National Engineering Laboratory for Lake Pollution Control and Ecological Restoration, Chinese Research Academy of Environmental Sciences, Beijing 100012, China; State Environmental Protection Scientific Observation and Research Station for Lake Dongting, Chinese Research Academy of Environmental Sciences, Beijing 100012, China; State Environmental Protection Key Laboratory of Drinking Water Source Protection, Chinese Research Academy of Environmental Sciences, Beijing 100012, China; State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China.
National Engineering Laboratory for Lake Pollution Control and Ecological Restoration, Chinese Research Academy of Environmental Sciences, Beijing 100012, China; State Environmental Protection Scientific Observation and Research Station for Lake Dongting, Chinese Research Academy of Environmental Sciences, Beijing 100012, China; State Environmental Protection Key Laboratory of Drinking Water Source Protection, Chinese Research Academy of Environmental Sciences, Beijing 100012, China; State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China; School of Ecological and Environmental Sciences, East China Normal University, Shanghai 200241, China.
Mar Pollut Bull. 2024 Dec;209(Pt A):117181. doi: 10.1016/j.marpolbul.2024.117181. Epub 2024 Oct 24.
This study analyzed the spatiotemporal distribution characteristics, ecological risks, biological toxicity, and sources of Cu, Zn, Pb, Cd, Hg, and As in the surface sediments of Dongting Lake, as well as the response of benthic macroinvertebrates to these pollutants. Among the three lake regions, the concentration of Cu, Zn, Pb, Cd, and As fell in the order of South Dongting Lake (SD) > East Dongting Lake (ED) > West Dongting Lake (WD), whereas the concentration of Hg fell in the order of WD > SD > ED. The concentrations of Cu, Zn, Pb, and As were 1.69-2.02 times the background values recorded in 1986, whereas the concentrations of Cd and Hg were 8.97 and 5.32 times the background values, respectively. The ecological risk was low for Cu, Zn, Pb, As but high for Hg and Cd. For Dongting Lake in aggregate, the heavy metals caused considerable ecological risk and high biotoxicity, although the situation was improving in recent years. Cd, As, Cu, Pb, Hg were mainly from agricultural sources, mining sources, tire wear and agricultural sources, industrial smelting and mining sources, industrial processing and smelting sources, respectively, and Zn was from mixed sources. A total of 66 species of benthic macroinvertebrates were identified from the sediments. From 2018 to 2022, the dominant benthic macroinvertebrates gradually shifted from the pollution-resistant in Tubificidae to those in Gammarus, Bellamya, Valvatidae, etc. Oligochaetes and Stictochironomus spp. exhibited extremely high response to heavy metals and could serve as indicator organisms of heavy metal pollution.
本研究分析了洞庭湖表层沉积物中 Cu、Zn、Pb、Cd、Hg 和 As 的时空分布特征、生态风险、生物毒性及来源,以及底栖大型无脊椎动物对这些污染物的响应。在三个湖区中,Cu、Zn、Pb、Cd 和 As 的浓度顺序为南洞庭湖(SD)>东洞庭湖(ED)>西洞庭湖(WD),而 Hg 的浓度顺序为 WD>SD>ED。Cu、Zn、Pb 和 As 的浓度分别是 1986 年背景值的 1.69-2.02 倍,而 Cd 和 Hg 的浓度分别是背景值的 8.97 和 5.32 倍。Cu、Zn、Pb 和 As 的生态风险较低,Hg 和 Cd 的生态风险较高。就洞庭湖整体而言,重金属造成了相当大的生态风险和高生物毒性,尽管近年来情况有所改善。Cd、As、Cu、Pb、Hg 主要来源于农业源、矿业源、轮胎磨损和农业源、工业冶炼和矿业源、工业加工和冶炼源,而 Zn 则来源于混合源。沉积物中共鉴定出 66 种底栖大型无脊椎动物。2018 年至 2022 年,底栖大型无脊椎动物的优势种逐渐从耐污种(如颤蚓科)向对重金属耐受能力较强的种(如沼虾属、圆田螺属、瓣鳃目等)转移。寡毛类和摇蚊科对重金属表现出极高的响应,可以作为重金属污染的指示生物。