真空紫外光降解瓦斯反应动力学规律

为了研究真空紫外光降解瓦斯过程的反应动力学规律,在自制的真空石英光化学反应器中以含甲烷标准气体模拟矿井瓦斯,运用Langmuir-Hinshelwood(L-H)拟一级反应动力学模型对不同光照强度、氧气体积分数、甲烷初始体积分数和水分子体积分数下瓦斯(甲烷)的降解过程进行拟合.结果表明:真空紫外光降解瓦斯反应动力学规律符合一级反应动力学特性;光照强度、甲烷初始体积分数、氧气体积分数和水分子体积分数是影响真空紫外光降解瓦斯的主要因素;瓦斯(甲烷)降解的反应速率随光照强度和氧气体积分数增大而增大,随甲烷初始体积分数增大而减小,随水分子体积分数增大而先增大后减小.     

Do aerosols act as catalysts in the OH radical initiated atmospheric oxidation of volatile organic compounds?

Smog chamber/FTIR techniques were used to study the relative reactivity of OH radicals with methanol, ethanol, phenol, C₂H₄, C₂H₂, and p-xylene in 750 Torr of air diluent at 296±2 K. Experiments were performed with, and without, 500–8000 μg m⁻³ (4000–50 000 μm² cm⁻³ surface area per volume) of NaCl, (NH₄)₂SO₄ or NH₄NO₃ aerosol. In contrast to the recent findings of Oh and Andino (Atmospheric Environment 34 (2000) 2901, 36 (2002) 149; International Journal of Chemical Kinetics 33 (2001) 422) there was no discernable effect of aerosol on the rate of loss of the organic compounds via reaction with OH radicals. Gas kinetic theory arguments cast doubt upon the findings of Oh and Andino. The available data suggest that the answer to the title question is “No”. As part of this work the rate constants for reactions of OH radicals with methanol, ethanol, and phenol in 750 Torr of air at 296 K were determined to be: k_OH+CH3OH=(8.12±0.54)×10⁻¹³, k_OH+C2H5OH=(3.47±0.32)×10⁻¹² and k_OH+phenol=(3.27±0.31)×10⁻¹¹ cm³ molecule⁻¹ s⁻¹.     

MnFe2O4活化过一硫酸盐降解废水中LAS

采用共沉淀法制备了铁锰双金属复合催化剂（MnFe₂O₄）,用于活化过一硫酸盐（PMS）产生强氧化性的硫酸根自由基（SO₄^-·）氧化降解水中阴离子表面活性剂（LAS）.采用傅立叶变换红外光谱仪（FTIR）、X射线粉末衍射仪（XRD）、扫描电子显微镜（SEM）对催化剂进行表征,表明成功合成了具有尖晶石结构的MnFe₂O₄催化剂.考察了催化剂投加量、PMS投加量以及初始pH值等各种因素条件对LAS的降解效率以及反应动力学的影响.实验结果表明,MnFe₂O₄活化PMS降解LAS的过程符合准一级动力学（R²>0.9）.在LAS初始浓度为80mg/L,催化剂投加量为2.0g/L,PMS的浓度为2.5mmol/L,初始pH值为7.0,反应时间为30min的情况下,LAS降解效率达到94.1%,此时LAS的降解速率常数达到0.192min^-1.通过自由基猝灭实验证明了MnFe₂O₄/PMS体系中起主要氧化降解作用的活性自由基为SO₄^-·.通过反应前后催化剂的X射线光电子能谱（XPS）,证实Fe和Mn之间存在协同作用,提高了MnFe₂O₄对PMS的活化效率.     

