有机物生物降解性QSBR/SBR方法初探

定量／ 定性结构生物降解性相关关系（ＱＳＢＲ／ＳＢＲ） 对研究有机物的生物降解性具有重要意义。本文比较了七种常用的ＱＳＢＲ／ＳＢＲ 模型方法,结合实例对其原理、优缺点等进行了论述。     

有机污染物湿地生物降解实验规律研究

本文以苯，甲苯和萘为对象，通过实验研究，测定有机污染物的土壤－水吸附平衡过程，在水溶液中生物降解过程以及在湿地系统（即土壤－水－微生物系统）中生物降解过程，并以质量守恒定律为基础，建立有机污染物湿地生物降解过程综合数学模型，数学模型通过实验验证，利用模型，定量预测了污染物生物降解所需的时间和程度，并提出动力学因子FK，判断污染物湿地生物降解速度的控制因素，定量预测了污染物在土壤固相的浓度分布规律。     

高盐条件下活性艳红K-2BP的生物脱色动力学模型研究

在高盐条件下,通过耐盐菌群对偶氮染料K-2BP废水厌氧降解动力学实验,模拟得出偶氮染料K-2BP和盐浓度对生物降解双重影响动力学模型.其抑制常数KIS和KT值分别为(329.5±175.8)mg/L和(39.7±27.1)g/L,并通过动力学模型预测的数据和实验数据对比,耐盐菌可用动力学模型描述其在高盐条件下对染料的降解.     

偶氮染料的微生物降解

本文主要综述了染料的微生物降解,重点介绍了偶氮染料降解微生物类群及其在自然界中的分布;降解偶氮染料的微生物菌种的筛选、分离、纯化、驯化;并从偶氮染料的分子结构探讨了其与微生物降解之间的关系;偶氮染料微生物降解代谢途径和遗传基础;讨论了微生物菌种在纺织印染工业废水的处理中的应用前景。     

废水中硝基酚类化合物生物降解的研究进展

硝基酚是一类重要且常用的化工原料，一些硝基酚毒性大且难以生物降解，被美国环保局列入“优先控制污染物名单”。在自然环境条件下，硝基酚的生物降解速率缓慢，导致硝基酚在环境中长期滞留和积累。分析了人工强化条件下废水中硝基酚的生物降解性能，主要从具有降解硝基酚能力的微生物、硝基酚的厌氧生物降解性、硝基酚的好氧生物降解性和硝基酚的共基质代谢降解方面进行了较全面的综述，讨论了该研究当前仍存在的一些问题和研究展望。     

脂肪酰基氨基酸对矿物润滑油生物降解性的影响研究

通过生物降解试验研究了N-月桂酰基谷氨酸、N-月桂酰基甘氨酸、N-月桂酰基丙氨酸和N-油酰基甘氨酸4种脂肪酰基氨基酸对HVI 350矿物润滑油生物降解性的影响，采用高倍电子显微镜分析了生物降解过程中微生物数量和形态变化。结果表明，在矿物润滑油中添加少量脂肪酰基氨基酸后，矿物润滑油的生物降解性能明显改善，且生物降解过程中微生物数量增多、形态发生变化，这可能是脂肪酰基氨基酸增加了微生物的营养，且具有表面活性，有利于细胞的吸收，从而促进了矿物润滑油生物降解。     

缺氧-好氧生物滤池中高效菌对活性红KN-3B的降解特性

为了研究高效脱色菌在缺氧好氧生物滤池（A/O biofilter）中对偶氮染料的降解特性，以活性红KN-3B（C.I. reactive red 180）为降解对象，缺氧生物滤池以火山碎石为填料，接种高效脱色菌CK3柯氏柠檬酸杆菌启动，好氧生物滤池以牡蛎壳为填料，接种污水处理厂活性污泥启动。试验考察了不同工况下缺氧-好氧生物滤池对色度和COD的去除效果，结果表明：生物滤池中微生物对偶氮染料活性红KN-3B的脱色和对COD降解的最适pH条件为弱酸性；缺氧滤池中高效菌对色度的去除需要外加碳源，且增加外加碳源有助于脱色率的提高；该高效菌为耐盐菌，当进水NaCl浓度达30 g/L时，色度去除率仍可达93%以上；当染料负荷达500 mg/L时，脱色率仍可达95%。通过紫外-可见扫描图谱分析初步推断CK-3柯氏柠檬酸杆菌对偶氮染料活性红KN-3B的脱色主要是生物降解作用。     

