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Aspects of the progesterone response in Hortaea werneckii: Steroid detoxification, protein induction and remodelling of the cell wall

Steroids, 2008
Progesterone in sublethal concentrations temporarily inhibits growth of Hortaea werneckii. This study investigates some of the compensatory mechanisms which are activated in the presence of progesterone and are most probably contributing to escape from growth inhibition. ......Read more
steroids 73 ( 2 0 0 8 ) 1465–1474 available at www.sciencedirect.com journal homepage: www.elsevier.com/locate/steroids Aspects of the progesterone response in Hortaea werneckii: Steroid detoxification, protein induction and remodelling of the cell wall Lidija Kri ˇ zanˇ ci´ c Bombek a , Ajda Lapornik a , Marjeta Ukmar a , Maja Matis a,b,c , Bronislava ˇ Creˇ snar a , Jasna Peter Katalini´ c b,c , Marija ˇ Zakelj-Mavriˇ c a, a Institute of Biochemistry, Faculty of Medicine, University of Ljubljana, Vrazov trg 2, SI-1000 Ljubljana, Slovenia b Institute for Medical Physics and Biophysics, Faculty of Medicine, University of Muenster, Robert-Koch Strasse 31, D-48149 Muenster, Germany c Institute of Molecular Medicine and Genetics, Medical College of Georgia, 1120 15th Street, Augusta, GA 30912, USA article info Article history: Received 15 October 2007 Received in revised form 30 July 2008 Accepted 11 August 2008 Published on line 28 August 2008 Keywords: Biotransformation Detoxification Hortaea werneckii Cell wall Yeast proteomics abstract Progesterone in sublethal concentrations temporarily inhibits growth of Hortaea werneckii. This study investigates some of the compensatory mechanisms which are activated in the presence of progesterone and are most probably contributing to escape from growth inhibition. These mechanisms lead on the one hand to progesterone biotransforma- tion/detoxification but, on the other, are suggested to increase the resistance of H. werneckii to the steroid. Biotransformation can detoxify progesterone efficiently in the early loga- rithmic phase, with mostly inducible steroid transforming enzymes, while progesterone biotransformation/detoxification in the late logarithmic and stationary phases of growth is not very efficient. The relative contribution of constitutive steroid transforming enzymes to progesterone biotransformation is increased in these latter phases of growth. In the presence of progesterone, activation of the cell wall integrity pathway is suggested by the overexpression of Pck2 which was detected in the stationary as well as the logarithmic phase of growth of the yeast. Progesterone treated H. werneckii cells were found to be more resis- tant to cell lysis than mock treated cells, indicating for the first time changes in the yeast cell wall as a result of treatment with progesterone. © 2008 Elsevier Inc. All rights reserved. 1. Introduction Steroid hormones are signalling molecules that regulate a host of organismal functions, exerting their actions by binding to the plasma membrane or intracellular receptors of the target cells. Steroids are hydrophobic and relatively stable molecules which cannot be degraded and used as a source of energy in higher organisms. After fulfilling their task they are deacti- vated, transformed into more soluble forms and excreted via urine and bile into the environment [1]. Corresponding author. Tel.: +386 1 543 76 45; fax: +386 1 543 76 41. E-mail address: Marija.Zakelj-Mavric@mf.uni-lj.si (M. ˇ Zakelj-Mavriˇ c). In contrast to higher organisms microorganisms are capa- ble of biotransformation and even mineralization of steroids [2,3]. Numerous microorganisms that inhabit human and ani- mal tissues, such as the skin and urinary and gastrointestinal tracts [4,5], come into contact with steroid hormones and can transform them [6–10]. After their release from the organisms, steroids are further degraded by mixtures of microorganisms in the sewage treatment plants and the environment [11–14]. These processes are very important because of the effects that undegraded steroid hormones can have on wildlife and on 0039-128X/$ – see front matter © 2008 Elsevier Inc. All rights reserved. doi:10.1016/j.steroids.2008.08.004
1466 steroids 73 ( 2 0 0 8 ) 1465–1474 man [15,16]. However, the environmental fate and the rate of mineralization of naturally produced steroid hormones are so far poorly characterized. Biotransformation of steroid hormones in the environ- ment takes place with mixtures of microorganisms, mostly bacteria, and the contribution of individual species is not known precisely. The importance of individual microorgan- isms for the production of commercially important steroids was first realized in 1952 when Peterson and Murray of the Upjohn Company patented the process of 11-hydroxylation of steroids by Rhizopus species [17]. Certain of the synthetic chemistry steps have since been replaced by specific microbial transformations which are able to achieve stereo- and regio- specific conversions of the substrates [18–22]. A currently important area is the use of genetic engineering to improve the capabilities of microorganisms as steroid-transforming agents [19,23]. In addition, microorganisms which are adapted to extreme environments have recently gained great interest due to their specific characteristics [24]. The primary interest in steroid biotransformation was at first focused on steroids and the production of commer- cially valuable products. With time it became evident that steroid hormones can provoke changes in microorganisms. Interest in these changes was increased when the levels of steroid hormones were suggested to affect susceptibility to fungal infection [25–32]. Experiments with exogenous steroids have confirmed the effects of steroids on fungal growth [33–40]. During exposure of microorganisms to steroid hor- mones, the expression of several members of various gene families is increased [41–43]. Steroid transforming enzymes were connected with defence against steroids. Microorgan- isms are thought to induce enzymes that detoxify steroids by transforming them into more soluble and less toxic forms [33]. The contribution of constitutive steroid trans- forming enzymes to steroid detoxification is presently not clear [44]. Our studies of progesterone/yeast interaction have been focused on the halophilic black yeast Hortaea werneckii. The natural habitat of this eukaryotic microorganism is hyper- saline water [45] but it is also known as the causative agent of Tinea nigra, a nonpathologic dermal change of the palms, more frequently observed in females and children [46]. Recently, analysis of the H. werneckii proteome suggests the interaction of progesterone with the cell growth and reproduction sig- nalling pathways [42]. In the present study we have focused on progesterone biotransformation and its contribution to pro- gesterone detoxification in different phases of growth of the yeast. We provide evidence for the activation of some of the processes which might, like induction of proteins and remod- elling of the cell wall, contribute to adaptation of the yeast to the presence of progesterone and hence its effective escape from growth arrest. 2. Experimental 2.1. Strains and materials The B-763 H. werneckii strain from the microbial culture col- lection of National Institute of Chemistry, Ljubljana, Slovenia (MZKI) was maintained and grown as described [47]. Steroids were obtained either from Sigma (St. Louis, MO) or from Steraloids Inc. (Wilton, U.S.A.). (1,2,6,7- 3 H) progesterone was supplied by NEN Du Pont (Dreiech, Germany). Lyticase, a -1, 3- glucanase from Arthrobacter luteus, was obtained from Sigma. All other chemicals were of analytical grade and obtained from standard suppliers. 2.2. Biotransformation of progesterone and product identification H. werneckii was grown at 28 C in YNB growth medium until early or late logarithmic and stationary growth phase. Yeast cells were obtained by centrifugation and resuspended in the growth medium to an optical density of A 600 = 2.5. After the addition of progesterone in N,N-dimethyl formamide (DMF) to 64 M final conc., biotransformation took place at 28 C for 24 h in the absence or presence of cycloheximide, 5 g/ml final conc. Steroids were extracted with chloroform and separated by TLC [48]. The Rf values of the biotrans- formation products were compared to those of standard steroids. The respective areas were scraped off, eluted with chloroform/methanol (1:1) and the structures of the biotrans- formation products confirmed by GC–MS analysis as described [48]. 2.3. Determination of progesterone biotransformation profile To elucidate the progesterone biotransformation profile the (1,2,6,7- 3 H) progesterone, 16 kBq/ml final conc., was submit- ted to biotransformation in the presence of 16 M unlabelled progesterone, under the same conditions as described above. The steroids were extracted with chloroform and separated by TLC as above. Radioactive compounds were visualized by fluorography after spraying the air-dried plates with 10% 2,5- diphenyloxazolone [48]. In a parallel experiment TLC separated labelled steroids were scraped off and evaluated quantitatively in a liquid scintillation counter (LKB 1214 Rackbeta liquid scintillation counter). 2.4. Growth inhibition assay The growth inhibition assay was performed by growing H. werneckii on YNB agar plates at 26 C in the presence of selected steroids. Yeast was grown to the logarithmic phase of growth and diluted to an optical density at 600 nm (OD 600 ) of 0.2. Identical volumes of 0.2 OD 600 culture, as well as of 1:10 and 1:100 serial dilutions were spotted onto agar plates containing 32 and 320 M final conc. of tested steroids. Tested compounds were dissolved in DMF and controls were prepared with the appropriate amount of the respective solvent. 2.5. Water solubility of steroids Water solubility of steroids expressed as Interactive Analysis (IA) log W was obtained by the IA LogP and LogW predictor website http://www.logp.com/.
s t e r o i d s 7 3 ( 2 0 0 8 ) 1465–1474 available at www.sciencedirect.com journal homepage: www.elsevier.com/locate/steroids Aspects of the progesterone response in Hortaea werneckii: Steroid detoxification, protein induction and remodelling of the cell wall Lidija Križančić Bombek a , Ajda Lapornik a , Marjeta Ukmar a , Maja Matis a,b,c , Bronislava Črešnar a , Jasna Peter Katalinić b,c , Marija Žakelj-Mavrič a,∗ a Institute of Biochemistry, Faculty of Medicine, University of Ljubljana, Vrazov trg 2, SI-1000 Ljubljana, Slovenia Institute for Medical Physics and Biophysics, Faculty of Medicine, University of Muenster, Robert-Koch Strasse 31, D-48149 Muenster, Germany c Institute of Molecular Medicine and Genetics, Medical College of Georgia, 1120 15th Street, Augusta, GA 30912, USA b a r t i c l e i n f o a b s t r a c t Article history: Progesterone in sublethal concentrations temporarily inhibits growth of Hortaea werneckii. Received 15 October 2007 This study investigates some of the compensatory mechanisms which are activated in Received in revised form the presence of progesterone and are most probably contributing to escape from growth 30 July 2008 inhibition. These mechanisms lead on the one hand to progesterone biotransforma- Accepted 11 August 2008 tion/detoxification but, on the other, are suggested to increase the resistance of H. werneckii Published on line 28 August 2008 to the steroid. Biotransformation can detoxify progesterone efficiently in the early logarithmic phase, with mostly inducible steroid transforming enzymes, while progesterone Keywords: biotransformation/detoxification in the late logarithmic and stationary phases of growth is Biotransformation not very efficient. The relative contribution of constitutive steroid transforming enzymes Detoxification to progesterone biotransformation is increased in these latter phases of growth. In the Hortaea werneckii presence of progesterone, activation of the cell wall integrity pathway is suggested by the Cell wall overexpression of Pck2 which was detected in the stationary as well as the logarithmic phase Yeast proteomics of growth of the yeast. Progesterone treated H. werneckii cells were found to be more resistant to cell lysis than mock treated cells, indicating for the first time changes in the yeast cell wall as a result of treatment with progesterone. © 2008 Elsevier Inc. All rights reserved. 