...
首页> 外文期刊>Environmetrics >HOW TO MEASURE NO EFFECT. PART III: STATISTICAL ASPECTS OF NOEC, ECx AND NEC ESTIMATES
【24h】

HOW TO MEASURE NO EFFECT. PART III: STATISTICAL ASPECTS OF NOEC, ECx AND NEC ESTIMATES

机译:如何测量无效。第三部分:NOEC,ECx和NEC估计的统计方面

获取原文
获取原文并翻译 | 示例
   

获取外文期刊封面封底 >>

       

摘要

One of the principal aims of ecotoxicity tests is to determine the concentration level below which the test chemical will have no or at most a negligible effect on the test parameter. Nowadays, the NOEC (no observed effect concentration) is normally used as an estimate for this concentration. The NOEC has, however, several major drawbacks as a summary statistic:(i) it is based on wrong usage of hypothesis testing—the acceptance of a null hypothesis (no difference);(ii) the estimate depends on the accuracy of the experimental test—when the sample error is small, i.e. the test is performed accurately, the NOEC will be lower;(iii) the estimate depends on the sample size—the larger the sample size, the lower the NOEC will be;(iv) the NOEC is a test concentration;(v) the NOEC depends on the chosen significance level.An alternative is proposed, the ECx, i.e. the concentration causing an effect of x per cent:1. To estimate the ECx a concentration–response model is needed. The value of x in the ECx estimation should be chosen so that the ECx estimate is not too model dependent.2. In NOEC estimation a certain deviation from the control is accepted. For an ECx estimation to give comparable protection with an NOEC, the x must be chosen somewhat smaller than the maximum non-significant deviation in the case where the test is performed according to normal guideline procedures and the variance in the control is the mean variance for such tests.Another alternative is parametric NEC (no effect concentration) estimation. The NEC is the threshold concentration below which the test chemical will not induce an effect.(a) All NEC estimates will be model dependent. Therefore, they are not appropriate in standard ecotoxicity tests where data will seldom be sufficient for model verification. © 1997 John Wiley & Sons, Ltd.
机译:生态毒性测试的主要目的之一是确定浓度水平,低于该浓度水平,测试化学品将对测试参数无影响或至多可以忽略不计。如今,通常将NOEC(未观察到作用浓度)用作该浓度的估算值。但是,NOEC作为汇总统计数据有几个主要缺点:(i)基于错误的假设检验使用-接受零假设(无差异);(ii)估计取决于实验的准确性测试-当样本误差较小时,即准确执行测试,则NOEC会较低;(iii)估计值取决于样本量-样本量越大,NOEC会越低;(iv) NOEC是测试浓度;(v)NOEC取决于所选的显着性水平。提出了一种替代方案ECx,即引起x%的影响的浓度:1。要估算ECx,需要一个浓度响应模型。应该选择ECx估计中的x值,以使ECx估计不会太依赖模型。在NOEC估算中,接受了与控件的一定偏差。为了使ECx估算值具有与NOEC相当的保护,在按照常规准则程序进行测试且控制方差为以下情况的平均方差的情况下,x必须选择为略小于最大非显着性偏差另一种选择是参数NEC(无效应集中)估计。 NEC是阈值浓度,低于该阈值浓度,测试化学品将不会产生影响。(a)所有NEC估计值都将取决于模型。因此,它们不适用于标准的生态毒性测试,因为这些数据很少足以用于模型验证。 ©1997 John Wiley&Sons,Ltd.

著录项

相似文献

  • 外文文献
  • 中文文献
  • 专利
获取原文

客服邮箱:kefu@zhangqiaokeyan.com

京公网安备:11010802029741号 ICP备案号:京ICP备15016152号-6 六维联合信息科技 (北京) 有限公司©版权所有
  • 客服微信

  • 服务号