脂肪酰基氨基酸对矿物润滑油生物降解性的影响研究

通过生物降解试验研究了N-月桂酰基谷氨酸、N-月桂酰基甘氨酸、N-月桂酰基丙氨酸和N-油酰基甘氨酸4种脂肪酰基氨基酸对HVI350矿物润滑油生物降解性的影响，采用高倍电子显微镜分析了生物降解过程中微生物数量和形态变化。结果表明，在矿物润滑油中添加少量脂肪酰基氨基酸后，矿物润滑油的生物降解性能明显改善，且生物降解过程中微生物数量增多、形态发生变化，这可能是脂肪酰基氨基酸增加了微生物的营养，且具有表面活性，有利于细胞的吸收，从而促进了矿物润滑油生物降解。     

精制油废水处理工艺研究

精制油废水的浓度高，水质变化大，生物降解性好，经试验，采用物化处理除油及生物处理后出水可达排放标准，对该废水的生物处理工艺，可生物降解性，营养，硫酸盐的影响，活性污泥率等作了较为深入的探讨。     

气相介质阻挡放电氧化降解酸性红88的机理

为了有效处理难生物降解的染料废水，采用气相介质阻挡放电产生以羟基自由基为主的氧化性物质，对偶氮染料酸性红88（AR88）进行了氧化降解，并对放电过程中各化学效应对AR88降解的作用机理进行了分析。结果表明，当用相对湿度100％的空气为气源时，放电过程中生成的活性物种如OH·、O，和H2O2是引起放电过程中AR88氧化降解反应的主体，其中OH·在AR88的降解过程中起主要作用，O3参与了对AR88的氧化降解，H2O2对AR88的降解没有明显作用。采用GC／MS分析AR88的主要降解中间产物为萘磺酸、1，2-萘醌、1，2-苯并吡喃酮、萘酚和邻苯二甲酸。通过产物测定和前线电子密度理论，推测了降解途径。     

The effect of pre-ozonation on the biocompatibility of reactive dye hydrolysates

Pre-ozonation of 14 different reactive dyestuff hydrolysates at alkaline pH was investigated to assess possible relationships between ozone transfer efficiency, first order decolourization kinetics, release of initially complexed heavy metals and relative changes in the biodegradability of the partially oxidized dye waste samples. Biocompatibility of the raw (untreated) and ozonated dye hydrolysates was comparatively tracked through specific oxygen uptake rate measurements from which the respirometric inhibition of biological activated sludge imparted by raw and ozonated reactive dye wastewater with respect to synthetic domestic wastewater was determined. It could be demonstrated that preliminary ozonation of reactive azo dyes increases their biological compatibility more significantly than formazan copper complex, copper complex azo and phythalocyanine dyes as a consequence of heavy metal release associated with the cleavage of associated chromophoric groupings right at the initial stages of pre-ozonation.     

Decolorization and biodegradability of photocatalytic treated azo dyes and wool textile wastewater

The photodegradation and biodegradability have been investigated for four non-biodegradable commercial azo dyes, Reactive YellowKD-3G, Reactive Red 15, Reactive Red 24, Cationic Blue X-GRL, an indicator. Methyl Orange, and one industrial wool textile wastewater, using TiO2 suspensions irradiated with a medium pressure mercury lamp. The color removal of dyes solution and dyeing wastewater reached to above 90% within 20-30 min. of photocatalytic treatment. Biochemical oxygen demand (BOD) was found to increase, while chemical oxygen demand (COD), total organic carbon (TOC) decreased, so that the ratio of BOD5/COD of the wastewater increased from original zero up to 0.75. The result implies that photocatalytic oxidation enhanced the biodegradability of the dye-containing wastewater and therefore relationship between decolorization and biodegradability exists. When the color disappeared completely, the wastewater biodegraded normally and could be discharged for further treatment. The experimental results demonstrate that it is possible to combine photocatalysis with conventional biological treatment for the remedy of wastewater containing generally non-biodegradable azo dyes.     

Degradation of azo dyes by algae

The degradation of azo dyes by algae was evaluated and it was found that certain algae can degrade a number of azo dyes to some extent. The reduction rate appears to be related to the molecular structure of the dyes and the species of algae used. The azo reductase of algae is responsible for degrading azo dyes into aromatic amine by breaking the azo linkage. The aromatic amine is then subjected to further metabolism by algae. It is proposed in this paper that in stabilization ponds, algae can play a direct role in the degradation of azo dyes, rather than only providing oxygen for bacterial growth.     

