The Microbial Transformation of Phenanthrene and Anthracene

The transformation of phenanthrene and anthracene by Rhodococcus rhodnii 135, Pseudomonas fluorescens 26K, and Arthrobacter sp. K3 is studied. Twenty-one intermediates of phenanthrene and anthracene transformation are identified by HPLC, mass spectrometry, and NMR spectroscopy. P. fluorescens 26K and Arthrobacter sp. K3 are found to produce a wide range of intermediates, whereas R. rhodnii 135 oxidizes phenanthrene, resulting in the formation of a sole product, 3-hydroxyphenanthrene. Putative transformation pathways of phenanthrene and anthracene are proposed for the three bacterial strains studied. These strains can be used to obtain valuable compounds (such as hydroxylated polycyclic aromatic hydrocarbons) that are difficult to produce by chemical synthesis.__________Translated from Mikrobiologiya, Vol. 74, No. 3, 2005, pp. 357–364.Original Russian Text Copyright © 2005 by Baboshin, Baskunov, Finkelstein, Golovlev, Golovleva.     

Fluorene degradation by bacteria of the genus Rhodococcus

Of the four investigated Rhodococcus strains (R. rhodochrous 172, R. opacus 4a and 557, and R. rhodnii 135), the first three strains were found to be able to completely transform fluorene when it was present in the medium as the sole source of carbon at a concentration of 12-25 mg/l. At a fluorene concentration of 50-100 mg/l in the medium, the rhodococci transformed 50% of the substrate in 14 days. The addition of casamino acids and sucrose (1-5 g/l) stimulated fluorene transformation, so that R. rhodochrous 172 could completely transform it in 2-5 days. Nine intermediates of fluorene transformation were isolated, purified, and structurally characterized. It was found that R. rhodnii 135 and R. opacus strains 4a and 557 hydroxylated fluorene with the formation of 2-hydroxyfluorene and 2,7-dihydroxyfluorene. R. rhodochrous 172 transformed fluorene via two independent pathways to a greater degree than did the other rhodococci studied.     

Phenanthrene and anthracene degradation by microorganisms of the genus <Emphasis Type="Italic">Rhodococcus</Emphasis>

The cells of Rhodococcus opacus 412 and R. rhodnii 135 were adapted to phenanthrene and anthracene on a solid mineral medium. Preliminary adaptation of the strains accelerated the metabolism of polyaromatic hydrocarbons and provided for the ability of microorganisms to grow on pheanthrene as a sole carbon and energy source in a liquid mineral medium. It was shown that phenanthrene was mineralized by the strains through 7,8-benzocoumarin, 1-hydroxy-2-naphthoaldehyde, 1-hydroxy-2-naphthoic acid, salicylaldehyde, salicylate and catechol to the intermediates of tricarbonic acid cycle and partially transformed with the accumulation of the products of subsequent monooxygenation (3-hydroxyphenanthrene and phenanthrene dihydroxylated not in ortho-position). As a result of the adaptation of the strains to anthracene on a solid mineral medium, the obtained variant of strain R. opacus 412 was able to transform anthracene in a liquid mineral medium to anthraquinone and 6,7-benzocoumarin.     

Plasmid-mediated mineralization of naphthalene, phenanthrene, and anthracene.

The well-characterized plasmid-encoded naphthalene degradation pathway in Pseudomonas putida PpG7(NAH7) was used to investigate the role of the NAH plasmid-encoded pathway in mineralizing phenanthrene and anthracene. Three Pseudomonas strains, designated 5R, DFC49, and DFC50, were recovered from a polynuclear aromatic hydrocarbon-degrading inoculum developed from a manufactured gas plant soil slurry reactor. Plasmids pKA1, pKA2, and pKA3, approximately 100 kb in size, were isolated from these strains and characterized. These plasmids have homologous regions of upper and lower NAH7 plasmid catabolic genes. By conjugation experiments, these plasmids, including NAH7, have been shown to encode the genotype for mineralization of [9-14C]phenanthrene and [U-14C]anthracene, as well as [1-14C]naphthalene. One strain, Pseudomonas fluorescens 5RL, which has the complete lower pathway inactivated by transposon insertion in nahG, accumulated a metabolite from phenanthrene and anthracene degradation. This is the first direct evidence to indicate that the NAH plasmid-encoded catabolic genes are involved in degradation of polynuclear aromatic hydrocarbons other than naphthalene.     

