Construction of an engineered strain free of antibiotic resistance gene markers for simultaneous mineralization of methyl parathion and ortho-nitrophenol

Pseudomonas sp. strain NyZ402, a native soil organism that grows on para-nitrophenol (PNP), was genetically engineered for the simultaneous degradation of methyl parathion (MP) and ortho-nitrophenol (ONP) by integrating mph (methyl parathion hydrolase gene) from Pseudomonas sp. strain WBC-3 and onpAB (ONP 2-monooxygenase and ONP o-benzoquinone reductase genes) from Alcaligenes sp. strain NyZ215 into the genome of strain NyZ402. Methyl parathion hydrolase (MPH), ONP 2-monooxygenase (OnpA) and o-benzoquinone reductase (OnpB) were constitutively expressed in the engineered strain NyZ-MO. Strain NyZ-MO was free of exogenous antibiotic resistance gene markers and the introduced genes were genetically stable. Degradation experiments showed that strain NyZ-MO could utilize MP or ONP as the sole carbon and energy source, and mineralize 0.1 mM MP–0.1 mM ONP simultaneously. This method may serve as a useful strategy for the construction of engineered strains in the degradation of multiple environmental pollutants.     

<Emphasis Type="Italic">para</Emphasis>-Nitrophenol 4-monooxygenase and hydroxyquinol 1,2-dioxygenase catalyze sequential transformation of 4-nitrocatechol in <Emphasis Type="Italic">Pseudomonas</Emphasis> sp. strain WBC-3

Pseudomonas sp. strain WBC-3 utilizes para-nitrophenol (PNP) as a sole source of carbon, nitrogen and energy. PnpA (PNP 4-monooxygenase) and PnpB (para-benzoquinone reductase) were shown to be involved in the initial steps of PNP catabolism via hydroquinone. We demonstrated here that PnpA also catalyzed monooxygenation of 4-nitrocatechol (4-NC) to hydroxyquinol, probably via hydroxyquinone. It was the first time that a single-component PNP monooxygenase has been shown to catalyze this conversion. PnpG encoded by a gene located in the PNP degradation cluster was purified as a His-tagged protein and identified as a hydroxyquinol dioxygenase catalyzing a ring-cleavage reaction of hydroxyquinol. Although all the genes necessary for 4-NC metabolism seemed to be present in the PNP degradation cluster in strain WBC-3, it was unable to grow on 4-NC as a sole source of carbon, nitrogen and energy. This was apparently due to the substrate’s inability to trigger the expression of genes involved in degradation. Nevertheless, strain WBC-3 could completely degrade both PNP and 4-NC when PNP was used as the inducer, demonstrating its potential in bioremediation of the environment polluted by both 4-NC and PNP.     

Genes Involved in Degradation of para-Nitrophenol Are Differentially Arranged in Form of Non-Contiguous Gene Clusters in Burkholderia sp. strain SJ98

Biodegradation of para-Nitrophenol (PNP) proceeds via two distinct pathways, having 1,2,3-benzenetriol (BT) and hydroquinone (HQ) as their respective terminal aromatic intermediates. Genes involved in these pathways have already been studied in different PNP degrading bacteria. Burkholderia sp. strain SJ98 degrades PNP via both the pathways. Earlier, we have sequenced and analyzed a ~41 kb fragment from the genomic library of strain SJ98. This DNA fragment was found to harbor all the lower pathway genes; however, genes responsible for the initial transformation of PNP could not be identified within this fragment. Now, we have sequenced and annotated the whole genome of strain SJ98 and found two ORFs (viz., pnpA and pnpB) showing maximum identity at amino acid level with p-nitrophenol 4-monooxygenase (PnpM) and p-benzoquinone reductase (BqR). Unlike the other PNP gene clusters reported earlier in different bacteria, these two ORFs in SJ98 genome are physically separated from the other genes of PNP degradation pathway. In order to ascertain the identity of ORFs pnpA and pnpB, we have performed in-vitro assays using recombinant proteins heterologously expressed and purified to homogeneity. Purified PnpA was found to be a functional PnpM and transformed PNP into benzoquinone (BQ), while PnpB was found to be a functional BqR which catalyzed the transformation of BQ into hydroquinone (HQ). Noticeably, PnpM from strain SJ98 could also transform a number of PNP analogues. Based on the above observations, we propose that the genes for PNP degradation in strain SJ98 are arranged differentially in form of non-contiguous gene clusters. This is the first report for such arrangement for gene clusters involved in PNP degradation. Therefore, we propose that PNP degradation in strain SJ98 could be an important model system for further studies on differential evolution of PNP degradation functions.     

