Fungal/bacterial interactions during the biodegradation of TEX hydrocarbons (toluene, ethylbenzene and p-xylene) in gas biofilters operated under xerophilic conditions

The treatment of air contaminated with toluene, ethylbenzene, and p-xylene was assayed in three laboratory-scale biofilters, each consisting of two modules connected in series, packed with a pelletized organic fertilizer and inoculated with a toluene-degrading liquid enrichment culture. Biofilters were operated in parallel for 185?days in which the volumetric organic loading rate was progressively increased. The operation regime was subjected to drying out, so that packing humidity generally remained below 40%. Significant process failure occurred with ethylbenzene and p-xylene, but the toluene biofilter comparatively sustained a significant elimination capacity. Microbial community characterization by quantitative PCR and denaturing gradient gel electrophoresis showed substantial fungal enrichment in the toluene biofilter. Ribotypes identical to the well-known toluene-degrading black yeast Exophiala oligosperma (Chaetotyriales) were found among the dominant species. The microbial community structure was similar in the biofilters loaded with toluene and ethylbenzene but with p-xylene was quite specific and encompassed other chaetothyrialean fungi. Several species of Actinomycetales were found in the packing while the inoculum was dominated by representatives of the Burkholderiales and Xanthomonadales. One single fungal ribotype homologous to Acremonium kiliense was detected in the inoculum. The implications of xerophilic biofilter operation on process biosafety and efficiency are discussed.     

Two New Mycobacterium Strains and Their Role in Toluene Degradation in a Contaminated Stream

Two toluene-degrading strains, T103 and T104, were isolated from rock surface biomass in a freshwater stream contaminated with toluene. The strains exhibit different capacities for degradation of toluene and other aromatic compounds and have characteristics of the genus Mycobacterium. Both are aerobic, rod-shaped, gram-positive, nonmotile, and acid-alcohol fast and produce yellow pigments. They have mainly straight-chain saturated and monounsaturated fatty acids with 10 to 20 carbon atoms and large amounts of tuberculostearic acid that are typical of mycobacteria. Fatty acid analyses indicate that T103 and T104 are different mycobacterial strains that are related at the subspecies level. Their identical 16S rDNA sequences are most similar to Mycobacterium aurum and Mycobacterium komossense, and they constitute a new species of fast-growing mycobacteria. Ecological studies reveal that toluene contamination has enriched for toluene-degrading bacteria in the epilithic microbial community. Strains T103 and T104 play only a small role in toluene degradation in the stream, although they are present in the habitat and can degrade toluene. Other microorganisms are consequently implicated in the biodegradation.     

Fungal biocatalysts in the biofiltration of VOC-polluted air

Gas-phase biofilters used for the treatment of waste gases were originally packed with compost or other natural filter beds containing indigenous microorganisms. Over the past decade much effort has been made to develop new carrier materials, more performant biocatalysts and new types of bioreactors. Elimination capacities reached nowadays are 5 to 10 times higher than those originally reported with conventional compost biofilters. With the recently developed inert filter beds, inoculation is a prerequisite for successful start-up and operation. Either non-defined mixed cultures or pure bacterial cultures have originally been used. The search for efficient fungal biocatalysts started only a few years ago, mainly for the biofiltration of waste gases containing hydrophobic compounds, such as styrene, alpha-pinene, benzene, or alkylbenzenes. In this review, recently isolated new fungal strains able to degrade alkylbenzenes and other related volatile organic pollutants are described, as well as their major characteristics and their use as biocatalysts in gas-phase biofilters for air pollution control. In biofiltration, the most extensively studied organism belongs to the genus Exophiala, although strains of Scedosporium, Paecilomyces, Cladosporium, Cladophialophora, and white-rot fungi are all potential candidates for use in biofilters. Encouraging results were obtained in most of the cases in which some of those organisms were present in gas-phase biofilters. They allow reaching high elimination capacities and are resistant to low pH values and to reduce moisture content.     

