Functional expression, purification, and characterization of 3alpha-hydroxysteroid dehydrogenase/carbonyl reductase from Comamonas testosteroni

Hydroxysteroid Dehydrogenase-Catalyzed Highly Regio-, Chemo-, and Enantioselective Hydrogenation of 3-Keto in Steroids

A highly selective hydrogenation of 3-keto in steroids to 3-hydroxyl steroids catalyzed by hydroxysteroid dehydrogenases (HSDHs) was demonstrated. The Ct3α-HSDH-catalyzed hydrogenation generated 3α-hydroxyl steroids as the main enantiopure isomers in high yields, while the Ss3β-HSDH catalytic system afforded 3β-hydroxyl steroids in excellent yields. In both catalytic systems, the hydrogenation proceeded regioselectively at 3-keto with 7-, 11-, 17-, and 20-keto almost unreacted, and chemoselectively with the C═C bond and ester group unattacked. Our HSDH-promoted hydrogenation showed advantages like high regio-, chemo-, and enantioselectivity, good yields, mild conditions, a wide substrate scope, and being suitable for gram-scale synthesis. Notably, bioactive molecules like dehydroepiandrosterone, brienolone, and alfaxalone were obtained facilely in high yields via our hydrogenation approach.

Comprehensive summary of steroid metabolism in Comamonas testosteroni TA441: entire degradation process of basic four rings and removal of C12 hydroxyl group

Comamonas testosteroni is one of the representative aerobic steroid-degrading bacteria. We previously revealed the mechanism of steroidal A,B,C,D-ring degradation by C. testosteroni TA441. The corresponding genes are located in two clusters at both ends of a mega-cluster of steroid degradation genes. ORF7 and ORF6 are the only two genes in these clusters, whose function has not been determined. Here, we characterized ORF7 as encoding the dehydrase responsible for converting the C12β hydroxyl group to the C10(12) double bond on the C-ring (SteC), and ORF6 as encoding the hydrogenase responsible for converting the C10(12) double bond to a single bond (SteD). SteA and SteB, encoded just upstream of SteC and SteD, are in charge of oxidizing the C12α hydroxyl group to a ketone group and of reducing the latter to the C12β hydroxyl group, respectively. Therefore, the C12α hydroxyl group in steroids is removed with SteABCD via the C12 ketone and C12β hydroxyl groups. Given the functional characterization of ORF6 and ORF7, we disclose the entire pathway of steroidal A,B,C,D-ring breakdown by C. testosteroni TA441.IMPORTANCEStudies on bacterial steroid degradation were initiated more than 50 years ago, primarily to obtain materials for steroid drugs. Now, their implications for the environment and humans, especially in relation to the infection and the brain-gut-microbiota axis, are attracting increasing attention. Comamonas testosteroni TA441 is the leading model of bacterial aerobic steroid degradation with the ability to break down cholic acid, the main component of bile acids. Bile acids are known for their variety of physiological activities according to their substituent group(s). In this study, we identified and functionally characterized the genes for the removal of C12 hydroxyl groups and provided a comprehensive summary of the entire A,B,C,D-ring degradation pathway by C. testosteroni TA441 as the representable bacterial aerobic degradation process of the steroid core structure.

Identification of "missing links" in C- and D-ring cleavage of steroids by Comamonas testosteroni TA441

Comamonas testosteroni TA441 is capable of aerobically degrading steroids through the aromatization and cleavage of the A- and B-rings, followed by D- and C-ring cleavage via β-oxidation. While most of the degradation steps have been previously characterized, a few intermediate compounds remained unidentified. In this study, we proposed that the cleavage of the D-ring at C13-17 required the ScdY hydratase, followed by C-ring cleavage via the ScdL1L2 transferase. The anticipated reaction was expected to yield 6-methyl-3,7-dioxo-decane-1,10-dioic acid-coenzyme A (CoA) ester. To confirm this hypothesis, we constructed a plasmid enabling the induction of targeted genes in TA441 mutant strains. Induction experiments of ScdL1L2 revealed that the major product was 3-hydroxy-6-methyl-7-oxo-decane-1,10-dioic acid-CoA ester. Similarly, induction experiments of ScdY demonstrated that the substrate of ScdY was a geminal diol, 17-dihydroxy-9-oxo-1,2,3,4,5,6,10,19-octanorandrost-8(14)-en-7-oic acid-CoA ester. These findings suggest that ScdY catalyzes the addition of a water molecule at C14 of 17-dihydroxy-9-oxo-1,2,3,4,5,6,10,19-octanorandrost-8(14)-en-7-oic acid-CoA ester, leading to D-ring cleavage at C13-17. Subsequently, the C9 ketone of the D-ring cleavage product is converted to a hydroxyl group, followed by C-ring cleavage, resulting in the production of 3-hydroxy-6-methyl-7-oxo-decane-1,10-dioic acid-CoA ester.IMPORTANCEStudies on bacterial steroid degradation were initiated more than 50 years ago primarily to obtain substrates for steroid drugs. In recent years, the role of steroid-degrading bacteria in relation to human health has gained significant attention, as emerging evidence suggests that the intestinal microflora plays a crucial role in human health. Furthermore, cholic acid, a major component of bile acid secreted in the intestines, is closely associated with the gut microbiota. While Comamonas testosteroni TA441 is recognized as the leading bacterial model for aerobic steroid degradation, the involvement of aerobic steroid degradation in the intestinal microflora remains largely unexplored. Nonetheless, the presence of C. testosteroni in the cecum suggests the potential influence of aerobic steroid degradation on gut microbiota. To establish essential information about the role of these bacteria, here, we identified the missing compounds and propose more details of C-, and D-ring cleavage, which have remained unclear until now.

Identification of the Coenzyme A (CoA) Ester Intermediates and Genes Involved in the Cleavage and Degradation of the Steroidal C-Ring by Comamonas testosteroni TA441

Comamonas testosteroni TA441 degrades steroids aerobically via aromatization of the A-ring accompanied by B-ring cleavage, followed by D- and C-ring cleavage. We previously revealed major enzymes and intermediate compounds in A,B-ring cleavage, the β-oxidation cycle of the cleaved B-ring, and partial C,D-ring cleavage. Here, we elucidate the C-ring cleavage and the β-oxidation cycle that follows. ScdL1L2, a 3-ketoacid coenzyme A (CoA) transferase which belongs to the SugarP_isomerase superfamily, was thought to cleave the C-ring of 9-oxo-1,2,3,4,5,6,10,19-octanor-13,17-secoandrost-8(14)-ene-7,17-dioic acid-CoA ester, the key intermediate compound in the degradation of 9,17-dioxo-1,2,3,4,10,19-hexanorandrostan-5-oic acid (3aα-H-4α [3'-propionic acid]-7aβ-methylhexahydro-1,5-indanedione; HIP)-CoA ester in our previous study; however, the present study suggested that ScdL1L2 is the isomerase of the derivative with a hydroxyl group at C-14 which cleaves the C-ring. The subsequent ring-cleaved product was indicated to be converted to 4-methyl-5-oxo-octane-1,8-dioic acid-CoA ester mainly by ORF33-encoded CoA-transferase (named ScdJ), followed by dehydrogenation by ORF21- and 22-encoded acyl-CoA dehydrogenase (named ScdM1M2). Then, a water molecule is added by ScdN for further degradation by β-oxidation. ScdN is proposed to catalyze the last reaction in C,D-ring degradation by the enzymes encoded in the steroid degradation gene cluster tesB to tesR. IMPORTANCE Studies on bacterial steroid degradation were initiated more than 50 years ago primarily to obtain materials for steroid drugs. Steroid-degrading bacteria are globally distributed, and the role of bacterial steroid degradation in the environment, as well as in humans, is attracting attention. The overall degradation process of the four steroidal rings has been proposed; however, there is still much to be revealed to understand the complete degradation pathway. This study aimed to uncover the whole steroid degradation process in C. testosteroni, which is one of the most studied representative steroid-degrading bacteria and is suitable for exploring the degradation pathway because the involvement of degradation-related genes can be determined by gene disruption.

