微生物降解多环芳烃(PAHs)的研究进展

从多环芳烃(PAHs)的降解菌株的筛选、降解机制以及PAHs污染的生物修复等方面介绍了微生物降解PAHs的最新研究进展。     

植物-固定化菌剂联合修复多环芳烃污染土壤

以火凤凰根际土壤中发现的3种优势菌[分枝杆菌(Ⅰ)、产黄纤维单胞菌(Ⅱ)、少动鞘氨醇单胞菌(Ⅲ)]构建的多菌剂体系为供试菌剂,针对大港油田原油污染土壤,将固定化供试菌剂接种于修复植物火凤凰根际,探讨供试菌剂强化火凤凰修复多环芳烃(PAHs)污染土壤的效果.结果 表明:处理ⅠⅢ(有效活茵数为109 cfu·mL-1)和Ⅰ...     

土壤中高环多环芳烃微生物降解的研究进展

微生物修复是去除土壤中多环芳烃(PAHs)的主要措施。本文以微生物修复PAHs污染土壤的理论基础及其难点为主线,全面综述了土壤中高环PAHs的微生物降解机理。近年来,富集分离得到的以高环PAHs为唯一碳源和能源的优势降解菌逐渐增多,其中,主要是代谢降解四环PAHs的单株降解菌,一些降解菌还能以共代谢方式利用五环PAHs。高环PAHs污染土壤修复的一个难点是其低生物可利用性,微生物通过释放生物表面活性剂、形成生物膜以及分泌胞外多糖提高高环PAHs的生物可利用性,从而加速其降解。真菌和细菌联合作用能增强污染土壤实地修复的效果。因此,通过微生物修复技术来去除土壤中PAHs具有环境友好性、经济适用性以及可持续应用性。     

污染土壤中多环芳烃的共代谢降解过程

1　前　言多环芳烃是一类普遍存在于环境中的重要有机污染物 ,因其致癌性、致畸性、致突变性而被认为是危险物质。由于其水溶性低 ,辛醇 水分配系数高 ,因此 ,该类化合物易于从水中分配到生物体内、沉积层中。土壤成为多环芳烃的重要载体 ,多环芳烃污染土壤的生物修复也因此倍受关注。多环芳烃在土壤中有较高的稳定性 ,其苯环数与其生物可降解性明显呈负相关关系。很少有能直接降解高环数多环芳烃的微生物。研究表明 ,高分子量的多环芳烃的生物降解一般均以共代谢方式开始[1 3] 。共代谢作用可以提高微生物降解多环芳烃的效率 ,改变微生物碳…     

多环芳烃污染土壤微生物修复研究进展

多环芳烃是我国土壤环境质量标准中要求严格管控的一类持久性有机污染物,利用微生物技术修复有机污染土壤具有绿色、经济等突出特点,应用前景广泛。目前多学科的协同发展和新技术的研究应用,为多环芳烃土壤微生物转化机制与污染生态过程等方面带来了新的认识,同时对修复技术的实际应用与调控提供了新的思考方向。本文以多环芳烃污染土壤微生物修复为主体,从污染土壤微生物修复应用技术、多环芳烃微生物降解特征、土壤体系污染物归趋规律与微生物作用及土壤污染微生物群落响应与研究技术等方面进行综合评述,并针对现存应用技术瓶颈和理论空白作进一步思考和展望。     

固定化微生物降解土壤中菲和芘的研究

1　引　　言固定化微生物技术是 2 0世纪 70年代兴起的一种新型生物技术 ,目前已成为国内外学者的研究热点[8] ,现被广泛应用于处理化学工业废水 .其优点是可以大幅度提高参加反应微生物浓度 ;减少活性污泥数量 ;微生物被高分子材料包埋 ,耐环境冲击 ;根据需要选择有效微生物 ,可降低二次污染等特点 ,因而受到越来越多的关注[4,6 ,10 ] .包埋法是固定化技术最为普遍的使用方法 ,包埋载体的选择是固定化微生物的关键 ,理想的载体具有对微生物无毒性 ,传质性能好 ,性质稳定 ,不易被微生物分解 ,强度高寿命长和价格低廉等优点[2 ] .迄今 ,国内…     

