Barregard Lars, Horvat Milena, Mazzolai Barbara, Sällsten Gerd, Gibicar Darija, Fajon Vesna, Dibona Sergio, Munthe John, Wängberg Ingvar, Haeger Eugensson Marie
Department of Occupational and Environmental Medicine, Sahlgrenska University Hospital and Academy, Goteborg University, Goteborg, Sweden.
Sci Total Environ. 2006 Sep 1;368(1):326-34. doi: 10.1016/j.scitotenv.2005.08.048. Epub 2005 Oct 13.
As part of the European Mercury Emissions from Chlor Alkali Plants (EMECAP) project, we tested the hypothesis that contamination of ambient air with mercury around chlor alkali plants using mercury cells would increase the internal dose of mercury in people living close to the plants. Mercury in urine (U-Hg) was determined in 225 individuals living near a Swedish or an Italian chlor alkali plant, and in 256 age- and sex-matched individuals from two reference areas. Other factors possibly affecting mercury exposure were examined. Emissions and concentrations of total gaseous mercury (TGM) around the plants were measured and modeled. No increase in U-Hg could be demonstrated in the populations living close to the plants. This was the case also when the comparison was restricted to subjects with no dental amalgam and low fish consumption. The emissions of mercury to air doubled the background level, but contributed only about 2 ng/m(3) to long-term averages in the residential areas. The median U-Hg levels in subjects with dental amalgam were 1.2 microg/g creatinine (micro/gC) in Italy and 0.6 microg/gC in Sweden. In individuals without dental amalgam, the medians were 0.9 microg/gC and 0.2 microg/gC, respectively. The number of amalgam fillings, as well as chewing, fish consumption, and female sex were associated with higher U-Hg. The difference between the countries is probably due to higher fish consumption in Italy, demethylated methyl mercury (MeHg) being partly excreted in urine. Post hoc power calculations showed that if the background mercury exposure is low it may be possible to demonstrate an increase in U-Hg of as little as about 10 ng/m(3) as a contribution to ambient mercury from a point source.
作为欧洲氯碱厂汞排放(EMECAP)项目的一部分,我们检验了这样一个假设:使用汞电池的氯碱厂周围环境空气中的汞污染会增加居住在工厂附近人群体内的汞摄入量。我们测定了225名居住在瑞典或意大利氯碱厂附近的个体以及256名来自两个对照区域、年龄和性别匹配的个体的尿汞(U-Hg)含量。还研究了其他可能影响汞暴露的因素。测量并模拟了工厂周围总气态汞(TGM)的排放和浓度。未发现居住在工厂附近人群的U-Hg含量增加。即使将比较仅限于没有牙科汞合金填充物且鱼类消费量低的受试者,情况也是如此。汞向空气中的排放量使背景水平增加了一倍,但在居民区的长期平均水平中仅贡献了约2 ng/m³。有牙科汞合金填充物的受试者中,意大利的U-Hg中位数为1.2微克/克肌酐(μg/gC),瑞典为0.6 μg/gC。在没有牙科汞合金填充物的个体中,中位数分别为0.9 μg/gC和0.2 μg/gC。汞合金填充物的数量、咀嚼、鱼类消费和女性性别都与较高的U-Hg含量相关。两国之间的差异可能是由于意大利的鱼类消费量较高,脱甲基甲基汞(MeHg)部分通过尿液排出。事后功效计算表明,如果背景汞暴露水平较低,那么有可能证明作为点源对环境汞的贡献,U-Hg含量仅增加约10 ng/m³就能被检测到。