直链烷基苯磺酸盐(LAS)的生物降解性*

阴离子表面活性剂直链烷基苯磺酸盐 (LAS)在工业生产和人们生活中得到广泛应用 ,但大量产生的含有LAS的污水在环境中造成的污染也日益严重 ,因而引起了人们的高度重视。本文从LAS的好氧和厌氧生物降解以及LAS降解菌等诸多方面阐述了LAS生物降解性的研究进展。     

糖脂类生物表面活性剂的特性及其对白腐真菌降解蒽的强化作用

【目的】对铜绿假单胞菌(Pseudomonas aeruginosa)所产生物表面活性剂的稳定性进行分析,考察该生物表面活性剂对乳白耙齿菌F17(Irpex lacteus F17)降解蒽的强化作用。【方法】采用三氯甲烷萃取的方法从铜绿假单胞菌的发酵液中提取生物表面活性剂,采用表/界面张力仪测定该生物表面活性剂在不同条件下的表面张力值,对其进行稳定性研究。在乳白耙齿菌F17降解蒽的过程中加入适量的生物表面活性剂,测定蒽的降解率,探讨其对蒽生物降解的强化作用。【结果】铜绿假单胞菌所产生物表面活性剂的临界胶束浓度为40 mg/L,在15-150°C及pH 6.0-13.0范围内表现出优良的稳定性,对盐浓度的耐受性也很高。在蒽的生物降解过程中,生物表面活性剂能极大地促进蒽的降解,在生物表面活性剂浓度为50 mg/L时,第15天蒽的降解率达到了82.9%。生物表面活性剂在接种乳白耙齿菌F17前1天加入培养基中,能更好地促进蒽的降解。与化学表面活性剂相比,生物表面活性剂对蒽降解的强化作用更显著。【结论】该生物表面活性剂性能优良、稳定性好,能够显著强化乳白耙齿菌F17对蒽的降解,具有良好的应用前景。     

低能离子诱变烃降解菌所产表面活性剂的研究

菌株产表面活性剂的能力直接影响其对石油烃的降解和利用,大量的研究表明,生物表面活性剂可以通过胶束来渗透、润湿、乳化、增溶、发泡、消泡等作用促进石油的利用,有效提高石油烃的降解,加快油污土壤的生物修复过程。对菌株23产表面活性剂和菌株生长的关系,发酵液中表面活性剂的提取鉴定,以及生物表面活性剂的临界胶束浓度,对温度、pH、盐度的稳定性,对石蜡的乳化活性等理化性质进行了初步分析研究,为该菌株进一步的研究以及今后实际应用提供较多的资料和信息,为其应用领域提供理论依据,以便更好的发挥其在实际生产中的功能。     

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。     

聚乙烯醇的生物降解

聚乙烯醇(PVA)是较少的可溶于水并被生物降解的乙烯聚合物之一。研究表明,在受PVA污染的自然环境中存在着能降解PVA的微生物,并从中提取出了PVA降解酶。介绍了国内外研究聚乙烯醇生物降解的情况。分别讨论了聚乙烯醇被单一菌种、共生细菌和真菌降解过程中的生物化学和生理学特性,以及结构因素对聚乙烯醇生物降解的影响。这些研究促进了可有效生物降解的PVA类材料产品项目的发展。     

多环芳烃厌氧生物降解研究进展

多环芳烃（PAHs）是环境中广泛分布的一类持久性有机污染物,对生态环境和公众健康具有极大危害。微生物降解是环境中去除多环芳烃污染的有效途径,近年来PAHs厌氧生物降解研究逐渐取代好氧降解成为人们关注的重点。本文从PAHs厌氧生物降解的研究背景出发,从不同厌氧还原反应体系、厌氧降解微生物、PAHs厌氧生物转化途径等方面阐述了PAHs厌氧生物降解的研究概况,归纳了对PAHs厌氧生物降解有积极作用的影响因素,提出了PAHs厌氧降解研究目前存在的问题,并对该领域未来研究方向作了简述和展望。希望为多环芳烃厌氧生物降解与环境修复研究与实践提供参考。     

