Identification of 4-chlorobenzoyl-coenzyme A as intermediate in the dehalogenation catalyzed by 4-chlorobenzoate dehalogenase from Pseudomonas sp. CBS3

The intermediate in the reaction catalyzed by 4-chlorobenzoate dehalogenase from Pseudomonas sp. CBS3 was identified as 4-chlorobenzoyl-CoA. One component of 4-chlorobenzoate dehalogenase worked as a a 4-chlorobenzoyl-CoA ligase catalyzing the formation of 4-chlorobenzoyl-CoA from 4-chlorobenzoate, coenzyme A and ATP. This intermediate was detected spectrophotometrically and by HPLC. 4-chlorobenzoyl-CoA was the substrate for the dehalogenase component, which catalyzed the conversion to 4-hydroxybenzoate with concomitant release of coenzyme A.     

Identification of 4-chlorobenzoyl-coenzyme A as intermediate in the dehalogenation catalysed by 4-chlorobenzoate dehalogenase from Pseudomonas sp. CBS3

The intermediate in the reaction catalysed by 4-chlorobenzoate dehalogenase from Pseudomonas sp. CBS3 was identified as 4-chlorobenzoyl-CoA. One component of 4-chlorobenzoate debalogenase worked as a a 4-chlorobenzoyl-CoA ligase catalysing the formation of 4-chlorobenzoyl-CoA from 4-chlorobenzoate, coenzyme A and ATP. This intermediate was detected spectrophotometrically and by HPLC. 4-chlorobenzoyl-CoA was the substrate for the dehalogenase component, which catalysed the conversion to 4-hydroxybenzoate with concomitant release or coenzyme A.     

NADPH-dependent reductive ortho dehalogenation of 2,4-dichlorobenzoic acid in Corynebacterium sepedonicum KZ-4 and Coryneform bacterium strainNTB-1 via 2,4-dichlorobenzoyl coenzyme A.

Corynebacterium sepedonicum KZ-4, described earlier as a strain capable of growth on 2,4-dichlorobenzoate (G.M. Zaitsev and Y.N. Karasevich, Mikrobiologiya 54:356-369, 1985), is known to metabolize this substrate via 4-hydroxybenzoate and protocatechuate, and evidence consistent with an initial reductive dechlorination step to form 4-chlorobenzoate was found in another coryneform bacterium, strain NTB-1 (W.J.J. van den Tweel, J.B. Kok, and J.A.M. de Bont, Appl. Environ. Microbiol. 53:810-815, 1987). 2-Chloro-4-fluorobenzoate was found to be converted stoichiometrically to 4-fluorobenzoate by resting cells of strain KZ-4, compatible with a reductive process. Experiments with cell extracts demonstrated that Mg - ATP and coenzyme A (CoA) were required to stimulate reductive dehalogenation, consistent with the intermediacy of 2-chloro-4-fluoro-benzoyl-CoA and 2,4-dichlorobenzoyl-CoA thioesters. 2,4-Dichlorobenzoyl-CoA was shown to be converted to 4-chlorobenzoyl-CoA in a novel NADPH-dependent reaction in extracts of both KZ-4 and NTB-1. In addition to the ligase and reductive dehalogenase activities, hydrolytic 4-chlorobenzoyl-CoA dehalogenase and thioesterase activities, 4-hydroxybenzoate 3-monooxygenase, and protocatechuate 3,4-dioxygenase activities were demonstrated to be present in the soluble fraction of KZ-4 extracts following ultracentrifugation. We propose that the pathway for 2,4-dichlorobenzoate catabolism in strains KZ-4 and NTB-1 involves formation of 2,4-dichlorobenzoyl-CoA, NADPH-dependent ortho dehalogenation yielding 4-chlorobenzoyl-CoA, hydrolytic removal of chlorine from the para position to generate 4-hydroxybenzoyl-CoA, hydrolysis to form 4-hydroxybenzoate, oxidation to yield protocatechuate, and oxidative ring cleavage.     

Identification of genes coding for hydrolytic dehalogenation in the metagenome derived from a denitrifying 4-chlorobenzoate degrading consortium.