Microbial response and elimination capacity in biofilters subjected to high toluene loadings

Elimination capacity (EC) is frequently used as a performance and design criterion for vapor-phase biofilters without further verification of the microbial quantity and activity. This study was conducted to investigate how biofilters respond to high pollutant loadings and ultimately how this affects the EC of the biofilter. Two identical laboratory-scale biofilters were maintained at an initial toluene loading rate of 46 g m⁻³ h⁻¹ for a period of 24 days. After the initial biofilm development stage, the loading rates were increased to 91 g m⁻³ h⁻¹ and 137 g m⁻³ h⁻¹, respectively. Following a short period of pseudo-steady state, toluene removal efficiencies rapidly declined in both biofilters, with a concurrent decline in both critical and maximum ECs. The decline was mainly due to deterioration in the biodegradation activity of the biofilm and a decline in the toluene-degrading bacterial population within the biofilm phase. The findings imply that high toluene loadings accelerated the deterioration in overall performance due to a rapid accumulation of inactive biomass. As a result, care must be used when relying on EC values for biofilter design and operational purposes, since the values do not appropriately reflect the temporal changes in biodegradation activity and active biomass quantities that can occur in biofilters subjected to high inlet loadings.     

Investigations into the growth behaviour of a toluene-degrading Pseudomonas strain,taking the high vapour pressure of toluene into consideration

A toluene-degrading Pseudomonas species isolated from waste water was studied with regard to its growth behaviour. The dependence of the growth rate on the pH value, on the toluene concentration and on temperature, as well as the O₂ consumption of the isolate were determined. The fact that toluene is a highly volatile substrate, which is present both in the liquid and in the has phase of a reactor, was considered in the experiments. It is shown that the volatility of toluene has to be taken into consideration for an accurate determination of the toluene concentration in the medium.     

Phenol- and Toluene-Degrading Microbial Populations from an Aquifer in Which Successful Trichloroethene Cometabolism Occurred

We characterized the bacterial populations that grew in a Moffett Field, Calif., aquifer following three sequential field tests of phenol- or toluene-driven cometabolism of trichloroethene (TCE). Reducing the toluene and phenol concentrations in most-probable-number (MPN) tubes from 50 to 5 ppm increased the population density measured for these degraders by 1.5 and 1 log units, respectively, suggesting that natural populations might be quite sensitive to these substrates. Phenol and toluene degraders were isolated from the terminal MPN dilution tubes; 63 genetically distinct strains were identified among the 273 phenol- and toluene-degrading isolates obtained. TCE was cometabolized by 60% of the genetically distinct strains. Most strains (57%) grew on both phenol and toluene, and 78% of these strains hybridized to the toluene ortho-monooxygenase (TOM) probe. None of the strains hybridized to probes from the four other toluene oxygenase pathways. Gram-positive strains comprised 30% of the collection; all of these grew on phenol, and 47% of them also grew on toluene, but none hybridized to the TOM probe. Among the gram-negative strains, 86% of those that grew on both toluene and phenol hybridized to the TOM probe, while only 5% of those that were TOM-positive grew on toluene alone. A larger proportion of TCE degraders was found among gram-negative than gram-positive strains and among organisms that grew on phenol than those that grew on toluene. Hybridization of strains to the TOM probe was somewhat predictive of their TCE-cometabolizing ability, especially for strains isolated on toluene, but there was also a significant number (20%) of strains that hybridized to the TOM probe but were poor TCE cooxidizers. No Moffett Field isolates were as effective as Burkholderia cepacia G4 in cooxidizing TCE. Most of the aquifer strains ranged from moderately effective to ineffective in TCE cooxidation. Such populations, however, apparently accounted for the successful phenol- and toluene-stimulated TCE removal that occurred during the field assessment of this remediation process. This suggests that naturally occurring communities of only moderate TCE-cooxidizing ability may support successful TCE bioremediation as long as the phenol or toluene present is not limiting. This activity, however, may not be sustainable for the long term, because TCE-inactive populations that consumed toluene at rates equal to that of the best TCE degraders were present and hence would be expected to eventually dominate the community.     

Dynamic responses of biofilters to changes in the operating conditions in the process of removing toluene and xylene from air

The dynamic behaviour of biofilters intended to remove toluene and xylene from air was studied during transient states. Laboratory scale biofilters were filled with a mixture of peat, bark and wood and inoculated with a mixed microbial population. Toluene and xylene were applied both as single pollutants and as mixtures. Attention was focused on the evaluation of the following transients: the response of biofilters to step changes and peaks in pollutant concentrations, the effect of changes between single and multiple pollutant loadings and the response to shutdown periods. The biofilters demonstrated a good dynamic stability during transient states induced by change in inlet pollutant concentrations. Their time periods did not exceed three hours. No interaction between xylene and toluene degradation was observed during changes in loading with single pollutants or their mixture. The performance interruptions lasting less than 24 hours were found to have no significant influence on the removal efficiency of biofilters. When the biofilters were reacclimated after longer starvation periods, a short temporary decrease in efficiency whose minimum and duration were proportional to the length of a preceding shutdown period was observed. The longest starvation period (7 days) resulted in a reacclimation lasting 7 hours only. Adaptations of a microbial population to new operating conditions as well as sorption/desorption processes were suggested as the main factors influencing the dynamic reponse characteristics.     

