有机磷酸酯阻燃剂/增塑剂的生物降解及其机制研究进展

有机磷酸酯(Organophosphate Esters,OPEs)阻燃剂/塑化剂对人类有潜在的健康风险并且广泛分布在各种环境介质中,为应对OPEs带来的挑战,绿色、高效的生物降解方式成为了当前的研究热点.文章目的 是叙述目前已知的OPEs的生物降解过程及机制,主要围绕TBP、TPHP这2种热点OPEs来描述生物降解途...     

有机物生物降解性评价方法综述

评价有机物生物降解性的方法和文献很多,但缺乏系统性介绍评价方法及指导方法选择的综述性文献.本文围绕有机物的生物降解性评价,简要介绍了评价有机物生物降解性的指示性参数及厌、好氧有机物生物降解性评价方法,着重介绍了评价方法选择的标准和原则,并详细分析了不同试验方法使用过程中产生有机物生物降解率差异的原因.最后,以世界经济合作与发展组织(OECD)制定的标准为例,全面介绍了该评价方法的选择使用过程并整合这一评价体系绘制了方法选择路线图,指出了各项试验方法的优越性.     

细菌好氧反硝化研究进展

阐述了好氧反硝化细菌的种类及有关性质 ,并从电子理论、氧的浓度、反硝化酶系等方面对细菌好氧反硝化的作用机制进行了探讨 ,对细菌好氧反硝化的研究概况、进展及其研究意义和目前存在的问题作了较为详细的介绍。     

一株金黄杆菌对2-吡啶甲酸的好氧生物降解

【背景】2-吡啶甲酸具有高毒性、致癌性,能长期稳定存在于水体中,从而对环境造成危害。【目的】开发一种能够高效经济处理含2-吡啶甲酸废水的技术。【方法】筛选一株在好氧条件下以2-吡啶甲酸为唯一碳、氮、能源的菌株,考察该菌株的降解性能,建立降解动力学模型。【结果】经过16S r RNA基因序列分析,该菌株被鉴定为金黄杆菌(Chryseobacterium sp.),命名为ZD2。当2-吡啶甲酸初始浓度为100、200、400、600和800 mg/L时,ZD2完全降解2-吡啶甲酸的时间分别为10、18、22、78和114 h。零级动力学模型较好地描述了2-吡啶甲酸的降解行为,当初始浓度为100-400 mg/L时,降解速率常数随着浓度的增加而增加,并于400 mg/L时达到最大;600-800 mg/L时,降解速率常数开始下降,呈现抑制作用。【结论】菌株ZD2对2-吡啶甲酸的降解效果较好,能够为处理实际的2-吡啶甲酸工业废水提供理论依据。     

聚乙烯塑料生物降解研究进展

聚乙烯(polyethylene,PE)塑料是全球通用合成树脂中产量最丰富的品种,也是最难降解的塑料之一,其在环境中大量积累已造成严重的生态污染。传统的垃圾填埋、堆肥和焚烧处理技术难以满足生态环境的保护要求,生物降解是解决塑料污染问题的一种生态友好、成本低廉、前景可期的方法。本文对PE塑料的化学结构、降解微生物的种类、降解酶和代谢途径等方面进行了综述,结合国内外PE塑料生物降解的前沿和热点问题,建议重点开展高效降解菌株筛选、人工合成菌群构建、降解酶的挖掘与改造等方面的研究,为PE塑料生物降解研究提供路径选择和理论借鉴。     

活性污泥抗生素抗性基因研究进展

抗生素抗性在全球范围内的传播扩散严重威胁人类健康。活性污泥是污水处理系统重要的处理工艺,同时也是抗生素抗性及其发生水平基因转移的一个重要储库和热区。目前,随着研究手段和技术的不断更新,活性污泥中抗生素抗性的研究不断增加,但是仍有许多科学问题亟待解决。本文主要针对活性污泥抗生素抗性的5个主要方面进行深入讨论:(1)活性污泥中抗性基因的丰度和分布的影响因素;(2)污泥抗性基因的研究方法;(3)活性污泥抗性基因的传播与扩散;(4)污泥中抗性基因环境风险评估;(5)研究展望。本综述在活性污泥抗生素抗性研究基础上,阐述了驱动抗生素抗性扩散的基本微生物生态过程研究进展,旨在为污水处理工艺的发展和优化及抗性基因控制政策的制定提供科学基础。     

生物降解萘的研究进展*

萘的生物降解具有低成本,效果佳,无二次污染等优势,受到全世界的广泛关注。本文从萘降解菌的种类、降解质粒与降解基因的开发与研究、三种降解途径的发展以及表面活性剂、菌体固定化技术和有机溶剂在萘降解和环境污染治理当中的应用情况等方面综述了生物降解萘的发展历程。从降解菌株的研究和表面活性剂以及生物技术手段的应用情况等角度分析了目前生物降解萘还存在的问题,并为解决这些问题提出了合理的方案。论述了两相体系技术在生物降解萘上的可应性,对其强大的发展潜力进行了展望。     