Non-enzymatic reduction of azo dyes by NADH

Nicotinamide adenine dinucleotide (NADH) reduces a variety of azo dyes by four electrons to generate the corresponding aromatic amines. This reduction is pH-dependent and increases with decreasing pH. Reduction of 4-(4'-sulfophenylazo)-phenol and 2-(4'-sulfophenylazo)-phenol, specifically substituted with methyl, methoxy, halo, and nitro groups, was examined to determine the susceptibility of azo dyes to reduction by NADH. Except for the nitro-substituted azo dyes, all other azo dyes were reduced. Possible mechanisms of reduction are proposed. The implications of our findings to microbial degradation and mammalian metabolism of azo dyes are discussed.     

Ozonation of an azo dye C.I. Remazol Black 5 and toxicological assessment of its oxidation products

The effect of ozonation (20.5 mgl(-1)) on the degradation processes of an azo dye, Remazol Black 5 (RB5; CI) was studied. Conventional parameters such as chemical oxygen demand (COD), total organic carbon (TOC), pH, conductivity, colour removal, biodegradability (BOD(5/28)), and toxic potential of the dye and its degradation products were monitored during the process. The results obtained indicated that ozonation is a highly effective way to remove the colour of a corresponding dye solution. However, a considerable organic load still remained as indicated by high COD and TOC residues. The COD, TOC reductions were about 40% and 25% for 6 h ozonation of 2 gl(-1) RB5 aqueous solution. During the ozonation process the rapid decrease of pH and the sharp increase of conductivity indicated the formation of acidic by-products and small fragments and ions which were identified by high performance ion chromatography. The BOD28 data revealed that first by-products after partial ozonation (10-150 min) of RB5 were more biodegradable than the parent compound and ozonation can enhance the biodegradability of azo dyes. During the first 150 min of total 360 min of oxidation, the formation of first by-products with high toxic potential took place as it could be confirmed by two acute toxicity-screening tests, the bioluminescence test (Vibrio fischerii) and the neutral red cytotoxicity assay (rat hepatoma cells). The significant enhancement of microbial biodegradability after long-term ozonation could also be seen as a decrease of toxic intermediates in correlation with the ozonation time as indicated in BOD28 biological degradation test results.     

Decolorization of mono-azo dyes in wastewater by advanced oxidation process: A case study of acid red 1 and acid yellow 23

Advanced Oxidation Processes (AOPs) have been used as emerging wastewater treatment technologies which can effectively handle various hazardous organics in wastewater and groundwater. The photooxidation of two non-biodegradable azo dyes, acid red 1 and acid yellow 23, were studied in an UV/hydrogen peroxide photochemical reactor with a 5 kW low pressure mercury lamp. It was observed that the decomposition of both azo dyes were pseudo-first order reactions with respect to the azo dye concentrations. Simultaneously, the effects of hydrogen peroxide dosage, pH, initial concentration of the azo dyes and intensity of UV light were also studied. Moreover, the time required for the 50% removal of azo dyes and observed pseudo-first order rate constants were used as parameters to show the efficiency of azo dye treatment.     

Azo dye decolourisation by anaerobic granular sludge

The decolourisation of 20 selected azo dyes by granular sludge from an upward-flow anaerobic sludge bed (UASB) reactor was assayed. Complete reduction was found for all azo dyes tested, generally yielding colourless products. The reactions followed first-order kinetics and reaction rates varied greatly between dyes: half-life times ranged from 1 to about 100 h. The slowest reaction rates were found for reactive dyes with a triazine reactive group. There was no correlation between a dye's half-life time and its molecular weight, indicating that cell penetration was probably not an important factor. Since granular sludge contains sulphide, eight dyes were also monitored for direct chemical decolourisation by sulphide. All these dyes were reduced chemically albeit at slower rates than in the presence of sludge at comparable sulphide levels. Increasing sulphide concentrations, even when present in huge excess, stimulated the azo reduction rate. The results indicate that granular sludge can decolourise a broad spectrum of azo dye structures due to non-specific extracellular reactions. Reducing agents (e.g., sulphide) in sludge play an important role. The presence of anaerobic biomass is probably beneficial for maintaining the pools of these reduced compounds.     

Degradation mechanism of azo dye C. I. reactive red 2 by iron powder reduction and photooxidation in aqueous solutions

We have made a comparison of the UV-VIS spectra of three azo dyes, C. I. reactive red 2, orange II and C. I. reactive black 8, in aqueous solutions during treatment with iron powder reduction and photooxidation. From this, we propose their mechanisms for reduction photooxidation. GC/MS analyses of the degradation products of the dye C. I. reactive red 2 demonstrated some important steps producing hydrogenated azo structure, substituted benzene and substituted naphthalene.