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Nickel-resistant bacteria from anthropogenically nickel-polluted and naturally nickel-percolated ecosystems.

DNA fragments harboring the nickel resistance determinants from bacteria isolated from anthropogenically polluted ecosystems in Europe and Zaire were compared with those harboring the nickel resistance determinants from bacteria isolated from naturally nickel-percolated soils from New Caledonia by DNA-DNA hybridization. The biotinylated DNA probes were derived from the previously described Alcaligenes eutrophus CH34, Alcaligenes xylosoxidans 31A, Alcaligenes denitrificans 4a-2, and Klebsiella oxytoca CCUG 15788 and four new nickel resistance-determining fragments cloned from strains isolated from soils under nickel-hyperaccumulating trees. Nine probes were hybridized with endonuclease-cleaved plasmid and total DNA samples from 56 nickel-resistant strains. Some of the New Caledonian strains were tentatively identified as Acinetobacter, Pseudomonas mendocina, Comamonas, Hafnia alvei, Burkholderia, Arthrobacter aurescens, and Arthrobacter ramosus strains. The DNA of most strains showed homologies to one or several of the following nickel resistance determinants: the cnr and ncc operons of the strains A. eutrophus CH34 and A. xylosoxidans 31A, respectively, the nre operon of strain 31A, and the nickel resistance determinants of K. oxytoca. On the basis of their hybridization reactions the nickel resistance determinants of the strains could be assigned to four groups: (i) cnr/ncc type, (ii) cnr/ncc/nre type, (iii) K. oxytoca type, and (iv) others. The majority of the strains were assigned to the known groups. Among the strains from Belgium and Zaire, exclusively the cnr/ncc and the cnr/ncc/nre types were found. Among the New Caledonian strains all four types were represented. Homologies to the nre operon were found only in combination with the cnr/ncc operon. The homologies to the cnr/ncc operon were the most abundant and were detected alone or together with homologies to the nre operon. Only the DNA of the strains isolated from soil in Scotland and the United States and that of five of the New Caledonian strains did not show any detectable homologies to any of our probes. The nickel resistance fragment isolated from Burkholderia strain 32W-2 was studied in some detail. This 15-kb BamHI fragment conferred resistance to 1 to 5 mM NiCl(inf2) to Escherichia coli and resistance to up to 25 mM NiCl(inf2) to A. eutrophus. It showed strong homologies to both the cnr/ncc operon and the nre operon and conferred strictly regulated (inducible) nickel resistance to A. eutrophus.

Journal Article↗

Evidence for Intracellular and Extracellular Dimethylsulfoniopropionate (DMSP) Lyases and DMSP Uptake Sites in Two Species of Marine Bacteria.

The kinetics of dimethylsulfoniopropionate (DMSP) uptake and dimethylsulfide (DMS) production from DMSP in two bacterial species, Alcaligenes sp. strain M3A, an isolate from estuarine surface sediments, and Pseudomonas doudoroffii, from seawater, were investigated. In Alcaligenes cells induced for DMSP lyase (DL) activity, DMS production occurred without DMSP uptake. In DL-induced suspensions of P. doudoroffii, uptake of DMSP preceded the production of DMS, indicating an intracellular location of DL; intracellular DMSP levels reached ca. 7 mM. DMSP uptake rates in noninduced cells showed saturation at three concentrations (K(inft) [transport] values, 3.4, 127, and 500 (mu)M). In DL-induced cells of P. doudoroffii, DMSP uptake rates increased ca. threefold (V(infmax), 0.022 versus 0.065 (mu)mol of DMSP taken up min(sup-1) mg of cell protein(sup-1)), suggesting that the uptake binding proteins were inducible. DMSP uptake and DL activity in P. doudoroffii were both inhibited by CN(sup-), 2,4-dinitrophenol, and membrane-impermeable thiol-binding reagents, further indicating active uptake of DMSP by cell surface components. The respiratory inhibitors had limited or no effect on DL activity by the Alcaligenes sp. Of the structural analogs of DMSP tested for their effect on DMSP metabolism, glycine betaine (GBT), but not methyl-3-mercaptopropionic acid (MMPA), inhibited DMSP uptake by P. doudoroffii, suggesting that GBT shares a binding protein with DMSP and that MMPA is taken up at a separate site. Two models of DMSP uptake, induction, and DL location found in marine bacteria are presented.

