煤矸石堆附近耕作层土壤中重金属污染状况与评价——以鲁西南煤炭基地为例

通过对鲁西南煤炭基地若干混堆的煤矸石山周围耕作层土壤的实际调查及分析测试资料,研究了煤矸石堆附近耕作层土壤中重金属污染状况。结果表明,土壤局部已经受到Cd、Ni的污染,但未出现多金属复合污染状况。煤矸石堆附近土壤已经受到采矿等人类活动的影响,其中Cd,Hg的人为影响最大。从8种重金属元素含量随深度的变化曲线形态来看,Hg,Cd2种元素与Cr,Ni,Cu,Zn,Pb,As6种元素曲线形态显示差异性,Hg,Cd元素在土壤中赋存、迁移等应具特殊性,有待进一步研究。     

山东安丘地区土壤-小麦系统重金属等元素间的相互作用

为了研究土壤-小麦系统重金属等元素间的相互作用,通过相关分析,探讨了安丘地区40件小麦籽实及其根系土中重金属元素间的相互关系。研究发现:(1)小麦籽实Cd、Hg、Pb、As、Ni、Cu、Zn富集系数与土壤pH、CEC、黏粒含量呈负相关,Cr富集系数与pH呈正相关;(2)小麦籽实重金属等元素富集系数间多数呈正相关;(3)小麦籽实Pb、Cu含量分别与土壤As、Pb含量呈正相关,籽实Cu、Zn含量分别与土壤Cd、Pb含量呈正相关。籽实除Cr含量与土壤Mg含量呈显著正相关外,籽实中其他重金属元素含量与土壤元素Ca、Mg含量关系不显著。小麦籽实中Cd、Pb、As等重金属元素含量与土壤中Mn、Mo、F等微量元素含量少数呈显著-极显著正相关;(4)小麦籽实中Cd、Hg、Pb、As等重金属元素含量与籽实中Ca、Mg、Mn、Mo等其他元素含量之间多数呈显著正相关。这些研究结果表明,土壤-小麦系统重金属元素之间、重金属元素与其他元素之间存在协同或拮抗作用,但具体机制尚需要进一步研究。     

电感耦合等离子体发射光谱-逐级化学提取法研究低硫煤矸石中微量元素的赋存状态及其环境效应

煤矸石是我国堆存量最大的工业固体废物,本文应用电感耦合等离子体发射光谱法、逐级化学提取法和相关性分析研究了淮北临涣矿区低硫煤矸石中10种微量元素的含量及赋存状态,并运用风险评价指数法评价其环境效应。结果表明,低硫煤矸石中Ba、Co、Cr、Mn、Ni、Pb、V含量均高于淮北煤和中国煤均值,Mn、V的富集系数大于1,有一定迁移风险。微量元素主要以残渣态和铁锰氧化物结合态存在,两者质量分数之和为68.87%~92.93%,其中Cd、Co、Cr、Cu、Ni、Pb、Zn赋存于硫化物矿物中,V赋存于黏土矿物中,Mn赋存于碳酸盐矿物和硫化物矿物中。10种微量元素对环境的危害性大小为:MnZnNiPbCdCuBaVCrCo,表明低硫煤矸石堆存过程中活性态Mn对生态环境造成危害的可能性最大,由Mn可能引起的煤矸石山周边地区土壤及水体污染应当重视。     

吉林白山地区原煤微量元素地球化学特征

对吉林白山地区煤矿主采煤层中的As、B、Ba、Cd、Cu、Hg、Pb、Se、Sr等微量元素进行了分析,结果表明:太原组与山西组由于成煤环境不同,微量元素组成及其质量分数存在一定的差异,太原组原煤中As、B、Hg、Pb、Se、Zn的质量分数明显高于山西组,山西组原煤中Ba、Cr、Cu、Mn、V的质量分数明显高于太原组。白山地区原煤中As、B、Hg、Pb、Se的质量分数明显高于地壳元素平均值,呈富集状态;Co、Cd与地壳平均值接近,其他元素均亏损。与全国煤中微量元素的质量分数平均值相比,As、Ba、Co、Cr、Cu、Hg、Ni、Pb、Se、V、Zn的质量分数高于全国平均值。B、Mn、Sr质量分数低于全国平均值。微量元素赋存状态及相关分析表明,Fe与亲硫有害元素As、Cu、Hg、Pb、Se具有显著相关关系,说明煤中黄铁矿及其他硫化物是许多有害微量元素的重要载体。      

