炼锌固体废渣中重金属(Pb、Zn)的存在状态及环境影响

利用XRD、TEM/EDS和连续提取实验研究了土法炼锌固体废渣中重金属的矿物学特征及不同粒度中重金属的相态分布特征。与通常发现的重金属一般富集在小粒径废渣中的情况不同,本工作所研究的废渣样品中大粒径废渣与细粒径废渣相似,甚至有更高的金属含量。化学形态研究表明,冶炼过程形成的矿物(或玻璃质)集合体和堆积后的风化过程形成的次生矿物是废渣中重金属存在的主要化学相。同时发现Pb的残渣态很少(0.39%～15.75%),而Zn的残渣态较高(14.3%～46.2%),这可能与冶炼工艺所形成较多Zn的硅酸盐矿物有关。尽管可交换态Pb、Zn在不同相态中的相对比例非常小(Pb0.03%～1.30%;Zn0.03%～3.30%),但其绝对含量却比一般土壤或沉积物要高(Pb1.5～385μg/g;Zn3～590μg/g)。由于重金属可交换态有比其他化学相态更高的活动性和生物可利用性,因此,对环境有较大的潜在影响。废渣样品的微束分析表明,Pb在废渣中见有金属Pb存在形式或呈纳米金属Pb颗粒包裹于其他矿物或铁合金及熔球集合体中。同时不排除有Pb的碳酸盐矿物存在的可能。而以硅锌矿Zn2(SiO4)、锰硅锌矿(Zn,Mn)2犤SiO4犦和纤维状的丝锌铝石Zn8Al4犤(OH)8(SiO4)5犦·7H2O等矿物形式存在以及Fe、Mn等的铝硅酸盐形式存在的Zn,可能是导致Zn的残渣态较高的原因。与连续提     

Distribution and environmental impact of coal-mining wastes in Upper Silesia, Poland

 About 50 million tonnes/year of waste rock from coal-mining is generated in the limited area of the thickly populated Upper Silesian Coal Basin (USCB) in Poland. There are 380 coal-mining waste dumps, including 76 active dump sites covering over 2,000 ha. About 15-16 million tonnes/year of waste rock is being reused for civil engineering purposes in the same area. This brings about a problem of ground water deterioration by constituents leached from waste rock exposed to atmospheric conditions. The major factors determining the ground water contamination potential from waste rock are chloride salinity, sulfur content and acid generation potential. The concept behind the presented studies was to provide data for correct evaluation and prediction of contaminant release from the waste rock, based on the characterization of coal-mining waste properties, as well as on long-term laboratory, lysimetric and field studies. The results show that coal-mining waste dumps can be a long-term source of ground water contamination, lasting for decades and increasing with time. Ground water down-gradient from the disused 15–30-years-old part of the studied dump displays high and increasing acidification, high TDS, SO₄, and the highest, still increasing concentrations of Mn, Fe and Zn. Cost-effective and efficient pollution control measures, similar to the presented design and construction elements of the dump site, can mitigate the negative environmental impacts. Received: 3 July 1997 · Accepted: 9 September 1998     

Channel processes as a factor controlling accumulation of heavy metals in river bottom sediments: consequences for pollution monitoring (Upper Silesia, Poland)

 An evaluation of the influence of channel processes (erosion, accumulation, processing of channel sediments) on the dispersal of heavy metals in bottom sediments was carried out in the channels of the Sztoła and Biała Przemsza rivers in Upper Silesia, Poland. These rivers receive waters from a Zn and Pb mine. Mine waters transport a large amount of fine-grained sediments contaminated with heavy metals. The polluted material is accumulated in these stream courses and mixed with nearly homogeneous sandy sediment derived from erosion of the river banks and bed. Because these alluvia are easily set in motion, the distribution of heavy metal concentration in the channel in fraction <1 mm reflects differences in physical processes of sedimentation in its cross-section. The minimal values in active channel and maximal in the near-bank zone are typical for those channel sections where heavy metals, present in a solid state, are transported as a suspended load (normally the largest part of a polluted river course). In short sections heavy metals associated with the grains of a large mass which has accumulated in the active channel are transported as a bed load and the typical distribution pattern is reversed (in fractions both <1 mm and <0.063 mm). Such regularities can be disturbed in localities where strong, turbulent flow or frequent eddying occur and Mn oxides and hydrooxides and associated elements precipitate. The smallest variation in heavy metal concentration in the homogenous, fine-grained bank sediments which are trapped by plants below water level is a feature which recommends these localities as being the most suitable for monitoring of river pollution. Received: 11 November 1997 · Accepted: 12 March 1998     

