一株新分离的云芝栓孔菌Z-1应用于木质素降解及染料脱色

木质素是一种非结晶性的复杂三维网状酚类高分子聚合物,被认为是木质纤维素生物质抗降解的天然屏障。探索并开发高效降解木质素的微生物资源已成为近些年来的研究焦点。本研究对新分离的一株具有潜在木质素降解能力的菌株Z-1开展了系列研究。首先通过形态学和系统发育分析将菌株Z-1鉴定为云芝栓孔菌Trametes versicolor。平板定性检测初步表明云芝栓孔菌T. versicolor Z-1具有较强的产过氧化物酶和漆酶能力。以木质素为唯一碳源时,T. versicolor Z-1对木质素的降解率和脱色率分别可达13.38%和26.43%。酶活检测分析表明该菌主要是通过分泌漆酶和锰过氧化物酶（manganese peroxidase,MnP）降解木质素。利用傅里叶变换红外光谱（fourier transform-infrared spectroscopy,FT-IR）、扫描电镜（scanning electron microscope,SEM）及气相色谱-质谱联用（gas chromatography-mass spectroscopy,GC-MS）对云芝栓孔菌T. versicolor Z-1降解后木质素残渣结构以及代谢物的鉴定分析结果证实了该菌对木质素的强降解能力,并表明该菌对木质素的降解途径包括酚醚键的断裂、芳香环侧链氧化裂解以及芳香环开环反应等。此外,该菌还对多种芳香类染料展现出了强的脱色能力,其中对刚果红、孔雀石绿和考马斯亮蓝R-250 3种染料的脱色率达到100%。本研究表明云芝栓孔菌T. versicolor Z-1具有应用于工业化木质素降解与芳香化合物类染料脱色的开发前景。     

硝酸盐还原促进毒害性有机污染物降解的研究进展

大量具有高毒性、持久性和生物蓄积性的有机污染物被排放到环境中,对生态环境和人类健康造成了严重威胁。近年来,利用硝酸盐作电子受体在厌氧条件下降解毒害性有机污染物,已取得一定的进展。本文综述了硝酸盐还原体系中几种典型毒害性有机污染物(多环芳烃、单环或杂环芳烃类有机物及卤代有机物)的厌氧降解研究进展。在此基础上,提出了硝酸盐还原促进毒害性有机污染物降解研究中存在的主要问题及其在加速污染环境净化方面的应用前景。     

对污染物有独特降解作用的白腐真菌

简述了白腐真菌对木质素的特殊降解过程,进而讨论了该真菌在降解污染物及造纸制浆方面可能的潜在用途。     

微生物降解硝基芳烃及其卤代衍生物的研究进展

硝基芳烃化合物作为一种重要的化工原料,广泛应用于医药、染料、农药等化工产品的合成。在给人类社会带来空前的物质繁荣的同时,其造成的环境污染问题也成为人类社会面临的重要挑战之一。微生物在这些环境污染物的降解中起着重要的作用。近几十年,环境微生物工作者对微生物降解硝基芳香污染物的各个步骤,包括趋化感应、分解代谢及生物修复进行了大量的研究工作,获得了丰富的知识。本文综述了硝基芳烃及其卤代衍生物的微生物代谢途径、代谢机理、趋化及修复研究进展,并对本领域的研究进行了展望,有助于全面认知硝基芳烃污染物的微生物降解过程,为污染环境修复提供理论基础。     

染料脱色菌与芳胺降解菌的筛选及降解染料研究

从印染厂废水处理系统的曝气池中分离到17株对多种染料有较高脱色能力的细菌,其脱色率都在80%以上,但偶氮染料脱色后产生的中间产物多数为无色的芳香胺类化合物,大多数细菌不能将其进一步降解。为此,通过富集培养和梯度驯化又筛选到一株以对硝基苯胺为唯一碳、氮源的菌株J18,该菌株虽对染料脱色能力很弱,却能够降解芳香胺类化合物。将芳香胺降解菌J18与染料脱色菌H两菌株混合培养,在最适条件下,结果使染料的脱色率和芳胺降解率均到达90%和85%以上,从而达到了彻底降解染料的目的。     