Comparative study of xylose(glucose) isomerase synthesis in Arthrobacter strains

The substrate specificity of isomerases produced by six strains of Arthrobacter sp. was studied. The role of utilizable carbon sources in controlling enzyme biosynthesis was established. All of the strains studied were found to produce xylose isomerases efficiently, converting D-xylose into D-xylulose and D-glucose into D-fructose. All but A. ureafaciens B-6 strains showed low activity toward D-ribose, Arthrobacter sp. B-5 was slightly active toward L-arabinose, and A. ureafaciens B-6 and Arthrobacter sp. B-2239, toward L-rhamnose. In Arthrobacter sp. B-5, the synthesis of xylose/glucose isomerase was constitutive (i.e., it was not suppressed by readily metabolizable carbon sources). The synthesis of xylose/glucose isomerase induced by D-xylose in Arthrobacter sp. strains B-2239, B-2240, B-2241, and B-2242 and by D-xylose and xylitol in A. ureafaciens B-6 was suppressed by readily metabolizable carbon sources in a concentration-dependent manner. The data obtained suggest that D-xylose and/or its metabolites are involved in the regulation of xylose/glucose isomerase synthesis in the Arthrobacter sp. strains B-5, B-2239, B-2240, and B-2241.     

Phenanthrene degradation by bacteria of the genera Pseudomonas and Burkholderia in model soil systems

Degradation of phenanthrene by strains Pseudomonas putida BS3701 (pBS1141, pBS1142), Pseudomonas putida BS3745 (pBS216), and Burkholderia sp. BS3702 (pBS1143) was studied in model soil systems. The differences in accumulation and uptake rate of phenanthrene intermediates between the strains under study have been shown, Accumulation of 1-hydroxy-2-naphthoic acid in soil in the course of phenanthrene degradation by strain BS3702 (pBS143) in a model system has been revealed. The efficiency of phenanthrene biodegradation was assessed using the mathematical model proposed previously for assessment of naphthalene degradation efficiency. The efficiency of degradation of both phenanthrene and the intermediate products of its degradation in phenanthrene-contaminated soil is expected to increase with the joint use of strains P. putida BS3701 (pBS1141, pBS1142) and Burkholderia sp. BS3702 (pBS1143).     

Saturable, energy-dependent uptake of phenanthrene in aqueous phase by Mycobacterium sp. strain RJGII-135

The mechanism of uptake of phenanthrene by Mycobacterium sp. strain RJGII-135, a polycyclic hydrocarbon-degrading bacterium, was examined with cultures grown on phenanthrene (induced for phenanthrene metabolism) and acetate (uninduced). Washed cells were suspended in aqueous solutions of [9-(14)C]phenanthrene, and then the cells were collected by filtration. Low-level steady-state (14)C concentrations in uninduced cells were achieved within the first 15 s of incubation. This immediate uptake did not show saturation kinetics and was not susceptible to inhibitors of active transport, cyanide and carbonyl cyanide m-chlorophenylhydrazone. These results indicated that phenanthrene enters rapidly into the cells by passive diffusion. However, induced cells showed cumulative uptake over several minutes. The initial uptake rates followed saturation kinetics, with an apparent affinity constant (K(t)) of 26 +/- 3 nM (mean +/- standard deviation). Uptake of phenanthrene by induced cells was strongly inhibited by the inhibitors. Analysis of cell-associated (14)C-labeled compounds revealed that the concurrent metabolism during uptake was rapid and was not saturated at the substrate concentrations tested, suggesting that the saturable uptake observed reflects membrane transport rather than intracellular metabolism. These results were consistent with the presence of a saturable, energy-dependent mechanism for transport of phenanthrene in induced cells. Moreover, the kinetic data for the cumulative uptake suggested that phenanthrene is specifically bound by induced cells, based on its saturation with an apparent dissociation constant (K(d)) of 41 +/- 21 nM (mean +/- standard deviation). Given the low values of K(t) and K(d), Mycobacterium sp. strain RJGII-135 may use a high-affinity transport system(s) to take up phenanthrene from the aqueous phase.     