Characterization of a LuxR repressor for 3,17β-HSD in Comamonas testosteroni ATCC11996

3,17β-Hydroxysteroid dehydrogenase in Comamonas testosteroni (C. testosteroni) is a key enzyme involved in the degradation of steroid compounds. Recently, we found that LuxR is a negative regulator in the expression of the 3,17β-HSD gene. In the present work, we cultured wild-type and LuxR knock-out mutants of C. testosteroni with inducers such as testosterone, estradiol, progesterone or estrone. HPLC analysis showed that the degradation activities towards testosterone, estradiol, progesterone, and estrone by C.T.-LuxR-KO1 were increased by 7.1%, 9.7%, 11.9% and 3.1%, respectively compared to the wild-type strain. Protein conformation of LuxR was predicted by Phyre 2 Server software, where the N-terminal 86(Ile), 116(Ile), 118(Met) and 149(Phe) residues form a testosterone binding hydrophobic pore, while the C-terminus forms the DNA binding site (HTH). Further, luxr point mutant plasmids were prepared by PCR and co-transformed with pUC3.2-4 into E. coli HB101. ELISA was used to determine 3,17β-HSD expression after testosterone induction. Compared to wild-type luxr, 3,17β-HSD expression in mutants of I86T, I116T, M118T and F149S were decreased. The result indicates that testosterone lost its capability to bind to LuxR after the four amino acid residues had been exchanged. No significant changes of 3,17β-HSD expression were found in K354I and Y356 N mutants compared to wild-type luxr, which indicates that these two amino acid residues in LuxR might relate to DNA binding. Native LuxR protein was prepared from inclusion bodies using sodium lauroylsarcosinate. Molecular interaction experiments showed that LuxR protein binds to a nucleotide sequence which locates 87 bp upstream of the βhsd promoter. Our results revealed that steroid induction of 3,17β-HSD in C. testosteroni in fact appears to be a de-repression, where testosterone prevents the LuxR regulator protein binding to the 3,17β-HSD promoter domain.

The characterization of a short chain dehydrogenase/reductase (SDRx) in Comamonas testosteroni

C. testosteroni is a research topic that can degrade steroid hormones into water and carbon dioxide through a series of enzymes in the body. Short-chain dehydrogenase (SDR) are a class of NAD (P) H-dependent oxidoreductases in C. testosteroni. Its main function is catalyzing the redox of the hydroxyl/ketone group of the hormone. In this paper, a SDR gene(SDRx) is cloned from C. testosteroni ATCC11996 and expressed. The polyclonal antibody was prepared and the SDRx gene knocked out by homologous recombination. Wild type and mutant C. testosteroni induced by testosterone, estradiol, estrone and estriol. The growth curves of the bacteria were measured by spectrophotometer. ELISA established the expression of SDRx protein, and high-performance liquid chromatography(HPLC) detected the contents of various hormones. The results show that the growth of wild type was faster than mutant type induced by testosterone. The concentration of SDRx is 0.318 mg/ml under testosterone induction. It has a great change in steroid hormones residue in culture medium measured by HPLC: Testosterone residue in the mutant type group was 42.4 % more than the wild type in culture medium. The same thing happens with induced by estrone. In summary, this SDRx gene involved in the degradation of testosterone and estradiol, and effects the growth of C. testosteroni.

Biotransformation strategies for steroid estrogen and androgen pollution

The common steroid hormones are estrone (E1), 17β-estradiol (E2), estriol (E3), 17α-ethinylestradiol (EE2), and testosterone (T). These steroids are reported to contaminate the environment through wastewater treatment plants. Steroid estrogens are widespread in the aquatic environment and therefore pose a potential risk, as exposure to these compounds has adverse impacts on vertebrates. Excessive exposure to steroid estrogens causes endocrine disruption in aquatic vertebrates, which affects the normal sexual life of these animals. Steroid pollutants also cause several health problems in humans and other animals. Microbial degradation is an efficient method for removing hormone pollutants from the environment by remediation. Over the last two decades, microbial metabolism of steroids has gained considerable attention due to its higher efficiency to reduce pollutants from the environment. The present review is focused on the major causes of steroid pollution, concentrations of these pollutants in surface water, groundwater, drinking water, and wastewater, their effect on humans and aquatic animals, as well as recent efforts by various research groups that seek better ways to degrade steroids by aerobic and anaerobic microbial systems. Detailed overview of aerobic and anaerobic microbial biotransformation of steroid estrogens and testosterone present in the environment along with the active enzyme systems involved in these biotransformation reactions is described in the review article, which helps readers to understand the biotransformation mechanism of steroids in depth. Other measures such as co-metabolic degradation, consortia degradation, algal, and fungal steroid biotransformation are also discussed in detail.

Steroid Degradation in Comamonas testosteroni TA441: Identification of the Entire β-Oxidation Cycle of the Cleaved B Ring

Comamonas testosteroni TA441 degrades steroids via aromatization of the A ring, followed by degradation of 9,17-dioxo-1,2,3,4,10,19-hexanorandrostan-5-oic acid, mainly by β-oxidation. In this study, we revealed that 7β,9α-dihydroxy-17-oxo-1,2,3,4,10,19-hexanorandrostanoic acid-coenzyme A (CoA) ester is dehydrogenated by (3S)-3-hydroxylacyl CoA-dehydrogenase, encoded by scdE (ORF27), and then the resultant 9α-hydroxy-7,17-dioxo-1,2,3,4,10,19-hexanorandrostan-5-oic acid-CoA ester is converted by 3-ketoacyl-CoA transferase, encoded by scdF (ORF23). With these results, the whole cycle of β-oxidation on the side chain at C-8 of 9,17-dioxo-1,2,3,4,10,19-hexanorandrostan-5-oic acid is clarified; 9-hydroxy-17-oxo-1,2,3,4,10,19-hexanorandrostan-5-oic acid-CoA ester is dehydrogenated at C-6 by ScdC1C2, followed by hydration by ScdD. 7β,9α-Dihydroxy-17-oxo-1,2,3,4,10,19-hexanorandrostanoic acid-CoA ester then is dehydrogenated by ScdE to be converted to 9α-hydroxy-17-oxo-1,2,3,4,5,6,10,19-octanorandrostan-7-oic acid-CoA ester and acetyl-CoA by ScdF. ScdF is an ortholog of FadA6 in Mycobacterium tuberculosis H37Rv, which was reported as a 3-ketoacyl-CoA transferase involved in C ring cleavage. We also obtained results suggesting that ScdF is also involved in C ring cleavage, but further investigation is required for confirmation. ORF25 and ORF26, located between scdF and scdE, encode enzymes belonging to the amidase superfamily. Disrupting either ORF25 or ORF26 did not affect steroid degradation. Among the bacteria having gene clusters similar to those of tesB to tesR, some have both ORF25- and ORF26-like proteins or only an ORF26-like protein, but others do not have either ORF25- or ORF26-like proteins. ORF25 and ORF26 are not crucial for steroid degradation, yet they might provide clues to elucidate the evolution of bacterial steroid degradation clusters.IMPORTANCE Studies on bacterial steroid degradation were initiated more than 50 years ago primarily to obtain materials for steroid drugs. Steroid-degrading bacteria are globally distributed, and the role of bacterial steroid degradation in the environment as well as in relation to human health is attracting attention. The overall aerobic degradation of the four basic steroidal rings has been proposed; however, there is still much to be revealed to understand the complete degradation pathway. This study aims to uncover the whole steroid degradation process in Comamonas testosteroni TA441 as a model of steroid-degrading bacteria. C. testosteroni is one of the most studied representative steroid-degrading bacteria and is suitable for exploring the degradation pathway, because the involvement of degradation-related genes can be determined by gene disruption. Here, we elucidated the entire β-oxidation cycle of the cleaved B ring. This cycle is essential for the following C and D ring cleavage.

