高级检索
李继强, 陈锡永, 唐意佳, 赵磷石, 谢广宁, 邓俊兴, 丘义征. 环境镉污染及其对人群健康影响的研究状况分析[J]. 中国公共卫生, 2001, 17(3): 196-198. DOI: 10.11847/zgggws2001-17-03-02
引用本文: 李继强, 陈锡永, 唐意佳, 赵磷石, 谢广宁, 邓俊兴, 丘义征. 环境镉污染及其对人群健康影响的研究状况分析[J]. 中国公共卫生, 2001, 17(3): 196-198. DOI: 10.11847/zgggws2001-17-03-02
LI Ji-qing, . Environmental Cadmium Pollution and the Effect on Population Health[J]. Chinese Journal of Public Health, 2001, 17(3): 196-198. DOI: 10.11847/zgggws2001-17-03-02
Citation: LI Ji-qing, . Environmental Cadmium Pollution and the Effect on Population Health[J]. Chinese Journal of Public Health, 2001, 17(3): 196-198. DOI: 10.11847/zgggws2001-17-03-02

环境镉污染及其对人群健康影响的研究状况分析

Environmental Cadmium Pollution and the Effect on Population Health

  • 摘要: 目的比较某冶炼厂15年前后环境镉污染对人群健康影响的变化,并为该厂扩建投产后的污染变化评价提供依据.方法选取与上次调查相同的污染区和对照区,调查两区大米、蔬菜、饮水镉以及25岁以上妇女的尿中镉、β2M、NAG酶含量,并与上次资料比较.结果米镉(干重)、菜镉(湿重)、饮水镉、尿镉、尿β2M和尿NAG酶的几何均数,污染区分别为175mg/kg、0.27mg/kg、0.0008mg/L、13.34μg/g·cr、185.39μg/g·cr和5.80U/g·cr;对照区分别为0.46mg/kg、0.08mg/kg、0.001mg/L、2.27μg/g·cr、136.57μg/g·cr和4.06U/g·cr;其中米、菜、尿3项镉浓度,污染区比对照区高(P<0.01).尿镉、尿NAG酶、尿β2M及其总的异常率,污染区(37.63%、19.35%、18.28%和51.6%)高于对照区(7.23%、3.61%、7.23%和15.7%)(P=0.000~0.013);本次调查污染区的尿镉均值(23.80μg/L)和异常率(44.09%)约为1982年的(12.06μg/L和22.52%)2倍(P<0.01或P=0.022),并检出3例(32%)慢性早期健康危害者结论研究认为该污染区以及污染区人群仍在继续遭受某冶炼厂环境镉污染的影响,而且这种影响有不断累积加重的趋势.但该污染区镉尚未对当地人群构成慢性早期健康危害.

     

    Abstract: ObjectivesTo compare the change trend on health effect of environment Cd-pollution from certain smeltery past 15 years,and also to offer evaluation basis of Cd-pollution change some years later due to the factory extension,status of certain smeltery environmental Cd-pollution and its effect on health were investigated.MethodsSelecting the same areas as last investigation,the Cd concentration of rice,vegetable,drinking water and women's urinary Cd,beta(2)-microglobulin(β2-M),creatinine(cr),as well as N-acetyl-beta-D-glucosaminidase(NAG)activity in both polluted and control areas were detected and compared with last investigated information.ResultsThe geometric means of rice Cd(dry weight),vegetable Cd(wet weight),drinking water Cd,urinary Cd,β2-M and NAG are 1.75mg/kg,0.27mg/kg, 0.0008mg/L,13.34μg/g·cr,185.39μg/g·cr,5.80U/g·cr in the polluted area and 0.46mg/kg,0.08mg/kg,0.001mg/L,2.27μg/g·cr,136.57μg/g·cr,4.06U/g·cr in the control area respectively.Difference of the rice Cd,vegetable Cd and urinary Cd between polluted and control areas was statistically significant(P<0.01).The abnormity rate of the urinary Cdβ, 2-M,NAG and all of them are significantly higher in the polluted area(37.63%、19.35%、18.28% and 51.6% respectively)than in the control(7.23%、3.61%、7.23% and 15.7% respectively)(P=0.000~0.013).The mean value and the abnormity rate of urinary Cd in the polluted area in present investigation(23.80μg/L and 44.09% respectively)are twice in last investigation(12.06μg/L and 22.52% respectively)(P<=0.01.or.P=0.022).Three chronic early patients were diagnosed due to Cd exposure in the polluted area.ConclusionsThe results suggest that the polluted area as well as inhabitants living in polluted area have been affected continually by certain smeltery environmental cadmium pollution,also there is unceasing accumulating and aggravating trend of the affection.But Cd-pollution from certain smeltery has not caused adverse chronic early health effects on inhabitants living in polluted area according to the information of the present investigation.

     

/

返回文章
返回