U.S. Environmental Protection Agency, Office of Research and Development, National Center for Environmental Assessment, 26 Martin Luther King Dr. W, Cincinnati, OH 45268, USA.
Tetra Tech, Inc., 10711 Red Run Blvd., Suite 105, Owings Mills, MD 21117, USA.
Sci Total Environ. 2018 Aug 15;633:1637-1646. doi: 10.1016/j.scitotenv.2018.01.136. Epub 2018 Feb 7.
Most water quality criteria are based on laboratory toxicity tests and usually include chronic and acute magnitudes. Field-based criteria are typically based on long-term or continuous exposures, so they are chronic. Biological responses of quantified, short-term aqueous exposures are seldom documented in the field. However, acute values may be derived by estimating an upper limit using temporal variance and chronic values. This method estimates an upper limit from the variance of pollutant measurements from stream locations that attain the chronic criterion. The formula for deriving a 90th centile of a standard normal distribution is used to identify the upper limit, a criterion maximum exposure concentration (CMEC). The calculated CMEC is interpreted as a maximum exposure that 95% of organisms may tolerate if the chronic exposure is not exceeded. The methods of deriving chronic and acute criteria are illustrated with specific conductivity in a mountainous area in the eastern United States. The biological relevance of the CMEC was assessed using the maximum annual exposure during the life cycle of the most salt-intolerant genera. The method using the chronic criterion and the variance of water chemistry data is practical, whereas frequently collecting and analyzing paired biological and chemical samples at numerous sites is impractical and may give misleading results due to lags in biological response. This method can be used anywhere with sufficient data to estimate the temporal variability and may be applicable for field-based criteria other than the specific conductivity criteria illustrated here.
大多数水质标准都是基于实验室毒性测试制定的,通常包括慢性和急性指标。基于现场的标准通常基于长期或连续暴露,因此属于慢性指标。在现场很少记录量化的短期水相暴露的生物反应。然而,可以通过估计使用时间方差的上限值和慢性值来推导出急性值。该方法通过从达到慢性标准的溪流位置的污染物测量值的方差中估计上限值,即临界最大暴露浓度(CMEC)。用于确定标准正态分布 90 百分位数的公式用于确定上限值,即临界最大暴露浓度(CMEC)。计算得出的 CMEC 被解释为在不超过慢性暴露的情况下,95%的生物可能耐受的最大暴露量。使用美国东部山区的特定电导率来说明推导慢性和急性标准的方法。使用生命周期中最不耐盐属的最大年暴露量评估了 CMEC 的生物学相关性。使用慢性标准和水化学数据方差的方法是实用的,而在许多地点频繁采集和分析生物和化学样本的配对样本是不切实际的,并且由于生物反应的滞后,可能会产生误导性的结果。该方法可在任何有足够数据的地方使用,以估计时间变异性,并且可能适用于这里所示的特定电导率标准以外的基于现场的标准。