杨倩琪, 黄蕾, 布文博, 龚雨, 钟寰. 南京市人群膳食砷暴露健康风险研究[J]. 环境卫生学杂志, 2018, 8(3): 191-196. DOI: 10.13421/j.cnki.hjwsxzz.2018.03.006
    引用本文: 杨倩琪, 黄蕾, 布文博, 龚雨, 钟寰. 南京市人群膳食砷暴露健康风险研究[J]. 环境卫生学杂志, 2018, 8(3): 191-196. DOI: 10.13421/j.cnki.hjwsxzz.2018.03.006
    YANG Qianqi, HUANG Lei, BU Wenbo, GONG Yu, ZHONG Huan. The Risk of Arsenic Exposure via Dietary Fish and Rice in Nanjing[J]. Journal of Environmental Hygiene, 2018, 8(3): 191-196. DOI: 10.13421/j.cnki.hjwsxzz.2018.03.006
    Citation: YANG Qianqi, HUANG Lei, BU Wenbo, GONG Yu, ZHONG Huan. The Risk of Arsenic Exposure via Dietary Fish and Rice in Nanjing[J]. Journal of Environmental Hygiene, 2018, 8(3): 191-196. DOI: 10.13421/j.cnki.hjwsxzz.2018.03.006

    南京市人群膳食砷暴露健康风险研究

    The Risk of Arsenic Exposure via Dietary Fish and Rice in Nanjing

    • 摘要:
      目的 比较中国非污染地区典型城市消费者通过摄入鱼、米导致的膳食砷暴露风险。
      方法 在南京市进行问卷调查评估鱼和米的摄入率,同时在南京中心城区的市场收集大米和鱼类样本(常见海水鱼、淡水鱼品种)。将样品煮熟,然后通过电感耦合等离子体质谱法测定砷浓度并应用USEPA标准风险模型进行风险计算,通过蒙特卡罗模拟(MCS)进行不确定性分析。
      结果 显示南京市居民摄入鱼、米具有显著的非致癌风险(危害商/HQ:米和鱼平均分别为0.82、0.86,低于1)且致癌风险处于可接受范围内(终生癌症风险/ILCR:米和鱼的平均值为别为6.61E-05、7.50E-05,可接受范围:1.00E-06~1.00-E-04)。蒙特卡洛分析的结果表明米和鱼中的砷浓度以及它们的摄入率是其风险的主要控制因子。
      结论 上述结果表明摄入鱼、米对中国东南典型城市南京居民的砷暴露具有显著贡献。摄入鱼、米是两条膳食砷暴露的重要途径。

       

      Abstract:
      Objectives To investigate the risk of arsenic (As) exposure via fish and rice in the diet of a typical city in non-contaminated areas of China.
      Methods A questionnaire survey was conducted in Nanjing for assessing the consumption of fish and rice. Rice and fish samples (common seawater and freshwater species) were collected from markets and supermarkets in the central districts of Nanjing. The concentration of As in samples were detected after being cooked. A standard risk model parameterized with As concentration, consumption rate, and the body mass of consumer was used for risk calculation. Monte Carlo Simulation (MCS) was performed for sensitivity analysis.
      Results The result of risk calculation showed an elevated non-carcinogenic risks (hazard quotient/HQ:an average of 0.82 for rice and 0.86 for fish, all lower than 1.00), and carcinogenic risks were in the range of acceptable level (incremental lifetime cancer risk/ILCR:average 6.61E-05 for rice and 7.50E-05 for fish, the acceptable range:1.00E-06~1.00E-04). The result of MCS analysis indicated that the As level both in rice and fish, as well as the consumption rate of population were most important in controlling the risk of As exposure.
      Conclusions The consumption of rice and fish, the two major sources of dietary exposure to As in eastern and southern China, was important in controlling the health risk of As exposure. Our result provide a typical example in eastern and southern China, demonstrating that fish consumption together with rice consumption should be considered when assessing the risk of As via dietary exposure.

       

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