Genetics of naphthalene and phenanthrene degradation by Comamonas testosteroni

Naphthalene and phenanthrene have long been used as model compounds to investigate the ability of bacteria to degrade polycyclic aromatic hydrocarbons. The catabolic pathways have been determined, several of the enzymes have been purified to homogeneity, and genes have been cloned and sequenced. However, the majority of this work has been performed with fast growing Pseudomonas strains related to the archetypal naphthalene-degrading P. putida strains G7 and NCIB 9816-4. Recently Comamonas testosteroni strains able to degrade naphthalene and phenanthrene have been isolated and shown to possess genes for polycyclic aromatic hydrocarbon degradation that are different from the canonical genes found in Pseudomonas species. For instance, C. testosteroni GZ39 has genes for naphthalene and phenanthrene degradation which are not only different from those found in Pseudomonas species but are also arranged in a different configuration. C. testosteroni GZ42, on the other hand, has genes for naphthalene and phenanthrene degradation which are arranged almost the same as those found in Pseudomonas species but show significant divergence in their sequences. Received 10 August 1997/ Accepted in revised form 15 August 1997     

蚯蚓对细菌降解土壤中菲的作用

通过30d室内培养试验,分别研究了接种蚯蚓(E)、细菌(B)以及同时接种细菌和蚯蚓(BE)对土壤中菲降解的影响.结果表明: 在土壤中菲的初始污染浓度为50 mg*kg-1的条件下,各处理间菲的降解率差异显著,其降解率的大小顺序依次为:BE》B》E》CK(对照); 在150 mg*kg-1菲的初始污染浓度下,BE处理中菲的降解率高达98.86%,显著高于CK和E处理.B处理中细菌的双加氧酶活性在3种菲初始污染浓度下没有显著差异,而BE处理中双加氧酶的活性随着土壤中菲的初始污染浓度的升高而增加.在相同菲污染浓度下BE处理中蚯蚓体内的菲含量明显高于E处理.表明蚯蚓能够通过生物富集作用降低土壤中菲的浓度,而蚯蚓与细菌的相互作用能够进一步促进土壤中菲的降解.     

Pathway and rate-limiting step of glyphosate degradation by Aspergillus oryzae A-F02

Aspergillus oryzae A-F02, a glyphosate-degrading fungus, was isolated from an aeration tank in a pesticide factory. The pathway and rate-limiting step of glyphosate (GP) degradation were investigated through metabolite analysis. GP, aminomethylphosphonic acid (AMPA), and methylamine were detected in the fermentation liquid of A. oryzae A-F02, whereas sarcosine and glycine were not. The pathway of GP degradation in A. oryzae A-F02 was revealed: GP was first degraded into AMPA, which was then degraded into methylamine. Finally, methylamine was further degraded into other products. Investigating the effects of the exogenous addition of substrates and metabolites showed that the degradation of GP to AMPA is the rate-limiting step of GP degradation by A. oryzae A-F02. In addition, the accumulation of AMPA and methylamine did not cause feedback inhibition in GP degradation. Results showed that degrading GP to AMPA was a crucial step in the degradation of GP, which determines the degradation rate of GP by A. oryzae A-F02.     

Biodegradation of phenanthrene by Arthrobacter polychromogenes isolated from a contaminated soil

Summary Degradation of phenanthrene by Arthrobacter polychromogenes isolated from a contaminated soil was investigated. In experiments in which [9-¹⁴C]-phenanthrene was incubated with cultures of A. polychromogenes containing 150 mg phenanthrene/l it was shown that after 26 h of incubation 47.7% of the recovered radiolabelled carbon originally present was metabolized to ¹⁴CO₂, 47.8% was recovered from the aqueous fraction, and 4.5% remained in the dichloromethane fraction. Increasing phenanthrene concentration in the culture medium resulted in improved growth and degradation rates, probably due to the higher amount of phenanthrene crystals in the medium. Shifting the temperature from 30°C to 35°C did not influence phenanthrene degradation significantly but inhibited cell division of A. polychromogenes. Medium supplementation with glucose led to stimulation of phenanthrene degradation at low amounts of glucose (0.45 g/l) whereas at higher concentrations (3 g/l) phenanthrene mineralization decreased.Professor Dr. D. Behrens dedicated to his 65th birthdayOffprint requests to: H.-J. Rehm     

