Feng Jiang , Lu Sun , Fang Yang , Liang Tang , Ke Cheng , Nengjian Zheng , Yang Li , Meng Hou
{"title":"钒钛铁矿尾矿库生态系统的水文地球化学砷模拟:中国攀西地区案例研究","authors":"Feng Jiang , Lu Sun , Fang Yang , Liang Tang , Ke Cheng , Nengjian Zheng , Yang Li , Meng Hou","doi":"10.1016/j.oreoa.2024.100053","DOIUrl":null,"url":null,"abstract":"<div><p>The V-Ti-Fe mine tailings waste releases high concentrations of aquatic arsenic (As) ions to downstream ecosystems. The hydrogeochemical As simulation facilitates the prediction of toxicity (or redox state) and devising control strategies to mitigate the negative impacts. Therefore, this study utilizes the Wanniangou tailings pond (a V-Ti-Fe mine tailings reservoir) in the Panxi region, Sichuan province, China, as a case study to elucidate the As hydrogeochemical behaviour under varying pH and redox potential (Eh) conditions. Our study reveals that (1) the water-oxygen exchange and Mn are important to regulating the redox conditions in the filtrates. The Eh determines the valence states of As, which vary from reduced states to oxidized states during the runoff from the tailings pond to downstream (Rehe River). The flow of wastewater in Rehe River minimizes both the As toxicity and concentration, eventually improving water safety. (2) In a reducing environment, hematite exhibits a limited capacity for As(III) adsorption. In the case of oxidation conditions, goethite mainly adsorbed As(V), with an elevated adsorption capacity. Meanwhile, Fe-minerals remain relatively stable under varying redox and weakly acidic conditions. Consequently, targeted engineering interventions can achieve two crucial outcomes: (1) Minimize the acidity of the mine environment to retard the release of heavy metals from the tailings waste. (2) Prolonging the residence time of wastewater in Rehe River to promote the transition from a reducing state to an oxidizing state, thereby synergistically mitigating As toxicity.</p></div>","PeriodicalId":100993,"journal":{"name":"Ore and Energy Resource Geology","volume":"17 ","pages":"Article 100053"},"PeriodicalIF":0.0000,"publicationDate":"2024-05-09","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"https://www.sciencedirect.com/science/article/pii/S2666261224000154/pdfft?md5=caefa12c6dfd0ce36348a3f53e0fafb5&pid=1-s2.0-S2666261224000154-main.pdf","citationCount":"0","resultStr":"{\"title\":\"Hydrogeochemical arsenic simulation of V-Ti-Fe tailings pond ecosystem: A case study from Panxi region, China\",\"authors\":\"Feng Jiang , Lu Sun , Fang Yang , Liang Tang , Ke Cheng , Nengjian Zheng , Yang Li , Meng Hou\",\"doi\":\"10.1016/j.oreoa.2024.100053\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<div><p>The V-Ti-Fe mine tailings waste releases high concentrations of aquatic arsenic (As) ions to downstream ecosystems. The hydrogeochemical As simulation facilitates the prediction of toxicity (or redox state) and devising control strategies to mitigate the negative impacts. Therefore, this study utilizes the Wanniangou tailings pond (a V-Ti-Fe mine tailings reservoir) in the Panxi region, Sichuan province, China, as a case study to elucidate the As hydrogeochemical behaviour under varying pH and redox potential (Eh) conditions. Our study reveals that (1) the water-oxygen exchange and Mn are important to regulating the redox conditions in the filtrates. The Eh determines the valence states of As, which vary from reduced states to oxidized states during the runoff from the tailings pond to downstream (Rehe River). The flow of wastewater in Rehe River minimizes both the As toxicity and concentration, eventually improving water safety. (2) In a reducing environment, hematite exhibits a limited capacity for As(III) adsorption. In the case of oxidation conditions, goethite mainly adsorbed As(V), with an elevated adsorption capacity. Meanwhile, Fe-minerals remain relatively stable under varying redox and weakly acidic conditions. Consequently, targeted engineering interventions can achieve two crucial outcomes: (1) Minimize the acidity of the mine environment to retard the release of heavy metals from the tailings waste. 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引用次数: 0
摘要
钒钛铁矿尾矿废料会向下游生态系统释放高浓度的水生砷(As)离子。水文地球化学砷模拟有助于预测毒性(或氧化还原状态),并制定控制策略以减轻负面影响。因此,本研究以中国四川省攀西地区的万年沟尾矿库(钒钛铁矿尾矿库)为案例,阐明在不同 pH 值和氧化还原电位(Eh)条件下砷的水文地球化学行为。我们的研究发现:(1) 水氧交换和锰对调节滤液中的氧化还原条件非常重要。Eh 决定了 As 的价态,在从尾矿库流向下游(热河)的过程中,As 会从还原态变为氧化态。废水在热河中的流动可最大限度地降低 As 的毒性和浓度,最终改善水质安全。(2) 在还原环境中,赤铁矿对 As(III)的吸附能力有限。在氧化条件下,网纹石主要吸附 As(V),吸附能力较强。与此同时,铁矿物在不同的氧化还原和弱酸性条件下保持相对稳定。因此,有针对性的工程干预可以实现两个关键结果:(1)最大限度地降低矿山环境的酸度,以延缓尾矿废料中重金属的释放。(2) 延长废水在热河中的停留时间,促进废水从还原态过渡到氧化态,从而协同减轻砷的毒性。
Hydrogeochemical arsenic simulation of V-Ti-Fe tailings pond ecosystem: A case study from Panxi region, China
The V-Ti-Fe mine tailings waste releases high concentrations of aquatic arsenic (As) ions to downstream ecosystems. The hydrogeochemical As simulation facilitates the prediction of toxicity (or redox state) and devising control strategies to mitigate the negative impacts. Therefore, this study utilizes the Wanniangou tailings pond (a V-Ti-Fe mine tailings reservoir) in the Panxi region, Sichuan province, China, as a case study to elucidate the As hydrogeochemical behaviour under varying pH and redox potential (Eh) conditions. Our study reveals that (1) the water-oxygen exchange and Mn are important to regulating the redox conditions in the filtrates. The Eh determines the valence states of As, which vary from reduced states to oxidized states during the runoff from the tailings pond to downstream (Rehe River). The flow of wastewater in Rehe River minimizes both the As toxicity and concentration, eventually improving water safety. (2) In a reducing environment, hematite exhibits a limited capacity for As(III) adsorption. In the case of oxidation conditions, goethite mainly adsorbed As(V), with an elevated adsorption capacity. Meanwhile, Fe-minerals remain relatively stable under varying redox and weakly acidic conditions. Consequently, targeted engineering interventions can achieve two crucial outcomes: (1) Minimize the acidity of the mine environment to retard the release of heavy metals from the tailings waste. (2) Prolonging the residence time of wastewater in Rehe River to promote the transition from a reducing state to an oxidizing state, thereby synergistically mitigating As toxicity.