Journal Article↗

Determination of antigenic relationships among legionellae and non-legionellae by direct fluorescent-antibody and immunodiffusion tests.

Six isolates, five from water samples and one from a human tracheal swab taken at autopsy, reacted strongly with working dilutions of Legionella fluorescent-antibody conjugates. Of these, two isolates of Pseudomonas fluorescens (EB and CDC93), one isolate of the Flavobacterium-Xanthomonas group (CDC65), and one isolate of P. alcaligenes (CDC11) reacted with Legionella pneumophila serogroup 1 conjugate. P. alcaligenes ABB 50 reacted with an L. pneumophila serogroup 3 conjugate and of P. maltophilia reacted with the L. micdadei conjugate. Antisera and labeled conjugates were prepared for these new cross-reacting isolates, and their relationships to the legionellae were examined by direct fluorescent-antibody and immunodiffusion tests. A nonreciprocal cross-reaction existed between L. micdadei and P. maltophilia and also between serogroups 3 of L. pneumophila and P. alcaligenes ABB50. Of the four isolates that reacted with serogroup 1 of L. pneumophila, P. fluorescens CDC93 had the strongest relationship, and the other three had only minor relationships. Although cross-reactivity among non-legionellae and legionellae has not been a major problem, these findings are relevant to the interpretation of direct fluorescent-antibody tests for detecting these bacteria.

Antigens, Bacterial↗

Chemical resistance of the gram-negative bacteria to different sanitizers in a water purification system.

BACKGROUND: Purified water for pharmaceutical purposes must be free of microbial contamination and pyrogens. Even with the additional sanitary and disinfecting treatments applied to the system (sequential operational stages), Pseudomonas aeruginosa, Pseudomonas fluorescens, Pseudomonas alcaligenes, Pseudomonas picketti, Flavobacterium aureum, Acinetobacter lowffi and Pseudomonas diminuta were isolated and identified from a thirteen-stage purification system. To evaluate the efficacy of the chemical agents used in the disinfecting process along with those used to adjust chemical characteristics of the system, over the identified bacteria, the kinetic parameter of killing time (D-value) necessary to inactivate 90% of the initial bioburden (decimal reduction time) was experimentally determined. METHODS: Pseudomonas aeruginosa, Pseudomonas fluorescens, Pseudomonas alcaligenes, Pseudomonas picketti, Flavobacterium aureum, Acinetobacter lowffi and Pseudomonas diminuta were called in house (wild) bacteria. Pseudomonas diminuta ATCC 11568, Pseudomonas alcaligenes INCQS , Pseudomonas aeruginosa ATCC 15442, Pseudomonas fluorescens ATCC 3178, Pseudomonas picketti ATCC 5031, Bacillus subtilis ATCC 937 and Escherichia coli ATCC 25922 were used as 'standard' bacteria to evaluate resistance at 25 degrees C against either 0.5% citric acid, 0.5% hydrochloric acid, 70% ethanol, 0.5% sodium bisulfite, 0.4% sodium hydroxide, 0.5% sodium hypochlorite, or a mixture of 2.2% hydrogen peroxide (H2O2) and 0.45% peracetic acid. RESULTS: The efficacy of the sanitizers varied with concentration and contact time to reduce decimal logarithmic (log10) population (n cycles). To kill 90% of the initial population (or one log10 cycle), the necessary time (D-value) was for P. aeruginosa into: (i) 0.5% citric acid, D = 3.8 min; (ii) 0.5% hydrochloric acid, D = 6.9 min; (iii) 70% ethanol, D = 9.7 min; (iv) 0.5% sodium bisulfite, D = 5.3 min; (v) 0.4% sodium hydroxide, D = 14.2 min; (vi) 0.5% sodium hypochlorite, D = 7.9 min; (vii) mixture of hydrogen peroxide (2.2%) plus peracetic acid (0.45%), D = 5.5 min. CONCLUSION: The contact time of 180 min of the system with the mixture of H2O2+ peracetic acid, a total theoretical reduction of 6 log10 cycles was attained in the water purified storage tank and distribution loop. The contact time between the water purification system (WPS) and the sanitary agents should be reviewed to reach sufficient bioburden reduction (over 6 log10).

