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淡水生态系统中杀虫剂影响的阈值水平:综述

Threshold levels for effects of insecticides in freshwater ecosystems: a review.

作者信息

Van Wijngaarden René P A, Brock Theo C M, Van den Brink Paul J

机构信息

Alterra, Wageningen UR, P.O. Box 47, NL-6700 AA Wageningen, The Netherlands.

出版信息

Ecotoxicology. 2005 Apr;14(3):355-80. doi: 10.1007/s10646-004-6371-x.

Abstract

A literature review of freshwater (model) ecosystem studies with neurotoxic insecticides was performed to assess ecological threshold levels, to compare these levels with the first tier approach within European Union (EU) administration procedures, and to evaluate the ecological consequences of exceeding these thresholds. Studies published between 1980 and 2001 were reviewed. Most studies covered organophosphates and synthetic pyrethroids in lentic waters. The most sensitive taxa were representatives of crustaceans, insects and fish. Based on toxic units, threshold values were equivalent for compounds with a similar mode of action. This also accounted for the nature and magnitude of direct effects at higher concentrations. Although laboratory single species toxicity tests may not allow predictions on precise ecological effects, some generalisations on effects and recovery can be made with respect to acute standard laboratory EC50 data. The NOEC(ecosystem) usually is a factor of 10 or more higher than first tier acceptable concentrations, particularly in the case of single applications and acetylcholinesterase inhibitors. Acceptable concentrations, as set by the EU first tier approach, appear to be protective. Recovery of sensitive endpoints usually occurs within 2 months of the (last) application when peak concentrations remain lower than (0.1-1) x EC50 of the most sensitive standard test species. The consistency of response patterns found in model ecosystem studies can be useful when estimating the ecological risks of pesticides. The use of an effect classification system was also helpful in evaluating effects.

摘要

对使用神经毒性杀虫剂的淡水(模型)生态系统研究进行了文献综述,以评估生态阈值水平,将这些水平与欧盟管理程序中的一级方法进行比较,并评估超过这些阈值的生态后果。对1980年至2001年间发表的研究进行了综述。大多数研究涵盖了静水水体中的有机磷和合成拟除虫菊酯。最敏感的分类群是甲壳类动物、昆虫和鱼类的代表。基于毒性单位,具有相似作用模式的化合物的阈值是等效的。这也说明了较高浓度下直接影响的性质和程度。尽管实验室单物种毒性试验可能无法预测精确的生态影响,但可以根据急性标准实验室EC50数据对影响和恢复情况进行一些概括。生态系统无观测效应浓度(NOEC)通常比一级可接受浓度高10倍或更多,特别是在单次施用和乙酰胆碱酯酶抑制剂的情况下。欧盟一级方法设定的可接受浓度似乎具有保护作用。当峰值浓度低于最敏感标准测试物种的(0.1 - 1)×EC50时,敏感终点通常会在(最后一次)施用后的2个月内恢复。在估计农药的生态风险时,模型生态系统研究中发现的响应模式的一致性可能会很有用。使用效应分类系统也有助于评估影响。

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