脱水污泥中脱色偶氮染料功能菌

近年来,随着印染与染料工业的发展,染料的数量和品种不断增多,由染料废水造成的污染呈增加的趋势,开发环境友好、高效、快速、低成本的染料废水处理方法是当前研究的热点。国内外常用的偶氮染料废水处理的方法可以分为物理法、化学法和生物法。传统的物化法虽然效果好,但较高的成本以及严重的二次污染,限制了其在实际中的应用,生物法以廉价、高效与环境友好等优势而广为应用。目前利用微生物处理偶氮染料废水的应用和研究居于首位,许多研究者致力于高效脱色偶氮染料微生物的筛选、分离和驯化[1-2]。本刊2014年第12期刊登了解井坤、花莉等的文章《脱水污泥中脱色偶氮染料功能菌群的驯化分离》[3]。作者以脱水污泥作为脱色偶氮染料功能菌群的新来源,经驯化分离获得降解混合偶氮染料的高效降解菌株若干,菌株所制备干粉也可在无外源碳源的条件下完全脱色金橙I,研究表明脱水污泥是耐胁迫工程菌株的理想种质来源。近年来该研究团队利用研究所得菌株,对脱水污泥处理不同偶氮染料废水的微生物群落结构进行了基于分子生物学的分析,得到了偶氮染料结构和功能群落结构组成的信息,研究结果表明偶氮染料结构同降解菌群落组成有对应关系,不同偶氮染料驯化下的混合微生物更倾向于形成以优势种群为主的特定微生物群落结构,而群落多样性在偶氮染料的脱色作用中不是主要因素[4];基于脱污污泥中分离得到的偶氮染料脱色菌种构建的聚氨酯泡沫固定化微生物体系,能够快速、反复用于偶氮染料废水的脱色[5]。由于实际偶氮染料废水的成分十分复杂,针对不同的偶氮染料废水构建特定的高效脱色微生物群落结构在实际中的应用有待进一步探究;其次本研究在固定化微生物的脱色过程中,采用的是较小的反应器,对于反应器放大后的脱色效果也需要进一步的研究。进行了脱色偶氮染料废水的微生物燃料电池体系的搭建和运行,证明分离株能够有效进行胞外电子传递,在脱色偶氮染料的同时实现产能资源化,同时说明脱水污泥也可作为保外电子呼吸菌的种质来源[6-7];在MFC同步脱色产电性能的研究中,虽然MFC加速了偶氮染料的脱色,但是其产电水平整体偏低,达不到有效利用水平,所以如何进一步提升产电能力从而到达有效利用水平也是亟待解决的问题。     

偶氮染料的微生物脱色研究进展

微生物法是染料废水治理的重要方法。本文综述了特异性酶作用下好氧细菌和真菌对偶氮染料的脱色以及厌氧条件下氧化还原介质作为电子穿梭体时偶氮染料的非特异性还原过程。指出厌氧偶氮还原是偶氮染料还原的主要形式, 电子供体不同脱色效率不同。对目前生物法去除偶氮染料存在的问题进行了分析, 提出了相应的对策措施。     

脱色希瓦氏菌(Shewanella decolorationis)S12T的脱色特性

从印染废水活性污泥中分离到一株高效染料脱色菌,经鉴定该菌株为希瓦氏菌属的一个新种,命名为脱色希瓦氏菌(Shewanelladecolorationis)S12T。该菌株在偶氮染料浓度为50mg/L的培养基中培养4h后,染料去除率达到96%,对偶氮染料的最高脱色浓度达到2000mg/L。在浓度为500mg/L的偶氮染料平板上生长4d后,可观察到明显的脱色圈。全波长光谱扫描的结果表明希瓦氏菌S12T以生物降解的方式对偶氮染料进行脱色。希瓦氏菌S12T的脱色酶为组成型的胞内酶。     

微生物染料脱色研究进展*

近年来,利用微生物对各种染料及染料废水脱色的研究报道很多,包括细菌、真菌等,脱色机制包括吸附脱色和降解脱色。综述了国内外有关这两大类微生物脱色研究的最新进展,对各种脱色机制在实际染料废水处理中的应用现状和研究方向进行了讨论。     