Identification of 4-methyl-5-oxo-octane-1,8-dioic acid and the derivatives as metabolites of steroidal C,D-ring degradation in Comamonas testosteroni TA441

Comamonas testosteroni TA441 degrades steroids via 9,17-dioxo-1,2,3,4,10,19-hexanorandrostan-5-oic acid, which is presumed to be further degraded by β-oxidation. In the β-oxidation process, Coenzyme A (CoA)-ester of 9-oxo-1,2,3,4,5,6,10,19-octanor-13,17-secoandrost-8(14)-ene-7,17-dioic acid is produced and converted by β-ketoacyl-CoA-transferase encoded by ORF1 and ORF2 (scdL1L2) to cleave the remaining C-ring. In this study, we isolated and identified 4-methyl-5-oxo-octane-1,8-dioic acid and 4-methyl-5-oxo-3-octene-1,8-dioic acid from the culture of the ORF3 (scdN)-null mutant as metabolites of steroid degradation (ADD and cholic acid analogues; cholic acid, chenodeoxycholic acid, deoxycholic acid, and lithocholic acid). In addition of these compounds, UHPLC/MS analysis of the culture of the scdN-null mutant revealed significant accumulation of another compound, which was detected as a dominant peak of m/z 155 ([M-CO₂]^-) accompanied by a small peak of parental ion (m/z 199 [M^-]). On the bases of experimental data, this compound was presumed to be 4-methyl-5-oxo-2-octene-1,8-dioic acid, whose CoA-ester was indicated to be converted by scdN-encoded CoA-hydratase into the CoA-ester of 3-hydroxy-4-methyl-5-oxooctan-1,7-carboxylic acid.

Identification of 9-oxo-1,2,3,4,5,6,10,19-octanor-13,17-secoandrost-8(14)-ene-7,17-dioic acid as a metabolite of steroid degradation in Comamonas testosteroni TA441 and the genes involved in the conversion

Comamonas testosteroni TA441 degrades steroid compounds via aromatization of the A-ring to produce 9,17-dioxo-1,2,3,4,10,19-hexanorandrostan-5-oic acid (a metabolite with C- and D-rings), which is presumed to be further degraded via β-oxidation. In elucidating the complete steroid degradation process in C. testosteroni, we isolated 9-oxo-1,2,3,4,5,6,10,19-octanor-13,17-secoandrost-8(14)-ene-7,17-dioic acid and several other metabolites containing only C-ring. For conversion of the CoA-ester of this compound, a two-subunit β -ketoacyl-CoA-transferase encoded by ORF1 and ORF2 was shown to be indispensable. ORF1 and ORF2 are located just after tesB, the meta-cleavage enzyme gene in one of the two major steroid degradation gene clusters of strain TA441. Conversion by the CoA-transferase leads to cleavage of the remaining C-ring, and the product was suggested to be further degraded by β-oxidation involving other genes in the cluster. ORF1 and ORF2 are considered orthologues of ipdAB gene in Mycobacterium tuberculosis H37Rv, which is recently reported as the CoA-transferase of 9-oxo-1,2,3,4,5,6,10,19-octanor-13,17-secoandrost-8(14)-ene-7,17-dioic acid (Crowe AM, Casabon I, Brown KL, Liu J, Lian J, Rogalski JC, Hurst TE, Snieckus V, Foster LJ, Eltis LD. 2017. MBio 8).

Steroid Degradation in Comamonas testosteroni TA441: Identification of Metabolites and the Genes Involved in the Reactions Necessary before D-Ring Cleavage

Bacterial steroid degradation has been studied mainly with Rhodococcus equi (Nocardia restrictus) and Comamonas testosteroni as representative steroid degradation bacteria for more than 50 years. The primary purpose was to obtain materials for steroid drugs, but recent studies showed that many genera of bacteria (Mycobacterium, Rhodococcus, Pseudomonas, etc.) degrade steroids and that steroid-degrading bacteria are globally distributed and found particularly in wastewater treatment plants, the soil, plant rhizospheres, and the marine environment. The role of bacterial steroid degradation in the environment is, however, yet to be revealed. To uncover the whole steroid degradation process in a representative steroid-degrading bacterium, C. testosteroni, to provide basic information for further studies on the role of bacterial steroid degradation, we elucidated the two indispensable oxidative reactions and hydration before D-ring cleavage in C. testosteroni TA441. In bacterial oxidative steroid degradation, A- and B-rings of steroids are cleaved to produce 2-hydroxyhexa-2,4-dienoic acid and 9,17-dioxo-1,2,3,4,10,19-hexanorandrostan-5-oic acid. The latter compound was revealed to be degraded to the coenzyme A (CoA) ester of 9α-hydroxy-17-oxo-1,2,3,4,5,6,10,19-octanorandrostan-7-oic acid, which is converted to the CoA ester of 9,17-dioxo-1,2,3,4,5,6,10,19-octanorandrostan-7-oic acid by ORF31-encoded hydroxylacyl dehydrogenase (ScdG), followed by conversion to the CoA ester of 9,17-dioxo-1,2,3,4,5,6,10,19-octanorandrost-8(14)-en-7-oic acid by ORF4-encoded acyl-CoA dehydrogenase (ScdK). Then, a water molecule is added by the ORF5-encoded enoyl-CoA hydratase (ScdY), which leads to the cleavage of the D-ring. The conversion by ScdG is presumed to be a reversible reaction. The elucidated pathway in C. testosteroni TA441 is different from the corresponding pathways in Mycobacterium tuberculosis H37Rv.IMPORTANCE Studies on representative steroid degradation bacteria Rhodococcus equi (Nocardia restrictus) and Comamonas testosteroni were initiated more than 50 years ago primarily to obtain materials for steroid drugs. A recent study showed that steroid-degrading bacteria are globally distributed and found particularly in wastewater treatment plants, the soil, plant rhizospheres, and the marine environment, but the role of bacterial steroid degradation in the environment is yet to be revealed. This study aimed to uncover the whole steroid degradation process in C. testosteroni TA441, in which major enzymes for steroidal A- and B-ring cleavage were elucidated, to provide basic information for further studies on bacterial steroid degradation. C. testosteroni is suitable for exploring the degradation pathway because the involvement of degradation-related genes can be determined by gene disruption. We elucidated the two indispensable oxidative reactions and hydration before D-ring cleavage, which appeared to differ from those present in Mycobacterium tuberculosis H37Rv.