Disinfectants↗

Comparison of colony lift with direct spotting methods of blot preparation on the effect of colony hybridization in the detection of environmental organisms.

Nucleic acid probes are used on site to detect or to identify individual microbial cells without cultivation. This molecular technique can avoid some limitations of traditional identification methods including time consuming and imprecise. This study examined the factors affecting colony hybridization and compared the effectiveness of membrane prepared by colony lifting with direct spotting procedures using the universal probe Eub 338. The results of hybridization varied depending on the type of colony morphology. For dry and rough colonies, colony hybridization was not suitable for detecting Acinetobactersp. (CK2A, CK2B), Alcaligenes sp. (TH11 B), Xanthomonas sp. (TH7B), Arthrobacter globiformis (CCRC 10598) and Microbacterium sp. (CCRC 11036). Colonies of Acinetobacter sp. (CCRC 15425) and Alcaligenes spp. (CCRC 10828, H) on agar and membrane were thick and raised, and their detection signals of hybridization were diffused or blank. Colonies of Alcaligenes sp. (CM7A, ANV2) and Acinetobacter sp. (ANV8) isolated from the sludge of biological processes treating ABS wastewater were flat and smooth, and their hybridization signals were clear. For those strains suitable for colony hybridization, the colony blots prepared by colony lift and direct spotting procedures gave the same sensitivity for colony hybridization.

Bacteria↗

[Species composition and microbial contamination of atmospheric humidity condensate and potable water from the Mir water supply systems during Mir main missions 4 through 27].

Analyzed were quantitative and qualitative characteristics, and processes of formation and transformation of microflora in the atmospheric humidity condensate (AHC) and potable water (PW) regenerated from the condensate by the long-operating system (SRV-K) aboard space station Mir. The paper presents data on species composition of microflora of AHC, and PW regenerated by SRV-K in the period from 1989 through to 1999. The following microbial species were identified in AHC: Alcaligenes (14.8%), Bacillus (3.7%), Citrobacter (7.4%), Clostridium (11.1%), Enterobacter (7.4%), Proteus (7.4%), Pseudomonas (18.5%), and Staphylococcus (100%). There were two PW cocks in SRV-K--"hot" and "cold". "Hot" PW microflora included Alcaligenes (15%), Bacillus (5%), Citrobacter (20%), Clostridium (5%), Enterobacter (15%), Proteus (10%), Pseudomonas (15%), and Staphylococcus (75%). "Cold" PW microflora included Aeromonas (14.3%), Alcaligenes (21.4%), Bacillus (7.1%), Citrobacter (7.1%), Clostridium (7.1%), Enterobacter (7.1%), Moraxella (7.1%), Pseudomonas (7.1%), and Staphylococcus (78.5%). Microbial content averaged 8.9 x 10(2) +/- 1.3 (0.01-4) x 10(3) CFU/ml in condensate and 1.5 +/- 0.1 (0-3.0) CFU/ml in regenerated potable water.

Atmosphere↗

Precipitin response of potato processing workers to work-related microbial allergens.

Serum samples from 61 potato processing workers and 30 urban dwellers not exposed to organic dusts (as a reference group) were examined in agar-gel precipitation test performed by Ouchterlony double diffusion method with the antigens of 12 microorganisms associated with organic dusts. Each serum was tested twice: not concentrated, and three-fold concentrated, for the detection of low levels of precipitins. The antibody response of workers to the antigen of coryneform bacterium Agromyces ramosus was high, at both not concentrated and 3-fold concentrated sera (respectively 29.5% and 45.9%)--significantly greater than in reference group (p < 0.001). Workers' response to the antigens of Gram-negative bacterium Alcaligenes faecalis and thermophilic actinomycete Thermoactinomyces vulgaris was lower (respectively 13.1% and 13.1% at not concentrated sera, 24.6% and 29.5% at 3-fold concentrated sera) but in all cases significantly greater than in reference group (p < 0.05 at not concentrated sera, p < 0.01 and p < 0.001 at 3-fold concentrated sera). The frequency of positive precipitin reactions of potato workers to antigen of Penicillium citrinum was high only at 3-fold concentrated sera (55.7%)--significantly higher compared to reference group (p < 0.001). The antibody response of potato workers to other antigens was either unspecific or low, showing no significant difference compared to reference group. Twenty eight out of 61 examined potato processing workers (45.9%) reported the occurrence of the work-related pulmonary symptoms. The frequency of positive precipitin reactions to Agromyces ramosus, Alcaligenes faecalis, Thermoactinomyces vulgaris, Penicillium citrinum and Acinetobacter calcoaceticus was significantly greater in the subgroup of 28 workers reporting work-related pulmonary symptoms compared to 33 asymptomatic workers (p < 0.05). Study results suggest that antigens of Agromyces ramosus, Alcaligenes faecalis, Thermoactinomyces vulgaris and Penicillium citrinum should be considered as potential occupational allergens, probably stimulating an adverse immunopathological reaction in the exposed potato processing workers.

