Pappu Asokan, Saxena Mohini, Asolekar Shyam R
Regional Research Laboratory (CSIR), Habib Ganj Naka, Bhopal-462026, India.
Sci Total Environ. 2006 Apr 15;359(1-3):232-43. doi: 10.1016/j.scitotenv.2005.04.024. Epub 2005 Jun 22.
During metallic zinc extraction from zinc sulphide or sulphide ore, huge quantity of jarosite is being released universally as solid residues. The jarosite mainly contains iron, sulphur, zinc, calcium, lead, cadmium and aluminium. Jarosite released from such industrial process is complex and its quality and quantity make the task more complex for safe disposal. Apart from water contamination, jarosite already accumulated and its increasing annual production is a major source of pollution for surrounding environment including soil, vegetation and aquatic life and hence its disposal leads to major concern because of the stringent environmental protection regulations. An attempt was made to evaluate the characteristics of Indian jarosite with an objectives to understand its potentials for recycling and utilising as raw materials for developing value added products. Sand and Coal Combustion Residues (CCRs) was used as an admixture to attain good workability and detoxify the toxic substance in the jarosite. Result revealed that jarosite is silty clay loam in texture having 63.48% silt sized and 32.35% clay sized particles. The particle size of jarosite (D90=16.21+/-0.20 microm) is finer than the CCRs (D90=19.72+/-0.18 microm). The jarosite is nonuniform in structure and shape as compared to the CCRs having spherical, hollow shaped and some of them are cenosphere in nature. The major mineral phase of jarosite is Potassium Iron Sulphate Hydroxide {KFe3(SO4)2(OH)6}and Iron Sulphate Hydrate {2 Fe2O3SO3 x 5 H2O}. In CCRs the dominant phases are quartz {SiO2}, mullite {3 Al2O3 x 2 SiO2} and hematite {Fe2O3}. The high electrical conductivity of jarosite (13.26+/-0.437 dS/m) indicates that the presence of cations and anions are predominant over CCRs (0.498+/-0.007 dS/m). The major portion of jarosite consists of iron (23.66+/-0.18%), sulphur (12.23+/-0.2%) and zinc (8.243+/-0.075%). But CCRs main constituents are silicon (27.41+/-0.74%), aluminium (15.167+/-0.376%) and iron (4.447+/-0.69%). The other constituents such as calcium, aluminium, silicon, lead, and manganese are also present in the range of 0.5 to 5%. Heavy metals such as copper, chromium, and cadmium are found higher in jarosite as compared to the CCRs. The statistically designed experimental trials revealed that the density, water absorption capacity and compressive strength of fired jarosite bricks are 1.51 gm/cm3, 17.46% and 43.4 kg/cm2 respectively with jarosite sand mixture in the ratio of 3:1 indicating the potentials in developing building materials.
在从硫化锌或硫化矿中提取金属锌的过程中,大量的黄钾铁矾作为固体残渣被普遍排放。黄钾铁矾主要含有铁、硫、锌、钙、铅、镉和铝。这种工业过程中产生的黄钾铁矾成分复杂,其质量和数量使得安全处置的任务更加复杂。除了水污染外,已经积累的黄钾铁矾及其年产量的增加是包括土壤、植被和水生生物在内的周边环境的主要污染源,因此,由于严格的环境保护法规,其处置成为主要问题。本研究旨在评估印度黄钾铁矾的特性,以了解其回收利用潜力,并作为开发增值产品的原材料。使用砂和煤燃烧残渣(CCRs)作为掺合料,以获得良好的工作性能并去除黄钾铁矾中的有毒物质。结果表明,黄钾铁矾质地为粉质粘壤土,粉粒含量为63.48%,粘粒含量为32.35%。黄钾铁矾的粒径(D90=16.21±0.20微米)比CCRs(D90=19.72±0.18微米)更细。与具有球形、空心形状且部分为空心微珠的CCRs相比,黄钾铁矾的结构和形状不均匀。黄钾铁矾的主要矿物相是硫酸钾铁氢氧化物{KFe3(SO4)2(OH)6}和硫酸铁水合物{2 Fe2O3SO3 x 5 H2O}。在CCRs中,主要相是石英{SiO2}、莫来石{3 Al2O3 x 2 SiO2}和赤铁矿{Fe2O3}。黄钾铁矾的高电导率(13.26±0.437 dS/m)表明其阳离子和阴离子的含量高于CCRs(0.498±0.007 dS/m)。黄钾铁矾的主要成分是铁(23.66±0.18%)、硫(12.23±0.2%)和锌(8.243±0.075%)。但CCRs的主要成分是硅(27.41±0.74%)、铝(15.167±0.376%)和铁(4.447±0.69%)。其他成分如钙、铝、硅、铅和锰的含量也在0.5%至5%之间。与CCRs相比,黄钾铁矾中铜、铬和镉等重金属含量更高。统计设计的实验试验表明,黄钾铁矾烧制砖与砂的混合比例为3:1时,其密度、吸水能力和抗压强度分别为1.51克/立方厘米、17.46%和43.4千克/平方厘米,表明其在开发建筑材料方面具有潜力。