A metagenomic approach was taken to investigate the genetic basis for the ability of an anaerobic consortium to grow on either 4-chlorobenzoate or 4-bromobenzoate under denitrifying conditions. Degenerate PCR primers were designed for the family of 4-chlorobenzoyl-CoA dehalogenase genes. The primers were utilized to screen a metagenome library and two overlapping clones were identified which yield a PCR product. The complete sequence of one metagenome clone was determined and genes encoding 4-chlorobenzoyl-CoA ligase (FcbA) and 4-chlorobenzoyl-CoA dehalogenase (FcbB) were identified. Analysis of the ORFs present in the nucleotide sequence suggests that the metagenome clone originated from an uncultured denitrifying microorganism belonging to the Betaproteobacteria. Interestingly, unlike similar gene clusters reported in aerobes, a gene encoding 4-hydroxybenzoyl-CoA thioesterase was not present in the gene cluster. This suggests that 4-hydroxybenzoyl-CoA is further degraded via the anaerobic reduction pathway in the corresponding microorganism instead of through thioester hydrolysis to yield 4-hydroxybenzoate.     

Interchange of catalytic activity within the 2-enoyl-coenzyme A hydratase/isomerase superfamily based on a common active site template.

The structures and chemical pathways associated with the members of the 2-enoyl-CoA hydratase/isomerase enzyme superfamily are compared to show that a common active site design provides the members of this family with a CoA binding site, an expandable acyl binding pocket, an oxyanion hole for binding/polarizing the thioester C=O, and multiple active site stations for the positioning of acidic and basic amino acid side chains for use in proton shuttling. It is hypothesized that this active site template can be tailored to catalyze a wide range of chemical transformations through strategic positioning of acid/base residues among the active site stations. To test this hypothesis, the active site of one member of the 2-enoyl-CoA hydratase/isomerase family, 4-chlorobenzoyl-CoA dehalogenase, was altered by site-directed mutagenesis to include the two glutamate residues functioning in acid/base catalysis in a second family member, crotonase. Catalysis of the syn hydration of crotonyl-CoA, absent in the wild-type 4-chlorobenzoyl-CoA dehalogenase, was shown to occur with the structurally modified 4-chlorobenzoyl-CoA dehalogenase at kcat = 0.06 s-1 and Km = 50 microM.     

Electrostatic influence of active-site waters on the nucleophilic aromatic substitution catalyzed by 4-chlorobenzoyl-CoA dehalogenase

The 4-chlorobenzoyl-CoA dehalogenase catalyzes the hydrolytic dechlorination of 4-chlorobenzoyl-CoA via a two-step mechanism, namely nucleophilic aromatic substitution and ester hydrolysis. The mutation of an active-site Histidine residue has been shown to reduce the catalytic activity in both the substitution and subsequent hydrolysis steps. In this communication, we report a quantum mechanical/molecular mechanical simulation of the potential of mean force for the substitution step, which confirms the increased barrier height in the H90Q mutant and provides evidence on the electrostatic influence of two active-site waters on the rate-limiting barrier.     

Modulating electron density in the bound product, 4-hydroxybenzoyl-CoA, by mutations in 4-chlorobenzoyl-CoA dehalogenase near the 4-hydroxy group

The enzyme 4-chlorobenzoyl-CoA dehalogenase hydrolyzes 4-chlorobenzoyl-CoA (4-CBA-CoA) to 4-hydroxybenzoyl-CoA (4-HBA-CoA). Biochemical and crystallographic studies have identified a critical role for the dehalogenase residue Asp 145 in close proximity to the ligand's 4-hydroxy group in the structure of the product-enzyme complex. In the present study the effects of site selective mutations at Asp 145 on the product complex are explored by Raman spectroscopy. The spectral signatures of the WT-product complex, the large red shift in lambdamax, and the complete reorganization of the benzoyl ring modes in Raman data are absent for the D145E complex. The major spectral perturbations in the WT complex are brought about by strong electron "pull" at the benzoyl carbonyl and electron "push" by the side chain of Asp 145 near the 4-OH group. Acting in concert, these factors polarize the benzoyl's pi-electrons. Since the Raman data show that very strong electron pull occurs at the benzoyl's carbonyl in the D145E complex, it is apparent that the needed electron push near the benzoyl's 4-OH group is missing. Thus, very precise positioning of Asp 145's side chain near the benzoyl's 4-position is needed to bring about the dramatic electron reorganization seen in the WT complex, and this criterion cannot be met by the glutamate side chain with its additional CH2 group. For two other Asp145 mutants D145A and D145S that lack catalytic activity, Raman difference spectroscopic data for product complexes demonstrate the presence of a population of ionized product (i.e., 4-O-) in the active sites. The presence of the ionized phenolate form explains the observation that these complexes have highly red-shifted absorbance maxima with lambdamaxs near 400 nm. For the WT complex only the 4-OH form is seen, ionization being energetically expensive with the presence of the proximal negative charge on the Asp 145 side chain. Semiquantitative estimates of the pKa for the bound product in D145S and D145A indicate that this ionization lies in the pH 6.5-7.0 range. This is approximately 2 pH units below the pKa for the free product. The Raman spectrum of 4-dimethylaminobenzoyl-CoA undergoes major changes upon binding to dehalogenase. The bound form has two features near 1562 and 1529 cm-1 and therefore closely resembles the spectrum of product bound to wild-type enzyme, which underlines the quinonoid nature in these complexes. The use of a newly developed Raman system allowed us to obtain normal (nonresonance) Raman data for the dehalogenase complexes in the 100-300 microM range and heralds an important advance in the application of Raman spectroscopy to dilute solutions of macromolecules.     

