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通过对黔北桐梓、金沙煤矿调查及取样、样品分析测试,发现桐梓、金沙煤层普遍具有稀土和锂元素高富集特征,其中稀土和锂元素含量明显高于我国煤中稀土平均值（138 μg/g）和锂平均值（31.8 μg/g）（王登红等,2019; 代世峰等,2020）,而且稀土和锂含量比我国山西、内蒙古等地富稀土、锂等煤含量还要高,黔北煤中稀土、锂等金属元素含量如此之高在全国实属罕见,而且在这些煤矿废水中发现稀土元素超富集现象,其对研究煤层中稀土元素浸出机理提供了天然的实验场所。因此,揭示该区域煤中高富集稀土、锂等金属元素的富集特征、富集原因,废水中金属元素浸出机理是本次研究目的。 相似文献
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粉末压片制样波长色散X射线荧光光谱法测定钼矿石中9种元素 总被引：2，自引：2，他引：0
X射线荧光光谱(XRF)分析方法中,采用粉末压片制样存在粒度效应和矿物效应等问题,但当样品在一定的粒度、压制压力及压制时间条件下,矿物效应和粒度效应仅仅对钠、钙等轻元素的测试有影响,而对钼、铜、铅等元素的测试并无影响。基于此本文建立了粉末压片制样波长色散XRF直接测定钼矿石中Mo、W、Cu、Pb、Zn、F、S、As、Bi等9种元素的方法。采用价格低廉的低压聚乙烯粉作衬垫镶边材料,样品在35 t的压力下压制30 s,制备的样片坚固光滑、吸潮性小,长期保存不发生形变,消除了粒度效应。选用自制的钼含量呈梯度变化的钼矿石样品及钼矿石、钨矿石、铜矿石、铅矿石、铋矿石、锌矿石等国家标准物质作为校准样品建立标准曲线,降低了矿物效应,采用经验系数法消除谱线重叠和基体干扰。本方相对标准偏差小于2.1%,各元素的测定结果与电感耦合等离子发射光谱法等其他方法测量值吻合。与已报道的玻璃熔融和粉末压片制样方法相比较,检出限较低,如钼的检出限为3.67 μg/g,比玻璃熔融法的检出限(450 μg/g或24 μg/g)要低得多;砷的检出限为1.13 μg/g,低于其他粉末压片法的检出限(7.8 μg/g)。本方法提出了克服粒度效应及光谱诸干扰因素影响的详细解决方案,有利于XRF法应用于定量分析基体组成复杂的钼矿石。 相似文献
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江西玉山石煤烧结包裹与钒转化的研究 总被引：7，自引：0，他引：7
江西玉山含钒石煤既是低热值能源,又是一种新类型钒矿资源。为充分利用这种资源,在600～1150℃下进行了氧化培烧和钠化焙烧,测定了煤灰的松装密度d和钒转化率η,研究厂烧结包裹作用。结果表明:温度升高,煤灰烧结严重,对钒包裹几率加大,钒转化率降低。石煤作为能源利用时,燃烧温度不宜超过950℃,石煤钠化焙烧提钒最佳温度775℃。在两种焙烧条件下的石煤烧结机理作了探讨,并进一步得出玉山石煤烧结与包裹的关系式。 相似文献
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东秦岭大别山段中酸性小岩体成矿规律研究 总被引：1，自引：0，他引：1
东秦岭大别山段矿化中酸性小岩体集中分布在秦岭钼（钨）成矿带东段,是我国重要的钼（钨）矿带之一。矿化中酸性小岩体多是受北北西向和北北东向断裂构造控制的复式杂岩体。形成环境从浅成—超浅成—深成相,Mo元素丰度由高—低,分为浅成—超浅成斑岩钼（铜）矿化、中—深成斑岩—矽卡岩型钼（钨、铜）矿化和浅成斑岩型钼矿化三种类型。小岩体主导的钼（铜）矿床具有明显的金属（元素）或矿物组份分带,表现为各带间金属元素含量递变及不同矿物组合按序析出,成矿物质主要来源于下地壳。 相似文献
