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Endocrinology Vol. 142, No. 5 1841-1848
Copyright © 2001 by The Endocrine Society


ARTICLES

17ß-Estradiol Treatment Decreases Steroidogenic Enzyme Messenger Ribonucleic Acid Levels in the Rainbow Trout Testis1

Marina Govoroun2, Oonagh Marie McMeel2, Hocine Mecherouki, Terry J. Smith and Yann Guiguen

Institut National de la Recherche Agronomique, Laboratoire Institut National de la Recherche Agronomique-Station Commune de Recherches en Ichtyophysiologie, Biodiversité et Environement, Campus de Beaulieu (M.G., H.M., Y.G.), 35042 Rennes Cedex, France; and National Diagnostics Center, BioResearch Ireland, National University of Ireland (O.M.M., T.J.S.), Galway, Ireland

Address all correspondence and requests for reprints to: Dr. Yann Guiguen, Laboratoire Institut National de la Recherche Agronomique-Station Commune de Recherches en Ichtyophysiologie, Biodiversité et Environement, Campus de Beaulieu, 35042 Rennes Cedex, France. E-mail: guiguen{at}beaulieu.rennes.inra.fr


    Abstract
 Top
 Abstract
 Introduction
 Materials and Methods
 Results
 Discussion
 References
 
In fish, estrogens are well known for their involvement in ovarian differentiation and have been shown to be very potent feminizing agents when administrated in vivo during early development. However, the mechanism of action of exogenous estrogens is poorly understood. We report here on the feminizing effects of estrogen treatment on the testicular levels of some steroidogenic enzyme messenger RNAs [mRNAs; cholesterol side-chain cleavage (P450scc), 17-hydroxylase/lyase (P450c17), 3ß-hydroxysteroid dehydrogenase (3ßHSD), 11ß-hydroxylase (P45011ß), and aromatase (P450aro)] in the rainbow trout, Oncorhynchus mykiss. Treatment was carried out by dietary administration of 17ß-estradiol (E2; dosage of 20 mg/kg diet) to a genetically all male population. Steroidogenesis in the differentiating testis was demonstrated to be strongly altered by E2, as this treatment resulted in considerable decrease in P450c17, 3ßHSD, and P45011ß mRNAs after only 10 days of treatment. In contrast, P450scc and P450aro mRNA levels were unaffected by E2, with P450scc mRNA levels remaining unaltered and P450aro not stimulated by this feminizing estrogen treatment. To better characterize this E2 effect, the same treatment was applied on postdifferentiating males, and roughly the same expression pattern was detected with a considerable decrease in testicular P450c17, 3ßHSD, and P45011ß mRNAs and a significant, but reduced, decrease in P450scc mRNA. In the interrenal, these steroidogenic enzyme mRNAs were not significantly affected by this E2 treatment, except for a slight, but significant, decrease in P450scc mRNA. These results clearly demonstrate that estrogens have profound effects on testicular steroidogenesis and that they are acting specifically on the testis by decreasing mRNA steady state levels of many steroidogenic enzyme genes. The decrease in P45011ß mRNA, and thus inhibition of the synthesis of testicular 11-oxygenated androgens, may be an important step required for the active feminization of these genetic males.


    Introduction
 Top
 Abstract
 Introduction
 Materials and Methods
 Results
 Discussion
 References
 
FISH SEX differentiation, as in most nonmammalian vertebrates, is very sensitive to exogenous exposure to either steroids (1) or xenobiotics (2). In that respect, estrogens and estrogeno-mimetic xenobiotics have been shown to have profound effects on the resulting sex phenotype of fish exposed to these compounds (3). These perturbations are not specific to teleost fish, because these molecules also interfere with male physiology and fertility in mammals. However, even if these effects are well known, the mechanism of action of estrogens or estrogeno-mimetic molecules still remains poorly understood. In many nonmammalian vertebrates, including fish, estrogens are now well characterized as key hormones in the process of ovarian differentiation (1, 4, 5, 6, 7). However, their mechanisms of action remain unknown, and relatively few studies have investigated the possible downstream targets of estrogen action in the differentiating gonads of nonmammalian vertebrates (8, 9). In mammals the effects of estrogens are mediated through two estrogen receptors, namely, ER{alpha} and ERß. Recently, it has been demonstrated that female mutant mice homozygous for the targeted disruption of these two estrogen receptors ({alpha}ßERKO), exhibit some degree of morphological gonadal sex reversal together with an increase in biochemical characteristics of Sertoli cell differentiation (10). This strongly suggests that even in mammals, the estrogen response can also to some extent lead to perturbation in gonadal differentiation.

