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雨水生物滞留中金属形态分析:去除颗粒态、胶体态和真正溶解态金属。

Metal speciation in stormwater bioretention: Removal of particulate, colloidal and truly dissolved metals.

机构信息

Urban Water Engineering, Luleå University of Technology, Luleå, Sweden.

出版信息

Sci Total Environ. 2020 Jul 1;724:138121. doi: 10.1016/j.scitotenv.2020.138121. Epub 2020 Mar 21.

Abstract

For comprehensive estimation of the metal treatment efficiency of bioretention systems, information on metal speciation in the stormwater and the effluent is needed. However, so far, most bioretention studies only considered total metal concentrations. Despite their environmental importance, dissolved metals (defined as fractions < 0.45 μm) have only been evaluated in few studies. This study represents the first bioretention study to subdivide the <0.45 μm fraction further by filtration through a 3 kDa ultrafilter (corresponding to appr. 2-3 nm), thus enabling distinction between particulate, colloidal and truly dissolved metals. Higher bioavailability of the truly dissolved fraction has been indicated by previous research, underlining the importance of this study. Since vegetation and salt in stormwater both may be explanatory variables for metal fractionation, these have been added as factors in the utilized full factorial pilot-scale column experiment. While total metal removal was often >95%, detailed fractionation revealed that Cu and (when no salt was added) Zn removal in the <0.45 μm and <3 kDa fractions was significantly lower. Further, mean concentrations of Cu and (in one treatment) Cd in the <0.45 μm effluent fraction did not meet Swedish receiving water quality guidelines. By calculating the particulate, colloidal and truly dissolved fractions, it was shown that bioretention systems affect metal speciation of Cu and Zn. Colloidal and truly dissolved fractions were mostly prevalent in the effluent rather than the influent. Salt affected metal removal mostly negatively. Fractionation was affected by salt mainly in the influent where it increased the concentrations of Cd and Zn in the truly dissolved fraction (no effects on Cu and Pb fractions). In the effluent, Cu and Zn were only slightly affected by salt. Vegetation had mostly no significant effects on metal removal and fractionation. Further integration of detailed metal fractionation into sampling routines in bioretention research is recommended.

摘要

为了全面评估生物滞留系统的金属处理效率,需要了解雨水和出水的金属形态信息。然而,到目前为止,大多数生物滞留研究仅考虑了金属总量。尽管它们具有重要的环境意义,但溶解金属(定义为<0.45μm 部分)在少数研究中仅被评估过。本研究代表了第一个通过 3kDa 超滤(约 2-3nm)进一步细分<0.45μm 部分的生物滞留研究,从而能够区分颗粒状、胶体状和真正溶解的金属。以前的研究表明,真正溶解部分的生物利用度更高,强调了这项研究的重要性。由于雨水的植被和盐分都可能是金属分馏的解释变量,因此这些因素被添加为利用全因子中试柱实验的因子。虽然总金属去除率通常>95%,但详细的分馏表明,Cu 和(当没有盐添加时)Zn 在<0.45μm 和<3kDa 部分的去除率显著较低。此外,Cu 和(在一种处理中)Cd 的<0.45μm 出水部分的平均浓度不符合瑞典受纳水体质量指南。通过计算颗粒状、胶体状和真正溶解的部分,表明生物滞留系统会影响 Cu 和 Zn 的金属形态。胶体和真正溶解的部分主要存在于出水中,而不是在进水口。盐分主要对金属去除产生负面影响。分馏主要受到盐分的影响,在进水口增加了 Cd 和 Zn 在真正溶解部分的浓度(对 Cu 和 Pb 部分没有影响)。在出水中,盐分对 Cu 和 Zn 的影响较小。植被对金属去除和分馏的影响大多不显著。建议进一步将详细的金属分馏纳入生物滞留研究的采样程序中。

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