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Haloacetic acids in the aquatic environment. Part Ⅰ: macrophyte toxicity

机译:在水生环境中的卤乙酸。第一部分:大型植物毒性

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Haloacetic acids (HAAs) are contaminants of aquatic ecosystems with numerous sources, both anthropogenic and natural. The toxicity of HAAs to aquatic plants is generally uncharacterized. Laboratory tests were conducted with three macrophytes (Lemna gibba, Myriophyllum sibiricum and Myriophyllum spicatum) to assess the toxicity of five HAAs. Myriophyllum spp. has been proposed as required test species for pesticide registration in North America, but few studies have been conducted under standard test conditions. The HAAs in the present experiments were monochloroacetic acid (MCA), dichloroacetic acid (DCA), trichloroacetic acid (TCA), trifluoroacetic acid (TFA) and chlorodifluoroacetic acid (CDFA). MCA was the most toxic to Myriophyllum spp. with EC_(50) values ranging from 8 to 12.4 mg/l depending on the endpoint, followed by DCA (EC_(50) range 62-722.5 mg/l), TCA (EC_(50) range 49.5-1702.6 mg/l), CDFA (EC_(50) range 105.3 to > 10,000 mg/l) and with TFA (EC_(50) range 222.1 to 10,000 mg/l) the least toxic. Generally, L. gibba was less sensitive to 1HAA toxicity than Myriophyllum spp., with the difference in toxicity between them approximately threefold. The range of toxicity within Myriophyllum spp. was normally less than twofold. Statistically, plant length and node number were the most sensitive endpoints as they had the lowest observed coefficients of variation, but they were not the most sensitive to HAA toxicity. Toxicological sensitivity of endpoints varied depending on the measure of effect chosen and the HAA, with morphological endpoints usually an order of magnitude more sensitive than pigments for all plant species. Overall, mass and root measures tended to be the most sensitive indicators of HAA toxicity. The data from this paper were subsequently used in an ecological risk assessment for HAAs and aquatic plants. The assessment found HAAs to be of low risk to aquatic macrophytes and the results are described in the second manuscript of this series.
机译:卤乙酸(HAA)是人为和天然来源众多的水生生态系统污染物。 HAA对水生植物的毒性通常是未知的。实验室测试了三种大型植物(Lemna gibba,Myriophyllum sibiricum和Myriophyllum spicatum),以评估五种HAA的毒性。桃金娘科已提出将其作为北美农药注册所需的测试物种,但很少在标准测试条件下进行过研究。本实验中的HAA是一氯乙酸(MCA),二氯乙酸(DCA),三氯乙酸(TCA),三氟乙酸(TFA)和氯二氟乙酸(CDFA)。 MCA对桃金娘属植物的毒性最大。 EC_(50)值的范围从8到12.4 mg / l(取决于端点),然后是DCA(EC_(50)的范围是62-722.5 mg / l),TCA(EC_(50)的范围是49.5-1702.6 mg / l) ,CDFA(EC_(50)范围为105.3到> 10,000 mg / l)和TFA(EC_(50)范围为222.1到10,000 mg / l)毒性最小。通常,吉百乳杆菌对1HAA毒性的敏感性不及肉豆蔻属,它们之间的毒性差约为三倍。桃金娘属的毒性范围。通常小于两倍。从统计学上讲,植物长度和节数是最敏感的终点,因为它们的变异系数最低,但对HAA毒性不是最敏感。终点的毒理学敏感性根据所选择的作用程度和HAA的不同而有所不同,对于所有植物物种,形态学终点的敏感性通常比色素高一个数量级。总体而言,质量和根测量往往是HAA毒性的最敏感指标。该论文的数据随后被用于HAA和水生植物的生态风险评估。评估发现,HAA对水生植物的风险低,该结果在本系列的第二篇论文中进行了描述。

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