Functional analysis of genes involved in biphenyl, naphthalene, phenanthrene, and m-xylene degradation by Sphingomonas yanoikuyae B1

Sphingomonas yanoikuyae B1 is able to utilize toluene, m-xylene, p-xylene, biphenyl, naphthalene, phenanthrene, and anthracene as sole sources of carbon and energy for growth. A forty kilobase region of DNA containing most of the genes for the degradation of these aromatic compounds was previously cloned and sequenced. Insertional inactivation of bphC results in the inability of B1 to grow on both polycyclic and monocyclic compounds. Complementation experiments indicate that the metabolic block is actually due to a polar effect on the expression of bphA3, coding for a ferredoxin component of a dioxygenase. Lack of the ferredoxin results in a nonfunctional polycyclic aromatic hydrocarbon dioxygenase and a nonfunctional toluate dioxygenase indicating that the electron transfer components are capable of interacting with multiple oxygenase components. Insertional inactivation of a gene for a dioxygenase oxygenase component downstream of bphA3 had no apparent effect on growth besides a polar effect on nahD which is only needed for growth of B1 on naphthalene. Insertional inactivation of either xylE or xylG in the meta-cleavage operon results in a polar effect on bphB, the last gene in the operon. However, insertional inactivation of xylX at the beginning of this cluster of genes does not result in a polar effect suggesting that the genes for the meta-cleavage pathway, although colinear, are organized in at least two operons. These experiments confirm the biological role of several genes involved in metabolism of aromatic compounds by S. yanoikuyae B1 and demonstrate the interdependency of the metabolic pathways for polycyclic and monocyclic aromatic hydrocarbon degradation. Received 13 May 1999/ Accepted in revised form 05 July 1999     

The effect of inorganic and organic supplements on the microbial degradation of phenanthrene and pyrene in soils

The effects of several bioremediation stimulants, including potentialmetabolism pathway inducers, inorganic/organic nutrients, and surfactants onthe metabolism of phenanthrene and pyrene, as well as the populationdynamics of PAH degrading microorganisms was examined in five soils withdiffering background PAH concentrations, exposure histories and physicalproperties. Most of the supplements either had no significant effect ordecreased the mineralization of [¹⁴C]-phenanthrene and[¹⁴C]-pyrene in soil slurry microcosms. The effect of aparticular supplement, however, was often not uniform within or acrosssoils. Decreased mineralization of [¹⁴C]-phenanthrene and[¹⁴C]-pyrene was usually due to either preferential use of thesupplement as carbon source and/or stimulation of non-PAH degradingmicroorganisms. Many of the supplements increased populations ofheterotrophic microorganisms, as measured by plate counts, but did notincrease populations of phenanthrene degrading microorganisms, as measuredby the [¹⁴C]-PAH mineralization MPN analysis or cellularincorporation of [¹⁴C]-PAH. These results suggest that the PAHdegrading community at each site may be unique in their response tomaterials added in an attempt to stimulate PAH degradation. Thecharacteristics of the site, including exposure history, soil type, andtemporal variation may all influence their response.     

Degradation of phenanthrene and anthracene by Nocardia otitidiscaviarum strain TSH1, a moderately thermophilic bacterium