Adult↗

Studies on the biodegradation of nonionic surfactants applied in the polyester fiber industry. I. Activated sludge bacteria degrading the surfactants.

The paper presents characteristics of 76 strains of bacteria capable of utilizing nonionic surfactants Cirrasol FP, Cirrasol SF 200 and Cirrasol TCS as the source of carbon. The strains were isolated from two activated sludges adapted to the purification of wastes containing the above compounds at concentration 150--200 mg/l. The isolated strains belonged to the genera: Achromobacter, Alcaligenes, Arthrobacter, Flavobacterium, Mycobacterium, Nocardia, Pseudomonas and Xanthomonas. With load 0.11 mg surfactant/mg d.w./day bacteria belonging to Alcaligenes were dominating. With load 0.18--0.31 mg surfactant/mg d.w./day microorganisms were dominated by Pseudomonas. The highest intensity of degradation of the studied surfactant was shown by species: Alcaligenes viscolactis, Nocardia blackwellii and Pseudomonas rathonis.

Bacteria↗

[Susceptibilities of glucose non-fermentative gram-negative bacilli to antibiotics].

Glucose non-fermentative Gram-negative bacilli are important nosocomial pathogens. This study concerned with susceptibilities to antibacterial agents of strains of Glucose non-fermentative Gram-negative bacilli that were isolated from cultures of clinical materials at 123 hospital laboratories throughout Japan from September to December of 1991. The tests for susceptibilities were performed according to the disk dilution method recommended by NCCLS. The following bacteria were tested: Pseudomonas aeruginosa, Pseudomonas cepacia, Acinetobacter calcoaceticus, Alcaligenes spp., Alcaligenes xylosoxidans, Flavobacterium spp. and Xanthomonas maltophilia. The antibacterial agents tested were as follows: piperacillin (PIPC), ceftazidime (CAZ), aztreonam (AZT), imipenem (IPM), minocycline (MINO), gentamicin, amikacin (AMK) and ofloxacin (OFLX). 1. Eighty percent of the strains of P. aeruginosa and P. cepacia were sensitive to CAZ. More than ninety percent of the strains of A. calcoaceticus were sensitive to IPM, MINO, OFLX. To PIPC and IPM, about eighty percent of the strains of Alcaligenes spp. and A. xylosoxidans were sensitive. The strains of Flavobacterium spp. and X. maltophilia showed high sensitivities to MINO. 2. Annual changes in antimicrobial susceptibility patterns over 4 years (1988-1991) show that there has been a gradual increase in sensitive strains of P. aeruginosa to PIPC, CAZ and AMK. Sensitive strains of P. cepacia to AZT, IPM and MINO, and A. calcoaceticus to CAZ and MINO also have gradually increased. No yearly changes were observed in high sensitivity to MINO of the strains of Flavobacterium spp. and X. maltophilia.

Anti-Bacterial Agents↗

MEDIUM FOR DIFFERENTIATING THE GRAM-NEGATIVE, NONFERMENTING BACILLI OF MEDICAL INTEREST.