Rainbow trout (Oncorhynchus mykiss) is characterized by a male heterogametic (XY) sex determination system, and new viable male genotypes (XX or YY) can be produced by hormonal phenotypic inversion and subsequent progeny testing (11). Using these new male genotypes we can either produce all male or all female populations, allowing us to work on a whole population of fish in which the genetic and phenotypic sex is known before gonadal sex differentiation. Using these populations we investigated the effect of a classical feminizing 17ß-estradiol (E2) treatment on the testicular messenger RNA (mRNA) levels of steroidogenic enzyme genes. We first looked at the effects of estrogen treatment on the differentiating testis and secondly studied the effect of a similar treatment in postdifferentiating immature males on both the testis and the interrenal (equivalent of the mammalian adrenal) to check whether this effect was specific to the differentiating testis. Because 11ß-hydroxylase (P45011ß) and aromatase (P450aro) have already been characterized as important enzymes expressed in a sexually dimorphic fashion during gonadal sex differentiation (1, 12, 13), we also compared the mRNA levels of these two genes in the differentiating testis after E2 treatment and, in some instances, in female differentiating gonads.


    Materials and Methods
 Top
 Abstract
 Introduction
 Materials and Methods
 Results
 Discussion
 References
 
Animals
Research involving animal experimentation has been approved by the author’s institution (authorization 35–14 to Y.G.) and conforms to NIH guidelines. All male and all female populations of rainbow trout were obtained as previously described (12). E2 treatment was carried out at the Institut National de la Recherche Agronomique-SCRIBE experimental facilities (Rennes, France), by dietary administration starting from the onset of the first feeding i.e. reabsorption of the vitellin vesicle at 55 days postfertilization (dpf). E2 (Sigma, St. Louis, MO) was added to the food (dry pellet food, Aqualim, France) in ethanol (20 mg/kg diet), which was then evaporated to dryness. Fish were kept in 0.3-m3 tanks and fed ad libitum with dry pellet food. Gonads were sampled after killing the fish by decapitation, immediately frozen in liquid nitrogen, and pooled in 2-ml tubes according to their population. They were stored at -80 C until RNA extraction. For the estrogen-induced differentiation study gonads were sampled at 65 ± 2 dpf in all male control populations (duplicates of 752 and 781 gonads) and in all male populations treated with E2 (20 mg/kg food) for 10 days from the onset of the first feeding (duplicates of 778 and 500 gonads). For comparison by semiquantitative RT-PCR of P45011ß and P450aro gene expression between male and female, an all female population was sampled in the same way (65 ± 2 dpf; triplicates, 499, 785, and 755 gonads). For the analysis of the kinetics of gene expression after E2 treatment, a 4-month-old (120 dpf) all male rainbow trout population was treated with E2 (20 mg/kg food) for 1 week. Fish were sampled (gonads and interrenals) before the beginning of treatment (T0) and after 8 (T8), 24 (T24), 48 (T48), 96 (T96), and 192 (T192) h. Thirty-six fish were sampled at each time point. To be able to carry out RNA extraction and Northern blot analysis, tissues were pooled in 2 batches of 18 fish.

Total RNA extraction
Total RNA was isolated from frozen gonads (-70 C) using the TRIzol reagent (Life Technologies, Inc., Grand Island, NY). TRIzol (1 ml) at 65 C was added to the gonads. The tissue was drawn through a 26-gauge needle to ensure complete lysis. The TRIzol mixture was cooled to room temperature, 200 µl chloroform were added, and it was vortexed and centrifuged for 10 min at 14,000 rpm. The aqueous phase containing the RNA was retained, and RNA was precipitated with an equal volume of isopropanol. The RNA pellet was washed with 80% ethanol, dried, and resuspended in 50 µl diethylpyrocarbonate-treated water. The concentration of RNA was determined by spectrophotometry.

