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准确掌握煤矸石中重金属元素的溶出特征与释放规律对评价与防治煤矸石对土壤与地下水环境污染具有重要意义。笔者选取广西合山市里兰矿区的大型煤矸石堆(GD06)为研究对象,通过对煤矸石静态浸泡和动态淋滤的实验研究,揭示煤矸石中8种典型的有害重金属元素As、Cd、Cr、Cu、Mn、Ni、Pb、Zn在不同pH值、不同环境温度、与降水的不同作用方式下的溶出特征与释放规律。结果表明,煤矸石在静态浸泡过程中除未检出Mn外,其他7种重金属元素的溶出浓度随浸泡时间的延长而增加,表现出前期的快速释放和后期的慢速释放规律;而浸泡温度升高后,部分重金属元素如Cr、Cu、Pb在浸泡后期的释放速率呈增加趋势。动态淋滤过程中8种重金属元素表现出间歇性快速释放规律,且溶出浓度大于静态浸泡方式,对环境的影响更显著。pH值和温度是煤矸石静态浸泡重金属元素溶出特征的重要影响因素,重金属元素的溶出浓度随温度升高而增加,随pH值减小表现出不同的溶出特征与释放规律。Zn、Ni、Cd和As在静态浸泡和动态淋滤实验中的释放量和释放率较大,是煤矸石淋滤液中最易污染土壤和地下水的重金属元素。 相似文献
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《吉林大学学报(地球科学版)》2015,(Z1)
<正>近年来,矿山开采带来的环境污染问题日益严重,矿区内的尾矿坝及露天堆放的废石堆、矿石堆是矿区周围及其下游环境中重金属元素的主要来源,天然雨水淋溶浸泡作用对重金属元素的释放迁移具有一定的促进作用[1],因此,对尾矿、废石、矿石的模拟淋滤实验能够揭示污染源中矿物的分解转化规律、水-岩氧化还原反应机理、重金属元素在水-岩中的迁移转化规律以及影响因素等,从而能够为矿山环境污染 相似文献
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《吉林大学学报(地球科学版)》2015,(Z1)
<正>伴随矿产资源的开发与利用所引发的环境问题日益受到了广大学者的关注。目前,矿山环境研究从污染源如废石、尾矿、酸性排水至元素迁移介质如土壤、地表水、大气等均有涉及。此外,相关污染模拟实验及评价模型的建立也为矿山环境的修复及治理提供了切实可靠的方法。矿区内的尾矿坝及露天堆放的废石堆、矿石堆是矿区周围及其下游环境中重金属元素的主要来源,天然雨水淋溶浸泡作用对重金属元素的释放迁移具有一定的促进作用,因此许多国内外学者致力于尾矿、废石、矿石的模拟淋滤实验研究,包括 相似文献
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铜陵矿山酸性排水及固体废弃物中的重金属元素 总被引：8，自引：0，他引：8
在调查中国铜陵凤凰山铜矿和新桥硫铁矿两种不同类型矿山固体废弃物特征的基础上,研究了矿山尾矿和废石产生酸性排水的可能性及其差异以及矿山固体废弃物中重金属元素的赋存形式。结果表明,凤凰山铜矿的尾矿基本不产生矿山酸性排水,而新桥硫铁矿采矿废石产生矿山酸性排水,并且凤凰山铜矿的尾矿和新桥硫铁矿采矿废石中重金属元素的赋存形式也有差异,前者重金属Cu、Pb、Zn、Cd、As、Hg主要赋存于硅酸盐态中,而后者在还原态中有较高的含量,这反映了在地表条件下尾矿中大量重金属元素已经发生了迁移,而采矿废石已经开始氧化,且酸性排水的存在更有利于废石中重金属元素的迁移和扩散,进而导致矿区周围环境的污染。 相似文献
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酸雨可与MICP矿化作用过程中生成的碳酸盐反应,破坏材料的结构强度,使被固定的重金属离子再次释放,但该技术在酸雨环境下的研究较少,耐酸腐蚀性尚不明确,因此对酸雨入渗作用下MICP固化重金属污染土的淋滤特性的研究具有现实意义。本文设计了pH值为3.5、4.5、5.6的3种典型的酸雨条件,用pH值为7.5的去离子水作对照,通过土柱淋滤的方法对MICP固化粉土进行了实验研究,分析不同酸雨pH值对MICP固化铅污染土样的强度、pH值、Pb2+、Ca2+淋出量及Pb2+赋存形态的影响。结果表明：随酸液pH值降低,MICP固化试样的强度降低,淋出液pH值降低,Pb2+、Ca2+淋出量增加,固化试样中可交换态的Pb2+增加,当pH值为5.6时,试样受酸雨影响较小,pH值降为3.5时,试样变化显著。 相似文献
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对湘中桃江锰矿废矿堆的废石进行了主量元素、稀土元素、微量元素和重金属元素的地球化学分析。野外观察及分析结果表明:组成废矿堆的岩石主要是赋矿围岩中奥陶统黑色页岩和原生碳酸锰矿石。这些废石富含Cu、Pb、Zn、Cr、Tl、Sb、U等重金属元素。废石暴露地表而遭受风化分解,导致Sc、V、Cr、U、Cd、Th等重金属元素淋滤释出,在废石样品中均表现出不同程度的迁移特征,且以V、Cd、U的迁移性最为强烈。此外,黑色页岩中Ni、Cu、Zn、Pb、Tl、Sb也明显发生淋失。这些重金属元素如Cd、Tl等毒性极强,进入矿区周围不断积聚,便可能对环境造成严重的影响。故对区内分布的废矿堆作为重金属污染源应高度重视。 相似文献
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针对煤矸石山在降水淋滤作用下对矿区周边地下水造成污染的严重问题,用实验模拟法对包头石拐区一废弃煤矿进行饱和状态下煤矸石的淋滤实验研究。结果表明:煤矸石中Ca、Mg、Fe、Cu、Zn、NO3-、SO42-、Cl-的淋滤过程都遵循浓度先升高再降低到稳定值的基本规律,只是NO3-、SO42-、Cl-的淋出速率明显大于重金属的淋出速率,Ca和Mg、SO42-和Cl-、Pb和Cr、Cd有相似的淋出机制;重金属最强淋出率从大到小的顺序是Mg>Cd>Ca>Cu>Zn>Cr>Fe>Pb;Hg和As等含量甚微,均未检出。 相似文献
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ZHU Xiaoqing 《中国地球化学学报》2005,24(4):306-315
