六氯-1,3-丁二烯的微生物降解研究进展

六氯-1,3-丁二烯(hexachlorobutadiene,HCBD)是一种有毒有害的脂肪族氯代烃,曾经作为杀虫剂、除草剂、变压器油和传热流体等化学工业产品的重要成分被广泛应用于生产生活。HCBD因满足《关于持久性有机污染物的斯德哥尔摩公约》中风险筛选标准(如毒性、持久性、远距离环境迁移和生物累积性等),缔约方于2015年第七次会议中将其增列为持久性有机污染物,2017年又将其列入该公约的附件Ｃ以控制其环境排放量。目前关于HCBD的环境归趋仍是研究热点,但是对于HCBD的微生物降解转化机制尚缺乏深入研究。鉴于此,本文重点回顾并讨论了地下水、底泥等厌氧环境中已报道的HCBD微生物降解转化途径、速率及机制,并从热力学角度阐述HCBD及其降解产物作为电子受体通过还原性脱氯反应被厌氧脱卤微生物代谢转化的可行性。最后,本文根据现有研究结果,提出微生物厌氧降解HCBD的研究展望,包括多组学技术解析HCBD降解功能菌群结构和潜在互作机制、HCBD厌氧降解微生物的分离与纯化,以及HCBD厌氧降解菌剂的开发与污染场地原位生物修复应用等。     

含氧杂环及其衍生物的生物降解研究进展

含氧杂环化合物（Oxygen heterocycles）是污染环境中常见的一类难降解有机污染物,具有毒性和致癌特性,其所引发的环境问题受到人们广泛关注。本文综述了典型含氧单杂环化合物四氢呋喃、1,4-二氧六环以及含氧稠杂环化合物二苯并呋喃、二苯并对二噁英的生物降解研究进展,主要包括降解菌降解性能、降解途径和降解相关基因。此外,本文还对二噁英类衍生物的研究现状进行了讨论,并展望了含氧杂环及二噁英类衍生物生物降解的未来研究方向。     

一株有色金属矿山1-亚硝基-2-萘酚降解菌的筛选、鉴定和降解特性

1-亚硝基-2-萘酚是一类有色选矿药剂代表性的新型浮选药剂,在采选冶行业为了提高低品位矿物资源的利用率,被大量投入使用,该药剂的高稳定性进一步增大了矿山环境中重金属与有机选冶药剂复合污染的治理难度。微生物修复作为稠环芳烃(polycyclic aromatic hydrocarbons,PAHs)类污染物重要技术手段之一,具有安全、经济、高效和无二次污染等特点。【目的】本研究从我国广西河池市周边的典型有色金属尾矿环境中分离出1株高效降解1-亚硝基-2-萘酚的菌株,并分析其降解特性及其潜在的代谢途径,从而探究矿山复合污染生态系统中稠环芳烃类污染物的微生物修复技术的应用前景。【方法】从有色金属尾矿样本中筛选到以1-亚硝基-2-萘酚为唯一碳源的菌株,经16S rRNA基因序列鉴定,结合气相色谱-质谱联合(gas chromatography-mass spectrometer,GC-MS)检测分析菌株对1-亚硝基-2-萘酚的降解特性及中间代谢产物,并推测可能的代谢途径。【结果】筛选获得1株高效降解1-亚硝基-2-萘酚的Pseudomonas putida CUGB-JL11菌株,经鉴定为革兰氏阴性杆的恶臭假单胞菌。该菌株最适温度为30 ℃左右,最适pH值范围为6-8条件下,菌株5 d内对40 mg/L 1-亚硝基-2-萘酚的降解率高达81%。降解中间代谢产物主要为苯环类物质：苯甲羟肟酸甲酯和苯丙胺,但其母体及大部分中间产物都降解为小分子物质或者被完全降解。【结论】恶臭假单胞菌P. putida CUGB-JL11具有良好的1-亚硝基-2-萘酚降解能力和较强的环境适应性,有进一步被开发为微生物菌剂以用于稠环芳烃类污染修复的巨大潜力,为有色金属矿山生态系统中重金属和有机选冶药剂复合污染的微生物修复研究提供了理论依据和可利用的微生物资源。     