Semiquantitative RT-PCR
Semiquantification by RT-PCR was performed as previously described (12). Primer sequences were: 11ß-hydroxylase sense primer, 5'-T GAC GCC CAC AAG GCC CTG C-3'; 11ß-hydroxylase antisense primer, 5'-GTG AGT TCA TTG AGA TTA CCT G-3'; aromatase sense primer, 5'-CTC TCC TCT CAT ACC TCA GG-3'; aromatase antisense primer, 5'-CCA GAC TGA ACT CAT TGG GC-3'; ß-actin sense primer, 5'-AAA GAC CCT GAG TTC ATC ATG C-3'; and ß-actin antisense primer, 5'-CCC AGT CTC CAC TAA TCC CA-3'. To work in the exponential range of amplification, the number of cycles was set at 20 for ß-actin and aromatase and 30 for P45011ß. After PCR amplification, 1 µl of each PCR reaction including appropriate controls (water only and genomic DNA) was dotted on a nylon membrane (Hybond N+, Amersham Pharmacia Biotech, Arlington Heights, IL). The membrane was then denatured (3 min) and neutralized (5 min) by capillary transfer with denaturation solution (0.5 M NaOH and 1.5 M NaCl) and neutralization solution (0.5 M Tris-HCl and 1.5 M NaCl, pH 7), and finally rinsed briefly in 2 x SCC (standard saline citrate) before UV light cross-linking. Membranes were then hybridized with the corresponding probe, i.e. P45011ß, P450aro, or ß-actin, labeled by random priming with [{alpha}-32P]deoxy-CTP following the Ready-to-Go Labeling Beads (Amersham Pharmacia Biotech) protocol. Hybridization was carried out overnight at 65 C in 5 x SCC, 5 x Denhart’s, 0.5% SDS, and 20 µg/ml denatured calf thymus DNA. Membranes were washed to high stringency in 0.1 x SSC/0.1% SDS at 65 C and then quantitatively analyzed using an Instant Imager (Packard, Downers Grove, IL). Data were expressed as logarithms of gene of interest/ß-actin ratios. With these PCR conditions no amplification was detected in either the water or the genomic DNA control, and only a single band of the expected size was detected in all other PCR reactions.

Northern blot and virtual Northern blot analysis
Northern blots were carried out on total RNA as previously described (14) except for the use of ULTRAhyb hybridization buffer (Ambion, Inc., Austin, TX). Reprobing with 28S ribosomal RNA (rRNA) was used as an internal loading control, and both specific and 28S rRNA signals were quantified using an Instant imager (Packard). Because of the limiting amount of tissue available, techniques such as classical Northern blot were not feasible on differentiating gonads; thus, we used virtual Northern blots, as this technique has been shown to be both very sensitive and quantitative (15, 16). Virtual Northern blots were performed as previously described (12), except that the complete PCR reactions were precipitated with ammonium acetate (50 µl 4 M ammonium acetate and 375 µl 95% ethanol) and resuspended in 20 µl sterile water. Ten to 20 µl of this amplified complementary DNA (cDNA) solution were then loaded on a 1% Tris-borate EDTA/agarose gel. After migration, the gel was denatured and neutralized, and DNA was transferred to a nylon membrane (Hybond-N, Amersham Pharmacia Biotech) by capillary Southern blotting in 20 x SSC. DNA was fixed to the membrane by baking at 80 C for 2 h. The membrane was then hybridized overnight in ULTRAhyb solution (Ambion, Inc.) at 42 C using a [{alpha}-32P]deoxy-CTP-labeled cDNA probe. The membrane was washed in 0.2 x SSC/0.1% SDS at 65 C. The probe was removed from the membrane by incubation for 15 min in 0.1% SDS at 95 C. To confirm loading of cDNA samples and estimate the relative quantity of loaded cDNA between samples, the membrane was then reprobed with rainbow trout ß-actin.

