2-chlorophenol oxidation kinetic by photo-ssisted Fenton process

IntroductionTheo chlorophenolisaverytoxicandpoorlybiodegradablepollutant,whichisusedasanintermediateinthemanufactureofhigherchlorophenolandphenolresinsandforextractingsulphurandnitrogencompoundsfromcoals.Itisalsousedinorganicsynthesis(dyesandpesticide) .Oxidationofo chlorophenolwastewaterincatalyticwetairoxidationisofpracticalinterestsinceawastewatercontainingo chlorophenolover 2 0 0ppmmaynotbetreatedeffectivelybydirectbiologicalmethods.Advancedoxidationprocesses(AOPs)havebeensuccessfullyuse…     

悬浮态TiO_2光催化降解苯系物的方法研究

以高压汞灯为光源 ,在TiO2 粉末悬浮体系内 ,系统地研究了光照时间、光照距离、催化剂用量、苯系物浓度和溶液pH、空气流量、H2 O2 浓度、Fe3+ 浓度等因素对模拟水样中苯系物的光催化降解效率的影响。研究结果表明 ,当光照时间为 2 0min、光照距离为 6cm ,TiO2 用量为 4 0 0mg L、pH =7、苯系物浓度为 10 0mg L ,空气流量为 4 0 0mL min,苯系物降解率可达 93% ,添加H2 O2 与Fe3+ 能增加苯系物的降解率 ,当H2 O2 浓度为 6mmol L ,Fe3+ 浓度为 0 2mmol L ,苯系物可完全降解。实验测定精密度RSD为 0 5 %。     

利用轨迹模式模拟近地层臭氧日变化

提出在多条轨迹上应用轨迹模式，以实现对固 区臭氧浓度日变化的模拟，应用该方法对北京燕山石化炼油厂地区的Ｏ３浓度日变化进行了模拟，结果表明模拟值和实测值十分吻和。进一步模拟了当地的臭氧生物特征，并讨论了当地的气象条件和源排放对Ｏ３生成浓度的影响。结果说明削减ＮＯｘ的排放量是控制该地区光化学烟雾形成的关键，而降低燃烃和芳香烃在排放物中所占的比例也是控制该地区光学烟雾的重要手段。     

生物活性炭处理废水中有机物的研究探讨

生物活性炭(BAC)是一种处理有机废水的有效方法。现以BAC处理废水中的酚和甲醇为例,综述BAC处理废水中有机物的机理和影响因素。并通过生物活性炭吸附降解四氯乙烯(PCE)的综合模型得到BAC作用与吸附和生物降解的关系。最后简单介绍了BAC中活性炭与微生物的选择。     

塔里木盆地光温模式研究及其应用

建立了塔里木盆地光照、温度模式 ,该模式可以预测出塔里木盆地无资料地区各网格点的日照时数和冬季(1月)、夏季 (7月 )平均气温。在此基础上 ,应用统计学导出的极值分布和正态分布概率模式 ,预测了塔里木盆地各站上述要素不同概率的设计值。首次揭示了塔里木盆地无资料地区光照时间、温度分布规律。该模式为塔里木油田石油工业总体规划和大型工程设计及农业合理布局等提供了有效的科学依据     

太阳光助Fenton体系氧化降解苯酚废水的研究

探讨了太阳光助Fenton体系对苯酚的氧化降解。结果表明，太阳光能有效地增强Fenton试剂对苯酚的氧化降解，在晴天较强太阳光照下，Fenton试剂可在较短时间内使较高浓度的苯酚完全矿化。反应体系的初始pH值及Fe^2 用量均对苯酚的氧化降解有明显影响，反应的适宜pH值在3—4的酸性范围内；适量Fe^2 参与的太阳光—Fenton反应有助于苯酚的降解，但过高的Fe^2 用量反而不利于苯酚的降解。实验结果还表明，采用分批多次投加的方式可明显提高氧化剂H202的利用效率，降低H202的消耗量；苯酚废水降解的主要中间产物为苯醌和有机酸；一定程度的太阳光—Fenton预氧化处理可使废水的BOD5／C02cr比值由0.10捉高到0.32，可生化性明显提高。     

催化技术在污染物治理应用的研究进展

对近年来催化技术在污染物治理应用的研究进展进行了综述,指出了现在研究中存在的主要问题,并对其前景进行了展望。     

瓷砖釉面TiO2薄层对甲基橙的光催化降解

采用溶胶-凝胶法，在瓷砖釉面上制备了良好光催化活性TiO2薄层材料，研究结果表明瓷砖釉面TiO2薄层材料对甲基橙的光催化反应遵循一级动力学规律，光催化降解率与液层厚度符合指数关系。在太阳光照射下，釉面瓷砖TiO2薄层材料能对甲基橙有效地降解。     

室内有毒易爆气体的检测

随着城市生活水平的提高,室内装修装饰日益普及.各种新材料的引入,使得室内的各种有害气体总量日益增加.长期生活在这样的环境下,会对人体健康产生极为不利的影响.居民生活用煤气,在给人们生活带来便利的同时,作为一种可燃性、有毒气体,也具有极强的危害性.因此,研制一种能检测多种有害气体的实用仪器,具有很大的应用价值.本仪器为便携式多功能仪器,采用可充电电池供电,可以检测ppb的挥发性气体,显示气体浓度值,也可检测煤气,并具有声光报警功能.     

Effect of tracer dyes on initial deposits and persistence of bacillus thuringiensis subsp. kurstaki toxin after application of two commercial formulations onto spruce trees

Abstract

The effect of two tracer dyes [Erio Acid Red (EAR) and Acid Black 48 (AB‐48)] on initial deposits and persistence of Bacillus thuringiensis subsp. kurstaki (Btk) toxin (delta‐endotoxin) was studied after spraying two commercial formulations, Foray® 48B and Foray® 76B, over potted white spruce [Picea glauca (Moench) Voss] seedlings, at a dosage rate of 30 billion international units (BIU) per ha. Spray was applied using a spinning disc atomizer calibrated to deliver droplet sizes similar to those utilized in ultra‐low‐volume (ULV) treatments in operational insect control programs. The sprayed seedlings were left outdoors at the Sault Ste. Marie laboratory for 18 days under natural conditions of sunlight, wind and rainfall. Initial deposits and persistence of delta‐endotoxin protein in spruce foliage were determined by immunoassay [enzyme linked immunosorbent assay (ELISA)] quantification of the delta‐endotoxin. The total protein (inactive plus active) and delta‐endotoxin (active protein) concentrations in the two formulations were determined by a gravimetric procedure and by ELISA respectively.

The initial deposit levels of the toxin on foliage were not markedly affected by the addition of either of the two tracer dyes, and showed only a narrow range of 1521 to 1625 ng/g foliage (fresh weight) for Foray 48B, and 1789 to 2056 ng/g for Foray 76B. However, the persistence of the toxin was significantly influenced by the presence of the dyes. The toxin persisted in foliage only for 7 d post‐spray When the EAR dye was added to Foray 48B, compared to 10 d when no dye was added. The average half‐life (DT₅₀) of disappearance was 17.4 h for Foray 48B with EAR, and 20.9 h when no dye was present. In contrast, the situation was reversed in Foray 76B, since the duration of persistence was 10 d when EAR was added to Foray 76B, compared to 7 d when no dye was added. The average DT₅₀ was 27.9 h for Foray 76B with EAR, and 22.2 h without the dye. Persistence was the longest (14 d) when the AB‐48 dye was added to Foray 76B, and the DT₅₀ was 44.9 h.