Aims:  The metabolism of phenanthrene and anthracene by a moderate thermophilic Nocardia otitidiscaviarum strain TSH1 was examined.
Methods and Results:  When strain TSH1 was grown in the presence of anthracene, four metabolites were identified as 1,2-dihydroxy-1,2-dihydroanthracene, 3-(2-carboxyvinyl)naphthalene-2-carboxylic acid, 2,3-dihydroxynaphthalene and benzoic acid using gas chromatography-mass spectrometry (GC-MS), reverse phase-high performance liquid chromatography (RP-HPLC) and thin-layer chromatography (TLC). Degradation studies with phenanthrene revealed 2,2'-diphenic acid, phthalic acid, 4-hydroxyphenylacetic acid, o -hydroxyphenylacetic acid, benzoic acid, a phenanthrene dihydrodiol, 4-[1-hydroxy(2-naphthyl)]-2-oxobut-3-enoic acid and 1-hydroxy-2-naphthoic acid (1H2NA), as detectable metabolites.
Conclusions:  Strain TSH1 initiates phenanthrene degradation via dioxygenation at the C-3 and C-4 or at C-9 and C-10 ring positions. Ortho -cleavage of the 9,10-diol leads to formation of 2,2'-diphenic acid. The 3,4-diol ring is cleaved to form 1H2NA which can subsequently be degraded through o -phthalic acid pathway. Benzoate does not fit in the previously published pathways from mesophiles. Anthracene metabolism seems to start with a dioxygenation at the 1 and 2 positions and ortho -cleavage of the resulting diol. The pathway proceeds probably through 2,3-dicarboxynaphthalene and 2,3-dihydroxynaphthalene. Degradation of 2,3-dihydroxynaphthalene to benzoate and transformation of the later to catechol is a possible route for the further degradation of anthracene.
Significance and Impact of the Study:  For the first time, metabolism of phenanthrene and anthracene in a thermophilic Nocardia strain was investigated.     

Biodegradation of phenanthrene by Pseudomonas sp. BZ-3, isolated from crude oil contaminated soil

A phenanthrene (PHE) degrading bacterium strain BZ-3 was isolated from the crude oil contaminated soil in Binzhou, China. The isolate was identified as Pseudomonas sp. BZ-3 on the basis of 16S rRNA gene sequence. Various experiments were conducted to investigate the effect of pH, salinity and PHE concentration on the degradation efficiency of PHE. The degradation efficiency and degradation metabolites of PHE were detected by using GC–MS and HPLC-MS analyses. The strain BZ-3 could degrade 75% of PHE at an initial concentration of 50 mg/L under 20 g/L salinity in 7 days. PHE degradation kinetics was estimated in a first-order degradation rate model and the rate coefficient was calculated as 0.108 d⁻¹. On the basis of the identified degradation metabolites, the strain BZ-3 could degrade PHE in the salicylate metabolic pathway. In a mixture system consisting of PHE and other PAHs including naphthalene (NA), anthracene (ANTH), and pyrene (PYR), the strain BZ-3 showed an efficiently degradation capability. Further study showed that the strain BZ-3 could also use NA, ANTH, PYR, xylene, 1-hydroxy-2-naphthoic acid, and hexane as the sole carbon and energy source, but did not grow on nitrobenzene-containing medium.     

Biodegradation of phenanthrene by the indigenous microbial biomass in a zinc amended soil

AIMS: To study the effect of zinc on the biodegradation of phenanthrene by the microbial biomass in soil. METHODS AND RESULTS: Uncontaminated soil was amended with zinc and phenanthrene as single or co-contaminants, and microbial metabolic activity was measured using an intracellular dehydrogenase enzyme bioassay over 37 days. Contaminants were amended at optimum, action and double the action level specified in 'The New Dutch List' (Ministry of Housing, Spatial Planning and Environment, the Netherlands, 2000). Microbial activity in soils with zinc or phenanthrene alone indicated the presence of tolerant, albeit inhibited soil micro-organisms. A zinc concentration at the optimum level of 140 mg kg(-1) in the co-contaminated soil (phenanthrene at 40 mg kg(-1)) resulted in marginal stimulation of the rate of phenanthrene biodegradation. However, Zn2+ concentrations at the action and double the action level of zinc (720 and 1440 mg kg(-1)) inhibited phenanthrene degradation. CONCLUSIONS: Biodegradation of phenanthrene in soils co-contaminated with zinc at concentrations above the action value is impeded. SIGNIFICANCE AND IMPACT OF THE STUDY: Bioremediation efforts to remove polycyclic aromatic hydrocarbon in zinc co-contaminated soils are likely to be constrained.     

