基于物种敏感性分布模型的长三角地表水壬基酚生态风险评价

Zhang Jiawei, Qi Guanjing, Zhao Haoduo, G. Hui, L. Qingwei, Shi Jianghong, Yuan Xiangyi, Mao Yan, Guo Wei, Meng Yaobin, L. Xiaoyan
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In this study, SSD was applied to calculate the predicted no effect concentrations (PNECs) based on the acute and chronic toxicity data of the general sensitive species and native sensitive species in China. The results showed that there was little difference between the PNECs derived from the general sensitive species and native sensitive species based on the acute toxicity data, which indicated that the sensitivity of native species towards the acute toxicity effect of NP is similar to that of general species. However, the PNECs based on the chronic toxicity data were quite different, and the Chinese native species appeared to be more sensitive than general species to the chronic toxicity effect of NP. As a result, direct use of the PNECs derived from non-local species may lead to insufficient protection of Chinese native species. 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引用次数: 1

摘要

壬基酚是一种典型的具有内分泌干扰作用的持久性有机污染物。由于其耐降解性、生物蓄积性和在环境中的广泛分布,其生态风险日益引起人们的关注。物种敏感性分布法(SSD)已广泛应用于水环境生态风险评价和水质标准的建立。然而,所选的敏感物种在不同的地理区域可能表现出不同的毒性敏感性,这将影响WQC和ERA的结果。本研究基于中国一般敏感种和本地敏感种的急、慢性毒性数据,应用SSD计算预测无效应浓度(PNECs)。结果表明,根据急性毒性数据,一般敏感种的pnec与本地敏感种的pnec差异不大,表明本地物种对NP急性毒性效应的敏感性与一般物种相似。然而,基于慢性毒性数据的pnec存在较大差异,中国本土种对NP的慢性毒性作用似乎比一般种更敏感。因此,直接利用非本地物种衍生的pnec可能会导致对中国本地物种的保护不足。基于急性和慢性毒性数据得出的pnec,采用风险商(RQ)方法对长三角地表水NP的生态风险进行表征。结果表明,基于一般敏感物种急性数据和慢性数据的pnec的RQ可能导致生态风险的低估。基于中国本土敏感种慢性数据的pnec的平均RQ值为0.23 ~ 1.55。骆马湖呈高风险区,太湖和长江(南京)的最大RQ值均超过1,表明该地区存在较高风险区,值得进一步关注。综上所述,NP对中国本土水生生物的慢性毒性作用是可以确定的,应持续关注NP的长期不良影响,并采取措施确保水生生态系统的健康。
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Ecological Risk Assessment of Nonylphenol in Surface Waters of the Yangtze River Delta Based on Species Sensitivity Distribution Model
Nonylphenol (NP) is a typical type of persistent organic pollutants (POPs) with endocrine-disrupting effect. Its ecological risk has caused increasing concerns owing to its degradation-resistance, bioaccumulation, and widespread distribution in the environment. The species sensitivity distribution (SSD) method has been widely used for establishing water quality criteria (WQC) and performing ecological risk assessment (ERA) of the water environment. However, the selected sensitive species may exhibit different toxicity sensitivity in different geographical regions, which would affect the results of WQC and ERA. In this study, SSD was applied to calculate the predicted no effect concentrations (PNECs) based on the acute and chronic toxicity data of the general sensitive species and native sensitive species in China. The results showed that there was little difference between the PNECs derived from the general sensitive species and native sensitive species based on the acute toxicity data, which indicated that the sensitivity of native species towards the acute toxicity effect of NP is similar to that of general species. However, the PNECs based on the chronic toxicity data were quite different, and the Chinese native species appeared to be more sensitive than general species to the chronic toxicity effect of NP. As a result, direct use of the PNECs derived from non-local species may lead to insufficient protection of Chinese native species. Based on the PNECs derived from the acute and chronic toxicity data, the risk quotient (RQ) method was used to characterize the ecological risk of NP in the surface waters of Yangtze River Delta. The results showed that the RQ based on PNECs derived from the acute data and chronic data of general sensitive species may lead to an underestimation of the ecological risk. The mean RQ values based on the PNECs derived from the chronic data of Chinese native sensitive species ranged from 0.23 to 1.55. Luoma Lake was found at a high risk, and the maximum RQ values of Taihu Lake and Yangtze River (Nanjing) exceeded 1, indicating the high risk of the individual areas which deserve further attentions. In conclusion, the chronic toxic effect of NP on Chinese native aquatic organisms can be identified, and continuous attention should be paid to the long-term adverse effect of NP, for which actions should be taken to ensure the health of the aquatic ecosystem.
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