Naphthalene and phenanthrene are transformed by enzymes encoded by the pah gene cluster ofPseudomonas putida OUS82. The pahA and pahB genes, which encode the first and second enzymes, dioxygenase and cis-dihydrodiol dehydrogenase, respectively, were identified and sequenced. The DNA sequences showed that pahA and pahB were clustered and that pah/A consisted of four cistrons, pah/Aa paMAb, pahAc, and pahAd, which encode ferredoxin reductase, ferredoxin, and two subunits of the iron-sulfur protein, respectively.Pseudomonas putida OUS82 can assimilate naphthalene and phenanthrene as its sole carbon sources. The strain converts naphthalene and phenanthrene to salicylate and 1-hydroxy-2-naphthoate, respectively, by a shared catabolic pathway (the upper pathway; Fig. 1). Salicylate and 1-hydroxy-2-naphthoate are further degraded by other catabolic enzymes. The enzymes in the upper pathway have broad substrate specificities, and various polycyclic aromatic hydrocarbons other than naphthalene and phenanthrene are oxidized by a high-density suspension of OUS82 cells (9).Previously, we cloned the gene cluster encoding the enzymes of the upper pathway and named it pah (polycyclic aromatic hydrocarbon; 9). The pah region strongly hybridized to a corresponding region of plasmid NAH7 of P. putida G7, which degrades naphthalene (4). All recombinant plasmids carrying pahA have 6.5-and 3.0-kb Sall fragments. The two fragments were seen to be necessary for the dioxygenase phenotype (PahA). A restriction endonuclease map of a region in the fragments resembles that of the nahA region of NAH7 and pDTG1 in P. putida G7 and NCIB 9816-4, which degrade naphthalene (2, 4, 23). The pahA gene was expected to be in that region.Here, we describe the identification and characterization of the pahA and pahB genes, which encode dioxygenase PahA, which is the first enzyme of the pathway and converts polycyclic aromatic hydrocarbon (PAH) to the corresponding cis-dihydrodiol, and dehydrogenase PahB, the second enzyme of the pathway, which converts the product of PahA to the corresponding diol. P. putida OUS8211 (trp-82 Apah-821), a derivative of strain OUS82 that is defective in naphthalene and phenanthrene utilization, and plasmid pDIl, which carries the pahAB gene cluster, were described previously (9). Plasmid NAH7 was described elsewhere (4, 5). Escherichia coli JM109 and plasmid pUC119 were described by Yanisch-Perron et al. (21)

A 25-kb DNA SalI fragment cloned from the chromosomal DNA of Pseudomonas putida OUS82, which utilizes phenanthrene (Phn+) and naphthalene (Nah+), carried all of the genes necessary for upper naphthalene catabolism. Cosmid recombinant pIP7 complemented both the Nah- and Phn- defects of OUS8211 (Trp-Nah-Phn-Sal+[salicylate utilizing]Hna+[1-hydroxy-2-naphthoate utilizing]) and only the Phn- defect of OUS8212 (Trp-Nah-Phn-Sal-Hna+). The results indicate that strain OUS82 uses different pathways after o-hydroxycarboxylic aromatics in the catabolism of naphthalene and phenanthrene.

No abstract

Three strains of Pseudomonas pickettii that can grow with 2,4,6-trichlorophenol (2,4,6-TCP) as the sole source of carbon and energy were isolated from different mixed cultures of soil bacterial populations that had been acclimatized to 2,4,6-TCP. These strains released 3 mol of chloride ion from 1 mol of 2,4,6-TCP during the complete degradation of the TCP. Of these strains, P. pickettii DTP0602 in high-cell-density suspension cultures dechlorinated various chlorophenols (CPs). Cells that were preincubated with 2,4,6-TCP converted isomers of 4-CP to the corresponding chloro-p-hydroquinones, but those preincubated with 4-CP converted CPs lacking a chlorine atom(s) at the o position to isomers of chlorocatechol. The ability of DTP0602 to dechlorinate 2,4,6-TCP was induced by 2,6-dichlorophenol, 2,3,6- and 2,4,6-TCP, and 2,3,4,6-tetrachlorophenol and was repressed in the presence of succinate or glucose.

