二氧化钛对活性艳红X-3B的光催化降解研究

以TiO2作为光催化剂,研究了TiO2对活性艳红X-3B的光催化氧化降解行为。结果表明,以锐钛矿为主的混晶型Ti02的催化活性最好;X-3B的光催化降解动力学符合Langmuir-Hinshelwood动力学模式,并求出其动力学参数女(表观反应速率常数)为0．5921,KA(吸附平衡常数)为0．1725;温度对X-3B的降解影响很小,其活化能仅为6．04kJ／mol;溶液中盐度的增加会不断降低TiO2对X-3B的光催化降解速率。     

应用定量结构-性质相关法预测有机物的亨利常数

建立了预测有机物亨利常数的定量结构－性质相关方程，回归分析结果表明，此方程可以解释２０６种有机物９８％的实验数据变异，标准偏差为０．２５个对数单位，应用该方程能很好地预测许多有机化合物的亨利常数值。     

碳纳米管生殖毒性及其毒作用机制研究进展

随着碳纳米管(carbon nanotubes,CNTs)在各个领域应用的增加,人们接触到CNTs的几率也随之增加,越来越多的人开始关注CNTs对于人体是否具有毒性及其毒性的大小,近些年的体内和体外研究显示,CNTs可对生物体(如小鼠、斑马鱼、赤子爱胜蚓等)生殖系统产生毒性并遗传给后代,影响后代生长发育。本综述主要从CNTs种类、官能化和CNTs悬浮液中团聚体尺寸及所含杂质3个方面探讨CNTs的生殖毒性及毒作用机制,以及影响其毒性及毒作用机制的因素,从而为CNTs更加安全有效的应用提供依据。     

电子政务中的物理隔离技术

本文从电子政务必须高度安全的角度出发,详述了隔离技术的发展阶段和各发展阶段的主要产品并探讨了它的未来发展趋势。     

石油污染与微生物群落结构的相互影响

从两种土壤中分别分离出石油烃降解菌,并从中筛选出6株石油烃高效降解菌A1、A2、A6、A8和B2及B5,然后将各菌株鉴定至属,分别为A1假单胞菌属、A2鞘氨醇单胞菌属、A6微球菌属、A8节杆菌属、B2不动杆菌属和B5诺卡氏菌属。另外对比分析了单菌株及不同菌株重组对不同石油烃组分的利用情况,结果发现,从不同石油污染的土壤中分离到的菌株对石油烃组分的利用能力不同,从胜利原油污染的土壤中分离到的菌株A1、A2、A6和A8对石油烃组分的利用范围窄,主要利用饱和烃组分;而从经芳香烃驯化过的土壤中分离到的菌株B2及B5对石油烃利用组分的利用范围较宽,能同时利用饱和烃和芳香烃组分。     

现阶段国内外城市固体废弃物的治理技术与治理概况

城市固体废弃物是人们在工业生产活动、生活活动及商业活动中所产生的固体废物,这种废物随着国民经济的发展、人口的增长、人民生活水平的提高,数量不断增加。它破坏了市容,污染环境,给人民健康带来了极大的危害,因此,需加以处置和处理。本文将系统地介绍现阶段国内外城市固体废弃物的现状及处理技术,并针对我国国情,提出合理化的处理方案。     

空气中有机氯农药在不同粒径颗粒物上的分布

采用 DFJ-1型五段分级采样装置,对呼和浩特市冬夏两季空气中不同粒径(分别为≥7.0μ m,7.0-3.3μm,3.3-2.0μm,2.0-1.1μm,≤1.1μm)颗粒物上有机氯农药的残留量进行分析.测定结果表明:在空气颗粒物分级样品中,均检出有机氯农药(HCH-666 和p,p'-DDE)残留量;空气颗粒物中HCH-666冬季均值为0.502ng·m -3,夏季为1.070ng·m-3,而p,p'-DDE在冬季为0.0 85ng·m-3,夏季为0.108ng·m-3;呼和浩特市空气中有机氯农药残留量夏季均高于冬季,不同粒径空气颗粒物中有机氯农药的分布规律为:冬季主要富集在细小颗粒 (≤1.1μm)上,在30.6%-70.5%之间,在夏季有机氯农药的残留分散吸附在五个不同粒径级上.     

TG-DSC and FTIR study on pyrolysis of irradiation cross-linked polyethylene

Irradiation cross-linked polyethylene (PEX) and irradiation cross-linked polyethylene with carbon black filler (CB-PEX) are two types of scraps, generated in electric cable production. Their pyrolysis is studied in this work using instrumental TG\DSC\FTIR techniques and kinetic analysis. The experiments are performed at a constant heating rate of 10 °C/min in nitrogen flow at atmospheric pressure. It is found that the main pyrolysis stage is in the temperature range of 395–503 °C for PEX, and in range of 408–515 °C for CB-PEX. In the main pyrolysis stage, CB-PEX requires more external heat than PEX does. Olefins are the major products of pyrolysis for both materials, but they are quite different in their composition and molecular weight distribution. PEX can be converted almost quantitatively into volatile compounds. CB-PEX has a stronger coking tendency, as well as a larger residue composed of carbon black.     

纳米FeVO_4的制备及其可见光下降解甲苯的性能

以Fe(NO3)3或FeCl3作为铁源,采用水热法制备了纳米FeVO4光催化剂,通过XRD、SEM、DRS等手段表征了所合成FeVO4的物相、表面形貌及光学性质,研究了其可见光下光催化降解甲苯的性能。表征结果显示:FeVO4平均晶粒尺寸约为75 nm,为棒状;FeVO4在可见光区域(λ400 nm)表现出较高的吸光性,其吸光区域可红移至约600 nm;以FeCl3为铁源,水热反应3 h制备的FeVO4的禁带宽度为2.1 e V;以Fe(NO3)3为铁源制备的FeVO4的比表面积(74.70 m2/g)大于以FeCl3为铁源制备的FeVO4的比表面积(67.72 m2/g)。在初始甲苯质量浓度为494 mg/L、FeVO4为光催化剂、反应4 h的条件下,甲苯降解率达62%。甲苯降解最终产物为CO2和H2O。     

Bacteria inactivation by sulfate radical: progress and non-negligible disinfection by-products

● Status of inactivation of pathogenic microorganisms by SO₄^•− is reviewed. ● Mechanism of SO₄^•− disinfection is outlined. ● Possible generation of DBPs during disinfection using SO₄^•− is discussed. ● Possible problems and challenges of using SO₄^•− for disinfection are presented. Sulfate radicals have been increasingly used for the pathogen inactivation due to their strong redox ability and high selectivity for electron-rich species in the last decade. The application of sulfate radicals in water disinfection has become a very promising technology. However, there is currently a lack of reviews of sulfate radicals inactivated pathogenic microorganisms. At the same time, less attention has been paid to disinfection by-products produced by the use of sulfate radicals to inactivate microorganisms. This paper begins with a brief overview of sulfate radicals’ properties. Then, the progress in water disinfection by sulfate radicals is summarized. The mechanism and inactivation kinetics of inactivating microorganisms are briefly described. After that, the disinfection by-products produced by reactions of sulfate radicals with chlorine, bromine, iodide ions and organic halogens in water are also discussed. In response to these possible challenges, this article concludes with some specific solutions and future research directions.