Rainbow trout P450scc (17) and 3ß-hydroxysteroid dehydrogenase (3ßHSD) (18) were obtained by cloning PCR-amplified fragments as previously described (19). A 17-hydroxylase/lyase (P450c17) probe (20) was obtained by RT-PCR using the oligonucleotides designed against the rainbow trout P450c17 sequence [17-hydroxylase sense, 5'-GGAAACCACGTCAACAGTCC-3' (bases 980–999); 17-hydroxylase antisense, 5'-TTACAAGGGCTGTCTCTGCG-3' (bases 3132–2151)]. This fragment was then subcloned, and its identity was confirmed by sequencing on both strands using an ABI prism 310 automatic sequencer (Perkin-Elmer Corp., Norwalk, CT). Rainbow trout P450aro (21) was provided by Prof. Y. Nagahama (Okasaki, Japan) and used as a full-length probe. Cloning and characterization of rainbow trout P45011ß (Guiguen, Y., et al., unpublished results; Accession No. AF217273) will be published elsewhere, and rainbow trout ß-actin is an unpublished sequence displaying more than 90% nucleotide identity with the ß-actin sequence from another salmonid, Salmo salar (Accession No. AF012125).

Statistics
All statistical differences were determined using ANOVA combined with Newman-Keuls test and were calculated using Statistica software (Statsoft, Tulsa, OK).


    Results
 Top
 Abstract
 Introduction
 Materials and Methods
 Results
 Discussion
 References
 
mRNA levels of steroidogenic enzyme genes after a feminizing E treatment in undifferentiated animals
The virtual Northern analysis of mRNA steady-state levels of P450scc, 3ßHSD, and P450c17 in gonads sampled at 65 dpf (male vs. male treated with E2 after 10 days of treatment) is shown in Fig. 1Go. Levels of P450scc mRNA were not affected by E2 treatment, but 3ßHSD and P450c17 mRNAs were undetectable after E2 treatment, as shown by their nondetection by virtual Northern analysis in E2-treated male gonads compared with the control male gonads (Fig. 1Go). The P45011ß mRNA level was also investigated by virtual Northern analysis (Fig. 2AGo) and was detected in the control male population, but was totally absent in the E2-treated population. This noticeable decrease after 10 days of E2 treatment was confirmed (decrease by a factor of 40) by semiquantitative RT-PCR analysis (Fig. 2BGo), with P45011ß mRNA levels reduced to those observed during female gonadal differentiation (13). P450aro mRNA was not detectable in male gonads at that stage using virtual Northern analysis; thus, only the semiquantification by RT-PCR analysis is shown in Fig. 3Go. We detected, as previously shown (12), a high mRNA level of P450aro in female differentiating gonads compared with male gonads and no difference between males and males treated with E2.



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Figure 1. Schematic representation of possible gonadal steroidogenic pathways along with analysis by virtual Northern blot of P450scc, 3ßHSD, and P450c17 mRNA levels in male and E2-treated male gonads sampled at 65 dpf. Reprobing of the membrane with rainbow trout ß-actin is shown below each figure. The size marker ({lambda}HindIII) is shown on the right of each figure. M, Male (pool of 785 differentiating gonads); M. E2, male treated with E2 (20 mg/kg diet; pool of 752 differentiating gonads); P5, pregnenolone; 17P5, 17-hydroxypregnenolone; P4, progesterone; 17P4, 17-hydroxyprogesterone; {Delta}4, androstenedione; DHEA, dihydroepiandrosterone.

 


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Figure 2. Virtual Northern blot (A) and semiquantitative RT-PCR (B) analyses of the P45011ß mRNA levels in male (male, pool of 785 differentiating gonads) and E2-treated male gonads (male; E2, pool of 752 differentiating gonads) sampled at 65 dpf. For the virtual Northern reprobing of the membrane with rainbow trout actin-ß is shown below, and the size marker ({lambda}HindIII) is shown on the right. For semiquantitative RT-PCR, results are shown as a ratio of P45011ß/ß-actin with an arbitrary scale. F, Female; M, male; M. E2, male treated with E2 (20 mg/kg diet; during 10 days between 55–65 dpf). Each bar is the mean of two separate values (•) using two separate pools of n differentiating gonads for each determination [n = 785 and 755 (F), 752 and 781 (M), and 778 and 500 (M. E2)].