Cometabolic oxidation of phenanthrene to phenanthrene trans-9,10-dihydrodiol by Mycobacterium strain S1 growing on anthracene in the presence of phenanthrene.

Mycobacterium strain S1, originally described as Rhodococcus strain S1 by chemotaxonomic criteria, was isolated by growth on anthracene, and is unable to use any of nine other polycyclic aromatic compounds as carbon source. Metabolism of phenanthrene during growth on anthracene as sole carbon source results in the accumulation of traces of a dihydrodiol metabolite in the growth medium, which, by comparison with authentic standards, has been tentatively identified as phenanthrene trans-9,10-dihydrodiol. Anthracene metabolites were ruled out on the basis of comparisons with authentic anthracene dihydrodiols from Pseudomonas fluorescens D1 and chemically synthesized anthrols. The original source of phenanthrene for dihydrodiol production was phenanthrene present as a < 1% contaminant in the anthracene used as carbon source. However, addition of further phenanthrene to the anthracene growth medium increased the level of phenanthrene trans-9,10-dihydrodiol formed. Mycobacterium strain S1 also produced phenanthrene trans-9,10-dihydrodiol when grown in a glucose-salts medium in the presence of phenanthrene. This dihydrodiol is a dead-end metabolite, and neither it nor its parent hydrocarbon are able to support the growth of Mycobacterium strain S1. Studies with metyrapone and ancimidol, which did not inhibit growth on anthracene but did inhibit formation of phenanthrene trans-9,10-dihydrodiol, suggest it is likely the product of a cytochrome P450 monooxygenase-like activity.     

Survival and Phospholipid Fatty Acid Profiles of Surface and Subsurface Bacteria in Natural Sediment Microcosms

Although starvation survival has been characterized for many bacteria, few subsurface bacteria have been tested, and few if any have been tested in natural subsurface porous media. We hypothesized that subsurface bacteria may be uniquely adapted for long-term survival in situ. We further hypothesized that subsurface conditions (sediment type and moisture content) would influence microbial survival. We compared starvation survival capabilities of surface and subsurface strains of Pseudomonas fluorescens and a novel Arthrobacter sp. in microcosms composed of natural sediments. Bacteria were incubated for up to 64 weeks under saturated and unsaturated conditions in sterilized microcosms containing either a silty sand paleosol (buried soil) or a sandy silt nonpaleosol sediment. Direct counts, plate counts, and cell sizes were measured. Membrane phospholipid fatty acid (PLFA) profiles were quantified to determine temporal patterns of PLFA stress signatures and differences in PLFAs among strains and treatments. The Arthrobacter strains survived better than the P. fluorescens strains; however, differences in survival between surface and subsurface strains of each genus were not significant. Bacteria survived better in the paleosol than in the nonpaleosol and survived better under saturated conditions than under unsaturated conditions. Cell volumes of all strains decreased; however, sediment type and moisture did not influence rates of miniaturization. Both P. fluorescens strains showed PLFA stress signatures typical for gram-negative bacteria: increased ratios of saturated to unsaturated fatty acids, increased ratios of trans- to cis-monoenoic fatty acids, and increased ratios of cyclopropyl to monoenoic precursor fatty acids. The Arthrobacter strains showed few changes in PLFAs. Environmental conditions strongly influenced PLFA profiles.     

