罗非鱼作为采矿流域大坝金属污染生物监测的模式鱼:不同组织的诊断对比和健康风险评估。

IF 3.2 3区 环境科学与生态学 Q3 ENGINEERING, ENVIRONMENTAL Environmental Geochemistry and Health Pub Date : 2024-09-24 DOI:10.1007/s10653-024-02232-8
Federico Páez-Osuna, Aldivar Castro Espinoza, Eduardo Tirado Figueroa, César J Saucedo Barrón, Magdalena E Bergés-Tiznado
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引用次数: 0

摘要

罗非鱼是一种可用作污染生物监测器的示范鱼种,因为它具有耐受性,而且可在许多受污染的地点捕获。在加利福尼亚湾东南部地区受采矿影响的 11 个水坝(1、2 和 3 号水坝包括 55 个采矿点;4 号水坝包括 8 个采矿点;6、8、10 和 11 号水坝 ≤ 6 个采矿点;5、7 和 9 号水坝分别包括 19、20 和 16 个采矿点)采集了蓝罗非鱼标本(n = 320)。分析了肌肉、肝脏、鳃和内脏中的镉、铜、铅和锌浓度,以确定金属污染并评估风险和季节变化。不同的组织表现出不同的金属积累能力,因此可以对 11 个水坝进行诊断比较。一般来说,1 号、2 号、5 号和 9 号大坝的金属浓度较高,因为这些大坝的子流域内有较多的采矿点。1 号和 2 号水坝罗非鱼肝脏中的四种金属含量最高,这可能与下游流域(55 个矿点)现在和过去的采矿活动以及这些水坝的地热活动有关。总体而言,与之前记录的最高平均值(220 微克/克)相比,1、2、3、4、5 和 10 号水坝罗非鱼肝脏中的锌含量最高。非致癌风险表明,当罗非鱼肌肉的摄入量≥ 231.5 克/周-1 时,铅的风险会增加,这表明整个人群都有可能受到不利健康影响。
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Tilapia as a model fish for biomonitoring of metal pollution in dams associated with mining watersheds: contrasting diagnosis from different tissues and health risk assessment.

Tilapia is a model fish species used as a pollution biomonitor due to its tolerance and availability in many contaminated sites. Blue tilapia Oreochromis aureus specimens (n = 320) were collected in eleven dams influenced by mining in the SE Gulf of California region (dams 1, 2 and, 3 comprise 55 mining sites; dam 4 comprises 8; dams 6, 8, 10, and 11, ≤ 6; and dams 5, 7, and 9 include 19, 20, and 16 mining sites, respectively). Cadmium, Cu, Pb, and Zn concentrations were analyzed in the muscle, liver, gills, and guts to identify metal pollution and evaluate risks and seasonal changes. The distinct tissues exhibited different metal accumulation capacities, therefore allowed develop a diagnosis comparative between the eleven dams. In general, metal concentrations were higher in dams 1, 2, 5, and 9, which are associated with more mining sites in their sub-basins. The four metals exhibited the highest levels in the tilapia liver in dams 1 and 2, which can be related to the present and past mining activity in the lower watershed (55 sites) and the geothermal activity in these dams. In general, Zn exhibited the highest level in the tilapia livers from dams 1, 2, 3, 4, 5, and 10 compared to the maximum mean (220 µg/g) concentrations previously recorded. The non-carcinogenic risks indicated that the Pb risk was enhanced when the intake was ≥ 231.5 g week-1 of tilapia muscle, indicating a potential risk of adverse health effects for the entire population.

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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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