塑料生物降解检测方法的研究进展

塑料处理不当造成的污染问题已成为全球性难题。目前的解决办法除回收利用与使用可生物降解塑料替代之外,最主要途径仍是寻求高效的塑料降解方法。其中,采用微生物或酶处理塑料的方法因其具有条件温和、不产生次生环境污染的优势而受到越来越多的关注。塑料生物降解技术的核心是高效解聚微生物/酶,然而当前的分析检测方法无法满足塑料生物降解资源的高效筛选,因此开发准确、快速的塑料降解过程分析方法,对于生物降解资源筛选和降解效能评价具有重要意义。本文介绍了近年来在塑料生物降解领域的常用分析检测技术,包括高效液相色谱、红外光谱、凝胶渗透色谱以及透明圈测定等,重点讨论了荧光分析策略在快速表征塑料生物降解过程中的应用,为进一步规范塑料生物降解过程的表征与分析研究,以及开发更高效的塑料生物降解资源筛选方法提供借鉴。     

施氏假单胞菌YC-YH1的萘降解特性及产物分析

【目的】萘是一种重要的环境污染物,它在环境中的积累会对人类健康造成危害,生物降解是解决这一问题的有效方法。本实验室保存的施氏假单胞菌YC-YH1对萘具有较强的降解能力,在此基础上,研究和分析菌株对萘的降解特性、环境因素对萘降解率的影响以及代谢产物。【方法】本文首先采用单因素实验法研究pH、温度、接种量、萘初始浓度对萘降解率的影响;并在单因素实验结果的基础上,利用Design-Expert 8.0.5软件和Box-Behnken设计对pH、温度、接种量3个影响因素进行响应面优化分析,建立环境因素对萘降解率影响的优化模型。利用LC-MS检测萘降解过程中产生的重要代谢产物,从而推测菌株对萘的代谢途径。【结果】响应面分析结果表明,优化模型极显著(P<0.001),拟合度良好,预测结果可信度高。降解实验证明,在培养温度为32.4 °C、pH为7.10、接种量5.74% (体积比)的优化条件下培养3 d即可将浓度为100 mg/L的萘100%降解。LC-MS分析表明,菌株降解萘的过程中,能够被检测到的主要代谢产物有1,2-二羟基萘、水杨酸、邻苯二酚等。【结论】施氏假单胞菌YC-YH1对萘有高的降解效率,pH、温度、接种量3个因素对菌株的降解率有较大影响。利用响应面法优化菌株对萘的降解条件,能够提高YC-YH1菌株对萘的生物降解性能。初步推测菌株YC-YH1对萘的降解是通过水杨酸途径,萘首先被其代谢为1,2-二羟基萘,而后被转化为水杨酸和邻苯二酚,最后进入三羧酸循环被彻底降解。     

聚乳酸的生物降解

聚乳酸(polylactic acid, PLA)因其良好的理化性能、生物相容性和生物降解性而备受关注，已被认为是石油基塑料最具潜力的替代者，但在实际应用中仍然存在降解缓慢循环周期长的问题，因此对PLA的生物降解深入研究对于解决塑料垃圾污染和缓解能源危机至关重要。近年来，有关微生物(放线菌、细菌和真菌)和酶(蛋白酶、脂肪酶、酯酶和角质酶)降解PLA的研究已经取得了一定的进展。本文从降解微生物、降解酶和降解机制等方面综述了PLA生物降解的研究进展，并展望了PLA生物降解研究未来的发展趋势。     

石油烃降解菌的研究进展

该文归纳了细菌、真菌和藻类对石油烃的降解作用;讨论了微生物降解石油烃的影响因素,包括微生物种类、石油烃种类、温度、pH、营养物质、电子受体等;总结了微生物固定化技术、生物表面活性剂和基因工程技术在微生物降解石油烃领域的应用;最后,提出今后生物降解石油烃的研究重点可能是开发具有高效降解能力的菌群联合体。     