1. Introduction Steroid hormones are signalling molecules that regulate a host of organismal functions, exerting their actions by binding to the plasma membrane or intracellular receptors of the target cells. Steroids are hydrophobic and relatively stable molecules which cannot be degraded and used as a source of energy in higher organisms. After fulfilling their task they are deactivated, transformed into more soluble forms and excreted via urine and bile into the environment [1]. In contrast to higher organisms microorganisms are capable of biotransformation and even mineralization of steroids [2,3]. Numerous microorganisms that inhabit human and animal tissues, such as the skin and urinary and gastrointestinal tracts [4,5], come into contact with steroid hormones and can transform them [6–10]. After their release from the organisms, steroids are further degraded by mixtures of microorganisms in the sewage treatment plants and the environment [11–14]. These processes are very important because of the effects that undegraded steroid hormones can have on wildlife and on Corresponding author. Tel.: +386 1 543 76 45; fax: +386 1 543 76 41. E-mail address: Marija.Zakelj-Mavric@mf.uni-lj.si (M. Žakelj-Mavrič). 0039-128X/$ – see front matter © 2008 Elsevier Inc. All rights reserved. doi:10.1016/j.steroids.2008.08.004 ∗ 1466 s t e r o i d s 7 3 ( 2 0 0 8 ) 1465–1474 man [15,16]. However, the environmental fate and the rate of mineralization of naturally produced steroid hormones are so far poorly characterized. Biotransformation of steroid hormones in the environment takes place with mixtures of microorganisms, mostly bacteria, and the contribution of individual species is not known precisely. The importance of individual microorganisms for the production of commercially important steroids was first realized in 1952 when Peterson and Murray of the Upjohn Company patented the process of 11␣-hydroxylation of steroids by Rhizopus species [17]. Certain of the synthetic chemistry steps have since been replaced by specific microbial transformations which are able to achieve stereo- and regiospecific conversions of the substrates [18–22]. A currently important area is the use of genetic engineering to improve the capabilities of microorganisms as steroid-transforming agents [19,23]. In addition, microorganisms which are adapted to extreme environments have recently gained great interest due to their specific characteristics [24]. The primary interest in steroid biotransformation was at first focused on steroids and the production of commercially valuable products. With time it became evident that steroid hormones can provoke changes in microorganisms. Interest in these changes was increased when the levels of steroid hormones were suggested to affect susceptibility to fungal infection [25–32]. Experiments with exogenous steroids have confirmed the effects of steroids on fungal growth [33–40]. During exposure of microorganisms to steroid hormones, the expression of several members of various gene families is increased [41–43]. Steroid transforming enzymes were connected with defence against steroids. Microorganisms are thought to induce enzymes that detoxify steroids by transforming them into more soluble and less toxic forms [33]. The contribution of constitutive steroid transforming enzymes to steroid detoxification is presently not clear [44]. Our studies of progesterone/yeast interaction have been focused on the halophilic black yeast Hortaea werneckii. The natural habitat of this eukaryotic microorganism is hypersaline water [45] but it is also known as the causative agent of Tinea nigra, a nonpathologic dermal change of the palms, more frequently observed in females and children [46]. Recently, analysis of the H. werneckii proteome suggests the interaction of progesterone with the cell growth and reproduction signalling pathways [42]. In the present study we have focused on progesterone biotransformation and its contribution to progesterone detoxification in different phases of growth of the yeast. We provide evidence for the activation of some of the processes which might, like induction of proteins and remodelling of the cell wall, contribute to adaptation of the yeast to the presence of progesterone and hence its effective escape from growth arrest. 2. Experimental 2.1. Strains and materials (MZKI) was maintained and grown as described [47]. Steroids were obtained either from Sigma (St. Louis, MO) or from Steraloids Inc. (Wilton, U.S.A.). (1,2,6,7-3 H) progesterone was supplied by NEN Du Pont (Dreiech, Germany). Lyticase, a ␤-1, 3glucanase from Arthrobacter luteus, was obtained from Sigma. All other chemicals were of analytical grade and obtained from standard suppliers. 