Attachment of different soil bacteria to arbuscular mycorrhizal fungal extraradical hyphae is determined by hyphal vitality and fungal species

Attachment of certain bacteria to living arbuscular mycorrhizal fungal extraradical hyphae may be an important prerequisite for interactions between these microorganisms, with implications for nutrient supply and plant health. The attachment of five different strains of gfp-tagged soil bacteria (Paenibacillus brasilensis PB177 (pnf8), Bacillus cereus VA1 (pnf8), Pseudomonas fluorescens SBW25 :: gfp/lux, Arthrobacter chlorophenolicus A6G, and Paenibacillus peoriae BD62 (pnf8)) to vital and nonvital extraradical hyphae of the arbuscular mycorrhizal fungi Glomus sp. MUCL 43205 and Glomus intraradices MUCL 43194 was examined. Arthrobacter chlorophenolicus did not attach to hyphae, whereas the other bacterial strains did to a varying degree. Only P. brasilensis showed greater attachment to vital hyphae than nonvital hyphae of both Glomus species tested. Pseudomonas fluorescens showed a higher attachment to vital compared with nonvital Glomus sp. MUCL 43205 hyphae, whereas this relationship was opposite for attachment to G. intraradices. Both B. cereus and P. peoriae showed higher attachment to nonvital hyphae. This study provides novel evidence that under laboratory conditions soil bacteria differ in their ability to colonize vital and nonvital hyphae and that this can also be influenced by the arbuscular mycorrhizal fungal species involved. The significance of bacterial attachment to mycorrhizal fungal extraradical hyphae is discussed.     

Phenanthrene degradation by bacteria of the genera <Emphasis Type="Italic">Pseudomonas</Emphasis> and <Emphasis Type="Italic">Burkholderia</Emphasis> in model soil systems

Degradation of phenanthrene by strains Pseudomona, Moscow, KMK, 2004simova, I.A. and Chernov, I.s putida BS3701 (pBS1141, pBS1142), Pseudomonas putida BS3745 (pBS216), and Burkholderia sp. BS3702 (pBS1143) were studied in model soil systems. The differences in accumulation and uptake rate of phenanthrene intermediates between the strains under study have been shown. Accumulation of 1-hydroxy-2-naphthoic acid in soil in the course of phenanthrene degradation by strain BS3702 (pBS1143) in a model system has been revealed. The efficiency of phenanthrene biodegradation was assessed using the mathematical model proposed previously for assessment of naphthalene degradation efficiency. The efficiency of degradation of both phenanthrene and the intermediate products of its degradation in phenanthrene-contaminated soil is expected to increase with the joint use of strains P. Putida BS3701 (pBS1141, pBS1142) and Burkholderia sp. BS3702 (pBS1143).     

PAH Degradation and Bioaugmentation by a Marine Methanotrophic Enrichment

Methanotrophic bacteria were enriched from marine sediments and screened for their ability to biotransform polycyclic aromatic hydrocarbons (PAHs). Characterization of the methanotrophic enrichment showed that it was dominated by a Type I methanotroph, although significant amounts of 18:1 fatty acids were detected, suggesting the presence of Type II methanotrophs in marine systems. The methanotrophic enrichment degraded phenanthrene, anthracene, and fluorene to below detectable levels in 15 days. Partial transformation of fluoranthene occurred over 15 days, but pyrene was not transformed. Radiolabeled phenanthrene was oxidized to carbon dioxide with significant production of polar intermediates. The oxidation was inhibited by acetylene, an inhibitor of methane monooxygenase. The addition of the methanotrophic enrichment to a marine culture grown on PAHs as the sole carbon sources increased the transformation rate of phenanthrene, anthracene, and fluorene. The highest removal rates were obtained with a mixture containing 90% methanotroph enrichment and 10% PAH-degrading enrichment (by biomass). Fluoranthene and pyrene degradation rates by the PAH-degrading enrichment were not significantly increased by the addition of the methanotrophic enrichment. A possible mechanism for the increased transformation rate was the rapid oxidation of PAHs by methane monooxygenase, forming an intermediate that is more bioavailable for utilization by the PAH-degraders.     