聚对苯二甲酸乙二醇酯生物降解的研究进展

塑料广泛存在于人类的日常生活中,在给人们生活带来便利的同时,大量塑料废物也给环境带来很大压力。聚对苯二甲酸乙二醇酯(polyethylene terephthalate, PET)是一种以石油为原料的高分子热塑性材料,因其具有耐用、透明度高、重量轻等特性,已成为世界上使用最广泛的塑料之一。由于PET具有结构复杂以及难降解的特性,可在自然界中长期存在,不仅对全球生态环境造成严重的污染,而且已经威胁到人类健康。如何对PET废弃物进行降解已成为全球的难题之一,相较于物理法和化学法,生物降解法是目前处理PET废弃物最为绿色环保的方法。本文分别介绍了微生物和生物酶对PET生物降解的研究现状、PET的生物降解途径、PET生物降解机制以及PET降解酶的分子改造等方面的研究,并对如何实现PET的高效降解、寻找和改造可降解高结晶度PET的微生物或酶进行展望,为PET的生物降解微生物或酶的有效开发应用提供理论依据。     

氯酚类化合物的微生物降解研究进展

综述了近年在具有降解氯酚类化合物能力的微生物的筛选、氯酚类化合物的好氧和厌氧降解机制以及现代生物技术的开发利用研究．阐述了氯酚类化合物在不同条件下的降解路径．在好氧条件下,单氯酚和二氯酚在氧化酶的攻击下形成氯代邻二酚,邻二酚开环生成相应的氯代粘康酸或半醛,粘康酸内酯化过程中释放氯离子;高度氯代的化合物则是在氢氧化酶作用下生成氯代醌,并逐步脱去所有的氯原子生成苯酚后才开环．在厌氧或缺氧条件下,氯酚进行还原脱氯,在得到电子的同时去掉一个氯取代基．     

真菌降解木质素研究进展及在好氧堆肥中的研究展望

综述了近十年来真菌降解木质素的研究进展,包括木质素的存在与结构,真菌降解木质素生物学、酶系及作用机理、生理学以及在环境工程中应用方面的研究进展,并对好氧堆肥处理城市垃圾中木质素生物降解的研究作了展望 。     

大环内酯类抗生素微生物降解的研究进展

大环内酯类抗生素是一类以大环内酯为母核的广谱抗生素。近些年,由于人们对其不规范的生产和使用,抗生素污染成为了重要的环境问题。大量研究表明,微生物降解是现阶段处理抗生素污染的最理想方法。为进一步推动大环内酯类抗生素生物降解的研究,文中概述了大环内酯类抗生素的环境污染现状、微生物降解菌株、降解酶、降解途径和降解大环内酯类抗生素的微生物处理方法,并对大环内酯类抗生素生物降解亟待解决的瓶颈问题进行了讨论,以期为微生物降解后续研究提供参考。     

Ultrasonic pretreatment for thermophilic aerobic digestion in industrial waste activated sludge treatment

In order to enhance the degradation efficiency of waste activated sludge (WAS) by thermophilic aerobic digestion, an ultrasonic pretreatment was examined. It was observed that ultrasonic pretreatment increased the solubilization of organic matter in the WAS and that the solubilization ratio of the organics increased during the first 30 min but did not extensively increase thereafter. Therefore, a pretreatment time of 30 min was determined to be the economical pretreatment time from the experimental results. From the digestion experiments, which was conducted using the WAS collected from an oil refinery plant in Inchon, Korea, investigating the effects of an ultrasonic pretreatment on thermophilic aerobic digestion, it was confirmed that the proposed ultrasonic pretreatment was effective at enhancing the release of the cellular components in WAS and the degradation of released components in the thermophilic aerobic digestion.     

Reducing effect of aerobic selector on the toxicity of synthetic organic compounds in activated sludge process

The effects of phenol, 2-chlorophenol (2-CP), 2,4-dichlorophenol (2,4-DCP) and 1,2,4-trichlorobenzene (1,2,4-TCB) on the biodegradation kinetics of the conventional activated sludge system (CASS) and the selector activated sludge system (SASS) were investigated. Experiments were carried out using a respirometric method on unacclimated biomass from two lab-scale systems that were operated with the sludge age of 8 days. Toxicity of the test compounds for both reactors were arranged according to EC₅₀ (effective concentration) values in order as: 1,2,4-TCB > 2,4-DCP > 2-CP > phenol. All selected test compounds induced higher inhibition effect in the CASS. The SASS appeared to reduce inhibition effect in comparison to the CASS, by 21.36%, 66.95%, 64.37% and 33.33% for phenol, 2-CP, 2,4-DCP and 1,2,4-TCB, respectively. Consequently, the SASS may be recommended as a promising configuration alternative for the waste streams containing toxic compounds.     