 


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Figure 3. Semiquantification by RT-PCR of P450aro mRNA levels in gonads of males (M), females (F), and males treated with 17ß-estradiol (M. E2) sampled at 65 dpf. Data are the ratio of P450aro/ß-actin with an arbitrary scale. Each bar is the mean of two or three separate values (•) using two or three separate pools of differentiating gonads for each determination [n = 785, 755, and 499 (F), 752 and 781 (M), and 778 and 500 (M. E2)].

 
Kinetics of steroidogenic enzyme mRNA levels after E2 treatment in postdifferentiated animals
Representative Northern blots showing P45011ß mRNA levels in testis and interrenals after treatment with E2 are shown in Fig. 4Go. For each steroidogenic enzyme gene we further quantified the ratio of each mRNA over 28S rRNA, and this ratio for all genes studied is shown in Fig. 5Go. The P45011ß mRNA level in the testis after E2 treatment (Fig. 4Go) decreased rapidly, with the first detectable decrease occurring after 8 h (T8) of E2 treatment. This decrease in testicular P45011ß mRNA level in the E2-treated animals was more pronounced after 1 and 2 days (T24 and T48) of treatment (>50% decrease) and was statistically significant after 4 days (T96). It reached less than 5% of the initial expression 8 days after the beginning of the treatment (95% of inhibition at T192; significant difference vs. T0, P < 0.025). In contrast, the interrenal P45011ß mRNA level did not show any consistent or significant variation after E2 treatment (Fig. 4Go). Interrenal 3ßHSD and P450c17 mRNAs also did not show any significant variation after E2 treatment, but interrenal P450scc mRNA did decrease slightly (30% inhibition) and significantly (P < 0.05) after 8 days of treatment (Fig. 5Go). In the testis, however, the 3ßHSD mRNA level was strongly influenced by E2 treatment, with a decrease similar to that in P45011ß mRNA (>50% decrease 8 h posttreatment) and a final level reduced to less than 1% (>99% decrease; P < 0.05) of the level detected before the beginning of the treatment (Fig. 5Go). Testicular mRNA levels of P450scc and P450c17 were also affected by E2 treatment, but to a much lesser extent, i.e. 40–50% decrease in P450scc (significantly different from T0, P < 0.05) and 75% decrease in P450c17 (significantly different from T0, P < 0.05), after 8 days of E2 treatment. For P450c17 a transient, but significant (P < 0.001), increase was also detected after 24 h of E2 treatment.



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Figure 4. Northern blot analysis of P45011ß mRNA and 28S rRNA in the testis (left panels) and interrenal (right panels) of postdifferentiated male fish at different time points after the beginning of E2 treatment (20 mg/kg diet). Transcript sizes are indicated on the left. The ratio of P45011ß/28S rRNA is shown (percentage of the highest ratio) in the figures below. Data are shown with an arbitrary scale. Each bar is the mean of 2 separate values (•) using tissues pooled from 18 fish for each determination. **, Significant differences from T0, P < 0.025.

 


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Figure 5. Representation of the ratio of P450scc, 3ßHSD, and P450c17/28S rRNA in the testis (left) and interrenal (right) of postdifferentiated male fish at different time points after the beginning of E2 treatment (20 mg/kg diet). These data (percentage of the highest ratio) were calculated after quantification of specific signals on Northern blots using an instant imager (Packard). Data are shown with an arbitrary scale. Each bar is the mean of two separate values (•) using tissues pooled from 18 fish for each determination. Significant differences from T0: *, P < 0.05; **, P < 0.025; ***, P < 0.01.

 

    Discussion
 Top
 Abstract
 Introduction
 Materials and Methods
 Results
 Discussion
 References
 
Feminizing estrogen treatments have been widely used for sex control in fish aquaculture (22, 23). In the rainbow trout effective feminization with a 20 mg/kg diet dosage of E2 has been reported (24). As lower dosages described previously failed to produce 100% females (22), we carried out all of these experiments with a similar 20 mg/kg diet E2 treatment. The resulting sex ratio was not checked, but in our rearing conditions similar routine treatments have produced a high proportion of females.