2.2. Biotransformation of progesterone and product identification H. werneckii was grown at 28 ◦ C in YNB growth medium until early or late logarithmic and stationary growth phase. Yeast cells were obtained by centrifugation and resuspended in the growth medium to an optical density of A600 = 2.5. After the addition of progesterone in N,N-dimethyl formamide (DMF) to 64 ␮M final conc., biotransformation took place at 28 ◦ C for 24 h in the absence or presence of cycloheximide, 5 ␮g/ml final conc. Steroids were extracted with chloroform and separated by TLC [48]. The Rf values of the biotransformation products were compared to those of standard steroids. The respective areas were scraped off, eluted with chloroform/methanol (1:1) and the structures of the biotransformation products confirmed by GC–MS analysis as described [48]. 2.3. Determination of progesterone biotransformation profile To elucidate the progesterone biotransformation profile the (1,2,6,7-3 H) progesterone, 16 kBq/ml final conc., was submitted to biotransformation in the presence of 16 ␮M unlabelled progesterone, under the same conditions as described above. The steroids were extracted with chloroform and separated by TLC as above. Radioactive compounds were visualized by fluorography after spraying the air-dried plates with 10% 2,5diphenyloxazolone [48]. In a parallel experiment TLC separated labelled steroids were scraped off and evaluated quantitatively in a liquid scintillation counter (LKB 1214 Rackbeta liquid scintillation counter). 2.4. The growth inhibition assay was performed by growing H. werneckii on YNB agar plates at 26 ◦ C in the presence of selected steroids. Yeast was grown to the logarithmic phase of growth and diluted to an optical density at 600 nm (OD600 ) of 0.2. Identical volumes of 0.2 OD600 culture, as well as of 1:10 and 1:100 serial dilutions were spotted onto agar plates containing 32 and 320 ␮M final conc. of tested steroids. Tested compounds were dissolved in DMF and controls were prepared with the appropriate amount of the respective solvent. 2.5. The B-763 H. werneckii strain from the microbial culture collection of National Institute of Chemistry, Ljubljana, Slovenia Growth inhibition assay Water solubility of steroids Water solubility of steroids expressed as Interactive Analysis (IA) log W was obtained by the IA LogP and LogW predictor website http://www.logp.com/. s t e r o i d s 7 3 ( 2 0 0 8 ) 1465–1474 2.6. Lyticase sensitivity assay Structural changes in the cell wall of H. werneckii were monitored as described [49], using lyticase as the enzyme source. H. werneckii cells in the early logarithmic phase were exposed to 320 ␮M steroids (progesterone and other selected steroids), 32 ␮M progesterone, DMF (control) or Calcofluor White in a 100 ␮g/ml final conc. (positive control) for 4 h. After treatment the cells were harvested, washed with TE buffer (10 mM Tris–HCl, 1 mM EDTA, pH 7.5) and resuspended in 1.5 ml of the same buffer at OD600 of approximately 0.2. After the addition of lyticase in 220 U/ml final conc., cell lysis was followed at room temperature by measuring OD600 of the cell suspensions every 10 min up to 1 h. 2.7. Protein sample preparation and protein labelling H. werneckii cultures growing in the stationary phase of growth were either exposed to 32 ␮M progesterone or mock treated with DMF (control). After 4 h, progesterone treated cells and the control were harvested, washed with PGSK buffer (3.8 mM NaH2 PO4 , 49.4 mM Na2 HPO4 , 48.4 mM NaCl, 5 mM KCl, 61 mM glucose), frozen in liquid nitrogen, pelleted and mechanically disintegrated as described [42]. Powdered frozen lysates were then resuspended in lysis buffer (4% (w/v) CHAPS, 2 M thiourea, 7 M urea, 30 mM Tris–HCl, pH 8.5), sonicated and centrifuged at maximum speed for 10 min at 4 ◦ C in a tabletop centrifuge. Proteins from cell lysates were delipidated and desalted by chloroform/methanol extraction, washed with methanol and dissolved in lysis buffer. Protein concentration was determined with Bradford reagent (BIO-RAD). Proteins were labelled with CyDye DIGE Fluors Cy3 and with Cy5 (Amersham Biosciences, Upssala, Sweden); the two samples were combined and analyzed as described [42]. 2.8. identified proteins from the logarithmic phase of growth. The identity of the spots of interest was confirmed using mass spectrometric analysis as described [42]. 2.10. Isolation of RNA and Northern hybridisation H. werneckii in the early logarithmic, late logarithmic and stationary phases of growth was exposed to 320 ␮M progesterone or mock treated with DMF (control) for 10, 25 or 50 min. Total RNA was isolated as described [50]. The electrophoresis of RNA, reversible staining of RNA blots with methylene blue and hybridisation using 0.5 kb PvuII fragment of cDNA encoding Hsp-1 of fungus Rhizopus nigricans were carried out as described [43]. 3. Results 3.1. Progesterone biotransformation profiling Progesterone biotransformation was followed using radioactively labelled progesterone in the absence and presence of cycloheximide with H. werneckii cells from the early logarithmic, late logarithmic and stationary phases of growth. Progesterone was transformed into products with 98% efficiency with H. werneckii cells from the early logarithmic phase (Fig. 1, line 1). Quantitatively the main product was 11␣-hydroxy-progesterone which represented 34% of all the Protein separation and visualization Proteins were separated and visualized as described [42]. They were separated in the first dimension on IPG gels of pIs in the pH 4–7 range on an IPGpfor (Amersham Biosciences, Uppsala, Sweden). After isoelectric focusing the IPG strips were transferred on to 12% polyacrylamide gels and electrophoresed in an Ettan DALTtwelve system (Amersham Biosciences, Uppsala, Sweden) overnight at 2 W per gel at 18 ◦ C. 2D gels were scanned directly between glass plates with a Typhoon Imager (Amersham Biosciences, Upssala, Sweden) with the excitation and emission wavelengths for Cy3 and Cy5. Scanned gels were fixed in 10% methanol, 7% acetic acid for 2 h, stained in Sypro Ruby stain (BIO-RAD) overnight, destained (10% methanol, 7% acetic acid) for 1 h and scanned with the appropriate wavelength for Sypro Ruby stain. Differentially expressed proteins were determined as described [42]. 