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水泥窑共处置含Cr废物中Cr在不同温度下的形态转化
引用本文:范兴广,杨玉飞,黄启飞,李忠武,于泓锦.水泥窑共处置含Cr废物中Cr在不同温度下的形态转化[J].环境科学研究,2014,27(3):272-278.
作者姓名:范兴广  杨玉飞  黄启飞  李忠武  于泓锦
作者单位:1.湖南大学环境科学与工程学院, 湖南 长沙 410082
基金项目:国家自然科学基金项目(51178439)
摘    要:将Na2CrO4加入生料中模拟含Cr入窑物料〔掺加比例为0.048%(以w计)〕,以探索水泥窑共处置含Cr废物过程中Cr的形态转化. 将含Cr入窑物料在不同温度条件下进行煅烧,消解煅烧样品以分析Cr在不同温度下的残留率并利用XANES(X射线吸收近边结构光谱)技术分析煅烧样品中Cr的存在形态. 结果表明:对应900、1000、1100、1200、1300和1450℃煅烧条件下,熟料中Cr的残留率分别为88.2%、70.7%、73.7%、67.2%、69.5%和67.8%. 由于窑尾温度为1050~1100℃,并且Cr的残留率在1100℃较高,因此从窑尾添加含Cr废物可以减少水泥窑共处置含Cr废物过程中的Cr逸放. 在900~1450℃煅烧条件下,所有样品中的Cr主要以CrO3、Cr2O3和CaCrO4的形式存在. 1000℃煅烧温度下存在K2Cr2O7,但不存在K2CrO4;900℃和1100~1300℃煅烧温度下有K2CrO4存在,但不存在K2Cr2O7. 1100~1450℃煅烧温度下,Cr元素进入到水泥熟料的主要矿物中,并主要以CrO3和Cr2O3的形式与其他物质结合生成了较为复杂的Ca4A16O12CrO4、Ca6Al4Cr2O15等. 

关 键 词:水泥窑共处置    XANES(X射线吸收近边结构光谱)    重金属    形态转化
收稿时间:2013/7/26 0:00:00
修稿时间:2013/10/30 0:00:00

Form Transformation of Cr during Co-Processing Waste Contained Cr in Cement Kiln at Different Temperatures
FAN Xing-guang,YANG Yu-fei,HUANG Qi-fei,LI Zhong-wu and YU Hong-jin.Form Transformation of Cr during Co-Processing Waste Contained Cr in Cement Kiln at Different Temperatures[J].Research of Environmental Sciences,2014,27(3):272-278.
Authors:FAN Xing-guang  YANG Yu-fei  HUANG Qi-fei  LI Zhong-wu and YU Hong-jin
Institution:1.College of Environmental Science and Engineering, Hunan University, Changsha 410082, China2.Research Institute of Solid Waste Management, Chinese Research Academy of Environmental Sciences, Beijing 100012, China
Abstract:In orde to discover the form migration of Cr during co-processing hazardous wastes contained Cr,Na2CrO4was added to the raw material simulation Cr-containing material into the kiln (the mixing ratio is 0.048%(w)). The raw material mixing with Na2CrO4was calcined at different temperatures. The residual rate of Cr was studied by digestion of samples calcined. The chemical forms of Cr were obtained by X-ray absorption near edge structure (XANES). The results showed that, the conditions of Cr clinker residual rates were 88.2%, 70.7%, 73.7%, 67.2%, 69.5% and 67.8% at temperatures of 900-1450℃. The kiln tail of temperature was 1050-1100℃ and was closed to 1100℃, at the temperature of 1100℃. Therefore, it reduced the disposal of Cr during co-processing waste in the cement kiln adding waste at the kiln tail. Cr mainly existed in the forms of CrO3,Cr2O3and CaCrO4under the conditions of 900-1450℃. In addition, K2Cr2O7was produced under the condition of 1000℃ and K2CrO4was produced under the conditions of 900,0,1200and 1300℃. Cr entered into the main cement mineral combined with other substances to generate more complex Cr-containing substances such as Ca4Al6O12CrO4and this material was mainly in the form of CrO3and Cr2O3under the ranges from 1100℃ to 1450℃. 
Keywords:cement kiln co-processing  X-ray absorption near edge structure(XANES)  heavy metal  form transformation
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