...
首页> 外文期刊>RMZ/Materials and Geoenvironment >CHEMICAL COMPOSITION AND LEACHING OF ASH FROM ASH REPOSITORY PILE OF TRBOVLJE COAL FIRED PLANT IN SLOVENIA
【24h】

CHEMICAL COMPOSITION AND LEACHING OF ASH FROM ASH REPOSITORY PILE OF TRBOVLJE COAL FIRED PLANT IN SLOVENIA

机译:斯洛文尼亚TRBOVLJE煤制火电厂烟灰储存桩中灰分的化学组成和浸出

获取原文
获取原文并翻译 | 示例
   

获取外文期刊封面封底 >>

       

摘要

In the paper the influence on the environment of the ash from the ash repository pile of the Trbovlje coal-fired plant in Slovenia is described. The repository is located in the small valley of Prapreski graben which extends NNE of the Trbovlje power plant. The pile is situated in the medium, relatively gentle sloping part of the valley on Triassic dolomite. The rock is tectonically intensely fractured and permeable. The final capacity of the repository pile is about 12 million cube metres. The slopes of the pile have been revegetated. The surface is covered with a 30 cm thick layer of soil. On it grow orchard trees and clover. In the power plant mostly coal from brown coal pits in Zasavje in Slovenia is fired. Yearly about 280,000 tons of ash are deposited on the repository pile. From the repository pile 11 samples of ash of various ages were collected. Ash samples have been crushed and sieved to -0,063 mm powder. Leaching of ash was carried out by two procedures, by column leaching experiments, and by shake leaching. In the experiment three ash samples from the pile were used: sample 101 (flesh material), 107 (material approx. 10 years old), and 104 (approx. 20 years old), and one sample 112, of fresh fly ash from the electrostatic precipitator, before its contact with water or slag. The amounts of ash and distilled water in leaching tests were deliberately chosen. The glass column was filled with 100 g of ash and washed with distilled water. The ash was permeable for water. Silica wool at the bottom of the column prevented the passing of ash into the leachate. Each 100 ml of leached liquid represent one sample of leachate. In total through the column about 1000 ml of distilled water was passed for each ash sample, and 10 samples of leachate were obtained. In the investigation of adsorption of metals on ash, sample 101 was prepared in the same way as described above, and leached with solutions which contained each 200 mg/l of Cr(III), Cu and Cd in ionic form. Each 100 ml of eluate represented one sample. In a larger closed glass vessel 50 g ash in 1000 ml distilled water were shaken. In distinct time intervals (1 hour, 4 hours, 8 hours, 1 day, 14 days and 30 days) 100 ml of liquid were removed for analysis. In samples of ash Al, Mg, Mn, Ti, Ga, V, and Zr were determined with optical emission spectroscopy (OES), Ca, Fe, Na, Ag, As, Au, Ba, Br, Ce, Cs, Eu, Hf, Ir, Lu, Mo, Nd, Rb, Sb, Sc, Se, Sm, Ta, Tb, Th, U, Yb and W with instrumental neutron activation analysis (INAA), Cu, Pb and Zn with DCP ES, and