Biodegradation of 17β-estradiol by Bacterial Co-culture Isolated from Manure

Animal wastes are potential sources of natural and steroidal estrogen hormones into the environment. These hormones can be removed by microorganisms with induced enzymes. Two strains of 17β-estradiol-degrading bacteria (LM1 and LY1) were isolated from animal wastes. Based on biochemical characteristics and 16 S rDNA gene sequences, we identified strains LM1 and LY1 as belonging to the genus of Acinetobacter and Pseudomonas, respectively. Bacterial co-culture containing LM1 and LY1 bacterial strains could rapidly remove approximately 98% of E2 (5 mg L⁻¹) within 7 days. However, strains LM1 and LY1 degraded 77% and 68% of E2 when they were incubated alone, respectively. More than 90% of 17β-estradiol (E2, ≤ 20 mg L⁻¹) could be removed by bacterial co-culture. Low C/N ratio (1:35) was more suitable for bacterial growth and E2 degradation. The optimal pH for bacterial co-culture to degrade E2 ranged from 7.00 to 9.00. Coexisting sodium acetate, glucose and sodium citrate decreased E2 degradation in the first 4 days, but more E2 was removed when they were depleted. The growth of the bacterial co-culture was not significantly decreased by Ni, Pb, Cd or Cu at or below 0.8, 1.2, 1.6 or 0.8 mg L⁻¹, respectively. These data highlight the usefulness of bacterial co-culture in the bioremediation of estrogen-contaminated environments.

Expression, purification and functional characterization of a novel 3α-hydroxysteroid dehydrogenase from Pseudomonas aeruginosa

3α-Hydroxysteroid dehydrogenase (3α-HSD) catalyzes the oxidation of the 3-hydroxyl group of steroids. The enzymatic conversion is a critical step in the enzymatic assay of urinary sulfated bile acids (SBAs), which is a valuable diagnosis index of hepatobiliary diseases. However, the source of 3α-HSD for clinical applications is limited. In this study, an open reading frame (ORF) encoding a novel 3α-HSD was successfully cloned from Pseudomonas aeruginosa and expressed in Escherichia coli BL21 (DE3). The recombinant protein was purified by immobilized metal ion affinity chromatography. Enzyme characterization studies revealed that the protein has 3α-HSD activity and the Km value for sodium cholate is 1.06 mmol L(-1). More than 60% relative enzyme activity was observed in a wide range of pH and temperature, with an optimum pH at 8.0 and an optimum temperature at 30°C. The enzyme's good thermostability under 40°C would be favorable in clinical applications. Ion interference experiments indicated that Zn(2+) was an activating cofactor which increased the enzyme activity 1.75-fold. With the favorable characteristics mentioned above, the new 3α-HSD is a promising enzyme for clinical applications. More importantly, the present work is the first report on a 3α-HSD from P. aeruginosa.

Identification and isolation of a regulator protein for 3,17β-HSD expressional regulation in Comamonas testosteroni

Comamonas testosteroni (C. testosteroni) is able to catabolize a variety of steroids and polycyclic aromatic hydrocarbons. 3,17β-Hydroxysteroid dehydrogenase (3,17β-HSD) from C. testosteroni is a member of the short-chain dehydrogenase/reductase (SDR) superfamily. It is an inducible and key enzyme in steroid degradation. Elucidating the mechanism of 3,17β-HSD gene (βhsd) regulation may help us to generate prospective C. testosteroni mutants for bioremediation. The genome of C. testosteroni ATCC11996 was sequenced in our previous work. Upon examining the genome with bioinformatics tools, a gene (brp) coding for a regulator protein (BRP) for 3,17β-HSD expression was found upstream of the βhsd gene. A Blast search revealed high identities to a nucleotide binding protein with unknown function in other bacteria. Two potential promoters and two repeat sequences (RS, 16 bp), spaced to each other by 1661 bp, were also found upstream of the βhsd gene C. testosteroni. The brp gene was cloned into plasmid pK18 and pET-15b, expressed in Escherichia coli, and the recombinant BRP protein was purified on a Ni-column. In addition, a brp gene knock-out mutant of C. testosteroni was prepared. These knock-out mutants showed an enhanced expression of both the βhsd gene and the hsdA gene (the latter coding for 3α-HSD/CR) in the presence of testosterone. To characterize the BRP functional DNA domain, different fragments of the βhsd upstream regulatory region were tested in a cotransformation system. Our data reveal that the βhsd gene undergoes complex regulation involving the two promoters, a loop structure via the two repeat sequences, and the steroid testosterone. Furthermore, a proximal repressor gene for βhsd expression, phaR, had been identified in our previous investigations. The exact interplay between all these factors will be determined in future experiments.

One step affinity recovery of 3α-hydroxysteroid dehydrogenase from cloned Escherichia coli

3α-Hydroxysteroid dehydrogenase (3α-HSD), from Comamonas Testosterone, catalyze reversibly the oxidoreduction of 3α-hydroxyl groups of the steroid hormones. The gene encoding 3α-HSD (hsdA) from Comamonas Testosterone was expressed in Escherchia coli BL21 (DE3). A protocol for recovering 3α-HSD based on affinity strategy was designed and employed. Deoxycholic acid was chosen as the affinity ligand, and it was linked to Sepharose 4B with the aid of the spacers as cyanuric chloride and ethanediamine. With this specific affinity medium, the enzyme recovery process consisted of only one chromatography step to capture 3α-HSD. The target protein, analyzed on HPLC Agilent SEC-5 column, was of 94% pure among the captured protein, and 98% with SDS-PAGE analysis. The yield of the expressed enzyme was 8.8% of crude extracted proteins; the recovery yield of 3α-HSD was 73.2%. 3α-HSD was revealed as a non-covalent homodimer with molecular mass of ∼56kDa by 15.0% SDS-PAGE analysis and SE-HPLC analysis. The desorption constant Kd and the theoretical maximum absorption Qmax on the affinity medium were 4.5μg/g medium and 21.3mg/g medium, respectively.

Cloning, expression and characterization of a putative 2,5-diketo-D-gluconic acid reductase in Comamonas testosteroni

Aldo-keto reductases (AKRs) are a superfamily of soluble NAD(P)(H) oxidoreductases. The function of the enzymes is to reduce aldehydes and ketones into primary and secondary alcohols. We have cloned a 2,5-diketo-D-gluconic acid reductase (2,5DKGR) gene from Comamonas testosteroni (C. testosteroni) ATCC11996 (a Gram-negative bacterium which can use steroids as carbon and energy source) into plasmid pET-15b and over expressed in Escherichia coli BL21 (DE3). The protein was purified by His-tag Metal chelating affinity chromatography column. The 2,5-diketo-D-gluconic acid reductase (2,5DKGR) gene contains 1062 bp and could be translated into a protein of 353 amino acid residues. Three consensus sequences of the AKR superfamily are found as GxxxxDxAxxY, LxxxGxxxPxxGxG and LxxxxxxxxxDxxxxH. GxxxxDxAxxY is the active site, LxxxGxxxPxxGxG is the Cofactor-binding site for NAD(P)(H), LxxxxxxxxxDxxxxH is used for supporting the 3D structure. 2,5-diketo-D-gluconic acid reductase gene of C. testosteroni was knocked out and a mutant M-AKR was obtained. Compared to wild type C. testosteroni, degradations of testosterone, estradiol, oestrone and methyltestosterone in mutant M-AKR were decreased. Therefore, 2,5-diketo-D-gluconic acid reductase in C. testosteroni is involved in steroid degradation.