某金矿区农田土壤重金属元素Pb的累积速率

以某金矿区农田土壤重金属Pb为研究对象,分别以2004和2012年采集样品的测试结果作为计算农田土壤重金属Pb累积速率的依据,以2004—2012年作为计算时间区间,以农田土壤重金属Pb的累积速率为研究内容,采用对比分析方法,分析区域Pb的累积速率特征,阐明人类工程活动极大地影响着农田土壤重金属Pb的累积过程。研究结果表明,全区农田土壤Pb平均累积速率为31.8mg/kg·a-1。选取选矿厂、冶炼厂、尾矿库、污水灌溉区、车载尾矿弃渣等典型污染源,对周边农田土壤Pb累积的时空变化特征进行分析。结果显示,选矿厂对农田土壤Pb累积的影响最大,其周边农田土壤Pb累积速率相当于全区Pb累积速率的4倍,该结论对防治重金属污染及保障人体健康具有实际指导意义。     

某金矿区农田土壤重金属元素Pb的累积速率

以某金矿区农田土壤重金属Pb为研究对象,分别以2004和2012年采集样品的测试结果作为计算农田土壤重金属Pb累积速率的依据,以2004—2012年作为计算时间区间,以农田土壤重金属Pb的累积速率为研究内容,采用对比分析方法,分析区域Pb的累积速率特征,阐明人类工程活动极大地影响着农田土壤重金属Pb的累积过程。研究结果表明,全区农田土壤Pb平均累积速率为31.8mg/kg·a-1。选取选矿厂、冶炼厂、尾矿库、污水灌溉区、车载尾矿弃渣等典型污染源,对周边农田土壤Pb累积的时空变化特征进行分析。结果显示,选矿厂对农田土壤Pb累积的影响最大,其周边农田土壤Pb累积速率相当于全区Pb累积速率的4倍,该结论对防治重金属污染及保障人体健康具有实际指导意义。     

Barium and radium discharged from coal mines in the Upper Silesia, Poland

 Waters discharged from coal mines in the Upper Silesia in Poland cause contamination of rivers and their sediments. Saline waters discharged from coal mines of the southern region contain elevated barium and radium. The discharge of these elements can be reduced by treating these waters with sulphates in mine workings. Sources of sulphate used in treatments include gypsum, anhydrite and industrial wastes such as: fly ash, slags and flotation tailings. Gypsum and anhydrite are used in the coal mine workings as components of the fire protection walls. Industrial wastes from power plants are stored in the mine workings as fire- and methane-protection agents. Sulphates precipitate barium and radium from saline waters inflowing into the mine workings. The waters can be treated by flowing them through old mine workings. In this case, the source of sulphates is the natural oxidation of pyrite. Mining activities and the natural process of desulphurisation of the Carboniferous rocks reduce the amount of barium and radium that is discharged in the southern region of Upper Silesia. The processes for reducing the environmental impact of toxic discharges from the mines should be monitored. Received: 3 July 1997 · Accepted: 27 March 2000     

小秦岭某金矿区农田土壤重金属元素污染的潜在生态危害评价

土壤重金属元素污染的潜在生态危害程度及空间分布是土壤污染防治的前提和基础。为揭示土壤中重金属元素的潜在生态危害程度,在前期土壤污染调查评价的基础上,采用Hakanson的潜在生态危害指数,以研究区西邻无工矿影响的农田土壤重金属元素含量均值作为参比值,对矿区农田土壤进行了重金属元素污染的潜在生态环境危害评价。结果表明,Hg是农田土壤中潜在生态危害最严重的元素,其次是Cd和Pb。Hg、Pb、Cd对土壤污染危害的贡献率之和达97.41%,仅Hg的贡献率就达84.37%。多个重金属元素潜在生态危害很强、极强的土壤样品占样品总数的49.62%,影响面积达74.54%。从西北向东南,土壤重金属元素潜在生态危害程度激增,这种空间分布与目前金矿选冶的布局一致。土壤重金属元素潜在生态环境危害的后果已被前期研究成果所证实。     

