Burkholderia xenovorans LB400联苯双加氧酶及突变体对DDTs的降解

DDTs（dichlorodiphenyltrichloroethane,1,1,1-三氯-2,2-双氯苯基乙烷）是一种典型的持久性有机污染物,曾在疟疾防治和农业除虫方面被广泛应用。虽然包括我国在内的很多国家已经禁止使用DDTs,但目前对环境中DDTs的检测发现它仍然广泛存在且具有新的输入源。DDTs的持续存在对近海生态系统和人类健康具有一定危害,因此它所造成的环境污染问题仍然值得关注。由于Rieske型芳香羟化双加氧酶能够起始多种持久性污染物的降解,过去的几十年里一直是芳香化合物降解领域的焦点。[目的] 为探讨联苯双加氧酶对DDTs的降解特性及机制,本研究选取了食异生素伯克霍尔德氏菌LB400（Burkholderia xenovorans）联苯双加氧酶及突变体对p,p''-DDT和o,p''-DDT的降解过程进行研究。[方法] 以BphAE_LB400为亲本,通过两步定点突变将283位的丝氨酸突变为蛋氨酸,获得突变体BphAE_S283M。通过比较亲本酶与突变体对DDTs的催化性能,模拟突变蛋白结构和分子对接等方法,探究其降解特性及机制。[结果] BphAE_LB400和突变体BphAE_S283M都无法降解对位的p,p''-DDT,但突变体BphAE_S283M可以代谢o,p''-DDT并产生2个立体异构体。对接p,p''-DDT的BphAE_LB400和BphAE_S283M的结构分析表明,BphAE_LB400和BphAE_S283M中p,p''-DDT的反应环均不与原晶体结构中的联苯反应环重合。而对接o,p''-DDT的BphAE_S283M的结构分析表明o,p''-DDT的反应环与晶体结构中的联苯反应环距离很近,且2、3位的碳原子与单核铁原子催化中心的距离在0.5 nm以内,此外,BphAE_S283M的催化腔表面积和体积比BphAE_LB400更大,这很可能有助于BphAE_S283M与o,p''-DDT的结合。[结论] 283位氨基酸是影响BphAE_LB400对DDTs的催化代谢能力的关键氨基酸残基,它可以通过调节反应碳原子与催化中心的距离以及催化腔的大小来影响底物特异性。本次研究进一步阐明了283位氨基酸残基的影响机理,为更有效修复DDTs污染提供理论依据和技术支持。     

多氯联苯降解菌的选育及降解性能研究

从长期受PCBs污染的土壤中筛选出2 株多氯联苯降解菌,并对其形态和生物学特性进行了观察研究。通过对这2 株菌的驯化筛选,得到混菌对PCBs的降解效果最好。通过改变菌株的降解条件（pH、温度、接菌量及装液量）可知,混菌的最佳降解pH 值为7.0、温度为30 ℃ 、接菌量为OD600nm=1.0的菌液2 mL、装液量为10.00 mL。在上述最佳条件下,混菌对10 mg/L的PCBs降解15 d,去除率可达70%左右。通过表面活性剂的增效降解作用研究可知,混合表面活性剂表现为低浓度（<500 mg/L）促进混菌对PCBs的降解,高浓度（>700 mg/L）抑制混菌对PCBs的降解。在降解体系中添加300 mg/L的混合表面活性剂,经16 d 的降解,可以将PCBs降解率提高到91.5%。     

白腐菌木质素降解酶及其在木质素降解过程中的相互作用

木质素是一类不易降解的生物物质,在自然界中,白腐真菌对木质素的降解能力最强.白腐真菌降解木质素主要依靠分泌的三种酶:木质素过氧化物酶(Lip)、锰过氧化物酶(MnP)和漆酶(Lac).对白腐真菌分泌的三种木质素降解酶在性质、分布等方面进行了比较,系境地介绍三种木质素降解酶的催化作用,并阐述其在木质素降解过程中的相互作用.     