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熔融制样X射线荧光光谱法测定铜矿石中16种主次量元素 总被引：1，自引：1，他引：0
铜矿石类型繁多,矿石赋存状态各异,成分复杂。在现有的铜矿石熔融制样X射线荧光光谱（XRF）分析方法中,选取标准物质个数和矿石类型少、分析范围宽,与实际样品类型相差太大,且制备的熔融片质量不高。本文选用铜含量既有良好浓度变化范围,又符合铜矿石常见含量的包括铜金银铅锌钼铜镍等各类矿石的24个标准物质,以四硼酸锂-偏硼酸锂-氟化锂为混合熔剂,熔剂与样品质量比为30：1,以溴化锂为脱模剂,改进样品预处理方式,将通常采用样品预氧化后或熔融中加入脱模剂的方式,改进为加入脱模剂后再用混合熔剂完全覆盖的方法制备了高质量的熔融片,建立了XRF测定铜矿石中铜锌铅硅铝铁钛锰钙钾镁钼铋锑钴镍16种元素的分析方法。分析铜矿石国家标准物质GBW 07164、GBW 07169,各元素的精密度（RSD）为0.1%~5.4%。分析国家标准物质GBW 07163（多金属矿石）、GBW 07170（铜矿石）的测定值与标准值相符;分析实际铜矿石样品,铜锌铅钼铋锑钴镍的测试结果与电感耦合等离子体发射光谱法和其他方法的测定值相符。本文方法扩大了基体的适应性,提高了实际应用价值。 相似文献
6.
陕南石煤储量大、分布广,开采和利用历史久远,因富含Se等微量元素而备受关注。为了研究陕南石煤中的元素对其分布区水中元素含量和富集程度的影响程度和影响机理,共采集并分析了岚皋县北部佐龙镇晚前寒武纪—早古生代石煤出露区和开采区的天然水样35个。研究结果表明:石煤分布区的水质大部分较好,参照国家生活饮用水标准(GB 5749—2006)和世界卫生组织饮用水卫生标准(WHO)可知适于饮用的水样占总水样的62.86%。其中以Se含量高为特征,有11个水样中的Se达到中国饮用天然矿泉水标准(GB8537—2018)规定的含量标准(10~50μg/L)。水样pH值为6.72~8.34,呈近中性或弱碱性;所有样品均为淡水,溶解性总固体平均值为39.22 mg/L;水化学类型主要以Ca-HCO3和Ca·Mg-HCO3为主;水化学成分主要受岩石风化控制,水中Se主要来源于石煤风化以及水-石煤相互作用导致的元素溶出,富硒石煤是当地水中Se元素的主要来源。 相似文献
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石灰岩山地淡竹林“岩石-土壤-植物”的元素分布与迁移积聚特征 总被引：1，自引：0，他引：1
本研究以石灰岩山地淡竹林为研究对象,测定了岩石、土壤和4种淡竹群落植物[优势种淡竹(Phyllostachys glauca),伴生种枸骨(Ilex cornuta)、油茶(Camellia oleifera)和胡颓子(Elaeagnus pungens）]的N、P、K、Ca、Mg、Fe、Al、Mn和Na等9种元素含量,对元素迁移积聚特征进行了分析,结果表明:（1）淡竹林石灰岩Ca含量高（363.09 g· kg-1）;土壤Ca含量下降至2.68 g·kg-1,Fe、Al含量升高（48.12 g·kg-1、84.00 g·kg-1）;与土壤相比,植物N、P和Ca含量上升,其他元素含量则降低;（2）从岩石到土壤,Ca为纯迁移,迁移积累系数仅为0.01;Fe和Al明显富集,迁移积累系数分别高达9.98和14.10;从土壤到植物,N、Ca、P为富集,Fe、Al生物吸收系数很低,仅为1.41和2.08;（3）除K外,群落优势种淡竹的元素含量和生物吸收系数均小于伴生种。研究发现,强淋溶作用下淡竹林石灰岩发育为酸性红石灰土,其生长的植物均非喜钙植物;“岩石—土壤—植物”元素迁聚特征因土壤发育过程和植物种间特征而异,红石灰土Ca积累少;淡竹对土壤元素需求少可能是其在石灰岩生境占据竞争优势的生理基础。 相似文献
10.