植物-微生物联合对环境有机污染物降解的研究进展

环境中有机污染物的过量积累对生态系统及人类健康造成严重威胁。近年来,许多学者研究发现植物-微生物联合作用对环境中有机污染物的去除及生态系统的修复具有非常显著的效果。本文主要从植物-内生菌、植物-菌根菌以及植物-根际微生物这三个层面详细阐述植物-微生物联合降解有机污染物的研究现状,分析植物-微生物在联合降解中的作用,揭示植物-微生物联合降解的机理。但就目前而言,植物-微生物联合降解有机污染物仍存在许多问题,植物-微生物联合降解有机污染物的机理及生态学效应仍不清楚。因此,还需要进一步探讨其潜在作用机制并加强应用实践,这将有助于污染生态系统的治理,促进环境可持续发展。     

磷酸三(1-氯-2-丙基)酯降解菌筛选及其降解特性

【背景】磷酸三(1-氯-2-丙基)酯[tris-(1-chloro-2-propyl)phosphate,TCIPP]作为全球广泛关注的新兴有机污染物,具有环境赋存含量高、不易生物降解等特点,亟须开发TCIPP的高效去除技术。【目的】获得具有较高TCIPP降解效率并可用于TCIPP污染修复的新菌株。【方法】利用梯度提高无机盐培养基中TCIPP浓度的方法,从TCIPP污染土壤中筛选出1株能够降解液体中高浓度TCIPP (100 mg/L)的菌株,根据16S rRNA基因序列分析对其进行鉴定,并首次对其降解液体中TCIPP的特性进行研究。【结果】所筛选的TCIPP降解菌株DT-6为苍白杆菌(Ochrobactrum sp.),它能够利用TCIPP作为唯一碳源和能源;当TCIPP初始浓度为50 mg/L、培养时间为7 d时DT-6的生物量最大,对TCIPP的降解率也达到最高,为34.6%;蔗糖的加入能够显著促进DT-6的生长,但却抑制了其对TCIPP的降解。【结论】本研究报道了一株TCIPP高效降解菌Ochrobactrum sp. DT-6,能够为环境中TCIPP污染的生物修复提供新的种质...     

持久性有机污染物γ-六六六生物降解研究进展

γ-六六六(γ-Hexachlorocyclohexane,γ-HCH)是一种有机氯杀虫剂,由于它具有持久性和很高的毒性,成为顽固性的世界性污染物。目前从世界上不同的受HCH污染的地区中已经分离出许多能够降解HCH的微生物,其中一些微生物对γ-HCH的降解途径得到了阐明,降解基因/酶也得到了鉴定。综述了γ-HCH降解菌的多样性、降解途径、降解基因和酶,为γ-HCH的生物修复提供了参考。     

海洋石油污染物的微生物降解与生物修复

石油是海洋环境的主要污染物 ,已经对海洋及近岸环境造成了严重的危害。微生物降解是海洋石油污染去除的主要途径。海洋石油污染物的微生物降解受石油组分与理化性质、环境条件以及微生物群落组成等多方面因素的制约 ,N和P营养的缺乏是海洋石油污染物生物降解的主要限制因子。在生物降解研究基础上发展起来的生物修复技术在海洋石油污染治理中发展潜力巨大 ,并且取得了一系列成果。介绍了海洋中石油污染物的来源、转化过程、降解机理、影响生物降解因素及生物修复技术等方面内容 ,强调了生物修复技术在治理海洋石油污染环境中的优势和重要性 ,指出目前生物修复技术存在的问题。     

内生菌协同宿主植物修复土壤复合污染的研究进展

土壤复合污染日益严重,危及植物生长及人类发展,寻找修复土壤复合污染的有效方法已经成为环境领域的优先事项。复合污染指同一环境中存在两种或两种以上的污染物,分为复合重金属污染、复合有机污染物污染及重金属-有机污染物复合污染。近些年发现内生菌能定殖在植物中,并且被感染的植物不会引起任何外在病症,其主要通过促进宿主植物生长,改变植物摄取污染物能力和酶促降解污染物等方法增强植物修复能力。本文综述了具有复合重金属和复合有机污染抗性的内生菌种类及其作用机制,并展望了内生菌协同宿主植物修复环境中复合污染物的研究方向。     

嗜盐微生物在环境修复中的研究进展

人类活动产生的污染物,使一些天然盐环境遭受不同程度的污染,或者使环境受到污染物与高盐的双重污染。在高盐条件下,非嗜盐微生物的代谢会受到抑制,其生物修复效率明显降低,甚至丧失修复能力。嗜盐微生物则能够在高盐环境中栖息繁殖,凸显其修复被污染高盐环境的生物学效率和广阔的应用前景。就嗜盐微生物降解石油烃、芳香烃衍生物和有机磷等污染物的研究进展进行了综述和讨论。     

