Microbial degradation of plant toxins

Plants produce a variety of secondary metabolites in response to biotic and abiotic stresses. Although they have many functions, a subclass of toxic secondary metabolites mainly serve plants as deterring agents against herbivores, insects, or pathogens. Microorganisms present in divergent ecological niches, such as soil, water, or insect and rumen gut systems have been found capable of detoxifying these metabolites. As a result of detoxification, microbes gain growth nutrients and benefit their herbivory host via detoxifying symbiosis. Here, we review current knowledge on microbial degradation of toxic alkaloids, glucosinolates, terpenes, and polyphenols with an emphasis on the genes and enzymes involved in breakdown pathways. We highlight that the insect-associated microbes might find application in biotechnology and become targets for an alternative microbial pest control strategy.     

Some observations on the biosynthesis of the plant sulpholipid by Euglena gracilis

1. dl-Cysteine decreases the uptake of ³⁵SO₄²⁻ by Euglena gracilis but does not decrease the relative incorporation of the isotope into sulpholipid; cysteic acid, on the other hand, does not affect the uptake of ³⁵SO₄²⁻ but does dilute out its incorporation into the sulpholipid. 2. Both l-[³⁵S]cysteic acid and dl-+meso-[3-¹⁴C]cysteic acid appear almost exclusively in 6-sulphoquinovose. 3. Molybdate inhibits the incorporation of ³⁵SO₄²⁻ into sulpholipid but not its uptake into the cells; this suggests that adenosine 3′-phosphate 5′-sulphatophosphate may be concerned with the biosynthesis of sulpholipid, and it was shown to be formed by chloroplast fragments. 4. An outline scheme for sulpholipid biosynthesis based on these observations is discussed.     

木质纤维素的微生物降解

木质纤维素广泛存在于自然界中,因结构复杂,其高效降解需要多种微生物的协同互作,由于参与木质纤维素降解的微生物种类繁多,其协同降解机理尚不完全明确。随着微生物分子生物学和组学技术的快速发展,将为微生物协同降解木质纤维素机制的研究提供新的方法和思路。笔者前期研究发现,细菌复合菌系在50℃下表现出强大的木质纤维素降解能力,菌系由可分离培养和暂时不可分离培养细菌组成,但是可分离培养细菌没有降解能力。通过宏基因组和宏转录组研究表明,与木质纤维素降解相关的某些基因表达量发生显著变化,通过组学方法有可能更加深入解释微生物协同降解木质纤维素的微生物学和酶学机理。文中从酶、纯培养菌株和复合菌群三个方面综述了木质纤维素微生物降解研究进展,着重介绍了组学技术在解析复合菌群作用机理方面的现状和应用前景,以期为探索微生物群落协同降解木质纤维素的机理提供借鉴。     

Microbial degradation of alkenylbenzenes

Alkenylbenzenes are produced in large quantities by the petrochemical industry. The simplest of these alkenylbenzenes, styrene, is in widespread use in the polymer-processing industry and is thus found in many industrial effluents. Airborne gaseous emissions of styrene are particular problems due to the potential toxicity and carcinogenicity of the compound. The catabolic pathways involved in the degradation of styrene have been well characterised. With an increased knowledge of the adaptative response which microorganisms exhibit when exposed to higher styrene concentrations, together with an understanding of the genetic regulation of the catabolic pathways which operate in these microbial strains, it is likely that these organisms could be exploited in areas such as biotransformations, biocatalysis and bioremediation.The authors are with the Microbiology Department, University College, Cork, Ireland.     