2.9. 1467 Mass spectrometry analysis H. werneckii proteins from the stationary phase of growth were separated on 2D gels and compared to those of the previously Fig. 1 – Autoradiogram of the progesterone biotransformation products separated by TLC. Lines represent biotransformation profiles of radiolabelled progesterone with H. werneckii from the early (1 and 2), late logarithmic (3 and 4), and stationary (5 and 6) phases of growth. The biotransformations were performed in the absence (1, 3 and 5) and presence (2, 4 and 6) of cycloheximide. 5␣P: 5␣-pregnane-3,20-dione; Ta: testosterone acetate; P: progesterone; A: androstenedione; 20␣OHP: 20␣-hydroxy-progesterone; T: testosterone; 14OHP: 14-hydroxy-progesterone; 6␣OHP: 6␣-hydroxy-progesterone; 11␣OHP: 11␣-hydroxy-progesterone mark the Rf values of the main identified products. 1468 s t e r o i d s 7 3 ( 2 0 0 8 ) 1465–1474 Table 1 – Some characteristics of progesterone biotransformation by H. werneckii Type of biotransformation Identified progesterone biotransformation products Effect of cycloheximide Prevailing growth phase Hydroxylation 11␣-Hydroxy-progesterone 14-Hydroxy-progesterone 6␣-Hydroxy-progesterone I Early logarithmic Side chain cleavage Testosterone acetate Androstenedione Testosterone NSI Late logarithmic and stationary Reduction 4-Pregnen-20␣-ol-3-one 5␣-Pregnane-3,20-dione Pregnan-3-ol-20-one Pregnane-3,20-diol NSI All phases I – significant inhibition of the respective biotransformation detected; NSI – no significant inhibition of the respective biotransformation detected. recovered steroids. The involvement of inducible steroid transforming enzymes in progesterone biotransformation was suspected on the basis of the changed biotransformation profile in the presence of cycloheximide (Fig. 1, line 2). The presence of this inhibitor resulted in an increase of the percentage of untransformed progesterone from 2% to 35%, the amount of the recovered 11␣-hydroxyprogesterone was lowered to 8% while the amount of recovered androstenedione increased to 20% of the recovered steroids. In contrast, in the late logarithmic and stationary phases of growth, progesterone was transformed less effectively, with only 30% efficiency (Fig. 1, lines 3 and 5). Androstenedione was found to be the most important product, representing 15% of all the recovered steroids, while the amount of 11␣-hydroxy-progesterone was lowered to 3%. The presence of cycloheximide did not significantly affect the biotransformation with H. werneckii cells from the late logarithmic or stationary phase of growth (Fig. 1, lines 4 and 6). Analysis of the respective biotransformation products revealed three main types of reactions: hydroxylation at different sites of the steroid nucleus, cleavage of the progesterone side chain at C17 and reduction of the 3- and/or 20-keto groups and 4 -double bond (Table 1, Fig. 1). Hydroxylation prevailed in the early logarithmic phase of yeast growth and was catalyzed by inducible enzymes, while side chain cleavage occurred predominantly in the late logarithmic and stationary phases of growth and was not affected by the presence of cycloheximide (Fig. 1, Table 1). Reduction was a minor reaction and was catalyzed by constitutive enzymes in all phases of growth of H. werneckii (Table 1). Seven additional progesterone biotransformation products were identified; most of them were formed with H. werneckii from the early logarithmic phase. Pregnane-3,6,20-trione, pregna-4,7-diene-3,20-dione, pregna-4,16-diene-3,20-dione, methyl-testosterone, pregnane-3,20-dione, 21-hydroxyprogesterone and pregnenolone were present in small amounts and were not expected to contribute significantly to progesterone detoxification. The presence of very small amounts of additional steroids in the respective TLC areas (Fig. 1) cannot be excluded. 3.2. The contribution of different steroid transforming enzymes to progesterone detoxification The contribution of the individual biotransformation reactions to progesterone detoxification was estimated by comparing the inhibitory action of selected progesterone biotransformation products on the growth of H. werneckii with that of progesterone. All the tested progesterone derivatives were found to be less toxic than progesterone. Hydroxylation of progesterone, e.g., at the 11␣ position, prevails in the early logarithmic phase (Table 1) and can be considered as effective detoxification (Table 2). Induction of hydroxylases in this phase of growth contributes to the defence of the yeast. The most problematic modification of progesterone from the viewpoint of detoxification is the cleavage of the side chain of progesterone. Androstenedione, as one of the important products of this modification, was found to be only slightly less toxic than progesterone (Table 2). This steroid was detoxified when androstenedione was reduced to non-toxic testosterone in a reaction catalyzed by a constitutive 17␤-hydroxysteroid dehydrogenase (17␤-HSD) from H. werneckii (Table 2). Since the equilibrium of the reaction with the 17␤-HSD was found to be shifted towards reduction [51], constitutive 17␤-HSD contributes to steroid detoxification. The third type of reaction, e.g., reduction of the 20-keto group of progesterone, was only slightly less effective than hydroxylation of the steroid (Table 2). 