Sun Runxia, Luo Xiaojun, Tang Bin, Chen Laiguo, Liu Yu, Mai Bixian
State Key Laboratory of Organic Geochemistry and Guangdong Key Laboratory of Environmental Protection and Resources Utilization, Guangzhou Institute of Geochemistry, Chinese Academy of Sciences, Guangzhou 510640, People's Republic of China; University of Chinese Academy of Sciences, Beijing, 100049, People's Republic of China.
State Key Laboratory of Organic Geochemistry and Guangdong Key Laboratory of Environmental Protection and Resources Utilization, Guangzhou Institute of Geochemistry, Chinese Academy of Sciences, Guangzhou 510640, People's Republic of China.
Environ Pollut. 2017 Mar;222:165-174. doi: 10.1016/j.envpol.2016.12.060. Epub 2016 Dec 28.
Short chain chlorinated paraffins (SCCPs) are under review for inclusion into the Stockholm Convention on Persistent Organic Pollutants. However, limited information is available on their bioaccumulation and biomagnification in ecosystems, which is hindering evaluation of their ecological and health risks. In the present study, wild aquatic organisms (fish and invertebrates), water, and sediment collected from an enclosed freshwater pond contaminated by electronic waste (e-waste) were analyzed to investigate the bioaccumulation, distribution, and trophic transfer of SCCPs in the aquatic ecosystem. SCCPs were detected in all of the investigated aquatic species at concentrations of 1700-95,000 ng/g lipid weight. The calculated bioaccumulation factors (BAFs) varied from 2.46 to 3.49. The relationship between log BAF and the octanol/water partition coefficient (log K) for benthopelagic omnivorous fish species followed the empirical model of bioconcentration, indicating that bioconcentration plays an important role in accumulation of SCCPs. In contrast, the relationship for the benthic carnivorous fish and invertebrates was not consistent with the empirical model of bioconcentration, implying that the bioaccumulation of SCCPs in these species could be more influenced by other complex factors (e.g., habitat and feeding habit). Preferential distribution in the liver rather than in other tissues (e.g., muscle, gills, skin, and kidneys) was noted for the SCCP congeners with higher log K, and bioaccumulation pathway (i.e. water or sediment) can affect the tissue distribution of SCCP congeners. SCCPs underwent trophic dilution in the aquatic food web, and the trophic magnification factor (TMF) values of SCCP congener groups significantly correlated with their corresponding log K values (p < 0.0001). The present study results improved our understanding on the environmental behavior and fate of SCCPs in aquatic ecosystem.
短链氯化石蜡(SCCPs)正在接受审查,以确定是否将其纳入《关于持久性有机污染物的斯德哥尔摩公约》。然而,关于它们在生态系统中的生物累积和生物放大作用的信息有限,这阻碍了对其生态和健康风险的评估。在本研究中,对从一个受电子废物(电子垃圾)污染的封闭淡水池塘采集的野生水生生物(鱼类和无脊椎动物)、水和沉积物进行了分析,以研究短链氯化石蜡在水生生态系统中的生物累积、分布和营养转移。在所调查的所有水生物种中均检测到短链氯化石蜡,其浓度为1700-95000纳克/克脂重。计算得出的生物累积因子(BAFs)在2.46至3.49之间变化。底栖中上层杂食性鱼类的对数生物累积因子(log BAF)与正辛醇/水分配系数(log K)之间的关系遵循生物富集的经验模型,表明生物富集在短链氯化石蜡的累积中起重要作用。相比之下,底栖肉食性鱼类和无脊椎动物的关系与生物富集的经验模型不一致,这意味着这些物种中短链氯化石蜡的生物累积可能受其他复杂因素(如栖息地和摄食习惯)的影响更大。对于log K较高的短链氯化石蜡同系物,其在肝脏中的分布优先于其他组织(如肌肉、鳃、皮肤和肾脏),并且生物累积途径(即水或沉积物)会影响短链氯化石蜡同系物的组织分布。短链氯化石蜡在水生食物网中经历了营养稀释,短链氯化石蜡同系物组的营养放大因子(TMF)值与其相应的log K值显著相关(p < 0.0001)。本研究结果增进了我们对短链氯化石蜡在水生生态系统中的环境行为和归宿的理解。