酵母菌在疏水性有机污染物去除方面的应用

介绍了酵母菌处理技术在疏水性有机污染物降解中的研究和应用进展,并分析了酵母菌表面特征与其降解活性及在废水处理系统中的稳定性之间的关系。酵母菌技术可以在高含油色拉油废水及含高分于量多环芳烃（PAH）废水的处理中发挥细菌无法替代的作用,酵母菌重要表面特征,特别是其疏水性和乳化能力对于其在疏水性有机污染物处理体系中的稳定性具有重要影响。     

木质素的微生物降解机制

研究微生物降解木质素的反应机理,可以从根本上解释微生物或酶对木质素的作用过程,对提高木质素降解效率,治理环境污染等具有非常重要的意义。从木质素结构的差异出发,总结了近年来研究木质素微生物降解机制所采用的主要模型化合物、研究方法,概述了微生物对木质素的三大作用机理:侧链氧化、去甲基化和芳香环断裂,以及参与这三个反应的主要微生物。     

嗜热菌对有机污染物的降解及其应用研究进展

有机污染物造成的环境问题日趋严重,嗜热菌具有高效降解环境有机污染物的潜力.嗜热菌在高温条件下降解有机污染物,代谢速度快,嗜温杂菌的竞争减少,同时高温环境下一些难降解有机物的溶解度和生物可利用性大大提高,有机污染物可得到快速、彻底降解.因此,嗜热菌对有机废水生物处理及有机物污染场地生物修复等意义重大.本文从嗜热菌降解有机污染物的特点、温度的影响、降解途径、降解酶及其编码基因及工程应用等角度,介绍了嗜热菌降解有机污染物的研究进展,并对嗜热菌降解有机污染物的机理、菌种资源储备、技术策略及应用研发等研究方向进行了展望.     

漆酶可降解底物种类的研究进展

漆酶是一种含铜离子的多酚氧化酶,广泛存在于植物及真菌中。漆酶含特有的铜离子,其功能为传递结构中的电子,使漆酶具有了较强的氧化还原能力,能与木质素、胺类化合物、芳香化合物等底物发生作用,且大多数反应的唯一产物为水。目前,漆酶在降解多种有毒物质和有害污染物方面表现出高效、成本较低的特性,如白腐真菌所产的高水平漆酶已广泛成熟应用在工业废水处理等生物整治和修复领域。近年来最新研究利用载体固定化酶的技术使漆酶能够在使用后回收反复利用且更具有稳定性,这降低成本的同时还保持了漆酶催化氧化的特性,克服了不少漆酶在解决环境污染中出现的问题。利用介体的介导作用解决了漆酶氧化还原电势较低的问题,大量增多了可降解底物的种类,使其在废水处理、污染物降解、土壤修复、工业染料漂白等领域的应用前景更广阔。对现有漆酶应用于各领域进行研究总结,综述了降解各领域中的有害污染物等底物种类,提出了利用漆酶的降解过程中的现有不足和改进方向,以期为生物法降解环境污染物的研究提供参考。     

细菌降解木质素的研究进展

木质素是自然界最丰富的芳香化合物,其分解与陆地上碳循环密切相关。提取木质纤维素中的葡萄糖使其转化成乙醇,是生产第二代生物能源的关键步骤。但是由于木质素是一种非常稳定的化合物,难以降解是实现生物乙醇转化的主要屏障,因此关于木质素的生物降解研究具有非常重要的意义。真菌降解木质素的研究已经深入的进行了多年,并取得丰富的成果,但是关于细菌降解木质素的研究还处在初级阶段。由于广泛的生长条件和良好的环境适应能力,细菌在木质素降解方面深受研究人员的关注。本文通过总结前人的研究成果,讨论了木质素的降解机制、代谢途径及细菌降解木质素的工业应用前景,同时还展望了分子生物学及生物信息学在木质素降解方面的应用前景。     