3.3. Polarity of progesterone biotransformation products and their toxicity Hydroxylation of progesterone was found to increase water solubility of the steroid, as suggested by the predicted IA log W values for the hydroxylated derivatives of progesterone. At the same time, a decrease of toxicity was observed, as shown for 11␣-hydroxy-progesterone (Table 2). The connection between the polarity of progesterone derivatives and their toxicity was further investigated by growth inhibition assays with a water-soluble form of progesterone (progesterone WS) and pregnenolone. Neither steroid, with higher water solubilities than progesterone, was found to inhibit H. werneckii growth (Table 2). The same effect was s t e r o i d s 7 3 ( 2 0 0 8 ) 1465–1474 Table 2 – Water solubility of progesterone biotransformation products and other selected steroids and their potency in inhibiting H. werneckii growth Steroid IA log W H. werneckii growth inhibition Substrate Progesterone −4.72 I Biotransformation products 11␣-Hydroxy-progesterone 14-Hydroxy-progesterone 6␣-Hydroxy-progesterone Testosterone acetate Androstenedione Testosterone 4-Pregnen-20␣-ol-3-one 5␣-Pregnane-3,20-dione Pregnan-3-ol-20-one Pregnane-3,20-diol −3.44 −3.76 nd −4.64 −4.40 −4.20 −4.57 −4.84 −4.75 −5.00 NSI nd NSI nd I NSI i NSI NSI NSI Other selected steroids Pregnenolone Progesterone WS 11␤-Hydroxy-androstenedione 5␣-Androstane-3,17-dione 5␤-Androstane-3,17-dione 17␣-Methyl-testosterone 4-Estrene-3,17-dione −4.17 Water soluble −3.42 −4.43 −4.43 −4.42 −4.02 NSI NSI NSI I I i I I – stronger inhibition of H. werneckii growth at 320 ␮M and weak at 32 ␮M concentration of the respective steroid; i – weak inhibition of H. werneckii growth at 320 ␮M concentration and no significant inhibition at 32 ␮M concentration of the respective steroid; NSI – no significant inhibition detected; nd – not determined; IA log W – predicted water solubility of steroids as obtained by interactive analysis (IA) predictor website http://www.logp.com/. observed when the toxicity of androstenedione was compared to that of 11␤-hydroxy-androstenedione (Table 2). On the other hand an additional nonpolar methyl group of 17␣-methyltestosterone lowered water solubility and resulted in slightly increased toxicity (Table 2). These results are in accordance with the above hypothesis that reactions which increase water solubility of the steroid decrease its toxicity. A closer look at the products of the second group of reactions, which lead to C19 steroids, shows that the transformed products are also more water soluble than progesterone, although the increase is much smaller than that for hydroxylated derivatives of progesterone. Of these derivatives, androstenedione was still found to inhibit growth of H. werneckii only slightly less efficiently than progesterone. The reduction reactions of progesterone from the third group of progesterone biotransformations resulted in products with only slightly increased, as for 4-pregnen-20␣-ol-3one, or even decreased water solubility (Table 2). None of these products was found to be an inhibitor of H. werneckii growth. 3.4. Common structural characteristics of H. werneckii inhibitory steroids Progesterone and androstenedione, both toxic to H. werneckii, contain a 3-keto-4-ene structure and an additional keto group 1469 at C20 or C17. Therefore a steroid with the same functional groups from the estrane series, 4-estrene-3,17-dione, was tested for its toxicity on the yeast. It was also found to be toxic (Table 2), suggesting some of the common structural characteristics of steroids toxic to H. werneckii. In addition, two steroids of alternative stereochemistry, 5␣androstane-3,17-dione and 5␤-androstane-3,17-dione, were found to inhibit growth of H. werneckii with almost the same efficiency (Table 2). 3.5. The expression of the selected proteins in H. werneckii in the presence of progesterone We studied the effect of progesterone on the expression of H. werneckii proteins during the logarithmic and stationary phases of growth. Protein kinase C-like 2 (Pck2) and proliferating cell nuclear antigen (PCNA) were overexpressed in the presence of progesterone during the stationary phase of growth (Fig. 2). This is in accordance with our previous results showing an increase during logarithmic phase [42]. Hsp70 was not observed as one of the identified proteins with changed expression level during stationary phase. Its level did not change significantly in response to the steroid (Fig. 2), in contrast to Hsp70 overexpression in the presence of progesterone during the logarithmic phase of growth [42]. To further evaluate the changes following application of progesterone, we determined the H. werneckii Hsp70 transcript level by Northern blot analysis. Temporal analyses of Hsp70 mRNA abundance were carried out during treatment of the yeast grown to the early logarithmic, late logarithmic and stationary phases with progesterone (Fig. 3). The Hsp70 mRNA level was nearly undetectable when DMF was added to the growth medium in the early logarithmic and late logarithmic phases of growth, while the transcript level of Hsp70 was increased within 10 min of exposure of yeast to progesterone. In contrast, in the stationary phase of H. werneckii growth the amount of Hsp70 mRNA is nearly the same before and after exposure of the yeast to progesterone (Fig. 3). 