Department of Zoology, Fisheries and Illinois Aquaculture Center, Southern Illinois University, Carbondale, IL 62901, USA.
Arch Environ Contam Toxicol. 2011 Jul;61(1):83-92. doi: 10.1007/s00244-010-9614-2. Epub 2010 Nov 5.
Two hundred sediment samples were collected and their toxicity evaluated to aquatic species in a previous study in the agriculturally dominated Central Valley of California, United States. Pyrethroid insecticides were the main contributors to the observed toxicity. However, mortality in approximately one third of the toxic samples could not be explained solely by the presence of pyrethroids in the matrices. Hundreds of pesticides are currently used in the Central Valley of California, but only a few dozen are analyzed in standard environmental monitoring. A significant amount of unexplained sediment toxicity may be due to pesticides that are in widespread use that but have not been routinely monitored in the environment, and even if some of them were, the concentrations harmful to aquatic organisms are unknown. In this study, toxicity thresholds for nine sediment-associated pesticides including abamectin, diazinon, dicofol, fenpropathrin, indoxacarb, methyl parathion, oxyfluorfen, propargite, and pyraclostrobin were established for two aquatic species, the midge Chironomus dilutus and the amphipod Hyalella azteca. For midges, the median lethal concentration (LC₅₀) of the pesticides ranged from 0.18 to 964 μg/g organic carbon (OC), with abamectin being the most toxic and propargite being the least toxic pesticide. A sublethal growth endpoint using average individual ash-free dry mass was also measured for the midges. The no-observable effect concentration values for growth ranged from 0.10 to 633 μg/g OC for the nine pesticides. For the amphipods, fenpropathrin was the most toxic, with an LC₅₀ of 1-2 μg/g OC. Abamectin, diazinon, and methyl parathion were all moderately toxic (LC₅₀s 2.8-26 μg/g OC). Dicofol, indoxacarb, oxyfluorfen, propargite, and pyraclostrobin were all relatively nontoxic, with LC₅₀s greater than the highest concentrations tested. The toxicity information collected in the present study will be helpful in decreasing the frequency of unexplained sediment toxicity in agricultural waterways.
在之前针对美国加利福尼亚州中央谷地(农业为主导)的一项研究中,采集了 200 个沉积物样本并评估了其对水生物种的毒性。拟除虫菊酯杀虫剂是造成观察到的毒性的主要原因。然而,大约三分之一有毒样本的死亡率不能仅用基质中的拟除虫菊酯来解释。目前,加利福尼亚州中央谷地有数百种农药在使用,但在标准环境监测中仅分析了几十种。大量未解释的沉积物毒性可能是由于广泛使用但尚未在环境中常规监测的农药造成的,即使其中一些农药进行了监测,其对水生生物有害的浓度也是未知的。在这项研究中,为两种水生生物,即摇蚊 Chironomus dilutus 和淡水端足目 Hyalella azteca,建立了 9 种与沉积物相关的农药(包括阿维菌素、二嗪磷、三氯杀螨醇、溴氰虫酰胺、茚虫威、甲基对硫磷、氟磺胺草醚、丙溴磷和吡唑醚菌酯)的毒性阈值。对于摇蚊,这些农药的半致死浓度(LC₅₀)范围为 0.18 至 964 μg/g 有机碳(OC),其中阿维菌素毒性最大,丙溴磷毒性最小。还测量了摇蚊亚致死生长终点,即平均个体无灰干质量。九种农药的生长无观察效应浓度值范围为 0.10 至 633 μg/g OC。对于端足目,溴氰虫酰胺毒性最大,LC₅₀为 1-2 μg/g OC。阿维菌素、二嗪磷和甲基对硫磷均为中度毒性(LC₅₀为 2.8-26 μg/g OC)。三氯杀螨醇、茚虫威、氟磺胺草醚、丙溴磷和吡唑醚菌酯均相对无毒,LC₅₀大于测试的最高浓度。本研究中收集的毒性信息将有助于减少农业水道中未解释的沉积物毒性的频率。