Spectrophotometric method for the assay of steroid 5α-reductase activity of rat liver and prostate microsomes

A simple spectrophotometric method for the assay of steroid 5α-reductase (5α-SR) was developed in which 5α-dihydrotestosterone (5α-DHT) and 5α-androstane-3α,17β-diol (5α-diol), metabolites formed in the NADPH-dependent reduction of testosterone with enzyme sources of 5α-SR, were measured by enzymatic cycling using 3α-hydroxysteroid dehydrogenase in the presence of excess thionicotinamide-adenine dinucleotide (thio-NAD) and NADH. It was found that 5α-SR activity was proportional to the accumulated thio-NADH having an absorption maximum at 400 nm. Because of the high cycling rate (> 600 cycle per min) and no interference from testosterone, enzymatic cycling can determine the sum of 5α-DHT and 5α-diol at the picomole level without separation from excess testosterone. The present method was readily applicable to the assay of 5α-SR activity of rat liver and prostate microsomes as well as to the assay of inhibitory activity of finasteride, a synthetic inhibitor of 5α-SR.

Oligomerization and negative autoregulation of the LysR-type transcriptional regulator HsdR from Comamonas testosteroni

"3α-Hydroxysteroid dehydrogenase/carbonyl reductase regulator" (HsdR) from Comamonas testosteroni (C. testosteroni) was identified as a member of the LysR-type transcriptional regulator (LTTR) family. We have shown previously that HsdR activates the expression of the hsdA gene, encoding 3α-hydroxysteroid dehydrogenase/carbonyl reductase (3α-HSD/CR), which is an important enzyme involved in the degradation of steroid compounds. Phylogenetic analysis indicated that HsdR is related to the contact-regulated gene A (CrgA) from Neisseria meningitidis, which exists as a homooctamer. Therefore, to further elucidate the regulatory mechanism of HsdR, we investigated the oligomeric state and autoregulation of this transcriptional factor in the present study. To identify the active domains of HsdR, three truncated forms, HsdRΔN (N-terminus deleted), HsdRΔC (C-terminus deleted), and HsdRΔNC (both N- and C-terminus deleted), were constructed and purified. 3α-HSD/CR expression was measured by ELISA to detect the function of HsdR. Functional and biochemical analyses of wild type HsdR and its truncated forms indicated that HsdR may exist as an oligomer where the central domain is crucial for its oligomerization. Gel filtration chromatography revealed that there are two dominant oligomer forms which may be octamers and hexamers. According to electrophoretic mobility shift assays, HsdR specifically binds to its own promoter, where it negatively regulates its own expression. Therefore, the expression of non-functional HsdR variants (an hsdR-gfp fusion mutant and a hsdR gene disrupted mutant) increased compared to the wild type strain, because autorepression of HsdR was prevented. As a consequence, 3α-HSD/CR expression in these hsdR mutant strains was impaired. Combined, in our study we provide evidence that the transcription factor HsdR is a component of the steroid degradation machinery in C. testosteroni, which is active as an oligomer and negatively regulates its own expression.

Novel whole-cell biocatalysts with recombinant hydroxysteroid dehydrogenases for the asymmetric reduction of dehydrocholic acid

Ursodeoxycholic acid is an important pharmaceutical so far chemically synthesized from cholic acid. Various biocatalytic alternatives have already been discussed with hydroxysteroid dehydrogenases (HSDH) playing a crucial role. Several whole-cell biocatalysts based on a 7α-HSDH-knockout strain of Escherichia coli overexpressing a recently identified 7β-HSDH from Collinsella aerofaciens and a NAD(P)-bispecific formate dehydrogenase mutant from Mycobacterium vaccae for internal cofactor regeneration were designed and characterized. A strong pH dependence of the whole-cell bioreduction of dehydrocholic acid to 3,12-diketo-ursodeoxycholic acid was observed with the selected recombinant E. coli strain. In the optimal, slightly acidic pH range dehydrocholic acid is partly undissolved and forms a suspension in the aqueous solution. The batch process was optimized making use of a second-order polynomial to estimate conversion as function of initial pH, initial dehydrocholic acid concentration, and initial formate concentration. Complete conversion of 72 mM dehydrocholic acid was thus made possible at pH 6.4 in a whole-cell batch process within a process time of 1 h without cofactor addition. Finally, a NADH-dependent 3α-HSDH from Comamonas testosteroni was expressed additionally in the E. coli production strain overexpressing the 7β-HSDH and the NAD(P)-bispecific formate dehydrogenase mutant. It was shown that this novel whole-cell biocatalyst was able to convert 50 mM dehydrocholic acid directly to 12-keto-ursodeoxycholic acid with the formation of only small amounts of intermediate products. This approach may be an efficient process alternative which avoids the costly chemical epimerization at C-7 in the production of ursodeoxycholic acid.

Genome sequence of Comamonas testosteroni ATCC 11996, a representative strain involved in steroid degradation

Comamonas testosteroni strains belong to the family of Comamonadaceae and are known for their ability to utilize steroid compounds as carbon source. Here, we present the draft genome sequence of strain ATCC 11996, with a G+C content of 61.48%.

Hydroxysteroid dehydrogenases (HSDs) in bacteria: a bioinformatic perspective

Steroidal compounds including cholesterol, bile acids and steroid hormones play a central role in various physiological processes such as cell signaling, growth, reproduction, and energy homeostasis. Hydroxysteroid dehydrogenases (HSDs), which belong to the superfamily of short-chain dehydrogenases/reductases (SDR) or aldo-keto reductases (AKR), are important enzymes involved in the steroid hormone metabolism. HSDs function as an enzymatic switch that controls the access of receptor-active steroids to nuclear hormone receptors and thereby mediate a fine-tuning of the steroid response. The aim of this study was the identification of classified functional HSDs and the bioinformatic annotation of these proteins in all complete sequenced bacterial genomes followed by a phylogenetic analysis. For the bioinformatic annotation we constructed specific hidden Markov models in an iterative approach to provide a reliable identification for the specific catalytic groups of HSDs. Here, we show a detailed phylogenetic analysis of 3α-, 7α-, 12α-HSDs and two further functional related enzymes (3-ketosteroid-Δ(1)-dehydrogenase, 3-ketosteroid-Δ(4)(5α)-dehydrogenase) from the superfamily of SDRs. For some bacteria that have been previously reported to posses a specific HSD activity, we could annotate the corresponding HSD protein. The dominating phyla that were identified to express HSDs were that of Actinobacteria, Proteobacteria, and Firmicutes. Moreover, some evolutionarily more ancient microorganisms (e.g., Cyanobacteria and Euryachaeota) were found as well. A large number of HSD-expressing bacteria constitute the normal human gastro-intestinal flora. Another group of bacteria were originally isolated from natural habitats like seawater, soil, marine and permafrost sediments. These bacteria include polycyclic aromatic hydrocarbons-degrading species such as Pseudomonas, Burkholderia and Rhodococcus. In conclusion, HSDs are found in a wide variety of microorganisms including bacteria and archaea, suggesting that steroid metabolism is an evolutionarily conserved mechanism that might serve different functions such as nutrient supply and signaling. Article from a special issue on steroids and microorganisms.