为系统研究石煤矿山周边耕地富硒土壤地球化学特征及影响因素,在浙江省常山县辉埠石煤矿山周边耕地采集了表层土壤样品144件、农产品甘蔗样20件、土壤垂向剖面土壤样6件、岩石样5件和地表水样3件。通过样品Se、有机质、As、Cd、Cu、Pb、Zn、Ni、Hg、Cr等元素含量指标测定和统计,探究了该区富硒土壤地球化学特征。结果表明:区内表层土壤硒含量主要集中于0.47~1.34 mg/kg之间,平均含量0.87 mg/kg,远高于浙江省平均值,且硒含量高值区与辉埠石煤矿的走向一致;硒含量随着土壤深度增加而逐渐下降;89.58%的土壤样品和65%的甘蔗样品达到富硒标准,但存在土壤和农产品Cd等主要重金属元素含量超标的生态风险。土壤硒含量均值在寒武系下统荷塘组最高(1.31 mg/kg),奥陶系中—下统最低(0.64 mg/kg);旱地硒均值略高于水田,但差异不显著(p>0.05);硒含量均值高低变化为粗骨土>石灰岩土>水稻土>红壤。研究认为,土壤硒含量受地质背景、土壤类型和有机质等因素的影响,含石煤层黑色岩系和碳酸盐岩等富硒地层是形成富硒土壤的主要因素,小部分与矿山开采等人类活动有关。 相似文献
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煤炭与铀两种资源在空间配置和成矿上有关联性,其合理开发利用及污染控制是我国国民经济和社会持续发展的重大需求。基于大量文献调研及前期研究成果,探讨了铀在煤中赋存分布及其在洗选、燃烧、淋滤过程中的迁移特征,取得一些认识:①煤中铀的富集成矿与成煤大地构造演化相关联,西南富铀煤主要与峨眉山玄武岩及断裂构造有关;西北富铀煤一般分布在拗陷和断拗陷盆地开阔地带一侧并与上覆砂岩型铀矿有关。②煤中铀主要与煤中有机质（主要是腐殖酸）结合,富铀煤中铀可以微细粒含铀矿物形式存在,并与有机硫、硫化物紧密共生,故在选煤过程中,无论重选还是浮选,其洗选脱除率均不高（最高为68.3%）,部分煤浮选时铀甚至富集到精煤中;在煤燃烧过程中,铀或多或少都会以气相形式挥发到大气中。③富铀煤一般也同时富集V、Mo、Se、Re、Cr等高价态变价元素,这与有机体深埋分解造成的强还原环境有关,对于那些不变价元素如Sc、Y、La等的沉淀富集主要与腐殖酸形成的酸化条件有关;这些共生组合元素,在富铀煤的分选及煤矸石的淋滤过程中表现出一致的迁移行为。④电厂燃煤过程中铀主要富集（呈数量级的增加）到飞灰和底灰中,粉煤灰中铀淋出浓度一般随淋滤液pH的增加呈降低趋势,其萃取率随灰化温度的升高呈现降低趋势。研究结果为铀资源利用和环境污染控制提供参考和依据。 相似文献
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运用电感耦合等离子体质谱仪（ICP-MS）和电感耦合等离子体发射光谱仪（ICP-AES）分别对普安-晴隆矿区晚二叠世C17、C19、C22和C26号煤层中8个煤样和7个煤灰样进行微量元素含量的测试分析。结果表明,煤及煤灰中明显富集Li、Sc、V、Cr、Co、Ge、As、Nb、Mo、W、U等元素,且各元素在煤灰中更加富集,Nb、Zr、V、Ga和U等伴生金属元素的含量基本达到或超过了对应元素的边界品位或最低工业品位。煤中伴生元素的富集成因研究表明,V、Cr、Co、Nb和Zr等元素的富集主要受物源区峨眉山玄武岩风化碎屑物质供给的控制;U、S、Mo等元素的有限富集与海水作用有关;而受成煤期同沉积火山灰沉降的影响,煤中Li、Nb、Zr、Mo和U等微量元素表现出一致富集的特点;成煤期后的低温热液作用,使得各煤层,尤其是底部煤层（C19、C26）明显富集As、Mo、U和W等元素。综合分析认为,成煤期同沉积的火山灰沉降和成煤期后的低温热液作用是普安-晴隆矿区晚二叠世煤中伴生元素异常富集的主控地质因素。 相似文献
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《International Journal of Coal Geology》2005,61(3-4):141-196
The review presented covers: (a) historical introduction; (b) some analytical comments; (c) some peculiarities of the As geochemistry in environment; (d) an estimation of coal Clarke value of As; (e) some coals enriched in As; (f) mode of As occurrence in coal; (g) factors influencing the As distribution in coal matter and coal bed; (h) genetic topics; (i) some topics related to environmental impact of As by the coal combustion.The World average As content in coals (coal Clarke of As) for the bituminous coals and lignites are, respectively, 9.0±0.8 and 7.4±1.4 ppm. On an ash basis, these contents are higher: 50±5 and 49±8 ppm, respectively. Therefore, As is a very coalphile element: it has strong affinity to coal matter — organic and (or) inorganic but obligatory authigenic. The coalphile affinity of As is like that for Ge or S.There is strong regional variability of As distribution due to geologic variability of the individual coal basins. For example, bituminous coals in Eastern Germany, Czech Republic and SE China are enriched in As, whereas the coals in South Africa or Australia are very depleted compared to coal Clarke of As. In general, some relationship exists between As content and its mode of occurrence in coals. Typically, at high As content, sulphide sites dominate (pyrite and other more rare sulphides), whereas at low As content, Asorg dominates, both being authigenic. A contribution of the terrigenic As (in silicates) is usually minor and of the biogenic Asbio (derived from coal-forming plants) is poorly known.Both organic and inorganic As can exist not only as chemically bound form but also in the sorbed (acid leacheable) arsenate form. With increasing