细菌降解邻苯二甲酸酯的研究进展

邻苯二甲酸酯(Phthalates esters, PAEs)是一类混合在塑料中以增强其可塑性和多功能性的有机化合物。同时,PAEs也是一种典型环境内分泌干扰物,长期生产和使用塑料制品已对环境和生物体乃至人类身体健康造成危害。研究发现微生物降解已成为削减环境中PAEs的主要途径。文中对近年来国内外在PAEs的结构及分类、毒理学效应、在环境中的污染状况、细菌降解的菌株多样性、降解途径及分子机制等方面的相关研究进行了总结与回顾,以期对解决PAEs的污染问题提供参考。     

微生物降解多氯联苯的研究进展

多氯联苯是一种持续性有机污染物,在自然环境中很难降解。在目前研究的降解方法中,微生物降解最具潜力。本文对多氯联苯微生物降解的研究进展进行了综述,包括厌氧还原脱氯,好氧氧化以及生物表面活性剂的作用,介绍了几种降解方法耦合应用的现状和前景,指出了应用中存在的问题和今后的发展方向。     

利用雨养泥炭沼泽及湖泊沉积物重建多氯联苯污染时空变化趋势

为了重建不同历史时期多氯联苯(PCBs)的沉降速率以研究其污染的时空变化趋势,本研究分析了PCBs在泥炭芯和湖泊沉积柱芯中浓度和沉降速率的变化规律,并评估了泥炭芯和湖泊沉积柱芯用于PCBs沉降变化研究的适用性.对采集柱芯进行定年分析发现,泥炭沼泽可以很好地记录PCBs历史沉降变化,并且泥炭中的PCBs没有出现降解情况,...     

一株多糖降解菌的分离、鉴定与琼脂糖降解能力

【目的】筛选海洋来源的多糖降解菌,分析其多糖降解能力并初探机制。【方法】碘液染色法从海泥中初筛琼脂糖降解菌,唯一碳源生长法分析菌株的多糖利用能力,克隆16S rRNA基因以分析系统分类地位。用硫酸铵沉淀法制备胞外粗酶制剂,DNS-还原糖法测定琼胶酶活性,活性染色法分析胞外琼胶酶系的组成特征。分离、纯化琼脂糖的酶解产物,通过TLC测定寡糖Rf值、阳离子质谱测定分子量。【结果】分离到1株能液化琼脂糖的海洋细菌JZB09,鉴定至桃色杆菌属(Persicobacter)。JZB09能利用11种不同的多糖为唯一碳源生长,在利用琼脂糖、纤维素和木聚糖时生长较好。胞外粗酶制剂的琼胶酶活力约77.2U/mg,含有至少2条琼胶酶,大小约45kDa、70kDa。酶制剂降解琼脂糖后的产物是系列新琼寡糖,四糖是主产物,表明β-琼胶酶在胞外琼胶酶系降解琼脂糖时起关键作用。【结论】海洋细菌Persicobacter sp.JZB09是1株多能型多糖降解菌,可分泌β-琼胶酶降解琼脂糖且活性显著,具有潜在开发价值。     

天然和人工饲养水生生物及渔饲料中多氯联苯和多溴联苯醚的研究现状

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微生物降解菲的机理研究进展

针对微生物降解菲的机理研究进展,论述了细菌、真菌在好氧、厌氧条件下代谢菲的产物以及推测的降解途径;在此基础上概括了催化反应的酶系以及编码酶系的基因簇。简要介绍了基因探针的应用,并结合本实验室的初步研究,指出了该领域有待深入探讨的问题。     

氯代苯胺类化合物微生物降解的研究进展*

对氯代苯胺类化合物(Chlovoanilines,CAS)好氧微生物降解的研究现状进行了系统的综述,内容包括具有降解氯代苯胺类化合物能力的微生物、氯代苯胺类化合物的代谢途径及相关代谢酶的分析、降解质粒和关键代谢酶的基因克隆和表达,并提出了氯代苯胺类化合物好氧微生物降解研究中存在的问题和尚需进一步研究的方面。     

Response to (chloro)biphenyls of the polychlorobiphenyl-degrader Burkholderia xenovorans LB400 involves stress proteins also induced by heat shock and oxidative stress

