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2007 年施药后戴维斯湖内鱼藤酮制剂的命运。

Rotenone formulation fate in Lake Davis following the 2007 treatment.

机构信息

Department of Environmental Toxicology, University of California Davis, Davis, California, USA.

出版信息

Environ Toxicol Chem. 2012 May;31(5):1032-41. doi: 10.1002/etc.1795. Epub 2012 Mar 23.

DOI:10.1002/etc.1795
PMID:22407799
Abstract

In September 2007, Lake Davis (near Portola, California) was treated by the California Department of Fish and Game with CFT Legumine, a rotenone formulation, to eradicate the invasive northern pike (Esox lucius). The objective of this report is to describe the fate of the five major formulation constituents-rotenone, rotenolone, methyl pyrrolidone (MP), diethylene glycol monethyl ether (DEGEE), and Fennedefo 99-in water, sediment, and brown bullhead catfish (Ameiurus nebulosus; a rotenone-resistant species) by determination of their half-lives (t(1/2)) and pseudo first-order dissipation rate constants (k). The respective t(1/2) values in water for rotenone, rotenolone, MP, DEGEE, and Fennedefo 99 were 5.6, 11.1, 4.6, 7.7, and 13.5 d; in sediments they were 31.1, 31.8, 10.0, not able to calculate, and 48.5 d; and in tissues were 6.1, 12.7, 3.7, 3.2, and 10.4 d, respectively. Components possessing low water solubility values (rotenone and rotenolone) persisted longer in sediments (not detectable after 157 d) and tissues (<212 d) compared with water, whereas the water-miscible components (MP and DEGEE) dissipated more quickly from all matrices, except for Fennedefo 99, which was the most persistent in water (83 d). None of the constituents was found to bioaccumulate in tissues as a result of treatment. In essence, the physicochemical properties of the chemical constituents effectively dictated their fate in the lake following treatment.

摘要

2007 年 9 月,加利福尼亚鱼类和狩猎部门在加利福尼亚州的戴维斯湖(靠近波托拉)用 CFT Legumine(一种鱼藤酮制剂)处理,以消灭入侵的北方狗鱼(Esox lucius)。本报告的目的是描述五种主要制剂成分——鱼藤酮、鱼藤酮醇、甲基吡咯烷酮(MP)、二乙二醇单乙醚(DEGEE)和 Fennedefo 99 在水中、沉积物和褐鳜(Ameiurus nebulosus;一种抗鱼藤酮的物种)中的命运,方法是测定它们的半衰期(t(1/2))和拟一级消解速率常数(k)。鱼藤酮、鱼藤酮醇、MP、DEGEE 和 Fennedefo 99 在水中的半衰期分别为 5.6、11.1、4.6、7.7 和 13.5 d;在沉积物中的半衰期分别为 31.1、31.8、10.0、无法计算和 48.5 d;在组织中的半衰期分别为 6.1、12.7、3.7、3.2 和 10.4 d。水溶性低的成分(鱼藤酮和鱼藤酮醇)在沉积物中(157 天后无法检测到)和组织中(<212 天)的持久性更长,而水溶性成分(MP 和 DEGEE)在所有基质中的消解速度更快,除了 Fennedefo 99,它在水中的持久性最长(83 d)。由于处理,没有一种成分被发现在组织中生物积累。实际上,化学物质的物理化学性质有效地决定了它们在处理后在湖中命运。

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