Microbial degradation of lignin

The transformations of lignin that occur during its biodegradation are complex and incompletely understood. Certain fungi of the white-rot group, and possibly other fungi and bacteria, completely decompose lignin to carbon dioxide and water. Other fungi and bacteria apparently degrade lignin incompletely. Differences in lignin-degrading abilities observed for different organisms may result from differences in the completeness of their ligninolytic enzyme systems. Not all lignin components may be attacked by a particular organism. Alternatively, different organisms may differ in their basic mechanisms of attack on lignin. The basic pathways of lignin degradation have been elucidated only for certain representatives of the white-and brown-rot fungi. Although it is known that each of the principal structural components of lignin is attacked by other fungi and bacteria, the biochemistry of that attack has not been elucidated. Work with low molecular weight lignin models has provided only limited information on possible pathways of lignin degradation by microorganisms. There is little evidence to suggest a correlation between abilities to degrade single-ring aromatic or lignin model compounds and the ability to degrade polymeric lignin. More evidence has come from analysis of spent culture media for lignin breakdown products and from comparative chemical analyses of sound lignins versus decayed lignin residues. Accumulated evidence with the most thoroughly studied white-rot fungi suggests that with these fungi lignin degradation proceeds by way of extracellular mixed-function oxygenases and dioxygenases, which catalyse demethylations, hydroxylations and ring-fission reactions within a largely intact polymer, concomitant with some release of low molecular weight lignin fragments. There are also apparent relationships between lignin, carbohydrate and nitrogen metabolism for some organisms, but the relationships may vary from one organism to another. Although research is now mostly at a basic level, industrial applications may result from lignin degradation research. Considerable potential exists for the development of bioconversions which might produce low molecular weight chemicals from waste lignins, and thereby reduce our dependence on petroleum as a source of these chemicals. Alternatively, such bioconversions might produce chemically altered forms of polymeric lignin that may be valuable industrially.     

聚乙烯塑料的微生物降解

聚乙烯(polyethylene,PE)是产量最大的通用塑料之一,通常被加工成一次性包装材料(包括塑料袋及容器)和农用薄膜等。PE塑料的广泛应用导致大量PE废弃物的累积,对生态环境造成严重的威胁。自20世纪70年代以来,一些研究陆续报道了PE塑料被微生物降解的现象,并从土壤、海洋、垃圾堆置点及昆虫肠道等生境中分离筛选到了若干种具有一定PE塑料降解能力的菌株,而且发现一些单加氧酶、过氧化物酶和漆酶等氧化还原酶对PE塑料具有氧化降解能力。这些研究为发展PE塑料废弃物生物降解处理技术提供了一定的依据。本文总结和分析了PE塑料降解微生物的分离和筛选方法,以及已报道的PE塑料降解微生物和降解酶的研究进展,以期为进一步研究PE塑料的微生物降解机理和处理技术提供参考。     

Microbial degradation of polyethers

This paper summarizes studies on microbial degradation of polyethers. Polyethers are aerobically metabolized through common mechanisms (oxidation of terminal alcohol groups followed by terminal ether cleavage), well-characterized examples being found with polyethylene glycol (PEG). First the polymer is oxidized to carboxylated PEG by alcohol and aldehyde dehydrogenases and then the terminal ether bond is cleaved to yield the depolymerized PEG by one glycol unit. Most probably PEG is anaerobically metabolized through one step which is catalyzed by PEG acetaldehyde lyase, analogous to diol dehydratase. Whether aerobically or anaerobically, the free OH group is necessary for metabolization of PEG. PEG with a molecular weight of up to 20,000 was metabolized either in the periplasmic space (Pseudomonas stutzeri and sphingomonads) or in the cytoplasm (anaerobic bacteria), which suggests the transport of large PEG through the outer and inner membranes of Gram-negative bacterial cells. Membrane-bound PEG dehydrogenase (PEG-DH) with high activity towards PEG 6,000 and 20,000 was purified from PEG-utilizing sphingomonads. Sequencing of PEG-DH revealed that the enzyme belongs to the group of GMC flavoproteins, FAD being the cofactor for the enzyme. On the other hand, alcohol dehydrogenases purified from other bacteria that cannot grow on PEG oxidized PEG. Cytoplasmic NAD-dependent alcohol dehydrogenases with high specificity towards ether-alcohol compound, either crude or purified, showed appreciable activity towards PEG 400 or 600. Liver alcohol dehydrogenase (equine) also oxidized PEG homologs, which might cause fatal toxic syndrome in vivo by carboxylating PEG together with aldehyde dehydrogenase when PEG was absorbed. An ether bond-cleaving enzyme was detected in PEG-utilizing bacteria and purified as diglycolic acid (DGA) dehydrogenase from a PEG-utilizing consortium. The enzyme oxidized glycolic acid, glyoxylic acid, as well as PEG-carboxylic acid and DGA. Similarly, dehydrogenation on polypropylene glycol (PPG) and polytetramethylene glycol (PTMG) was suggested with cell-free extracts of PPG and PTMG-utilizing bacteria, respectively. PPG commercially available is atactic and includes many structural (primary and secondary alcohol groups) and optical (derived from pendant methyl groups on the carbon backbone) isomers. Whether PPG dehydrogenase (PPG-DH) has wide stereo- and enantioselective substrate specificity towards PPG isomers or not must await further purification. Preliminary research on PPG-DH revealed that the enzyme was inducibly formed by PPG in the periplasmic, membrane and cytoplasm fractions of a PPG-utilizing bacterium Stenotrophomonas maltophilia. This finding indicated the intracellular metabolism of PPG is the same as that of PEG. Besides metabolization of polyethers, a biological Fenton mechanism was proposed for degradation of PEG, which was caused by extracellular oxidants produced by a brown-rot fungus in the presence of a reductant and Fe3+, although the metabolism of fragmented PEG has not yet been well elucidated.     