氧气对混合菌群脱色降解偶氮染料效果的影响

【背景】偶氮染料及其中间产物具有一定的环境毒性,利用混合菌群降解偶氮染料是一种环境友好型方法,但降解过程中氧气的存在起到至关重要的作用,可以促进或抑制偶氮染料的微生物降解作用。【目的】探讨氧气对偶氮染料微生物脱色液的影响,分析氧气对混合菌群脱色降解偶氮染料效果的影响。【方法】利用混合菌群DDMY1在3种培养条件(好氧、厌氧、兼氧)下,对7种偶氮染料进行脱色降解,探讨偶氮染料脱色液对氧气的响应情况,利用紫外可见分光光度法(ultraviolet visible spectrophotometry,UV-vis)和傅里叶变换红外光谱法(Fourier transform infrared spectroscopy,FTIR)对脱色产物进行分析。【结果】在兼氧和厌氧条件下反应48 h后的染料脱色液,与氧气充分接触后,部分偶氮染料微生物脱色液发生较为明显的复色现象,如活性黑5、直接黑38;UV-vis分析结果表明,这种复色现象是由于脱色液与氧气接触之后产生新物质所致;FTIR分析结果表明,混合菌群对发生复色反应的偶氮染料仍然具有一定脱色降解效果,但是脱色尚不够完全。【结论】兼氧和厌氧条件下,氧气对部分偶氮染料微生物脱色液具有较为明显的影响,从而影响混合菌群对偶氮染料的整体脱色效果,这可为今后研究偶氮染料彻底生物降解提供理论基础。     

微生物染料脱色研究进展

近年来,利用微生物对各种染料及染料废水脱色的研究报道很多,包括细菌、真菌等,脱色机制包括吸附脱色和降解脱色。综述了国内外有关这两大类微生物脱色研究的最新进展,对各种脱色机制在实际染料废水处理中的应用现状和研究方向进行了讨论。     

脱色希瓦氏菌(Shewanella decolorationis)S12T的脱色特性*

从印染废水活性污泥中分离到一株高效染料脱色菌,经鉴定该菌株为希瓦氏菌属的一个新种,命名为脱色希瓦氏菌(Shewanelladecolorationis)S12^T。该菌株在偶氮染料浓度为50mg/L的培养基中培养4h后,染料去除率达到96%,对偶氮染料的最高脱色浓度达到2000mg/L。在浓度为500mg/L的偶氮染料平板上生长4d后,可观察到明显的脱色圈。全波长光谱扫描的结果表明希瓦氏菌S12^T以生物降解的方式对偶氮染料进行脱色。希瓦氏菌S12相似文献   

脱水污泥中脱色偶氮染料功能菌群的驯化分离

【目的】获得降解混合偶氮染料的高效降解菌,应用于印染行业偶氮染料废水的生物处理和资源化。【方法】以某污水处理厂的脱水污泥作为分离源,经偶氮染料废水驯化后,分离筛选出9株偶氮染料脱色株(命名为T-1-T-9),通过形态观察、生理特征及基于16S rRNA基因序列的分子生物学鉴定,初步认定分离株分属于芽孢杆菌属(Bacillus)、微小杆菌属(Exiguobacterium)、寡单胞菌属(Stenotrophomonas)和副球菌属(Paracoccus)。【结果】所得分离株纯培养均可不同程度地脱色单一偶氮染料和混合偶氮染料,其中T-8对甲基橙和金橙I的脱色速率最大,40 h的脱色率分别为85.9%和86.2%,T-8菌株干粉也可在无外源碳源的条件下完全脱色金橙I。分离株混合培养脱色混合偶氮染料的效率明显高于纯培养,可达90.1%。【结论】脱水污泥作为脱色偶氮染料功能菌群的新来源具有良好的应用价值。     

绒毛栓孔菌菌丝体在无营养条件下对偶氮染料刚果红的脱色作用

【目的】在无营养条件下,利用白腐真菌绒毛栓孔菌(Trametes pubescens)菌丝体对染料进行脱色可减少试验成本,提高染料处理的实用性。【方法】将该菌株液体培养的菌丝体在无营养条件下对染料进行脱色,并对其中脱色效果较好的偶氮染料刚果红的脱色过程进行分析。在此过程中,测定了该菌株分泌的胞外胞内酶活力,优化影响因子如初始pH值、温度、染料浓度和盐度,同时利用气相色谱-质谱联用技术分析无营养条件下偶氮染料刚果红的降解产物。植物毒性试验测定刚果红经绒毛栓孔菌菌丝体脱色前后的毒性变化。【结果】菌丝体对偶氮染料刚果红有较好的脱色效果,在初始pH值为2.0,温度为30°C,染料浓度为80 mg/L,盐度为2.5%(质量体积比)时,150 r/min转速下培养7 d后脱色率可达80.52%。在此过程中,菌丝体可被连续使用2次,且其所分泌的酶系可降解染料。此外,通过气相色谱-质谱联用分析得到刚果红的降解产物为萘胺、联苯胺和叠氮萘。植物毒性试验显示在无营养条件下的绒毛栓孔菌菌丝体对染料有明显的脱毒作用。【结论】研究发现绒毛栓孔菌菌丝体在无营养条件下的偶氮染料废水处理中具有广阔的应用前景。     