Molecular characterization of a novel ortho-nitrophenol catabolic gene cluster in Alcaligenes sp. strain NyZ215

Alcaligenes sp. strain NyZ215 was isolated for its ability to grow on ortho-nitrophenol (ONP) as the sole source of carbon, nitrogen, and energy and was shown to degrade ONP via a catechol ortho-cleavage pathway. A 10,152-bp DNA fragment extending from a conserved region of the catechol 1,2-dioxygenase gene was obtained by genome walking. Of seven complete open reading frames deduced from this fragment, three (onpABC) have been shown to encode the enzymes involved in the initial reactions of ONP catabolism in this strain. OnpA, which shares 26% identity with salicylate 1-monooxygenase of Pseudomonas stutzeri AN10, is an ONP 2-monooxygenase (EC 1.14.13.31) which converts ONP to catechol in the presence of NADPH, with concomitant nitrite release. OnpC is a catechol 1,2-dioxygenase catalyzing the oxidation of catechol to cis,cis-muconic acid. OnpB exhibits 54% identity with the reductase subunit of vanillate O-demethylase in Pseudomonas fluorescens BF13. OnpAB (but not OnpA alone) conferred on the catechol utilizer Pseudomonas putida PaW340 the ability to grow on ONP. This suggests that OnpB may also be involved in ONP degradation in vivo as an o-benzoquinone reductase converting o-benzoquinone to catechol. This is analogous to the reduction of tetrachlorobenzoquinone to tetrachlorohydroquinone by a tetrachlorobenzoquinone reductase (PcpD, 38% identity with OnpB) in the pentachlorophenol degrader Sphingobium chlorophenolicum ATCC 39723.     

A Two-Component para-Nitrophenol Monooxygenase Initiates a Novel 2-Chloro-4-Nitrophenol Catabolism Pathway in Rhodococcus imtechensis RKJ300

Rhodococcus imtechensis RKJ300 (DSM 45091) grows on 2-chloro-4-nitrophenol (2C4NP) and para-nitrophenol (PNP) as the sole carbon and nitrogen sources. In this study, by genetic and biochemical analyses, a novel 2C4NP catabolic pathway different from those of all other 2C4NP utilizers was identified with hydroxyquinol (hydroxy-1,4-hydroquinone or 1,2,4-benzenetriol [BT]) as the ring cleavage substrate. Real-time quantitative PCR analysis indicated that the pnp cluster located in three operons is likely involved in the catabolism of both 2C4NP and PNP. The oxygenase component (PnpA1) and reductase component (PnpA2) of the two-component PNP monooxygenase were expressed and purified to homogeneity, respectively. The identification of chlorohydroquinone (CHQ) and BT during 2C4NP degradation catalyzed by PnpA1A2 indicated that PnpA1A2 catalyzes the sequential denitration and dechlorination of 2C4NP to BT and catalyzes the conversion of PNP to BT. Genetic analyses revealed that pnpA1 plays an essential role in both 2C4NP and PNP degradations by gene knockout and complementation. In addition to catalyzing the oxidation of CHQ to BT, PnpA1A2 was also found to be able to catalyze the hydroxylation of hydroquinone (HQ) to BT, revealing the probable fate of HQ that remains unclear in PNP catabolism by Gram-positive bacteria. This study fills a gap in our knowledge of the 2C4NP degradation mechanism in Gram-positive bacteria and also enhances our understanding of the genetic and biochemical diversity of 2C4NP catabolism.     