多环芳烃微生物降解基因的研究进展

多环芳烃(PAHs)是环境中普遍存在的一类有机污染物,微生物的降解是PAHs去除的主要途径。近年来,有关PAHs微生物降解途径和代谢产物的研究已有很多报道。小分子PAHs一般可以直接被微生物降解,而大分子PAHs则需要微生物以共代谢的方式降解。在过去20年中,微生物降解PAHs的基因相继被发现,各种基因在调控PAHs降解过程中的功能也越来越清晰。本文概述了PAHs微生物降解基因方面的研究进展,详细介绍了微生物对萘、菲的降解基因,最后对PAHs微生物降解基因的应用前景进行了展望。     

厌氧微生物降解多环芳烃研究进展

多环芳烃(PAHs)是一类普遍存在于环境介质中的难降解有机污染物,相对于好氧微生物降解PAHs的研究,厌氧微生物降解PAHs的研究则相对较少.本文从厌氧微生物降解PAHs的研究背景,厌氧降解微生物的特点和不同厌氧降解还原反应体系的角度综述了厌氧微生物降解PAHs的概况;结合厌氧微生物降解萘和菲转化途径的介绍,推断了其降解机制的内在原因;同时通过总结影响厌氧微生物降解PAHs的主要因素(包括:PAHs的生物可利用性、外源营养物质的添加、外源电子受体的添加、特定厌氧降解菌的筛选强化和部分环境因素等),指出了制约降解进程的潜在限制因子;并对厌氧微生物降解PAHs研究目前存在的问题和未来的发展方向作了简述与展望.     

多环芳烃污染生物修复研究进展

多环芳烃(polycyclic aromatic hydrocarbon,PAHs)是一类对环境有严重危害的持久性有机污染物。具有高生物富集性、致癌性、致毒性和难降解性,修复治理PAHs污染环境备受国内外政府及学者的关注。目前主要采用物理、化学以及生物方法对多环芳烃污染的土壤和水体进行修复。其中生物修复是一种高效、经济和生态可承受的环保技术,具有成本低、无二次污染等优点。本文从植物修复、微生物修复以及植物-微生物联合修复方面,阐述了国内外生物修复PAHs污染的最新研究进展。指出了生物修复PAHs污染环境需要进一步解决的问题,并对未来发展趋势进行了展望。     

油田区多环芳烃污染盐碱土壤活性微生物群落结构解析

多环芳烃(Polycyclic aromatic hydrocarbons,PAHs)是土壤中广泛存在的、美国环保总署(USEPA)优先控制的一类有毒(致癌、致突变)的持久性污染物,主要来源于人类活动。土壤微生物多样性是表征土壤质量变化的敏感指标之一。磷脂脂肪酸(PLFAs)分析方法是基于活性微生物细胞膜的PLFAs组分的生化检测技术,克服了传统培养方法只能分离出少量微生物(1%)的缺点。采用PLFAs方法,解析了土壤活性微生物对PAHs污染胁迫的反应。结果表明,土壤微生物分布情况可分为4种类型:Ⅰ型,微生物PLFAs种类最多,占该区土壤微生物PLFAs种类总数的57.7%,PAHs对变量的解释量最小;Ⅱ型,微生物PLFAs占PLFAs总数的30.8%,PAHs对变量的解释量较小;Ⅲ型,微生物PLFAs种类占总数的7.68%,PAHs对变量的解释量较大;Ⅳ型,微生物PLFAs的种类仅占总数的3.85%,PAHs对变量的解释量最大。相关性分析表明:土壤微生物PLFAs的种类、生物量和生态多样性指数与土壤中萘(Nap)、芴(Flu)、蒽(Ant)、苯并[K]荧蒽(Bkf)、苯并[a]芘(Bap)、茚并[1,2,3-cd]芘(Ind)的相对含量呈负相关关系;与苊(Ace)、菲(Phe)、荧蒽(Fla)、芘(Pyr)、苯并[a]蒽(Baa)的相对含量呈正相关关系;与PAHs的种类和浓度呈负相关关系。结果将为开展PAHs污染土壤的生态风险评价和微生物生物修复技术研究提供理论依据。     