Biodegradation Kinetics of Naphthalene in Soil Medium Using Pleurotus Ostreatus in Batch Mode with Addition of Fibrous Biomass as a Nutrient

The efficiency and kinetics of naphthalene biodegradation in a soil medium using Pleurotus ostreatus (a type of white rot fungus) in batch mode with and without the addition of oil palm fiber (OPF) as a nutrient are evaluated in this study. Three batches are considered in the biodegradation study: (i) control—spiked soil; (ii) spiked soil with fungus; and (iii) spiked soil with both fungus and OPF. Biodegradation is conducted over a period of 22 days for which soil naphthalene concentrations are determined with respect to microwave extraction and high-performance liquid chromatography (HPLC) analysis. The results indicate that inoculation with Pleurotus ostreatus significantly enhances soil naphthalene biodegradation to 84%, which is further enhanced upon the addition of OPF to 98% with respect to the degradation rate. The high carbon content in OPF (>40%) affords it the capacity to be a viable nutrient supplement for Pleurotus ostreatus, thereby enhancing the potential of Pleurotus ostreatus in the biodegradation of polycylic aromatic hydrocarbons (PAHs), and indicating the potential of OPF as a nutrient for PAH biodegradation. A relationship between OPF mass and the biodegradation rate constant has been determined to be linear according to the following equation: k = 0.0429 × OPF + 0.1291.     

Dynamic response of naphthalene biodegradation in a continuous flow soil slurry reactor

Periodic perturbations were used to evaluate the system stability and robustness of naphthalene biodegradation in a continuous flow stirred tank reactor (CSTR) containing a soil slurry. The experimental design involved perturbing the test system using a sinusoidal input either of naphthalene or non-naphthalene organic carbon at different frequencies during steady state operation of the reactors. The response of the test system was determined by using time series off-gas analysis for naphthalene liquid phase concentration and degradation, total viable cell counts, and gene probe analysis of naphthalene degradative genotype, and by batch mineralization assays.Naphthalene biodegradation rates were very high throughout the experimental run (95 to >99% removed) resulting in very low or undetectable levels of naphthalene in the off-gas and reactor effluent. Attempts to reduce the rate of naphthalene biotransformation by either reducing the reactor temperature from 20°C to 10°C or the dissolved oxygen level (>1 mg/L) were unsuccessful. Significant naphthalene biodegradation was observed at 4°C. While variable, the microbial community as measured by population densities was not significantly affected by temperature changes. In terms of naphthalene biotransformation, the system was able to adapt readily to all perturbations in the reactor.Department of Chemical EngineeringDepartment of Microbiology and The Graduate Program in EcologyDepartment of Civil Engineering, New Orleans University     

Rhizosphere strain of <Emphasis Type="Italic">Pseudomonas chlororaphis</Emphasis> capable of degrading naphthalene in the presence of cobalt/nickel

Combination of genetic systems of degradation of polyaromatic hydrocarbons, resistance to heavy metals, and promotion of plant growth/protection is one of the approaches to the creation of polyfunctional strains for phytoremediation of soils after co-contamination with organic pollutants and heavy metals. A plant-growth-promoting rhizosphere strain Pseudomonas chlororaphis PCL1391 (pBS216^*, pBS501) has been obtained, in which the nah operon of plasmid pBS216 provides naphthalene biodegradation and the cnr-like operon of plasmid pBS501 provides resistance to cobalt and nickel due to the extrusion of heavy metal cations from the cells. In the presence of 100 μM of nickel, the viability, growth rate, and naphthalene biodegradation efficiency of the resistant strain PCL1391 (pBS216^*, pBS501) were much higher as compared with the sensitive PCL1391 (pBS216). During the growth of the resistant strain, in contrast to the sensitive strain, nickel (100 μM) had no inhibiting effect on the activity of the key enzymes of naphthalene biodegradation. Original Russian Text ? T.V. Siunova, T.O. Anokhina, A.V. Mashukova, V.V. Kochetkov, A.M. Boronin, 2007, published in Mikrobiologiya, 2007, Vol. 76, No. 2, pp. 212–218.     