内蒙古香林香达铜矿区地球化学找矿研究

针对矿区地表及井下四个中段共采集地层和构造蚀变岩样品194件,分析Ti、V、Cr、Mn、Co、Ni、Au、Ag、Cu、Pb、Zn、W、Sn、Mo、Bi、As、Sb、Hg等18种微量元素含量,编制各元素地球化学0号勘探线横剖面图,综合利用地球化学图件分析法与格里戈良分带指数法,确定元素的轴向分带序列。通过地质地球化学资料可知,石英闪长岩、构造蚀变岩中Cu、Ag、As、Au、Mo、Sn元素含量高,变异系数大,表明这些元素参与成矿蚀变作用。矿区原生晕轴向分带序列为:(Zn、Cr1、Hg1、Ni、As)→(Pb、V、Mn、W、Cr_2、Ti)→(Hg_2、Sb、Co、Bi、Sn、Ag、Au、Mo、Cu),根据元素地球化学横剖面图中主成矿元素异常高值带向下延伸未封闭、矿体向下未尖灭、特征前缘晕元素Hg、成矿晕元素Cu出现矿尾晕等特征,说明矿体向下仍有一定的延伸,预示着深部具有一定的找矿潜力。     

攀枝花钒钛磁铁矿区土壤重金属地球化学特征及污染评价

为了解攀枝花钒钛磁铁矿区土壤重金属的特征及污染程度,采集了矿区表层土壤样品和两个土壤剖面,用多种分析方法有针对性地分析了Cu、Pb、Zn、Ti、V、Co、Ni、As、Cd、Cr、Hg、Mn十二种元素。在分析分布特征基础上,对重金属进行了污染物负荷指数评价,结果发现:1)攀枝花钒钛磁铁矿矿区表层土壤大部分属于中等污染,少数属于强污染,个别达到了极强污染;2)Co、V、Cu、Cd、Ti几种元素的最高污染系数大,Zn、Mn、Ni、Cr四种元素的最高污染系数次之,Hg、Pb两种元素的最高污染系数较小,As的最高污染系数最小;3)从各区域的污染物负荷指数来看,排土场周围和朱矿采矿场下游附近污染程度较大,远离矿区以及矿区上游污染较小。     

吉南地区不同沉积环境原煤微量元素地球化学特征

对吉林南部地区煤矿主采煤层中的As、B、Ba、Cd、Cu、Hg、Pb、Se、Sr等微量元素的分析结果表明，太原组与山西组由于成煤环境不同，微量元素组成及含量存在一定的差异：太原组原煤中As、B、Hg、Pb、Se、Zn的含量明显高于山西组，山西组原煤中Ba、Cr、Cu、Mn、V的含量明显高于太原组。吉南煤区原煤中As、B、Hg、Pb、Se明显高于地壳元素平均值，呈富集状态，Co、Cd与地壳平均值接近，其他元素均亏损。与全国煤中微量元素相比，该区原煤中As、Ba、Co、Cr、Cu、Hg、Ni、Pb、Se、V、Zn的含量高于全国平均值，B、Mn、Sr含量低于全国平均值。微量元素赋存状态及相关分析表明，Fe与亲硫有害元素As、Cu、Hg、Pb、Se具有显著相关关系，说明煤中黄铁矿及其他硫化物是许多有害微量元素的重要载体。     