邻苯二甲酸酯在不同品种通菜-土壤系统中的累积效应研究

在邻苯二甲酸(2-乙基己基)酯(DEHP)不同污染程度的水稻土上盆栽不同品种通菜,应用GC／MS联机检测技术研究了通菜-土壤系统中DEHP的环境行为与归宿．结果表明,通菜中DEHP的含量为0．335～12．710mg·kg^-1,与土壤的污染程度呈正相关．不同品种通菜之间对DEHP的吸收累积效应存在显著差异,与其叶子大小存在一定的正相关关系．种植不同品种通菜后土壤中DEHP的残留量(1．424～19．834mg·kg^-1)存在显著差异．通菜对土壤中DEHP的BCFs都小于1．0,与土壤的污染程度呈负相关．不同通菜品种的BCFs之间存在显著差异,中等叶子通菜品种的BCFs相对较大。     

Isolation of Cyclic 3′,5′-Guanosine Monophosphate from Bacterial Culture Fluids

To clarify the biosynthetic pathway of maridomycin, the biosynthetic relation among 16-membered macrolide antibiotics belonging to leucomycin-maridomycin group was examined with intact cells or growing cultures of Streptomyces hygroscopicus No. B–5050–HA and its mutants.

Carbomycin A, B and leucomycin A₃ were converted to maridomycin II in the pH range of 5.5-7.5 with an optimum between 6.0-6.5. But, maridomycin II was not converted to leucomycin A₃ or carbomycin B. These findings were confirmed by culture experiment. Leucomycin A₃, carbomycin A and B added to the culture at 48 hr were almost completely converted to maridomycin II.

On the basis of these facts, we propose a biosynthetic relation among leucomycin A₃, carbomycin A, carbomycin B and maridomycin II.     

Cell-free synthesis of the enzymes of peroxisomal beta-oxidation

Three enzymes of peroxisomal β-oxidation of rat liver were synthesized in a cell-free protein-synthesizing system derived from rabbit reticulocyte lysate. The $\text{in}\text{vitro}$ products of acyl-CoA oxidase and enoyl-CoA hydratase-3-hydroxyacyl-CoA dehydrogenase multifunctional protein were similar in size to or slightly larger than the subunit of the respective mature enzymes. The $\text{in}\text{vitro}$ product of peroxisomal 3-ketoacyl-CoA thiolase was about 3,000 daltons larger than the mature subunit. The hepatic levels of translatable mRNAs coding for these three enzymes were about 10 times higher in rats fed a di(2-ethylhexyl)phthalate-containing diet than in control animals.     

Inhibition of Bacillus circulans F-2 Amylase by Guanine Nucleotides

We investigated the relationship between protein and tryptophan intake and the adverse-effect-level of di(2-ethylhexyl)phthalate (DEHP). Growth retardation of young rats due to DEHP was strengthened by increasing protein level. The addition of tryptophan to the diet caused extreme increases in the nicotinamide formation, but no growth retardation was observed.     

Biosorption of di(2-ethylhexyl)phthalate by seaweed biomass

Samples of various Sargassum species were collected in the Hong Kong marine environment and used for studies on biosorption of di(2-ethylhexyl)phthalate (DEHP). Batch adsorption experiments were carried out to determine the removal capacity and removal efficiency of the biosorbents. The DEHP removal ability was similar among beached seaweed and three freshly collected Sargassum species. Different physico-chemical factors were evaluated in order to enhance the performance of the biosorbents. Under optimized conditions (25 mg biomass, initial pH 4, 25 °C, 40 mg L^–1 DEHP), the mean removal capacity of beached seaweed and Sargassum siliquastrum was 5.68 and 6.54 mg g^–1, respectively. Examination of the Langmuir and Freundlich adsorption isotherms showed that the biosorption phenomenon by these biosorbents could well be described by these models. Desorption of DEHP was also assessed with methanol, which showed the most satisfactory desorbing ability. Further study in multiple adsorption–desorption of DEHP by the biosorbents demonstrated the reusability of both beached seaweed and S. siliquastrum for biosorption of DEHP.     