Biodegradation of p-nitrophenol by Pseudomonas aeruginosa HS-D38 and analysis of metabolites with HPLC–ESI/MS

Pseudomonas aeruginosa strain HS-D38 was capable of mineralizing p-nitrophenol (PNP) as the sole source of carbon, nitrogen and energy. Degradation of 200 mg L^?1 PNP was examined in different media including: (i) MSM (mineral salts medium, no carbon and nitrogen source); (ii) addition of 1% ammonium chloride as additional nitrogen source (ANM); and (iii) addition of 1% glucose as a carbon source (ACM). Complete degradation of 200 mg L^?1 PNP was achieved in 12 h in MSM. Additional ammonium chloride accelerated the PNP degradation, but additional glucose inhibited this process. This strain metabolized as high concentration as 300 and 500 mg L^?1 of PNP in 14 h and 24 h, respectively, in MSM. The degradation was accompanied by release of stoichiometric amount of nitrate from PNP. During the bacterial growth on PNP, hydroquinone and 1,2,4-benzenetriol were observed as the key degradation intermediates by using a combination of techniques, including HPLC–DAD and LC–ESI/MS compared with the authentic standards. These results indicated that PNP was degraded via a hydroquinone pathway.     

Degradation and induction specificity in actinomycetes that degrade p-nitrophenol.

We have isolated two soil bacteria (identified as Arthrobacter aurescens TW17 and Nocardia sp. strain TW2) capable of degrading p-nitrophenol (PNP) and numerous other phenolic compounds. A. aurescens TW17 contains a large plasmid which correlated with the PNP degradation phenotype. Degradation of PNP by A. aurescens TW17 was induced by preexposure to PNP, 4-nitrocatechol, 3-methyl-4-nitrophenol, or m-nitrophenol, whereas PNP degradation by Nocardia sp. strain TW2 was induced by PNP, 4-nitrocatechol, phenol, p-cresol, or m-nitrophenol. A. aurescens TW17 initially degraded PNP to hydroquinone and nitrite. Nocardia sp. strain TW2 initially converted PNP to hydroquinone or 4-nitrocatechol, depending upon the inducing compound.     

Biodegradation of 3-nitrotoluene by Rhodococcus sp. strain ZWL3NT

A pure bacterial culture was isolated by its ability to utilize 3-nitrotoluene (3NT) as the sole source of carbon, nitrogen, and energy for growth. Analysis of its 16S rRNA gene showed that the organism (strain ZWL3NT) belongs to the genus Rhodococcus. A rapid disappearance of 3NT with concomitant release of nitrite was observed when strain ZWL3NT was grown on 3NT. The isolate also grew on 2-nitrotoluene, 3-methylcatechol and catechol. Two metabolites, 3-methylcatechol and 2-methyl-cis,cis-muconate, in the reaction mixture were detected after incubation of cells of strain ZWL3NT with 3NT. Enzyme assays showed the presence of both catechol 1,2-dioxygenase and catechol 2,3-dioxygenase in strain ZWL3NT. In addition, a catechol degradation gene cluster (catRABC cluster) for catechol ortho-cleavage pathway was cloned from this strain and cell extracts of Escherichia coli expressing CatA and CatB exhibited catechol 1,2-dioxygenase activity and cis,cis-muconate cycloisomerase activity, respectively. These experimental evidences suggest a novel pathway for 3NT degradation with 3-methylcatechol as a key metabolite by Rhodococcus sp. strain ZWL3NT.     

Effects of organic compounds on the degradation ofp-nitrophenol in lake and industrial wastewater by inoculated bacteria

