用于评价人工入渗设施中重金属迁移率的重金属滞留指数(HMRI)的建立与验证

Manish Kumar , Hiroaki Furumai
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引用次数: 0

摘要

在这项研究中,基于实验室批量顺序提取和同位素稀释实验,首次确定了控制金属迁移率的最重要参数,这些实验使用了三种类型的样本,即表层土壤、下层土壤(深度>;1.0m)和在东京收集的浸润沉积物(n=3)。首先将选定的参数进行归一化步骤,将每个参数转换为0-100%的比例,然后分配反映每个参数对金属保持性能重要性的相对权重因子。然后,重金属保留指数(HMRI)将不同的参数组合成一个唯一的数字(指数),以便于比较。通过这种方式,以HMRI的形式获得归一化因子的层次级别,以做出决策。本研究中评估的性质有三种类型:i)经典的物理化学性质,即粘土、有机物、Fe-Mn氧化物、硅酸盐和CEC的含量,因此随特定样品而变化;ii)每种金属的具体变量,如同位素可交换性(%E值)、吸附系数(Kd)和可交换分数,其随每种金属类型(即Cu、Zn和Pb)而变化;以及iii)用于开发HMRI的综合性质(样品特异性和金属特异性两者)。最后,将所有这些结果与在实验室中使用公路道路灰尘和去离子水(液固比=25L/kg)制备的人工道路径流(ARR)连续浸出10天后获得的柱状结果进行比较。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Development and validation of heavy metal retention index (HMRI) for the evaluation of heavy metal mobility in artificial infiltration facilities

In this study, the most important parameters governing metal mobility were first identified based on laboratory batch sequential extraction and isotope dilution experiments with three types of samples, i.e., surface soil, underlying soil (depth > 1.0 m) and soakaway sediment collected at Tokyo (n = 3). The selected parameters were first brought to normalization step, where each parameter was transformed into a 0–100 % scale, followed by assigning relative weight factors reflecting the importance of each parameter for metal retention property. Heavy Metal Retention Index (HMRI) then combined the different parameters in a unique number (index) to facilitate the comparison. In this way, hierarchical levels of normalized factors were obtained in the form of HMRI to make the decision. Properties that were evaluated in this study were of three types: i) classical physicochemical properties, i.e., the content of clay, organic, Fe-Mn oxide, silicates and CEC and thus varied with a particular sample; ii) specific variables for each metal like isotopic exchangeability (% E-value), sorption coefficient (Kd) and exchangeable fraction which varies with each metal type viz. Cu, Zn and Pb; and iii) integrated properties (both sample-specific and metal-specific properties) using which HMRI were developed. Finally, all these results were compared with column results obtained after 10 days of continuous leaching with artificial road runoff (ARR), prepared in the laboratory using highway road dust and deionized water (liquid/solid ratio = 25 L/kg).

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