Dehalogenation of 4-chlorobenzoate

Pseudomonas sp. CBS3 is capable of growing with 4-chlorobenzoate as sole source of carbon and energy. The removal of the chlorine of 4-chlorobenzoate is performed in the first degradation step by an enzyme system consisting of three proteins. A 4-halobenzoate-coenzyme A ligase activates 4-chlorobenzoate in a coenzyme A, ATP and Mg²⁺ dependent reaction to 4-chlorobenzoyl-coenzyme A. This thioester intermediate is dehalogenated by the 4-chlorobenzoyl-coenzyme A dehalogenase. Finally coenzyme A is split off by a 4-hydroxybenzoyl-CoA thioesterase to form 4-hydroxybenzoate. The involved 4-chlorobenzoyl-coenzyme A dehalogenase was purified to apparent homogeneity by a five-step purification procedure. The native enzyme had an apparent molecular mass of 120,000 and was composed of four identical polypeptide subunits of 31 kDa. The enzyme displayed an isoelectric point of 6.7. The maximal initial rate of catalysis was achieved at pH 10 at 60 °C. The apparent K _m value for 4-chlorobenzoyl-coenzyme A was 2.4–2.7 µM. V _max was 1.1 × 10^–7 M sec^–1 (2.2 µmol min^–1 mg^–1 of protein). The NH₂-terminal amino acid sequence was determined. All 4-halobenzoyl-coenzyme A thioesters, except 4-fluorobenzoyl-coenzyme A, were dehalogenated by the 4-chlorobenzoyl-CoA dehalogenase.Abbreviations CBA chlorobenzoate - CoA coenzyme A - HBA hydroxybenzoate - DTT dithiothreitol - HPLC high performance liquid chromatography - PAGE polyacrylamide gel electrophoresis     

Contributions of long-range electrostatic interactions to 4-chlorobenzoyl-CoA dehalogenase catalysis: a combined theoretical and experimental study

It is well established that electrostatic interactions play a vital role in enzyme catalysis. In this work, we report theory-guided mutation experiments that identified strong electrostatic contributions of a remote residue, namely, Glu232 located on the adjacent subunit, to 4-chlorobenzoyl-CoA dehalogenase catalysis. The Glu232Asp mutant was found to bind the substrate analogue 4-methylbenzoyl-CoA more tightly than does the wild-type dehalogenase. In contrast, the kcat for 4-chlorobenzoyl-CoA conversion to product was reduced 10000-fold in the mutant. UV difference spectra measured for the respective enzyme-ligand complexes revealed an approximately 3-fold shift in the equilibrium of the two active site conformers away from that inducing strong pi-electron polarization in the ligand benzoyl ring. Increased substrate binding, decreased ring polarization, and decreased catalytic efficiency indicated that the repositioning of the point charge in the Glu232Asp mutant might affect the orientation of the Asp145 carboxylate with respect to the substrate aromatic ring. The time course for formation and reaction of the arylated enzyme intermediate during a single turnover was measured for wild-type and Glu232Asp mutant dehalogenases. The accumulation of arylated enzyme in the wild-type dehalogenase was not observed in the mutant. This indicates that the reduced turnover rate in the mutant is the result of a slow arylation of Asp145, owing to decreased efficiency in substrate nucleophilic attack by Asp145. To rationalize the experimental observations, a theoretical model is proposed, which computes the potential of mean force for the nucleophilic aromatic substitution step using a hybrid quantum mechanical/molecular mechanical method. To this end, the removal or reorientation of the side chain charge of residue 232, modeled respectively by the Glu232Gln and Glu232Asp mutants, is shown to increase the rate-limiting energy barrier. The calculated 23.1 kcal/mol free energy barrier for formation of the Meisenheimer intermediate in the Glu232Asp mutant represents an increase of 6 kcal/mol relative to that of the wild-type enzyme, consistent with the 5.6 kcal/mol increase calculated from the difference in experimentally determined rate constants. On the basis of the combination of the experimental and theoretical evidence, we hypothesize that the Glu232(B) residue contributes to catalysis by providing an electrostatic force that acts on the Asp145 nucleophile.     