Many microorganisms fail to degrade pollutants when introduced in different natural environments. This is a problem in selecting inocula for bioremediation of polluted sites. Thus, a study was conducted to determine the success of four inoculants to degradep-nitrophenol (PNP) in lake and industrial wastewater and the effects of organic compounds on the degradation of high and low concentrations of PNP in these environments.Corynebacterium strain Z4 when inoculated into the lake and wastewater samples containing 20 µg/ml of PNP degraded 90% of PNP in one day. Addition of 100 µg/ml of glucose as a second substrate did not enhance the degradation of PNP and the bacterium utilized the two substrates simultaneously. Glucose used at the same concentration (100 µg/ml), inhibited degradation of 20 µg of PNP in wastewater byPseudomonas strain MS. However, glucose increased the extent of degradation of PNP byPseudomonas strain GR. Phenol also enhanced the degradation of PNP in wastewater byPseudomonas strain GR, but had no effect on the degradation of PNP byCorynebacterium strain Z4.Addition of 100 µg/ml of glucose as a second substrate into the lake water samples containing low concentration of PNP (26 ng/ml) enhanced the degradation of PNP and the growth ofCorynebacterium strain Z4. In the presence of glucose, it grew from 2×10⁴ to 4×10⁴ cells/ml in 3 days and degraded 70% of PNP as compared to samples without glucose in which the bacterium declined in cell number from 2×10⁴ to 8×10³ cells/ml and degraded only 30% PNP. The results suggest that in inoculation to enhance biodegradation, depending on the inoculant, second organic substrate many play an important role in controlling the rate and extent of biodegradation of organic compounds.Abbreviations PNP p-nitrophenol     

Construction of an engineered strain capable of degrading two isomeric nitrophenols via a sacB- and gfp-based markerless integration system

In this study, a gfp-based novel markerless allelic exchange integration system was developed. By employing gfp gene and sacB gene as counter-selectable markers, an ortho-nitrophenol degradation operon (onpABC gene cluster) was successfully inserted into the chromosome of meta-nitrophenol utilizer Cupriavidus necator JMP134. Through two rounds of recombination, the engineered strain (strain JMP134-ONP) was directly selected from the plate by fluorescence screening and has the ability to degrade both ortho-nitrophenol and meta-nitrophenol, simultaneously. This relatively simple and efficient method can be used as an alternative strategy of allelic exchange insertion for the application of metabolic engineering in various bacterial strains, complementary to existing gene knock-in procedures.     

Co-metabolic degradation of tribenuron methyl,a sulfonylurea herbicide,by Pseudomonas sp. strain NyZ42

A co-metabolic degradation of tribenuron methyl bacterial strain NyZ42 was isolated from polluted agricultural soil and classified as genus Pseudomonas by its 16S rRNA gene sequencing. The degradation efficiency of tribenuron methyl was about 80% of the originally supplemented 200 mg l⁻¹ tribenuron methyl in liquid minimal medium within four days, when either glucose or succinate was used as a supplemental carbon source. Three intermediates formed during the degradation of tribenuron methyl mediated by strain NyZ42 were captured by LC-MS, and two alternative pathways were proposed for the microbial mediated tribenuron methyl degradation, via either cleavage of the sulfonylurea bridge or saponification of alkyl-group. Furthermore, inoculation of strain NyZ42 enhanced the degradation of tribenuron methyl in the sterilized soil samples, although the biodegradation/co-metabolism ability of NyZ42 was not obvious in the nonsterilized soil samples when compared with the indigenous microbial consortium under current laboratory conditions.     

Biodegradation of p-nitrophenol by methyl parathion-degrading Ochrobactrum sp. B2

Ochrobactrum sp. B2, a methyl parathion-degrading bacterium, was proved to be capable of using p-nitrophenol (PNP) as carbon and energy source. The effect of factors, such as temperature, pH value, and nutrition, on the growth of Ochrobactrum sp. B2 and its ability to degrade p-nitrophenol (PNP) at a higher concentration (100 mg l⁻¹) was investigated in this study.The greatest growth of B2 was observed at a temperature of 30 °C and alkaline pH (pH 9–10). pH condition was proved to be a crucial factor affecting PNP degradation. Enhanced growth of B2 or PNP degradation was consistent with the increase of pH in the minimal medium, and acidic pH (6.0) did not support PNP degradation. Addition of glucose (0.05%, 0.1%) decreased the rate of PNP degradation even if increased cell growth occurred. Addition of supplemental inorganic nitrogen (ammonium chloride or ammonium sulphate) inhibited PNP degradation, whereas organic nitrogen (peptone, yeast extract, urea) accelerated degradation.     