Sellers, Walter (U.S. Air Force School of Aerospace Medicine, Brooks Air Force Base, Tex.). Medium for differentiating the gram-negative, nonfermenting bacilli of medical interest. J. Bacteriol. 87:46-48. 1964.-An agar-slant medium is described for differentiating gram-negative, nonfermenting bacilli of medical interest. Differences in the ability of bacilli to grow anaerobically in the presence of nitrate, to produce pH changes, to produce N(2) from nitrite and nitrate (singly and in combination), to fluoresce, and to oxidize a drop of glucose solution to acid in the presence of high peptone concentrations were used in the development of the medium. Organisms differentiated by the medium include Pseudomonas aeruginosa, Bacterium anitratum, Mima polymorpha, and Vibrio alcaligenes or Alcaligenes faecalis.

Acinetobacter↗

A tunable switch to regulate the synthesis of low and high molecular weight microbial polyesters.

The addition of poly(ethylene glycol) (Mn = 200 g/mol) (PEG-200) to the fermentation media of Alcaligenes eutrophus and Alcaligenes latus at various stages of growth resulted in the synthesis of poly(3-hydroxybutyrate) (PHB) with bimodal molecular weight distributions. The presence of 2% w/v-PEG-200 did not have deleterious effects on PHB volumetric yields and cell productivity. In general, the Mn values of the high (H) and low (L) fractions showed little variability as a function of the time at which PEG-200 was added to the cultures. By this approach, the H:L ratios (w/w) of the PHB synthesized by A. eutrophus and A. latus were varied from 9:91 to 76:24 and from 16:84 to 88:12, respectively. It is believed that the H fractions were formed prior to the addition of PEG-200 to the cultures. Also, once PEG-200 was made available to the cells, PEG-200 acted as a switch so that the reduced molecular weight fraction was formed. In addition, a necessary requirement for the above is that the frequency of transesterification reactions during polymer synthesis was small. The efficiency that PEG-200 reduced the molecular weight of the PHBs formed by both bacteria appears similar. Indirect evidence suggests that the PHB L fractions formed by A. latus subsequent to PEG-200 addition consist primarily of chains that have PEG terminal groups. This terminal chain structure was not observed for PHB formed by A. eutrophus.

Alcaligenes↗

Localization and stability of hydrogenases from aerobic hydrogen bacteria.

Alcaligenes eutrophus strains H 16, B 19, G 27 and N9A contained two different hydrogenases. One enzyme catalyzed the reduction of NAD by hydrogen and was strictly localized in the soluble cell fraction. While the second enzyme was found to be particulate and unable to react with NAD. All other tested strains, Alcaligenes paradoxus SA 29, Pseudomonas facilis, P. palleronii RH 2, Pseudomonas sp. strain GA 3, Paracoccus denitrificans, Aquaspirillum autotrophicum SA 32, and Corynebacterium autotrophicum 14g and 7C contained only a single enzyme exclusively bound to membranes. This was established using fractional centrifugation, indicator enzyme systems, gently methods of cell disintegration and discontinuous sucrose density gradient centrifugation. In cell-free extracts obtained by rough disruption (sonication) of cells, hydrogenase was associated to particles of different size and sedimentation velocity. A partial solubilization of hydrogenase caused by sonication was observed with P. facilis. Without exception, the particulate hydrogenases were found (1) to be unable to reduce pyridine nucleotides, and (2) to reduce methylene blue at an extremely high activity. The eminent reaction rate of 34 micronmoles H2 oxidized per min and mg protein has been determined in particle suspensions of Pseudomonas sp. strain GA 3. All hydrogenases were stable during storage under hydrogen atmosphere, except the soluble enzyme for A. eutrophus H 16 which was shown to be more stable under aerobic conditions.

Aerobiosis↗

Autecological properties of 3-chlorobenzoate-degrading bacteria and their population dynamics when introduced into sediments.