ESR技术应用于逆胶束酶体系性能的研究

采用鼠李糖脂构建逆胶束体系,并利用电子自旋共振（ESR）技术研究了鼠李糖脂逆胶束及鼠李糖脂逆胶束酶体系的性能.采用ESR光谱技术计算得出逆胶束体系中超精细分裂常数变化,研究表明鼠李糖脂在正己烷中的临界胶度为0.07mmol/L.通过分析ESR光谱中旋转相关时间的变化,探究电子自旋探针在逆胶束中运动受阻和翻转所需时间的情况同时,ESR光谱的峰值体现了样品中自由基含量的多少.通过对比逆胶束体系、逆胶束酶体系以及逆胶束酶-苯酚体系的ESR光谱,结果表明鼠李糖脂逆胶束-苯酚体系的自由基最多.通过研究对16-氮氧自由基硬脂酸对两个体系作用,推测出电子自旋探针自由基团定位于逆胶束水核中,并且推断电子自旋探针位于水核的边缘区域,即结合水水层.该研究为逆胶束酶体系的应用提供了坚实的理论基础.     

近红外光腔衰荡光谱系统设计及研究

目的搭建一套近红外光腔衰荡光谱测量系统,实现水汽吸收的探测。方法通过测量有无样品存在时的衰荡时间,实现腔内介质吸收的探测。通过测量空腔衰荡时间,计算腔镜反射率。通过测量不同浓度的水汽吸收,验证系统是否可用于分子吸收的测量。结果该装置的空腔衰荡时间约为3.75μs,对应的腔镜反射率为99.982%,有效吸收光程为1.1 km。测量了6627.7 cm~(-1)处水汽的吸收,结果与HITRAN数据库一致。结合文献报道结果和HITRAN数据库吸收谱线,模拟得到了NH_3、C_2H_2、HO_2自由基在6625～6626 cm~(-1)范围内的吸收系数。结论该装置实现了水汽吸收的探测,在该装置的激光器工作波长范围内,可应用于NH_3、C_2H_2、HO_2自由基的实时探测。     

UV/H2O2降解美罗培南的影响因素及毒性研究

利用波长为254 nm的紫外灯活化过氧化氢(H_2O_2)氧化降解美罗培南(MPN),考察了H_2O_2投加量、初始pH值、水中常见共存阴离子(Cl~-、HCO~-_3、NO~-_3)和天然有机化合物(NOM)等重要影响因素对MPN降解的影响.结果表明,紫外光功率为4 W,初始pH为7.0,n(H_2O_2)/n(MPN)=20∶1时,反应20 min后,MPN的降解率达到97.8%.H_2O_2投加量的增加会加快MPN的降解速率,Cl~-和HCO~-_3对UV/H_2O_2体系中MPN去除效果的影响较小,极少量的NO~-_3会促进MPN的降解,当NO~-_3的浓度≥10 mg·L~(-1)时,MPN的降解受到抑制,且离子浓度越高,抑制程度表现越明显.NOM的存在对MPN的降解有抑制作用.与纯水相比,MPN在实际水体中的去除受到抑制,归因于水体基质的影响.大肠杆菌的急性毒性实验研究表明,MPN的中间转化产物保留了一些抗菌性能,但光解的最终产物无抗菌性能.     

纳米零价铜活化分子氧降解水中恩诺沙星

采用纳米零价铜(nanoscale zero-valent copper,nZVC)活化分子氧对水中恩诺沙星(enrofloxacin,ENR)的去除进行了系统研究.通过表征可以发现,纳米铜粉比表面积高于微米级铜粉,无孔隙结构,表面粗糙且容易团聚.纳米级ZVC活化分子氧的性能明显优于微米级ZVC,这主要归因于其较大的比表面积,更容易被腐蚀.通过探究活化机制可以发现,活化分子氧产生的H_2O_2和表面腐蚀产生的Cu+构成了新型类Fenton体系,持续释放的羟基自由基是造成水中ENR高效去除的主导活性物种;同时,反应过程中产生的超氧自由基能够促进Cu2+还原成Cu+,从而加速ENR的去除过程.反应条件对nZVC活化分子氧降解ENR有一定的影响,较高的nZVC投加量、较低ENR浓度、较高的反应温度以及强酸性条件均有利于ENR的去除.     