Microbial degradation of octamethylcyclotetrasiloxane

The microbial degradation of low-molecular-weight polydimethylsiloxanes was investigated through laboratory experiments. Octamethylcyclotetrasiloxane was found to be biodegraded under anaerobic conditions in composted sewage sludge, as monitored by the occurrence of the main polydimethylsiloxane degradation product, dimethylsilanediol, compared to that found in experiments with sterilized control samples.     

Microbial degradation of pentachlorophenol

Pentachlorophenol (PCP) was the most prevalent wood preservative for many years worldwide. Its widespread use had led to contamination of various environments. Traditional methods of PCP clean-up include storage in land-fill sites, incineration and abiotic degradation processes such as photodecomposition. Some aerobic and anaerobic microorganisms can degrade PCP under a variety of conditions. Axenic bacterial cultures, Flavobacterium sp., Rhodococcus sp., Arthrobacter sp., Pseudomonas sp., Sphingomonas sp., and Mycobacterium sp., and fungal cultures, Phanerochaete sp. and Trametes sp. exhibit varying rates and extent of PCP degradation. This paper provides some general information on properties of PCP and reviews the influence of nutrient amendment, temperature and pH on PCP degradation by various aerobic and anaerobic microorganisms. Where information is available, proposed degradation pathways, intermediates and enzymes are reviewed.     

Microbial degradation of 1,3-dichlorobenzene

A gram-negative, peritrichously flagellated rod, tentatively identified as an Alcaligenes sp., was isolated from a mixture of soil and water samples by using 1,3-dichlorobenzene as the sole carbon and energy source. During growth on 1,3-dichlorobenzene, almost stoichiometric amounts of chloride were released. Simultaneous adaptation studies, as well as enzyme studies, indicated that 1,3-dichlorobenzene was metabolized via 3,5-dichloro-cis-1,2-dihydroxycyclohexa-3,5-diene to 3,5-dichlorocatechol. Subsequently, the latter product was cleaved, yielding 2,4-dichloromuconate. No initial hydrolytic step yielding 3-chlorophenol was detected in this species.     

石油基塑料的微生物降解

石油基塑料种类繁多、数量巨大、应用广泛,常见的有聚乙烯(PE)、聚丙烯(PP)、聚苯乙烯(PS)、聚氯乙烯(PVC)、聚对苯二甲酸乙二醇酯(PET)、聚氨酯(PUR)等。这些合成塑料因其高分子量、高疏水性及高化学键能的特点难以被微生物降解,从而在环境中长期存在和累积,"白色污染"已经成为一个全球性问题。因此安全经济的微生物降解合成塑料是人类面临的一个选择和难题。文中从微生物资源及相关酶学研究方面综述了聚苯乙烯、聚乙烯、聚丙烯、聚氨酯、聚对苯二甲酸乙二醇酯和聚氯乙烯这6种石油基塑料的生物降解的研究现状。目前关于上述6种石油基塑料的微生物降解研究依然大多停留在微生物资源的寻找中,已发现的具备相关能力的菌株种类较少,并且微生物降解效率均非常缓慢;对于其降解机理及关键基因和酶的研究比较少。文中为进一步开展塑料生物降解研究,寻找高效的塑料降解菌株资源以及进一步在遗传、分子和生化水平研究塑料生物降解机理研究,从而最终实现合成塑料的彻底降解和高值化利用提供了借鉴。     

环境中雌激素的微生物降解

环境中的雌激素是一类重要的环境内分泌干扰物,微生物降解是去除环境雌激素的主要途径。通过归纳已报道的雌激素降解细菌、总结其降解雌激素的机制、分析雌激素降解途径以及其他真核微生物的雌激素降解作用4个方面,概括阐述了雌激素的微生物降解作用,并对未来的研究方向提出展望。     

