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首页> 外文期刊>Ecological engineering: The Journal of Ecotechnology >Potential risk assessment of heavy metals in sediments during the denitrification process enhanced by calcium nitrate addition: Effect of AVS residual
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Potential risk assessment of heavy metals in sediments during the denitrification process enhanced by calcium nitrate addition: Effect of AVS residual

机译:硝酸钙添加反硝化过程中沉积物中重金属的潜在风险评估:AVS残留的影响

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摘要

Calcium nitrate addition has been proved to be a effective technology for sediment odor control, however, when sulfide was oxidized, metals those combined to sulfide might potentially threatened the aquatic ecosystem. In this work, for the purpose of assessing the effect of acid volatile sulfide (AVS) residual on ecological risk of heavy metals (Cu, Cd, Pb and Zn) in anoxic sediments during the denitrification, limited calcium nitrate (20 g/kgdw) was added into sediments in microcosm systems, and then was exhausted within two weeks, along with 95.0% AVS removed. During the treatment, simultaneously extracted metal (SEM) to AVS ratio increased with sulfide removal, but remained lower than 1 because of the residual of AVS. Furthermore, geoaccumulation index (I-geo,), sediment quality guidelines (SQGs) and risk assessment code (RAC) all indicated that the risk level of all metals in treated sediments showed no significant change compared to that in initial sediments. It suggested that certain content of AVS residual could keep ecological risk of heavy metals at a low level during the treatment with calcium nitrate addition. However, limitations of each assessment index were observed as well. I-geo and SQGs were found to be unsuitable for temporal dynamic evaluation, but useful for identifying which metal got higher pollution level and risk level, and thus deserved more concerns. In addition, RAC was appropriate for Cu assessment rather than Zn, Cd and Pb evaluation, while AVS-SEM method was suitable for Zn, Cd and Pb evaluation instead of Cu assessment. Thus, all these indexes should be taken into account as a whole when used. (C) 2015 Elsevier B.V. All rights reserved.
机译:硝酸钙的添加已被证明是控制沉积物气味的有效技术,但是,当硫化物被氧化时,与硫化物结合的金属可能会威胁水生生态系统。在这项工作中,为了评估酸性挥发性硫化物(AVS)残留物对反硝化过程中缺氧沉积物中重金属(Cu,Cd,Pb和Zn)的生态风险的影响,限量硝酸钙(20 g / kgdw)将其添加到微观系统的沉积物中,然后在两周内耗尽,并去除了95.0%的AVS。在处理过程中,同时萃取的金属(SEM)与AVS的比率随着硫化物的去除而增加,但由于AVS的残留而保持低于1。此外,地质累积指数(I-geo),沉积物质量准则(SQGs)和风险评估代码(RAC)均表明,与初始沉积物相比,处理过的沉积物中所有金属的风险水平均未显示出显着变化。这表明在添加硝酸钙的过程中,一定量的AVS残留物可以将重金属的生态风险保持在较低水平。但是,也观察到每个评估指标的局限性。发现I-geo和SQG不适合进行时间动态评估,但对于识别哪种金属的污染水平和风险水平较高有用,因此值得更多关注。另外,RAC适合于铜评估,而不适合于Zn,Cd和Pb评估,而AVS-SEM方法适合于锌,Cd和Pb评估,而不适合Cu评估。因此,在使用时应将所有这些索引作为一个整体考虑。 (C)2015 Elsevier B.V.保留所有权利。

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