We report the effects of 4-chlorobiphenyl and biphenyl on the physiology, morphology and proteome of the polychlorobiphenyl-degrader Burkholderia xenovorans LB400. The exposure to 4-chlorobiphenyl decreases the growth of LB400 on glucose, and cells exhibit irregular outer membranes, a larger periplasmic space and electron-dense granules in the cytoplasm. Additionally, lysis of cells was observed during incubation with 4-chlorobiphenyl or biphenyl. Proteome of B. xenovorans LB400 exposed to biphenyl and 4-chlorobiphenyl were analysed by two-dimensional gel electrophoresis. Besides induction of the Bph enzymes of biphenyl catabolic pathways, incubation with 4-chlorobiphenyl or biphenyl results in the induction of the molecular chaperones DnaK and GroEL. Induction of these chaperones, which were also induced during heat shock, strongly suggests that exposure to (chloro)biphenyls constitutes stress conditions for LB400. During growth of LB400 on biphenyl, oxidative stress was evidenced by the induction of alkyl hydroperoxide reductase AhpC, which was also induced during exposure to H(2)O(2). 4-chlorobiphenyl and biphenyl induced catechol 1,2-dioxygenase, as well as polypeptides involved in energy production, amino acid metabolism and transport.     

Elucidating the reaction mechanism of the benzoate oxidation pathway encoded aldehyde dehydrogenase from Burkholderia xenovorans LB400

Oxidation of cis-3,4-dehydroadipyl-CoA semialdehyde to cis-3,4-dehydroadipyl-CoA by the aldehyde dehydrogenase, ALDH(C) (EC.1.2.1.77), is an essential step in the metabolism of benzoate in Burkholderia xenovorans LB400. In a previous study, we established a structural blueprint for this novel group of ALDH enzymes. Here, we build significantly on this initial work and propose a detailed reaction mechanism for ALDH(C) based on comprehensive structural and functional investigations of active site residues. Kinetic analyses reveal essential roles for C296 as the nucleophile and E257 as the associated general base. Structural analyses of E257Q and C296A variants suggest a dynamic charge repulsion relationship between E257 and C296 that contributes to the inherent flexibility of E257 in the native enzyme, which is further regulated by E496 and E167. A proton relay network anchored by E496 and supported by E167 and K168 serves to reset E257 for the second catalytic step. We also propose that E167, which is unique to ALDH(C) and its homologs, serves a critical role in presenting the catalytic water to the newly reset E257 such that the enzyme can proceed with deacylation and product release. Collectively, the reaction mechanism proposed for ALDH(C) promotes a greater understanding of these novel ALDH enzymes, the ALDH super-family in general, and benzoate degradation in B. xenovorans LB400.     

Biochemical and structural characterization of the paralogous benzoate CoA ligases from Burkholderia xenovorans LB400: defining the entry point into the novel benzoate oxidation (box) pathway

Xenobiotic aromatic compounds represent one of the most significant classes of environmental pollutants. A novel benzoate oxidation (box) pathway has been identified recently in Burkholderia xenovorans LB400 (referred to simply as LB400) that is capable of assimilating benzoate and intimately tied to the degradation of polychlorinated biphenyls (PCBs). The box pathway in LB400 is present in two paralogous copies (boxM and boxC) and encodes eight enzymes with the first committed step catalyzed by benzoate CoA ligase (BCL). As a first step towards delineating the biochemical role of the box pathway in LB400, we have carried out functional studies of the paralogous BCL enzymes (BCLM and BCLC) with 20 different putative substrates. We have established a structural rationale for the observed substrate specificities on the basis of a 1.84 A crystal structure of BCLM in complex with benzoate. These data show that, while BCLM and BCLC display similar overall substrate specificities, BCLM is significantly more active towards benzoate and 2-aminobenzoate with tighter binding (Km) and a faster reaction rate (Vmax). Despite these clear functional differences, the residues that define the substrate-binding site in BCLM are completely conserved in BCLC, suggesting that second shell residues may play a significant role in substrate recognition and catalysis. Furthermore, comparison of the active site of BCLM with the recently solved structures of 4-chlorobenzoate CoA ligase and 2, 3-dihydroxybenzoate CoA ligase offers additional insight into the molecular features that mediate substrate binding in adenylate-forming enzymes. This study provides the first biochemical characterization of a Box enzyme from LB400 and the first structural characterization of a Box enzyme from any organism, and further substantiates the concept of distinct roles for the two paralogous box pathways in LB400.     