Identification of a new steroid degrading bacterial strain H5 from the Baltic Sea and isolation of two estradiol inducible genes

The presence of steroid hormones in the aquatic environment is potentially threatening the population dynamics of all kinds of sea animals and public health. Environmental estrogens in water have been reported to be associated with abnormal sexual development and abnormal feminizing responses in some animals. New approaches for the bioremediation of steroid hormones from the environment are therefore urgently sought. We have previously isolated a steroid degrading bacterial strain (H5) from the Baltic Sea, at Kiel, Germany. In the present investigation, 16S rRNA analysis showed that marine strain H5 belongs to the genus Vibrio, family Vibrionaceae and class Gamma-Proteobacteria. To enable identification of steroid inducible genes from bacterial strain H5, a library was constructed of H5 chromosomal DNA fragments cloned into a fluorescent reporter (pKEGFP-2). A reporter plasmid pK3α-4.6-EGFP3 containing the estrogen-inducible gene 3α-hydroxysteroid dehydrogenase/carbonyl reductase (3α-HSD/CR) from Comamonas testosteroni (C. testosteroni) was created as a positive control. Steroid induction could be detected by a microplate fluorescence reader, when the plasmids were transformed into Escherichia coli (E. coli) HB101 cells. With our meta-genomic pKEGFP-2 approach, we identified two estradiol-inducible genes from marine strain H5, which are obviously involved in steroid degradation. Sequencing of the pKEGFP-2 inserts and data base research at NCBI revealed that one gene corresponds to 3-ketosteroid-delta-1-dehydrogenase from several Mycobacterium strains, while the other showed high similarity to carboxylesterase in Sebadella termitidis and Brachyspira murdochii. Both 3-ketosteroid-delta-1-dehydrogenase and carboxylesterase are one of the first enzymes in steroid degradation. In addition, we identified a strain H5 specific DNA sequence of 480bp which allows sensitive PCR detection and quantification of strain H5 bacteria in "unknown" seawater samples. Currently, the exact characterization and systematic classification of the marine steroid degrading bacterial strain H5 is envisaged, which might be used for the bioremediation of steroid contaminations in seawater. Article from a special issue on steroids and microorganisms.

Identification and characterization of the LysR-type transcriptional regulator HsdR for steroid-inducible expression of the 3α-hydroxysteroid dehydrogenase/carbonyl reductase gene in Comamonas testosteroni

3α-Hydroxysteroid dehydrogenase/carbonyl reductase (3α-HSD/CR) from Comamonas testosteroni is a key enzyme in steroid degradation in soil and water. 3α-HSD/CR gene (hsdA) expression can be induced by steroids like testosterone and progesterone. Previously, we have shown that the induction of hsdA expression by steroids is a derepression where steroidal inducers bind to two repressors, RepA and RepB, thereby preventing the blocking of hsdA transcription and translation, respectively (G. Xiong and E. Maser, J. Biol. Chem. 276:9961-9970, 2001; G. Xiong, H. J. Martin, and E. Maser, J. Biol. Chem. 278:47400-47407, 2003). In the present study, a new LysR-type transcriptional factor, HsdR, for 3α-HSD/CR expression in C. testosteroni has been identified. The hsdR gene is located 2.58 kb downstream from hsdA on the C. testosteroni ATCC 11996 chromosome with an orientation opposite that of hsdA. The hsdR gene was cloned and recombinant HsdR protein was produced, as was anti-HsdR polyclonal antibodies. While heterologous transformation systems revealed that HsdR activates the expression of the hsdA gene, electrophoresis mobility shift assays showed that HsdR specifically binds to the hsdA promoter region. Interestingly, the activity of HsdR is dependent on decreased repression by RepA. Furthermore, in vitro binding assays indicated that HsdR can come into contact with RNA polymerase. As expected, an hsdR knockout mutant expressed low levels of 3α-HSD/CR compared to that of wild-type C. testosteroni after testosterone induction. In conclusion, HsdR is a positive transcription factor for the hsdA gene and promotes the induction of 3α-HSD/CR expression in C. testosteroni.

Steroid degradation and two steroid-inducible enzymes in the marine bacterium H5

Natural and synthetic steroid hormones excreted into the environment are potentially threatening the population dynamics of all kinds of animals and public health. We have previously isolated a steroid degrading bacterial strain (H5) from the Baltic Sea, at Kiel, Germany. 16S-rRNA analysis showed that bacterial strain H5 belongs to the genus Vibrio, family Vibrionaceae and class Gamma-Proteobacteria. Bacterial strain H5 can degrade steroids such as testosterone and estrogens, which was shown in this study by determining the (3)H labeled steroid retaining in the bacterial H5 culture medium at incubation times of 5 h and 20 h. Since 3α-hydroxysteroid dehydrogenase/carbonyl reductase (3α-HSD/CR) is a key enzyme in adaptive steroid degradation in Comamonas testosteroni (C. testosteroni), in previous investigations, a meta-genomic system with the 3α-HSD/CR gene as a positive control was established. By this meta-genomic system, two estradiol inducible genes coding 3-ketosteroid-delta-1-dehydrogenase and carboxylesterase, respectively, which are involved in steroid degradation, were found in marine strain H5. In the present work, the 3-ketosteroid-delta-1-dehydrogenase and carboxylesterase genes were subcloned into plasmids pET38-12 and pET24-17, respectively. Overexpression in Escherichia coli (E. coli) strain BL21(DE3)pLysS cells resulted in corresponding proteins with an N-terminal His-tag sequence. After induction with isopropyl-β-D-thiogalactoside, 3-ketosteroid-delta-1-dehydrogenase and carboxylesterase were purified in one step using nickel-chelate chromatography. After protein determination, 3-ketosteroid-delta-1-dehydrogenase (0.48 mg/ml) and carboxylesterase (1.28 mg/ml) were used to prepare antibodies to determine steroid binding specificity in future research. In summary, we have shown that the marine strain H5 could metabolize steroids; have isolated two estradiol inducible genes from strain H5 chromosomal DNA, and purified the corresponding proteins for further research. The exact characterization and systematic classification of the marine steroid degrading bacterial strain H5 is envisaged. The strain might be used for the bioremediation of steroid contaminations in seawater.

Identification, cloning, heterologous expression, and characterization of a NADPH-dependent 7β-hydroxysteroid dehydrogenase from Collinsella aerofaciens

A gene encoding an NADPH-dependent 7β-hydroxysteroid dehydrogenase (7β-HSDH) from Collinsella aerofaciens DSM 3979 (ATCC 25986, formerly Eubacterium aerofaciens) was identified and cloned in this study. Sequence comparison of the translated amino acid sequence suggests that the enzyme belongs to the short-chain dehydrogenase superfamily. This enzyme was expressed in Escherichia coli with a yield of 330 mg (5,828 U) per liter of culture. The enzyme catalyzes both the oxidation of ursodeoxycholic acid (UDA) forming 7-keto-lithocholic acid (KLA) and the reduction of KLA forming UDA acid in the presence of NADP(+) or NADPH, respectively. In the presence of NADPH, 7β-HSDH can also reduce dehydrocholic acid. SDS-PAGE and gel filtration of the expressed and purified enzyme revealed a dimeric nature of 7β-HSDH with a size of 30 kDa for each subunit. If used for the oxidation of UDA, its pH optimum is between 9 and 10 whereas for the reduction of KLA and dehydrocholic acid it shows an optimum between pH 4 to 6. Usage of the enzyme for the biotransformation of KLA in a 0.5-g scale showed that this 7β-HSDH is a useful biocatalyst for producing UDA from suitable precursors in a preparative scale.

