Unlü K, Haskök S
Department of Environmental Engineering, Middle East Technical University, Ankara-Turkey.
Waste Manag Res. 2001 Jun;19(3):217-28. doi: 10.1177/0734242X0101900304.
Developing treatment and disposal strategies and health-based clean-up standards for chromium containing wastes continues to be an important environmental regulatory issue because of the opposing solubility and toxicity characteristics of chromium species under diverse environmental conditions. In this study, leaching characteristics of total Cr and Cr(VI) were investigated using laboratory column studies. The data obtained from the experimental studies were analysed to assess the treatability of chromite ore processing waste (COPW) by leaching and to identify the leaching strategies that enhance mass removal rates of chromium species. COPW used for laboratory soil column studies was obtained from an industrial plant producing sodium chromate in Mersin, Turkey. Laboratory investigations involved chemical characterisation of waste material and column studies. For waste characterisation, U.S. EPA toxicity characterisation leaching procedure (TCLP) was performed on COPW to determine the concentrations of metal species in the TCLP extract. For column studies, various laboratory columns containing plain COPW material, 1:1 COPW/reducing agent (elemental iron or manure) mixture and different type soils (sand, loam and clay) overlain by COPW were subjected to leaching tests using acidic, neutral and alkaline influent water to determine Cr mass leaching efficiencies. Based on the TCLP analyses, COPW is classified as hazardous waste. As a result of comparing the leaching efficiency data from twelve leaching columns, the maximum removal of total Cr was achieved by leaching COPW/manure mixture using acidic (pH 4.78) influent water. The highest Cr(VI) leaching efficiency was achieved in the columns of plain COPW and COPW/manure mixture using highly alkaline (pH 12.0) influent water. The least effective leaching efficiency for both total Cr and Cr (VI) was obtained by leaching plain COPW with neutral (pH 7.0) influent water. Land-disposal of the treated COPW material by mixing with clayey soils seems to be a viable alternative.
由于铬物种在不同环境条件下具有相反的溶解性和毒性特征,因此制定含铬废物的处理与处置策略以及基于健康的清理标准仍然是一个重要的环境监管问题。在本研究中,通过实验室柱实验研究了总铬和六价铬的浸出特性。对实验研究获得的数据进行分析,以评估铬铁矿加工废料(COPW)的可浸出处理性,并确定提高铬物种质量去除率的浸出策略。用于实验室土壤柱研究的COPW取自土耳其梅尔辛一家生产铬酸钠的工厂。实验室研究包括废料的化学表征和柱实验。对于废料表征,对COPW进行了美国环保署毒性特性浸出程序(TCLP),以确定TCLP提取物中金属物种的浓度。对于柱实验,对各种装有纯COPW材料、1:1 COPW/还原剂(元素铁或粪肥)混合物以及不同类型土壤(砂、壤土和粘土)且覆盖有COPW的实验室柱,使用酸性、中性和碱性进水进行浸出试验,以确定铬的质量浸出效率。根据TCLP分析,COPW被归类为危险废物。通过比较12个浸出柱的浸出效率数据,使用酸性(pH 4.78)进水浸出COPW/粪肥混合物可实现总铬的最大去除。使用高碱性(pH 12.0)进水时,纯COPW柱和COPW/粪肥混合物柱实现了最高的六价铬浸出效率。用中性(pH 7.0)进水浸出纯COPW时,总铬和六价铬的浸出效率最低。将处理后的COPW材料与粘性土壤混合进行土地处置似乎是一种可行的选择。