Ecologically significant properties of wild-type and genetically engineered bacteria capable of degrading 3-chlorobenzoate (3-CB) were compared in the laboratory, and isolates were introduced into streambed sediments in microcosms to observe their population dynamics. 3-CB metabolism, growth on algal extract, temperature optima, and ingestion by protozoa were ecological properties considered relevant to the persistence of these bacteria if introduced into nature. Cell-specific Vmax for 3-CB metabolism and cell-specific mineralization rates each spanned approximately 2 orders of magnitude, but isolates did not rank consistently. The Ks for 3-CB metabolism for Alcaligenes sp. BR60 was approximately 40-fold lower than the mean value for the other isolates, which differed only approximately 4-fold among themselves. All isolates grew on an algal extract nearly as well as on tryptone-yeast extract, implying potential for survival on natural metabolic substrates in situ. Most isolates had temperature optima that were 3-15 degrees C higher than maximum stream water temperature (22 degrees C). Ciliates preferentially ingested P. acidovorans M3GY, and either P. putida RC-4(pSI30) or its parent strain were least preferred, but microflagellates did not exhibit consistent preferences. Fluorescent antibodies were prepared against isolates to permit detection of target cells in natural communities. In three different microcosm experiments the cell densities of introduced isolates declined over a period of days. In one experiment, 3-CB additions (100 mg/L) led to increases of P. alcaligenes C-0 and P. acidovorans M3GY cell densities within 1 day, although P. putida RC-4(pSI30) took 4 days. In a second experiment, the persistence of P. putida RC-4(pSI30) and its parent strain P. putida RC-4 were compared and rates of initial population decline were not statistically different. 3-CB addition stimulated the growth of other organisms while densities of the P. putida strains further declined. In a third experiment exposure to 100 mg 3-CB/L slowed the rate of decline of P. acidovorans M3GY densities compared to a 10 mg/L concentration or unamended control. Competition with the native flora was a significant factor affecting the persistence of introduced 3-CB degraders.

Alcaligenes↗

Regioselective hydroxylation of quinolinic acid, lutidinic acid and isocinchomeronic acid by resting cells of pyridine dicarboxylic acid-degrading microorganisms.

Microorganisms aerobically degrading quinolinic acid, lutidinic acid or isocinchomeronic acid were isolated and the microbial regioselective hydroxylation of these pyridine dicarboxylic acids was studied. Alcaligenes sp. UK21 cells converted quinolinic acid into 6-hydroxypicolinic acid, suggesting the involvement of two enzyme reactions catalyzing hydroxylation at position C6 and decarboxylation at position C3 of quinolinic acid. Resting cells of Alcaligenes sp. UK21 accumulated 94.9 mM 6-hydroxypicolinic acid (13.2 g l(-1)), with a 96% molar conversion yield by 48 h incubation. Rhizobium sp. LA17 and Hydrogenophaga sp. IMA01 catalyzed the regioselective hydroxylation of lutidinic acid and isocinchomeronic acid into 6-hydroxylutidinic acid and 6-hydroxyisocinchomeronic acid, respectively. 6-Hydroxylutidinic acid accumulated up to 95.4 mM (17.5 g l(-1)) by 24 h incubation in the resting cells reaction, using Rhizobium sp. LA17, with a 99% molar conversion yield. Resting cells of Hydrogenophaga sp. IMA01 produced 88.7 mM 6-hydroxyisocinchomeronic acid (16.2 g l(-1)) by 24 h incubation, with a 81% molar conversion yield.

Alcaligenes↗

Molecular cloning and characterization of catechol 2,3-dioxygenases from biphenyl/polychlorinated biphenyls-degrading bacteria.

Catechol 2,3-dioxygenases were cloned from Alcaligenes sp. KF711, Pseudomonas putida KF715, and Achromobacter xylosoxidans KF701 which are biphenyl/polychlorinated biphenyls-degrading bacteria. All of the cloned enzymes were purified by preparative polyacrylamide gel electrophoresis (PAGE). The purified catechol 2,3-dioxygenases were significantly different from one another in ring-fission activities to catechol and its derivatives. The catechol 2,3-dioxygenase from Alcaligenes sp. KF711 exhibited higher ring-fission activity to 4-chlorocatechol than those from P. putida KF715 and A. xylosoxidans KF701. In electrophoretic mobilities, the three enzymes were different from one another on nondenaturing PAGE but the same on SDS-PAGE.

Alcaligenes↗

Use of DNA probes and plasmid capture in a search for new interesting environmental genes.