光合细菌对芳香族化合物厌氧降解的研究进展

许多被有毒性的芳香族化合物污染的环境实际上是缺氧的 ,因此芳香族化合物的厌氧降解逐渐引起人们的兴趣。芳香族化合物的厌氧还原降解机制从根本上不同于好氧条件下的氧化降解机制 ,而光合细菌一直以来是研究芳香族化合物厌氧降解的模式菌株。因此 ,从生理学、酶学及分子生物学角度出发概括了对光合细菌厌氧降解芳香族化合物的研究动态。     

Azo-dye degradation in an anaerobic-aerobic treatment system operating on simulated textile effluent

 Decolorisation of azo dyes during biological effluent treatment can involve both adsorption to cell biomass and degradation by azo-bond reduction during anaerobic digestion. Degradation is expected to form aromatic amines, which may be toxic and recalcitrant to anaerobic treatment but degradable aerobically. Methods for the quantitative detection of substituted aromatic amines arising from azo-dye cleavage are complex. A simple qualitative method is suggested as a way in which to investigate whether decolorisation is actually due to degradation, and whether the amines generated are successfully removed by aerobic treatment. Samples from a combined anaerobic-aerobic system used for treating a simulated textile wastewater containing the reactive azo dye Procion Red H-E7B were analysed by high-performance liquid chromatoraphy/ultraviolet (HPLC-UV) methods. Anaerobic treatment gave significant decolorisation, and respiration-inhibition tests showed that the anaerobic effluent had an increased toxicity, suggesting azo-dye degradation. The HPLC method showed that more polar, UV-absorbing compounds had been generated. Aerobically, these compounds were removed or converted to highly polar compounds, as shown by HPLC analysis. Since the total organic nitrogen (TON) decreased aerobically as organic N-containing compounds were mineralised, aromatic amine degradation is suggested. Although only a simple qualitative HPLC method was used, colour removal, toxicity and TON removal all support its usefulness in analysing biotreatment of azo dyes. Received: 2 August 1999 / Accepted: 3 September 1999     

藻对偶氮染料降解作用的研究

本实验系统地研究了藻对偶氮染料的降解作用。实验结果表明,藻对多种偶氮染料具有一定的降解作用,其降解程度与染料的结构和藻的种类等因素有关。通过降解机理的研究表明,,藻能够利用偶氮还原酶,作用于偶氮染料的偶氮双键,使其断裂,形成芳香胺类中间产物。藻还可以进一步利用芳香胺类物质。本研究结果启示,应重新评价藻在氧化塘降解有机物质过程中所起的作用,即在氧化塘中,藻不仅起供氧作用,还能够直接参与有机物质的降解。     

海洋石油降解微生物及其降解机理

微生物修复作为一种新型环保的生物修复技术,已成为海洋石油污染生物修复的核心技术。对海洋石油降解微生物的种类即细菌、蓝藻、真菌以及藻类进行了总结,对微生物对石油烃的降解途径与降解机理进行了综述。微生物降解烷烃的过程包括末端氧化、烷基氢过氧化物以及环己烷降解3种形式。微生物对芳香烃的降解是通过芳香烃被氧化酶氧化导致苯环开环来实现的。微生物对多环芳烃的降解是在单加氧酶或双加氧酶的催化作用下被最终降解为二氧化碳和水而被分解。并对影响石油烃降解微生物的因素包括温度、营养物质等因素进行了分析。     

Biodegradation of polycyclic aromatic hydrocarbons

The intent of this review is to provide an outline of the microbial degradation of polycyclic aromatic hydrocarbons. A catabolically diverse microbial community, consisting of bacteria, fungi and algae, metabolizes aromatic compounds. Molecular oxygen is essential for the initial hydroxylation of polycyclic aromatic hydrocarbons by microorganisms. In contrast to bacteria, filamentous fungi use hydroxylation as a prelude to detoxification rather than to catabolism and assimilation. The biochemical principles underlying the degradation of polycyclic aromatic hydrocarbons are examined in some detail. The pathways of polycyclic aromatic hydrocarbon catabolism are discussed. Studies are presented on the relationship between the chemical structure of the polycyclic aromatic hydrocarbon and the rate of polycyclic aromatic hydrocarbon biodegradation in aquatic and terrestrial ecosystems.     