白腐真菌对染料废水脱色及降解的研究

染料废水是最难处理的工业废水之一,近年来许多学者就白腐真菌对染料废水的脱色进行了广泛的研究,系统介绍了白腐真菌对染料脱色和降解作用的研究进展,脱色机理及其影响因素,旨在为以后真菌对染料废水的脱色及降解提供参考和依据。     

Bacterial Decolorization of Azo Dyes by Rhodopseudomonas palustris

Summary The ability of Rhodopseudomonas palustris AS1.2352 possessing azoreductase activity to decolorize azo dyes was investigated. It was demonstrated that anaerobic conditions were necessary for bacterial decolorization, and the optimal pH and temperature were pH 8 and 30–35 °C, respectively. Decolorization of dyes with different molecular structures was performed to compare their degradability. The strain could decolorize azo dye up to 1250 mg l⁻¹, and the correlation between the specific decolorization rate and dye concentration could be described by Michaelis–Menten kinetics. Long-term repeated operations showed that the strain was stable and efficient during five runs. Cell extracts from the strain demonstrated oxygen-insensitive azoreductase activity in vitro.     

藜芦醇和吐温80对白腐菌产木质素降解酶的影响及在偶氮染料脱色中的作用

担子菌PM2在限氮液体培养下,分泌木质素过氧化物酶和锰过氧化物酶;藜芦醇、吐温 80的补充,提高了该菌锰过氧化物酶的产生,获得的最大锰过氧化物酶Mnp酶活为254.2u/L、190.2 u/L,分别是对照的3.4倍和2.5倍。选择三种偶氮染料,在染料体系下,进一步分析藜芦醇、吐温 80对担子菌PM2产过氧化物酶及染料脱色的影响。结果表明,担子菌PM2分泌的锰过氧化物酶Mnp与染料脱色有关,脱色程度受其分子结构特征影响;吐温80的补充,更有利于染料的脱色降解,48h后三种染料均可达到80%以上的脱色率。     

Effectiveness of Rice Agricultural Waste,Microbes and Wetland Plants in the Removal of Reactive Black-5 Azo Dye in Microcosm Constructed Wetlands

Azo dyes are commonly generated as effluent pollutants by dye using industries, causing contamination of surface and ground water. Various strategies are employed to treat such wastewater; however, a multi-faceted treatment strategy could be more effective for complete removal of azo dyes from industrial effluent than any single treatment. In the present study, rice husk material was used as a substratum in two constructed wetlands (CWs) and augmented with microorganisms in the presence of wetland plants to effectively treat dye-polluted water. To evaluate the efficiency of each process the study was divided into three levels, i.e., adsorption of dye onto the substratum, phytoremediation within the CW and then bioremediation along with the previous two processes in the augmented CW. The adsorption process was helpful in removing 50% dye in presence of rice husk while 80% in presence of rice husk biocahr. Augmentation of microorganisms in CW systems has improved dye removal efficiency to 90%. Similarly presence of microorganisms enhanced removal of total nitrogen (68% 0 and Total phosphorus (75%). A significant improvement in plant growth was also observed by measuring plant height, number of leaves and leave area. These findings suggest the use of agricultural waste as part of a CW substratum can provide enhanced removal of textile dyes.     

Bioremediation of Textile Azo Dyes by Trichophyton rubrum LSK-27

Summary The potential of a recently isolated wood-degrading fungus, Trichophyton rubrum LSK-27, for effective decolorization of textile azo dyes was evaluated. Within two days of dye addition, the fungus was able to decolorize 83% of Remazol Tiefschwarz, 86% of Remazol Blue RR and 80% of Supranol Turquoise GGL in liquid cultures. The reactive dyes, Remazol Tiefschwarz and Remazol Blue, were removed by fungal biodegradation, while decolorization of the acid dye, Supranol Turquoise GGL, was accomplished mainly by bioadsorption. Therefore the fungus proved to be efficiently capable of both biodegradation and biosorption as the major dye removal mechanisms. The extent of biodegradation was associated with the levels of the extracellular ligninolytic enzymes such as manganese peroxidase and laccase.     