Biosurfactant-Mediated Biodegradation of Polycyclic Aromatic Hydrocarbons—Naphthalene

The present study is aimed at the naphthalene degradation with and without biosurfactant produced from Pseudomonas aeruginosa isolated from oil-contaminated soil. The present study was carried out to isolate the bacterial strains for the naphthalene degradation and also for biosurfactant production. The isolated strains were screened for their ability to degrade the naphthalene by the methods of optimum growth rate test and for the production of biosurfactants by cetyltrimethylammonium bromide, blood agar medium, and thin-layer chromatography. The present study also focused on the effect of biosurfactant for the degradation of naphthalene by isolate-1. Two bacterial strains were isolated and screened, one for biodegradation and another for biosurfactant production. The second organism was identified as Pseudomonas aeruginosa by 16S rRNA analysis. The purified biosurfactant reduces the surface tension of water and also forms stable emulsification with hexadecane and kerosene. The end product of naphthalene degradation was estimated as salicylic acid equivalent by spectrophotometric method. The results demonstrated that Pseudomonas aeruginosa has the potential to produce biosurfactant, which enhances the biodegradation of naphthalene. The study reflects the potential use of biosurfactants for an effective bioremediation in the management of contaminated soils.     

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。     

Naphthalene,phenanthrene and surfactant biodegradation

The impact of surfactants on naphthalene and phenanthrene biodegradation and vice versa after surfactant flushing were evaluated using two anionic surfactants: sodium dodecyl sulfate (SDS) and sodium dodecyl benzene sulfonate (SDBS); and two nonionic surfactants: POE (20) sorbitan monooleate (T-maz-80) and octylphenol poly(ethyleneoxy) ethanol (CA-620). Naphthalene and phenanthrene biodegradation varied differently in the presence of different surfactants. Naphthalene biodegradation was not impacted by the presence of SDS. In the presence of T-maz-80 and CA-620, naphthalene biodegradation occurred at a lower rate (0.14 d^-1 for T-maz-80 and 0.19 d^-1 for CA-620) as compared to un-amended control (0.29 d^-1). Naphthalene biodegradation was inhibited by the presence of SDBS. In the presence of SDS, phenanthrene biodegradation occurred at a lower rate (0.10 d^-1 as compared to un-amended control of 0.17 d^-1) and the presence of SDBS, CA-620 and T-maz-80 inhibited phenanthrene biodegradation. The surfactants also responded differently to the presence of naphthalene and phenanthrene. In the presence of naphthalene, SDS biodegradation was inhibited; SDBS and T-maz-80 depleted at a lower rate (0.41d^-1 and 0.12 d^-1 as compared to 0.48 d^-1 and 0.22 d^-1). In the absence of naphthalene, CA-620 was not degradable, while in the presence of naphthalene, CA-620 began to degrade at a comparatively low rate (0.12 d^-1). In the presence of phenanthrene, SDS biodegradation occurred at a lower rate (1.2 d^-1 as compared to 1.68 d^-1) and a similar trend was observed for T-maz-80. The depletion of SDBS and CA-620 did not change significantly. The choice of SDS for naphthalene-contaminated sites would not adversely affect the natural attenuation of naphthalene, in addition, naphthalene was preferentially utilized to SDS by naphthalene-acclimated microorganisms. Therefore, SDS was the best choice. T-maz-80 was also found to be usable in naphthalene-contaminated sites. For phenanthrene contaminated sites, SDS was the only choice.     

