A variety of regulatory requirements for ecotoxicity test data exist in the US and each of these is able to specify what test protocols and endpoints are used. General practice is to calculate regression curve endpoints, usually EC50 values, for acute tests, and hypothesis test endpoints (e.g. NOEC, LOEC) for chronic studies. However, tests of wastewater effluents often use a hypothesis test endpoint which has been derived using site-specific information to represent a pass-fail standard for compliance. Field work, such as site assessments, tends to use hypothesis tests, but such work does not seek the doseresponse curve sought in standard laboratory tests. The risk-based approaches being developed use cither type of endpoint, but this seems to be an accommodation to existing data; preference is for dose-response curves, not just a single ECx value. Endpoints are only one component of the conventional paradigm of environmental protection. Experience with various tests and endpoints suggest several perspectives: quality is critical, test species must be reliable and relevant, extrapolations will dominate decisions, and basing environmental decisions on the most sensitive endpoint of the most sensitive species may not remain a feasible paradigm for protecting ecological systems.

译文

在美国,对生态毒性测试数据有各种监管要求,并且每项监管要求都可以指定所使用的测试协议和终点。一般做法是为急性试验计算回归曲线终点,通常为EC50值,对于慢性研究,计算假设试验终点(例如NOEC,LOEC)。但是,废水流出物的测试通常使用假设测试终点,该终点是使用特定于地点的信息得出的,以表示合格的通过/失败标准。现场评估(例如现场评估)倾向于使用假设检验,但此类研究并未寻求标准实验室检验中所寻求的剂量反应曲线。正在开发的基于风险的方法使用其他类型的端点,但这似乎可以容纳现有数据。首选是剂量响应曲线,而不仅仅是单个ECx值。端点只是传统的环境保护范例的一个组成部分。各种测试和端点的经验提出了以下几种观点:质量至关重要,测试物种必须可靠且相关,外推法将主导决策,将环境决策基于最敏感物种的最敏感端点可能仍不是保护生态的可行范例系统。

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