Improved degradation of 4-chlorobiphenyl, 2,3-dihydroxybiphenyl, and catecholic compounds by recombinant bacterial strains

ThepcbC gene encoding (4-chloro-)2,3-dihydroxybiphenyl dioxygenase was cloned from the genomic DNA ofPseudomonas sp. P20 using pKT230 to construct pKK1. A recombinant strain,E. coli KK1, was selected by transforming the pKK1 intoE. coli XL1-Blue. Another recombinant strain,Pseudomonas sp. DJP-120, was obtained by transferring the pKK1 ofE. coli KK1 intoPseudomonas sp. DJ-12 by conjugation. Both recombinant strains showed a 23.7 to 26.5 fold increase in the degradation activity to 2,3-dihydroxybiphenyl compared with that of the natural isolate,Pseudomonas sp. DJ-12. The DJP-120 strain showed 24.5, 3.5, and 4.8 fold higher degradation activities to 4-chlorobiphenyl, catechol, and 3-methylcatechol than DJ-12 strain, respectively. The pKK1 plasmid of both strains and their ability to degrade 2,3-dihydroxybiphenyl were stable even after about 1,200 generations.     

The in vivo construction of 4-chloro-2-nitrophenol assimilatory bacteria

Pseudomonas sp. N31 was isolated from soil using 3-nitrophenol and succinate as sole source of nitrogen and carbon respectively. The strain expresses a nitrophenol oxygenase and can use either 2-nitrophenol or 4-chloro-2-nitrophenol as a source of nitrogen, eliminating nitrite, and accumulating catechol and 4-chlorocatechol, respectively. The catechols were not degraded further. Strains which are able to utilize 4-chloro-2-nitrophenol as a sole source of carbon and nitrogen were constructed by transfer of the haloaromatic degrading sequences from either Pseudomonas sp. B13 or Alcaligenes eutrophus JMP134 (pJP4) to strain N31. Transconjugant strains constructed using JMP134 as the donor strain grew on 3-chlorobenzoate but not on 2,4-dichlorophenoxyacetate. This was due to the non-induction of 2,4-dichlorophenoxyacetate monooxygenase and 2,4-dichlorophenol hydroxylase. Transfer of the plasmid from the 2,4-dichlorophenoxyacetate negative transconjugant strains to a cured strain of JMP134 resulted in strains which also had the same phenotype. This indicates that a mutation has occurred in pJP4 to prevent the expression of 2,4-dichlorophenoxyacetate monooxygenase and 2,4-dichlorophenol hydroxylase.     

Characterization and comparison of putative Stenotrophomonas maltophilia methyl parathion hydrolases

Three Stenotrophomonas maltophilia isolates, KKWT11, CBF10-1, TTF10, were collected from organophosphate (OP)-contaminated soil in the Houston metropolitan area. A conserved metallo-β-lactamase (MBL) enzyme purported to function as a methyl parathion hydrolase was identified and found to be distantly homologous to the characterized Pseudomonas sp. WBC-3 methyl parathion hydrolase and shared no significant homology with other organophosphate hydrolases. Following expression of MBL enzymes cloned from S. maltophilia strains KKWT11, CBF10-1, and TTF10, respectively, an enzymatic preference for paraoxon was observed, with concentrations of 70, 40, and 30 µM of p-nitrophenol (PNP) formed after 48 h. Comparatively limited hydrolysis against the phosphorothioate methyl parathion was recorded with concentrations of PNP ranging from 9.5 to 3.5 µM after 48 h. A coexpressive construct harboring a modified organophosphorus hydrolase enzyme and the CBF10-1 MBL enzyme yielded only a slight improvement in degradation of methyl parathion, resulting in 75 µM of PNP formed compared with 69 µM formed by the organophosphorus hydrolase (OPH) control over 48 h. These results suggest that S. maltophilia MBL enzymes are currently insufficient for broad-spectrum hydrolysis of phosphorothioate insecticides. Future studies will thus seek to elucidate their catalytic efficiency against other notable phosphotriester oxons, including chlorpyrifos oxon, and malaoxon.     