Molecular diagnostics and chemical analysis for assessing biodegradation of polychlorinated biphenyls in contaminated soils

Summary The microbial populations in PCB-contaminated electric power substation capacitor bank soil (TVA soil) and from another PCB-contaminated site (New England soil) were compared to determine their potential to degrade PCB. Known biphenyl operon genes were used as gene probes in colony hybridizations and in dot blots of DNA extracted from the soil to monitor the presence of PCB-degrading organisms in the soils. The microbial populations in the two soils differed in that the population in New England soil was enriched by the addition of 1000 p.p.m. 2-chlorobiphenyl (2-CB) whereas the population in the TVA capacitor bank soil was not affected. PCB degradative activity in the New England soil was indicated by a 50% PCB disappearance (gas chromatography), accumulation of chlorobenzoates (HPLC), and¹⁴CO₂ evolution from¹⁴C-2CB. The PCB-degrading bacteria in the New England soil could be identified by their positive hybridization to thebph gene probes, their ability to produce the yellowmeta-cleavage product from 2,3-dihydroxybiphenyl (2,3-DHB), and the degradation of specific PCB congeners by individual isolates in resting cell assays. Although the TVA capacitor bank soil lacked effective PCB-degrading populations, addition of a PCB-degrading organism and 10 000 p.p.m. biphenyl resulted in a >50% reduction of PCB levels. Molecular characterization of soil microbial populations in laboratory scale treatments is expected to be valuable in the design of process monitoring and performance verification approaches for full scale bioremediation.     

Novel maltotriose esters enhance biodegradation of Aroclor 1242 by Burkholderia cepacia LB400

The objective of this research was to evaluate the effect of enzymatically synthesized maltotriose fatty acid monoesters (Ferrer, M., et al. 2000 Tetrahedron 56, 4053–4061) on Aroclor 1242 solubilization and biodegradation. Three forms of the surfactant, laurate, palmitate and stearate monoester, were tested. Potential enhancement of solubilization of hydrophobic substances mediated by these non-ionic surfactants was exploited in this study. A polychlorinated biphenyl (PCB) degrading organism, Burkholderia cepacia LB400, was also selected. It was found that all surfactants were effective in solubilizing Aroclor 1242 but the rate of Aroclor 1242 biodegradation proceeded rapidly only in the presence of 6-O-palmitoylmaltotriose. For example, the addition of 48 mg 6-O-palmitoylmaltotriose/l increased the apparent solubility from 140 to 305 g/l. As a result, only 8% of the Aroclor remained at the end of 24 h incubation. In contrast, 49.2% of the Aroclor 1242 remained in the absence of surfactant. It appears that maltotriose fatty acid monoesters can significantly increase the bioavailability, and thereby accelerate the biodegradation of highly chlorinated PCBs, particularly Aroclor 1242, by Burkholderia cepacia LB400. The possibility of obtaining these biodegradable surfactants with high yield, easy recovery and high purity by using a new enzymatic methodology, makes maltotriose esters available for bioremediation purposes.     

The effect of polychlorinated biphenyls (PCBs) on the membrane lipids of Pseudomonas stutzeri

In this study we examined the effect of polychlorinated biphenyls (PCBs) on biomass production of a PCB-degrading Pseudomonas stutzeri, and on the fatty acid profile of its major membrane lipids. Growth based on biomass weight was stimulated when PCBs were added at the time of inoculation, but PCB addition three days after inoculation led to a significant decrease in biomass. Simultaneous addition of PCBs plus biphenyl or PCBs plus carvone negatively affected P. stutzeri biomass (addition of biphenyl or carvone at the time of inoculation and PCBs to three-day-old culture). In the presence of PCBs alone the amount of the prevalent fatty acids C16:0 and C17-cyclopropyl fatty acid (C17-CP) of P. stutzeri in total and neutral lipids was significantly reduced. When PCBs were added together with carvone (carvone at the time of inoculation and PCBs after three days) a significant reduction of these fatty acids was obtained, but, in addition, oleic, cis-vaccenic, and cyclononadecanic (C19-CP) acids were increased. When PCBs were combined to biphenyl the prevalent fatty acids were reduced and oleic, cis-vaccenic, and cyclononadecanic acids were increased in total and neutral lipids. Addition of 3-chlorobenzoic acid led to a significant growth inhibition and to the production of oleic and cis-vaccenic acids in the membrane fraction phosphatidylcholine.     