3.6. Changes in the cell wall of H. werneckii in the presence of progesterone Possible structural changes in the cell wall of H. werneckii as a result of exposure to progesterone were investigated using the lyticase sensitivity assay. The results indicate decreased sensitivity to lyticase for H. werneckii cells treated with progesterone (Fig. 4). The effect was most clearly seen with cells from the early logarithmic phase of growth, but could only just be observed with cells from the stationary phase of growth (data not shown). The effect was found to be specific for the free form of progesterone, being only just observed with the water-soluble form of progesterone (Fig. 4A). Exposure of H. werneckii cells to progesterone resulted in an effect similar to that on exposure to Calcofluor White and concentration dependent (Fig. 4B) but was only just observed with the nontoxic steroid 11␣-hydroxy-progesterone (Fig. 4A). Intra-assay variability of the results of duplicate experiments was low (data not shown) while inter-assay/inter-sample variability was higher. The results suggest some differences in the cell 1470 s t e r o i d s 7 3 ( 2 0 0 8 ) 1465–1474 Fig. 2 – The effect of progesterone on the expression of proteins in H. werneckii during the stationary phase of growth. (A) Overlay of 2D-GE images of control sample (green) and progesterone-stimulated sample (red). (B) Enlarged regions of the identified proteins. On the left are images of gels loaded with control sample and on the right gels loaded with progesterone-stimulated sample. The arrows point to heat shock protein 70 (Hsp70), proliferating cell nuclear antigen (PCNA), and protein kinase C-like 2 (Pck2). (For interpretation of the references to colour in this figure legend, the reader is referred to the web version of the article.) wall composition between the cultures grown for each individual experiment (Fig. 4). 4. Discussion The biotransformation of progesterone has been studied extensively during the last decades [3,20,35,52–65]. It was found to affect the growth of different eukaryotic microorganisms [33–40], provoke the induction of steroid hydroxylating enzymes [33,66–68], trigger the induction of heat shock proteins [43] and ABC transporters [69–71]. In an expression profiling of the progesterone response in Saccharomyces cerevisiae, 163 genes were found to be upregulated and 40 downregulated [41]. In our previous study progesterone was found to cause a transitional arrest of cell growth and a change in gene expression in H. werneckii [42]. Here, we were interested in progesterone biotransformation/detoxification by the same microorganism. The major progesterone biotransformation products suspected to have the greatest effect on progesterone detoxification were identified from different phases of H. werneckii growth (Table 1). We compared the amounts of identified products obtained during biotransformation in the absence and presence of cycloheximide. In this way we were able to study the contribution of different types of biotransformation to progesterone detoxification and suggest the role of constitutive and inducible steroid transforming enzymes. The results show that induction of steroid transforming enzymes by progesterone constitutes an effective part of the defence of the yeast in the early logarithmic phase of growth. Our data confirm the hypothesis that reactions with inducible steroid transforming enzymes, e.g. hydroxylases, increase the polarity of steroids and effectively contribute to their detoxification (Tables 1 and 2). This type of defence is less effective in the late logarithmic and stationary phases of growth of H. werneckii. The yield of biotransformation products in these phases of growth is much lower and some of the products, e.g. androstenedione, are still toxic (Fig. 1 and Table 2). The yeast appears not to be able to respond, by increasing the expression of detoxifying enzymes, to the same extent as in the early logarithmic phase of growth. In the late logarithmic and stationary phases the relative contribution of constitutive steroid transforming enzymes, e.g., 17␤-HSD, is increased. These enzymes are less effective in detoxifying progesterone and its derivatives. At the same time we could not establish a clear relationship between the water solubility of biotransformation products of constitutive steroid transforming enzymes and their toxicity (Table 2). Steroids that inhibit growth of H. werneckii, e.g., progesterone, androstenedione, 4-estrene-3,17-dione, possess common structural characteristics. Our results show that partial or complete detoxification of progesterone or its derivative androstenedione can be achieved by e.g., reduction of 20- or 17-keto groups, which appear to be important for the toxicity of the respective steroids. However, the stereochemistry of steroids has almost no effect on the effectiveness of H. werneckii growth inhibition, as shown for the stereochemically different 5␣-androstane-3,17-dione and 5␤-androstane-3,17dione (Table 2). Progesterone biotransformation is just one of the processes that might contribute to the escape of the H. werneckii from growth arrest. Recently, H. werneckii cells treated with progesterone in the logarithmic phase of growth were investigated and the overexpression of Pck2 was noted [42]. In the present study we show that progesterone provokes an increase in Pck2 levels in H. werneckii in the stationary phase of growth (Fig. 2). These results are in accordance with the observation that quiescent cells are still able to respond to environmental signals by inducing the expression of genes similar to those in proliferating cells, despite their increased resistance to environmental stress [72,73]. Pck2 is a member of the cell wall integrity pathway which is activated under the conditions that jeopardize cell wall stability [74]. The mechanism by which progesterone stimu- s t e r o i d s 7 3 ( 2 0 0 8 ) 1465–1474 1471 Fig. 3 – Temporal analysis of Hsp70 mRNA levels during treatment of H. werneckii with progesterone. The H. werneckii cells in early, late logarithmic and stationary phases of growth were exposed to N,N-dimethylformamide (DMF) alone (C) and, for the indicated times (min), to 320 ␮M progesterone. Total RNA blots were prepared, stained reversibly (lower panels) and hybridised (upper panels) as described in Section 2.10. lates the induction of Pck2 and its activation in H. werneckii is not known. Steroid hormones are most probably, because of their low