A comprehensive investigation of the occurrence and speciation of arsenic in the water, sediments and aquatic products in Dongping Lake, an important drinking water source in East China.

IF 3.2 3区 环境科学与生态学 Q3 ENGINEERING, ENVIRONMENTAL
Ju Zhang, Huanguang Deng, Zhibo Zhang, Huaizhen Zhang, Dongqi Wang, Qiaoyan Li, Hao Wang, Linsong Yu
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Abstract

The total arsenic (TAs), inorganic arsenic (iAs) including arsenate (As(V)) and arsenite (As(III)) distribution in water, surface/core sediments and aquatic products in Dongping Lake was investigated. The pollution levels and associated risks were evaluated using the methods of geoaccumulation index, single factor index, health risk model and potential ecological risk index. The results showed that As(V) dominated across all environmental matrices. TAs concentrations in water (1.36-3.90 μg/L) were all below the threshold set by the World Health Organization (10 μg/L). The average concentrations of As(V) and As(III) in water were 0.82 ± 0.48 μg/L and 0.28 ± 0.31 μg/L, respectively, while those in surface sediments were 7.30 ± 2.58 mg/kg and 1.16 ± 0.38 mg/kg. Laohu Wharf, the Dawen River inlet and the northern outlet area were identified as hot spots for elevated arsenic levels in water and surface sediments. In core sediments, the maximums were detected at a depth of 1-2 cm or 2-3 cm. As(V) and As(III) in water were significantly correlated with dissolved organic carbon, Chla, dissolved inorganic nitrogen and pH. As(V) in sediments were closely associated with oxidation-reduction potential, organic carbon and total nitrogen. Shellfish had significantly higher TAs and iAs levels compared to fish and shrimp. Collectively, shellfish and fish had been polluted with iAs. The average carcinogenic risks caused by iAs through daily intake of shellfish (3.72 × 10-4/a) exceeded the acceptable level (10-4/a). The TAs pollution in sediments was at a slight to moderate contamination level and posed a considerable ecological risk.

华东地区重要饮用水源地东平湖水体、沉积物及水产品中砷的赋存形态综合调查
研究了东平湖水体、表层/核心沉积物和水产品中的总砷(TAs)、无机砷(iAs),包括砷酸盐(As(V))和亚砷酸盐(As(III))的分布。采用地理累积指数、单因子指数、健康风险模型和潜在生态风险指数等方法对污染水平和相关风险进行了评估。结果表明,As(V)在所有环境基质中均占主导地位。水中的 TAs 浓度(1.36-3.90 μg/L)均低于世界卫生组织设定的阈值(10 μg/L)。水中As(V)和As(III)的平均浓度分别为0.82±0.48微克/升和0.28±0.31微克/升,而表层沉积物中As(V)和As(III)的平均浓度分别为7.30±2.58毫克/千克和1.16±0.38毫克/千克。老湖码头、大汶河入海口和北部出海口地区被确定为水体和表层沉积物中砷含量升高的热点地区。在岩心沉积物中,砷含量最高的深度为 1-2 厘米或 2-3 厘米。水中的 As(V) 和 As(III) 与溶解有机碳、Chla、溶解无机氮和 pH 值有显著相关性。沉积物中的 As(V) 与氧化还原电位、有机碳和总氮密切相关。贝类的 TAs 和 iAs 含量明显高于鱼类和虾类。总的来说,贝类和鱼类都受到了碘砷的污染。每天摄入贝类的 iAs 平均致癌风险(3.72 × 10-4/a)超过了可接受水平(10-4/a)。沉积物中的 TAs 污染处于轻度至中度污染水平,对生态构成了相当大的风险。
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来源期刊
Environmental Geochemistry and Health
Environmental Geochemistry and Health 环境科学-工程:环境
CiteScore
8.00
自引率
4.80%
发文量
279
审稿时长
4.2 months
期刊介绍: Environmental Geochemistry and Health publishes original research papers and review papers across the broad field of environmental geochemistry. Environmental geochemistry and health establishes and explains links between the natural or disturbed chemical composition of the earth’s surface and the health of plants, animals and people. Beneficial elements regulate or promote enzymatic and hormonal activity whereas other elements may be toxic. Bedrock geochemistry controls the composition of soil and hence that of water and vegetation. Environmental issues, such as pollution, arising from the extraction and use of mineral resources, are discussed. The effects of contaminants introduced into the earth’s geochemical systems are examined. Geochemical surveys of soil, water and plants show how major and trace elements are distributed geographically. Associated epidemiological studies reveal the possibility of causal links between the natural or disturbed geochemical environment and disease. Experimental research illuminates the nature or consequences of natural or disturbed geochemical processes. The journal particularly welcomes novel research linking environmental geochemistry and health issues on such topics as: heavy metals (including mercury), persistent organic pollutants (POPs), and mixed chemicals emitted through human activities, such as uncontrolled recycling of electronic-waste; waste recycling; surface-atmospheric interaction processes (natural and anthropogenic emissions, vertical transport, deposition, and physical-chemical interaction) of gases and aerosols; phytoremediation/restoration of contaminated sites; food contamination and safety; environmental effects of medicines; effects and toxicity of mixed pollutants; speciation of heavy metals/metalloids; effects of mining; disturbed geochemistry from human behavior, natural or man-made hazards; particle and nanoparticle toxicology; risk and the vulnerability of populations, etc.
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