Experimental studies were undertaken on leaching of sedimentary rocks （ dolomite and sandstone） and Hg, Sb ores by distilled water under the condition of a completely open system （room temperature and room pressure）. The aim is to find whether the halogen elements or metal elements first enter the solution at the early stage of meteoric waters converting to groundwaters and ore fluids, and, at the same time, to understand how and when they enter distilled water solutions from the rocks. The experimental resuhs have shown that F and Cl began to enter the fluids in the initial period of thirty days. With increasing leaching duration, the amounts of the elements that entered the fluids increased steadily. During the period from 120 days to 150 days the amounts increased more drastically, followed a slow increase. It is found that the capability of Cl entering the solutions is much greater than that of F. Hg and Sb were found not to have entered the solutions till 120 days later. During this period of time the pH value of the solutions began to drop. As for Hg and Sb ores, Hg and Sb began to enter the solutions on the 60th or 90th day, greatly ahead of schedule, but the two metallic elements in the rock samples began to enter the solutions 150 days later. Relatively speaking, Hg is more easily leached out than Sb from the rocks. In some rock samples, Sb could be detected in the solutions at the end of the experiment. However, Cu, Pb and Zn had not been detected in the leaching solutions from the beginning to the end of the experiment. In the whole leaching process the pH value of the solutions tend to decrease slowly from 7.1 at the beginning to 6.5 at the end. That is to say, in the interaction between pure water and rock the halogen elements in the rocks were preferentially leached out and then entered the fluids. With increasing water/rock reaction duration and amount of halogen-group elements in the solution and with decreasing pH value of the solution, some active metallic elements began to release in small amounts. This experimental result can explain the source and mechanism of volatile components and trace metals in underground waters. Meanwhile, as for those ore deposits produced by ore fluids derived from meteoric waters, the experimental result is also helpful to the understanding of the geochemical variation trend at the initial stage of conversion of meteoric waters to ore fluids. 相似文献
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渔塘坝是中国较为典型的高硒地区之一。从该区选取了4个典型的富硒碳质岩样品,并在常温条件下进行了淋滤实验研究(pH=2.0,4.0和6.5)。初步结果表明:随着液固比的增大和淋滤时间的延长,淋滤液中硒含量变化的总体呈降低趋势。不同岩类间硒的淋失量有所差别,但岩石总量硒并不是影响硒淋失的主要因素。淋滤原液的不同pH值对岩石硒的淋失有显著影响,其淋失量的排列顺序是pH=2.0>pH=6.5>pH=4.0。岩石中碳酸盐与黄铁矿含量之比同淋滤液pH的变化有关,并且极可能是影响岩石风化初始阶段硒淋失的重要因素之一。 相似文献
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Phosphate amendment of metalliferous waste rocks, Century Pb-Zn mine, Australia: Laboratory and field trials 总被引：1，自引：0，他引：1
Amy MauricBernd G. Lottermoser 《Applied Geochemistry》2011,26(1):45-56