微生物降解持久性有机污染物的研究进展与展望

持久性有机污染物（POPs）是伴随着人类工业化发展而产生的合成类污染物,具有高毒性、持久性、长迁移性和高生物富集性等特点,POPs污染物的微生物降解一直是环境科学与技术应用领域的研究热点。微生物降解技术修复POPs污染环境具有无二次污染、成本低、快速简便等优点,拥有广泛的应用前景。本文论述了各种POPs微生物分解代谢的最新研究进展,包括降解性微生物资源以及降解机制。此外,还讨论了计算生物学、合成生物学、基因组学等技术在POPs微生物降解中的潜力和应用,以期为环境中持久性有机污染物的修复提供参考。     

A Pseudomonas putida Strain Genetically Engineered for 1,2,3-Trichloropropane Bioremediation

1,2,3-Trichloropropane (TCP) is a toxic compound that is recalcitrant to biodegradation in the environment. Attempts to isolate TCP-degrading organisms using enrichment cultivation have failed. A potential biodegradation pathway starts with hydrolytic dehalogenation to 2,3-dichloro-1-propanol (DCP), followed by oxidative metabolism. To obtain a practically applicable TCP-degrading organism, we introduced an engineered haloalkane dehalogenase with improved TCP degradation activity into the DCP-degrading bacterium Pseudomonas putida MC4. For this purpose, the dehalogenase gene (dhaA31) was cloned behind the constitutive dhlA promoter and was introduced into the genome of strain MC4 using a transposon delivery system. The transposon-located antibiotic resistance marker was subsequently removed using a resolvase step. Growth of the resulting engineered bacterium, P. putida MC4-5222, on TCP was indeed observed, and all organic chlorine was released as chloride. A packed-bed reactor with immobilized cells of strain MC4-5222 degraded >95% of influent TCP (0.33 mM) under continuous-flow conditions, with stoichiometric release of inorganic chloride. The results demonstrate the successful use of a laboratory-evolved dehalogenase and genetic engineering to produce an effective, plasmid-free, and stable whole-cell biocatalyst for the aerobic bioremediation of a recalcitrant chlorinated hydrocarbon.     

The effectiveness of organophosphate acaricides on stored product mites interacting in biological control

Three organophosphates (pirimiphos-methyl, chlorpyrifos-methyl, chlorpyrifos) were tested on a laboratory strain of Cheyletus eruditus (Schrank), a predatory mite used for biological control of stored food mites, and on tow species of acaroid mites, Acarus siro L. and Tyrophagus putrescentiae (Schrank). Biological control is often preceded by a chemical treatment with organophosphates and thus it is important to know how the acaricides affect the predators. It was found that chlorpyrifos-methyl was the most toxic organophosphate on C. eruditus. The effectiveness of pirimiphos-methyl and chlorpyrifos was approximately equal and was three times lower than the effectiveness of chlorpyrifos-methyl. The organophosphates were nearly equally effective on both acaroid mites but A. siro was slightly more susceptible than T. putrescentiae. On the basis of these results, the use of pirimiphos-methyl or chlorpyrifos rather than chlorpyrifos-methyl is recommended for protection of empty stores or stored grain against resiliant populations of stored food mites.     

Toxicity and bioremediation of pesticides in agricultural soil

Pesticides are one of the persistent organic pollutants which are of concern due to their occurrence in various ecosystems. In nature, the pesticide residues are subjected to physical, chemical and biochemical degradation process, but because of its high stability and water solubility, the pesticide residues persist in the environment. Moreover, the prevailing environmental conditions like the soil characteristics also contribute for their persistence. Bioremediation is one of the options for the removal of pesticides from environment. One important uncertainty associated with the implementation of bioremediation is the low bioavailability of some of the pesticides in the heterogeneous subsurface environment. Bioavailability of a compound depends on numerous factors within the cells of microorganism like the transportation of susbstrate across cell membrane, enzymatic reactions, biosurfactant production etc. as well as environment conditions such as pH, temperature, availability of electron acceptor etc. Pesticides like dichlorodiphenyltrichloroethane (DDT), hexachlorocyclohexane (HCH), Endosulfan, benzene hexa chloride (BHC), Atrazine etc. are such ubiquitous compounds which persist in soil and sediments due to less bioavailability. The half life of such less bioavailable pesticides ranges from 100 to 200 days. Most of these residues get adsorbed to soil particles and thereby becomes unavailable to microbes. In this review, an attempt has been made to present a brief idea on ‘major limitations in pesticide biodegradation in soil’ highlighting a few studies.     

