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超富集植物蜈蚣草中砷化学形态的EXAFS研究 总被引:6,自引:0,他引:6
采用同步辐射扩展X射线吸收精细结构(SR EXAFS)技术研究了超富集植物蜈蚣草(Pteris vittata L.)中As的化学形态及其在转运过程中的变化.结果表明,蜈蚣草中的As主要以As(Ⅲ)与O配位的形态存在.As(Ⅴ)被植物吸收后,很快转化为As(Ⅲ),其转化过程主要发生在根部.As(Ⅲ)向地上部转运的过程中价态基本不变.在植物的根部和部分叶柄中存在少量与As-GSH相似的As-S结合方式,但是在As含量最高的羽叶中基本上未发现这种结合方式.与需要提取和分离过程的化学方法相比,采用EXAFS方法研究植物中的砷形态不需经过预分离或化学预处理就可以直接测定植物样品中元素的化学形态,因此可以避免样品预处理过程对As形态的干扰,并获得可靠的砷化学形态方面的信息. 相似文献
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Inorganic arsenic in dietary staples (i.e., yams and rice) may have substantially contributed to exposure and adverse health effects observed in an endemic Taiwanese population historically exposed to arsenic in drinking water. Observations of this population were used by the U.S. Environmental Protection Agency to derive toxicity values that form the basis for arsenic risk assessment and various regulations in the United States. However, data were previously insufficient to accurately estimate dietary intake. Rice and yam samples collected in 1993 and 1995 from Taiwanese districts with endemic arsenic were analyzed for total arsenic and for inorganic and organic mono and dimethylarsenic. The acid digestion techniques used in the analyses are among the best to preserve organic arsenic in the test sample. Furthermore, concurrent analyses of the proportion of inorganic arsenic in split samples of rice and yams collected in the 1995 investigation were in good agreement, despite using a different digestion method. These data support a likely mean dietary intake of 50?µg/day with a range of 15 to 211?µg/day. Consideration of dietary intake may result in a downward revision of the assumed potency of ingested arsenic as reflected in EPA's toxicity values. 相似文献
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超富集植物蜈蚣草中砷化学形态的EXAFS研究 总被引:4,自引:0,他引:4
采用同步辐射扩展X射线吸收精细结构(SREXAFS)技术研究了超富集植物蜈蚣草(PterisvittataL.)中As的化学形态及其在转运过程中的变化。结果表明,蜈蚣草中的As主要以As(Ⅲ)与O配位的形态存在。As(V)被植物吸收后,很快转化为As(Ⅲ),其转化过程主要发生在根部。As(Ⅲ)向地上部转运的过程中价态基本不变。在植物的根部和部分叶柄中存在少量与As-GSH相似的As-S结合方式,但是在As含量最高的羽叶中基本上未发现这种结合方式。与需要提取和分离过程的化学方法相比,采用EXAFS方法研究植物中的砷形态不需经过预分离或化学预处理就可以直接测定植物样品中元素的化学形态,因此可以避免样品预处理过程对As形态的干扰,并获得可靠的砷化学形态方面的信息。 相似文献
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Total arsenic in urine is often the principal means for assessing chronic exposure to arsenic-contaminated drinking water. This approach ignores many components of the human diet, especially fish and seafood that contain arsenic at significant concentrations. The toxicity differences between the inorganic forms and the dietary forms suggest both should be evaluated when attempting to assess risk from arsenic exposure. Urine biomonitoring for 53 participants was used to confirm reduction in arsenic exposure resulting from well water remediation removing inorganic arsenic from drinking water. Initially, only total arsenic urine assays were performed, but spikes in total arsenic urine concentrations were determined to be diet related and demonstrated the need for analytical methods that differentiate the arsenic species. A secondary analysis was added that quantified inorganic-related arsenic in urine and the dietary forms related to fish and seafood by subtraction from total arsenic. Significant differences were found between the inorganic arsenic component and the total arsenic measured in their urine. On average, approximately 76% of total arsenic in urine was attributed to fish and other organo-arsenic dietary sources, implying a potential significant overestimate of exposure, and demonstrating the need for differentiation of the inorganic-related arsenic from dietary arsenic. 相似文献
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W. A. Maher 《Biological trace element research》1984,6(2):159-164
A review of the nature and accumulation of arsenic in marine organisms is presented. A study of the literature has revealed a lack of information about the mechanisms of uptake, molecular transformations, and biochemical associations of arsenic within organisms, and it remains unclear whether a few forms of arsenic are ubiquitous. The arsenic forms present in marine sediments and their role in the biogeochemical cycling of arsenic are also largely unknown. 相似文献
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