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Journal of Andrology, Vol. 26, No. 2, March/April 2005
Copyright © American Society of Andrology

Effects of Maternal Exposure to 3,3',4,4',5-Pentachlorobiphenyl (PCB126) or 3,3',4,4',5,5'-Hexachlorobiphenyl (PCB169) on Testicular Steroidogenesis and Spermatogenesis in Male Offspring Rats

MASAKO YAMAMOTO*, AKIKO NARITA*, MARI KAGOHATA*, MITSUYUKI SHIRAI{dagger}, FUMIAKI AKAHORI{dagger} AND KAZUYOSHI ARISHIMA*

From the Departments of * Anatomy II and {dagger} Pharmacology, Azabu University School of Veterinary Medicine, Sagamihara, Japan.

Correspondence to: Dr Masako Yamamoto, Department of Anatomy II, Azabu University School of Veterinary Medicine, 1-17-71 Fuchinobe, Sagamihara, Kanagawa 229-8501, Japan (e-mail: masako{at}azabu-u.ac.jp).
Received for publication July 2, 2004; accepted for publication November 5, 2004.

   Abstract
 Top
 Abstract
 Materials and Methods
 Results
 Discussion
 References
 
On days 7-21 of gestation, Sprague-Dawley rats were orally administered 3 or 30 µg/kg/d of 3,3',4,4',5-pentachlorobiphenyl (PCB126) or 3,3',4,4',5,5'-hexachlorobiphenyl (PCB169) daily. Their male offspring were autopsied at 3, 6, and 15 weeks after birth to investigate the effects of the 2 polychlorinated biphenyls (PCBs) on spermatogenesis and steroidogenesis in their testes. PCB treatment caused a decrease in the area ratio of 3ß-hydroxysteroid dehydrogenase (HSD)-expressing cells (Leydig cells)/testis at 3 weeks after birth. When PCB126 was administered to pregnant rats, the plasma testosterone levels in their offspring were decreased at 3 weeks. The expression levels of P450scc, 3ß-HSD, and P45017{alpha} mitochondrial RNAs (mRNAs) were unchanged, although the StAR (steroidogenic acute regulatory protein) mRNA expression level was increased at 6 weeks. On the other hand, when PCB169 was administered, plasma testosterone levels were decreased at 3 and 6 weeks and were increased at 15 weeks. Plasma luteinizing hormone (LH) levels were decreased at 6 weeks, and plasma follicle-stimulating hormone (FSH) levels were increased at 15 weeks. The expression levels of 3ß-HSD and P45017{alpha} were increased, and the mRNA level of 5{alpha}-reductase 1 was decreased at 15 weeks. PCB169 treatment suppressed the conversion of round spermatids between stages VII and VIII. These results indicate that in utero and lactational exposure to PCB126 or PCB169 decreases plasma testosterone levels in 3-week-old rats, with no change in the expression levels of the mRNAs of enzymes, and that PCB169 inhibits testicular steroid synthesis more strongly than PCB126. PCB169 greatly altered the concentration of testosterone, indicating a stronger inhibitory effect on spermatogenesis. Low testosterone and LH levels in prenatally PCB169-exposed rats until 6 weeks after birth presumably retard the functional differentiation of testicular Leydig cells; however, the increased testosterone levels at 15 weeks suggest that Leydig cells in PCB-exposed rats are virtually mature by the 15th week.

     Key words: PCB, androgen, pituitary



It is well known that environmental pollutants disrupting endocrine function and affecting reproductive function in wild animals, experimental animals, and humans still occur widely (Colborn and Clement, 1992; Colborn et al, 1993; Crisp et al, 1998). Coplanar polychlorinated biphenyls (PCBs), polychlorinated dibenzo-p-dioxins (PCDDs), and polychlorinated dibenzofurans (PCDFs) are categorized as dioxins and related compounds because these compounds show various adverse toxicities similar to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) through a common pathway via an aryl hydrocarbon receptor. In particular, in utero and lactational exposure to dioxins causes adverse effects on the male reproductive system, such as reduced sperm count (Mably et al, 1992c; Wilker et al, 1996; Gray et al, 1997) and reduced reproductive organ size (Mably et al, 1992b; Roman et al, 1998).

The toxicity of these homologs is evaluated by the toxicity equivalence factor (TEF), which is the relative toxicity when that of the most toxic TCDD is defined as 1; for example, 3,3',4,4',5-pentachlorobiphenyl (PCB126) has a TEF of .1, and 3,3',4,4',5,5'-hexachlorobiphenyl (PCB169) has one of .01 (Van den Berg et al, 1998). Many studies have investigated the inhibitory effects of PCBs on reproductive function, developmental abnormality, and impaired reproductive ability (Sager, 1983; Brezner et al, 1984; Sager et al, 1987, 1991; Safe, 1990; Backlin and Bergman, 1992; Hansen, 1998). Also, several studies have reported the effects of PCBs on the in vivo and in vitro synthesis of steroids in the testis and adrenal gland or on spermatogenesis (Goldman and Yawetz, 1992; Kovacevic et al, 1995; Pflieger-Bruss et al, 1999). Data available for individual PCB congeners are from reproductive studies in laboratory animals with commercial PCB mixtures. Furthermore, few experiments with single PCBs administered exclusively during the prenatal period have been performed, and the precise mechanisms of PCB-induced abnormalities in the testicular steroid-synthesizing system and spermatogenesis have not been elucidated.

