Aerobic biodegradation of vinyl chloride in groundwater samples

Studies were conducted to examine the biodegradation of 14C-labeled vinyl chloride in samples taken from a shallow aquifer. Under aerobic conditions, vinyl chloride was readily degraded, with greater than 99% of the labeled material being degraded after 108 days and approximately 65% being mineralized to 14CO2.     

Involvement of coenzyme M during aerobic biodegradation of vinyl chloride and ethene by Pseudomonas putida strain AJ and Ochrobactrum sp. strain TD

The involvement of coenzyme M in aerobic biodegradation of vinyl chloride and ethene in Pseudomonas putida strain AJ and Ochrobactrum sp. strain TD was demonstrated using PCR, hybridization, and enzyme assays. The results of this study extend the range of eubacteria known to use epoxyalkane:coenzyme M transferase.     

Aerobic biodegradation of vinyl chloride in groundwater samples.

Studies were conducted to examine the biodegradation of 14C-labeled vinyl chloride in samples taken from a shallow aquifer. Under aerobic conditions, vinyl chloride was readily degraded, with greater than 99% of the labeled material being degraded after 108 days and approximately 65% being mineralized to 14CO2.     

Aerobic biodegradation of vinyl chloride by a highly enriched mixed culture

Lower chlorinated compounds such as cis-dichloroethene (cis-DCE) and vinyl chloride (VC) often accumulate in chloroethene-contaminated aquifers due to incomplete reductive dechlorination of higher chlorinated compounds. A highly enriched aerobic culture that degrades VC as a growth substrate was obtained from a chloroethene-contaminated aquifer material. The culture rapidly degraded 50-250 microM aqueous VC to below GC detection limit with a first-order rate constant of 0.2 day(-1). Besides VC, the culture also degraded ethene as the sole carbon source. In addition, the culture degraded cis-DCE, but only in the presence of VC. However, no degradation of trans-DCE or TCE occurred either in the presence or absence of VC. The ability of the TRW culture to degrade cis-DCE is significant for natural attenuation since both VC and cis-DCE are often found in chloroethene-contaminated groundwater. Experiments examining the effect of oxygen threshold on VC degradation showed that the culture was able to metabolize VC efficiently at extremely low concentrations of dissolved oxygen (DO). Complete removal of 150 micromoles of VC occurred in the presence of only 0.2 mmol of oxygen (1.8 mg/L DO). This is important since most groundwater environments contain low DO (1-2 mg/L). Studies showed that the culture was able to withstand long periods of VC starvation. For example, the culture was able to assimilate VC with minimal lag time even after 5 months of starvation. This is impressive from the point of its sustenance under field conditions. Overall the culture is robust and degrades VC to below the detection limit rendering this culture suitable for field application.     

Isolation of an aerobic vinyl chloride oxidizer from anaerobic groundwater

Vinyl chloride (VC) is a known human carcinogen and common groundwater contaminant. Reductive dechlorination of VC to non-toxic ethene under anaerobic conditions has been demonstrated at numerous hazardous waste sites. However, VC disappearance without stoichiometric production of ethene has also been observed at some sites and in microcosms. In this study we identify an organism responsible for this observation in presumably anaerobic microcosms and conclude that oxygen was not detectable based on a lack of color change from added resazurin. This organism, a Mycobacterium sp. closely related to known VC oxidizing strains, was present in high numbers in 16S rRNA gene clone libraries from a groundwater microcosm. Although the oxidation/reduction indicator resazurin remained in the clear reduced state in these studies, these results suggest inadvertent oxygen contamination occurred. This study helps to elucidate the dynamic behavior of chlorinated ethenes in contaminated groundwater, through the isolation of a strictly aerobic organism that may be responsible for at least some disappearance of VC without the concomitant production of ethene in groundwater considered anaerobic.     

Thermosensitivity of naphthalene biodegradation plasmids

The object of the work was to study the functional expression of naphthalene and salicylic acid catabolism systems and the stability of naphthalene biodegradation plasmids NAH, pBS2, pBS3 and NPL-41 in Pseudomonas aeruginosa PAO. The catabolic systems of the plasmids were shown to be thermosensitive, with a slight variation between one another. The plasmids became unstable at a high temperature; the temperature of effective elimination was 41 degrees C for plasmids NPL-41 and pBS3, and 42 degrees C for plasmids NAH and pBS2. NAH and pBS2 produced a weak inhibiting effect while NPL-41 and pBS3 caused a strong inhibition of the PAO strain growth at 42 degrees C. As a result, many anomalous filamentous cells (partly in the state of lysis) appeared in the cultural broth. Only PAO cells that had lost their plasmid were capable of normal growth in a medium with MPA at an elevated temperature; this creates a convenient system for selection of clones that have lost the plasmids of naphthalene biodegradation. Some of these plasmids can inhibit growth of Pseudomonas strains at an elevated temperature; this fact should be taken into account when the capability of Pseudomonas to grow at a high temperature is used as a taxonomic feature.     