Filamentous fungi with high paraquat-degrading activity isolated from contaminated agricultural soils in northern Thailand

The contamination of paraquat (1,1′-dimethyl-4,4′-bipyridylium dichloride) herbicide from the farming area has become a public concern in many countries. This herbicide harms to human health and negatively effects the soil fertility. Several methods have been introduced for the remediation of paraquat. In this study, 20 isolates of the paraquat-tolerant fungi were isolated from the contaminated soil samples in northern Thailand. We found that isolate PRPY-2 and PFCM-1 exhibited the highest degradation activity of paraquat on synthetic liquid medium. About 80 and 68% of paraquat were removed by PRPY-2 and PFCM-1 respectively after 15 days of cultivation. Based on the morphological characteristic and molecular analysis, the fungal isolate PRPY-2 and PFCM-1 were identified as Aspergillus tamarii and Cunninghamella sp. respectively. The biosorption of paraquat on these fungal mycelia was also investigated. It was found that only 8–10% of paraquat could be detected on their mycelia, while 24–46% of paraquat was degraded by fungal mycelia. This is the first report on paraquat degrading ability by A. tamarii and Cunninghamella sp. It is demonstrated that these filamentous fungi are promising microorganisms available for remediation of paraquat contaminated environment.     

双加氧酶活力对细菌降解菲的指示作用

在液体培养基中选用两种石油降解细菌进行菲降解实验,研究了菲降解率和双加氧酶活力的变化。结果表明,菲降解率受其浓度的影响,当菲浓度为100mg·L-1时,其降解率为最高。而菲浓度高于100mg·L-1时,其降解率下降。实验发现在菲浓度为50～250mg·L-1条件下,细菌的双加氧酶活力与其菲的降解率存在较好的相关性,对细菌降解菲具有指示作用,可将双加氧酶活力作为菲降解率变化的评价指标。     

Application of microscopic fungi isolated from polluted industrial areas for polycyclic aromatic hydrocarbons and pentachlorophenol reduction

The growth abilities of fifteen fungal strains isolated fromcontaminated areas, in the presence of xenobiotics compounds mixture (overworked cuttingfluid, crude and waste oil) were examined. Strains with the richest growth were chosen for anthracene, phenanthrene and pentachlorophenol biodegradation in Sabouraudmedium (with initial xenobiotic concentration 250 mg/l in cultures with polycyclicaromatic hydrocarbons and 10 mg/l for the chlorinated substrate). Strains IM 1063and IM 6325 were able to attack phenanthrene forming its derivative 9-phenanthrenolwith the yields 5.22 mg/l and 2.82 mg/l, respectively. Strain IM 1063 and IM 6325 transformed pentachlorophenol to an intermediatecompound – pentachloromethoxybenzene. Final content of pentachloromethoxybenzene reached 3.46 mg/l and3.2 mg/l, respectively. Strain IM 6203 (contrary to other strains) released an intermediateproduct of pentachlorophenol metabolism – 2,3,5,6-tetrachlorohydroquinone(8.73 mg/l substrate remaining and 1.2 mg/l 2,3,5,6-tetrachlorohydroquinone forming).The IM 6203 strain was identified as Mucor ramosissimus. The chlorinatedpesticide degradation by M. ramossimus was improved significantly on a medium with overworked oil. Only 8.3% of pentachlorophenol and 4.3% of 2,3,5,6-tetrachlorohydroquinone in relation to the introduced substrate (10 mg/l) were found, after7 days of incubation. The growth of M. ramosissimus on medium with overworked oil in pentachlorophenol presence was associated with oil emulgation,which enhanced fungal growth and the pesticide degradation.     

利用黄粉虫分离土壤昆虫病原真菌

利用黄粉虫Tenebrio molitorL.作为寄主从土壤中诱感并分离昆虫病原真菌。结果显示,从吉林市的18个土样中分离出球孢白僵菌(Beauveria bassiana)、金龟子绿僵菌(Metarhiziumanisopliae)和玫烟色拟青霉(Paecilomyces fumosoroseus)。土样中的昆虫病原真菌检出率为77.78%。这表明利用黄粉虫分离土壤中的昆虫病原真菌是一种简单、有效的方法。     

Biodegradation of hexahydro-1,3,5-trinitro-1,3,5-triazine by novel fungi isolated from unexploded ordnance contaminated marine sediment