小秦岭某金矿区农田土壤重金属污染的潜在生态危害评价

土壤重金属元素污染的潜在生态危害程度及空间分布是土壤污染防治的前提和基础.为揭示土壤中重金属元素的潜在生态危害程度,在前期土壤污染调查评价的基础上,采用Hakanson的潜在生态危害指教,以研究区西邻无工矿影响的农田土壤重金属元素含量均值作为参比值,对矿区农田土壤进行了重金属元素污染的潜在生态环境危害评价.结果表明,Hg是农田土壤中潜在生态危害最严重的元素,其次是Cd和Pb.Hg、Pb、Cd对土壤污染危害的贡献率之和达97.41%.仅Hg的贡献率就达84.37%.多个重金属元素潜在生态危害很强、极强的土壤样品占样品总数的49.62%,影响面积达74.54%.从西北向东南,土壤重金属元素潜在生态危害程度激增,这种空间分布与目前金矿选冶的布局一致.土壤重金属元素潜在生态环境危害的后果已被前期研究成果所证实.     

Estimation of heavy metals (Cu,Zn, Pb) input into Punat Bay

The fate of heavy metals (Cu, Pb, Zn) from their sources to the final sink was analysed. Investigations included the identification of sources, the input from each source as well as transport towards their temporary (soil, vegetation, and marine water) and final sink (marine sediments). Research was conducted in the catchment area of Punat Bay on the island of Krk (Northern Adriatic, Croatia). Four sources were identified: long-range transport, traffic, antifouling paints and eroded material which annually introduced about 158 kg of Cu, 175 kg of Pb and 666 kg of Zn into the Bay. Antifouling paints were significant but not the main source of pollution in this area as was considered in previous investigations. Due to long-range transport, the input of Zn was almost four times greater, whereas the input of Pb was almost six times greater than the input from antifouling paints. Aerosols emitted from motor vehicles still represent the mayor source of Pb in this area. Cu originates mostly from antifouling paints and long-range transport. It was estimated that only around 30% of analysed elements introduced into the water column would be deposited in their final sink, i.e. marine sediments.     

Assessment of heavy metal contamination in soils around lead (Pb)-zinc (Zn) mining areas in Enyigba,southeastern Nigeria

Mining activities have been undertaken for over 95 years in Enyigba area of southeastern Nigeria. In this area, thirty-six (36) trace metals including those that are essential for plant and animal nutrition have been analyzed from forty-nine (49) soil samples that were collected from three Pb-Zn mines. The aim of the analysis is to assess the level of contamination of the soils caused by mining activities. Potentially harmful elements which are commonly associated with Pb-Zn mines were of special interest. Such elements included Pb, Zn, As, Cd, Mn, Fe, Se, Sb, Cu and Bi. Generally, the samples analyzed showed elevated concentrations of Pb, Zn, Cd, Cu and Cr when compared with concentrations documented in the international agricultural soil standards. Geo-accumulation indices of soils that occur closer to the mines indicate moderate to extreme level of contamination in Pb and moderate levels in Cd. Enrichment factor (EF) showed very high enrichment to extremely high enrichment in Pb. Cd and Zn enrichment were found to be significant and moderate respectively. Conversely, the geo-accumulation indices for soil samples located away from the mines indicate moderate to heavy contamination in Pb but had moderate to significant enrichment in Cd and moderate in Bi and Cr. In general, soil quality all around the mines were found to have deteriorated as revealed by the pollution load index. Thus the results of this study call for immediate remedial measures to be initiated. In addition, miners and local communities living around the mines need to be enlightened about the dangers of exposure to these heavy metal contaminants.     

Assessing the concentration and potential dietary risk of heavy metals in vegetables at a Pb/Zn mine site,China

Cd, Pb, Cu and Zn were measured in vegetables in Xiguadi village around Lechang Pb/Zn mine in Guangdong province, South China. The daily intake (DI) of these metals from vegetables by local people was also determined. The respective Cd, Pb, Cu and Zn concentration was 0.05–0.90 (mean 0.25), 1.04–5.82 (2.64), 0.53–7.07 (2.00) and 3.87–25.20 (11.68) mg kg⁻¹, of which Cd concentration in all vegetables exceeded the safe limit given by FAO/WHO. The DI was found to be 49.76, 475.56, 360.36 and 2,102.63 μg, respectively. The present results indicated local mining activity caused vegetable heavy metal contamination and Cd concentration exceeding the stipulated standards for all vegetables indicating potentially serious dietary risks for local people.     