In this study, we aimed to elucidate the mechanism of the influence of PCBs on spermatogenesis and steroidogenesis in the male immature and mature offspring of mothers that had received PCBs of different structures, PCB126 and PCB169, during pregnancy.


   Materials and Methods
 Top
 Abstract
 Materials and Methods
 Results
 Discussion
 References
 
Animals and Treatments

Sprague-Dawley rats (Japan SLC, Hamamatsu, Japan) were given a commercial diet (CE-2, CLEA, Tokyo, Japan) and water, both ad libitum. Females were placed with males overnight and were examined the next morning for the presence of sperm in the vaginal smear. The day on which sperm was detected was counted as day 0 of gestation. Pregnant rats were housed individually and maintained in a 12 hour to 12 hour light-dark cycle at a room temperature of 21°C ± 2°C and 55% ± 5% humidity. Pregnant rats were divided into 3 groups, PCB126-treated, PCB169-treated, and control. The rats in each group received daily oral administration of PCB126 (3 µg/kg/d; 99% purity) or PCB169 (30 µg/kg/d; 99% purity) dissolved in corn oil (Sigma Chemical Co, St Louis, Mo) or corn oil alone (control) on days 7 through 21 of gestation. The PCBs were obtained from AccuStandard Inc (New Haven, Conn). The dose for PCB126 was determined from preliminary dose range studies. The dose used in this study produced no obvious signs of developmental toxicity (eg, reduced maternal weight gain, smaller litter size, fewer live births). The dose for PCB169 was based on TEF, with the toxicity equivalence factor of PCB169 equal to PCB126.

After birth, the pups were controlled to 4 males and 4 females in each litter. The pups were kept with their natural mothers until weaning on day 21. Male rats at postnatal weeks 3, 6, and 15 were autopsied under diethyl ether anesthesia to collect blood samples individually. The testes of each pup were removed, and the left testis was subjected to RNA extraction and the right testis to histologic analysis.

To determine the transplacental transfer of PCBs, at 20 days of gestation, 3 dams of each group were autopsied. Eight fetal livers in each litter were pooled and stored at -80°C.

The study described in this paper was carried out in accordance with the Azabu University Animal Experiment Guidelines.

PCB Analysis

Metocean Environment Inc (Tokyo, Japan) analyzed the pooled fetal livers for content of PCB126 or PCB169 by high-resolution gas chromatograph-mass spectrometry.

Plasma Hormone Assay

The blood samples were centrifuged at 4°C, and the plasma was stored at -80°C until assay. The concentration of plasma testosterone was measured by radioimmunoassay with the [125I] total testosterone assay kit (Diagnostic Products Corp, Los Angeles, Calif). The sensitivity was determined to be 4 ng/dL. The concentrations of luteinizing hormone (LH) and follicle-stimulating hormone (FSH) were measured by the rat luteinizing hormone enzyme immunoassay system and the rat FSH [125I] Biotrak assay system (Amersham Biosciences, Buckinghamshire, United Kingdom). The sensitivities were determined to be 0.1 ng/mL and 0.9 ng/mL, respectively.

Morphological Analysis of Leydig Cells

At autopsy, testes at 3 weeks were immediately frozen in embedding OCT compound (Sakura Finetechnical Co Ltd, Tokyo, Japan) with liquid nitrogen. Frozen sections (8 µm) were air dried for a few minutes, fixed in acetone at -20°C for 10 minutes, and completely air dried. Five slides for each sample were stained by tetrazorium reactions (Levy et al, 1959) to detect 3ß-hydroxysteroid dehydrogenase (HSD). Stained sections were digitized by a Nikon Coolpix 990 digital camera (Nikon Co, Tokyo, Japan) attached to a light microscope, and the images were input into Adobe Photoshop 5.5 image editing software (Adobe, San Jose, Calif). The area of the 3ß-HSD-positive cells and the whole area of the testis was measured with NIH Image (National Institutes of Health, Bethesda, Md). The area ratio was expressed as a percentage and averaged across the sections observed in each testis.

Spermatogenesis

Testes at 6 and 15 weeks were fixed with Boiuns fluid. Fixed testes were dehydrated, embedded in paraffin, and sectioned at 5 µm. Sections were stained with periodic acid-Schiff and counterstained with hematoxylin. Seminiferous tubules were staged according to the criteria published by Hess (1990). Five hundred tubules per testis were classified into the following groups: stage I, II/III, IV, V, VI, VII, VIII, IX, X, XI, XII, XIII, and XIV.

