首页> 外文期刊>Environmental toxicology and chemistry >DISTRIBUTION AND BIOMAGNIFICATION OF SELENIUM IN A RESTORED UPLAND GRASSLAND CONTAMINATED BY SELENIUM FROM AGRICULTURAL DRAIN WATER
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DISTRIBUTION AND BIOMAGNIFICATION OF SELENIUM IN A RESTORED UPLAND GRASSLAND CONTAMINATED BY SELENIUM FROM AGRICULTURAL DRAIN WATER

机译:农业污水中硒污染的旱地草地中硒的分布与生物放大作用。

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Kesterson Reservoir was a wetland contaminated with selenium (Se)-enriched agricultural drainage water. As part of the remediation of the selenium contamination, evaporation ponds at Kesterson were dried out and the selenium-contaminated wetlands were transformed into an upland grassland. The distribution of Se in both the soil and vegetation was monitored in these upland grasslands for 5 years. From May 1989 to September 1993 the distribution of soil Se in the sediment did not change significantly, and the soil Se inventory was not remobilized. Biomagnification of selenium in seven sites representing a gradient of soil Se concentrations was examined for three food-chain trophic levels. The pattern of Se bioaccumulation shows that there was a considerable increase from the water-extractable soil Se concentration (source) to the plant (producer) tissue Se concentration and from the grasshopper (primary consumer) tissue Se concentration to praying mantis (secondary consumer) tissue Se concentration. No consistent pattern of increase in Se concentration from the plant to the grasshopper level was apparent. The absolute values of Se bioaccumulation in the insects reflect the available Se concentrations in the soil of the habitat. This relationship indicates that the insects were not actively moving from their local habitat. This discovery suggests that, indeed, a Se biomagnification process did occur in this upland grassland ecosystem. In comparison with the previous state of Kesterson wetland, the upland grassland had Se bioaccumulations less than 10% of those found in the wetland. The upland grassland appears to provide a safer habitat than the wetland with respect to the elevated soil Se concentrations. However, some existing high soil Se concentration sites in the grassland may produce toxic levels of Se in the food chain. Additional research is needed to restore this deteriorated habitat and ensure the safety of wildlife and humans.
机译:凯斯特森水库(Kesterson Reservoir)是被富含硒(Se)的农业排水污染的湿地。作为硒污染修复的一部分,克斯特森(Kesterson)的蒸发池被弄干了,被硒污染的湿地变成了高地草原。在这些高地草原上监测了硒在土壤和植被中的分布,为期5年。 1989年5月至1993年9月,沉积物中土壤Se的分布没有明显变化,土壤Se的库存没有动员。对七个食物链营养水平的硒在七个代表土壤硒浓度梯度的部位进行了生物放大。硒的生物积累模式表明,从水可提取的土壤硒浓度(源)到植物(生产者)组织中的硒浓度以及从蚱((主要消费者)组织中的硒浓度到螳螂(次要消费者)都有相当大的增加。组织硒浓度。从植物到蚱hopper水平的硒浓度没有一致的增加模式。昆虫中硒生物富集的绝对值反映了栖息地土壤中可用的硒浓度。这种关系表明这些昆虫没有从其本地栖息地积极活动。这一发现表明,确实在这种山地草原生态系统中发生了硒生物放大过程。与以前的Kesterson湿地相比,高地草原的硒生物蓄积量少于湿地中的生物蓄积量的10%。就土壤硒含量升高而言,高地草原似乎比湿地提供了更安全的栖息地。但是,草原上一些现有的土壤富硒高位点可能在食物链中产生有毒的硒。需要进一步的研究来恢复这种恶化的栖息地,并确保野生动植物和人类的安全。

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