一株转化淀粉或麦芽寡糖生成海藻糖的菌株D-97鉴定

由东北大田采集的土样中筛选到菌株D-97,该菌株胞内酶可以利用淀粉或麦芽寡糖合成海藻糖。通过生理、形态、结构特征分析及16SrDNA基因全序列与参比菌株的序列比较,菌株D-97与食尼古丁节杆菌的16SrDNA序列同源性高达97．98％,故将该菌株命名为食尼古丁节杆菌D-97（Arthrobacter nicotinovorus D-97)。我们还将D-97菌株与日本林原公司的海藻糖生产苗——节杆菌Q36的有关生理生化特征进行了比较。     

Efficient polycyclic aromatic hydrocarbons dihydroxylation in direct micellar systems

Optimization of whole-cell bioconversion of the polycyclic aromatic hydrocarbons (PAHs) anthracene, phenanthrene, and naphthalene to the enantiomerically pure corresponding cis-dihydroxydihydro derivatives by the Escherichia coli JM109 (pPS1778) recombinant strain, carrying the naphthalene dioxygenase and corresponding regulatory genes cloned from Pseudomonas fluorescens N3, in micellar systems, is presented. We show that direct microemulsion systems, where a nonionic surfactant such as 1.5% (v/v) Triton X-100 plus 0.6% to 1.0% (v/v) selected oils are able to solubilize the PAHs tested at relatively high concentrations (initial concentrations in the reaction medium > or =10 mM for naphthalene and phenanthrene and > or =2 mM for anthracene), and allow for more efficient substrate bioconversion. These media, while not affecting bacteria viability and performance, provide increased efficiency and final product yields (100% for naphthalene, >30% for anthracene, >60% for phenanthrene). The phase behavior of the direct microemulsion systems for the different substrates and oils utilized was monitored as a function of their volume fraction by light scattering experiments, and related to the bioconversion results. For anthracene and phenanthrene, the dihydroxylated products have an inhibitory effect on the conversion reactions, thus hindering complete turnover of the substrates. We ascertain that such inhibition is reversible because removal of the products formed allowed the process to start over at rates comparable to initial rates. To allow for complete conversion of the PAHs tested a stepwise or continuous separation of the product formed from the micellar reaction environment is being developed.     

NAH plasmid-mediated catabolism of anthracene and phenanthrene to naphthoic acids.

Pseudomonas fluorescens 5R contains an NAH7-like plasmid (pKA1), and P. fluorescens 5R mutant 5RL contains a bioluminescent reporter plasmid (pUTK21) which was constructed by transposon mutagenesis. Polymerase chain reaction mapping confirmed the localization of lux transposon Tn4431 300 bp downstream from the start of the nahG gene. Two degradation products, 2-hydroxy-3-naphthoic acid and 1-hydroxy-2-naphthoic acid, were recovered and identified from P. fluorescens 5RL as biochemical metabolites from the biotransformation of anthracene and phenanthrene, respectively. This is the first report which provides direct biochemical evidence that the naphthalene plasmid degradative enzyme system is involved in the degradation of higher-molecular-weight polycyclic aromatic hydrocarbons other than naphthalene.     

Characterization of selected actinomycetes degrading polyaromatic hydrocarbons in liquid culture and spiked soil

Summary Five strains of the Rhodococcus and Gordonia genera were evaluated for their potential use in bioremediation of polycyclic aromatic hydrocarbons (PAH) with or without another substrate (co-substrate). Their ability to produce biosurfactants or to degrade phenanthrene when growing on glucose, hexadecane and rapeseed oil was tested in liquid medium at 30 °C. All strains showed biosurfactant activity. The highest reduction in surface tension was recorded in whole cultures of Rhodococcus sp. DSM 44126 (23.1%) and R. erythropolis DSM 1069 (21.1%) grown on hexadecane and Gordonia sp. APB (20.4%) and R. erythropolis TA57 (18.2%) grown on rapeseed oil. Cultures of Gordonia sp. APB and G. rubripertincta formed emulsions when grown on rapeseed oil. After 14 days of incubation, Rhodococcus sp. DSM 44126 degraded phenanthrene (initial concentration 100 μg ml⁻¹) as sole carbon source (79.4%) and in the presence of hexadecane (80.6%), rapeseed oil (96.8%) and glucose (below the limit of detection). The other strains degraded less than 20%, and then with a co-substrate only. Rhodococcus sp. DSM 44126 was selected and its performance evaluated in soil spiked with a mixture of PAH (200 mg kg⁻¹). The effect of the addition of 0, 0.1 and 1% rapeseed oil as co-substrate was also tested. Inoculation enhanced the degradation of phenanthrene (55.7% and 95.2% with 0.1% oil and without oil respectively) and of anthracene (29.2% with 0.1% oil). Approximately 96% of anthracene and 62% of benzo(a)pyrene disappeared from the soil (inoculated and control) after 14 days and anthraquinone was detected as a metabolite. Rhodococcus sp. DSM 44126 was identified as Rhodococcus wratislaviensis by 16S rRNA sequencing and was able to degrade anthracene as sole carbon source in liquid culture.     