coal rank, sorbed exchangeable arsenate content decreases, with a minimum in the coking coals (German data: the Ruhr coals).Relations of As content in coal to ash yield (or its partitioning in sink–float fractions) and to coal petrographic composition are usually complicated. In most cases, these relations are controlled by main site (form) of As — Aspyr or Asorg. If Aspyr dominates, an As accumulation in heavy fractions (or in high-ash coals) is observed, and if Asorg dominates, it is enriched in medium-density fractions (or low- and medium-ash coals). Arsenic is in part accumulated in the inertinite vs. vitrinite (Asorg ?).There are four genetic types of As accumulation on coal: two epigenetic and two syngenetic: (1) Chinese type—hydrothermal As enrichment, sometimes similar to known Carlin type of As-bearing telethermal gold deposits; (2) Dakota type—hypergene enrichment from ground waters draining As-bearing tufa host rocks; (3) Bulgarian type—As enrichment resulting from As-bearing waters entered coal-forming peat bogs from sulphide deposit aureoles; (4) Turkish type—volcanic input of As in coal-forming peat bog as exhalations, brines and volcanic ash.During coal combustion at power plants, most of the initial As in coal volatilizes into the gaseous phase. At the widely used combustion of pulverized coal, most of Asorg, Aspyr and “shielded” As-bearing micromineral phases escape into gaseous and particulate phase and only minor part of Asclay remains in bottom ash. The dominant fraction of escaping As is in fly ash. Because 97–99% of the fly ash is collected by electrostatic precipitators, the atmospheric emission of As (solid phase and gaseous) is usually assumed as rather minor (10–30% from initial As in coal). However, fly ash disposal creates some difficult environmental problems because it is potentially toxic in natural waters and soils. The As leaching rate from ash disposal is greatly controlled by the ash chemistry. In natural environment, As can be readily leached from acid (SiO2-rich) bituminous coal ashes but can be very difficult from alkali (CaO-rich) lignite ashes.If the Aspyr form dominates, conventional coal cleaning may be an efficient tool for the removing As from coal. However, organic-bound or micromineral arsenic (“shielded” grains of As-bearing sulphides) are not removed by this procedure.Some considerations show that “toxicity threshold” of As content in coal (permissible concentration for industrial utility) may be in the range 100–300 ppm As. However, for different coals (with different proportions of As-forms), and for different combustion procedures, this “threshold” varies. 相似文献
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M. Ishaq F. Akbar Jan M. Shakirullah I. Ahmad Hina Ali 《Arabian Journal of Geosciences》2013,6(11):4109-4118
In the present study, coal from Chakwal (Pakistan) was leached with an aqueous solutions of iodine monochloride (ICl) and diethylenetriamine pentaacetic acid (DPTA) of different concentrations. The effect of stirring time, concentration and pH was studied on the leaching of different metals from coal. The physicochemical parameters indicated that the coal was of reasonably good quality. The results indicated that with increase in time duration, the extraction of metals increased. In most of the cases, metal concentration increased in the leachate with increasing the concentration of the leaching agents. DPTA was found to be the best leaching agent for most of the metals. Higher extraction of metals from coal fly ash indicated that coal organic matter has a pronounced effect on the leaching. Higher concentration of metals was extracted from virgin coal and coal fly ash at low pH (p?