Metal Toxicity Reduction in Naphthalene Biodegradation by Use of Metal-Chelating Adsorbents

A model system comprising microbial degradation of naphthalene in the presence of cadmium has been developed to evaluate metal toxicity associated with polyaromatic hydrocarbon biodegradation and its reduction by the use of unmodified and surfactant-modified clays in comparison with a commercially available chelating resin (Chelex 100; Bio-Rad). The toxicity of cadmium associated with naphthalene biodegradation was shown to be reduced significantly by using the modified-clay complex and Chelex resin, while unmodified clay has no significant impact on this reduction. The degree of metal toxicity reduction can be quantitatively related to the metal adsorption characteristics of these adsorbents, such as adsorption capacity and selectivity.     

Bacterial chemotaxis to naphthalene desorbing from a nonaqueous liquid

Bacterial chemotaxis has the potential to increase the rate of degradation of chemoattractants, but its influence on degradation of hydrophobic attractants initially dissolved in a non-aqueous-phase liquid (NAPL) has not been examined. We studied the effect of chemotaxis by Pseudomonas putida G7 on naphthalene mass transfer and degradation in a system in which the naphthalene was dissolved in a model NAPL. Chemotaxis by wild-type P. putida G7 increased the rates of naphthalene desorption and degradation relative to rates observed with nonchemotactic and nonmotile mutant strains. While biodegradation alone influenced the rate of substrate desorption by increasing the concentration gradient against which desorption occurred, chemotaxis created an even steeper gradient as the cells accumulated near the NAPL source. The extent to which chemotaxis affected naphthalene desorption and degradation depended on the initial bacterial and naphthalene concentrations, reflecting the influences of these variables on concentration gradients and on the relative rates of mass transfer and biodegradation. The results of this study suggest that chemotaxis can substantially increase the rates of mass transfer and degradation of NAPL-associated hydrophobic pollutants.     

Horizontal transfer of catabolic plasmids and naphthalene biodegradation in open soil

The horizontal transfer of naphthalene biodegradation plasmids and the parallel process of its microbial degradation were studied for the first time. The tagged naphthalene-degrading strains bearing labeled biodegradation plasmids were used for the monitoring of horizontal plasmid transfer in open soil. The population kinetics of microorganisms, the survival rate and competitiveness of introduced strains, and the transfer of biodegradation plasmids to indigenous strains were investigated. The transfer of the labeled plasmid pNF142::TnMod-OTc to the introduced plasmid-free recipient P. putida KT2442 and to indigenous soil microorganisms of the genus Pseudomonas was shown both under selection pressure (in the presence of naphthalene) and in its absence. The 16S rRNA gene sequencing showed that the soil strains that had acquired plasmids were close to the species P. lini, P. frederiksbergensis, P. jessenii, P. graminis, P. putida, and P. alcaligenes. Thus, direct evidence of dissemination of the naphthalene biodegradation plasmids in microbial populations in open soil under selective and nonselective conditions has been obtained.     

The P-7 Incompatibility Group Plasmids Responsible for Biodegradation of Naphthalene and Salicylate in Fluorescent Pseudomonads

Analysis of seven plasmids (77 to 135 kb in size) of the P-7 incompatibility group that are responsible for the biodegradation of naphthalene and salicylate has shown that the main natural host of IncP-7 plasmids is the species Pseudomonas fluorescens. The IncP-7 plasmids are structurally diverse and do not form groups, as is evident from their cluster analysis. The naphthalene catabolism genes of six of the IncP-7 plasmids are conservative and homologous to the catabolic genes of NAH7 and pDTG1 plasmids. The pAK5 plasmid contains the classical nahA gene, which codes for naphthalene dioxygenase, and the salicylate 5-hydroxylase gene (nagG) sequence, which makes the conversion of salicylate to gentisate possible.__________Translated from Mikrobiologiya, Vol. 74, No. 3, 2005, pp. 342–348.Original Russian Text Copyright © 2005 by Izmalkova, Sazonova, Sokolov, Kosheleva, Boronin.