Adaptation to a stressed environment leads to organisms bearing DNA, encoding defense mechanisms. These mechanisms can be heavy metal resistance, catabolism of organic xenobiotics or stress reactions. Genes responsible for these mechanisms can be used for monitoring changing environments and therefore it can be important to store such bacteria in a bank. DNA-probing will be presented by the use of DNA fragments (of Alcaligenes eutrophus) coding for heavy metal resistance or xenobiotic degradation. Some strains do not grow on petri dishes and accordingly cannot be isolated from soils. In order to isolate plasmids from such strains, coding for heavy metal resistances or xenobiotic degradations, an exogenous plasmid isolation method was developed. In this method, the endogenous population is conjugated with Pseudomonas or Alcaligenes strains bearing a retrotransfer plasmid like RP4. In that way new plasmids from various sources including non-culturable strains could be obtained. With these methods, a large number of specimens adapted to stressed situations can be isolated or constructed (in the case of the exogenous plasmid isolation method). They form a source of interesting genetic material that can be used to restore polluted areas in natural areas, if necessary with the aid of genetic engineering (in vitro or in vivo techniques). Full knowledge of such bacteria and their resistance mechanisms or degradation pathways, can lead to new constructions able to attack recalcitrant mixtures of different organics and to resist heavy metals.

Alcaligenes↗

Site-directed mutagenesis alters DnaK-dependent folding process.

The overproduction of d-aminoacylase (A6-d-ANase) of Alcaligenes xylosoxydans subsp. xylosoxydans A-6 (Alcaligenes A-6) is accompanied by aggregation of the overproduced protein, and its soluble expression is facilitated by the coexpression of DnaK-DnaJ-GrpE (DnaKJE). When the A6-d-ANase gene was expressed in the Escherichia coli dnaK mutant dnaK756, little activity was observed in the soluble fraction, and it was restored by the coexpression of DnaKJE or the substitution of the R354 residue of A6-d-ANase for lysine. These results suggest that the guanidino group of the R354 residue of A6-d-ANase disturbs its proper folding in the absence of DnaK and the disturbance is eliminated by binding of DnaK to the R354 residue in the presence of DnaK. This is the first report that the DnaK-dependent folding process of the enzyme is altered by site-directed mutagenesis.

Alcaligenes↗

The cis-diol dehydrogenase cbaC gene of Tn5271 is required for growth on 3-chlorobenzoate but not 3,4-dichlorobenzoate.

The nucleotide sequence of cbaC, the 1-carboxy-3-chloro-4,5-dihydroxycyclohexa-2,6-diene (cis-diol) dehydrogenase gene from the 3-chlorobenzoate (3-Cba) catabolic transposon Tn5271 was determined. The functional significance of the deduced open reading frame was evaluated by deletion of an internal BstEII restriction site in cbaC and by the creation of nested deletions using exonuclease III. Expression studies were carried out with Alcaligenes sp. strain BR6024, a chloramphenicol-resistant, tryptophan auxotroph derived from the wild-type isolate BR60. BR6024 hosts carrying complete cbaAB (3-Cba 3,4-(4,5)-dioxygenase and reductase) genes, with deletions of cbaC, metabolized 3Cba to the cis-4,5-diol metabolite. These mutants failed to grow on 3-Cba; however, they grew on 3,4-dichlorobenzoate, accumulating 5-chloroprotocatechuate transiently. These results indicated the cbaC dehydrogenase was not required for re-aromatization of the unstable 3,4-dCba cis-4,5-diol metabolite. Spontaneous elimination of HCl from this metabolite is proposed to generate 5-chloroprotocatechuate, which is a substrate for the protocatechuate metaring fission pathway in Alcaligenes sp. BR60. The relationship of the deduced amino acid sequence of cbaC with 15 other oxidoreductases and sequences of unknown function from bacteria, plants and animals revealed a conserved N-terminal GxxGxG dinucleotide-binding domain and a conserved region with a H(x11)KHVLxEKPxA consensus flanked by alpha-helical domains. o-Phthalate cis-diol dehydrogenase (Pseudomonas putida), glucose-fructose oxidoreductase (Zymomonas mobilis), myo-inositol-2-dehydrogenase (Bacillus subtilis) and D-galactose-1-dehydrogenase (Pseudomonas fluorescens) are related proteins. These dehydrogenases are unrelated to the Type I, II and III dehydrogenase superfamilies that include the cis-diol dehydrogenases involved in benzoate, toluene, biphenyl and naphthalene catabolism (Type II) and benzene catabolism (Type III).

Alcaligenes↗