solubility, present in aqueous medium as a suspension [75]. During the process of crossing the cell wall and cell membrane, progesterone and other toxic steroids might therefore cause an acute stretching of the plasma membrane and/or otherwise modify the plasma membrane, thus acti- Fig. 4 – The effect of selected steroids on the susceptibility of H. werneckii to lytic action by lyticase. Yeast cells from the early logarithmic phase were treated for 4 h with: (A) progesterone (P), 11␣-hydroxy-progesterone (11␣OHP), water soluble form of progesterone (PWS) or N,N-dimethylformamide (DMF) alone; (B) progesterone (P), lower concentration of progesterone (Plow ), Calcofluor White (CFW) or DMF alone. The steroid concentrations were 320 ␮M; progesterone Plow was 32 ␮M. The percentage of the initial absorption A600 after the addition of lyticase (220 U/ml final conc.) is presented. Data are means ± standard deviations of at least three independent experiments performed in duplicate. vating specific cell surface sensor proteins [74]. On the other hand perturbation of the plasma membrane affects the activity of the plasma membrane-bound enzymes involved in cell wall synthesis and indirectly weakens the cell wall [76]. It has been shown that chitosan, as a plasma membrane perturbing substance, which can bind membrane phospholipids, affects the cell wall integrity pathway [77]. In our study we were interested in changes that progesterone might provoke in the plasma membrane of H. werneckii. Measurements of the fluidity of the H. werneckii membrane showed no detectable changes following the addition of progesterone (M. Turk and M. Žakelj-Mavrič, unpublished results). Cell wall stress provokes a global transcriptional response in S. cerevisiae [78]. The cell wall integrity pathway is activated with the help of specific plasma membrane sensor proteins, leading finally to alterations in the cell wall [74,78–80]. In S. cerevisiae and Schizosaccharomyces pombe the components of the cell wall integrity pathway, e.g. protein kinase C homologues pkc1 and pck1p/pck2p, respectively, have been extensively studied and their cell wall targets identified [74,78,81–85]. The pathway was suggested to be conserved in several yeasts and filamentous fungi [86–88]. Although in H. werneckii the cell wall integrity pathway has not yet been investigated, the overexpression of Pck2, and most probably its increased activity in the presence of progesterone, suggested that changes in the cell wall could be one of the possible effects of progesterone action. In our study we showed for the first time that structural changes occur in the cell wall of H. werneckii treated with progesterone, treated H. werneckii cells being more resistant to cell lysis (Fig. 4). The effect is specific for the free form of progesterone and was not detected with H. werneckii cells exposed to 11␣-hydroxy-progesterone. The effect of progesterone is comparable to that of Calcofluor White which has been shown to hinder normal cell wall assembly in S. cerevisiae and consequently activate the cell wall integrity pathway [89]. Our results suggest that changes in the H. werneckii cell wall induced by progesterone most probably contribute to an adaptation of the yeast to the presence of the steroid. Another protein whose biosynthesis is stimulated in the presence of progesterone in the logarithmic [42] and stationary phases of growth is proliferating cell nuclear antigen (PCNA) (Fig. 2). PCNA has an essential role in the nucleic acid 1472 s t e r o i d s 7 3 ( 2 0 0 8 ) 1465–1474 metabolism of all eukaryotes. It can interact with a large number of proteins and is involved in several processes, e.g., DNA replication, DNA repair, cell cycle regulation, and apoptosis [90]. The role of increased expression PCNA in progesterone stimulated H. werneckii cells however remains unclear. Although cells of H. werneckii in the stationary phase of growth are able to respond to stress triggered by progesterone by increasing the expression of proteins such as Pck2 and PCNA, they are not able to increase the levels of Hsp70 mRNA and protein (Figs. 2 and 3). One explanation is that cells of H. werneckii in the stationary phase of growth are most probably stressed due to lack of nutrients. This could be the reason for the increased levels of Hsp70 mRNA and protein in untreated cells from the stationary phase of growth. These levels do not increase when progesterone is added. Finally, the question remains as to whether the response to progesterone is unique for H. werneckii. On the basis of preliminary experiments on S. cerevisiae (data not shown) and some published data [32,41,91,92] we believe it is not unique to H. werneckii, although the extent of the response is most probably yeast cell specific. The results presented in this paper lead to the conclusion that progesterone is toxic to H. werneckii, inhibiting its growth. Progesterone biotransformation contributes to an escape from growth arrest of the yeast, most efficiently in the early logarithmic phase of growth. The overexpression of Pck2 in the presence of progesterone suggests the cell wall as one of the possible targets of progesterone action. The progesterone induced changes observed in the yeast cell wall most probably contribute to an adaptation of the yeast to the presence of the steroid. Acknowledgements This work was supported by the research grant P1-0170-0381 from the Slovenian Research Agency. The instrumentation used for mass spectrometry analysis of proteins was financed by the Georgia Research Alliance Grant to the IMMAG, MCG, GA, USA. We are indebted to Professor R.K. Yu (MCG, GA) for ongoing support. The authors thank Dr. Dušan Žigon from the Jožef Stefan Institute for the GC–MS analysis of steroids. 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