Peroxidase mediated decolorization and remediation of wastewater containing industrial dyes: a review

In this article an effort has been made to review literature based on the role of peroxidases in the treatment and decolorization of a wide spectrum aromatic dyes from polluted water. Peroxidases can catalyze degradation/transformation of aromatic dyes either by precipitation or by opening the aromatic ring structure. Peroxidases from plant sources; horseradish, turnip, tomato, soybean, bitter gourd, white radish and Saccharum uvarum and microbial sources; lignin peroxidases, manganese peroxidases, vanadium haloperoxidases, versatile peroxidases, dye decolorizing peroxidases have been employed for the remediation of commercial dyes. Soluble and immobilized peroxidases have been successfully exploited in batch as well as in continuous processes for the treatment of synthetic dyes with complex aromatic molecular structures present in industrial effluents at large scale. However, recalcitrant dyes were also decolorized by the action of peroxidases in the presence of redox mediators.     

Gut microbiota promotes production of aromatic metabolites through degradation of barley leaf fiber

Barley leaf (BL) contains abundant plant fibers, which are important substrates for the metabolism and degradation by the gut microbiota. Here we show that mice fed a diet supplemented with BL exhibited altered gut bacterial composition characterized by the enrichment of fiber-degrading bacteria Lachnospiraceae and Prevotella. Gut microbiota-mediated BL degradation promoted butyrate and propionate production. Metabolomic analysis showed increased aromatic metabolites such as ferulic acid, 3-phenylpropanoic acid, 3-hydroxyphenylacetic acid and 3-hydroxyphenylpropionic acid in feces of mice fed with BL. Finally, antibiotic treatment and anaerobic fermentation confirmed the obligate role of gut microbiota in the production of aromatic metabolites during BL degradation. Together, these findings provide insights into a gut microbiota-mediated degradation process of BL fiber components, which results in the production of microbial-associated metabolites that may exert potential active effects on host physiology.     

Remediation and treatment of organopollutants mediated by peroxidases: a review

In this paper an effort has been made to review the literature on the role of peroxidases in the remediation and treatment of a wide spectrum of aromatic pollutants. Peroxidases can catalyse degradation/transformation of polycyclic aromatic hydrocarbons, polychlorinated biphenyls, organochlorines, 2,4,6-trinitrotoluene, phenolic compounds and dyes. These enzymes are also capable of treating various types of recalcitrant aromatic compounds in the presence of redox mediators. Immobilised peroxidases from plant and fungal sources have been used for the remediation of such types of industrial pollutants on a large scale.     

Fate and biodegradability of sulfonated aromatic amines

Ten sulfonated aromatic amines were tested for their aerobic and anaerobic biodegradability and toxicity potential in a variety of environmental inocula. Of all the compounds tested, only two aminobenzenesulfonic acid (ABS) isomers, 2- and 4-ABS, were degraded. The observed degradation occurred only under aerobic conditions with inocula sources that were historically polluted with sulfonated aromatic amines. Bioreactor experiments, with non-sterile synthetic wastewater, confirmed the results from the aerobic batch degradation experiments. Both ABS isomers were degraded in long-term continuous experiment by abioaugmented enrichment culture. The maximum degradation rate in the aerobic bioreactor was 1.6–1.8 gl^–1 d^–1 for 2-ABS and a somewhat lower value for 4-ABS at hydraulic retention times (HRT) of 2.8–3.3h. Evidence for extensive mineralization of 2- and 4-ABS was based on oxygen uptake and carbon dioxide production during the batch experiments and the high levels of chemical oxygen demand (COD) removal in the bioreactor. Furthermore, mineralization of the sulfonate group was demonstrated by high recovery of sulfate. The sulfonated aromatic amines did not show any toxic effects on the aerobic and anaerobic bacterial populations tested. The poor biodegradability of sulfonated aromatic amines indicated under the laboratory conditions of this study suggests that these compounds may not be adequately removed during biological wastewater treatment.