Hydrogen Peroxide and Ultraviolet Irradiations in Water Treatment

Trihalomethanes (THMs) the by-products of chlorination in water treatment are recognised as a threat to public health due to their carcinogenicity. The photodegradation of THMs using hydrogen peroxide has been found to give increased removal efficiency and the outcome of the study may find, its application in designing a unit process for water treatment. Batch experiments were carried out using UV lamp of 83 W and 40% w/w Hydrogen peroxide (H₂O₂) in test waters between 2.5–10 pH range of chloroform, bromodichloromethane, dibromochloromethane and bromoform at 50–200 μg L⁻¹ initial concentration. 92–100% removal of chloroform, bromodichloromethane, dibromochloromethane and bromoform were found with 0.1% of H₂O₂ and 90 min of UV exposure.     

Practical applications of the fenton reaction to the removal of chlorinated aromatic pollutants

BACKGROUND: Chlorophenols (CPs) constitute a group of organic pollutants that are introduced into the environment as a result of several man-made activities, such as uncontrolled use of pesticides and herbicides, and as byproducts in the paper pulp bleaching. Promising removal technologies of chlorinated aromatics consist in the application of advanced oxidation processes (AOPs) that can provide an almost total degradation of a variety of contaminants. Among these, wide application find Fenton systems based on generation of reactive species having a high oxidizing power, such as hydroxyl radical HO*. Our objective was that of determining the overall degradation efficiency of the model compound 2,4-dichlorophenol (DCP) by thermal Fenton-type oxidation systems with a view toward defining in more details relevant process parameters, the effect of reaction temperature and of co-catalyst Cu2+. METHODS: Reaction conditions were similar to those generally adopted as optimal in many practical applications, i.e. pollutant/Fe2+ (as FeSO4) ratio ca. 20, Fe2+/Cu2+ (co-catalyst) 2:1, pH adjusted and controlled at pH 3, and H2O2 in excess (up to four-fold over the stoichiometric amount required for complete mineralization). RESULTS AND DISCUSSION: The results demonstrate that it is advantageous to carry out the reaction at a temperature markedly higher (70 degrees C) than ambient. The stepwise addition of H2O2 in aliquots yields an efficient transformation, while allowing a convenient control of the reaction exothermicity. Under these conditions, the essentially complete removal of the initial DCP is accomplished using just one equiv of H2O2 during 15 min; excess H2O2 (5 equivalents) yields extensive substrate mineralization. Also relevant, at 70 degrees C dechlorination of the initial DCP (and of derived reaction intermediates) is remarkably extensive (3-5% residual TOX), already with the addition of 1 equiv of H2O2. At the end of the reaction, IC and IC-MS analyses of the solution reveal that only low-molecular weight carboxylic acid (acetic, formic, oxalic, malonic, tartaric, etc.) contribute to the residual TOC. CONCLUSIONS: The whole of the results herein point to the advantage of performing the process at temperatures substantially higher than ambient (70 degrees C). Under the conditions adopted, almost complete degradation of the initial toxic compound can be achieved using hydrogen peroxide in fair excess (e.g., 3.5 equiv H2O2). RECOMMENDATIONS AND OUTLOOK: In applying practical Fenton-type degradation systems to heavily polluted wastes, either for the pre-treatment of waters with a high COD value prior to biodegradation or for complete mineralization of pollutants, the set up of appropriate reaction conditions appears to be a key factor. Also, it is desirable to keep the concentration of iron salts within the lower limits in order to minimize the production and disposal of iron oxide sludges.     

氯氟烃替代物与OH自由基光化学反应

保护生物多样性生物多样性是人类社会赖以生存和发展的物质基础，保护生物多样性，保证生物资源的持续利用是一项全球性任务，也是全球环境保护行动计划的重要组成部分。按照生物多样性国际公约的定义，生物多样性“是指所有来源和形形色色的生物体，这些来源包括陆地、海...