Product catalyzes the deamidation of D145N dehalogenase to produce the wild-type enzyme

Aspartate 145 plays an essential role in the active site of 4-chlorobenzoyl-CoA dehalogenase, forming a transient covalent link at the 4-position of the benzoate during the conversion of the substrate to 4-hydroxybenzoyl-CoA. Replacement of Asp 145 by residues such as alanine or serine results in total inactivation, and stable complexes can be formed with either substrate or product. The Raman spectroscopic characterization of some of the latter is described in the preceding publication (Dong et al.). The present work investigates complexes formed by D145N dehalogenase and substrate or product. Time-resolved absorption and Raman difference spectroscopic data show that these systems evolve rapidly with time. For the substrate complex, initially the absorption and Raman spectra show the signatures of the substrate bound in the active site of the asparagine 145 form of the enzyme but these signatures are accompanied by those for the ionized product. After several minutes these signatures disappear to be replaced with those closely resembling the un-ionized product in the active site of wild-type dehalogenase. Similarly, for the product complex, the absorption and Raman spectra initially show evidence for ionized product in the active site of D145N, but these are rapidly replaced by signatures closely resembling the un-ionized product bound to wild-type enzyme. It is proposed that product bound to the active site of asparagine 145 dehalogenase catalyzes the deamidation of the asparagine side chain to produce the wild-type aspartate 145. For the complexes involving substrate, the asparagine 145 enzyme population contains a small amount of the WT enzyme, formed by spontaneous deamidation, that produces product. In turn, these product molecules catalyze the deamidation of Asn 145 in the major enzyme population. Thus, conversions of substrate to product and of D145N to D145D dehalogenase go on simultaneously. The spontaneous deamidation of asparagine 145 has been characterized by allowing the enzyme to stand at RT in Hepes buffer at pH 7.5. Under these conditions deamidation occurs with a rate constant of 0.0024 h-1. The rate of product-catalyzed deamidation in Hepes buffer at 22 degrees C was measured by stopped-flow kinetics to be 0.024 s-1, 36000 times faster than the spontaneous process. A feature near 1570 cm-1 could be observed in the early Raman spectra of both substrate and product-enzyme complexes. This band is not associated with either substrate or product and is tentatively assigned to an ester-like species formed by the attack of the product's 4-O- group on the carbonyl of asparagine's side chain and the subsequent release of ammonia. A reaction scheme is proposed, incorporating these observations.     

DL-2-Haloacid dehalogenase from Pseudomonas sp. 113 is a new class of dehalogenase catalyzing hydrolytic dehalogenation not involving enzyme-substrate ester intermediate.

DL-2-Haloacid dehalogenase from Pseudomonas sp. 113 (DL-DEX 113) catalyzes the hydrolytic dehalogenation of D- and L-2-haloalkanoic acids, producing the corresponding L- and D-2-hydroxyalkanoic acids, respectively. Every halidohydrolase studied so far (L-2-haloacid dehalogenase, haloalkane dehalogenase, and 4-chlorobenzoyl-CoA dehalogenase) has an active site carboxylate group that attacks the substrate carbon atom bound to the halogen atom, leading to the formation of an ester intermediate. This is subsequently hydrolyzed, resulting in the incorporation of an oxygen atom of the solvent water molecule into the carboxylate group of the enzyme. In the present study, we analyzed the reaction mechanism of DL-DEX 113. When a single turnover reaction of DL-DEX 113 was carried out with a large excess of the enzyme in H(2)(18)O with a 10 times smaller amount of the substrate, either D- or L-2-chloropropionate, the major product was found to be (18)O-labeled lactate by ionspray mass spectrometry. After a multiple turnover reaction in H(2)(18)O, the enzyme was digested with trypsin or lysyl endopeptidase, and the molecular masses of the peptide fragments were measured with an ionspray mass spectrometer. No peptide fragments contained (18)O. These results indicate that the H(2)(18)O of the solvent directly attacks the alpha-carbon of 2-haloalkanoic acid to displace the halogen atom. This is the first example of an enzymatic hydrolytic dehalogenation that proceeds without producing an ester intermediate.     

