排序方式: 共有11条查询结果,搜索用时 22 毫秒
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采用气相色谱法,在CP-7906毛细管柱上以正十九烷作内标,用FID检测器测定甲草胺、乙草胺和莠去津的含量。3种有效成分在同一条件下测定,甲草胺、乙草胺和莠去津的标准偏差分别为0.13%、0.10%、0.12%;变异系数分别为0.59%、1.09%、1.10%;平均回收率分别为100.9%、101.9%、100.1%;线性相关系数分别为0.9998、0.9999、0.9998。 相似文献
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溶解性有机质对甲草胺在土壤中吸附行为影响 总被引:2,自引:0,他引:2
土壤对甲草胺的吸附解吸作用是甲草胺在土壤中迁移转化行为之一,对土壤环境质量变化有重要影响.在松花江沿江3个城市郊区农田(佳木斯(S1)、依兰(S2)和哈尔滨(S3)),采集3种不同理化性质的土壤,采用批量实验方法研究甲草胺在土壤上的吸附-解吸过程以及溶解性有机质对甲草胺吸附-解吸过程的影响.结果表明:溶解性有机质对甲草胺在土壤中的吸附过程有抑制作用,而对解吸过程有促进作用;甲草胺在3种土壤中的吸附-解吸过程符合Freundlich方程(R2>0.858);在3种土壤样品中的吸附量大小依次为S1>S2>S3;甲草胺在3种土壤中吸附-解吸存在滞后现象. 相似文献
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0 INTRODUCTIONThesedays ,someman madeorganiccompoundsandtheirdegradationproductsarefoundtobeharmfultohor mone secretinginbodyofbothpeopleandanimalsandtheycouldresultindisorderofincretion .Thesecom poundsarenowbedefinedasenvironmentalendocrinedisruptor[1] .Itiswell knownthatthesecompoundsareverydifficulttodegradebynatureprocess .Andbecausetheyarelipid soluble ,theyareeasytoamassinlipidandliverandhardtodischargeoutofbody .Thetoxicityissynergicanditssymptomshowspersisting ,slowandgrad ual.… 相似文献
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凝胶渗透色谱-气相色谱-质谱联用快速测定大豆中克百威、乙草胺、甲草胺、异丙甲草胺、氟乐灵的残留量 总被引:4,自引:0,他引:4
建立了气相色谱-质谱(GC/MS)法,电子轰击离子化(EI)法同时测定及确证大豆中克百威、乙草胺、甲草胺、异丙甲草胺、氟乐灵的残留量。试样经乙腈提取,共提物中的色素和油脂用凝胶色谱(GPC)净化去除。采用GC/MS-SIM法对克百威、乙草胺、甲草胺、异丙甲草胺、氟乐灵进行定性和定量分析。结果表明,采用GPC净化,并设定收集时间在5~15 min内,能够有效避免大豆中油脂峰干扰,缩短分析时间。5种农药的加标回收率为66.6%~104.9%,测定的相对标准偏差为2.2%~12.3%。5种农药在0.01~0.1 mg/L范围内具有较好的线性,相关系数达0.996以上,方法中克百威、乙草胺、甲草胺、异丙甲草胺、氟乐灵的定量限均为0.01 mg/kg。 相似文献
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酰胺类除草剂甲草胺的微生物降解研究进展 总被引:1,自引:0,他引:1
主要介绍了氯乙酰胺类除草剂甲草胺微生物降解的研究现状。甲草胺是一种世界上广泛使用的芽前除草剂,也是普遍存在的危险且难矿化的有机污染物。在被污染的土壤中,有氧条件下的生物降解是其归宿的主要过程。部分土壤微生物能以甲草胺为唯一碳源和能量的方式进行代谢,但共代谢是去除土壤中母体化合物的主要途径。介绍了降解的甲草胺微生物及其主要代谢产物,但因为缺少实验室条件下足够的矿化信息,还不能提出完整的代谢路径。建议继续加强高效降解微生物(群落)的筛选,澄清甲草胺的代谢途径,应用宏基因组学的新技术发掘新的降解基因,并在此基础上探讨了工程微生物(群落)在原位生物修复过程中的作用。 相似文献
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Kinetics of alachlor transformation and identification of metabolites under anaerobic conditions 总被引:3,自引:0,他引:3
Alachlor is one of the two most commonly used herbicides in the United States. In the environment, little mineralization of this compound has been found to occur, and metabolites of alachlor may be formed and could accumulate. The objectives of this study were to determine the rate of alachlor biotransformation and to identify the transformation intermediates formed under aqueous denitrifying, methanogenic, and sulfate-reducing conditions. Second-order biotrasnformation coefficients for alachlor were determined to be 7.6 × 10−5 (±4.0 × 10−5), 2.9 × 10−3 (±1.6 × 10−3), and 1.5 × 10−2 (±1.4 × 10−2) 1 mg VSS−1 day−1 under denitrifying, methanogenic, and sulfate-reducing conditions, respectively. Acetyl alachlor and diethyl aniline were positively identified as transformation products of alachlor under all conditions. In denitrifying reactors aniline was identified as a product of alachlor. When acetyl alachlor was fed as the parent compound, aniline was also identified as a transformation product under methanogenic conditions. This research showed that although alachlor is degraded under denitrifying, methanogenic, and sulfate-reducing conditions, significant concentrations of several metabolites are formed and are only slowly degraded. 相似文献