Hg with flameless atomic absorption spectrometry (AAS). Contents of oxides of major elements in ash were determined with wet chemical analysis. In leachates of ash were determined pH, Ca, Na and K with flame photometry, Cd, Cr, Cu and Zn with AAS, and cyanides with amperometric method. Quality control of analytical methods was carefully carried out. Accuracy of analytical methods was monitored with blind determinations of geological standards, and is considered acceptable. Precision is passable for all chemical analysis. Chemical composition of power plant ash from the repository pile is very similar to the composition of ash of coal from Zasavje collieries Trbovlje (Tab. 1). Ranges of major element oxides in examined ash samples are given in Slovenian text. Means of 5 determinations of ash samples are 13 mg/g U and 19 mg/g Th. Emission of radon at the repository pile was estimated to be 4,000 Bq/m~3. Concentration of radon in air rapidly decreases with distance from the pile, and reaches at several hundred meters the natural background. The aim of leaching experiments of ash was the assessment of the influence of ash from the repository pile of power plant ash on surface and ground water. With leaching on the column conditions of percolating water through the repository pile can be simulated. As shown by experiments (Fig. 1, Tab. 2 and 3), in normal conditions no appreciable short term influence on waters can be expected beside
机译:在本文中,描述了斯洛文尼亚Trbovlje燃煤电厂的灰烬堆放对灰烬环境的影响。该储存库位于Prapreski抓斗的小山谷中,该山谷延伸了Trbovlje电厂的NNE。该桩位于三叠纪白云岩中中等偏斜的山谷部分。岩石在构造上强烈破裂并具有渗透性。储存库堆的最终容量约为1200万立方米。堆的斜坡已重新植被。表面覆盖着30厘米厚的土壤层。在它上面种有果园树和三叶草。在发电厂中,斯洛文尼亚Zasavje的褐煤坑中的大部分煤被烧掉。每年约有28万吨的灰分沉积在储存堆中。从储存库堆中收集了11个不同年龄的灰分样品。灰分样品已被粉碎并过筛为-0,063 mm粉末。灰分的浸出通过两种方法进行,即通过柱浸出实验和通过摇动浸出。在该实验中,使用了来自堆的三个灰烬样品:样品101(肉质材料),107(材料约10年的历史)和104(约20年的历史),以及一个样品112,来自粉煤灰的新鲜粉煤灰。静电除尘器,在与水或炉渣接触之前。故意选择浸出试验中的灰分和蒸馏水量。玻璃柱中装满100克灰烬,并用蒸馏水洗涤。灰烬是水可渗透的。塔底部的硅胶防止了灰分进入渗滤液。每100毫升浸出的液体代表一个渗滤液样品。每个灰分样品总共通过该柱约1000 ml的蒸馏水,并获得10个渗滤液样品。在研究金属在灰烬上的吸附时,以与上述相同的方式制备样品101,并用溶液浸出,该溶液分别含有200 mg / l的离子形式的Cr(III),Cu和Cd。每100毫升洗脱液代表一个样品。在一个更大的密闭玻璃容器中,将50克灰分溶解在1000毫升蒸馏水中。在不同的时间间隔(1小时,4小时,8小时,1天,14天和30天)中,取出100毫升液体进行分析。在灰分的样品中,通过光发射光谱法(OES)测定了Al,Mg,Mn,Ti,Ga,V和Zr中的Ca,Fe,Na,Ag,As,Au,Ba,Br,Ce,Cs,Eu,使用仪器中子活化分析(INAA)的Hf,Ir,Lu,Mo,Nd,Rb,Sb,Sc,Se,Sm,Ta,Tb,Th,U,Yb和W,使用DCP ES的Cu,Pb和Zn汞的无焰原子吸收光谱法(AAS)。用湿化学分析法测定灰分中主要元素的氧化物含量。用火焰光度法测定灰分的沥出液中的pH,Ca,Na和K,采用AAS测定镉,Cr,Cu和Zn,采用安培法测定氰化物。认真进行分析方法的质量控制。分析方法的准确性通过对地质标准的盲目确定进行监控,被认为是可以接受的。所有化学分析的精度都是可以接受的。储存堆中发电厂灰分的化学成分与Zasavje煤矿Trbovlje(表1)的煤灰成分非常相似。斯洛文尼亚教科书中给出了灰分样品中主要元素氧化物的范围。 5次灰分测定的平均值为13 mg / g U和19 mg / g Th。储存堆中of的排放估计为4,000 Bq / m〜3。空气中ra的浓度随与堆的距离的增加而迅速降低,并达到自然背景的数百米。灰分浸出实验的目的是评估电厂灰堆中灰分对地表水和地下水的影响。通过对柱子的浸提,可以模拟渗水通过储层堆的情况。如实验所示(图1,表2和3),在正常条件下,除了水,短期内不会有明显的影响。

著录项

相似文献

  • 外文文献
  • 中文文献
  • 专利
获取原文

客服邮箱:kefu@zhangqiaokeyan.com

京公网安备:11010802029741号 ICP备案号:京ICP备15016152号-6 六维联合信息科技 (北京) 有限公司©版权所有
  • 客服微信

  • 服务号