豫西成矿带潭头盆地金矿区农田土壤重金属污染及来源解析

为查明豫西成矿带潭头盆地金矿区农田土壤重金属污染特征及污染来源,在该盆地农田中系统采集土壤样品,分析土壤中的重金属含量,采用聚类分析和主成分分析/绝对主成分分数(PCA/APCS)受体模型对污染源进行解析并计算污染源贡献率。结果显示:研究区农田土壤重金属Hg、As、Cr、Ni、Cu、Pb、Zn、Cd含量平均值均低于农用地土壤污染风险筛选值,整体土壤污染风险较低,仅部分样品Hg、As、Cu、Pb、Zn、Cd含量超过风险筛选值;Pb、Zn和Cd主要呈区域性污染,其他重金属元素主要呈孤立点状污染。Hg、Cd、Pb变异系数达到强变异水平,表明潭头盆地农田土壤中Hg、Cd、Pb元素受人类活动干扰比较强烈。综合聚类分析、主成分分析及空间分布特征,8种重金属主要来源于4类污染源:Cu、Pb、Zn和Cd污染来源于交通源(PC1);Cr和Ni污染来源于自然源(PC2);As污染来源于与金矿开采和尾矿堆存相关的矿业源(PC3);Hg污染来源于与小作坊汞溶解炼金相关的矿业源(PC4)。     

铜陵矿区土壤重金属元素的空间变异及污染分析

运用地统计学分析手段对铜陵矿区土壤中的As、Cd、Hg、Pb和Zn5种重金属元素进行空间变异分析及空间插值,并进行污染分析,以期为铜陵矿区土壤环境评价、土壤污染修复及环境决策提供科学依据。数据来源于"安徽省江淮流域多目标区域地球化学调查"结果,采用Johnson变换进行正态转换,地统计拟合变异函数中,As、Cd元素为球状模型,Pb、Zn元素为五球形模型,Hg元素为指数模型。结果表明,As、Cd、Pb、Zn元素的变异函数表现为各向异性,其方向性可能主要受矿床分布控制;Hg元素块金效应较大,表明其受小     

内蒙古半拉山钼铅锌多金属矿区物化探异常特征及找矿方向

半拉山铅锌多金属矿位于内蒙古自治区东部阿鲁科尔沁旗。文章系统总结了矿区地球物理及地球化学特征,圈定了异常区。根据物、化探成果及地质资料,成功预测了矿区东侧为"斑岩型钼矿"成矿区。提出了找矿方向。     

Environmental Geochemistry of Heavy Metal Contaminants in Soil and Stream Sediment in Panzhihua Mining and Smelting Area,Southwestern China

Mining and smelting activities are the main causes for the increasing pollution of heavy metals in soil, Water body and stream sediment. An environmental geochemical investiga-tion was carried out in and around the Panzhihua mining and smelting area to determine the ex-tent of chemical contamination in soil and sediment. The main objective of this study was to in-vestigate the environmental geochemistry of Ti, V, Cr, Mn, Cu, Pb, Zn and As in soil andsediment and to assess the degree of pollution in the study area. The data of heavy metal con-centrations reveal that soils and sediments in the area have been slightly contaminated. Geo-chemical maps of Igeo of each heavy metal show that the contaminated sites are located in V-Ti-magnetite sloping and smelting, gangues dam. The pollution sources of the selected elementscome mainly from dusts resultant from mining activities and other three-waste-effluents. The areaneeds to be monitored regularly for trace metal, especially heavy metal enrichment.     

Exploring Cd,Cu, Pb,and Zn dynamic speciation in mining and smelting-contaminated soils with stable isotopic exchange kinetics