Degradation of Azo Dyes by Laccase and Ultrasound Treatment

The goal of this work was to investigate the decomposition of azo dyes by oxidative methods, such as laccase and ultrasound treatments. Each of these methods has strong and feeble sides. The laccase treatment showed high decolorization rates but cannot degrade all investigated dyes (reactive dyes), and high anionic strength led to enzyme deactivation. Ultrasound treatment can decolorize all tested dyes after 3 h at a high energy input, and prolonged sonication leads to nontoxic ionic species, which was demonstrated by ion chromatography and toxicity assays. For the first time, it was shown that a combination of laccase and ultrasound treatments can have synergistic effects, which was shown by higher degradation rates. Bulk light absorption and ion-pairing high-performance liquid chromatography (IP-HPLC) were used for process monitoring, while with reversed-phase HPLC, a lower number of intermediates than expected by IP-HPLC was found. Liquid chromatography-mass spectrometry indicated that both acid orange dyes lead to a common end product due to laccase treatment. Acid Orange 52 is demethylated by laccase and ultrasound treatment. Further results confirmed that the main effect of ultrasound is based on ˙OH attack on the dye molecules.     

Degradation of Azo Dyes by Trametes villosa Laccase over Long Periods of Oxidative Conditions

Trametes villosa laccase was used for direct azo dye degradation, and the reaction products that accumulated after 72 h of incubation were analyzed. Liquid chromatography-mass spectrometry (LC-MS) analysis showed the formation of phenolic compounds during the dye oxidation process as well as a large amount of polymerized products that retain azo group integrity. The amino-phenol reactions were also investigated by ¹³C-nuclear magnetic resonance and LC-MS analysis, and the polymerization character of laccase was shown. This study highlights the fact that laccases polymerize the reaction products obtained during long-term batch decolorization processes with azo dyes. These polymerized products provide unacceptable color levels in effluents, limiting the application of laccases as bioremediation agents.     

Biodegradation perspectives of azo dyes by yeasts

Azo dyes are the largest class of synthetic dyes, which are widely used in the textile industry. The amount of dyestuff does not bind to the fibers and is lost in wastewater during textile processing. The discharge of colored effluents into the environment is not only aesthetically unpleasing. Moreover, dyes and their break-down products cause toxic effects and they affect photosynthetic activity of aquatic systems by reducing light penetration. A number of microorganisms belonging to different taxonomic groups of bacteria, algae, fungi and yeast have been reported for their ability to decolorize azo dyes. In the literature the ability to decolorize azo dyes by yeasts, compared to bacterial and fungal species, has been studied in a few reports. Within this review, an attempt is made to elucidate some basic biological aspects associated with the azo dye degradation by yeasts and enzymes involved that are responsible for degradation process.     

耐碱的偶氮染料脱色菌筛选及其特性的研究

从浙江某污水处理厂的活性污泥中筛选出若干株在高pH条件下对偶氮染料酸性大红GR有脱色能力的菌株,经脱色验证得到一株具有高效脱色活性的菌株Z1,经鉴定为巴斯德葡萄球菌(Staphylococcus pasteuri),并对此菌株的脱色特性进行了初步研究。结果表明,在厌氧条件下,Z1在pH7~12,40h对50mg/L的酸性大红GR脱色率均可达90%以上。该菌株对染料有较强的耐受力,在酸性大红GR浓度为300mg/L时,48h的脱色率仍可达93%。此外,该菌株能够对多种偶氮染料脱色,具有较好的脱色广谱性,有望应用于处理工业废水中的偶氮染料。     

Reactive red azo dye degradation in a UASB bioreactor: Mechanism and kinetics

Textile industry uses azo dyes in its processes, which are complex organic molecules that are not easy to be degraded. Reactive dyes are especially difficult to remove from wastewater because of the characteristics of the molecule: one or more azo bonds, naphthalene‐disulfonate, triazine or chloro‐triazine, and phenyl‐amine groups. The degradation of the azo dye reactive red 272 was studied under anaerobic conditions in a hybrid Upflow Anaerobic Sludge Bed reactor (UASB) with an activated carbon bed. An adapted consortium of microorganisms was used in the kinetic study (batch) and to inoculate the UASB reactor. The experimental design identified the main factors determining the dye reduction efficiency are the initial concentration of dye and dextrose (as electron donor) and the residence time in the reactor. Dye reduction rate was decreased as the concentration increases in the wastewater; as a result, a kinetic model with a change from first to second order is proposed. The kinetic study showed that the process is first abiotic (adsorption) and then biotic (biodegradation).