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Mitigation and Remedy of Groundwater Arsenic Menace in India

Mitigation and Remedy of Groundwater Arsenic Menace in India

Mitigation and Remedy of Groundwater Arsenic Menace in India

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ABSTRACT<strong>Groundwater</strong> is a hidden <strong>and</strong> common pool resource. It is commonly believed thatgroundwater is omnipresent, <strong>and</strong> can be drawn on dem<strong>and</strong> <strong>in</strong> any quantity wherever <strong>and</strong>whenever required. This conception has given rise to <strong>in</strong>discrim<strong>in</strong>ate boom <strong>of</strong> groundwaterwithdrawal structures <strong>of</strong> various types namely, h<strong>and</strong>-pumps, bore-wells, tube-wells, etc. to meetever <strong>in</strong>creas<strong>in</strong>g dem<strong>and</strong>s <strong>in</strong> <strong>in</strong>dividual household, community <strong>and</strong> social sector for differentuses. Those, over the years, have triggered a number <strong>of</strong> <strong>in</strong>vad<strong>in</strong>g issues such as; depletion <strong>of</strong>groundwater level <strong>and</strong> deteriorat<strong>in</strong>g groundwater quality. As a consequence <strong>of</strong> which haveemerged a threat to scarcity <strong>of</strong> groundwater, failure <strong>of</strong> wells, severe health hazards, etc.Deterioration <strong>of</strong> groundwater quality is <strong>in</strong>creas<strong>in</strong>gly be<strong>in</strong>g recognized as the cause <strong>of</strong> waterscarcity <strong>in</strong> many areas.<strong>Groundwater</strong>, when it is <strong>in</strong> aquifer, possesses some fasc<strong>in</strong>at<strong>in</strong>g features, such as;usually it travels very slowly <strong>and</strong> hence has long residence time. The space-time availability <strong>of</strong>groundwater is characterized by the porosity <strong>and</strong> permeability <strong>of</strong> the geological formations <strong>of</strong>the aquifer. The geological nature <strong>of</strong> the soil also determ<strong>in</strong>es the chemical composition <strong>of</strong> thegroundwater. There is a misconception that the composition <strong>of</strong> groundwater does not changenaturally. However, a common cause <strong>of</strong> change <strong>in</strong> water quality is <strong>in</strong>teraction between aquifermaterial <strong>and</strong> the water flow<strong>in</strong>g through them. Factors that control the dissolved m<strong>in</strong>erals <strong>in</strong>groundwater <strong>in</strong>clude (i) the types <strong>of</strong> m<strong>in</strong>erals that make up the aquifer, (ii) the length <strong>of</strong> timethat the water is <strong>in</strong> contact with the m<strong>in</strong>erals, <strong>and</strong> (iii) the chemical state <strong>of</strong> the groundwater.Different rocks have different m<strong>in</strong>erals <strong>and</strong> groundwater <strong>in</strong> contact with those materials willhave different compositions. The longer the contact time with m<strong>in</strong>erals, the grater the extent <strong>of</strong>its reaction with those m<strong>in</strong>erals <strong>and</strong> the higher will be the content <strong>of</strong> dissolved m<strong>in</strong>erals. Thechemical state <strong>of</strong> groundwater is generally def<strong>in</strong>ed <strong>in</strong> terms <strong>of</strong> three parameters: thetemperature, pH, <strong>and</strong> oxidation-reduction potential. These factors are <strong>of</strong>ten <strong>in</strong>fluenced bychemical reactions between the groundwater <strong>and</strong> aquifer materials <strong>and</strong> <strong>in</strong> turn control thechemical composition <strong>of</strong> groundwater. If the aquifer material processed the toxic elementsfrom weathered rocks, the changes <strong>in</strong> the chemical state <strong>of</strong> groundwater, which may be due todifferent water levels <strong>and</strong> annual recharge events, may trigger activation or dissolution <strong>of</strong> toxicelements <strong>in</strong> the groundwater.Occurrence <strong>of</strong> <strong>Arsenic</strong> <strong>in</strong> groundwater, <strong>in</strong> excess to the permissible limit <strong>of</strong> 50 µg/L <strong>in</strong>the Ganges-Brahmaputra fluvial pla<strong>in</strong>s <strong>in</strong> <strong>India</strong> cover<strong>in</strong>g seven states namely, West-Bengal,Jharkh<strong>and</strong>, Bihar, Uttar Pradesh <strong>in</strong> flood pla<strong>in</strong> <strong>of</strong> Ganga River; Assam <strong>and</strong> Manipur <strong>in</strong> floodpla<strong>in</strong> <strong>of</strong> Brahamaputra <strong>and</strong> Imphal rivers <strong>and</strong> Rajn<strong>and</strong>gaon village <strong>in</strong> Chhattisgarh state, is onesuch large scale groundwater quality disaster, described <strong>in</strong>ternationally as the World biggestnatural groundwater calamity to the mank<strong>in</strong>d after Bangladesh. These fluvial pla<strong>in</strong>s representHolocene aquifers <strong>of</strong> recent alluvial sediments <strong>and</strong> have the routes orig<strong>in</strong>ated from theHimalayan region. S<strong>in</strong>ce the groundwater arsenic contam<strong>in</strong>ation first surfaced <strong>in</strong> 1983 fromvi

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