Mortality curves of blind cave crayfish (Orconectes australis australis) exposed to chlorinated stream water

Chlorinated stream water toxicity was tested on the blind cave crayfish Orconectes australis australis from Merrybranch Cave, White County, Tennessee. An undisturbed natural cavern, Merry-branch was formed between two strata of sandstone having a mean elevation of 354 meters (MSL). Test water was collected from a subterranian stream in the cave supporting the hypogean crayfish population, and transported to the laboratory. No chlorinity was detected in the underground stream water.In the laboratory, cave water was chlorinated with sodium hypechlorus solution at various concentrations of total residual chlorine, combined residual, and free chlorine content as measured by Standard Methods titration procedure. Thirty-six crayfish, six crayfish per test solution, were subjected to a three day acclimation period at chlorine concentrations ranging from 0.21–1.50 mg./l. total residual chlorine, 0.20–0.30 mg./l. combined residual chlorine, and 0.01–1.20 mg./l. free chlorine; and then subjected t0 a 24 hour time-to-death (hourly) bioassay at the following chlorine water dilutions (mg./l.): (1) 7.45 total residual, 0.45 combined residual, and 7.00 free, (2) 3.39 total residual, 0.39 combined residual, and 3.00 free, (3) 2.85 total residual, 0.35 combined residual, and 2.50 free, (4) 2.30 total residual, 0.30 combined residual, and 2.00 free, (5) t.96 total residual, 0.21 combined residual, and 1.75 free, and (6) control. Fluctuations within these concentrations ranged from ± 0.20 free chlorine. All test solutions and a control were delivered by an Esvelt serial diluter. In addition, a 24 hour time-to-death (hourly) bioassay was conducted at the same dilutions 0n crayfish not acclimated to chlorine.These test demonstrated that crayfish mortalities generally increased with increasing concentrations of chlorine in both bio-assays, while acclimated crayfish tended to be more tolerant than non-acclimated ones.Funds for this research were provided by the Aquatic Ecology Fund, Biology Dept., Tennessee Technological University     

Chlorine decay and bacterial inactivation kinetics in drinking water in the tropics

The decay of free chlorine (Cl₂) and combined chlorine (mostly monochloramine: NH₂Cl) and the inactivation of bacteria was examined in Dar es Salaam, Tanzania. Batch experiments, pilot-scale pipe experiments and full-scale pipe experiments were carried out to establish the kinetics for both decay and inactivation, and to compare the two disinfectants for use under tropical conditions. The decay of both disinfectants closely followed first order kinetics, with respect to the concentration of both disinfectant and disinfectant-consuming substances. Bacterial densities exhibited a kinetic pattern consisting of first order inactivation with respect to the density of the bacteria and the concentration of the disinfectant, and first order growth with respect to the bacterial density. The disinfection kinetic model takes the decaying concentration of the disinfectant into account. The decay rate constant for free chlorine was 114 lg^-1h^-1, while the decay rate constant for combined chlorine was 1.84 lg^-1h^-1 (1.6% of the decay rate for free chlorine). The average concentration of disinfectant consuming substances in the water phase was 2.6 mg Cl₂/l for free chlorine and 5.6 mg NH₂Cl/l for combined chlorine. The decay rate constant and the concentration of disinfectant consuming substances when water was pumped through pipes, depended on whether or not chlorination was continuous. Combined chlorine especially could clean the pipes of disinfectant consuming substances. The inactivation rate constant , was estimated at 3.06×10⁴ lg^-1h^-1. Based on the inactivation rate constant, and a growth rate constant determined in a previous study, the critical concentration of free chlorine was found to be 0.08 mg Cl₂/l. The critical concentration is a value below which growth rates dominate over inactivation.The authors are with the Technical University of Denmark, IMT, CDC, Build. 208, DK-2800 Lyngby, Denmark     

Changes of chlorine isotope composition characterize bacterial dehalogenation of dichloromethane

Fractionation of dichloromethane (DCM) molecules with different chlorine isotopes by aerobic methylobacteria Methylobacterium dichloromethanicum DM4 and Albibacter nethylovorans DM10; cell-free extract of strain DM4; and transconjugant Methylobacterium evtorquens Al1/pME 8220, expressing the dcmA gene for DCM dehalogenase but unable to grow on DCM, was studied. Kinetic indices of DCM isotopomers for chlorine during bacterial dehalogenation and diffusion were compared. A two-step model is proposed, which suggests diffusional DCM transport to bacterial cells.     

