Cis- and trans-regulatory elements of 3α-hydroxysteroid dehydrogenase/carbonyl reductase as biosensor system for steroid determination in the environment

Identification of the EdcR Estrogen-Dependent Repressor in Caenibius tardaugens NBRC 16725: Construction of a Cellular Estradiol Biosensor

In this work, Caenibius tardaugens NBRC 16725 (strain ARI-1) (formerly Novosphingobium tardaugens) was isolated due to its capacity to mineralize estrogenic endocrine disruptors. Its genome encodes the edc genes cluster responsible for the degradation of 17β-estradiol, consisting of two putative operons (OpA and OpB) encoding the enzymes of the upper degradation pathway. Inside the edc cluster, we identified the edcR gene encoding a TetR-like protein. Genetic studies carried out with C. tardaugens mutants demonstrated that EdcR represses the promoters that control the expression of the two operons. These genetic analyses have also shown that 17β-estradiol and estrone, the second intermediate of the degradation pathway, are the true effectors of EdcR. This regulatory system has been heterologously expressed in Escherichia coli, foreseeing its use to detect estrogens in environmental samples. Genome comparisons have identified a similar regulatory system in the edc cluster of Altererythrobacter estronivorus MHB5, suggesting that this regulatory arrangement has been horizontally transferred to other bacteria.

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.

Quantitative determination of testosterone levels with biolayer interferometry

Natural and synthetic steroid hormones are widely spread in the environment and are considered as pollutants due to their endocrine activities, even at low concentrations, which are harmful to human health. To detect steroid hormones in the environment, a novel biosensor system was developed based on the principle of biolayer interferometry. Detection is based on changes in the interference pattern of white light reflected from the surface of an optical fiber with bound biomolecules. Monitoring interactions between molecules does not require radioactive, enzymatic, or fluorescent labels. Here, 2 double-stranded DNA fragments of operator 1 (OP1) and OP2 containing 10-bp palindromic sequences in chromosomal Comamonas testosteroni DNA (ATCC11996) were surface-immobilized to streptavidin sensors. Interference changes were detected when repressor protein RepA bound the DNA sequences. DNA-protein interactions were characterized and kinetic parameters were obtained. The dissociation constants between the OP1 and OP2 DNA sequences and RepA were 9.865 × 10^-9 M and 2.750 × 10^-8 M, respectively. The reactions showed high specifically and affinity. Because binding of the 10-bp palindromic sequence and RepA was affected by RepA-testosterone binding, the steroid could be quantitatively determined rapidly using the biosensor system. The mechanism of the binding assay was as follows. RepA could bind both OP1 and testosterone. RepA binding to testosterone changed the protein conformation, which influenced the binding between RepA and OP1. The percentage of the signal detected negative correlation with the testosterone concentration. A standard curve was obtained, and the correlation coefficient value was approximately 0.97. We could quantitatively determine testosterone levels between 2.13 and 136.63 ng/ml. Each sample could be quantitatively detected in 17 min. These results suggested that the specific interaction between double-stranded OP1 DNA and the RepA protein could be used to rapidly and quantitatively determine environmental testosterone levels by the biolayer interferometry technique.

Functional analysis of a novel repressor LuxR in Comamonas testosteroni

Comamonas testosteroni (C. testosteroni) ATCC11996 is a gram negative bacterium which can use steroid as a carbon and energy source. 3,17β-hydroxysteroid dehydrogenase (3,17β-HSD) is a key enzyme for the degradation of steroid hormones in C. testosteroni. The LuxR regulation family is a group of regulatory proteins which play important role in gram negative bacterium. The luxr gene is located on 58 kb upstream of 3,17β-HSD gene with the opposite transcription orientation in the chromosomal DNA of C. testosteroni. An open reading frame of this putative luxr gene consists of 1125 bp and is translated into a protein containing 374 amino acids. The luxr gene was cloned into plasmid pK18 and plasmid pK-LuxR1 was obtained. E. coli HB101 was co-transformed by pK-LuxR1 and pUC912-10, pUC1128-5 or pUC3.2-4 (which contain βhsd gene and different length promoter, repeat sequences). The result of ELISA showed that LuxR protein is a negative regulator for 3,17β-HSD expression. The luxr gene in C. testosteroni was knock-out by homologous integration. 3,17β-HSD expression was increased in the mutant (C.T.-L-KO1) comparing to that in wild-type C. testosteroni (C.T.) after 0.5 mM testosterone induction. The mutant C.T.-L-KO1 and wild-type C. testosteroni were cultured at 27 °C and 37 °C. The result of growth curve proved that LuxR has also effect on the bacterial growth.

