首页> 外文期刊>Journal of testing and evaluation >Sorptive Response of Chromium (Cr~(+6)) and Mercury (Hg~(+2)) From Aqueous Solutions Using Chemically Modified Soils
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Sorptive Response of Chromium (Cr~(+6)) and Mercury (Hg~(+2)) From Aqueous Solutions Using Chemically Modified Soils

机译:化学改性土壤对水溶液中铬(Cr〜(+6))和汞(Hg〜(+2))的吸附响应

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The presence of xenobiotic (human induced) chemicals from mining, refining and electroplating industries causes significant damage to the natural soil system, altering its physico-chemical geochemistry. Most of these chemicals contain metal pollutants that are non-biodegradable and the only way to contain or limit their movement is through sorption. In this study, the sorptive response of two most commonly found metal contaminants, hexavalent chromium (Cr~(+6)) and mercury (Hg~(+2)), were studied using two semi-arid soils from Saudi Arabia. To enhance their retention capacity, these soils were amended with lime. The response to sorption at varying initial contaminant concentrations, pH conditions, temperature levels, and dilution ratios was investigated. Relying on empirical models (Langmuir and Freundlich), the nature of sorption (monolayer or heterogeneous) was ascertained. Furthermore, kinetic models were employed to validate the type and nature of sorption occurring (whether pseudo first-order or second-order). It was found that the experimental results correlated well with the selected empirical models for both the Al-Ghat and Al-Qatif soils when amended with lime and attenuate Cr and Hg to satisfactory levels. The R~2 values were close to 1 for all the tested models. The order of sorption was Cr > Hg for heavy metals considered, and also for soils and soil mixtures considered Al-Qatif soil amended with 6 % lime > Al-Ghat soil with 6 % lime > Al-Qatif > Al-Ghat. Lime treated soils sorbed 69 % and 63 % more than the untreated soils for Cr and Hg, respectively.
机译:来自采矿,精炼和电镀行业的异源(人为)化学物质的存在对自然土壤系统造成了重大破坏,从而改变了其物理化学地球化学。这些化学物质中的大多数含有不可生物降解的金属污染物,抑制或限制其移动的唯一方法是通过吸附。在这项研究中,使用两种来自沙特阿拉伯的半干旱土壤研究了两种最常见的金属污染物,六价铬(Cr〜(+6))和汞(Hg〜(+2))的吸附响应。为了提高其保留能力,这些土壤用石灰进行了改良。研究了在不同的初始污染物浓度,pH条件,温度水平和稀释比下对吸附的响应。依靠经验模型(Langmuir和Freundlich),确定了吸附性质(单层或非均质)。此外,动力学模型被用来验证发生吸附的类型和性质(伪一级或二级)。结果发现,实验结果与所选用的Al-Ghat和Al-Qatif土的经验模型很好地相关,当用石灰修正时,Cr和Hg衰减到令人满意的水平。对于所有测试模型,R〜2值均接近于1。考虑到重金属的吸附顺序为Cr> Hg,考虑到土壤和土壤混合物的吸附,Al-Qatif土壤用6%石灰改性> Al-Ghat土壤用6%石灰> Al-Qatif> Al-Ghat。石灰处理过的土壤中铬和汞的吸附量分别比未处理过的土壤高69%和63%。

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