Microbial linear plasmids

While plasmids were originally considered to be generally circular until almost two decades ago, linear elements were reported to exist as well. They are now known to be common genetic elements in both, pro- and eukaryotes. Two types of linear plasmids exist, the so-called hairpin plasmids with covalently closed ends and those with proteins bound to their 5′ termini. Hairpin plasmids are common in human-pathogenic Borrelia spirochetes, in which they are instrumental in escape from the immunological response; cryptic hairpin elements are present in mitochondria of the plant pathogenic fungus Rhizoctonia solani. Plasmids with 5′ attached proteins constitute the largest group. In actinomycetous bacteria they are conjugative and usually confer advantageous phenotypes, e.g. formation of antibiotics, degradation of xenobiotics, heavy-metal resistance and growth on hydrogen as the sole energy source. In contrast, the majority of linear plasmids from eukaryotes are cryptic, with only a few exceptions. In some yeasts a killer phenotype may be associated, the most thoroughly investigated elements being those from Kluyveromyces lactis killer strains. In Neurospora spp. and in Podospora anserina, senescence and longevity respectively are correlated with linear plasmids. This review focuses on the biology of linear plasmids, their environmental significance and their use as tools in molecular and applied microbiology. Received: 15 November 1996 / Received revision: 23 December 1996 / Accepted: 30 December 1996     

Evolution of linear plasmids

Summary Linear plasmids are genetic elements commonly found in yeast, filamentous fungi, and higher plants. In contrast to all other plasmids they possess terminal inverted repeats and terminal bound proteins and encode their own DNA and RNA polymerases. Here we present alignments of conserved amino acid sequences of both the DNA and RNA polymerases encoded by those linear plasmids for which DNA sequence data are available. Additionally these sequences are compared to a number of polymerases encoded by related viral and cellular entities. Phylogenetic trees have been established for both types of polymerases. These trees appear to exhibit very similar subgroupings, proving the accuracy of the method employed.Abbreviations TIR terminal inverted repeats - mt mitochondrial - ORF open reading frame Offprint requests to: F. Kempken     

Substrate interactions during aerobic biodegradation of benzene

This study dealt with the interactions with benzene degradation of the following aromatic compounds in a mixed substrate: toluene, o-xylene, naphthalene, 1,4-dimethylnaphthalene, phenanthrene, and pyrrole. The experiment was performed as a factorial experiment with simple batch cultures. The effect of two different types of inocula was tested. One type of inoculum was grown on a mixture of aromatic hydrocarbons; the other was grown on a mixture of aromatic hydrocarbons and nitrogen-, sulfur-, and oxygen-containing aromatic compounds (NSO compounds), similar to some of the compounds identified in creosote waste. The culture grown on the aromatic hydrocarbons and NSO compounds was much less efficient in degrading benzene than the culture grown on only aromatic hydrocarbons. The experiments indicated that toluene- and o-xylene-degrading bacteria are also able to degrade benzene, whereas naphthalene-, 1,,4-dimethylnaphthalene-, and phenanthrene-degrading bacteria have no or very little benzene-degrading ability. Surprisingly, the stimulating effect of toluene and o-xylene was true only if the two compounds were present alone. In combination an antagonistic effect was observed, i.e., the combined effect was smaller than the sum from each of the compounds. The reason for this behavior has not been identified. Pyrrole strongly inhibited benzene degradation even at concentrations of about 100 to 200 micrograms/liter. Future studies will investigate the generality of these findings.     

New plasmids of herbicide 2,4-dichlorophenoxyacetic acid biodegradation

Three herbicide 2,4-D metabolizing bacterial strains were isolated from three independent soil samples of Estonia. The strains, although belonging to various species, contain 2,4-D degradative plasmids with identical restriction patterns. pEST4001 is a 78 kb conjugative plasmid. All Pseudomonas putida PaW340 2,4-D+ transconjugants obtained a 70 kb plasmid pEST4011 - a deletion derivative of the pEST4001. The restriction patterns of the plasmids mentioned above are considerably different from those of the other 2,4-D plasmids pJP4 and pRC10 reported previously.     