Chiral inversion of RS-8359: a selective and reversible MAO-A inhibitor via oxido-reduction of keto-alcohol

RS-8359, (+/-)-4-(4-cyanoanilino)-5,6-dihydro-7-hydroxy-7H-cyclopenta[d]-pyrimidine is a selective and reversible MAO-A inhibitor. The (S)-enantiomer of RS-8359 has been demonstrated to be inverted to the (R)-enantiomer after oral administration to rats. In the current study, we investigated the chiral inversion mechanism and the properties of involved enzymes using rat liver subcellular fractions. The 7-hydroxy function of RS-8359 was oxidized at least by the two different enzymes. The cytosolic enzyme oxidized enantiospecifically the (S)-enantiomer with NADP as a cofactor. On the other hand, the microsomal enzyme catalyzed more preferentially the oxidation of the (S)-enantiomer than the (R)-enantiomer with NAD as a cofactor. With to product enantioselectivity of reduction of the 7-keto derivative, it was found that only the alcohol bearing (R)-configuration was formed by the cytosolic enzyme with NADPH and the microsomal enzyme with NADH at almost equal rate. The reduction rate was much larger than the oxidation rate of 7-hydroxy group. The results suggest that the chiral inversion might occur via an enantioselectivity of consecutive two opposing reactions, oxidation and reduction of keto-alcohol group. In this case, the direction of chiral inversion from the (S)-enantiomer to the (R)-enantiomer is governed by the enantiospecific reduction of intermediate 7-keto group to the alcohol with (R)-configuration. The enzyme responsible for the enantiospecific reduction of the 7-keto group was purified from rat liver cytosolic fractions and identified as 3alpha-hydroxysteroid dehydrogenase (3alpha-HSD) via database search of peptide mass data obtained by nano-LC/MS/MS.

Understanding oligomerization in 3α-hydroxysteroid dehydrogenase/carbonyl reductase from Comamonas testosteroni: An in silico approach and evidence for an active protein

3alpha-Hydroxysteroid dehydrogenase/carbonyl reductase (3alpha-HSD/CR) from Comamonas testosteroni belongs to the short chain dehydrogenase/reductase (SDR) protein superfamily and catalyzes the oxidoreduction of a variety of steroid substrates, including the steroid antibiotic fusidic acid. The enzyme also mediates the carbonyl reduction of non-steroidal aldehydes and ketones such as a novel insecticide. It is suggested that 3alpha-HSD/CR contributes to the bioremediation of natural and synthetic toxicants by C. testosteroni. Crystallization and structure analysis showed that 3alpha-HSD/CR is active as a dimer. Dimerization takes place via an interface axis which has exclusively been observed in homotetrameric SDRs but never in the structure of a homodimeric SDR. The formation of a tetramer is blocked in 3alpha-HSD/CR by the presence of a predominantly alpha-helical subdomain which is missing in all other SDRs of known structure. For example, 3alpha/20beta-HSD from Streptomyces hydrogenans exhibits two main subunit interfaces arranged about two non-crystallographic two-fold axes which are perpendicular to each other and referred to as P and Q. This mode of dimerization is, however, sterically impossible in 3alpha-HSD/CR because of a 28 amino acids insertion into the classical Rossmann-fold motif between strand betaE and helix alphaF. This insertion is masking helices alphaE and alphaF, thus preventing the formation of a four helix bundle and enables the dimerization via a P-axis interface. This type of dimerization in SDRs has never been observed in a crystal structure so far. The aim of this study was to investigate whether the lack of this predominantly alpha-helical subdomain keeps 3alpha-HSD/CR to be an active enzyme and whether, by an in silico approach, the formation of a homotetramer or even a novel oligomerization mode can be expected. Redesign of this interface was performed on the basis of site directed mutagenesis and according to other SDR structures by an approach combining "in silico" and "wet chemistry". Simulations of sterical and structural effects after different mutations, by applying a combination of homology modelling and molecular dynamic simulations, provided an effective tool for extensive mutagenesis studies and indicated the possibility of tetramer formation of truncated 3alpha-HSD/CR. In addition, despite lacking the extra loop domain, mutant 3alpha-HSD/CR was shown to be active towards a variety of standard substrates.

Crystallization and preliminary X-ray analysis of the complex of NADH and 3alpha-hydroxysteroid dehydrogenase from Pseudomonas sp. B-0831

The NAD(P)(+)-dependent enzyme 3alpha-hydroxysteroid dehydrogenase (3alpha-HSD) catalyzes the reversible interconversion of hydroxyl and oxo groups at position 3 of the steroid nucleus. The complex of NADH and 3alpha-HSD from Pseudomonas sp. B-0831 was crystallized by the hanging-drop vapour-diffusion method. Refinement of crystallization conditions with microseeding improved the quality of the X-ray diffraction data to a resolution of 1.8 A. The crystals belonged to the orthorhombic space group P2(1)2(1)2(1), with unit-cell parameters a = 62.46, b = 82.25, c = 86.57 A, and contained two molecules, reflecting dimer formation of 3alpha-HSD, in the asymmetric unit.

Kinetic study of the enzymatic cycling reaction conducted with 3alpha-hydroxysteroid dehydrogenase in the presence of excessive thio-NAD(+) and NADH

We have established a simple kinetic model applicable to the enzyme cycling reaction for the determination of 3alpha-hydroxysteroids. This reaction was conducted under the reversible catalytic function of a single 3alpha-hydroxysteroid dehydrogenase (3alpha-HSD) with nucleotide cofactors, thio-NAD(+) (one of the NAD(+) analogues) for the oxidation of 3alpha-hydroxysteroids and NADH for the reduction of 3-oxosteroids. This model was constructed based on the reaction mechanism of 3alpha-HSD, following an ordered bi-bi mechanism with cofactor binding first, under the assumption that the respective enzyme-cofactor complexes were distributed according to the initial ratio of thio-NAD(+) to NADH by the rapid equilibrium of both enzyme-cofactor complexes. The cycling rate in the new kinetic model could be expressed with the dissociation constants of enzyme-cofactor complexes and the initial concentrations of cofactors and enzyme. The cycling rate was verified by a comparison with the experimental data using 3alpha-HSD from Pseudomonas sp. B-0831. The results showed that the experimental data corresponded well with the results obtained from the kinetic model.

