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基于SOM-PMF模型的土壤重金属源解析及风险量化:对生态与人类健康管理的启示

Source apportionment and risk quantification of soil heavy metals using SOM-PMF model: implications for ecological and human health management.

作者信息

Lv Xinghao, Li Chao, Wang Huanhuan, Yang Shufeng, Wang Shiqi, Yang Chao, Teng Fei, Zhao Jing, Xu Xuesheng, Zhang Hao, Shang Jianbo

机构信息

Ecological Environment Bureau of Xiangxi Tujia and Miao Autonomous Prefecture, Xiangxi, Hunan, 416000, People's Republic of China.

Geophysical and Geochemical Survey Institute Of Hunan Province, 898 Wanjiali South Road, Changsha, Hunan, 410000, People's Republic of China.

出版信息

Environ Monit Assess. 2025 Jul 5;197(8):868. doi: 10.1007/s10661-025-14310-0.

Abstract

Precise source tracing and risk quantification of multi-source heavy metals (HMs) contamination in soil pose significant challenges for regional environmental management. This study proposed an innovative dynamic coupling model that combines a self-organizing map (SOM) and positive matrix factorization (PMF), overcoming the limitations of single models. The geo-accumulation index (I) and the initial ecological risk index (RI) were integrated with human health risks to form a comprehensive evaluation chain of "pollution source-exposure pathway-risk contribution." The results showed that the average concentrations of eight HMs in soil exceeded background levels, with Cd exhibiting the highest exceedance ratio (0.67 mg/kg, 4.17 × background value). Cd, Zn, and As are influenced by human activities, as evidenced by variation coefficients greater than 70%. The SOM-PMF model successfully identified five pollution sources and their respective contribution rates (contribution/main elements): agricultural sources (8.48%, As), traffic sources (30.24%, Pb, As, Cr), natural background sources (23.04%, Ni, Cu, Cr), industrial sources (18.34%, Cd, Pb, Zn), and smelting sources (19.91%, Mn). Ecological risk assessments have indicated that Cd represents the most significant environmental cumulative risk (  = 1.52) and potential ecological risk (   = 0.34). However, source-risk coupling analysis reveals that agricultural activities (47.3% of As) contribute 24% to the biological risk, with As replacing Cd as the priority element for control. Traffic sources are the primary contributors to health risks, with Pb and As being the main elements (with proportions of 65.18% and 45.52%, respectively), followed by agricultural sources primarily associated with As (47.3%). These sources contribute over 42% to both carcinogenic and non-carcinogenic risks. As was the major contributor to health risks in the study area, with carcinogenic and non-carcinogenic risks in children significantly higher than in adults (3.28 and 4.24 times, respectively). This study provides a scientific basis and technical support for the zonal management and collaborative control of multi-source soil HM pollution.

摘要

土壤中多源重金属污染的精确溯源及风险量化对区域环境管理构成重大挑战。本研究提出了一种创新的动态耦合模型,该模型将自组织映射(SOM)和正定矩阵因子分解(PMF)相结合,克服了单一模型的局限性。将地累积指数(I)和初始生态风险指数(RI)与人体健康风险相结合,形成了“污染源—暴露途径—风险贡献”的综合评价链。结果表明,土壤中8种重金属的平均浓度超过背景水平,其中Cd的超标率最高(0.67毫克/千克,为背景值的4.17倍)。Cd、Zn和As受人类活动影响,变异系数大于70%即为证。SOM-PMF模型成功识别出5个污染源及其各自的贡献率(贡献/主要元素):农业源(8.48%,As)、交通源(30.24%,Pb、As、Cr)、自然背景源(23.04%,Ni、Cu、Cr)、工业源(18.34%,Cd、Pb、Zn)和冶炼源(19.91%,Mn)。生态风险评估表明,Cd代表最显著的环境累积风险(=1.52)和潜在生态风险(=0.34)。然而,源风险耦合分析表明,农业活动(As的47.3%)对生物风险的贡献率为24%,As取代Cd成为优先控制元素。交通源是健康风险的主要贡献者,Pb和As是主要元素(比例分别为65.18%和45.52%),其次是主要与As相关的农业源(47.3%)。这些源对致癌和非致癌风险的贡献率均超过42%。As是研究区域健康风险的主要贡献者,儿童的致癌和非致癌风险显著高于成人(分别为3.28倍和4.24倍)。本研究为多源土壤重金属污染的分区管理和协同控制提供了科学依据和技术支持。

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