土壤脲酶和脱氢酶对活性X-3B红污染暴露的耐受性及机理研究

采用微宇宙实验方法,研究了棕壤、褐土、红壤等3种我国典型土壤中脲酶和脱氢酶对染料活性X-3B红污染的耐受性及其机理.实验结果表明,3种土壤中的脲酶和脱氢酶活性在试验较低浓度的活性X-3B红污染的环境中均被促进,但被促进的程度有所差异,具体表现为棕壤脲酶活性被促进的效果最为明显,其次红壤,褐土最弱;较低浓度的活性X-3B红污染对褐土脱氢酶活性的促进作用最强,其次红壤,棕壤最弱.3种土壤的脲酶和脱氢酶活性被促进的效果随着时间的推移逐渐减弱.3种土壤的脲酶和脱氢酶活性对高浓度的活性X-3B红污染并没有显示受抑制的趋势.相反,二者基本维持在未受染料活性X-3B红污染的对照土壤的活性水平.因此可以初步认为,土壤脲酶和脱氢酶对染料活性X-3B红的污染暴露毒性有耐受作用.基于实验结果,还就2种酶对活性X-3B红污染暴露的耐受机理进行了分析与探讨.     

Involvement of chloride anion in photocatalytic process

The effect of Cl^- on photocatalytic degradation（PCD） of pollutants is an important factor since it is ubiquitous in nature. In general, Cl^- showed an inhibition on photodegradation due to its scavenging HO- radicals. In this paper, experiments were carried out to examine the effects of CI on the PCD of Methylene Blue （MB） and Orange II （OII） in aqueous TiO2 suspensions under UV light illumination. It was found that low concentration of Cl^- （ 〈 0.01 mol/L） showed little influence on both dyes, however, high concentration of Cl^- （ 〉 0.10 mol/L） had a very different influence on the decolorization of dyes： a significant inhibition for MB but a great promotion for Oll. In the presence of 0.50 mol/L Cl^- , the rate decreased by 70% for MB while increased 7.5-fold for Oll. Furthermore, two bands in the ultraviolet region of Oll were rapidly broken down. The proposed mechanism was discussed in detail.     

羟基铝蒙脱石去除染料弱酸性深蓝GR的研究

在[OH^-]/[A1³⁺]=2.4的反应条件下,利用A1³⁺与碱液反应制备出Keggin离子,并由此制备出羟基铝蒙脱石.XRD-衍射数据表明:羟基铝蒙脱石的层间距由原来的12.58A(d₀₀₁)增加到18.63A.研究了染料弱酸性深蓝GR在7种改性蒙脱石上的吸附.结果表明:酸性条件下,羟基铝蒙脱石处理有机污染物的去除率高,用0.0200g处理25ml弱酸性深蓝GR溶液,去除率可高达95%以上.由等温吸附线可知:弱酸性深蓝GR在不同改性蒙脱石上的吸附机理主要为表面吸附、离子交换和分配作用.     

Cadmium transport mediated by soil colloid and dissolved organic matter： A field study

This study investigated the potential role of soil colloids and dissolved organic matter (DOM) in transporting Cd through in situ undisturbed paddy soil monoliths. Brilliant Blue was used as a tracer to assess the e ect of preferential flow on Cd down migration. Experimental results showed that deep penetration of Cd and Brilliant Blue into the soil profile took place due to the preferential flow through macropores, mainly earthworm channels, with much of chemicals thus bypassing the soil matrix. Dye tracer and Cd distribution within the soil matrix was fairly restricted to several centimeters. Colloid restrained the migration of both dye and Cd in the matrix and preferential flow area. DOM facilitated the transport of Cd and Brilliant Blue in matrix and macropores by about 10 cm over that of the control. Pearson’s is correlation analysis revealed strong associations between Brilliant Blue concentrations, exchangeable Cd and total Cd concentrations in three studied plots indicating that they had taken the same preferential flow pathway.     