A model study based on experiments on toluene removal under high load condition in biofilters

As a control measure for substrate inhibition phenomenon in biofilters caused by toxic gases with high concentration, an appropriate mathematical model is required to calculate gas concentrations at various positions within and outside biofilms. Thus validation of the Deshussess model, Devinny–Hodge model and Luong Model were carried out for high toluene load conditions, and the results were examined for their veracity. Calculated concentrations using the modified Deshussess model, which considers sorption volume of carriers, approximated to measurements. This appears to mean the contribution of porosity in inorganic ceramic carriers to the biological removal of toluene vapor. Since toluene removal capacities for high liquid concentrations, which were calculated using the Luong model, approximated to the measurements, the generality and usefulness of the Luong model in predicting the substrate elimination capacity in biofilters with substrate inhibition appear to be manifested. Simplified Devinny–Hodge model turned out to be not applicable to predicting gas concentration along longitudinal axis of biofilters with high gas load. Various model parameters, needed for modeling studies, including critical toluene load per unit biomass and time, maximum toluene degradation rate, half velocity toluene concentration, and maximum toluene concentration in liquid, above which biodegradation is inhibited, were experimentally determined.     

Biofiltration of waste gases containing both ethyl acetate and toluene using different combinations of bacterial cultures

To investigate the microbial degradation of ethyl acetate and toluene mixtures in biofiltration, three strains were selected, identified and studied in a shake-flask culture, and finally inoculated into biofilters. These strains, namely AC6, TO3 and B5, can degrade different substrates at a different rate. The results showed that competitive inhibition from substrate and microbial community would affect the toluene degradation efficiency. Owing to substrate competition, the toluene degradation efficiency of strain B5 would decrease in the presence of high concentration of ethyl acetate. However, the addition of strain AC6 would alleviate such inhibition because it could remove ethyl acetate rapidly. Microbial community competition from strain AC6 or B5 would impede the toluene degradation efficiency of strain TO3 unless a large amount of strain TO3 was inoculated. In biofiltration, strain B5 would be a better choice for inoculation into biofilters than strains AC6 and TO3, as it would grow rapidly under a low concentration of ethyl acetate.     

Complete oxidation of toluene under strictly anoxic conditions by a new sulfate-reducing bacterium.

A toluene-degrading sulfate-reducing bacterium, strain Tol2, was isolated from marine sediment under strictly anoxic conditions. Toluene was toxic if applied directly to the medium at concentrations higher than 0.5 mM. To provide toluene continuously at a nontoxic concentration, it was supplied in an inert hydrophobic carrier phase. The isolate had oval, sometimes motile cells (1.2 to 1.4 by 1.2 to 2.0 microns). The doubling time was 27 h. Toluene was completely oxidized to CO2, as demonstrated by measurement of the degradation balance. The presence of carbon monoxide dehydrogenase and formate dehydrogenase indicated a terminal oxidation of acetyl coenzyme A via the CO dehydrogenase pathway. The use of hypothetical intermediates of toluene degradation was tested in growth experiments and adaptation studies with dense cell suspensions. Results do not support a degradation of toluene via one of the cresols or methylbenzoates, benzyl alcohol, or phenylacetate as free intermediate. Benzyl alcohol did not serve as growth substrate; moreover, it was a strong, specific inhibitor of toluene degradation, whereas benzoate utilization was not affected by benzyl alcohol. Sequencing of 16S rRNA revealed a relationship to the metabolically dissimilar genus Desulfobacter and on a deeper level to the genus Desulfobacterium. The new genus and species Desulfobacula toluolica is proposed.     