The aim of the study was to determine whether the application of phosphate compounds (phosphorite rock, phosphate fertilizer) to polyminerallic waste rocks can inhibit sulfide oxidation and metal mobility (Cu, Pb, Zn, Cd, Ni, Mn, Mg). Waste rocks comprised sulfidic carbonaceous shales and were sourced from the Century Pb-Zn mine, NW Queensland, Australia. The acid producing, Pb-Zn rich rocks consisted of major quartz, muscovite/illite, dolomite, siderite and kaolinite as well as smaller amounts of sulfide minerals (e.g. galena, sphalerite, pyrite). Laboratory leach experiments were conducted on finely granulated phosphate-treated waste rocks (>2 to <30 mm) over 13 weeks, whereas phosphate amendment of coarsely granulated waste rocks (sand to boulder size) was investigated using heap leach piles at the mine site over an 11 months period. Results of the laboratory experiments demonstrate that the treatment of finely granulated waste rocks with phosphorite rock produced leachates with near-neutral pH values due to calcite dissolution. This in turn did not allow the leaching of apatite, formation of secondary phosphate phases and phosphate stabilization to occur. Metal mobility in these amended wastes was restricted by the dissolution of calcite and the resultant near-neutral pH conditions. By contrast, the application of the water-soluble phosphate fertilizer MKP (KH2PO4) to polyminerallic sulfidic waste rocks during the short-term laboratory experiments led to the formation of phosphate coatings and precipitates and inhibited acid and metal release (Cd, Mn, Ni, Pb, Zn). At least in the short term, the application of phosphate fertilizers proved to be an effective method. However, results of the long-term field trials demonstrate that coarsely granulated waste rocks were not coated by secondary phosphate phases and that amendment by phosphorite rock or superphosphate fertilizer did not improve leachate quality compared to the unamended waste. Thus, phosphate stabilization appears ineffective in suppressing oxidation of sulfides in coarsely granulated mine wastes. 相似文献
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《Journal of Geochemical Exploration》2006,90(3):157-165
A study was initiated to analyse metal flows from alum shale to the environment in an area in Öland, Sweden. The study was performed by elemental analysis and leaching experiments of alum shale together with analysis of groundwater and surface water samples.The metal concentrations in non-weathered alum shale were much higher than in weathered or burnt shale, especially for cadmium (Cd), nickel (Ni) and zinc (Zn), indicating a loss of metals during weathering or burning of the shale. The release of metals through weathering was clearly demonstrated by the leaching tests. A 36-week leaching period of non-weathered shale resulted in a