TiO2及负载Fe(Ⅲ)可见光催化H2O2降解扑草净的协同效应

以TiO2P25(TIO-P25)及Fe(NO3)3为前驱物制备TiO2负载Fe3+多相催化剂Fe/TIO-P25,研究Fe/TIO-P25可见光催化H2O2降解扑草净的协同效应.XRD、XPS、EDS及SEM结果表明,Fe元素以Fe2O3形式高度分散于TiO2表面,负载量约1.5%(wt%),未对TIO-P25的粒径及形貌产生明显影响,Fe/TIO-P25的粒径约20~40nm;光催化结果表明,Fe/TIO-P25能可见光催化H2O2降解扑草净,反应30min降解率达100%,远大于TIO-P25的催化活性,负载Fe与TIO-P25之间存在明显的协同效应;通过对反应体系的荧光光谱分析显示,扑草净的降解涉及较单纯羟基自由基(·OH)过程更为复杂的反应机理.     

磁性Mn0.6Zn0.4Fe2O4@SiO2催化H2O2降解亚甲基蓝效能及机制

为制备易固液分离和稳定性好的高效非均相类Fenton催化剂,利用正硅酸乙酯水解对Mn_0.6Zn_0.4Fe₂O₄磁性纳米颗粒（SF-MNPs）进行功能化修饰,制备得到Mn_0.6Zn_0.4Fe₂O₄@SiO₂（MZF@SiO₂）磁性纳米复合物催化剂,采用透射电镜、 X射线光电子能谱和振动样品磁强计等对MZF@SiO₂进行了表征,以难生物降解偶氮染料亚甲基蓝（MB）为目标污染物,考察了不同初始pH对MZF@SiO₂催化效能的影响,在近中性条件下（pH=6.5）研究了H₂O₂用量、 MZF@SiO₂投加量和温度等对MB去除率的影响,及MZF@SiO₂的稳定性和循环使用性能,推测了催化反应机制.结果表明,无定形SiO₂将SF-M...     

Ce改性钒磷氧催化剂的制备及其脱硝性能研究

采用Ce调控负载型钒磷氧（VPO/TiO₂）催化剂的表面酸性并与之形成密切相关的微观结构,研究催化剂VPO-Ce/TiO₂的脱硝性能.结果表明,当P/V为1/3、Ce/V为1/4、活性组分负载量10%、催化剂焙烧温度为400℃时,催化剂的脱硝活性最好,反应温度250~350℃范围内的脱硝率高于96.0%.BET测试结果表明,催化剂0.1VP（0.33）O-Ce（0.25）/TiO₂的比表面积为10.74m²/g,较0.1VP（0.33）O/TiO₂提高了约58.6%.0.1VP（0.33）O/TiO₂表面化学吸附氧（O_α）和晶格氧（O_β）的比例O_α/O_β为72%,掺杂Ce后O_α/O_β升高至85%,Ce掺杂还能促进相邻V⁵⁺和V⁴⁺的形成,提高催化剂的氧化还原性能.Ce掺杂对催化剂的表面酸性影响较大,当Ce/V为1/4时催化剂表面Brønsted酸最强,这与活性测试相吻合.控制烟气中SO₂和水蒸气的体积浓度分别为200×10^-6和4vol.%,催化剂的脱硝活性在150~300℃温度范围内最高下降约15.8%,当温度高于300℃时催化剂的脱硝活性几乎不下降,且反应后的催化剂表面无硫酸根生成,催化剂呈现出较强的抗SO₂和水蒸汽的性能.     

再谈废催化剂中金属的回收

介绍了含钯,钴,钼,钨的废催化剂的来源及从废催化剂中回收上述金属的工艺。     

催化超临界水氧化废水处理技术的研究进展

简要介绍了作为反应介质的超临界水的物化性质及超临界水氧化的特点 ,阐述了催化超临界水氧化的一般工艺流程并分析了其过程的影响因素及各影响因素的相互关系 ,归纳了超临界水氧化的催化机理、动力学、水对多相催化反应的影响以及催化剂的研究进展 ,探讨了该项技术发展的前景与趋势     

NOx气体的催化治理

综述了ＮＯｘ—Ｈ２反应的机理，介绍了催化剂的特点及影响催化剂性能的主要因素     

In situ IR,pulse reaction and TPD-ITD study of catalytic performance of room-temperature carbon monoxide oxidation on supported gold catalysts

With in situ IR, two different CO adsorption bands were detected on various chemical state gold catalysts. One band is attributed to the linear CO on an oxidized gold catalyst(2100 cm i ), the other one is ascribed to the bridged CO on metallic gold (2085 cm- i ). CO pulse reaction showed that Au/Fe203 catalyst had a room-temperature activity even in the presence of moisture. The produced CO2 was detained and more easily desorbed from supported gold catalyst than support oxide. TPD-IDT results indicated that the 02- superoxide ions are the possible active oxygen species.     

M—铁氧体对印染废水催化脱色试验研究

本文介绍了用含不同组分的铁氧体(M-铁氧体)作为催化剂,对印染废水进行催化空气氧化脱色的试验研究.实验发现Ni-铁氧体对不溶性还原染料废液有较好的催化脱色能力,脱色率通常可达90％以上.红外光谱分析结果表明,Ni-铁氧体参与的不溶性还原染料废液的催化脱色反应是通过将染液中的助剂保险粉彻底氧化,从而使染料转化为不溶性沉淀物被分离而完成的.     

Catalytic wet air oxidation for the treatment of emulsifying wastewater

The wet air oxidation (WAO) and catalytic WAO(CWAO) of the high strength emulsifying wastewater containing nonionic surfactants have been investigated in terms of COD and TOC removal. The WAO and homogeneous CWAO processes were carried out at the temperature from 433 K to 513 K, with initial oxygen pressure 1.2 MPa. It was found that homogeneous catalyst copper(Cu(NO3)2) had an fairly good catalytic activity for the WAO process, and the oxidation was catalyzed when the temperature was higher than 473K. Moreover, several heterogeneous catalysts were proved to be effective for the WAO process. At the temperature 473 K, after 2h reaction, WAO process could achieve about 75% COD removal and 66% TOC removal, while catalysts Cu/Al2O3 and Mn-Ce/Al2O3 elevated the COD removal up to 86%-89% and that of TOC up to 82%. However, complete elimination of COD and TOC was proved to be difficult even the best non-noble catalyst was used. Therefore, the effluent from WAO or CWAO process need to be further disposed. The bioassay proved that the effluent from WAO process was amenable to the biochemical method.     

二氧化钛的制备及光催化降解阳离子艳红染料

以Ti(OC4H9) 4为原料 ,采用沉淀法制备出光催化剂TiO2 微粒 ,并用所制得的样品对阳离子艳红染料进行了光催化降解实验。讨论了催化剂的制备条件对催化剂TiO2 降解性能的影响。结果表明 :沉淀pH为 8 0、粒径 <2 0 0目、经蒸馏水和无水乙醇洗涤、焙烧温度为 5 0 0℃所得的微粒催化降解效果最好。在此催化剂的作用下 ,经 3 0min的照射 ,阳离子艳红染料的降解率大于 87%