We determined the entire nucleotide sequence of the Klebsiella aerogenes W70 pullulanase gene (pulA) contained on a 4.2-kilobase-pair fragment of plasmid pPB174. The amino acid composition deduced from an open reading frame of 3,288 base pairs agreed closely with that determined for the intracellular pullalanase. The precursor enzyme consisted of 1,096 amino acid residues and contained a hydrophobic N-terminal signal peptide and the consensus sequence for the bacterial prelipoprotein signal peptide cleavage site.Pullulanase (EC 3.2.1.41, pullulan 6-glucanohydrolase), a starch-debranching enzyme, hydrolyzes (1-6)-a-glucosidic linkages in pullulan and starch to form maltotriose. This enzyme is produced by the gram-negative bacterium Kleb-0 1.0 genes W70 (19). We sequenced the entire pullulanase gene (pulA) and showed that the precursor enzyme contained N-terminal signal peptide. The precursor and mature proteins deduced from the DNA sequence showed a high degree

No abstract

Most studies of bacterial denitrification have used nitrate (NO 3؊ ) as the first electron acceptor, whereas relatively less is understood about nitrite (NO 2 ؊ ) denitrification. We isolated novel bacteria that proliferated in the presence of high levels of NO 2 ؊ (72 mM T proliferated even in the presence of higher levels of NO 2 ؊ (100 mM), and both were considerably more resistant to acidic NO 2 ؊ than were the other strains noted above. These results indicated that O. anthropi YD50.2 is a novel denitrifier that has evolved reactive nitrogen oxide tolerance mechanisms.Environmental bacteria maintain the global nitrogen cycle by metabolizing organic and inorganic nitrogen compounds. Denitrification is critical for maintenance of the global nitrogen cycle, through which nitrate (NO 3 Ϫ ) or nitrite (NO 2 Ϫ ) is reduced to gaseous nitrogen forms such as N 2 and nitrous oxide (N 2 O) (19, 47). Decades of investigations into denitrifying bacteria have revealed their ecological impact (9), their molecular mechanisms of denitrification (13,25,47), and the industrial importance of removing nitrogenous contaminants from wastewater (31, 36). Bacterial denitrification is considered to comprise four successive reduction steps, each of which is catalyzed by NO 3 Ϫ reductase (Nar), NO 2 Ϫ reductase (Nir), nitric oxide (NO) reductase (Nor), and N 2 O reductase (Nos). The reaction of each enzyme is linked to the electron transport chain on the cellular membrane and accompanies oxidative phosphorylation, implying that bacterial denitrification is of as much physiological significance as anaerobic respiration (25, 47). Most denitrifying bacteria are facultative anaerobes and respire with oxygen under aerobic conditions. Because denitrification is induced in the absence of oxygen, it is considered an alternative mechanism of energy conservation that has evolved as an adaptation to anaerobic circumstances (13, 47).Nitrite and NO are hazardous to bacteria, since they generate highly reactive nitrogen species (RNS) under physiological conditions and damage cellular DNA, lipid, and proteins (28,37). Denitrifying bacteria are thought to be threatened by RNS since they reduce NO 3 Ϫ to generate NO 2 Ϫ and NO as denitrifying intermediates. Furthermore, denitrifying bacteria often inhabit environments where they are exposed to NO 2 Ϫ and NO and hence high levels of RNS. Recent reports suggest that pathogenic bacteria invading animal tissues are attacked by NO generated by macrophages (12). Such bacteria involve denitrifiers, and some of them, for example, Neisseria meningitidis (1) and Pseudomonas aeruginosa, acquire resistance to NO by producing Nor (44). The utilization (reduction) of NO by Brucella increases the survival of infected mice (2). These examples suggest that production of a denitrifying mechanism affects bacterial survival of threats from both endogenous and extracellular RNS. However, the mechanism of RNS tolerance induced by denitrifying bacteria is not fully understood.Ubiquitous gram-negative Ochrobactrum strains ar...

The host range of coliphage Mu was greatly expanded to various genera of gram-negative bacteria by using the hybrid plasmid RP4::Mu cts, which is temperature sensitive and which confers resistance to ampicillin, kanamycin, and tetracycline. These drug resistance genes were transferred from Escherichia coli to members of the genera Klebsiella, Enterobacter, Citrobacter, Salmonella, Proteus, Erwinia, Serratia, Alcaligenes, Agrobacterium, Rhizobium, Pseudomonas, Acetobacter, and Bacillus. Mu phage was produced by thermal induction from the lysogens of all these drug-resistant bacteria except Bacillus. Mu phage and RP4 or the RP4: :Mu plasmid were used to create intergeneric recombinant strains by transfer of some genes, including the arylsulfatase gene, between Klebsiella aerogenes and E. coli. Thus, genetic analysis and intergeneric gene transfer are possible in these RP4: :Mu-sensitive bacteria.