drastic drop in pH and a significant increase in metal concentrations in the leachate. The metal concentrations in groundwater were inversely related to the pH. For surface waters, the concentrations of Cd, copper (Cu), Ni and Zn were generally increased compared to background values.In conclusion, metals are released through weathering or burning of alum shale, as well as from heaps of weathered or burnt shale. The release of metals is strongly related to low pH, especially for Cd, Ni and Zn. 相似文献
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Lallan Prasad Gupta Hodaka Kawahata Mio Takeuchi Hidekazu Ohta Yoshiro Ono 《Resource Geology》2005,55(4):357-372
Abstract. Municipal solid waste combustion leads to concentration of various metals in the solid residue (fly ash) remaining after combustion. These metals pose serious environmental hazard and require proper handling and monitoring in order to control their harmful effects. Leachability of some metals from fly ash was examined in fly ash and Milli-Q water mixture (liquid-to-solid ratio, 100) under various temperature and pH conditions in the laboratory. The leaching experiments conducted for 24 hours showed that pH was generally more important than temperature in controlling the amount of metals leached out of the fly ash. However, at a given pH, rise in temperature led to different degree of (usually one to two fold) enhanced or reduced leaching of metals. Owing to amphoteric nature of oxides of Al, Cr, Pb and Zn, these metals often yielded typical pattern of increase and decrease in their concentrations with change in pH. The extent of leaching of Cr and Pb in our experiments suggests that decrease of pH to acidic range in the case of Pb and to neutral to acidic range for Cr over a long period of storage of fly ash at solid waste dumping site may facilitate leaching of these metals from fly ash, leading to contamination of groundwater to the level that exceeds beyond the level permitted by the environmental laws. 相似文献
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铜陵鸡冠山硫铁矿废矿堆积区的重金属分布与磁化率变化 总被引：2，自引：1，他引：2
应用ICP-AES、EMPA和矿物磁测,对铜陵市鸡冠山硫铁矿废矿堆积区的废矿及周围进行系统分析.发现不同堆放时间的废矿样品中重金属含量的变化规律不同,在堆放时间为10年和6年的剖面(分别为XO、XM剖面)呈现富集-淋滤-富集的变化模式,而在堆放时间<3年的剖面(XN剖面)呈现富集-淋滤的变化模式.结合重金属迁移的特性,证明重金属对周边的生态环境存在着潜在的危害性.同时还分析了风化程度不同的XO、XM、XN剖面样品中磁化率与重金属的关系,证实两者之间存在较好的相关性.磁化率是重金属含量变化的一个有效指数,它的研究为重金属污染研究提供了一个新的方法. 相似文献
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焙烧分离-氢化物发生-原子荧光光谱法测定铜铅锌矿石中的硒 总被引：2，自引：2，他引：0
样品经艾斯卡试剂(碳酸钠和氧化锌)半熔法分解,沸水提取,使硒与主量金属元素铜、铅、锌及其他过渡金属和贵金属元素得到分离;滞留在溶液中的干扰元素,通过在酸性介质中加铁盐来掩蔽。采用焙烧分离-氢化物发生-原子荧光光谱法测定铜矿石、铅矿石和锌矿石中的硒,干扰少、灵敏度高。确定了最佳条件为盐酸浓度30%,硼氢化钾浓度20 g/L,铁盐浓度1 mg/mL;干扰元素的允许量铜为40 mg/L,铅为8 mg/L,锌为400 mg/L。同时对铜、铅、锌主量金属元素进行分离效率试验,效果好。方法检出限为0.0203μg/g,测定范围为0.15～100μg/g。经全国不同地区7家实验室采用铜矿石、铅矿石和锌矿石国家标准物质验证,精密度的重复性限和再现性良好,准确度高。建立的方法也适合于土壤及多金属矿物中硒的测定。 相似文献