Identification of a toluene-degrading bacterium from a soil sample through H(2)(18)O DNA stable isotope probing

DNA stable isotope probing (DNA-SIP) with H(2)(18)O was used to identify a toluene-degrading bacterium in soil amended with 48 ppm toluene. After quantification of toluene degradation rates in soil, DNA was extracted from soil incubated with H(2)(18)O, H(2)(16)O, H(2)(16)O and 48 ppm toluene, or H(2)(18)O and 48 ppm toluene. A single DNA band formed along a cesium chloride gradient after isopycnic centrifugation of extracts from soils incubated with H(2)(16)O. With extracts from soils to which only H(2)(18)O was added, two distinct DNA bands formed, while three bands formed when DNA extracted from soil incubated with both H(2)(18)O and toluene was analyzed. We suggest that this third band formed because toluene does not contain any oxygen atoms and toluene-degrading organisms had to transfer oxygen atoms from H(2)(18)O into metabolic intermediates to form nucleic acids de novo. We extracted the third DNA band and amplified a large fraction of the bacterial 16S rRNA gene. Direct sequencing of the PCR product obtained from the labeled DNA, as well as cloned 16S rRNA amplicons, identified a known toluene degrader, Rhodococcus jostii RHA1. A toluene-degrading bacterial strain was subsequently isolated from soil and shown to be Rhodococcus jostii RHA1. Finally, quantitative real-time PCR analysis showed that the abundance of the 16S rRNA gene of Rhodococcus jostii RHA1 increased in soil after toluene exposure but not in soils from which toluene was withheld. This study indicates that H(2)(18)O DNA-SIP can be a useful method for identifying pollutant-degrading bacteria in soil.     

Evidence for acetyl coenzyme A and cinnamoyl coenzyme A in the anaerobic toluene mineralization pathway in Azoarcus tolulyticus Tol-4.

A toluene-degrading denitrifier, Azoarcus tolulyticus Tol-4, was one of eight similar strains isolated from three petroleum-contaminated aquifer sediments. When the strain was grown anaerobically on toluene, 68% of the carbon from toluene was found as CO2 and 30% was found as biomass. Strain Tol-4 had a doubling time of 4.3 h, a Vmax of 50 micromol x min-1 x g of protein-1, and a cellular yield of 49.6 g x mol of toluene-1. Benzoate appeared to be an intermediate, since F-benzoates accumulated from F-toluenes and [14C]benzoate was produced from [14C]toluene in the presence of excess benzoate. Two metabolites, E-phenylitaconic acid (1 to 2%) and benzylsuccinic acid (<1%), accumulated from anaerobic toluene metabolism. These same products were also produced when cells were grown on hydrocinnamic acid and trans-cinnamic acid but were not produced from benzylalcohol, benzaldehyde, benzoate, p-cresol, or their hydroxylated analogs. The evidence supports an anaerobic toluene degradation pathway involving an initial acetyl coenzyme A (acetyl-CoA) attack in strain Tol-4, as proposed by Evans and coworkers (P. J. Evans, W. Ling, B. Goldschmidt, E. R. Ritter, and L. Y. Young, Appl. Environ. Microbiol. 58:496-501, 1992) for another toluene-degrading denitrifier, strain T1. Our findings support a modification of the proposed pathway in which cinnamoyl-CoA follows the oxidation of hydrocinnamoyl-CoA, analogous to the presumed oxidation of benzylsuccinic acid to form E-phenylitaconic acid. Cinnamic acid was detected in Tol-4 cultures growing in the presence of toluene and [14C]acetate. We further propose a second acetyl-CoA addition to cinnamoyl-CoA as the source of benzylsuccinic acid and E-phenylitaconic acid. This pathway is supported by the finding that monofluoroacetate added to toluene-growing cultures resulted in a significant increase in production of benzylsuccinic acid and E-phenylitaconic acid and by the finding that [14C]benzylsuccinic acid was detected after incubation of cells with toluene, [14C]acetate, and cinnamic acid. Evidence for anaerobic toluene metabolism by methyl group oxidation was not found, since benzylsuccinic acid and E-phenylitaconic acid were not detected after incubation with benzylalcohol and benzaldehyde, nor were benzylalcohol and benzaldehyde detected even in 14C trapping experiments.     

