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Evaluation of fluoride enrichment processes in groundwater of Chimakurthy granitic pluton complex in Prakasam District India

机译:印度Prakasam地区Chimakurthy花岗岩质岩体中地下水中氟的富集过程评估

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Hydrogeochemical evaluation of aquifers belonging to Chimakurthygranitic pluton complex reveals wide spatial and temporal variation in F- distribution. F- concentration in groundwaterof different aquifers varies from 0. 50 to 9.84 mg/l. Among three sampled episodes, the mean value of F- is high in July 2010 and 61% of samples have values above maximum permissible limit as per the Bureau of Indian Standards. In April 2008, 44% and in February 2009, 41% of samples were not fit for drinking purposes due to enrichment of F-. Northern half of the area is almost free from F- but south central part, which has witnessed igneous activity with mafic intrusive form the core area of F- mineralization. Cent percent testing of all the groundwater structures in fifteen villages show uneven distribution of F- even within limited terrain. F- show close positive correlation with pH (0.57), Na+ (0.68), HCO3- (0.61) and distinct negative correlation (-0.31) with Ca2+. The groundwater facies is of sodium bicarbonate chloride type, sodium magnesium bicarbonate type and calcium magnesium bicarbonate type. Among 23 analyzed trace elements, Zn is the most dominant (mean 3200 µmg/l). Trace elements concentrations do not exhibit any distinct control over F- contribution to groundwater. F- content in rock samples varies drastically from below detectable limit (BDL) to 492 ppm whereas in soil it varies between (BDL) and 612 ppm. F- concentration of rock-soil-groundwater does not synchronize depicting latter enrichment of F- into formation water. Ratios, indices and plots indicate multiple mechanisms were responsible in F- absorption into groundwater. Water-rock interactions, ion exchange followed by evapotranspiration have facilitated the F- mineralization of groundwater. Na+/Cl- ratio of 1in almost all the samples of three sampling sessions establish silicate weathering. Ca2+/Mg2+, Na+/Ca2+, Ca2+, Mg2+ and HCO3- ratios authenticate carbonate dissolution is responsible for alkali earths addition. Sodic rich and calcium depleted water together with balanced alkalinity has enabled F- enrichment. Presence of fluorite as accessory mineral apart from occurrence of F- in mineral lattice of biotite, hornblende, muscovite, and pyroxene were the potential sources of F- to the percolating pore waters. Though F- was abundantly available in solid solution the receptive hydrochemical character of solute was governing the F- adsorption which could be one of the strong reasons for uneven distribution of F- with in similar petrological setup.
机译:属于Chimakurthygranitic岩体复合体的含水层的水文地球化学评估显示F-分布的时空变化很大。不同含水层的地下水中F-浓度在<0. 50至9.84 mg / l之间变化。在三个采样事件中,F-的平均值在2010年7月较高,并且61%的采样值高于印度标准局的最大允许限值。由于F-的富集,2008年4月有44%,2009年2月有41%的样品不适合饮用。该地区的北半部几乎没有F-,而中南部则见证了火成岩活动,而镁铁质侵入体是F-矿化的核心区域。对15个村庄的所有地下水结构进行的百分比测试表明,即使在有限的地形内,F-的分布也不均匀。 F-与pH(0.57),Na +(0.68),HCO3-(0.61)密切相关,与Ca2 +呈明显负相关(-0.31)。地下水相为碳酸氢钠氯化物型,碳酸氢钠镁型和碳酸氢钙镁型。在分析的23种微量元素中,锌是最主要的(平均3200 µmg / l)。微量元素的浓度对F对地下水的贡献没有表现出任何明显的控制作用。岩石样品中的F含量从低于可检测极限(BDL)到492 ppm急剧变化,而在土壤中,其F-含量在(BDL)和612 ppm之间变化。岩石-土壤-地下水中的F-浓度不同步,这说明后来F-富集到地层水中。比率,指数和曲线表明,多种机制是导致地下水吸收F的原因。水-岩相互作用,离子交换和蒸散作用促进了地下水的F-矿化作用。在三个采样阶段的几乎所有样品中,Na + / Cl-比率均> 1,可建立硅酸盐风化作用。 Ca2 + / Mg2 +,Na + / Ca2 +,Ca2 +,Mg2 +和HCO3-的比例可证明碳酸盐的溶解是碱土添加的原因。富含苏打水和贫钙的水以及均衡的碱度使F富集。除了在黑云母,角闪石,白云母和辉石的矿物晶格中出现F-以外,萤石还作为辅助矿物存在,是渗滤孔隙水中F-的潜在来源。尽管固溶体中F-的含量很高,但溶质的接受水化学特性决定着F-的吸附,这可能是在相似的岩石构造中F-分布不均匀的重要原因之一。

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