We demonstrated in this study that the short-term effect of this E2 treatment on steroidogenic enzyme genes during gonadal differentiation was a marked decrease in mRNA levels of all of the steroidogenic enzyme genes studied, except P450scc. This effect probably resulted in highly impaired gonadal steroidogenesis in these animals. Such a perturbation of gonadal steroidogenesis has been previously described in the differentiating gonad of rainbow trout after treatment of monosex populations with E2 (8). These researchers found that a 5 mg/kg diet E2 treatment was totally ineffective in feminizing an all male population, as at 2 yr of age, all of the E2-treated males had well developed testes. Despite the absence of effect on the resultant sex ratio, gonadal androgen production was significantly decreased in E2-treated males compared with that in normal males (8). The gonadal mRNA pattern of steroidogenic enzyme genes detected in our experiments during E2-induced female differentiation is very different from the natural ovarian differentiation in which 3ßHSD, P450c17, and P450aro are well expressed (25). The only similarity between E2-induced and normal ovarian differentiation is the noticeable decrease in gonadal P45011ß mRNA that is normally expressed only during testicular differentiation (13). The decrease in P45011ß mRNA together with the decrease in 3ßHSD and P450c17 probably result in complete inhibition of gonadal 11-oxygenated androgen production. These 11-oxygenated androgens have been shown to be naturally synthesized by the trout testis around the time of sex differentiation (1) and are also recognized as potent masculinizing steroids in several fish species (26, 27, 28, 29). The inhibition of their synthesis through the decrease in P45011ß mRNA may, therefore, be one of the crucial steps required in the active feminization of these genetic males by E2. As a result of this decrease in P45011ß mRNA, E2-induced feminization occurs at an elevated ratio of estrogens/11-oxygenated androgens.

E2 production has been previously detected in normal differentiating female gonads, but no gonadal E2 secretion was found in E2-treated males (8). This is completely consistent with our own results, as the P450aro mRNA level was not elevated by E2 treatment and thus did not reach the expression level found in normal differentiating ovaries (12). Conversely, in female Japanese flounders, Paralichthys olivaceus, inhibition of aromatase enzyme activity, and consequently E2 levels, has been shown to depress P450aro gene expression (30). The same results were found in the female chicken, where coadministration of the aromatase inhibitor with E2 restored P450aro mRNA to the levels found in normal differentiating ovaries (31). This suggests that aromatase gene expression may be under the positive control of estrogens in the female differentiating gonad. However, this does not appear to be the case in the differentiating male gonad, as E2 treatment did not increase the P450aro mRNA level (present data) or E2 synthesis (8).

The same experiment carried out on postdifferentiating males gave us the opportunity to analyze the kinetics of the same steroidogenic enzyme mRNAs after E2 treatment in two different steroidogenic organs, i.e. the testis and the interrenal. In the postdifferentiating testis, we found a similar pattern of mRNA levels as that observed during testis differentiation, with, after 10 days of E2 treatment, a large decrease in 3ßHSD, P450c17, and P45011ß mRNAs and a less marked decrease in P450scc mRNA. This decrease was detectable as early as 8 h postapplication of the E2 treatment for P45011ß and 3ßHSD. In the Atlantic croaker, Micropogonias undulatus, estrogens have been shown to inhibit gonadotropin-stimulated 11-ketotestosterone testicular production (32). This estrogen effect was very rapid (<5 min) and was further characterized as a nongenomic mechanism, probably mediated by a membrane receptor. The E2 effects found in our study reflect mRNA changes that are probably mediated at the transcriptional level through a classical genomic mechanism involving a nuclear steroid hormone receptor.