Active compost biofiltration of toluene

Composting of leaves and alfalfa (i.e. active compost) was used for thebiofiltration of toluene-contaminated air in a 6-L biofilter (initial bedheight: 180 mm). During the thermophilic phase (45 to 55 °C), toluenebiodegradation rates reached 110 gtoluene.m^-3.h^-1 at an inlet concentration ofabout 5 g.m^-3.h^-1 and a gas residence time of 90 seconds. Thehighest rates were obtained late in the thermophilic phase suggesting amicrobial adaptation was occurring. Biodegradation rates decreased rapidly(50% in 48h) in the cooling stage. Under mesophilic conditions, themaximum biodegradation rates that could be obtained by increasing the inlettoluene concentration were near 89 gtoluene.m^-3.h^-1 which issimilar to that reported in the literature for mature compost biofilters. Novolatile by-product was detected by gas chromatography. Mineralization of¹⁴C-toluene and benzene showed that they were completelydegraded into CO₂ and H₂O under boththermophilic and mesophilic conditions. Bacteria isolated from latemesophilic stage had the capacity to degrade all BTEX compounds but were notable to transform chlorinated compounds. No organisms were isolated whichcould use toluene as their sole source of carbon and energy at 50 °C.Active compost biofiltration should be an excellent process for thetreatment of gaseous BTEX by biofiltration. This is the first report ofthermophilic biofiltration of toluene.     

Biomass control in waste air biotrickling filters by protozoan predation

Two protozoan species as well as an uncharacterized protozoan consortium were added to a toluene-degrading biotrickling filter to investigate protozoan predation as a means of biomass control. Wet biomass formation in 23.6-L reactors over a 77-day period was reduced from 13.875 kg in a control biotrickling filter to 11.795 kg in a biotrickling filter enriched with protozoa. The average toluene vapor elimination capacity at 1 g/m3 toluene and 64 m3/(m3. h) was 31.1 g/(m3. h) in the control and 32.2 g/(m3. h) in the biotrickling filter enriched with protozoa. At higher toluene inlet concentrations, toluene degradation rates increased and were slightly higher in the biotrickling filter enriched with protozoa. The lower rate of biomass accumulation after the addition of protozoa was due to an increase of carbon mineralization (68% as compared to 61% in the control). Apparent biomass yield coefficients in the control and enriched trickling filter were 0.72 and 0.59 g dry biomass/g toluene, respectively. The results show that protozoan predation may be a useful tool to control biomass in biotrickling filters, however, further stimulation of predation of the biomass immobilized in the reactor is required to ensure long-term stability of biotrickling filters.     

Succession and convergence of biofilm communities in fixed-film reactors treating aromatic hydrocarbons in groundwater.

Community composition, succession, and performance were compared in three fluidized bed reactors (FBR) operated to test preemptive colonization and the influence of toluene compared with a mixture of benzene, toluene, and p-xylene (BTX) as feeds. One reactor was inoculated with toluene-degrading strains Pseudomonas putida PaW1, Burkholderia cepacia G4, and B. pickettii PKO1. PaW1 outcompeted the other two strains. When groundwater strains were allowed to challenge the steady-state biofilm developed by inoculated strains, they readily displaced the inoculated strains and further reduced the toluene effluent concentration from 0.140 to 0.063 mg/liter for 98% removal. Amplified ribosomal DNA restriction analysis (ARDRA) of reactor community DNA showed a succession of populations to a pattern that was stable for at least 4 months of operation. Parallel reactors fed toluene and BTX but inoculated directly from groundwater had the same treatment performance and the same ARDRA profiles as each other and as the seeded reactor once the groundwater community took over. Convergence and stability of populations were confirmed by genotype analysis of 120 isolates taken from all reactors and at several times. Ninety percent of the isolates were of 4 of the 12 genotypes found, and their ARDRA patterns accounted for most of the community ARDRA patterns. Estimates of the maximum specific growth rates (mu max), half-saturation constants (K(m)), and maximum substrate utilization rates (Vmax) of the 12 genotypes isolated revealed a rather high diversity of toluene use kinetics even though the toluene in the feed was constant. The climax populations, however, generally showed kinetic parameters indicative of greater competitiveness than the inocula. rRNA sequence analysis of three codominant strains showed them to be members of the alpha, beta, and gamma subdivisions of the Proteobacteria. Two were similar to Comamonas and Pseudomonas putida, but the member of the alpha group was somewhat distant from any organism in the rRNA database. The convergence of communities to the same composition from three different starting conditions and their constancy over several months suggests that a rather stable community was selected.     

