煤矸石的环境问题及其资源化利用

煤矸石是煤炭生产中的一种副产品,目前煤矿的排矸量约占煤炭开采量的10%~25%,煤矸石已成为我国累积堆积量和占用场地最多的工业废物。文中介绍了国内外煤矸石综合利用现状及工程利用的主要领域,并就如何提高我国煤矸石工程利用水平提出作者的观点。      

溴酸钾—酸性铬红—CTMAB动力学光度法测定硒的研究

根据痕量硒（Ⅳ）对溴酸钾氧化酸性铬红的褪色催化作用,建立了一种测定硒的新方法。检出限为4μg／L,硒的含量在20～240μg／L内符合比耳定律。方法用于食品中硒的测定,结果满意。     

铬渣浸出毒性试验研究

铬渣给环境带来的危害一直困扰着铬盐行业的发展 ,其浸出毒性研究有利于对铬渣危害的监测评估、治理及综合利用。本试验对新渣和陈渣的浸出毒性进行了探讨 ,同时对铬渣中Cr(Ⅵ )进行全量溶取 ,并分析铬渣中主要阴、阳离子的浸出行为。从而提出适宜于评价铬渣浸出毒性的试验方法 ,即 :液固比 2 0∶1,浸取时间 8h、提取剂为HAC NaAC(pH5 0± 0 2 ) ,粒径为 12 0目的浸出体系     

铬天青S-铝(Ⅲ)-聚乙二醇4000体系的共振散射光谱及其应用

在pH5 0的NaAc HAc缓冲溶液及非离子表面活性剂聚乙二醇 40 0 0存在下 ,铬天青S与铝 (Ⅲ )形成络合物微粒体系 ,在 40 0nm和 5 30nm处出现两个较强的共振散射峰 .共振散射光强度与Al(Ⅲ )的浓度在 0 0 84— 0 84μg·ml- 1 范围内呈良好的线性关系 ,考察了适宜的反应条件及共存物质的影响 .建立了一个共振散射光谱测定水中Al的方法 ,其结果与分光光度法一致 .     

化学法处理高浓度电镀废水

分析、总结了采用化学法处理高浓度电镀废水中的含氰废水、含镍废水、含铬废水和含酸废水的工程设计、调试和实际运行情况。实践表明,化学法处理高浓度电镀废水是行之有效的,而用PH／ORP计控制好废水处理中的化学反应是稳定运行的关键。     

铬渣制取铬黄淋滤液中过量铅离子的去除研究

用累托石做吸附剂来处理铬渣淋滤液制铬黄过程中产生的过量Pb^2-。当pH为5．6～7．3,反应时间90min,吸附剂与水量比为24g／L.pbe^2 浓度由2．5mg／L降到0．05mg／L,Pb^2 的去除率最高可达98％,外排废水符合GB8978—1996一级标准。     

Stabilization effects of surplus soft clay with cement and GBF slag

Utilization of industrial waste and surplus construction soft clay as construction material was recommended, and many attempts at geotechnical waste utilization were undertaken. This study aimed at the application of cement and a kind of industrial wastes, i.e. granulated blast furnace slag, on stabilization of surplus soft clay. The results showed that the cement and slag can successfully stabilize Ariake clays even though this high organic clay fails to be stabilized by lime and cement. Addition of slag in cement for stabilization induces higher strength than cement alone for longer curing time. The application of the cement with slag is more suitable than cement alone for stabilization because of economical consideration.     

炼钢精炼渣气固碳酸化反应吸附CO2

采用炼钢精炼渣,通过气固碳酸化反应吸附CO₂,考察了不同吸附温度下精炼渣对纯CO₂和模拟高炉煤气中CO₂的吸附能力。实验结果表明：吸附温度对精炼渣吸附CO₂反应有显著的影响,升高温度可以提高精炼渣对CO₂的吸附能力;在400 ℃时,精炼渣吸附纯CO₂和模拟高炉煤气中CO₂的量分别为4.7 mg/g和9.8 mg/g;吸附温度升高到500 ℃和550 ℃时,精炼渣对纯CO₂的吸附能力强于高炉煤气中CO₂;在550 ℃时,精炼渣吸附纯CO₂和模拟高炉煤气中CO₂的量达到最高,分别为14.7 mg/g和12.9 mg/g。     

钢渣对水体中磷的去除性能及机制解析

针对不同类型钢渣在除磷过程中存在的显著差异,以电炉渣为研究对象,探讨了环境因素（吸附时间、吸附温度）对钢渣除磷的影响,验证了其对磷酸盐、焦磷酸盐及实际水体的除磷效果,联合采用扫描电镜（SEM）、能量色散X射线能谱（EDS）、X射线荧光光谱（XRF）和X射线衍射光谱（XRD）技术探究其除磷机制,对比分析了钢渣与陶粒和沸石的除磷效率,并对钢渣除磷的安全性能进行了评估.结果表明,吸附时间显著影响钢渣除磷效果,当吸附时间为30 min时钢渣对质量浓度范围为1~20 mg·L^-1的磷酸盐溶液的去除率均可达到97%以上.温度对实验所用钢渣的除磷效果影响并不显著.钢渣对焦磷酸盐吸附能力弱于正磷酸盐,其对初始质量浓度为3 mg·L^-1的焦磷酸盐的去除率为82.45%.光谱分析结果表明,钢渣除磷的主要机制为化学吸附并辅以物理吸附,CaHPO₄·2H₂O为主要沉淀物质.钢渣对生物池出水和湿地系统中的磷素去除效果显著,总磷去除率分别为98.36%和93.33%.对比可知,钢渣对磷酸盐的去除效果优于陶粒和沸石,其对PO₄^3-的去除率分别为96%、40%和10%.钢渣浸出液中各重金属含量均符合地表水Ⅰ类标准要求,钢渣安全可靠.     

Characteristics of the stabilized/solidified municipal solid wastes incineration fly ash and the leaching behavior of Cr and Pb

Fly ash is a hazardous byproduct of municipal solid wastes incineration (MSWI). An alkali activated blast furnace slag-based cementitious material was used to stabilize/solidify the fly ash at experimental level. The characteristics of the stabilized/solidified fly ash, including metal leachability, mineralogical characteristics and the distributions of metals in matrices, were tested by toxic characteristic leaching procedure (TCLP), X-ray diffraction (XRD) and scanning electron microscopy-energy dispersive spectrometer (SEM-EDS) respectively. Continuous acid extraction was utilized to extract metal ions and characterize their leaching behavior. The stabilization/solidification procedure for MSWI fly ash demonstrates a strong fixing capacity for the metals by the formation of C-S-H phase, hydrated calcium aluminosilicate and ettringite. The stabilized/solidified fly ash shows a dense and homogeneous microstructure. Cr is mainly solidified in hydrated calcium aluminosilicate, C-S-H and ettringite phase through physical encapsulation, precipitation, adsorption or substitution mechanisms, and Pb is mainly solidified in C-S-H phase and absorbed in the Si-O structure.