Identification and characterization of chlorpyrifos-methyl and 3,5,6-trichloro-2-pyridinol degrading Burkholderia sp. strain KR100

A chlorpyrifos-methyl (CM) degrading bacterium (designated strain KR100) was isolated from a Korean rice paddy soil and was further tested for its sensitivity against eight commercial antibiotics. Based on morphological, biochemical, and molecular characteristics, this bacterium showed greatest similarity to members of the order Burkholderiales and was shown to be most closely related to members of the Burkholderia cepacia group. Strain KR100 hydrolyzed CM to 3,5,6-trichloro-2-pyridinol (TCP) and utilized TCP as the sole source of carbon for its growth. The isolate was also able to degrade chlorpyrifos, dimethoate, fenitrothion, malathion, and monocrotophos at 300 μg/ml but diazinon, dicrotophos, parathion, and parathion-methyl at 100 μg/ml. The ability to degrade CM was found to be encoded on a single plasmid of ~50 kb, pKR1. Genes encoding resistance to amphotericin B, polymixin B sulfate, and tetracycline were also located on the plasmid. This bacterium merits further study as a potential biological agent for the remediation of soil, water, or crop contaminated with organophosphorus compounds because of its greater biodegradation activity and its broad specificity against a range of organophosphorus insecticides.     

Effets sur le spermatozoïde humain du Diuron (3-(3,4-dichlorophényl)-1,1-diméthyl-urée) et de l’un de ses produits de transformation, la 3,4-dichloroaniline (3,4-DCA) (Etude préliminaire)

Diuron belongs to the family of halogenophenylureas, one of the main groups of herbicides used for more than 40 years. These herbicides absorb sunlight and can be photochemically transformed in the environment (herbicides are transformed on the soil surface exposed to sunlight) or biotransformed by microorganisms present in soil or in water. The metabolites (chlorohydroxyphenylurea, chlorophenylaniline, respectively) are more toxic than the parent compound, as demonstrated by a bioluminescence inhibition assay performed with a marine bacterium (Vibrio fischeri toxicity test). The lipophilicity of these pesticides makes the cell membrane a target for their action, especially the spermatozoa cell membrane. The aim of this study is to use human spermatozoa to evaluate the effect of this urea pesticide and its biotransformed product on the spermatozoa membrane. We investigated the structural and functional effects of these environmental pollutants on spermatozoa. Three million spermatozoa purified on a 95/47.5% Percoll gradient were suspended in 250 μl of modified Earle’s medium (without phenol red) supplemented with 7.5% of human decomplemented serum. Pesticides (Diuron or 3,4-dichloroaniline (3,4-DCA)) were added at a final concentration of 0.1; 1 and 5 mM. Samples were incubated at room temperature for 24 hours. We show that both Diuron and 3,4-DCA decrease motility and vitality of spermatozoa incubated with the highest concentration of pesticides. Our preliminary results show that the effects are more rapid and more intense with the biotransformed product (3,4-DCA) than with Diuron. Addition of herbicide to human spermatozoa increases membrane fluidity, assessed by measuring the fluorescence polarisation anisotropy with a fluorescent probe: 1,6-diphenyl-1,3,5-hexatriene (DPH). Changes in membrane fluidity may be a primary toxic effect of these herbicides. These results suggest that human spermatozoa may constitute a valuable indicator of the toxic effects of pesticides.     

Dual-level toxicity assessment of biodegradable pesticides to aquatic species

The use of ecological models to assess the effects of pesticides on the structure and function of aquatic ecosystems is of growing interest. Of utmost concern is assessment of pesticides that have the potential to biodegrade into metabolites that are as toxic as the parent pesticide. In this work, a mathematical model to predict and evaluate the effect of two pesticides on the population of aquatic biospecies where both pesticides are bio-available in water and sediments with one of the pesticides capable of biodegrading into the other but not vice versa is formulated and analyzed. Conditions for nonlinear stability, instability and Hopf-bifurcation are obtained. The model undergoes a Hopf-bifurcation when the rate of discharge of pesticides crosses a critical value, so that the population of the aquatic species follows an oscillatory pattern. Four hypotheses involving the concentration of the pesticides and the population of the aquatic species where qualitatively investigated: the aquatic species will completely die out with time, the population of the aquatic biospecies will remain under certain conditions, the pesticide will continually remain in water and there will be a periodic variation in the population of the aquatic species over time. Results also indicate that the biodegradation potential of one of the pesticides had significant effect on the population dynamics of the aquatic species.     