Comparative genomic analysis of solvent extrusion pumps in<Emphasis Type="Italic"> Pseudomonas</Emphasis> strains exhibiting different degrees of solvent tolerance

Organic solvents are inherently toxic for microorganisms. Their effects depend not only on the nature of the compound, but also on the intrinsic tolerance of the bacterial species and strains. Three efflux pumps belonging to the RND (resistance-nodulation-cell division) family of multidrug extrusion pumps are the main factor involved in the high intrinsic tolerance to toluene of Pseudomonas putida DOT-T1E. We have analyzed the tolerance to toluene shocks [0.1% and 0.3% (v/v)] of a number of strains belonging to different species of the genus Pseudomonas upon growth in the absence and in the presence of sublethal concentrations of toluene. The strains can be grouped in three categories: (1) highly resistant strains, in which almost 100% of the cells precultured in the presence of sublethal concentrations of toluene withstood a 0.3% (v/v) toluene shock, (2) moderately resistant strains, in which only a fraction (10(-4)-1) of the cells withstood a 0.1% (v/v) toluene shock, but fewer than 1 in 10(7) cells survived a sudden 0.3% (v/v) toluene shock regardless of the growth conditions, and (3) sensitive strains, in which regardless of the growth conditions fewer than 10(-5) cells survived a 0.1% (v/v) toluene shock. We also studied the number and type of efflux pumps in different strains in comparison with the P. putida DOT-T1E strain.     

Microbial characterization of toluene-degrading denitrifying consortia obtained from terrestrial and marine ecosystems

The degradation characteristics of toluene coupled to nitrate reduction were investigated in enrichment culture and the microbial communities of toluene-degrading denitrifying consortia were characterized by denaturing gradient gel electrophoresis (DGGE) technique. Anaerobic nitrate-reducing bacteria were enriched from oil-contaminated soil samples collected from terrestrial (rice field) and marine (tidal flat) ecosystems. Enriched consortia degraded toluene in the presence of nitrate as a terminal electron acceptor. The degradation rate of toluene was affected by the initial substrate concentration and co-existence of other hydrocarbons. The types of toluene-degrading denitrifying consortia depended on the type of ecosystem. The clone RS-7 obtained from the enriched consortium of the rice field was most closely related to a toluene-degrading and denitrifying bacterium, Azoarcus denitrificians (A. tolulyticus sp. nov.). The clone TS-11 detected in the tidal flat enriched consortium was affiliated to Thauera sp. strain S2 (T. aminoaromatica sp. nov.) that was able to degrade toluene under denitrifying conditions. This indicates that environmental factors greatly influence microbial communities obtained from terrestrial (rice field) and marine (tidal flat) ecosystems.     

Activity-dependent fluorescent labeling of bacterial cells expressing the TOL pathway

3-Ethynylbenzoate (3EB) functions as a novel, activity-dependent, fluorogenic, and chromogenic probe for bacterial strains expressing the TOL pathway, which degrade toluene via conversion to benzoate, followed by meta ring fission of the intermediate catechol. This direct physiological analysis allows the fluorescent labeling of cells whose toluene-degrading enzymes have been induced by an aromatic substrate.     

Activity of Toluene-degrading Pseudomonas putida in the early growth phase of a biofilm for waste gas treatment

A biological trickling filter for treatment of toluene-containing waste gas was studied. The overall kinetics of the biofilm growth was followed in the early growth phase. A rapid initial colonization took place during the first three days. The biofilm thickness increased exponentially, whereas the incease of active biomass and polymers was linear. In order to investigate the toluene degradation, various toluene degraders from the multispecies biofilm were isolated, and a Pseudomonas putida was chosen as a representative of the toluene-degrading population. A specific rRNA oligonucleotide probe was used to follow the toluene-degrading P. putida in the multispecies biofilm in the filter by means of number and cellular rRNA content. P. putida appeared to detach from the biofilm during the first three days of growth, after which P. putida was found at a constant level of 10% of the active biomass in the biofilm. Based on the rRNA content, the in situ activity was estimated to be reduced to 20% of cells grown at maximum conditions in batch culture. The toluene degraded by P. putida was estimated to be a minor part (11%) of the overall toluene degradation. (c) 1997 John Wiley & Sons, Inc. Biotechnol Bioeng 54: 131-141, 1997.