Mechanistic Roles of Ser-114, Tyr-155, and Lys-159 in 3α-Hydroxysteroid Dehydrogenase/Carbonyl Reductase from Comamonas testosteroni

3alpha-hydroxysteroid dehydrogenase/carbonyl reductase (3alpha-HSD/CR) from Comamonas testosteroni, a short chain dehydrogenase/reductase, catalyzes the oxidation of androsterone with NAD+ to form androstanedione and NADH. A catalytic triad of Ser-114, Tyr-155, and Lys-159 in 3alpha-HSD/CR has been proposed based on structural analysis and sequence alignment of the short chain dehydrogenase/reductase family. The 3alpha-HSD/CR-catalyzed reaction has not been kinetically analyzed in detail, however. In this study, we combined steady-state kinetics, site-directed mutagenesis, and pH profile to explore the function of Ser-114, Tyr-155, and Lys-159 in 3alpha-HSD/CR-catalyzed reaction. The catalytic efficiency of wild-type and mutants S114A, Y155F, K159A, and Y155F/K159A is 4.3 x 10(7), 7.3 x 10(4), 1.7 x 10(4), 2.4 x 10(5), and 71 m(-1)s(-1), respectively. The values of pKa on kcat/Km for the wild-type, S114A, Y155F, K159A, and Y155F/K159A are 7.2, 7.4, 8.4, 9.1, and 10.2, respectively. Mutant S114A/Y155F exhibits a pH-independent profile with 10(-5) times of wild-type activity at pH 10.5. The activity decreases as the pH lowers, which indicates that a functional group with an apparent pKa of 7.2 is involved in the general base catalysis for wild-type 3alpha-HSD/CR. The pKa shift to 9.1 for mutant K159A suggests the role of Lys-159 is to lower the pKa of the residues involved in the general base catalysis. Because pH dependence is observed for both S114A and Y155F mutants and pH independence is observed in S114A/Y155F, Tyr-155 may be important as a general base catalysis in the wild-type, whereas Ser-114 may act as a general base on mutant Y155F to catalyze the reaction.

Steroid degradation gene cluster of Comamonas testosteroni consisting of 18 putative genes from meta-cleavage enzyme gene tesB to regulator gene tesR

Steroid degradation genes of Comamonas testosteroni TA441 are encoded in at least two gene clusters: one containing the meta-cleavage enzyme gene tesB and ORF1, 2, 3; and another consisting of ORF18, 17, tesI, H, A2, and tesA1, D, E, F, G (tesA2 to ORF18 and tesA1 to tesG are encoded in opposite directions). Analysis of transposon mutants with low steroid degradation revealed 13 ORFs and a gene (ORF4, 5, 21, 22, 23, 25, 26, 27, 28, 30, 31, 32, 33, and tesR) involved in steroid degradation in the downstream region of ORF3. TesR, which is almost identical to that of TeiR, a positive regulator of Delta1-dehydrogenase (corresponds to TesH in TA441) and 3alpha-dehydrogenase (currently not identified in TA441), in C. testosteroni ATCC11996 (Pruneda-Paz, 2004), was shown to be necessary for induction of the steroid degradation gene clusters identified in TA441, tesB to tesR, tesA1 to tesG, and tesA2 to ORF18. At least some of the ORFs from ORF3 to ORF33 were suggested to be involved in 9,17-dioxo-1,2,3,4,10,19-hexanorandrostan-5-oic acid degradation.

Transient-phase kinetic studies on the nucleotide binding to 3alpha-hydroxysteroid dehydrogenase from Pseudomonas sp. B-0831 using fluorescence stopped-flow procedures

The dual nucleotide cofactor-specific enzyme, 3alpha-hydroxysteroid dehydrogenase (3alpha-HSD) from Pseudomonas sp. B-0831, is a member of the short-chain dehydrogenase/reductase (SDR) superfamily. Transient-phase kinetic studies using the fluorescence stopped-flow method were conducted with 3alpha-HSD to characterize the nucleotide binding mechanism. The binding of oxidized nucleotides, NAD(+), NADP(+) and nicotinic acid adenine dinucleotide (NAAD(+)), agreed well with a one-step mechanism, while that of reduced nucleotide, NADH, showed a two-step mechanism. This difference draws attention to previous characteristic findings on rat liver 3alpha-HSD, which is a member of the aldo-keto reductase (AKR) superfamily. Although functionally similar, AKRs are structurally different from SDRs. The dissociation rate constants associated with the enzyme-nucleotide complex formation were larger than the k(cat) values for either oxidation or reduction of substrates, indicating that the release of cofactors is not rate-limiting overall. It should also be noted that k(cat) for a substrate, cholic acid, with NADP(+) was only 6% of that with NAD(+), and no catalytic activity was detectable with NAAD(+), despite the similar binding affinities of nucleotides. These results suggest that a certain type of nucleotide can modulate nucleotide-binding mode and further the catalytic function of the enzyme.

3alpha-Hydroxysteroid dehydrogenase/carbonyl reductase from Comamonas testosteroni: biological significance, three-dimensional structure and gene regulation

3alpha-Hydroxysteroid dehydrogenase/carbonyl reductase (3alpha-HSD/CR) catalyses the oxidoreduction at carbon 3 of steroid hormones and is postulated to initiate the complete mineralisation of the steroid nucleus to CO(2) and H(2)O in Comamonas testosteroni. The enzyme was found to be functional towards a variety of steroid substrates, including the steroid antibiotic fusidic acid. The enzyme also catalyses the carbonyl reduction of non-steroidal aldehydes and ketones such as a novel insecticide. It is suggested that 3alpha-HSD/CR contributes to important defense strategies of C. testosteroni against natural and synthetic toxicants. The 3alpha-HSD/CR gene (hsdA) is 774 base pairs long and the deduced amino acid sequence comprises 258 residues with a calculated molecular mass of 26.4 kDa. A homology search revealed 3alpha-HSD/CR as a new member of the short-chain dehydrogenase/reductase (SDR) superfamily. Upon gel permeation chromatography the purified enzyme elutes as a 49.4 kDa protein indicating a dimeric nature of 3alpha-HSD/CR. The protein was crystallised and the structure solved by X-ray analysis. The crystal structure reveals one homodimer per asymmetric unit, thereby verifying its dimeric nature. Dimerisation takes place via an interface essentially built-up by helix alphaG and strand betaG of each subunit. So far, this type of intermolecular contact has exclusively been observed in homotetrameric SDRs, but never in the structure of a homodimeric SDR. The formation of a tetramer is blocked in 3alpha-HSD/CR by the presence of a predominantly alpha-helical subdomain, which is missing in all other SDRs of known structure. The promoter domain was localised within the 93 bp region upstream of hsdA and the transcriptional start site was identified at 28 bp upstream of the translation start site. Interestingly, hsdA expression was found to be under negative control by two repressor proteins, the genes of which were found in opposite direction downstream or overlapping with hsdA. Based on our results, we propose that induction of hsdA expression in C. testosteroni by steroids actually appears to be a de-repression by preventing the binding of repressor proteins to regulatory regions.

The crystal structure of 3alpha -hydroxysteroid dehydrogenase/carbonyl reductase from Comamonas testosteroni shows a novel oligomerization pattern within the short chain dehydrogenase/reductase family

The crystal structure of 3alpha-hydroxysteroid dehydrogenase/carbonyl reductase from Comamonas testosteroni (3alpha-HSDH) as well as the structure of its binary complex with NAD(+) have been solved at 1.68-A and 1.95-A resolution, respectively. The enzyme is a member of the short chain dehydrogenase/reductase (SDR) family. Accordingly, the active center and the conformation of the bound nucleotide cofactor closely resemble those of other SDRs. The crystal structure reveals one homodimer per asymmetric unit representing the physiologically active unity. Dimerization takes place via an interface essentially built-up by helix alphaG and strand betaG of each subunit. So far this type of intermolecular contact has exclusively been observed in homotetrameric SDRs but never in the structure of a homodimeric SDR. The formation of a tetramer is blocked in 3alpha-HSDH by the presence of a predominantly alpha-helical subdomain which is missing in all other SDRs of known structure.