Effects of oxygen on aerobic solid-state biodegradation kinetics

Oxygen is a critical control variable for composting and other solid-state biodegradation processes. In this study we examined the effect of varying oxygen concentrations (1%, 4%, and 21% O2 (v/v)) on biodegradation kinetics under different substrate (sewage sludge and synthetic food waste), temperature (35, 45, 55, and 65 degrees C), and moisture (36-60% H2O) conditions. Three forms of a saturation or Monod-type model and one form of an exponential model were evaluated against data from extensive experiments under carefully controlled environmental conditions. The exponential model performed well at temperatures from 35 to 55 degrees C but had problems at higher temperatures. The Monod-type models yielded the best fit based on R2 values. Multiple linear regression was used to express the oxygen half-saturation coefficient as a function of temperature and moisture. For a modified one-parameter saturation model the half-saturation coefficient varied from -0.67% to 1.74% v/v O2 under the range of conditions typical of composting systems. While the positive correlation of biodegradation rate with oxygen concentration reported by previous researchers held true for temperatures below 55 degrees C, an inverse relationship was found at 65 degrees C. Although this study did not directly examine anaerobic conditions, the results under microaerophilic conditions suggest oxygen may not offer kinetic advantages for extreme thermophilic biodegradation processes.     

Substrate interactions during aerobic biodegradation of benzene.

This study dealt with the interactions with benzene degradation of the following aromatic compounds in a mixed substrate: toluene, o-xylene, naphthalene, 1,4-dimethylnaphthalene, phenanthrene, and pyrrole. The experiment was performed as a factorial experiment with simple batch cultures. The effect of two different types of inocula was tested. One type of inoculum was grown on a mixture of aromatic hydrocarbons; the other was grown on a mixture of aromatic hydrocarbons and nitrogen-, sulfur-, and oxygen-containing aromatic compounds (NSO compounds), similar to some of the compounds identified in creosote waste. The culture grown on the aromatic hydrocarbons and NSO compounds was much less efficient in degrading benzene than the culture grown on only aromatic hydrocarbons. The experiments indicated that toluene- and o-xylene-degrading bacteria are also able to degrade benzene, whereas naphthalene-, 1,,4-dimethylnaphthalene-, and phenanthrene-degrading bacteria have no or very little benzene-degrading ability. Surprisingly, the stimulating effect of toluene and o-xylene was true only if the two compounds were present alone. In combination an antagonistic effect was observed, i.e., the combined effect was smaller than the sum from each of the compounds. The reason for this behavior has not been identified. Pyrrole strongly inhibited benzene degradation even at concentrations of about 100 to 200 micrograms/liter. Future studies will investigate the generality of these findings.     

Modeling the temperature kinetics of aerobic solid-state biodegradation

This study evaluated three models of microbial temperature kinetics using CO2 respiration data from aerobic solid-state biodegradation experiments. The models included those of Andrews and Kambhu/Haug, Ratkowsky et al., and the Cardinal Temperature Model with Inflection (CTMI) of Rosso et al. A parameter estimation routine implemented the Complex-Box search method for each model on 48 data sets collected during the composting of synthetic food waste or sewage-sludge (biosolids) mixed with maple wood chips at different oxygen concentrations and extents of decomposition. Each of the three nonlinear temperature kinetic functions proved capable of modeling a wide range of experimental data sets. However, the models differed widely in the consistency of their parameters. Parameters in the CTMI model were more stable over the course of the degradation process, and that variability which did arise was directly related to changes in the microbial process. Additional benefits of the CTMI model include the ease of parameter determinations, which can be approximated directly from laboratory experiments or full-scale system analysis, and the direct value of its parameters in engineering design and process control under a wide range of biodegradation conditions.     

Bacterial degradation of vinyl chloride

Summary Mycobacterium L1 can grow on vinyl chloride as sole carbon and energy source. Application of this bacterium to remove vinyl chloride from waste gases is proposed. From air containing 1% vinyl chloride 93% of the vinyl chloride was removed by passing the air through a fermentor containing a growing population ofMycobacterium L1.     

Horizontal transfer of catabolic plasmids and naphthalene biodegradation in open soil

The horizontal transfer of naphthalene biodegradation plasmids and the parallel process of its microbial degradation were studied for the first time. The tagged naphthalene-degrading strains bearing labeled biodegradation plasmids were used for the monitoring of horizontal plasmid transfer in open soil. The population kinetics of microorganisms, the survival rate and competitiveness of introduced strains, and the transfer of biodegradation plasmids to indigenous strains were investigated. The transfer of the labeled plasmid pNF142::TnMod-OTc to the introduced plasmid-free recipient P. putida KT2442 and to indigenous soil microorganisms of the genus Pseudomonas was shown both under selection pressure (in the presence of naphthalene) and in its absence. The 16S rRNA gene sequencing showed that the soil strains that had acquired plasmids were close to the species P. lini, P. frederiksbergensis, P. jessenii, P. graminis, P. putida, and P. alcaligenes. Thus, direct evidence of dissemination of the naphthalene biodegradation plasmids in microbial populations in open soil under selective and nonselective conditions has been obtained.     