江西省赣县沙地土壤重金属的来源及环境等级评价

为研究赣县沙地土壤中重金属的来源,进行环境等级影响评价,在研究区采取了2708件土壤样对Cd、Cr、As、Hg、Cu、Pb、Zn、Ni八种重金属元素及pH进行分析测试,按照现有环境地球化学等级标准进行评价,利用地质统计分析法和空间分析法,探讨分析重金属元素可能来源。结果表明:研究区土壤中的As、Pb和Cu平均值均低于赣州市背景值,Cd、Hg、Cr、Zn和Ni平均值略高于赣州市背景值。与全国土壤背景值相比,Cd、Pb平均值高于全国土壤背景值,As、Co、Ni、pH、Cu低于全国土壤背景值,土壤中Hg、Zn背景值含量与全国背景值相差不大;各重金属元素具有较好的空间相关性,空间变异主要受结构性因素为主,受随机性因素较小;基于各元素半差函数块基比,结合元素间相关系数及因子载荷分析,研究区中Cd、Cr、Cu、Pb、Zn和Ni主要受地球化学成因影响,得出AS、Cd和Pb土壤污染主要来自地质高背景。     

神木北部矿区不同土壤类型下重金属污染特征与评价

通过测量神木北部矿区及其毗邻地区2种土壤类型(风沙区和黄土区)下8种重金属(As、Cd、Cr、Hg、Pb、Cu、Zn、Ni)元素含量,评价矿区整体土壤重金属污染情况。结果表明:研究区2种土壤条件下除Pb和Cd外,其他6种重金属含量较毗邻未开采区具有显著增加,但8种土壤重金属含量均没有超过国家土壤环境质量二级标准;风沙区土壤污染程度较黄土区大;重金属元素污染分担率表现为HgZnAsCuNiCrPbCd;Hg、Zn和Cr 3种元素在两种土壤类型中均为重度污染,As、Cu和Ni属于中轻度污染,Cd和Pb属清洁安全类。     

徐州城市表层土壤中重金属环境风险测度与源解析

研究了徐州城市表层土壤的21个样品中重金属元素富集特征,结果表明,与我国土壤元素的背景值(算术平均值)相比,表层土壤中Zn、Cd、As、Hg、Sb、Sn和Ag等元素富集程度高;Se、Sc、Ba、Bi、Pb、Cu、Ni、Cr、Mn、Mo、Be、Ga和Co等元素的富集程度较低。不同城市表层土壤中重金属元素有着不同的来源,统计分析结果表明,研究区表层土壤样品中重金属元素可分成4种类别:“自然因子”类别元素(Ti、Ga、Li、V、Co、Mn、Be和Pt);“交通因子”类别元素(Ag、Se、Sc、Pb、Cu、Zn、Cd、Br、S、Mo和Au);“燃煤因子”类别元素B(i、Cr、Hg、As、Sb和Pd)和混合源类别元素(Sn和Ba)。环境风险指数的计算结果表明,表层土壤中重金属污染具有较大的环境风险,其中属于中等环境风险级别以上的样品占近40%。     

新庄孜矿塌陷区煤矸石中重金属迁移对覆土影响

针对淮南新庄孜矿覆土造地中煤矸石填充带来的重金属元素迁移污染进行了研究。结果表明:煤矸石中有毒元素Pb、As、Cd、Hg向覆土有一定迁移,且距离煤矸石越近的土壤中重金属含量明显增高;虽然覆土中重金属含量均超过淮南土壤的均值,但是该土壤中Pb、As和Cd含量均符合国家二级标准;其中土壤中Hg含量分别符合国家一级标准和二级标准。须对覆土中重金属元素进行跟踪研究。      

Proton-induced X-ray emission measurements of trace elements in water samples collected from an Indiana coal mining locality