Structural and biochemical characterization of a novel aldehyde dehydrogenase encoded by the benzoate oxidation pathway in Burkholderia xenovorans LB400

The recently identified benzoate oxidation (box) pathway in Burkholderia xenovorans LB400 (LB400 hereinafter) assimilates benzoate through a unique mechanism where each intermediate is processed as a coenzyme A (CoA) thioester. A key step in this process is the conversion of 3,4-dehydroadipyl-CoA semialdehyde into its corresponding CoA acid by a novel aldehyde dehydrogenase (ALDH) (EC 1.2.1.x). The goal of this study is to characterize the biochemical and structural properties of the chromosomally encoded form of this new class of ALDHs from LB400 (ALDH_C) in order to better understand its role in benzoate degradation. To this end, we carried out kinetic studies with six structurally diverse aldehydes and nicotinamide adenine dinucleotide (phosphate) (NAD ⁺ and NADP ⁺). Our data definitively show that ALDH_C is more active in the presence of NADP ⁺ and selective for linear medium-chain to long-chain aldehydes. To elucidate the structural basis for these biochemical observations, we solved the 1.6-Å crystal structure of ALDH_C in complex with NADPH bound in the cofactor-binding pocket and an ordered fragment of a polyethylene glycol molecule bound in the substrate tunnel. These data show that cofactor selectivity is governed by a complex network of hydrogen bonds between the oxygen atoms of the 2′-phosphoryl moiety of NADP ⁺ and a threonine/lysine pair on ALDH_C. The catalytic preference of ALDH_C for linear longer-chain substrates is mediated by a deep narrow configuration of the substrate tunnel. Comparative analysis reveals that reorientation of an extended loop (Asn478-Pro490) in ALDH_C induces the constricted structure of the substrate tunnel, with the side chain of Asn478 imposing steric restrictions on branched-chain and aromatic aldehydes. Furthermore, a key glycine (Gly104) positioned at the mouth of the tunnel allows for maximum tunnel depth required to bind medium-chain to long-chain aldehydes. This study provides the first integrated biochemical and structural characterization of a box-pathway-encoded ALDH from any organism and offers insight into the catalytic role of ALDH_C in benzoate degradation.     

多氯联苯的环境毒理研究动态

本文综述了当前国内外对多氯联苯这种持留性有机污染物环境生态毒理的研究现状,详细论述了多氯联苯的来源、分布、迁移变化等环境行为,特别强调了多氯联苯这种持留性有机污染物在生态系统中因食物网营养关系产生的积累、富集、放大进而影响人类健康的可能性,并对多氯联苯对生物影响的早期预警研究作了展望。     

Enhancement of PCB degradation by Burkholderia xenovorans LB400 in biphasic systems by manipulating culture conditions

Two-phase partitioning bioreactors (TPPBs) can be used to biodegrade environmental contaminants after their extraction from soil. TPPBs are typically stirred tank bioreactors containing an aqueous phase hosting the degrading microorganism and an immiscible, non-toxic and non-bioavailable organic phase functioning as a reservoir for hydrophobic compounds. Biodegradation of these compounds in the aqueous phase results in thermodynamic disequilibrium and partitioning of additional compounds from the organic phase into the aqueous phase. This self-regulated process can allow the delivery of large amounts of hydrophobic substances to degrading microorganisms. This paper explores the reactor conditions under which the polychlorinated biphenyl (PCB) degrader Burkholderia xenovorans LB400 can degrade significant amounts of the PCB mixture Aroclor(R) 1242. Aroclor(R) degradation was found to stall after approximately 40 h if no carbon source other than PCBs was available in the reactor. Sodium pyruvate was found to be a suitable carbon source to maintain microbial activity against PCBs and to function as a substrate for additional cell growth. Both biphenyl (while required during the inoculum preparation) and glucose had a negative effect during the Aroclor(R) degradation phase. Initial Aroclor(R) 1242 degradation rates in the presence of pyruvate were high (6.2 mg L(-1) h(-1)) and 85% of an equivalent concentration of 100 mg Aroclor(R) 1242 per L aqueous phase could be degraded in 48 h, which suggest that solvent extraction of PCBs from soil followed by their biodegradation in TPPBs might be a feasible remediation option.