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Mitigation and Remedy of Groundwater Arsenic Menace in India

Mitigation and Remedy of Groundwater Arsenic Menace in India

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<strong>Mitigation</strong> <strong>and</strong> <strong>Remedy</strong> <strong>of</strong> <strong>Groundwater</strong> <strong>Arsenic</strong> <strong>Menace</strong> <strong>in</strong> <strong>India</strong> : A Vision Documentarsenic-rich m<strong>in</strong>e dra<strong>in</strong>age <strong>and</strong> the subsequent decrease <strong>of</strong> arsenic content, down gradient fromwhere discharges crossed limestone outcrops, <strong>in</strong>dicated that limestone is a possible arsenicremoval medium (Davis et al., 1999). Surface area <strong>of</strong> the limestone is a key parameter,controll<strong>in</strong>g the efficiency <strong>of</strong> the process. The smaller gra<strong>in</strong> sizes have provided a greater surfacearea per unit weight. Thus, better arsenic removal has been demonstrated.The areas <strong>of</strong> major concern, regard<strong>in</strong>g feasibility <strong>of</strong> a limestone-based arsenic removalprocess, are ionic <strong>in</strong>terference, the stability <strong>and</strong> disposal <strong>of</strong> arsenic-saturated limestone, <strong>and</strong> therate at which the process can treat water. Each <strong>of</strong> these concerns should be addressed. Theprocess should be studied at the molecular level, regard<strong>in</strong>g what compound is formed on orwith<strong>in</strong> the limestone. A better underst<strong>and</strong><strong>in</strong>g <strong>of</strong> the entire process <strong>and</strong> the composition <strong>of</strong> thearsenic-rich limestone waste product would likely result from such a study. Perhaps a material,other than limestone, needs to be added to the process to enhance waste product stability. Basedon previous research, iron oxide seems an appropriate choice. Other lime stones should betested. A rock unit can conta<strong>in</strong> various constituents <strong>and</strong> still qualify for classification aslimestone. One <strong>of</strong> these m<strong>in</strong>or constituents could greatly enhance the process. Various othernatural waters should be used <strong>in</strong> upcom<strong>in</strong>g work with a batch reactor. Chemical analyses <strong>of</strong>these natural waters should be done <strong>in</strong> an attempt to identify as to which ions preferentially<strong>in</strong>terfere. Column experiments, us<strong>in</strong>g a constant flow rate, are needed. Underst<strong>and</strong><strong>in</strong>g the flowmechanics <strong>of</strong> the process will be essential to the development <strong>of</strong> a prototype.A prototype cartridge must be designed. Experimental data regard<strong>in</strong>g mass adsorptionratios <strong>and</strong> necessary residence times, <strong>in</strong>dicat<strong>in</strong>g an appropriate cartridge size <strong>and</strong> flow rate,would assist <strong>in</strong> the design <strong>of</strong> a prototype. The <strong>in</strong>tent <strong>of</strong> any design should be to maximize theefficiency <strong>of</strong> the limestone-based arsenic removal process, with regard to both limestone mass<strong>and</strong> water volume or flow rate. This assumes the use <strong>of</strong> 58 smallest feasible limestone gra<strong>in</strong>sizes. Cost <strong>and</strong> availability factors could affect that assumption. Initial experimental work hasbeen successful <strong>in</strong> demonstrat<strong>in</strong>g the use <strong>of</strong> limestone to reduce the arsenic concentrations <strong>of</strong> aprepared st<strong>and</strong>ard solution. Prototype design <strong>and</strong> arsenic-rich limestone disposal must be addressed,before the ultimate feasibility <strong>of</strong> apply<strong>in</strong>g limestone-based arsenic removal systems,can be determ<strong>in</strong>ed. Further work should focus on exp<strong>and</strong><strong>in</strong>g the applications <strong>of</strong> the process,namely, to <strong>in</strong>clude remov<strong>in</strong>g arsenic from natural waters as well as st<strong>and</strong>ard solutions.6.3.3 Remediation <strong>of</strong> <strong>Arsenic</strong> contam<strong>in</strong>ated Soils by <strong>in</strong> situ Chemical FixationSubsurface soils, from several <strong>in</strong>dustrial facilities, are contam<strong>in</strong>ated with arsenicbecause <strong>of</strong> the application <strong>of</strong> arsenic conta<strong>in</strong><strong>in</strong>g herbicide. Low cost <strong>in</strong> situ chemical fixationtreatment is designed to react with contam<strong>in</strong>ated soils directly, aga<strong>in</strong>st the treatment solutions tocause the formation <strong>of</strong> <strong>in</strong>soluble arsenic-bear<strong>in</strong>g phases, <strong>and</strong> thereby, decreases theenvironmental leachability <strong>of</strong> arsenic (Xang, Li et al). Comb<strong>in</strong>ations <strong>of</strong> ferrous sulfate, potassiumpermanganate <strong>and</strong> calcium carbonate are used as major reagents for the chemical fixationNIH & CGWB 117

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