Recruitment of a double bond isomerase to serve as a reductive dehalogenase during biodegradation of pentachlorophenol

Tetrachlorohydroquinone dehalogenase catalyzes the replacement of chlorine atoms on tetrachlorohydroquinone and trichlorohydroquinone with hydrogen atoms during the biodegradation of pentachlorophenol by Sphingomonas chlorophenolica. The sequence of the active site region of tetrachlorohydroquinone dehalogenase is very similar to those of the corresponding regions of maleylacetoacetate isomerases, enzymes that catalyze the glutathione-dependent isomerization of a cis double bond in maleylacetoacetate to the trans configuration during the catabolism of phenylalanine and tyrosine. Furthermore, tetrachlorohydroquinone dehalogenase catalyzes the isomerization of maleylacetone (an analogue of maleylacetoacetate) at a rate nearly comparable to that of a bona fide bacterial maleylacetoacetate isomerase. Since maleylacetoacetate isomerase is involved in a common and presumably ancient pathway for catabolism of tyrosine, while tetrachlorohydroquinone dehalogenase catalyzes a more specialized reaction, it is likely that tetrachlorohydroquinone dehalogenase arose from a maleylacetoacetate isomerase. The substrates and overall transformations involved in the dehalogenation and isomerization reactions are strikingly different. This enzyme provides a remarkable example of Nature's ability to recruit an enzyme with a useful structural scaffold and elaborate upon its basic catalytic capabilities to generate a catalyst for a newly needed reaction.     

The Life Cycle of Chlorine, Part II: Conversion Processes and Use in the European Chemical Industry

The major purpose of this article is to construct a plausible emissions profile for the European chemical industry from process data and mass balance considerations.' In it we describe this industry and its major conversion processes and emissions. Four major process chains, beginning with methane, ethylene, propylene, and benzene are analyzed, along with five important stand-alone processes. A self-consistent version of the industry is constructed for 1992, based on data from a variety of sources.
In 1992 Europe consumed 9,297 metric kilotons as measured by weight of chlorine (kMT[CI]) of salt and 2 I I kMT(CI) of recycled hydrochloric acid (HCI) to produce 86 I0 kMT of virgin elemental chlorine, plus 278 kMT(CI) of virgin by-product HCI. Total chlorine input to the industry was 8,689 kMT including I2 kMT(CI) of recycled chlorinated hydrocarbons (CHCs) and (net) 79 kMT(CI) of HCI. Shipments of chlorine and HCI to other sectors was 1,367 kMT(CI), while 7,322 kMT(CI) was embodied in products or lost within the sector: Of this subtotal, 350 kMT(CI) was used to manufacture identified inorganic chemicals, 5,694 kMT(CI) for identified organic chemicals, and 1,278 kMT(CI) for "other unspecified" chemicals.
We estimate that products account for 41.6% of inputs (measured at the "fence"), while wastes account for 24.7%     

Relationship between inactivation kinetics of a Listeria monocytogenes suspension by chlorine and its chlorine demand

AIMS: Chlorine demand by Listeria monocytogenes cells and inactivation of L. monocytogenes by chlorine (0.6-1.0 mg l(-1)) at different temperatures (4, 20 and 30 degrees C) have been investigated in a batch reactor. METHODS AND RESULTS: Chlorine demand depended on the microbial concentration and was independent on the initial chlorine concentration and temperature. Chlorine decay was modelled by the addition of two first-order decay equations. Inactivation of L. monocytogenes by chlorine depended on the initial microbial concentration, initial chlorine concentration and temperature. A mathematical model based on a biphasic inactivation properly described survival curves of L. monocytogenes and a tertiary model was developed that satisfactorily predicted the inactivation of L. monocytogenes by different concentrations of initial chlorine at different temperatures. CONCLUSIONS: Both available chlorine decay and inactivation of L. monocytogenes by chlorine were biphasic and can be modelled by a two-term exponential model. SIGNIFICANCE AND IMPACT OF THE STUDY: The biphasic nature of survival curves of L. monocytogenes did not reflect the effect of a change of available chlorine concentration during the treatment. The microbial inactivation was caused by successive reactions that occur after the consumption of the chlorine by the bacterial cell components.     