>?0.00) as compared to high pH. DPTA extracted metals in higher concentration from virgin coal and coal fly ash at low pH as compared to ICl. Based on the present study, the most leached metals were Fe, Cu, Mn and the least were Pb, Ni, Cd and Cr. 相似文献
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Leaching processes are believed to be responsible for the unusually low-ash content (sometimes less than 1%) of the thick (up to 35 m) Cretaceous coals located in the Greymouth coalfield, South Island, New Zealand. Although leaching of inorganics in peat is a generally accepted process, little is known about leaching after burial. The “Main” and “E” seams in the Greymouth coalfield show good correlation between low ash and bed thickness. The ash content, however, is often less than 1%, which is lower than most known modern analogues (i.e. peat). There are several lines of evidence that suggest that mineral matter may have been removed from the coal not only in the peat stage but also after burial. For example, etching features found in quartz grains and clay aggregates indicate that some leaching processes have taken place. In addition, liptinitic material (e.g., bitumen) in the cleat networks supports the conclusion that there has been some movement of solutions through the coal after burial. These solutions may have helped to remove some of the inorganics originally within the Greymouth coals. 相似文献
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The major element and Sr isotope systematics and geochemistry of coal fly ash and its interactions with environmental waters were investigated using laboratory flow-through column leaching experiments (sodium carbonate, acetic acid, nitric acid) and sequential batch leaching experiments (water, acetic acid, hydrochloric acid). Column leaching of Class F fly ash samples shows rapid release of most major elements early in the leaching procedure, suggesting an association of these elements with soluble and surface bound phases. Delayed release of certain elements (e.g., Al, Fe, Si) signals gradual dissolution of more resistant silicate or glass phases as leaching continues. Strontium isotope results from both column and batch leaching experiments show a marked increase in 87Sr/86Sr ratio with continued leaching, yielding a total range of values from 0.7107 to 0.7138. For comparison, the isotopic composition of fluid output from a fly ash impoundment in West Virginia falls in a narrow range around 0.7124. The experimental data suggest the presence of a more resistant, highly radiogenic silicate phase that survives the combustion process and is leached after the more soluble minerals are removed. Strontium isotopic homogenization of minerals in coal does not always occur during the combustion process, despite the high temperatures encountered in the boiler. Early-released Sr tends to be isotopically uniform; thus the Sr isotopic composition of fly ash could be distinguishable from other sources and is a useful tool for quantifying the possible contribution of fly ash leaching to the total dissolved load in natural surface and ground waters. 相似文献
17.
