聚对苯二甲酸乙二醇酯生物降解的研究进展

塑料广泛存在于人类的日常生活中,在给人们生活带来便利的同时,大量塑料废物也给环境带来很大压力。聚对苯二甲酸乙二醇酯(polyethylene terephthalate, PET)是一种以石油为原料的高分子热塑性材料,因其具有耐用、透明度高、重量轻等特性,已成为世界上使用最广泛的塑料之一。由于PET具有结构复杂以及难降解的特性,可在自然界中长期存在,不仅对全球生态环境造成严重的污染,而且已经威胁到人类健康。如何对PET废弃物进行降解已成为全球的难题之一,相较于物理法和化学法,生物降解法是目前处理PET废弃物最为绿色环保的方法。本文分别介绍了微生物和生物酶对PET生物降解的研究现状、PET的生物降解途径、PET生物降解机制以及PET降解酶的分子改造等方面的研究,并对如何实现PET的高效降解、寻找和改造可降解高结晶度PET的微生物或酶进行展望,为PET的生物降解微生物或酶的有效开发应用提供理论依据。     

Biodegradation of polyethylene by the thermophilic bacterium Brevibacillus borstelensis

AIM: To select a polyethylene-degrading micro-organism and to study the factors affecting its biodegrading activity. METHODS AND RESULTS: A thermophilic bacterium Brevibaccillus borstelensis strain 707 (isolated from soil) utilized branched low-density polyethylene as the sole carbon source and degraded it. Incubation of polyethylene with B. borstelensis (30 days, 50 degrees C) reduced its gravimetric and molecular weights by 11 and 30% respectively. Brevibaccillus borstelensis also degraded polyethylene in the presence of mannitol. Biodegradation of u.v. photo-oxidized polyethylene increased with increasing irradiation time. Fourier Transform Infra-Red (FTIR) analysis of photo-oxidized polyethylene revealed a reduction in carbonyl groups after incubation with the bacteria. CONCLUSIONS: This study demonstrates that polyethylene--considered to be inert--can be biodegraded if the right microbial strain is isolated. Enrichment culture methods were effective for isolating a thermophilic bacterium capable of utilizing polyethylene as the sole carbon and energy source. Maximal biodegradation was obtained in combination with photo-oxidation, which showed that carbonyl residues formed by photo-oxidation play a role in biodegradation. Brevibaccillus borstelensis also degraded the CH2 backbone of nonirradiated polyethylene. SIGNIFICANCE AND IMPACT OF THE STUDY: Biodegradation of polyethylene by a single bacterial strain contributes to our understanding of the process and the factors affecting polyethylene biodegradation.     

Biodegradation of starch–polyethylene films in soil and by microbial cultures

Among the starch-containing low density polyethylene films tested for biodegradation, films containing 30% starch showed maximum biodegradation leading to a loss of 6.3% in weight and 84.5% starch upon burial in a soil–compost mixture for 48weeks. Biodegradation of this film was accelerated by incubation with an acclimatized culture in a shake-flask showing 11.2% and 68.9% loss of weight and starch respectively, after only 6 weeks. FTIR and 13C NMR analysis revealed that the loss of starch in biodegraded films is accompanied by structural changes in polyethylene in terms of reduction in the peak area of polyethylene backbone and short chain branches.     

