南京林业大学学报(自然科学版) ›› 2025, Vol. 49 ›› Issue (2): 203-211.doi: 10.12302/j.issn.1000-2006.202308049
蓝洋1(), 李岩1,*(
), 董珍1, 冯笛珂1, 刘科2, 贾振毅3, 范庆斌4, 李柠1, 程新宇1, 温佳乐1, 黄浩然1, 叶子1, 虞叶1
收稿日期:
2023-08-25
接受日期:
2023-12-18
出版日期:
2025-03-30
发布日期:
2025-03-28
通讯作者:
*李岩(lyle@njfu.edu.cn),副教授。作者简介:
蓝洋(lany@njfu.edu.cn)。
基金资助:
LAN Yang1(), LI Yan1,*(
), DONG Zhen1, FENG Dike1, LIU Ke2, JIA Zhenyi3, FAN Qingbin4, LI Ning1, CHENG Xinyu1, WEN Jiale1, HUANG Haoran1, YE Zi1, YU Ye1
Received:
2023-08-25
Accepted:
2023-12-18
Online:
2025-03-30
Published:
2025-03-28
摘要:
【目的】通过对南京市地下车库中地表尘重金属的来源解析和生态风险及人体健康风险的评估,提高公众对地下车库风险危害的认知。【方法】采集了南京市不同区域内地下车库中地表尘作为样本进行重金属检测,通过绝对因子分析-多元线性回归(APCS-MLR)受体模型进行源解析;生态风险方面运用地累积指数法、潜在生态风险指数法评估;运用人体健康风险评估模型进行人体健康风险评估。【结果】①南京市地下车库中地表尘重金属来源有4个因子,分别为燃料燃烧源、工业源、道路和工业降尘源、机动车排放源。②研究区Zn和Cu的平均地累积指数都达到了中至强度污染,潜在生态风险指数综合表现为较强风险。③对于人体健康来说,6种重金属的总非致癌风险对于儿童大于1,处于安全阈值之外;对于成人小于1,处于可控范围;而对于人体致癌风险来说,两种重金属元素Ni、Cr的值都大于相对安全标准的1×10-4。【结论】南京市地下车库中地表尘重金属无论对于生态还是人体健康都有负面影响,需要采取防治措施。
中图分类号:
蓝洋,李岩,董珍,等. 南京市地下车库地表尘重金属源解析及风险评估[J]. 南京林业大学学报(自然科学版), 2025, 49(2): 203-211.
LAN Yang, LI Yan, DONG Zhen, FENG Dike, LIU Ke, JIA Zhenyi, FAN Qingbin, LI Ning, CHENG Xinyu, WEN Jiale, HUANG Haoran, YE Zi, YU Ye. Analysis of heavy metal sources and risk assessment of surface dust in underground parking garages in Nanjing City[J].Journal of Nanjing Forestry University (Natural Science Edition), 2025, 49(2): 203-211.DOI: 10.12302/j.issn.1000-2006.202308049.
表1
健康风险评价模型的参数"
参数名称parameters name | 变量variable | 儿童children | 成年人adult | 文献source |
---|---|---|---|---|
暴露频率/(d·a-1) exposure frequency | IEF | 365 | 365 | [ |
暴露年限/a exposure duration | IED | 6 | 24 | [ |
受体体质量/kg body weight | IBW | 15.9 | 56.8 | [ |
摄入速率/(mg·d-1) ingestion rate | IIngR | 200 | 100 | [ |
呼吸速率/(m3·d-1) inhalation rate | IInhR | 7.5 | 14.5 | [ |
平均暴露时间/d average exposure time | IAT | 暴露年限×365 | 暴露年限×365 | [ |
颗粒物排放因子/(m3·kg-1) particle emission factor | IPEF | 1.36×109 | 1.36×109 | [ |
皮肤暴露面积/cm2 skin exposure area | ISA | 2 800 | 5 700 | [ |
皮肤黏着度/(mg·cm-2·d-1) soil adhesion rate | ISL | 0.20 | 0.07 | [ |
皮肤吸收因子absorption factor | IABS | 0.001 | 0.001 | [ |
表2
不同暴露途径的IRfD和ISF参考值"
元素 element | IRfD/(mg·kg-1·d-1) | ISF | ||||||
---|---|---|---|---|---|---|---|---|
经口摄入 Aing | 呼吸摄入 Ainh | 皮肤摄入 Aderm | 经口 摄入 Aing | 呼吸 摄入 Ainh | 皮肤 摄入 Aderm | |||
Cr | 3.00×10-3 | 2.86×10-5 | 6.00×10-5 | 0.5 | 42.0 | 2.0 | ||
Ni | 2.00×10-2 | 2.06×10-2 | 5.40×10-3 | 1.70 | 0.84 | 42.50 | ||
Cu | 4.00×10-2 | 4.00×10-2 | 1.20×10-2 | — | — | — | ||
Zn | 3.00×10-1 | 3.00×10-1 | 6.00×10-2 | — | — | — | ||
Cd | 1.00×10-3 | 1.00×10-3 | 1.00×10-5 | 6.1 | 6.3 | — | ||
Pb | 3.50×10-3 | 3.52×10-3 | 5.25×10-4 | — | — | 8.50×10-3 |
表3
重金属含量描述性统计"
元素 element | 平均值/ (mg·kg-1) mean | 最大值/ (mg·kg-1) max | 最小值/ (mg·kg-1) min | 变异 系数/% CV | 背景值/ (mg·kg-1) background value |
---|---|---|---|---|---|
Cr | 299.96 | 637.29 | 70.42 | 61.47 | 83.00 |
Ni | 178.45 | 522.43 | 31.87 | 86.51 | 40.00 |
Cu | 1 395.85 | 13 768.72 | 67.75 | 280.38 | 31.00 |
Zn | 1 337.14 | 7 026.53 | 189.88 | 137.88 | 79.00 |
Cd | 0.79 | 1.73 | 0.24 | 48.58 | 0.14 |
Pb | 153.36 | 584.78 | 38.18 | 108.27 | 23.00 |
表5
因子分析矩阵及主成分分析结果"
元素element | 因子(贡献率/%)factor(contribution rate) | |||
---|---|---|---|---|
1 | 2 | 3 | 4 | |
Cr | 0.935(78.49) | 0.242(12.39) | 0.091(5.37) | -0.102(3.75) |
Ni | 0.976(85.91) | 0.081(4.35) | -0.132(8.16) | -0.041(1.57) |
Cu | -0.096(14.51) | -0.104(9.59) | -0.107(11.24) | 0.984(64.67) |
Zn | 0.055(8.02) | 0.992(87.62) | 0.016(1.64) | -0.043(2.72) |
Cd | 0.527(44.54) | 0.803(41.53) | 0.125(7.39) | -0.178(6.54) |
Pb | -0.029(3.54) | 0.062(4.72) | 0.992(86.07) | -0.105(5.67) |
解释方差/% explained variance | 35.310 | 28.493 | 17.279 | 17.085 |
累积解释总方差/% cumulative explained variance | 35.310 | 63.803 | 81.082 | 98.167 |
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