷(體積比為9∶1)混閤溶液直接萃取,用氣相色譜法同時測定樣品中稻瘟酰胺和咪鮮胺殘留。該方法在0.0122 mg /L ~2.68 mg /L 範圍內線性良好,稻田土壤、田水、水稻植株中稻瘟酰胺的檢齣限分彆為2.75μg /kg、1.83μg /L、3.80μg /kg,咪鮮胺的檢齣限分彆為3.55μg /kg、2.66μg /L、5.62μg /kg。空白稻田土壤、稻田水和水稻植株樣品3箇濃度水平的加標迴收率為80.3%~104%,RSD 為3.0%~13.2%。
채용이록갑완췌취도전수양품,토양양품용병동-이록갑완(체적비위9∶1)혼합용액제취,이록갑완췌취,수도식주양품용을정-이록갑완(체적비위9∶1)혼합용액직접췌취,용기상색보법동시측정양품중도온선알화미선알잔류。해방법재0.0122 mg /L ~2.68 mg /L 범위내선성량호,도전토양、전수、수도식주중도온선알적검출한분별위2.75μg /kg、1.83μg /L、3.80μg /kg,미선알적검출한분별위3.55μg /kg、2.66μg /L、5.62μg /kg。공백도전토양、도전수화수도식주양품3개농도수평적가표회수솔위80.3%~104%,RSD 위3.0%~13.2%。
Fenoxanil and prochloraz residue in paddy field (soil,water and rice plant)were determined simultaneously by gas chromatography.The residues in the paddy-field water,paddy-field soil,and rice plants were extracted with methylene chloride,acetone-methylene chloride(volume ratio is 9∶1 ),and acetonitrile-meth-ylene chloride(volume ratio is 9∶1 )respectively.The results showed that the linearity was favorable in a range between 0.012 2 mg /L ~2.68 mg /L,the detection limits of fenoxanil in paddy-field soil,paddy-field water and paddy rice were 2.75 μg /kg、1 .83 μg /L、3.80 μg /kg,and the detection limits of prochloraz were 3.55 μg /kg、2.66 μg /L、5.62 μg /kg.The spiked recovery test of three concentration levels were done in paddy-field soil, paddy-field water and paddy rice,the recovery rate ranged from 80.3% ~104%,RSD ranged from 3.0% ~13.2%.