A Pseudomonas putida Strain Genetically Engineered for 1,2,3-Trichloropropane Bioremediation

1,2,3-Trichloropropane (TCP) is a toxic compound that is recalcitrant to biodegradation in the environment. Attempts to isolate TCP-degrading organisms using enrichment cultivation have failed. A potential biodegradation pathway starts with hydrolytic dehalogenation to 2,3-dichloro-1-propanol (DCP), followed by oxidative metabolism. To obtain a practically applicable TCP-degrading organism, we introduced an engineered haloalkane dehalogenase with improved TCP degradation activity into the DCP-degrading bacterium Pseudomonas putida MC4. For this purpose, the dehalogenase gene (dhaA31) was cloned behind the constitutive dhlA promoter and was introduced into the genome of strain MC4 using a transposon delivery system. The transposon-located antibiotic resistance marker was subsequently removed using a resolvase step. Growth of the resulting engineered bacterium, P. putida MC4-5222, on TCP was indeed observed, and all organic chlorine was released as chloride. A packed-bed reactor with immobilized cells of strain MC4-5222 degraded >95% of influent TCP (0.33 mM) under continuous-flow conditions, with stoichiometric release of inorganic chloride. The results demonstrate the successful use of a laboratory-evolved dehalogenase and genetic engineering to produce an effective, plasmid-free, and stable whole-cell biocatalyst for the aerobic bioremediation of a recalcitrant chlorinated hydrocarbon.     

Expression of the 4-chlorobenzoate dehalogenase genes from Pseudomonas sp.-CBS3 in Escherichia coli and identification of the gene translation products.

The genes encoding the 4-chlorobenzoate dehalogenase of Pseudomonas sp. strain CBS3 were, in an earlier study, cloned in Escherichia coli DH1 with the cosmid vector pPSA843 and then mobilized to the 4-chlorobenzoate dehalogenase minus strain Pseudomonas putida KT2440. In this paper we report on the expression of 4-chlorobenzoate dehalogenase in these clones and on the polypeptide composition of the active enzyme. The dehalogenase activity in whole cells suspended in 3.2 mM 4-chlorobenzoate (30 degrees C) was determined to be approximately 27 units (micromoles 4-hydroxybenzoate produced per minute) per 100 g of E. coli-pPSA843 cells and approximately 28 units per 100 g of P. putida-pPSA843 cells. Dehalogenase activity in fresh cellular extracts (pH 7.4, 30 degrees C) prepared from the E. coli and P. putida clones was unstable and at least 20-fold lower than that observed with the whole cells. The polypeptide components of the dehalogenase were identified by selective expression of the cloned dehalogenase genes and analysis of the gene translation products. Analysis of dehalogenase activity in omega insertion mutants and deletion mutants circumscribed the dehalogenase genes to a 4.8-kilobase (4.8 kb) stretch of the 9.5-kb DNA fragment. Selective expression of the dehalogenase genes from a cloned 4.8-kb DNA fragment in a maxicell system revealed a 30-kDa polypeptide as one of the components of the dehalogenase system. Selective expression of the dehalogenase genes using the T7 polymerase promoter system revealed the 30-kDa polypeptide and 57- and 16-kDa polypeptide products. Determination of which of the three polypeptides were translated in deletion mutants provided the relative positions of the encoding genes on a single DNA strand and the direction in which they are transcribed.     

Changes of chlorine isotope composition characterize bacterial dehalogenation of dichloromethane

Fractionation of dichloromethane (DCM) molecules with different chlorine isotopes by aerobic methylobacteria Methylobacterium dichloromethanicum DM4 and Albibacter methylovorans DM10; cell-free extract of strain DM4; and transconjugant Iethylobacterium extorquens AI1/pME 8220, expressing the dcmA gene for DCM dehalogenase but unable to grow on DCM, was studied. Kinetic indices of DCM isotopomers for chlorine during bacterial dehalogenation and diffusion were compared. A two-step model is proposed, which suggests diffusional DCM transport to bacterial cells.