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Spatial distribution of arsenic, uranium and vanadium in the volcanic-sedimentary aquifers of the Vicano–Cimino Volcanic District (Central Italy)

机译:Vicano-Cimino火山区(意大利中部)火山 - 沉积含水层中砷,铀和钒的空间分布

摘要

Arsenic concentrations were analysed for 328 water samples collected in the Vicano–Cimino Volcanic District(VCVD), an areawhere severe contamination of groundwater has become a serious problemfollowing the recentapplication of the EU Directive on the maximum allowable concentration level for As in drinking waters. Inaddition, uranium and vanadium concentrations were also analysed in light of the enhanced interest on theirenvironmental toxicity. Waters were collected from springs and wells fed by cold and shallow volcanic–sedimentaryaquifers, which locally represent the main drinking water source. Thermal springs (≤63 °C) relatedto an active hydrothermal reservoir and waters associated with a CO2-rich gas phase of deep provenance werealso analysed. The collected data showed that the As concentrations in the shallow aquifers varied in a widerange (0.05–300 μg/L) and were primarily controlled by water–rock interaction processes. High As concentrations(up to 300 μg/L) were measured in springs and wells discharging from the volcanic products, and about66% exceeded the limit of 10 μg/L for drinkingwaters,whereaswaters circulatingwithin the sedimentary formationsdisplayed much lower values (0.05–13 μg/L; ~4% exceeding the threshold limit). Thermal waters showedthe highest As concentrations (up to 610 μg/L) as the result of the enhanced solubility of As-rich volcanic rocksduring water–rock interaction processes at high temperatures. Where the local structural setting favoured therise of fluids from the deep hydrothermal reservoir and their interaction with the shallow volcanic aquifer, relativelyhigher concentrations were found. Moreover, well overexploitation likely caused the lateral inflow ofAs-rich waters towards not contaminated areas.Uraniumand vanadiumconcentrations ofwaters circulating in the volcanic rocks ranged from0.01 to 85 μg/L and0.05 to 62 μg/L, respectively. Less than 2% of analysed samples exceeded theWorld Health Organization's provisionalguidelines for U (30 μg/L), while none of them was above the Italian limit value of V in drinking water(120 μg/L). Lower U (0.07–22 μg/L and 0.02–13 μg/L, respectively) and V concentrations (0.05–24 μg/L and0.18–17 μg/L, respectively) were measured in the water samples from the sedimentary aquifer and thermalwaters. Local lithology appeared as the main factor affecting the U and V contents in the shallow aquifers, dueto the high concentrations of these two elements in the volcanic formations when compared to the sedimentaryunits. In addition, high U concentrations were found in correspondence with U mineralization occurring withinthe VCVD, fromwhich U is released in solution mainly through supergene oxidative alteration. Redox conditionsseem to play amajor role in controlling the concentrations of U and V inwaters. Oxidizing conditions characterizingthe cold waters favour the formation of soluble U- and V-species, whereas thermal waters under anoxicconditions are dominated by relatively insoluble species. Geostatistical techniques were used to draw contourmaps by using variogram models and kriging estimation aimed to define the areas of potential health risk characterizedby As, U and V-rich waters, thus providing a useful tool for water management in a naturally contaminatedarea to local Authorities.
机译:在维卡诺–西米诺火山区(VCVD)采集的328个水样中,分析了砷的浓度,该地区是继最近针对饮用水中砷的最大允许浓度水平应用欧盟指令之后,地下水严重污染的一个严重问题。此外,还根据人们对铀和钒对环境毒性的关注,对铀和钒的浓度进行了分析。水是从泉水和泉水中收集的,这些泉水和水是由浅层和浅层火山沉积水层供给的,这些水层是当地的主要饮用水来源。还分析了与活跃的热液储层有关的温泉(≤63°C)和与具有深渊源的富含二氧化碳的气相有关的水。收集的数据表明,浅层含水层中的As浓度在较大范围内(0.05-300μg/ L)变化,并且主要受水-岩相互作用过程的控制。在从火山产品排出的泉水和井中测得的高砷浓度(高达300μg/ L),约有66%的浓度超过了饮用水的10μg/ L的限值,而在沉积物中循环的水显示出低得多的值(0.05–13μg / L;超出阈值限制约4%)。温泉水在高温水与岩石相互作用过程中,富含As的火山岩溶解度提高,结果显示As浓度最高(高达610μg/ L)。在当地的结构环境有利于深部热液储层的流体上升及其与浅层火山含水层的相互作用的地方,发现了相对较高的浓度。此外,过度开采可能导致富砷水横向流入未受污染的区域。火山岩中循环水的铀和钒浓度分别为0.01至85μg/ L和0.05至62μg/ L。少于2%的分析样品超过了世界卫生组织关于U的暂行准则(30μg/ L),但没有一个超过意大利饮用水中V的极限值(120μg/ L)。在沉积含水层的水样中测出了较低的U(分别为0.07–22μg/ L和0.02–13μg/ L)和V浓度(分别为0.05–24μg/ L和0.18–17μg/ L)。和温泉水。局部岩性似乎是影响浅层含水层中U和V含量的主要因素,因为与沉积单元相比,火山岩层中这两种元素的浓度很高。此外,发现高浓度的铀与VCVD中发生的铀矿化相对应,铀主要通过超基因氧化改变从铀中释放出来。氧化还原条件似乎在控制水中U和V的浓度中起主要作用。表征冷水的氧化条件有利于可溶性U和V物种的形成,而缺氧条件下的热水主要由相对不溶的物种主导。地统计学技术通过使用变异函数模型和kriging估计来绘制等高线图,旨在定义富含As,U和V的水的潜在健康风险区域,从而为地方当局提供了在自然污染区域进行水管理的有用工具。

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