利用高炉瓦斯泥-H_2O_2处理硝基苯废水

以高炉瓦斯泥为铁源,通过其在酸性条件下与H2O2形成Fenton/类Fenton反应体系来处理硝基苯废水,考察了p H、H2O2用量、高炉瓦斯泥用量及反应时间对硝基苯降解率的影响,并对降解机理进行了分析表征。实验结果表明,在p H为3、高炉瓦斯泥用量为0.5 g/L、H2O2用量为10 m L/L、反应时间为60 min的条件下,100 mg/L的硝基苯溶液中硝基苯的降解率达87.88%;硝基苯先被氧化生成硝基苯酚、硝基苯二酚、对苯醌等中间产物,然后再进一步氧化生成二氧化碳和水达到降解的目的。     

密度泛函理论方法研究铝-麦芽酚配合物的形态结构与水交换反应

在B3LYP/6-311+G(d,p)基组水平下采用密度泛函理论方法系统开展了以下工作:(1)优化得到1∶1、1∶2和1∶3铝-麦芽酚配合物10种可能构型的静态结构、NPA电荷以及能量参数,计算得到Al(ma)3配合物4种异构体的核磁共振、紫外和红外等光谱学数据并与文献实验值比较,证明本文采用的计算方法和模型适用于铝-麦芽酚体系的研究;(2)模拟1∶1和1∶2铝-麦芽酚配合物9种可能位点的水交换反应,其中3个位点计算得到的水交换反应速率对数log kex(s-1)分别为2.4(Al(ma)(H2O)2+4(cis to ma))、2.6(cis-Al(ma)2(H2O)+2(I))和3.0(trans-Al(ma)2(H2O)+2(I)),与实验值2.5(Al(ma)2+)和3.3(Al(ma)+2)相符,说明相应位点为反应活性位点;(3)探讨铝-麦芽酚配合物毒性与其形态结构之间的相关机制。     

Fenton流化床陶瓷膜反应器处理造纸废水的膜污染与清洗

采用Fenton流化床陶瓷膜反应器处理造纸废水二级出水,研究了陶瓷膜膜污染的机理,提出了相应的清洗再生方案。实验结果表明:Fenton流化床陶瓷膜反应器处理后废水的溶解性有机碳和色度去除率分别达到84.2%和94.1%。通过Darcy定律模型计算,过滤阻力主要来自于滤饼层阻力,约占总阻力的62.1%;滤饼层中主要污染物为悬浮固体,约占滤饼层总质量的75.4%;疏水性有机物是造成滤饼层污染的主要溶解性有机物,而亲水性有机物更易造成膜孔堵塞;腐殖酸对滤饼层和膜孔堵塞影响较大,而蛋白质比多糖更易引起膜孔堵塞。采用HNO_3清洗污染膜效果最佳,在HNO_3质量分数1.00%、反应时间15 min时,膜通量恢复率达73.6%。     

Citrobacter sp. CK3对活性红KN-3B的脱色反应动力学研究

采用脱色菌Citrobacter sp. CK3,以活性红KN-3B染料为处理对象,在厌氧批式反应条件下,系统考察了pH值,温度和染料浓度对脱色反应速度的影响;通过动力学模拟及反应过程中染料的UV-Vis扫描图分析,探讨了脱色反应机理。结果表明：Citrobacter sp. CK3对活性红KN-3B的脱色反应的适宜pH为7～9;脱色反应速度在温度为32℃时达到最大。染料初浓度从57 mg/L逐渐增大到458 mg/L时脱色率逐渐降低。脱色过程中染料的偶氮键发生断裂,脱色反应符合二级反应动力学。     

磷酸活化石墨的氧还原特性以及用于微生物燃料电池阴极

研究了磷酸活化对石墨电极上氧还原反应的影响,并考察了磷酸活化石墨材料应用于微生物燃料电池阴极的可行性。首先以循环伏安和电化学阻抗谱等电化学方法考察了经磷酸活化的石墨材料的氧还原能力,发现经质量分数为85%磷酸活化12 h后其氧还原能力最强;然后将活化石墨材料应用于微生物燃料电池的阴极,进行极化曲线和功率密度曲线的测定。结果表明,磷酸活化阴极微生物燃料电池的最大功率密度可达7.92 W/m3,为未活化石墨阴极微生物燃料电池的3.4倍;同时进行了电化学比表面积的测定及FTIR的分析测定,结果表明,磷酸活化石墨颗粒的比表面积(7.716m2/g)较未活化颗粒(10.940 m2/g)略有减小,但其表面官能团的数量和种类发生了很大变化。表面官能团的变化可能是导致石墨材料氧还原能力增强及MFCs产电性能提高的重要原因。     