Undersea deposition of unexploded ordnance (UXO) constitutes a potential source of contamination of marine environments by hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) and octahydro-1,3,5,7-tetranitro-1,3,5,7-tetrazocine (HMX). Using sediment from a coastal UXO field, Oahu Island, Hawaii, we isolated four novel aerobic RDX-degrading fungi HAW-OCF1, HAW-OCF2, HAW-OCF3 and HAW-OCF5, tentatively identified as members of Rhodotorula, Bullera, Acremonium and Penicillium, respectively. The four isolates mineralized 15–34% of RDX in 58 days as determined by liberated ¹⁴CO₂. Subsequently we selected Acremonium to determine biotransformation pathway(s) of RDX in more details. When RDX (100 μM) was incubated with resting cells of Acremonium we detected methylenedinitramine (MEDINA), N₂O and HCHO. Also we detected hexahydro-1-nitroso-3,5-dinitro-1,3,5-triazine (MNX) together with trace amounts of hexahydro-1,3-dinitroso-5-nitro-1,3,5-triazine (DNX) and hexahydro-1,3,5-trinitroso-1,3,5-triazine (TNX). Under the same conditions MNX produced N₂O and HCHO together with trace amounts of DNX and TNX, but we were unable to detect MEDINA. TNX did not degrade with Acremonium. These experimental findings suggested that RDX degraded via at least two major initial routes; one route involved direct ring cleavage to MEDINA and another involved reduction to MNX prior to ring cleavage. Nitrite was only detected in trace amounts suggesting that degradation via initial denitration did take place but not significantly. Aerobic incubation of Acremonium in sediment contaminated with RDX led to enhanced removal of the nitramine.     

Production of rhamnolipids and diesel oil degradation by bacteria isolated from soil contaminated by petroleum

Biosurfactants are microbial secondary metabolites. The most studied are rhamnolipids, which decrease the surface tension and have emulsifying capacity. In this study, the production of biosurfactants, with emphasis on rhamnolipids, and diesel oil degradation by 18 strains of bacteria isolated from waste landfill soil contaminated by petroleum was analyzed. Among the studied bacteria, gram‐positive endospore forming rods (39%), gram positive rods without endospores (17%), and gram‐negative rods (44%) were found. The following methods were used to test for biosurfactant production: oil spreading, emulsification, and hemolytic activity. All strains showed the ability to disperse the diesel oil, while 77% and 44% of the strains showed hemolysis and emulsification of diesel oil, respectively. Rhamnolipids production was observed in four strains that were classified on the basis of the 16S rRNA sequences as Pseudomonas aeruginosa. Only those strains showed the rhlAB gene involved in rhamnolipids synthesis, and antibacterial activity against Escherichia coli, P. aeruginosa, Staphylococcus aureus, Bacillus cereus, Erwinia carotovora, and Ralstonia solanacearum. The highest production of rhamnolipids was 565.7 mg/L observed in mineral medium containing olive oil (pH 8). With regard to the capacity to degrade diesel oil, it was observed that 7 strains were positive in reduction of the dye 2,6‐dichlorophenolindophenol (2,6‐DCPIP) while 16 had the gene alkane mono‐oxygenase (alkB), and the producers of rhamnolipids were positive in both tests. Several bacterial strains have shown high potential to be explored further for bioremediation purposes due to their simultaneous ability to emulsify, disperse, and degrade diesel oil. © 2015 American Institute of Chemical Engineers Biotechnol. Prog., 32:262–270, 2016     

Aerobic biodegradation of methyl tert-butyl ether (MTBE) by pure bacterial cultures isolated from contaminated soil

Summary Methyl tert-Butyl Ether (MTBE) has been used in gasoline as a substitute for lead-based additives, which have been demonstrated to be toxic. MTBE however, is persistent in soil and water, showing high affinity for water and low affinity for soil, and has become an important contaminant. Therefore, the aim of this work was to isolate and identify soil microorganisms capable of degrading MTBE. Two samples were taken from a gasoline-contaminated soil at a service station and 59 different bacterial strains were isolated by enrichment culture with three consecutive selective transfers. Biochemical and morphological characterization of the bacterial isolates classified them into the following groups: Bacillus, Rhodococcus, Micrococcus, Aureobacterium and Proteus. Twelve strains were selected for evaluation of MTBE biodegradation depending on visual growth and biomass production of the isolates in minimal salt broth. Six strains significantly reduced MTBE concentration (22–37%) compared to an abiotic control after 5 days of incubation. Although it has been considered that MTBE is degraded mainly by cometabolism, our results demonstrate that these microorganisms are able to reduce MTBE concentration when MTBE is the sole source of carbon.     