A new method of simultaneous multi-elemental analysis, Proton Induced X-ray Emission (PIXE), was used to detect trace elements in waters associated with a coal strip-mining operation in southern Indiana. Stream, pond, and ground water samples were collected and analyzed monthly from, or near, Sulphur Creek in Sullivan County. The concentrations of 26 major and trace elements were determined in samples from eleven locations: K, Ca, Ti, V, Cr, Mn, Fe, Co, Ni, Cu, Zn, Ga, As, Se, Br, Rb, Sr, Mo, Cd, Sn, Sb, I, Ba, Hg, Pb, and U. Elemental concentrations fluctuated considerably throughout the 13-month sampling period and also among sampling sites. Nickel, Zn, As, Cd, Mn, Fe, and Ca were highest in the upstream water which was most acidic (pH = 2.9–4.0) because of old unreclaimed mining operations. The highest values recorded were Ni = 1662 ppb, Zn = 4953 ppb, As = 26 ppb, Cd = 93 ppb, Mn = 5063 ppb, Fe = 63 ppm, and Ca = 325 ppm. The concentrations of these elements decreased downstream as the pH of Sulphur Creek increased which was likely due to the influence of the calcareous glacial till cover in the area and the recent mining activity which disturbed overburden containing a high percentage of calcareous materials. Lead, I, Br, and Ti values were highest (661 ppb, 86 ppb, 70 ppb, and 45 ppb, respectively) in the ground water from the coal seam (pH approximately 7). Other elements which were relatively high in the pH 7 waters closest to the current mining operations (pond, stream, and groundwater) included K (17 ppm), Sr (3408 ppb), Ba (173 ppb), As (14 ppb), Rb (16 ppb), Sn (14 ppb), and Cu (3840 ppb). The highest Cu concentration was recorded at the point where drainage water from the mine entered Sulphur Creek. Gallium, U, Hg, and Mo were found in low (< 13 ppb for Ga and Hg; < 205 ppb for Mo and U) concentrations and only in the ponds within the mine.     

煤矸石释放重金属环境效应研究--淮南煤矿塌陷区水体试验场实例调查

概要分析了淮南新孜5号井煤矸石所含的重金属元素对塌陷区鱼塘水质的影响,指出除个别水样中Zn、Cu超标外,其他均不超标,该鱼塘水质适宜养鱼要求。矸石样与华北及整个地壳泥岩中元素的丰度比,矸石中Cr、Pb、Zn与泥岩丰度基本持平,而Cd、Cu均超过其他泥岩中丰度值。因此,煤矸石在地面遭受风化,其所含有害物质可能会释放到环境,在煤矸石堆放处适当进行监测还是必要的。     

Abundances and modes of occurrence of trace elements in the Çan coals (Miocene), Çanakkale-Turkey

This study presents the concentrations and modes of occurrence of trace elements in 81 coal samples from the Çan basin of northwestern Turkey. The concentration of trace elements in coal were determined by inductively coupled plasma-mass spectrometry and inductively coupled plasma-atomic emission spectrometry. Additionally, traditional coal parameters were studied by proximate, ultimate, X-ray diffraction, and petrographic analyses. Twenty trace elements, including As, B, Ba, Be, Cd, Cu, Co, F, Hg, Mo, Ni, Pb, Sb, Se Sn, Th, Tl, U, V, and Zn, receive much attention due to their related environmental and human health concerns. The Çan coals investigated in this study are lignite to sub-bituminous coal, with a broad range of ash yields and sulphur contents. The trace element concentrations show variety within the coal seams in the basin, and the affinities vary among locations. The concentrations of B, Ba, Be, Cd, Cu, Co, F, Hg, Mo, Ni, Pb, Sb, Se, Sn, Tl, and Zn in Çan coals are within the Swaine's worldwide concentration range, with the exception of As, Th, U, and V. On the other hand, compared with world coals, the Çan basin coals have higher contents of As, B, Cu, Co, Mo, Pb, Th, U, V, and Zn. Based on statistical analyses, most of the trace elements, except for U, show an affinity to ash yield. Elements including As, Cd, Hg, Se, Cu, Mo, Ni, and Zn, show a possible association with pyrite; however, the elements Se, B, and Mo can be have both organic and inorganic associations.     

