Department of Sciences, Pandit Deendayal Petroleum University, Raisan, Gandhinagar, Gujarat, 382007, India.
Physical Research Laboratory, Geosciences Division, Ahmedabad, India.
Environ Geochem Health. 2021 Oct;43(10):4043-4059. doi: 10.1007/s10653-021-00894-2. Epub 2021 Mar 26.
Fluoride contamination in groundwaters of a rural region in semi-arid Western India has been studied using combination of geochemical-and-isotopic techniques, in conjunction with Health Quotient assessment approach. The objective of this study is to determine the sources and controls on fluoride content and to evaluate probabilistic non-carcinogenic risk associated with its long-term consumption. F ranges from 0.3 to 12 mg L, shows high spatial variability, and ~ 35% of the samples have F > 1.5 mg L (WHO maximum limit for drinking). Two sources are identified: high F results from water-rock interaction of F-bearing minerals in granites and gneisses, while phosphate fertilizers can contribute up to ~ 0.46 mg L of groundwater F that can be significant for low F samples. High F samples are characterized by high pH, Na and alkalinity, and low Ca. Calcite precipitation drives the solubility of F-bearing minerals. Kinetic fractionation of water isotopes (O and H) demonstrates that evaporation plays role in enriching groundwater F. Non-carcinogenic risk, estimated by Hazard Quotient ([Formula: see text]), ranges from 0.13-5.72 to 0.26-11.86 for adult and children, respectively. Conservative estimate shows that ~ 0.467 million of adults and~0.073 million of children in four sub-districts are under the risk of fluorosis-while the residents of other five sub-districts remain safe from it. Finally, we suggest stakeholders to install F treatment plants to ensure the health safety of local residents in the high-risk zones, create awareness in farmers for optimum use of fertilizers, and promote rainwater harvesting, for better management of groundwater resources and quality in the region.
氟化物污染在半干旱印度西部农村地区的地下水已经研究了使用地球化学和同位素技术的组合,结合健康商评估方法。这项研究的目的是确定氟含量的来源和控制,并评估与其长期消费相关的概率非致癌风险。氟化物浓度范围为 0.3 至 12 毫克/升,显示出高度的空间变异性,约 35%的样本氟化物浓度大于 1.5 毫克/升(世界卫生组织饮用水最大限值)。确定了两个来源:高氟是由于氟化物矿物与花岗岩和片麻岩的水岩相互作用所致,而磷酸盐肥料可使地下水氟化物增加高达 0.46 毫克/升,这对低氟样本可能很重要。高氟样本的特点是 pH 值、Na 和碱度高,Ca 低。方解石沉淀驱动含氟矿物的溶解度。水同位素(O 和 H)的动力学分馏表明,蒸发在富集中起着作用地下水氟化物。非致癌风险,通过危害商 ([Formula: see text]) 估计,成人分别为 0.13-5.72 至 0.26-11.86,儿童分别为 0.13-5.72 至 0.26-11.86。保守估计表明,在四个分区中,约有 0.467 万成年人和 0.073 万儿童面临氟中毒风险,而其他五个分区的居民则没有这种风险。最后,我们建议利益相关者在高风险地区安装氟化物处理厂,以确保当地居民的健康安全,提高农民对肥料最佳使用的认识,并促进雨水收集,以更好地管理该地区的地下水资源和质量。