大麦虫及其肠道微生物对聚乙烯的生物降解

【背景】废旧塑料聚乙烯因具有较高的化学惰性,不易被自然降解而形成长期污染。【目的】探究聚乙烯泡沫塑料对大麦虫生长发育的影响,为大麦虫作为降解聚乙烯泡沫塑料的昆虫推广提供理论依据。【方法】以大麦虫幼虫为研究对象,选用常见的泡沫塑料(聚乙烯),采用4种不同的饲喂方式T1 (麦麸)、T2 (泡沫塑料)、T3 (泡沫塑料+麦麸)、T4 (不饲喂)进行驯化,处理30 d后对大麦虫进行解剖,取肠道内容物于LB培养基中进行富集培养,将富集培养后的菌液加入以聚乙烯(polyethylene,PE)为唯一碳源的LCFBM培养基进行选择性培养,从中筛选分离得到对PE塑料有降解能力的菌株。【结果】取食泡沫塑料30d后,与单一饲喂PE相比,麦麸和PE混合饲喂后大麦虫幼虫的存活率为76%。采用傅里叶变换红外光谱检测发现虫粪组分中主要官能团中峰值明显变化,表明PE长链有断裂现象,并从肠道中分离得到3株可以对PE薄膜边缘造成明显侵蚀的菌株。【结论】大麦虫可取食并消化PE塑料,其肠道内的微生物对PE塑料的降解起到关键作用,研究结果为塑料污染的生物降解提供了科学证据。     

Biodegradation of polyethylene glycol by symbiotic mixed culture (obligate mutualism)

Neither Flavobacterium sp. nor Pseudomonas sp. grew on a polyethylene glycol (PEG) 6000 medium containing the culture filtrate of their mixed culture on PEG 6000. The two bacteria did not grow with a dialysis culture on a PEG 6000 medium. Flavobacterium sp. grew well on a dialysis culture containing a tetraethylene glycol medium supplemented with a small amount of PEG 6000 as an inducer, while poor growth of Pseudomonas sp. was observed. Three enzymes involved in the metabolism of PEG, PEG dehydrogenase, PEG-aldehyde dehydrogenase and PEG-carboxylate dehydrogenase (ether-cleaving) were present in the cells of Flavobacterium sp. The first two enzymes were not found in the cells of Pseudomonas sp. PEG 6000 was degraded neither by intact cells of Flavobacterium sp. nor by those of Pseudomonas sp., but it was degraded by their mixture. Glyoxylate, a metabolite liberated by the ether-cleaving enzyme, inhibited the growth of the mixed culture. The ether-cleaving enzyme was remarkably inhibited by glyoxylate. Glyoxylate was metabolized faster by Pseudomonas sp. than by Flavobacterium sp., and seemed to be a key material for the symbiosis.     

Biodegradation of polyethylene terephthalate (PET) by diverse marine bacteria in deep-sea sediments

PET plastic waste entering the oceans is supposed to take hundreds of years to degrade and tends to accumulate in the deep sea. However, we know little about the bacteria capable of plastic degradation therein. To determine whether PET-degrading bacteria are present in deep-sea sediment, we collected the samples from the eastern central Pacific Ocean and initiated microbial incubation with PET as the carbon source. After enrichment with PET for 2 years, we gained all 15 deep-sea sediment communities at five oceanic sampling sites. Bacterial isolation for pure culture and further growth tests confirmed that diverse bacteria possess degradation ability including Alcanivorax xenomutans BC02_1_A5, Marinobacter sediminum BC31_3_A1, Marinobacter gudaonensis BC06_2_A6, Thalassospira xiamenensis BC02_2_A1 and Nocardioides marinus BC14_2_R3. Furthermore, four strains were chosen as representatives to reconfirm the PET degradation capability by SEM, weight loss and UPLC-MS. The results showed that after 30-day incubation, 1.3%–1.8% of PET was lost. De-polymerization of PET by the four strains was confirmed by the occurrence of the PET monomer of MHET and TPA as the key degradation products. Bacterial consortia possessing PET-degrading potential are prevalent and diverse and might play a key role in the removal of PET pollutants in deep oceans.     

Cellular proliferation, differentiation and apoptosis in polyether-polyurethane sponge implant model in mice

The integration of implanted material to host organism requires spatial and temporal organization of several cellular processes, such as proliferation, differentiation and apoptosis. Despite the clinical relevance of these processes, there is little information regarding the sequence of such events in synthetic matrices. Here, we present a combination of techniques used to characterize the fibrovascular response in subcutaneous polyether-polyurethane sponge implants in mice at days 4, 7, 10 and 14 postimplantation. The AgNOR technique was modified and used as a surrogate marker for proliferating and activated cells invading the implant. The number of AgNOR-stained cells increased progressively from day 4 (606+/-76) to day 14 (2146+/-71) postimplantation. The number of TUNEL-positive (apoptotic index) cells also increased progressively from day 4 (459+/-40) to day 14 (1157+/-119) postimplantation. However, the ratio of TUNEL-labeled/proliferating cells had its highest peak in the early phase of the process remaining stable until day 14. Using Picrosirius staining it was shown that thin collagen increased from day 4, peaking at day 10 and falling markedly at day 14, whereas dense collagen increased progressively during the whole period. These experiments hold potential to investigate not only distinct phases of tissue repair induced by synthetic matrices but also to study underlying mechanisms involved.     