The exchange kinetics of Cd, Cu, Pb, and Zn in seven mining and smelting-contaminated soils and the other two anthropogenically contaminated soils was investigated by using multi-elementary stable isotopic exchange kinetic (SIEK) method, and the experimental results were successfully interpreted by modelling using a sum of pseudo first order kinetics equations. SIEK results show that in the studied soils the isotopic exchange of Cd is a relatively fast process, and the exchange almost reaches an apparent plateau after 3-d equilibration; whereas for Cu, Pb, and Zn, the exchange is more sluggish, suggesting that it is important to understand the time-dependent metal mobility for risk assessment and management of contaminated soils. In most of the soils, the total isotopically exchangeable pool is divided, for all the metals, into two distinct pools: a fast exchangeable pool (E₁) with a kinetic rate constant k₁ having values around 1 min⁻¹ and a much slower exchangeable pool (E₂) with k₂ ranging from 0.0001 min⁻¹ to 0.001 min⁻¹. The distribution of the two exchangeable pools varies significantly among metals. The amount of isotopically exchangeable Cd related to the fast pool is dominant, accounting for on average 60% of total isotopically exchangeable pool in the soils; whereas this pool is smaller for Cu, Zn, and Pb. The sequence of average k₁ values is Cd > Pb ≈ Zn > Cu, consistent with the reported sequence of stability constants of metal-humic substances (HS) complexes while the average k₂ values follow the order: Cd > Pb > Cu > Zn, probably controlled by the slow desorption of metal ions associated with soil organic matter (SOM) fraction. Our results imply that further study on the exchange kinetics of metals on each individual sorption surface in soils, especially SOM, is critical to help understanding the overall exchange kinetics of heavy metals in whole soils.     

Provenance implications of Th–U–Pb electron microprobe ages from detrital monazite in the Carboniferous Upper Silesia Coal Basin, Poland

This paper reports the results of CHIME (chemical Th–U–Pb isochron method) dating of detrital monazites from Carboniferous sandstones in the Upper Silesia Coal Basin (USCB). A total of 4739 spots on 863 monazite grains were analyzed from samples of sandstone derived from six stratigraphic units in the sedimentary sequence. Age distributions were identified in detrital monazites from the USCB sequence and correlated with specific dated domains in potential source areas. Most monazites in all samples yielded ca. 300–320 Ma (Variscan) ages; however, eo-Variscan, Caledonian and Cadomian ages were also obtained. The predominant ages are comparable to reported ages of certain tectonostratigraphic domains in the polyorogenic Bohemian Massif (BM), which suggests that various crystalline lithologies in the BM were the dominant sources of USCB sediments.     

雄安新区某金属冶炼区土壤重金属污染程度及风险评价

为支撑雄安新区土地资源科学管理,完善中国土壤污染评价体系,文章以雄安新区某废旧金属冶炼区为研究区开展地质调查,采集541件表层土壤样品,测定了土壤中的Cd、Hg、Pb、As、Cu、Zn、Cr、Ni八种重金属元素的含量和pH,采用主成分分析法研究重金属元素的组合及分布特征,通过单因子指数法、内梅罗综合指数法、地质累积指数...     

西藏多不杂矿区土壤重金属特征及环境问题防治

在矿产开发前,充分了解矿区的土壤重金属环境特征对矿产绿色开发和合理开采具有重要意义。位于西藏改则县的多不杂矿床是多龙矿集区内的重要矿床之一,目前已探明铜资源量达234. 44万吨。本文以多不杂矿区为例,在地表选取4条剖面采集了37件土壤样品,开展了重金属元素(Cu、Pb、Zn、As、Cd、Cr、Hg)含量和pH值测试,对其中10件样品进行了重金属形态特征分析。采用单因子污染指数和内梅罗综合污染指数法分析研究了多不杂矿区内地表土壤重金属的含量、污染指数和形态特征,探讨了重金属元素来源及其对环境的影响程度。结果表明,多不杂矿区地表为碱性土壤,7种重金属元素中,Cu在所有样品中的含量均超过GB15618 1995Ⅲ级标准;Zn、Cd仅有最大值超过Ⅲ级标准;Pb、As、Cr、Hg含量均不超标。单因子污染指数呈现出Cu>Zn>As>Cd>Cr>Pb>Hg的分布特征,综合指数平均值为11. 60,表明重金属对环境的综合影响程度较高。Cu主要以铁锰氧化态和残渣态存在,分别占48. 40%和14. 73%,Pb、Zn、As、Cr主要以残渣态形式存在,分别占90. 27%、71. 48%、79. 59%、86. 12%。Cd主要以铁锰氧化态和碳酸盐态形式存在,分别占40. 05%和22. 42%,Hg主要以残渣态和腐殖酸态存在,分别占40. 16%和22. 54%。7种重金属元素来源主要有3类：Cu、Zn、Cd、Hg源于黄铜矿的氧化淋滤;Pb、As源于黄铁矿的氧化;Cr源于岩石的自然风化。针对重金属相关的环境问题,提出了针对性的防治建议。