In the interrenal, only a slight decrease in the P450scc mRNA level was detected after E2 treatment. The difference in the pattern of expression of steroidogenic enzyme genes between testis and interrenal may be related to their upstream transcriptional control by the central nervous system with, respectively, ACTH and gonadotropin hormones (Gths). In fish, Gths are well known to regulate gonadal steroid hormone biosynthesis (33). However, estrogens have also been shown to inhibit Gths-stimulated testicular steroidogenesis in mammals (34, 35, 36), amphibians (37, 38), and fish (39). Whatever the effect of E2 on steroidogenic enzyme mRNAs seen in postdifferentiated fish, its effect may be slightly different, in terms of its upstream transcriptional control, from the effect in differentiating fish. In rainbow trout, Gth stimulation of steroid secretion occurs late, i.e. 117 dpf (8), compared with the timing of histological sex differentiation (~80 dpf in our study), but several studies have also demonstrated that the hypothalamo-pituitary axis is potentially active around the time of sex differentiation (1). In that regard it should be noted that a much earlier Gth stimulation of androstenedione synthesis in the interrenal has been demonstrated in the rainbow trout (8). This interrenal steroid production may be relevant with respect to gonadal differentiation, as a hypothesis has been proposed involving the participation of that tissue in the production of steroids potentially acting on gonadal differentiation (40). The fact that steroidogenic enzyme mRNA levels in the interrenal are only slightly decreased by E2 after sex differentiation now deserves more interest, and future investigations should concentrate on the differentiation period. However, no effect of E2 on interrenal steroid production could be detected in rainbow trout during gonadal differentiation, and thus, it has been concluded that this effect is gonad specific (8).

Gth stimulation of steroid secretion only occurs after gonadal differentiation in the rainbow trout (8); thus, the E2 effects that we reported here in the predifferentiating testis are probably induced independently from an inhibition of Gth secretion. However, in postdifferentiating gonads the question still remains as to whether E2 effects are mediated either directly on the testis and/or through a feedback inhibition of Gth secretion. Apart from these classical feedback effects of estrogens there is some supporting evidence that estrogens can have a direct action on the testis (41). For instance, in the frog, Rana esculenta, E2 can decrease in vitro testis androgen production (38) and inhibit steroidogenesis (37). In the rat, neonatal exposure to estrogen affects the expression levels of the estrogen receptors, ER{alpha} and ERß, and the androgen receptor independently of an estrogen-induced suppression of Gths secretion (42). Some direct inhibitory effect of estrogens on testicular androgen production have also been found on human testis in vitro (43), and in the rat, estrogens also decrease testicular androgen production without a concomitant decrease in serum LH (44). This assumption that estrogens can act directly on the testis is also confirmed by the pattern of expression of ERs, which are expressed in the testis (42). This is further reinforced by the fact that transgenic mice in which the genes for aromatase (45), ER{alpha} (46), or both ER{alpha} and ERß (10) have been inactivated develop disorders of spermatogenesis.

Many studies have reported an impaired steroidogenesis profile after estrogen treatment. However, only a few studies have investigated this effect at the level of the steroidogenic enzyme gene expression. In the rat, diethylstilbestrol (a synthetic estrogen) and 4-octylphenol (a xenoestrogen) both inhibit fetal testicular P450c17 gene expression (47). This has been shown to correlate with the inhibition of the steroidogenic factor-1 (SF1) gene by both diethylstilbestrol and 4-octylphenol (48). SF1 is a transcription factor that has been shown to be essential for both gonadal differentiation (49) and transcriptional control of most steroidogenic cytochrome P450 genes (49, 50) and also 3ßHSD (51). As such it has been postulated that the estrogen effects on the inhibition of fetal testicular P450c17 gene expression may be mediated via the alteration of SF1 gene expression (48). The same could also hold in our case, as the simultaneous decreases in 3ßHSD, P450c17, and P45011ß mRNAs produced by E2 treatment suggest a common transcriptional upstream control, and SF1 would be a good candidate for such a role. Future studies will focus on this transcriptional upstream control, but our present observations clearly suggest that estrogen action on steroidogenesis in the rainbow trout testis is mediated through changes in steroidogenic enzyme mRNA steady state levels and that these effects may explain the active feminization caused by estrogens in fish.


    Acknowledgments
 
We acknowledge the experimental facility staff of the Institut National de la Recherche Agronomique-SCRIBE laboratory for his help with fish rearing. We acknowledge Dr. Alexis Fostier for critical reading of the manuscript.


    Footnotes
 
1 This work has been funded by a European Community project (PL 97–3796). Back

2 Supported by a European Community project (PL 97–3796). Back

Received October 10, 2000.


    References
 Top
 Abstract
 Introduction
 Materials and Methods
 Results
 Discussion
 References
 

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