Isolation and identification of a repressor TetR 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 key enzyme in steroid degradation. Understanding the mechanism of 3,17β-HSD gene (βhsd) induction may help us to elucidate its complete molecular regulation. Sequencing the C. testosteroni ATCC11996 genome lead us to identify the tetR (522 bp) downstream of βhsd. Two repeat sequences (RS; 13 bp), that are separated to each other by 1661 bp, were found upstream of βhsd. A bioinformatic analysis revealed that TetR family proteins act as transcriptional repressors which are sensitive to environmental signals. Since, C. testosteroni responds to environmental steroid induction and upregulates steroid catabolic genes, we hypothesized that TetR might act in C. testosteroni as repressor for βhsd expression. The tetR was cloned into different plasmids, including an EGFP reporter system, for functional characterization and/or overexpression. The data indicate that, indeed, TetR acts as a repressor for 3,17β-HSD expression. Testosterone in turn, which is known to induce βhsd expression, could not resolve TetR repression. To further substantiate TetR as repressor for βhsd expression, a tetR gene knock-out mutant of C. testosteroni was generated. TetR gene knock-out mutants showed the same basal low level of βhsd expression as the C. testosteroni wild type cells. Interestingly, testosterone induction leads to a strong increase in βhsd expression, especially in the tetR gene knock-out mutants. The result with the knock-out mutant, in principle, supports our hypothesis that TetR is a repressor for βhsd expression, but the exact role of testosterone in this context remains unknown. Finally, it turned out that TetR is obviously also involved in the regulation of the hsdA gene.

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.

The Comamonas testosteroni steroid biosensor system (COSS)--reflection on other methods

Natural and synthetic steroid hormones are released uncontrolled into the environment and are considered as pollutants with regard to their endocrine activity and negative influence on all kind of organisms. Due to their widespread presence, endocrine activity even at low concentrations, and their potential adverse effects in both the environment and human health, there is an increasing need for the development of rapid, sensitive and quantitative techniques for measuring trace levels of these steroids. In addition to classical analytical methods like GC-MS, LC-MS and others, several techniques have been established that are based on human nuclear steroid receptors as reporter systems. However, many of these systems require human or yeast cell culture and are therefore time consuming and expensive, while others suffer from too low sensitivity or cover only one specific steroid compound. These are some of the main reasons that limit current techniques for environmental application. The remarkable ability of certain microorganisms to transform and degrade the steroid nucleus and to respond with the induced expression of steroid regulated genes lead us to explore, whether the steroid signalling machinery of Comamonas testosteroni could be used to construct a steroid sensoring system that is sensitive, rapid, easy to perform, and which could also be applied to detect environmental steroid mixtures at low concentrations. Both whole C. testosteroni mutant cells as well as the cytosol thereof were used as new and sensitive fluorescence based biosensor systems for the successful determination and quantification of a variety of different steroids. We could show that our COSS (Comamonas testosteroniSteroid Sensor) is able to detect testosterone, estradiol and cholesterol in concentrations of 29pg/mL, 0.027pg/mL, and 9.7pg/mL, respectively. The sensitivity of the COSS together with the fact that it is very fast, reproducible and can be used for high-throughput screening in a microplate format makes it suitable for the detection of single steroid hormones or steroid hormone mixtures in environmental samples at low costs. In summary, the COSS is able to detect steroid hormone effects at the molecular level through activation of bacterial steroid-sensing systems. In the future, it may be further developed as a useful tool for the integrative assessment of ecotoxicological potentials caused by hormonally active agents and endocrine-disrupting compounds.