Mycoremediation of crude oil contaminated soil by specific fungi isolated from Dhahran in Saudi Arabia

Crude oil biodegrading microorganism considers the key role for environmental preserving. In this investigation, crude oil biodegrading fungal strains have been isolated in polluted soil of crude-oil at khurais oil ground in Kingdom of Saudi Arabia. Among of 22 fungal isolates, only three isolates reflected potential capability for oil degradation. These isolates were identified and submitted to GenBank as (A1) Aspergillus polyporicola (MT448790), (A2) Aspergillus spelaeus (MT448791) and (A3) Aspergillus niger (MT459302) through internal-transcribed spacer-regions (ITS1&ITS2) for sequencing in molecular marker. Comparing with controls, strain (A1) Aspergillus niger was superior for biodegradation ability (58%) comparing with Aspergillus polyporicola and Aspergillus spelaeus degrading were showed 47 and 51% respectively. Employed CO₂ evolution as indicator for petroleum oil biodegradation by the fungal isolates reflected that, Aspergillus niger emission highest CO2 (28.6%) comparing with Aspergillus spelaeus and Aspergillus polyporicola which showed 13% and 12.4% respectively. capability of Aspergillus sp. to tolerate and adapted oil pollutants with successful growth rate on them, indicated that it can be employed as mycoremediation agent for recovering restoring ecosystem when contaminated by crude oil.     

Initial oxidative and subsequent conjugative metabolites produced during the metabolism of phenanthrene by fungi

Three filamentous fungi were examined for the ability to biotransform phenanthrene to oxidative (phase I) and conjugative (phase II) metabolites. Phenanthrene metabolites were purified by high-performance liquid chromatography (HPLC) and identified by UV/visible absorption, mass, and¹H NMR spectra.Aspergillus niger ATCC 6275,Syncephalastrum racemosum UT-70, andCunninghamella elegans ATCC 9245 initially transformed [9-¹⁴C]phenanthrene to produce metabolites at the 9,10-, 1,2-, and 3,4- positions. Subsequently, sulfate conjugates of phase I metabolites were formed byA. niger, S. racemosum, andC. elegans. Minor glucuronide conjugates of 9-phenanthrol and phenanthrenetrans-9,10-dihydrodiol were formed byS. racemosum andA. niger, respectively. In addition,C. elegans produced the glucose conjugates 1-phenanthryl -d-glucopyranoside and 2-hydroxy-1-phenanthryl -d-glucopyranoside, a novel metabolite. [9-¹⁴C]Phenanthrene metabolites were not detected in organic extracts from biotransformation experiments with the yeasts,Candida lipolytica 37-1,Candida tropicalis ATCC 32113, andCandida maltosa R-42.     

水溶性有机质对土壤吸附菲的影响

研究了来源于稻草腐熟物的外源水溶性有机质(DOM)和土壤本身固有的内源DOM对有机碳含量不同的3种土壤吸附菲的影响.结果表明,不同处理土壤对菲的吸附曲线均为线性,其吸附系数(K_d)与土壤有机碳含量(f_oc)正相关.去除内源DOM后,黄棕壤、红粘田和黑土吸附菲的K_d值增加了7.08%～21.4%,增加量(ΔK_d)和增加幅度与f_oc正相关,表明土壤中存在的内源DOM抑制土壤对菲的吸附.而外源DOM对土壤吸附菲的影响与其浓度密切相关.在供试浓度范围(0～106 mg DOC·L^-1)内,红粘田吸附菲的K_d值随加入外源DOM浓度的提高先增大后减小.外源DOM浓度为28 mg DOC·L^-1时,红粘田吸附菲的K_d值增加了19.5%;而当外源DOM浓度≥52 mg DOC·L^-1时,则明显抑制菲的吸附.内源和外源DOM对土壤吸附菲的影响,主要与DOM和菲在溶液中的结合作用、在土壤中的累积吸附效应等有关.