聚氨酯塑料的微生物降解

未被合理处置的废塑料污染已成为全球性的环境问题,探索塑料废弃物的无害化处理技术势在必行。近来,研究证实了自然界中存在可以降解塑料的微生物及酶。利用微生物或酶对废塑料进行生物处理成为可能。聚氨酯塑料(Polyurethane,PUR)是广泛应用的通用塑料之一,其废弃物量已占到所有废塑料总体积的30%。文中将PUR塑料发明应用70年来有关微生物降解的研究进行了全面综述,对PUR塑料降解真菌、细菌、降解基因与酶、降解产物及相关的生物处理技术系统等进行了总结与分析,并对实现PUR废塑料高效生物处理需解决的关键科学问题进行了展望。     

Microbial degradation of chlorinated phenols

Chlorophenols have been introduced into the environment through their use as biocides and as by-products of chlorine bleaching in the pulp and paper industry. Chlorophenols are subject to both anaerobic and aerobic metabolism. Under anaerobic conditions, chlorinated phenols can undergo reductive dechlorination when suitable electron-donating substrates are available. Halorespiring bacteria are known which can use both low and highly chlorinated congeners of chlorophenol as electron acceptors to support growth. Many strains of halorespiring bacteria have the capacity to eliminate ortho-chlorines; however only bacteria from the species Desulfitobacterium hafniense (formerly frappieri) can eliminate para- and meta-chlorines in addition to ortho-chlorines. Once dechlorinated, the phenolic carbon skeletons are completely converted to methane and carbon dioxide by other anaerobic microorganisms in the environment. Under aerobic conditions, both lower and higher chlorinated phenols can serve as sole electron and carbon sources supporting growth. The best studied strains utilizing pentachlorophenol belong to the genera Mycobacterium and Sphingomonas. Two main strategies are used by aerobic bacteria for the degradation of chlorophenols. Lower chlorinated phenols for the most part are initially attacked by monooxygenases yielding chlorocatechols as the first intermediates. On the other hand, polychlorinated phenols are converted to chlorohydroquinones as the initial intermediates. Fungi and some bacteria are additionally known that cometabolize chlorinated phenols.     

Microbial degradation of chlorinated benzenes

Chlorinated benzenes are important industrial intermediates and solvents. Their widespread use has resulted in broad distribution of these compounds in the environment. Chlorobenzenes (CBs) are subject to both aerobic and anaerobic metabolism. Under aerobic conditions, CBs with four or less chlorine groups are susceptible to oxidation by aerobic bacteria, including bacteria (Burkholderia, Pseudomonas, etc.) that grow on such compounds as the sole source of carbon and energy. Sound evidence for the mineralization of CBs has been provided based on stoichiometric release of chloride or mineralization of (14)C-labeled CBs to (14)CO(2). The degradative attack of CBs by these strains is initiated with dioxygenases eventually yielding chlorocatechols as intermediates in a pathway leading to CO(2) and chloride. Higher CBs are readily reductively dehalogenated to lower chlorinated benzenes in anaerobic environments. Halorespiring bacteria from the genus Dehalococcoides are implicated in this conversion. Lower chlorinated benzenes are less readily converted, and mono-chlorinated benzene is recalcitrant to biotransformation under anaerobic conditions.     

Microbial degradation of chlorinated phenols

The chlorinated phenols comprise a large group of toxic, man-made chemicals that are serious environmental pollutants. Microorganisms can degrade many, but not all, of the chlorinated phenols, often using chlorophenol-specific catabolic enzymes. Novel technologies are evolving for using specific microorganisms to clean contaminated soils and waters of chlorophenols.     

Microbial degradation of piperonylic acid

Several organisms were isolated for their ability to utilize piperonylate as a sole carbon source for growth and aPseudomonas species (Ps. PP-2) was selected for a study of the degradation of this substrate. Only vanillate, isovanillate,p-hydroxybenzoate and protocatechuate, of several possible catabolities, served as growth and oxidation substrates for the organism. Detailed analysis of the culture fluid from piperonylate-grown cells revealed the presence of vanillate and protocatechuate but isovanillate,p-hydroxybenzoate andm-hydroxybenzoate were not detected. The evidence presented suggests that piperonylate is metabolized first to vanillate by methylenedioxy ring cleavage and next to protocatechuate by direct demethylation of vanillate.