Bioaugmentation of a methyl parathion contaminated soil with Pseudomonas sp. strain WBC-3

Pseudomonas sp. strain WBC-3 utilizes methyl parathion (MP) and para-nitrophenol as the sole source of carbon, nitrogen and energy. In this study, strain WBC-3 was inoculated into lab-scale MP-contaminated soil for bioaugmentation. Accelerated removal of MP was achieved in bioaugmentation treatment compared to non-bioaugmentation treatment, with complete removal of 0.536 mg g⁻¹ dry soil in bioaugmentation treatment within 15 days and without accumulation of toxic intermediates. The analysis of denaturing gradient gel electrophoresis and real-time PCR showed that strain WBC-3 existed stably during the entire bioaugmentation period. Simultaneously, redundancy analysis for evaluating the relationships between the environmental factors and microbial community structure indicated that the indigenous bacterial community structure was significantly influenced by strain WBC-3 inoculation (P = 0.002).     

Simultaneous Degradation of Atrazine and Phenol by Pseudomonas sp. Strain ADP: Effects of Toxicity and Adaptation

The strain Pseudomonas sp. strain ADP is able to degrade atrazine as a sole nitrogen source and therefore needs a single source for both carbon and energy for growth. In addition to the typical C source for Pseudomonas, Na₂-succinate, the strain can also grow with phenol as a carbon source. Phenol is oxidized to catechol by a multicomponent phenol hydroxylase. Catechol is degraded via the ortho pathway using catechol 1,2-dioxygenase. It was possible to stimulate the strain in order to degrade very high concentrations of phenol (1,000 mg/liter) and atrazine (150 mg/liter) simultaneously. With cyanuric acid, the major intermediate of atrazine degradation, as an N source, both the growth rate and the phenol degradation rate were similar to those measured with ammonia as an N source. With atrazine as an N source, the growth rate and the phenol degradation rate were reduced to ~35% of those obtained for cyanuric acid. This presents clear evidence that although the first three enzymes of the atrazine degradation pathway are constitutively present, either these enzymes or the uptake of atrazine is the bottleneck that diminishes the growth rate of Pseudomonas sp. strain ADP with atrazine as an N source. Whereas atrazine and cyanuric acid showed no significant toxic effect on the cells, phenol reduces growth and activates or induces typical membrane-adaptive responses known for the genus Pseudomonas. Therefore Pseudomonas sp. strain ADP is an ideal bacterium for the investigation of the regulatory interactions among several catabolic genes and stress response mechanisms during the simultaneous degradation of toxic phenolic compounds and a xenobiotic N source such as atrazine.     

Nuclear Magnetic Resonance Spectroscopic Studies on the Microbial Degradation of Mononitrophenol Isomers

The biochemical pathways followed by a mixed bacterial culture and one of its constituent strains, Sarcina maxima, MTCC 5216 (hitherto unreported) during the degradation of mononitrophenol isomers was studied using extensive nuclear magnetic resonance (NMR) spectroscopy (One- and Two-Dimensional Heteronuclear Multiple Quantum Coherence Transfer-2D HMQCT NMR). NMR investigations revealed that o-nitrophenol (ONP) could be degraded by the consortium to metabolites such as catechol, cis, cis-muconic acid, γ-hydroxymuconic semialdehyde, maleylacetate and β-ketoadipate. The spectra of ONP reaction mixture degraded by S.␣maxima showed that formation of maleylacetate from γ-hydroxymuconic semialdehyde should go through a new metabolite γ-hydroxymaleylacetate, hitherto unreported. The consortium could breakdown m-nitrophenol (MNP) to 4-aminocatechol indicating that it came from 3-hydroxyaminophenol. However, S. maxima MTCC 5216, could convert MNP to hitherto unreported 2-nitrohydroquinone and the subsequent 2-hydroxylaminohydroquinone to 1,2,4-benzenetriol along with γ-hydroxymuconic semialdehyde, muconolactone and maleylacetate. The pathway followed by the consortium during p-nitrophenol (PNP) degradation was by the formation of 4-nitrocatechol, maleylacetate and β-ketoadipate. PNP reaction mixture of S.␣maxima, MTCC 5216 on the other hand, showed that the pathway could proceed through the formation of p-hydroquinone as the initial metabolite. The present study conclusively established the nitrophenol-degrading ability of both the consortium and S. maxima MTCC 5216, including exhibiting slight deviations from the pathways followed by the other reported microorganisms.