Degradation of polycyclic aromatic hydrocarbons by a strain of Pseudomonas fluorescens 16N2

The growth of Pseudomonas fluorescens 16N2 on naphthalene was accompanied with accumulation of salicylate in the culture medium and induction of gentisate 1,2-dioxygenase and catechol 1,2-dioxygenase. The transformation of anthracene by the cells growing on hexadecane led to the formation of 3-hydroxy-2-naphthoate and salicylate. Pathways for naphthalene and anthracene degradation are proposed.     

The strategy of strain selection for a mixed culture performing rapid conversion of a mixture of polyaromatic compounds

The strain Sphingomonas sp. VKM V-2434 converts the mixture of seven polyaromatic compounds (PACs): fluorene, dibenzothiophene, carbazole, phenanthrene, anthracene, fluoranthene, and pyrene. The effect of each of the above PACs on the rate of mixture conversion was determined. The following two strains, which utilize the substances inhibiting the studied process, were added to the culture: strain FON-11 utilizing 9-fluorenone (fluorene metabolite) and strain CBZ-21 utilizing carbazole. In the case of the mixed culture of three strains, conversion rates were 1.5 and 1.2–3.8 times higher for the PAC mixture and its individual components, respectively, than the rates for Sphingomonas sp. VKM V-2434 monoculture. The degree of degradation of PAC conversion products increased from 32 to 44%. The rate of PAC conversion by the mixed culture exceeded the sum of conversion rates for the individual component strains; this cooperative effect was particularly marked for anthracene and pyrene.     

牧效黄杆菌对蒽菲芘的降解性能研究

采用定时、定量、逐步提高驯化所用碳源物浓度的方法,以萘为唯一碳源驯化长期被焦化废水污染的泥土浸出液,7周后,平板划线分离出两株黄杆菌FCN1及FCN2。并对这两株菌降解多环芳烃的特性及无机离子对反应的刺激作用进行了研究。结果表明,FCN1及FCN2能降解转化蒽、菲、芘。加入FCN1,反应10h后,蒽、菲、芘去除率分别为84％、69％、80％,而加入FCN2,各物质的去除率分别为76％、40％、71％。反应进行106h,FCN1对蒽、菲、芘所产生的总有机碳（TOC）的去除率分别为70％、54％、69％,而FCN2对相应物的TOC去除率分别为63％、50％、46％。Fe^3 、Mg^2 的加入对FCN1降解多环芳烃有促进作用。     

Isolation and characterization of catechol 1,2-dioxygenases from Rhodococcus rhodnii strain 135 and Rhodococcus rhodochrous strain 89: comparison with analogous enzymes of the ordinary and modified ortho-cleavage pathways.

Catechol 1,2-dioxygenases of the ordinary ortho-cleavage pathway have been isolated from strains Rhodococcus rhodnii 135 and Rhodococcus rhodochrous 89 grown on phenol as the sole source of carbon and energy. The activities of the catechol 1,2-dioxygenases with 3- and 4-methylpyrocatechols were 1.3-1.5 times higher than those with pyrocatechol. The rate of oxidation of 3-chloropyrocatechol catalyzed by both enzymes was 20% of the rate of oxidation of unsubstituted pyrocatechol. The enzymes are homodimers composed of 37-kD subunits.