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。     

偶氮染料的厌氧——好氧生物降解过程和影响因素

偶氮染料是总量最大、种类最多的合成染料,其降解处理通常采用厌氧-好氧技术。厌氧过程可实现偶氮染料的还原,好氧过程则完成还原产物芳香胺的去除。厌氧过程受偶氮染料结构和浓度、底物的种类和浓度、其他电子受体、氧化还原介体、温度和DO等环境因素以及水力停留时间的影响。好氧条件下芳香胺的降解过程受其自身的结构、浓度、外加碳源以及降解体系等影响,且自氧化过程影响了芳香胺的生物降解。在实际废水处理中应创造良好的条件提高偶氮染料的厌氧一好氧生物降解效率。     

The application of iron mesh double layer as anode for the electrochemical treatment of Reactive Black 5 dye

In this work a novel anode configuration consisting of an iron mesh double layer is proposed for the electrochemical treatment of wastewater. The removal of Reactive Black 5 dye(RB5) from synthetic contaminated water was used as a model system. At a constant anode surface area, identical process operating parameters and batch process mode, the iron mesh double layer electrode showed better performance compared to the conventional single layer iron mesh. The double layer electrode was characterized by RB5 and chemical oxygen demand(COD) removal efficiency of 98.2% and 97.7%, respectively, kinetic rate constant of 0.0385/min, diffusion coefficient of 4.9 × 10~(-5)cm~2/sec and electrical energy consumption of 20.53 kWh/kgdye removed. In the continuous flow system, the optimum conditions suggested by Response Surface Methodology(RSM) are: initial solution p H of 6.29,current density of 1.6 m A/cm~2, electrolyte dose of 0.15 g/L and flow rate of 11.47 m L/min which resulted in an RB5 removal efficiency of 81.62%.     

Photocatalytic degradation of Acid Blue 62 over CuO-SnO2 nanocomposite photocatalyst under simulated sunlight

The novel CuO-SnO2 nanocomposite oxide photocatalysts were prepared by simple co-precipitation method, and characterized by X- ray diffraction, transmission electron microscopy, N2 adsorption-desorption measurement and UV-Vis diffuse reflectance spectroscopy. The photocatalytic activities of CuO-SnO2, evaluated using the photodegradation of Acid Blue 62 as a probe reaction under the irradiation of Xenon light, were also found to be related to the calcination temperature and the molar ratio of Cu to Sn. The maximum photocatalytic activity of the CuO-SnO2 photocatalyst was observed to be calcined at 500~C for 3 h （the molar ratio of Cu to Sn was 1：1） due to the sample with good crystallization and high surface area. It also showed much higher photocatalytic activity in treatment dye wastewater under simulated sunlight irradiation compared to Degussa P25 TiO2.     

臭氧氧化四种偶氮染料废水的效果研究

以酸性大红、中性枣红、阳离子红、活性黑5四种模拟印染废水开展O3氧化偶氮染料的效果研究.实验中发现O3对染料具有非常好的脱色效果,30 min后除中性枣红外其他三种染料脱色率接近100％,但是单独O3的TOC去除率不高.光谱扫描表明,处理后染料的特征吸收峰很快消失,而紫外光区的吸收峰变化很小,推测O3氧化以直接氧化为主,打开了染料分子的发色基团,但并未将染料分子彻底氧化.还应加强O3氧化能力、彻底矿化去除污染物的研究.     

Decolorization of Orange II using an anaerobic sequencing batch reactor with and without co-substrates

We investigated the decolorization of Orange II with and without the addition of co-substrates and nutrients under an anaerobic sequencing batch reactor (ASBR). The increase in COD concentrations from 900 to 1750 to 3730 mg/L in the system treating 100 mg/L of Orange II-containing wastewater enhanced color removal from 27% to 81% to 89%, respectively. In the absence of co-substrates and nutrients, more than 95% of decolorization was achieved by the acclimatized anaerobic microbes in the bioreactor treating 600 mg/L of Orange II. The decrease in mixed liquor suspended solids concentration by endogenous lysis of biomass preserved a high reducing environment in the ASBR, which was important for the reduction of the Orange II azo bond that caused decolorization. The maximum decolorization rate in the ASBR was approximately 0.17 g/hr in the absence of co-substrates and nutrients.