Biodegradation of methoxychlor and kelthane

Summary From the series of organochlorine insecticides, kelthane and methoxychlor were most easily degraded by the bacteria tested. The amount of metabolites from methoxychlor was low and recovery of the insecticide from a bacterial suspension was not possible. Details for biodegradation of methoxychlor are described. Anaerobiosis, neutral pH, and a large number of bacteria are necessary. Some reducing substances, however, may replace anaerobic conditions. The contact of bacteria with kelthane or methoxychlor liberates Cl^– but the quantity does not correspond to the expected theoretical value. A dechlorination of the ethane portion of the molecule is hypothesized.Antiseptics added to the bacterial suspension and autoclaving lower the amount transformed. Metabolites are never obtained under these conditions which indicates an active process in addition to a passive absorption phenomenon.     

Biodegradation of EDTA

The chelating agent ethylenediaminetetraacetate (EDTA) is not degraded by conventional biological and physicochemical methods for the treatment of wastewater and the purification of drinking water. Of the measurable organic compounds it is the one present at the highest concentration in many surface and drinking waters. In recent years, however, studies have demonstrated that EDTA can be degraded by specially enriched bacterial cultures and in wastewater treatment plants receiving EDTA-containing effluents. The amounts of EDTA released into the aquatic environment could thus be reduced by establishing appropriate biological wastewater treatment plants. This article describes the degradation of EDTA and its metal chelates by different bacterial cultures, catabolic steps in EDTA degradation, and biological methods for the removal of this chelating agent from wastewaters. Received: 14 September 1998 / Received revision: 9 December 1998 / Accepted: 11 December 1998     

Biodegradation and biotransformation of explosives

Explosives now contaminate millions of hectares of land in the US alone, with global levels of contamination difficult to fully assess. Understanding the biology behind the metabolism of these toxic compounds by microorganisms and plants is imperative for managing these pollutants in the environment. Towards this aim, recent studies have identified, and are now characterizing, plant genes involved in 2,4,6-trinitrotoluene detoxification and the biochemical pathways of nitramine degradation in microorganisms. A key scientific goal continues to be identification of enzymes capable of degrading 2,4,6-trinitrotoluene and this still remains elusive, although recent reports give insights into the origin of nitrite released during biotransformation of this major contaminant. Promising phytoremediation research using transgenic model plant systems has now been transferred to poplar, a species with field applicability.     

Biodegradation of o-Benzyl-p-Chlorophenol

The extent of biodegradation of o-benzyl-p-chlorophenol, marketed as a germicide under the name Santophen((R)) 1 (Monsanto Co.), in river water, sewage, and activated sludge was determined. Biodegradation was assessed by use of a colorimetric procedure for phenolic materials, carbon analysis, and CO(2) evolution. In unacclimated river water, 0.1 mg of Santophen 1 per liter was degraded within 6 days. In sewage, 0.5 and 1.0 mg/liter levels of Santophen 1 were degraded in 1 day. Acclimated activated sludge achieved 80% biodegradation of 1.0 mg/liter Santophen 1 in 8 h and 100% in 24 h. When effluent from a semicontinuous activated sludge unit, acclimated to 20 mg of Santophen 1 per liter was used as the inoculum for the CO(2) evolution procedure, 60% of the total theoretical CO(2) was evolved from Santophen 1. Based on the results of these studies, indicating Santophen 1 to be readily biodegraded in at least four biological systems, the continued use of present levels of Santophen 1 should present no significant environmental problems.     