淮南煤田深部A组煤中有害微量元素地球化学特征

以淮南煤田深部A 组煤为研究对象,全层刻槽采集了煤、夹矸和顶底板岩石样品,采用电感耦合等离子质谱仪 （ICP-MS） 测试分析了样品中13 种有害微量元素的含量,对比研究了其分布特征,结合Tessier 五步形态提取法和相关性分 析探讨了煤中有害微量元素的赋存形态。结果表明：（1） 与中国上陆壳中各种微量元素含量均值相比,淮南深部A 组煤中 B,As,Se,Mo,Cd,Pb,Hg 的富集系数均大于1,在A 组煤中表现为富集;A 组煤中B,As,Se,Cd 的含量均高于淮南煤 田上部B 组煤、华北煤以及中国煤中的含量均值;（2） 相关性分析和逐级提取实验结果表明,A 组煤中微量元素主要以残 渣态和铁锰氧化物结合态存在,两者质量分数之和达到55%~98%,其中Ni,Mo,Cd,Hg,Cu,Pb 和Zn 主要赋存于硫化物 矿物中,Mn 主要赋存于碳酸盐矿物中,V,Cr,Se,B 和As 主要赋存于硅铝酸盐等黏土矿物中。（3） B 元素示踪物源及沉 积环境结果显示,淮南煤田深部A 组煤成煤环境为海相咸水沉积环境,稳定的咸水沉积环境以及受海水影响等因素导致A 组煤中微量元素出现不同程度的富集。     

Environmental contamination of trace elements in the vicinity of Okpara coal mine, Enugu, Southeastern Nigeria

Water, sediment, and mine spoil samples were collected within the vicinity of the Okpara coal mine in Enugu, Southeastern Nigeria, and analyzed for trace elements using ICP-MS to assess the level of environmental contamination by these elements. The results obtained show that the mine spoils and sediments are relatively enriched in Fe, with mean values of 1,307.8(mg/kg) for mine spoils and 94.15% for sediments. As, Cd, Cr, Mn,Ni, Pb, and Zn in the sediments were found to be enriched relative to the mean values obtained from the study area, showing contamination by these elements. The mean values of Fe, Mn, Cu, and Cr in the mine spoils and mean values of Fe, Cu, Pb, Zn, Ni, Cr, and Mn in sediments, respectively, are above the background values obtained from coal and shale in the study area, indicating enrichment with these elements. The water and sediments are moderately acidic, with mean pH values of 4.22?±?1.06 and 4.66?±?1.35, respectively. With the exception of Fe, Mn, and Ni, all other elements are within the Nigerian water quality standard and WHO limits for drinking water and other domestic purposes. The strong to moderate positive correlation between Fe and Cu (r?=?0.72), Fe and Zn (r?=?0.88), and Fe and As (r?=?0.60) at p?<?0.05 as obtained for the sediments depict the scavenging effect of Fe on these mobile elements. As also shows a strong positive correlation with Mn (r?=?≥ 0.70, p?<?0.05), indicating that Mn plays a major role in scavenging elements that are not co-precipitated with Fe. In water, the strong positive correlation observed between Cr and Cd (r?=?1.00), Cu and Ni (r?=?0.94), Pb and Cu (r?=?0.87) and Zn and Cu (r?=?0.99); Ni and Pb (r?=?0.83) and Zn and Ni (r?=?0.97); and between Pb and Zn (0.84) at p?<?0.05 may indicate similar element–water reaction control on the system due to similarities in chemical properties as well as a common source. Elevated levels of heavy metals in sediments relative to surface water probably imply that sorption and co-precipitation on Al and Fe oxides are more effective in the mobilization and attenuation of heavy metals in the mine area than acid-induced dissolution. The level of concentration of trace elements for the mine spoils will serve as baseline data for future reference in the study area.     