Effect of propanil,linuron, and dicamba on the degradation kinetics of 2,4‐dichlorophenoxyacetic acid by Burkholderia sp. A study by differential analysis of 2,4‐dichlorophenoxyacetic acid degradation data

The successive application of distinct pesticides, or mixtures of them, is a frequent practice that could adversely affect the microbial species inhabiting soil and aquatic ecosystems. The ability of soil or aquatic microbiota to degrade a pesticide could be affected by the presence of another. If the degradation rate of the first compound is inhibited, its dissipation half‐life in the environment could be hazardously enlarged. Few studies have been made to quantify the impact on the biodegradation rate of pesticides in soils or water by the presence of other pesticides. In this work, a method for assessing the effect of a pesticide on the biodegradation rate of another, measuring its effect on the biodegradation kinetics of a single bacterial strain is presented. The mathematical analysis is a powerful tool to study the stoichiometry and kinetics of microbial processes, which was used to evaluate independently, in detail, the effect of three pesticides (propanil, linuron, and dicamba) on the biodegradation kinetics of 2,4‐dichlorophenoxyacetic acid by a strain of Burkholderia sp. It was evidenced that linuron and dicamba caused a decay of more than 40% in the top instantaneous degradation rate of 2,4‐dichlorophenoxyacetic acid, while propanil showed a minimal effect.     

Biodegradation of Chlorpyrifos and Its Hydrolysis Product 3,5,6-Trichloro-2-Pyridinol by a New Fungal Strain Cladosporium cladosporioides Hu-01

Intensive use of chlorpyrifos has resulted in its ubiquitous presence as a contaminant in surface streams and soils. It is thus critically essential to develop bioremediation methods to degrade and eliminate this pollutant from environments. We present here that a new fungal strain Hu-01 with high chlorpyrifos-degradation activity was isolated and identified as Cladosporium cladosporioides based on the morphology and 5.8S rDNA gene analysis. Strain Hu-01 utilized 50 mg·L⁻¹ of chlorpyrifos as the sole carbon of source, and tolerated high concentration of chlorpyrifos up to 500 mg·L⁻¹. The optimum degradation conditions were determined to be 26.8°C and pH 6.5 based on the response surface methodology (RSM). Under these conditions, strain Hu-01 completely metabolized the supplemented chlorpyrifos (50 mg·L⁻¹) within 5 d. During the biodegradation process, transient accumulation of 3,5,6-trichloro-2-pyridinol (TCP) was observed. However, this intermediate product did not accumulate in the medium and disappeared quickly. No persistent accumulative metabolite was detected by gas chromatopraphy-mass spectrometry (GC-MS) analysis at the end of experiment. Furthermore, degradation kinetics of chlorpyrifos and TCP followed the first-order model. Compared to the non-inoculated controls, the half-lives (t _1/2) of chlorpyrifos and TCP significantly reduced by 688.0 and 986.9 h with the inoculum, respectively. The isolate harbors the metabolic pathway for the complete detoxification of chlorpyrifos and its hydrolysis product TCP, thus suggesting the fungus may be a promising candidate for bioremediation of chlorpyrifos-contaminated water, soil or crop.     

Biocatalytic degradation of pollutants

Microbial reactions play key roles in biocatalysis and biodegradation. The recent genome sequencing of environmentally relevant bacteria has revealed previously unsuspected metabolic potential that could be exploited for useful purposes. For example, oxygenases and other biodegradative enzymes are benign catalysts that can be used for the production of industrially useful compounds. In conjunction with their biodegradative capacities, bacterial chemotaxis towards pollutants might contribute to the ability of bacteria to compete with other organisms in the environment and to be efficient agents for bioremediation. In addition to the bacterial biomineralization of organic pollutants, certain bacteria are also capable of immobilizing toxic heavy metals in contaminated aquifers, further illustrating the potential of microorganisms for the removal of pollutants.