碱性高炉矿渣制备多孔混凝土掺合料及其净化酸性水的试验研究

碱性高炉矿渣和多孔混凝土都有良好的净水性能,将碱性高炉矿渣作为掺合料制成掺高炉矿渣多孔混凝土(BSPC),对其处理模拟酸性水的效果进行研究。结果表明:经BSPC处理后,进水p H由2~3变成8.5~9.1。与普通多孔混凝土相比,添加高炉矿渣的混凝土对酸性水浊度、CODcr、TP和Cd的平均去除率依次提高了6.2%,8.8%,5.2%和4.5%,分别达到74.3%,74.5%,91.7%和86.5%。同时,BSPC孔隙率在处理酸性水前后有所下降,下降幅度较小,为6.2%,不影响BSPC对酸性水的处理。实验最后对混凝土表面白色絮状物进行了红外和XRD表征,初步分析其中含有CaCO_3、SiO_2和水化硅酸钙(C-S-H)等无机物,初步判定来源于BSPC的溶出物。     

Recent advances in catalytic decomposition of ozone

Ozone(O₃), as a harmful air pollutant, has been of wide concern. Safe, efficient, and economical O₃ removal methods urgently need to be developed. Catalytic decomposition is the most promising method for O₃ removal, especially at room temperature or even subzero temperatures. Great efforts have been made to develop high-efficiency catalysts for O₃ decomposition that can operate at low temperatures, high space velocity and high humidity. First, this rev...     

老化的生物质炭性质变化及对菲吸持的影响

将稻壳分别在350℃和550℃热解温度下制备成生物质炭,避光条件下恒温培养300 d,通过傅里叶变换红外光谱、扫描电镜和核磁共振等技术手段及平衡吸附实验,探究生物质炭老化前后的动态结构变化及对菲吸持作用的影响.结果表明,生物质炭老化过程中氧含量增加,含氧基团增多,对菲的非线性吸附行为显著增强.热解温度的不同决定了生物质炭老化过程中性质变化的差异,350℃热解的生物质炭,老化后极性增强,芳香性减弱,而550℃热解的生物质炭,老化后脂肪族碳类物质增加,羧基减少,芳香性增强,Langmiur预测的菲在350℃热解的生物质炭上老化前后的最大吸附量分别为3.57 mg·g-1、2.35mg·g-1,主要是老化后性质变化抑制了表面吸附作用,而550℃热解的生物质炭上老化前后的最大吸附量分别为0.42mg·g-1、4.17 mg·g-1,老化后吸附量的显著增加主要是生物质炭性质变化促进了对菲的分配作用与表面吸附作用.研究生物质炭在自然环境中的老化行为对环境污染物固定的稳定性有着重要意义.     

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.     

市政污泥热解过程中重金属迁移特性及环境效应评估

以昆明某市政污泥为原料,研究生物炭制备过程中重金属Fe、Zn、Mn和Ni的迁移特性,并基于其潜在环境风险确定污泥基生物炭制备的最佳热解温度.本实验选择总量较高的4种重金属Fe、Zn、Mn和Ni,采用BCR提取法测定不同热解温度下4种重金属的形态和含量变化,得到各金属的形态分布变化规律和迁移路径,利用潜在生态风险指数(P...     

环境内分泌干扰物筛选和测试研究中的鱼类实验动物

环境内分泌干扰物的筛选与测试方法的研究是近年来环境科学领域的热点问题．在水生态毒理学研究中，目前的研究重点之一是发展方法学，如基于鱼类实验动物的离体或活体测试方法．对内分泌干扰物鱼类筛选测试的科学基础、内分泌干扰物的生物性标志、筛选测试方法以及用于内分泌干扰物筛选测试的几种主要鱼类实验动物进行了介绍，同时提出了建立适合我国实际情况的内分泌干扰筛选测试鱼类实验动物，并提出系统的鱼类实验动物培育和筛选测试方法体系的必要性．     

钢渣吸附Pb2+的动力学研究

采用批式振荡吸附法研究了钢渣吸附Pb^2＋的动力学。研究结果表明,钢渣吸附Pb^2＋的动力学控制步骤（简称动力学控制步骤）随实验条件的变化而变化：钢渣粒径大于120μm、振荡器转速小于150r/min或Pb^2＋初始质量浓度小于150mg/L时,孔扩散是动力学控制步骤;钢渣粒径小于120μm、振荡器转速大于150r/min或Pb^2＋初始质量浓度大于150mg/L时,表面扩散是动力学控制步骤;钢渣对Pb^2＋的吸附反应是二级反应,其吸附速率为13.26g/（mg.min）。     

镍渣制备建筑用微晶玻璃的初步研究

对从镍渣中提取铁同时制备建筑用微晶玻璃的进行了研究.结果表明,熔渣中铁的质量分数可以降到0.5%左右,满足制备微晶玻璃的要求.对微晶玻璃样品进行了显微镜、X射线衍射、扫描电镜分析.其主晶相是透辉石(CaO·MgO·2SiO2),晶体的形貌为短柱状,分布均匀.本文所介绍的制备工艺是可行的.     

黄海北部对虾放流水域污染分析

根据１９９６－１９９８年对黄海北部中国虾放流增殖水域的调查，对该水域的污染状 评价，结果表明，除个别站位ＣＯＤ、Ｃｕ、Ｚｎ、Ｈｇ有少量超标外，综合评价和单因子评价均符合渔业水质标准规定的要求，水质良好，适合幼对虾的栖息和生长。但污染物含量特别是重金属含量有逐年增高的趋势。     

Seasonal and spatial occurrence and distribution of atmospheric polycyclic aromatic hydrocarbons (PAHs) in rural and urban areas of the North Chinese Plain

Passive air sampling (PAS) was employed to study the occurrence of gaseous and particle-bound PAHs in the North Chinese Plain. The averaged concentrations of gaseous and particle-bound PAHs were 485 ± 209 ng/m³ and 267 ± 161 ng/m³, respectively. The PAHs concentrations at urban sites were generally higher than those at rural ones with ratios <1.5 in spring, summer and fall, but differences between them were not significant for the wintertime and annually averaged concentrations. This urban-rural distribution pattern was related to the PAHs emission sources. PAHs spatial variation can be partially (49%) explained by emission with a simple linear regression method. Both the gaseous and particle-bound PAHs were highest in winter and lowest in summer, with winter/summer ratios of 1.8 and 8, respectively. Emission strength was the most important factor for the seasonality.