Groundwater nitrate contamination around a municipal landfill: hydrogeochemical insights, source identification, and health risk assessment.

IF 3.2 3区 环境科学与生态学 Q3 ENGINEERING, ENVIRONMENTAL
Misbah Fida, Peiyue Li, Jing Ning, S M Khorshed Alam, Yuanhang Wang
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Abstract

This study intended to investigate the hydrochemical characteristics and sources of nitrate (NO3-N) in groundwater, and to evaluate the potential health risks in the vicinity of the Jiangcungou landfill in Northwest China. To fulfill these purposes, a total of 41 groundwater sourced primarily from the phreatic aquifer were collected and analyzed. The study found that NO3-N concentrations in the area varied between 0.57 mg/L and 47.69 mg/L, with 26.67% of samples exceeded China's drinking water threshold (20 mg/L as N) and 31.7% surpassing the WHO guideline (11.3 mg/L as N). The background level of NO3-N was estimated to be 1.11 mg/L through a probabilistic approach and was exceeded by 85.4% of the samples. Ionic ratios and land use analysis highlighted significant NO3-N contributions from domestic sewage, industrial, and agricultural sources. These findings were reinforced by principal component analysis (PCA) and the absolute principal component score-multiple linear regression (APCS-MLR) model, which attributed 40.12% of NO3-N to domestic sewage and wastewater and 7.78% to industrial and agricultural activities. Although Jiangcungou landfill is not the primary contributor, lingering leachate still affects groundwater quality, especially in nearby wells with high NO3-N concentrations. Furthermore, health risk assessments indicated significant NO3-N associated non-carcinogenic risks (HQoral > 1) for infants (63.4%), children (46.3%), females (41.5%), and males (34.1%). The Monte Carlo Simulation further supports these findings, highlighting elevated risks, especially for infants and children. This study provides important scientific support and guidance for implementing sustainable groundwater management practices and the protection of human health in affected areas.

城市垃圾填埋场周围的地下水硝酸盐污染:水文地球化学见解,来源识别和健康风险评估。
本研究旨在调查江村沟垃圾填埋场附近地下水中硝态氮(NO3-N)的水化学特征和来源,并评价其潜在的健康风险。为了实现这些目的,共收集和分析了41种主要来自潜水含水层的地下水。研究发现,该地区NO3-N浓度在0.57 mg/L ~ 47.69 mg/L之间,26.67%的样本超过中国饮用水标准(20 mg/L as N), 31.7%的样本超过世界卫生组织(11.3 mg/L as N)。通过概率法估计NO3-N的本底水平为1.11 mg/L, 85.4%的样本超过本底水平。离子比和土地利用分析强调了生活污水、工业和农业来源对NO3-N的贡献。主成分分析(PCA)和绝对主成分评分-多元线性回归(APCS-MLR)模型进一步证实了上述结论,其中40.12%的NO3-N来自生活污水和废水,7.78%来自工农业活动。虽然江村沟垃圾填埋场不是主要污染源,但残留的渗滤液仍然影响地下水质量,特别是在附近NO3-N浓度较高的井中。此外,健康风险评估显示,婴儿(63.4%)、儿童(46.3%)、女性(41.5%)和男性(34.1%)存在显著的NO3-N相关非致癌风险(HQoral bbb1)。蒙特卡洛模拟进一步支持了这些发现,强调了风险的增加,特别是对婴儿和儿童。本研究为受影响地区实施可持续地下水管理措施和保护人类健康提供了重要的科学支持和指导。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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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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