Biodegradation of N-Methylmorpholine-N-oxide

N-Methylmorpholine-N-oxide (NMMO) is capable of dissolving cellulose without any further addition of chemicals. The solution can be used to produce cellulosic staple fibres by pressing it through spinning jets into an aqueous spinning bath. Because of results from conventional biodegradation tests using non-adapted activated sludge, the solvent is generally considered being persistent. The object of the described work was to show, whether and how activated sludge can be adapted to N-methylmorpholine-N-oxide and whether it is possible to purify NMMO-containing wastewaters in conventional wastewater treatment plants. The experiments showed that the sludge can be adapted within about 15–20 days. Adapted sludge can degrade the substance itself and its most important metabolites to concentrations below their detection levels and retain this ability even during limited periods without solvent being present in the wastewater. The main requirement for a successful adaptation is a high sludge age. The degradation takes place in several steps. First, NMMO is reduced to N-methylmorpholine. The next step is a demethylation of N-methylmorpholine to morpholine. This step is crucial for the adaptation process. Once morpholine has been formed, the adaptation proceeds very quickly until none of the substances in question can be detected any longer. So the next step must be the cleavage of the morpholine ring structure.     

Biodegradation of plastics

Widespread studies on the biodegradation of plastics have been carried out in order to overcome the environmental problems associated with synthetic plastic waste. Recent work has included studies of the distribution of synthetic polymer-degrading microorganisms in the environment, the isolation of new microorganisms for biodegradation, the discovery of new degradation enzymes, and the cloning of genes for synthetic polymer-degrading enzymes.     

Biodegradation of haloalkanes

Halogenated alkanes constitute a significant group among the organic pollutants of environmental concern. Their industrial and agricultural uses are extensive, but until 1978 they were considered to be non-biodegradable. In recent years, microorganisms were described that could degrade, partially or fully, singly or in consortia, many of the compounds tested. The first step in haloalkane degradation appears to be universal: removal of the halogen atom(s). This is mediated by a group of enzymes, generally known as dehalogenases, acting in most cases either as halidohydrolases or oxygenases. Nevertheless, information is still severely lacking regarding the biochemical pathways involved in these processes, as well as their genetic control.A recently isolated Pseudomonas strain, named ES-2, was shown to possess a very wide degradative spectrum, and to contain at least one hydrolytic dehalogenase. The utilization by this organism of water-insoluble haloalkanes, such as 1-bromooctane, appears to consist of three phases: extracellular emulsification by a constitutively excreted surface active agent, periplasmic dehalogenation by an inducible dehalogenase, and intracellular degradation of the residual carbon skeleton.     

Biodegradation of polyhydroxyalkanoates

Abstract Degradation of poly(3-hydroxybutyrate) and copolymers with 3-hydroxyvaleric acid was investigated in natural environments, and the microorganisms involved were isolated and identified. The influence of abiotic and biotic factors on the degradation is discussed.     

Biodegradation of nitro-explosives

Environmental contamination by nitro compounds is associated principally with the explosives industry. However, global production and use of explosives is unavoidable. The presently widely used nitro-explosives are TNT (Trinitrotoluene), RDX (Royal Demolition Explosive) and HMX (High Melting Explosive). Nevertheless, the problems of these nitro-explosives are almost parallel due to their similarities of production processes, abundance of nitro-explosives and resembling chemical structures. The nitro-explosives per se as well as their environmental transformation products are toxic, showing symptoms as methaemoglobinaemia, kidney trouble, jaundice etc. Hence their removal/degradation from soil/water is essential. Aerobic and anaerobic degradation of TNT and RDX have been reported, while for HMX anaerobic or anoxic degradation have been described in many studies. A multisystem involvement using plants in remediation is gaining importance. Thus the information about degradation of nitro-explosives is available in jigsaw pieces which needs to be arranged and lacunae filled to get concrete degradative schemes so that environmental pollution from nitro-explosives can be dealt with more successfully at a macroscale. An overview of the reports on nitro-explosives degradation, future outlook and studies done by us are presented in this review.