Extraction of activated sludge bacteria exopolymers by ultrasonication

Ultrasonication for the extraction of activated sludge exopolymers was evaluated by total cell count, exopolymer extraction and transmission electron microscopy (TEM). A high deflocculation was achieved after 30 s of sonication in PBS (phosphate-buffered saline). TEM showed that cell lysis was minimal only when sludges were sonicated for 30 s. For sludges sonicated for 30, 90 and 420 s and stained with Ruthenium Red, exopolymers were not extracted on a large scale without considerable cell lysis. Sludges sonicated for 30 s in EDTA gave a larger fraction of damaged cells and also showed copious amounts of attached exopolymers.     

利用剩余活性污泥合成聚羟基脂肪酸酯的研究进展

利用单一微生物发酵是现阶段获得聚羟基脂肪酸酯 (PHA) 的主要方式,但过高的生产成本限制了其大规模应用。近年来利用活性污泥菌群混合培养合成PHA被广泛研究。将剩余污泥处理与PHA合成相结合,不仅可以省去纯培养所必需的灭菌环节,同时可以实现剩余污泥的资源化利用。剩余污泥的水解酸化、菌群富集驯化及PHA合成受环境因素影响,深入的生物合成机制研究有助于混合培养合成PHA的推广应用。文中主要介绍利用剩余污泥合成PHA的可行性、影响剩余污泥水解酸化的因素、污泥菌群富集驯化合成PHA及其机制等方面的研究进展。     

药品与个人护理品生物降解研究进展

药品与个人护理品(Pharmaceuticals and personal care products, PPCPs)包括各种处方药和非处方药(如各类抗生素、人工合成麝香、止痛药、降压药、避孕药、催眠药和减肥药等)与个人护理用品(如化妆品、香料、遮光剂、发胶、染发剂和杀菌剂等)。作为一类新兴环境微污染物,PPCPs因具有潜在的环境毒理学效应和人体健康风险逐渐受到人们的广泛关注。有关PPCPs的生物降解研究已展开了大量的工作并取得了较大进展。文中总结概括了目前国内外PPCPs生物降解方法、功能菌种类、PPCPs的生物降解特性及产物组成与降解途径等,分析了PPCPs微生物降解机理,并对PPCPs生物降解的研究方向进行了展望。     

厌氧发酵液中溶解性有机物对活性污泥合成聚羟基脂肪酸酯影响的研究进展

利用活性污泥微生物将剩余污泥发酵液中的挥发性脂肪酸(Volatile fatty acids,VFAs)转化为聚羟基脂肪酸酯(Polyhydroxyalkanoates,PHA)是目前环境生物技术领域的研究热点.但针对发酵液中非VFAs物质(主要是溶解性有机物,Dissolved organic matter,DOM)...     

Anaerobic and aerobic biodegradation of chlorophenols using UASB and ASG bioreactors

Chlorophenol degradation was studied by combined anaerobic–aerobic treatments as a single or multi-substrate system. 2,4-Dichlorophenol (2,4-DCP) was degraded to the extent of 52 and 78% in up-flow anaerobic sludge blanket (UASB) and aerobic suspended growth (ASG) reactors respectively, at organic loading rates of 0.18kg/m³/day and hydraulic retention time of 26.4h in the presence of glucose. The UASB represents the dominating facultative anaerobic microbial population. When the effluent from the anaerobic reactor (UASB) was subjected to aerobic treatment on the ASG reactor, 2,4-DCP and COD removals of 86 and 95% respectively were achieved. Aerobic degradation of chlorophenol by acclimated mixed bacterial isolates was found to be sequential: 2-Chlorophenol (2-CP) and 4-CP were degraded first, followed by 2,4-DCP and 2,4,6-Trichlorophenol (2,4,6-TCP) while the contrary was obtained in anaerobic degradation. In anaerobic degradation by acclimated mixed bacterial cells, 2,4-DCP and 2,4,6-TCP were degraded first followed by mono-chlorophenols. The anaerobic/aerobic bioreactors were most efficient when operated in sequence (series) rather than in parallel.     

Heterogeneous diffusion in aerobic granular sludge

Aerobic granular sludge (AGS) technology allows simultaneous nitrogen, phosphorus, and carbon removal in compact wastewater treatment processes. To operate, design, and model AGS reactors, it is essential to properly understand the diffusive transport within the granules. In this study, diffusive mass transfer within full-scale and lab-scale AGS was characterized with nuclear magnetic resonance (NMR) methods. Self-diffusion coefficients of water inside the granules were determined with pulsed-field gradient NMR, while the granule structure was visualized with NMR imaging. A reaction-diffusion granule-scale model was set up to evaluate the impact of heterogeneous diffusion on granule performance. The self-diffusion coefficient of water in AGS was ∼70% of the self-diffusion coefficient of free water. There was no significant difference between self-diffusion in AGS from full-scale treatment plants and from lab-scale reactors. The results of the model showed that diffusional heterogeneity did not lead to a major change of flux into the granule (<1%). This study shows that differences between granular sludges and heterogeneity within granules have little impact on the kinetic properties of AGS. Thus, a relatively simple approach is sufficient to describe mass transport by diffusion into the granules.