基于正矩阵因式分解和蒙特卡罗模拟的城市公园尘埃多环芳烃特定来源概率健康风险评估。

IF 3.2 3区 环境科学与生态学 Q3 ENGINEERING, ENVIRONMENTAL
Haijing Duan, Yanfeng Wang, Haoxin Shen, Chong Ren, Jing Li, Jiaheng Li, Yangyang Wang, Yanxia Su
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引用次数: 0

摘要

了解城市公园灰尘中多环芳烃 (PAH) 的健康风险并确定优先控制源对于公共卫生和污染管理至关重要。将特定来源和蒙特卡洛相结合,不仅能降低管理成本,还能提高评估的准确性。为了评估城市公园粉尘中多环芳烃的来源以及不同来源可能造成的健康风险,采用气相色谱-质谱联用仪(GC-MS)对开封市 13 个热门公园的粉尘样本进行了多环芳烃分析。结果表明,研究区域的地表尘埃多环芳烃含量介于 332.34 微克-千克-1 至 7823.03 微克-千克-1 之间,平均值为 1756.59 微克-千克-1。研究区域的内默罗综合污染指数介于 0.32 至 14.41 之间,平均值为 2.24,表明总体污染情况值得关注。利用正矩阵因式分解(PMF)模型确定了四个污染源:运输源、运输-煤炭和生物质燃烧源、焦炉排放源和石油源,其贡献率分别为 33.74%、25.59%、22.14% 和 18.54%。蒙特卡罗癌症风险模拟结果表明,公园粉尘中的多环芳烃对所有三个人群(儿童、成年男性和成年女性)都有潜在的癌症风险。此外,儿童的致癌风险普遍高于成年男性和成年女性,而运输来源是致癌风险的主要来源。最后,敏感性分析结果显示,毒性当量浓度(CS)是对致癌风险影响最大的参数,其次是暴露持续时间(ED)。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Source-specific probabilistic health risk assessment of dust PAHs in urban parks based on positive matrix factorization and Monte Carlo simulation.

Understanding the health risks of polycyclic aromatic hydrocarbons (PAHs) in dust from city parks and prioritizing sources for control are essential for public health and pollution management. The combination of Source-specific and Monte Carlo not only reduces management costs, but also improves the accuracy of assessments. To evaluate the sources of PAHs in urban park dust and the possible health risks caused by different sources, dust samples from 13 popular parks in Kaifeng City were analyzed for PAHs using gas chromatograph-mass spectrometer (GC-MS). The results showed that the surface dust PAH content in the study area ranged from 332.34 µg·kg-1 to 7823.03 µg·kg-1, with a mean value of 1756.59 µg·kg-1. Nemerow Composite Pollution Index in the study area ranged from 0.32 to 14.41, with a mean of 2.24, indicating that the overall pollution warrants attention. Four pollution sources were identified using the positive matrix factorization (PMF) model: transportation source, transportation-coal and biomass combustion source, coke oven emission source, and petroleum source, with contributions of 33.74%, 25.59%, 22.14%, and 18.54%, respectively. The Monte Carlo cancer risk simulation results indicated that park dust PAHs pose a potential cancer risk to all three populations (children, adult male and adult female). Additionally, the cancer risk for children was generally higher than that for adult males and females, with transportation sources being the main contributor to the carcinogenic risk. Lastly, sensitivity analyses results showed that the toxic equivalent concentration (CS) is the parameter contributing the most to carcinogenic risk, followed by Exposure duration (ED).

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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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