Geochemical and mineralogical anomalies of the late Permian coal in the Zhijin coalfield of southwest China and their volcanic origin 总被引：2，自引：0，他引：2
Shifeng Dai Deyi Ren Xiaoqiang Hou Longyi Shao 《International Journal of Coal Geology》2003,55(2-4):117-138
This paper describes the influence of volcanic ash on the concentrations and occurrences of associated elements in coal in the Zhijin Coalfield in western Guizhou Province, China. Our studies reveal that the No. 9 coal seam in the Zhijin Coalfield has very high content of Fe (4.34%), Cu (369.90 μg/g), U (49.6 μg/g), Mo (63.10 μg/g), Zn (33.97 μg/g), and Zr (841.80 μg/g). The studies have also found that elements, such as Fe and Cu, do not occur as sulfides in this coal seam, in sharp contrast to many other coal seams in China. The geochemical and mineralogical anomalies of the coal seam are attributed to synsedimentary volcanic ash. In addition to normal macerals and minerals in coal, a volcanic-influenced material (VIM) derived from volcanic ash, detrital material of terrigenous origin and organic matter was identified under polarized-light reflectance microscopy and scanning electron microscopy equipped with energy-dispersive X-ray (EDX) analyzer. The volcanic-influenced material is the main carrier of the above elements in this coal. Six types of the volcanic-influenced material (VIM-1, VIM-2, VIM-3, VIM-4, VIM-5, and VIM-6) are further distinguished on the basis of their structures and compositions. To the best of our knowledge, this is the first report that presents a detailed classification of coal components with a high content of volcanic ash. 相似文献
18.
Contamination of the environmental ecosystems by trace elements from mining activities of Badao bone coal mine in China 总被引：5，自引：0，他引：5
Bone coal, as a main mining object, can be used by local inhabitants as daily fuel and by local industrial enterprises as industrial fuel in Pinglin County, Shaanxi Province, China. This study reports how the environmental ecosystems have been polluted around the Badao bone coal mine. Geochemical samples (e.g. rock, water, soil, edible plant and animal) were collected. Bone coal from the Badao mine contains Se up to 75 µg/g Se and 28 µg/g Se in ashes after its combustion, with higher contents of other trace elements. Bone coal and its ash seem to be the main geochemical source of trace elements in soils and plants, which may cause contamination of the local environmental ecosystems. Three ways by which soils have been contaminated by these trace elements derived from bone coal are proposed in this paper. Radishes and beans have the ability to accumulate Mo and Se from soils. There is no obvious difference in concentrations of Cu, Cr and F in each plant from the two areas. 相似文献
19.
石煤是一种可综合利用的矿产资源,提取石煤中钒、钼、镍等金属是其综合利用之一.石煤在发电燃烧过程中钒的物相发生显著变化,而钒物相的变化对钒的可浸出性产生较大的影响.笔者采用选择性连续提取方法对四川某地石煤原矿和石煤飞灰进行分析研究,发现石煤原矿中钒主要存在于硅铝酸盐相和有机质相中,部分存在于铁锰氧化物相及吸附态中,极少部分存在于碳酸盐相中.而石煤发电飞灰中钒主要存在于有机质相、硅铝酸盐相和铁锰氧化物相中,少量的钒以吸附态形式赋存.燃烧过程中石煤的各种含钒矿物发生离解,其中的钒得到释放并被氧化成高价态.高价钒一部分与Na、Cl等结合生成可溶性化合物,形成吸附态的钒;另一部分与Fe、Na、Ca等发生反应生成难溶性化合物,并以一定形式富集在飞灰的有机质相、硅铝酸盐相和铁锰氧化物相中. 相似文献
20.
Recent researches on Au in coal ash were summarized in this paper, including the distribution law and the migration rule of gold in coal ash, as well as the influencing factors on volatility and use feasibility of Au in the progress of coal combustion. Au content in coal ash is much higher than that in the raw coal in most cases worldwide, only a small number of opposite cases are found in certain places. Occurrence of Au in coal, geological-geochemical environment of coal-forming and combustion conditions are the main factors controlling the volatility of gold in coal combustion, while the occurrence of Au in coal dominates the redistribution of Au. Through preliminary calculation, gold in coal ash is expected to have a considerable utilization potential in the southwestern Guizhou Province. 相似文献