Successful expression of a novel bacterial gene for pinoresinol reductase and its effect on lignan biosynthesis in transgenic Arabidopsis thaliana.

Pinoresinol reductase and pinoresinol/lariciresinol reductase play important roles in an early step of lignan biosynthesis in plants. The activities of both enzymes have also been detected in bacteria. In this study, pinZ, which was first isolated as a gene for bacterial pinoresinol reductase, was constitutively expressed in Arabidopsis thaliana under the control of the cauliflower mosaic virus 35S promoter. Higher reductive activity toward pinoresinol was detected in the resultant transgenic plants but not in wild-type plant. Principal component analysis of data from untargeted metabolome analyses of stem, root, and leaf extracts of the wild-type and two independent transgenic lines indicate that pinZ expression caused dynamic metabolic changes in stems, but not in roots and leaves. The metabolome data also suggest that expression of pinZ influenced the metabolisms of lignan and glucosinolates but not so much of neolignans such as guaiacylglycerol-8-O-4'-feruloyl ethers. In-depth quantitative analysis by liquid chromatography-tandem mass spectrometry (LC-MS/MS) indicated that amounts of pinoresinol and its glucoside form were markedly reduced in the transgenic plant, whereas the amounts of glucoside form of secoisolariciresinol in transgenic roots, leaves, and stems increased. The detected levels of lariciresinol in the transgenic plant following ß-glucosidase treatment also tended to be higher than those in the wild-type plant. Our findings indicate that overexpression of pinZ induces change in lignan compositions and has a major effect not only on lignan biosynthesis but also on biosynthesis of other primary and secondary metabolites.

Distribution of hydrocarbon-degrading bacteria in the soil environment and their contribution to bioremediation.

A real-time PCR quantification method for indigenous hydrocarbon-degrading bacteria (HDB) carrying the alkB gene in the soil environment was developed to investigate their distribution in soil. The detection limit of indigenous HDB by the method was 1 × 10(6) cells/g-soil. The indigenous HDB were widely distributed throughout the soil environment and ranged from 3.7 × 10(7) to 5.0 × 10(8) cells/g-soil, and the ratio to total bacteria was 0.1-4.3 %. The dynamics of total bacteria, indigenous HDB, and Rhodococcus erythropolis NDKK6 (carrying alkB R2) during bioremediation were analyzed. During bioremediation with an inorganic nutrient treatment, the numbers of these bacteria were slightly increased. The numbers of HDB (both indigenous bacteria and strain NDKK6) were gradually decreased from the middle stage of bioremediation. Meanwhile, the numbers of these bacteria were highly increased and were maintained during bioremediation with an organic nutrient. The organic treatment led to activation of not only the soil bacteria but also the HDB, so an efficient bioremediation was carried out.

Characterization of the isophthalate degradation genes of Comamonas sp. strain E6.

The isophthalate (IPA) degradation gene cluster (iphACBDR) responsible for the conversion of IPA into protocatechuate (PCA) was isolated from Comamonas sp. strain E6, which utilizes phthalate isomers as sole carbon and energy sources via the PCA 4,5-cleavage pathway. Based on amino acid sequence similarity, the iphA, iphC, iphB, iphD, and iphR genes were predicted to code for an oxygenase component of IPA dioxygenase (IPADO), a periplasmic IPA binding receptor, a 1,2-dihydroxy-3,5-cyclohexadiene-1,5-dicarboxylate (1,5-DCD) dehydrogenase, a reductase component of IPADO, and an IclR-type transcriptional regulator, respectively. The iphACBDR genes constitute a single transcriptional unit, and transcription of the iph catabolic operon was induced during growth of E6 on IPA. The iphA, iphD, and iphB genes were expressed in Escherichia coli. Crude IphA and IphD converted IPA in the presence of NADPH into a product which was transformed to PCA by IphB. These results suggested that IPADO is a two-component dioxygenase that consists of a terminal oxygenase component (IphA) and a reductase component (IphD) and that iphB encodes the 1,5-DCD dehydrogenase. Disruption of iphA and iphB resulted in complete loss of growth of E6 on IPA. Inactivation of iphD significantly affected growth on IPA, and the iphC mutant did not grow on IPA at neutral pH. These results indicated that the iphACBD genes are essential for the catabolism of IPA in E6. Disruption of iphR resulted in faster growth of E6 on IPA, suggesting that iphR encodes a repressor for the iph catabolic operon. Promoter analysis of the operon supported this notion.

Enzymatic properties of terephthalate 1,2-dioxygenase of Comamonas sp. strain E6.

The tphA1 II and tphA2 II A3 II genes of Comamonas sp. E6 perhaps code for the terephthalate (TPA) 1,2-dioxygenase (TPADO). To characterize E6 TPADO, these genes were expressed in a His-tagged form in Escherichia coli, and the recombinant proteins were purified. TPADO activity was reconstituted from TphA1 II and TphA2 II A3 II, indicating that TPADO consists of a reductase (TphA1 II) and a terminal oxygenase component (TphA2 II and TphA3 II). TphA1(II) contains FAD, and the presence of a plant-type [2Fe-2S] cluster was suggested. These results indicate that TPADO is a class IB aromatic ring-hydroxylating dioxygenase. NADH and NADPH were effective as electron donors for TphA1 II, but NADPH appeared to be the physiological electron donor, based on the kinetic parameters. TPADO showed activity only toward TPA, and Fe2+ was required for it. The Km values for TPA and the Vmax were determined to be 72+/-6 microM and 9.87+/-0.06 U/mg respectively.