用YYG型冷原子荧光测汞仪测定天然水中总汞的仪器工作条件选择

国产YYG型系列测汞仪是利用原子荧光测定汞具有较高的灵敏度这一特点设计的测汞专用仪器。本文通过分析实验,对使用YYG型测汞仪时如何选择仪器最佳使用条件进行了分析探讨,使之能够满足测定天然水中汞的要求。     

Comparison of homologous and heterologous formats in nanocolloidal gold-based immunoassays for parathion residue determination

The effectiveness of homologous and heterologous formats in a nanocolloidal gold-based immunoassay for pesticide residue determination was investigated. Parathion, one of the most toxic organophosphorus pesticides, was used as the target analyte. One-step homologous and heterologous test strips based on a nanocolloidal gold-labeled monoclonal antibody were developed for the rapid detection of parathion residues. The results showed that the heterologous format was more effective than the homologous format, being more sensitive, more specific to parathion and more tolerant of matrix interferences. The best competitive hapten was found to have a moderate heterology and the opposite electronic distribution to the immunizing hapten. The detection limits for parathion using the preferred heterologous strip were 1 μg/L in water samples and 5 μg/kg in soil and food samples.     

水合改性对钙基吸收剂循环捕集CO2的影响

在钙基吸收剂捕集CO2的过程中,吸收剂转化率会随着循环次数的增加而迅速降低。钙基吸收剂的水合改性作为改善吸收剂循环转化率的主要方法之一受到了国内外学者的广泛关注。总结了目前国内外研究者对不同的吸收剂、循环捕集条件下的水合改性方法的研究成果。结果表明,在循环过程中的不同阶段对吸收剂进行水合处理后得到的效果不同。其中,在碳酸化阶段、煅烧阶段、循环捕集前预处理以及煅烧后对吸收剂水合改性．吸收剂捕集CO2的能力均得到了改善;碳酸化反应后对吸收剂进行水合处理是否对循环吸收有利还存在争议。目前,利用水合改性的方法提高钙基吸收剂循环捕集CO2能力的机理还存在争议,且水合改性后的吸收剂机械性能差以及此方法能耗高的问题尚待解决。     

Influence of oxalic acid formed on the degradation of phenol by Fenton reagent

The objective of this work is to examine the influence of oxalic acid formed on the degradation of phenol by Fenton reagent. Oxalic acid formed at initial stage within 30 min significantly suppresses the reduction of ferric ion, thus terminating degradation reaction. The yield of oxalic acid is dependent on the amount of ferrous ion dosed since the minimal amount of oxalic acid is formed after the degradation reaction terminates. Mineralization of phenol by Fenton reagent stagnates after 120 min under the conditions used in this study. The reason why the mineralization stagnated can be assumed to be following two mechanisms other than the depletion of H₂O₂. In the case where a small amount of ferrous ions is dosed, the reduction of ferric ions is minimal by oxalic acid formed. In the case where a large amount of ferrous ions is dosed, the amount of degradable organic compounds is insufficient owing to preferential conversion to oxalic acid. The mineralization can be enhanced by the intermittent dosing of ferrous ions, which facilitates the suppression of oxalic acid formation during the degradation by Fenton reagent.     

Method of removal of volatile organic compounds by using wet scrubber coupled with photo-Fenton reaction - Preventing emission of by-products

The photo-Fenton reaction was applied as a novel method for the removal of volatile organic compounds (VOCs) in the gas phase, and its effectiveness was experimentally examined. In conventional VOCs removal methods using a photocatalyst or ozone, VOCs are oxidized in the gas phase. Therefore, incompletely oxidized intermediates, which may have adverse effects on health, are likely to contaminate the treated air. On the other hand, in the VOCs removal method developed in this study, because the VOCs are oxidized in the liquid phase by the photo-Fenton reaction, any incompletely oxidized intermediates produced are confined to the liquid phase. As a result, the contamination of the treated air by these harmful intermediates can be prevented. Using a semi-batch process, it was found that the removal efficiency for toluene in a one-pass test (residence time of 17 s) was 61%, for an inlet toluene gas concentration of 930 ppbv, an initial iron ion concentration of 20 mg L⁻¹, and an initial hydrogen peroxide concentration of 630 mg L⁻¹. The removal efficiency was almost constant as long as H₂O₂ was present in the solution. Proton transfer reaction mass spectrometry analysis confirmed the absence of any incompletely oxidized intermediates in the treated air.