Degradation of polychloroaromatic insecticides by Pseudomonas aeruginosa containing biodegradation plasmids

The work was aimed at studying the degradation of DDT, its metabolites and analogs by BS 816 and BS 827 strains constructed on the basis of Pseudomonas aeruginosa 640x strains and carrying biodegradation plasmids pBS2 and pBS3, respectively. DDT and kelthane were degraded by the BS 816 strain at a greater rate than by the parent culture. The investigation of enzymes involved in the oxidation of the aromatic cycle has shown that the plasmid-carrying strains possess the activity of metapyrocatechase and salicylate hydroxylase which is absent in P. aeruginosa 640x. The activity of pyrocatechase increased. In contrast to the parent strain where homogentisate induced only homogentisate oxygenase, this compound induces also metapyrocatechase in the constructed strains.     

Inheritance of biodegradation plasmids in the cells of homo- and heterologous hosts

A systematic analysis of the inheritance of D plasmids of the IncP-9 group (alpha-, beta-, gamma-, delta-, epsilon-, zeta-, eta-, theta-subgroups), IncP-7, as well as of those of undefined systematic affiliation in the cells of homologous (Pseudomonas putida) and heterologous (Escherichia coli) hosts was performed for the first time. For this purpose, mini-Tn5 transposons determining resistance to kanamycin (or streptomycin) were introduced into all the D plasmids under study. It has been established that all IncP-9 plasmids can be transmitted to the cells of a heterologous host E. coli (with the exception of plasmid pSVS15 from theta-subgroup). IncP-7 plasmids and those of undefined systematic affiliation do not possess this property and can be transmitted and stably inherited only in P. putida. The distinctive feature of most IncP-9 plasmids (alpha-, beta-, gamma-, delta-, epsilon-, and zeta-subgroups) is strict dependence of their inheritance on the temperature factor. At 37 degrees C, the plasmids of delta-, zeta-, and theta-subgroups are unstable in P. putida cells, while in E. coli nearly all plasmids of this systematic group are unstable. The exceptions are the plasmids of eta- and gamma-subgroups. Inheritance of these plasmids does not depend on temperature. At 28 degrees C and 37 degrees C, the eta plasmid is not maintained stably (inheritance stability is 2%), while the gamma plasmid has almost 100% stability under the same conditions.     

Toluene biodegradation and biofilm growth in an aerobic fixed-film reactor

Summary Aerobic biodegradation of toluene in a biofilm system was investigated. Toluene is easily biodegradable, like several other aromatic compounds. The degradation was first order at bulk concentrations lower than 0.14 mg/l and zero order above 6–8 mg/l. An average yield coefficient of 1 mg biomass/mg toluene degraded was found. A chemical oxygen demand balance relative to three biofilm growth scenarios showed that only a minor fraction of the carbon in the influent accumulated as biomass in the reactor. Of this accumulated biomass only a small fraction was active biomass, about 5% protein. A characterization of the carbon fractions leaving the reactor showed a significant production of soluble polymers and formation of suspended biomass. The latter was probably due to the detachment of filamentous bacteria. A decrease in toluene degradation was observed when the oxygen concentration was increased from 5 to about 20 mg/l. Future studies must show if this effect was due to inhibition.Correspondence to: J. P. Arcangeli     

Inheritance of biodegradation plasmids in the cells of homo- and heterologous hosts

A systematic analysis of the inheritance of D plasmids of the IncP-9 group (α-, β-, γ-, δ-, ?-, ζ-, η-, and θ-subgroups), IncP-7, as well as of those of undefined systematic affiliation in the cells of homologous (Pseudomonas putida) and heterologous (Escherichia coli) hosts was performed for the first time. For this purpose, mini-Tn5 transposons determining resistance to kanamycin (or streptomycin) were introduced into all the D plasmids under study. It has been established that all IncP-9 plasmids can be transmitted to the cells of a heterologous host E. coli (with the exception of plasmid pSVS15 from gq-subgroup). IncP-7 plasmids and those of undefined systematic affiliation do not possess this property and can be transmitted and stably inherited only in P. putida. The distinctive feature of most IncP-9 plasmids (α-, β-, δ-, ?-, and ζ-subgroups) is strict dependence of their inheritance on the temperature factor. At 37°C, the plasmids of δ-, ζ-, and θ-subgroups are unstable in P. putida cells, while in E. coli nearly all plasmids of this systematic group are unstable. The exceptions are the plasmids of η- and γ-subgroups. Inheritance of these plasmids does not depend on temperature. At 28°C and 37°C, the η plasmid is not maintained stably (inheritance stability is 2%), while the γ-plasmid has almost 100% stability.