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垃圾焚烧厂的环境空气、飞灰和土壤二噁英水平研究及风险评价
引用本文:王宇珊,钟昌琴,刘成坚,陈晓燕,吴仕森,陈继鑫,杨文超,黄道建.垃圾焚烧厂的环境空气、飞灰和土壤二噁英水平研究及风险评价[J].华南师范大学学报(自然科学版),2020,52(5):49-56.
作者姓名:王宇珊  钟昌琴  刘成坚  陈晓燕  吴仕森  陈继鑫  杨文超  黄道建
作者单位:1.生态环境部华南环境科学研究所,广州 510655
基金项目:广东省科技计划;中央级公益性科研院所基本科研业务费专项
摘    要:为评价珠三角某垃圾焚烧厂内工人和周边村民的二噁英健康风险,采集并分析了该垃圾焚烧厂的厂内环境(空气和飞灰)邻近敏感点(邻近村落)环境(空气和土壤)的二噁英(PCDD/Fs)质量水平,运用美国环保署(USEPA)风险评价体系和蒙特卡洛模拟(Monte Carlo simulation)对厂内工人、邻近敏感点村民(成人、青少年和儿童)在呼吸吸入、皮肤接触和经口摄入等暴露途径的健康风险进行评估.结果表明:(1)该垃圾焚烧厂固化飞灰中的PCDD/Fs毒性当量(以I-TEQ计)范围为8.99~240.00 ng TEQ/kg,环境空气中的为0.03~0.20 pg TEQ/m3,邻近敏感点土壤中的为0.81~2.04 ng TEQ/kg. (2)飞灰、厂内环境空气和邻近敏感点环境空气的PCDD/Fs单体分布特征更加接近,土壤中PCDD/Fs单体分布稍有差别. (3)厂内工人和村民(成人、青少年和儿童)的致癌风险(CR)合计第95%值范围为4.55×10-7~6.04×10-6,为可接受风险范围(<10-5);非致癌风险(HI)合计第95%值范围为4.61×10-3~4.28×10-2,远低于1,非致癌风险极低;(4)厂内工人和成人村民的CR较高, 第95%值分别占风险安全值的60%和39%.厂内工人的CR从环境空气吸入(包括在厂内和敏感点)和飞灰意外经口摄入方式占比最高,分别达55.12%和38.43%;成人村民的CR中从环境空气吸入占主导(占97.79%).建议加强对环境空气二噁英监控和飞灰经口摄入的风险管控.

关 键 词:垃圾焚烧厂    二噁英    暴露途径    健康风险
收稿时间:2020-06-10

PCDD/Fs Concentration in Air,Fly Ash and Soil around a Municipal Solid Waste Incinerator and its Risk Assessment
Institution:1.South China Institute of Environmental Science, Ministry of Ecology and Environment, Guangzhou 510655, China2.Environment Monitoring Station of Guangzhou Development Zone, Guangzhou 510663, China3.Environment Monitoring Station of Yangchun, Yangjiang 529600, China
Abstract:The concentrations of polychlorinated dibenzo-p-dioxins and polychlorinated dibenzofurans (PCDD/Fs) in the air and fly ash in a municipal solid waste incinerator (MSWI) in the Pearl River Delta and in the air and soil at the nearest environment-sensitive spot (an adjacent village) were investigated to evaluate PCDD/Fs health risk to on-site workers and adjacent villagers. Human health risk evaluation manual from US Environmental Protection Agency (USEPA) and Monte Carlo simulation were used to evaluate the PCDD/Fs health risk to on-site workers and adjacent villagers (adults, teens and children) under inhalation, dermal and ingestion exposure. The results are as follows. First, the toxic equivalent concentration (I-TEQ) values of PCDD/Fs were 8.99~240.00 ng TEQ/kg in the fly ash after solidification, 0.03~0.20 pg TEQ/m3 in the air, 0.81~2.04 ng TEQ/kg in the soil of the environment-sensitive spot. Second, PCDD/Fs congener profiles in the fly ash, the air in MSWI and the air at the environment-sensitive spot were similar, while PCDD/Fs congener profiles in the soil samples showed a little difference. Third, the 95th percentile carcinogenic risk (CR) values for on-site workers and villagers (adults, teens and children) were 4.55×10-7~6.04×10-6, suggesting that the CR values were on an acceptable level (< 1×10-5); the 95th percentile non-carcinogenic risk values for the four groups of people were 4.61×10-3~4.28×10-2, much lower than the threshold values of 1, suggesting a quite low non-carcinogenic risk. Fourth, the 95th percentile CR for on-site workers and adult villagers were relatively high, accounting for 60% and 39% of the risk safety value respectively; inhalation of air (in the MSWI and at the environment-sensitive spot) and accidental ingestion of fly ash contributed most to CR to on-site workers, accounting for 55.12% and 38.43%, respectively; and inhalation of air was the largest contributor of CR to adult villagers, accounting for 97.79%. It is suggested to monitor PCDD/Fs concentrations in the air and controll risk of accidental ingestion of fly ash.
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