Removal of polycyclic aromatic hydrocarbons from oil-contaminated Kuwaiti soil

In the uncontaminated farm soil, more than 80% of the supplemented acenaphthene, fluoranthene, and pyrene (100 mg/100 g soil) decreased in 90 days, while ratio of removal was about 20%, 30%, and 0%, respectively, in the Kuwaiti oil-contaminated soil. Simultaneous addition of naphthalene, phenanthrene, and anthrathene (100 mg of each compound/100 g soil) led the acenaphthene to a decrease of about 20% to 45% but not of fluoranthene and pyrene. Addition of the farm soil to the Kuwaiti soil did not enhance the decrease of these three PAHs.     

邻苯二甲酸二(2-乙基己基)酯对大鼠胎盘组织的影响

目的:探讨孕期不同剂量邻苯二甲酸二(2-乙基己基)酯(DEHP)暴露对大鼠胎盘组织形态学和超微结构的影响,以推断DEHP对胎盘结构和功能的损害。方法:健康雌性Wistar大鼠40只,随机分为4组,妊娠第11日起每日给予DEHP灌胃,剂量分别为:对照组(玉米油)、低剂量组(100 mg/kg)、中剂量组(500 mg/kg)和高剂量组(1000 mg/kg),妊娠第19日处死孕鼠,取胎盘组织分别做HE染色和电镜制片,观察各剂量组胎盘形态学及超微结构的变化。结果:各剂量组胎盘形态学和超微结构的变化与DEHP摄入量呈负相关,低剂量组胎盘无明显改变;中剂量组胎盘缩小,空泡化细胞增多,微观结构显示胞质内线粒体水肿;高剂量组胎盘迷路带血窦扩张淤血严重,滋养细胞变性、坏死。结论:DEHP可导致大鼠胎盘形态结构发生改变,这种病理改变是胎盘功能减退的形态学基础,可直接影响胚胎发育和妊娠结局。     

Degradation of polycyclic aromatic hydrocarbons by an immobilized mixed bacterial culture

The mixed bacterial culture MK1 was capable of degrading a wide spectrum of aromatic compounds both as free and as immobilized cells. By offering anthracene oil or a defined mixture of phenol, naphthalene, phenanthrene, anthracene and pyrene (in concentrations of 0.1–0.2 mm, respectively) as sources of carbon and energy, a specific degradation pattern correlating with the condensation degree was observed. Regarding the defined mixture of aromatic hydrocarbons, complete metabolism was reached for phenol (0.1 mm) after 1 day, for naphthalene (0.1 mm) after 2 days and for phenanthrene (0.1 mm) after 15 days of cultivation. The conversion of anthracene (0.1 mm) and pyrene (0.1 mm) resulted in minimal residual concentrations, analogous to fluoranthene and pyrene of the anthracene oil (0.1%). Maximal total degradation for the tricyclic compounds dibenzofurane, fluorene, dibenzothiophene, phenanthrene and anthracene of the anthracene oil (0.1%) occurred after 5 days. In general, a significant metabolisation of the tetracyclic aromatic hydrocarbons fluoranthene and pyrene was observed after the degradation of phenol, naphthalene and most of the tricyclic compounds. Doubling the start concentrations of the polycyclic aromatic hydrocarbons effected higher degradation rates. Cell growth occurred simultaneously with the conversion of phenol, naphthalene and the tricyclic compounds. The immobilized cells showed stable growth and, compared to freely suspended cells, the same degradation sequence as well as an equivalent degradation potential — even in a model soil system. Correspondence to: I. Wiesel