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首页> 外文期刊>Environmental earth sciences >The diagenetic geochemistry and contamination assessment of iron, cadmium, and lead in the sediments from the Shuangtaizi estuary, China
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The diagenetic geochemistry and contamination assessment of iron, cadmium, and lead in the sediments from the Shuangtaizi estuary, China

机译:双台子河口沉积物中铁,镉和铅的成岩地球化学特征及污染评价

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摘要

Sediment and pore water samples have been collected from the coastal tidal flat in the Shuangtaizi estuary, China, in order to investigate the geochemical behavior of iron, cadmium, and lead during diagenesis and to assess the degree of contamination. The calculated enrichment factors and geoaccumulation indices for separate elements show that anthropogenic activities have had no significant influence on the distribution of Fe and Pb in the study area, whereas the distribution of Cd has been closely influenced in this way. The high percentage of exchangeable Cd (average of 56.34%) suggests that Cd represents a potential hazard to benthic organisms in the estuary. The calculated diffusive fluxes of metals show that the most mobilized metal is Fe (9.22 mg m(-2) a(-1)), followed by Cd (0.54 mg m(-2) a(-1)) and Pb (0.42 mg m(-2) a(-1)). Low Fe2+ contents in surface pore water, alongside high chromium-reducible sulfur contents, and low acid-volatile sulfur, and elemental sulfur contents at 0-25 cm epth in sediments show that Fe2+ is formed by the reduction of Fe oxides and is transformed first to a solid phase of iron monosulfides (FeS) and eventually to pyrite (FeS2). The release of adsorbed Pb due to reductive dissolution of Fe/Mn oxides during early diagenesis could be a source of Pb2+ in pore water. From the relatively low total organic carbon contents measured in sediments (0.46-1.28%, with an average of 0.94%) and the vertical variation of Cd2+ in pore water, sulfide or Fe/Mn oxides (instead of organic matter) are presumed to exert a significant influence on carrying or releasing Cd by the sediments.
机译:为了调查成岩过程中铁,镉和铅的地球化学行为并评估其污染程度,从中国双台子河口的沿海滩涂中收集了沉积物和孔隙水样品。计算得出的单独元素的富集因子和地积累指数表明,人为活动对研究区铁和铅的分布没有显着影响,而镉的分布受到了这种方式的密切影响。高比例的可交换镉(平均56.34%)表明,镉对河口底栖生物具有潜在危害。计算得出的金属扩散通量表明,迁移最多的金属是Fe(9.22 mg m(-2)a(-1)),然后是Cd(0.54 mg m(-2)a(-1))和Pb(0.42毫克m(-2)a(-1))。地表孔隙水中的Fe2 +含量低,铬可还原的硫含量高,酸挥发性硫含量低,沉积物在0-25 cm epth处的元素硫含量低,表明Fe2 +是通过还原Fe氧化物而形成的,并先转化生成单硫化铁(FeS)的固相,最后生成黄铁矿(FeS2)。在早期成岩过程中,由于Fe / Mn氧化物的还原溶解而导致的吸附的Pb释放可能是孔隙水中Pb2 +的来源。根据在沉积物中测得的相对较低的总有机碳含量(0.46-1.28%,平均为0.94%)和孔隙水中Cd2 +的垂直变化,推测是硫化物或Fe / Mn氧化物(代替有机物)发挥了作用对沉积物携带或释放Cd的影响很大。

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