淮南矿区煤中12种微量元素的赋存状态及环境效应

为研究淮南矿区煤中微量元素的赋存状态和环境效应,在淮南矿区7个矿井共采集17个样品,采用电感耦合等离子质谱仪（ICP-MS）测定了12种微量元素的含量,分别利用聚类分析和因子分析,结合其地球化学性质,讨论了它们的赋存状态,并采用静态燃烧实验研究其挥发性。结果表明:研究的元素没有异常富集;Zn和Cu赋存于闪锌矿中,Cr、Pb和Cd被粘土矿物吸附,Ba可能赋存于铁白云石和方解石中,Ni、Mo、Co和As主要赋存于黄铁矿中,Be和Se以有机结合态存在;研究的元素大多不易挥发,但Zn和Pb易挥发,且含量较高,环境危害较大,Zn和Pb分别赋存于闪锌矿和粘土矿物中,可通过洗选脱除减小其危害。      

Selective chemical extraction of heavy metals in tailings and soils contaminated by mining activity: Environmental implications

Total concentrations of chemical elements in soils may not be enough to understand the mobility and bioavailability of the elements. It is important to characterise the degree of association of chemical elements in different physical and chemical phases of soil. Another geochemical characterisation methodology is to apply sequential selective chemical extraction techniques. A seven-step sequential extraction procedure was used to investigate the mobility and retention behaviour of Al, Fe, Mn, Cu, Zn, Pb, Cr, Co, Ni, Mo, Cd, Bi, Sn, W, Ag, As and U in specific physical–chemical and mineral phases in mine tailings and soils in the surroundings of the abandoned Ervedosa mine. The soil geochemical data show anomalies associated with mineralised veins or influenced by mining. Beyond the tailings, the highest recorded concentrations for most elements are in soils situated in mineralised areas or under the influence of tailings. The application of principal components analysis allowed recognition of (a) element associations according to their geochemical behaviour and (b) distinction between samples representing local geochemical background and samples representing contamination. Some metal cations (Mn, Cd, Cu, Zn, Co, Cr, Ni) showed important enrichment in the most mobilisable and bioavailable (i.e., water-soluble and exchangeable) fractions due likely to the acidic conditions in the area. In contrast, oxy-anions such as Mo and As showed lower mobility because of adsorption to Fe oxy-hydroxides. The residual fraction comprised largest proportions of Sn and Al and to a lesser extent Zn, Pb, Ni, Cr, Bi, W, and Ag, which are also present at low concentrations in the bioavailable fractions. The elements in secondary mineral phases (mainly Fe, Mn, Cu, Zn, Cd, Pb, W, Bi, Mo, Cr, Ni, Co, As and U) as well as in organic matter and sulphides are temporarily withheld, suggesting that they may be released to the environment by changes in physico-chemical conditions.     

Mobility of trace and potentially harmful elements in the environment from high sulfur Indian coal mines

Coal mine rejects and sulfide bearing coals are prone to acid mine drainage (AMD) formation due to aqueous weathering. These acidic effluents contain dissolved trace and potentially harmful elements (PHEs) that have considerable impact on the environment. The behavior of these elements in AMD is mainly controlled by pH. The focus of the present study is to investigate aqueous leaching of mine rejects for prediction of acid producing potential, rates of weathering, and release of PHEs in mine drainage. Mine reject (MR) and coal samples from the active mine sites of Meghalaya, India typically have high S contents (1.8–5.7% in MR and 1.7–4.7% in coals) with 75–90% of the S in organic form and enrichment of most of the PHEs in rejects. Aqueous kinetic leaching experiments on mine rejects showed high acid producing potential and release of trace and potentially harmful elements. The elements (Sb, As, Cd, Cr, Co, Cu, Pb, Mn, Ni, V and Zn) in mine sample leachates are compared with those in mine waters. The concentrations of Al, Si, P, K, Ti, Mn, Fe, Co, Ni, Cu, Zn and Pb are found to increase with leaching time and are negatively correlated with pH of the solution. The processes controlling the release of these elements are acid leaching, precipitation and adsorption. The critical loads of PHEs in water affected by AMD are calculated by comparing their concentrations with those of regulatory levels. The Enrichment Factors (EFs) and soil pollution indices (SPIs) for the elements have shown that PHEs from coal and mine reject samples are mobilized into the nearby environment and are enriched in the associated soil and sediment.