Semiquantitative Reverse Transcription-PCR

Total RNA from the testis of offspring from intact and PCB-treated mothers was extracted with Isogen (Nippon Gene Co, Toyama, Japan) according to the manufacturer's protocol.

PCR amplification from reverse-transcribed complementary DNA (cDNA) was carried out with the following primers: StAR (steroidogenic acute regulatory protein), P450scc, 3ß-HSD, P45017{alpha} (17{alpha}-hydroxylase + C17-21 lyase), 5{alpha}-reductase 1, and ß-actin (Table 1). The reactions were performed according to the manufacturer's instruction for the SuperScript 1-step reverse transcription (RT)-PCR (Invitrogen). Total volume of 50 µL of the reaction mixture contained RNA, 10 nM sense and antisense primers, tag Mix and 1x reaction mix, or 2.0 mM MgSO4 for 3ß-HSD. cDNA synthesis and predenaturation were performed with 1 cycle of 50°C for 30 minutes and 94°C for 2 minutes. Amplification was carried out in a thermal cycler (Bio-Rad), as shown in Table 2.


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Table 1. PCR primers for the detection of various gene expressions used in this study
 

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Table 2. Cycling parameters for the polymerase chain reaction
 

Following PCR, the amplified DNA was separated by electrophoresis in a 2.5% agarose gel with an appropriate molecular mass marker (Bio-Rad, Hercules, Calif). Gels were stained with ethidium bromide and photographed with a Polaroid camera, and the intensity of the band was digitized on an Epson scanner. The signal intensities were measured in 3 individual animals and 2 independent RT-PCRs for each sample. The digitized signals were imported into NIH Image, and the average optical density of each band was measured and normalized to ß-actin to obtain the ratio of target product to ß-actin for each sample.

Statistical Analysis

Duncan's new multiple range test was used for statistical analysis of results, with significance at P less than .05.


   Results
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 Abstract
 Materials and Methods
 Results
 Discussion
 References
 
PCB Content in Fetal Livers

PCB126 and PCB169 were detected in the fetal livers in the PCB126- and PCB169-administered groups, respectively (Table 3). The amounts of PCB169 in the fetal livers from the PCB169-administered group were 10-fold those of PCB126 in the fetal livers from the PCB126 group. In the PCB169-treated group, PCB126 was found in the fetal livers.


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Table 3. Polychlorinated biphenyl content in fetal livers following maternal PCB126 or PCB169 administration during days 7-20 of gestation*{dagger}
 

Hormone Levels

The plasma testosterone levels in the offspring of both PCB-administered groups were significantly lower than those in the offspring from the control group at 3 weeks after birth (Table 4). At 6 weeks after birth, the plasma testosterone levels in the offspring from the PCB169-administered group were significantly lower than in the offspring from the control group, but those in the offspring from the PCB126-administered group were unchanged. At 15 weeks after birth, plasma testosterone levels in the offspring from the PCB169-administered group were significantly increased compared with those in the control offspring.


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Table 4. Effects of prenatal exposure to polychlorinated biphenyls on plasma hormone concentrations
 

At 3 weeks after birth, the plasma LH levels in the offspring from the PCB-administered groups did not significantly differ from those in the control offspring. At 6 weeks after birth, the plasma LH levels in the offspring from the PCB169-administered group were significantly lower than in the control offspring.

At 6 weeks after birth, the plasma FSH levels in the offspring from the PCB-administered groups did not significantly differ from those in the control offspring. At 15 weeks after birth, the plasma FSH levels in the offspring from the PCB169-administered group were significantly higher than those in the control offspring.

Leydig Cells and Spermatogenesis

In the testis interstitium of the 3-week-old offspring from the control group, there were few Leydig cells, with small cytoplasm and a large number of mesenchymal cells. At 3 weeks after birth, the ratios of the area of 3ß-HSD-positive cells to the whole area of the testis in the offspring from the PCB-administered groups were lower than those in the control offspring (Table 5).


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Table 5. Changes in area ratio of 3ß-hydroxysteroid dehydrogenase (HSD)-positive cells/testis
 

At 6 weeks after birth, matured spermatids did not yet present in the lumen of the seminiferous tubules from all groups (Figure 1). However, the stages of the cycle in testicular seminiferous epithelium could be divided into 13 stages, and the obtained frequency of the stages in the control group was almost equal to the result of the previous study (Hess et al, 1990). The number of stage VI seminiferous tubules was significantly higher in the offspring from the PCB-administered groups than in the offspring from the control group (Table 6). The administration of PCB126 reduced the number of stage XIII seminiferous tubules, whereas the administration of PCB169 reduced the numbers of stage II/III, VII, and IX seminiferous tubules. At 15 weeks after birth, the number of stage XI seminiferous tubules was significantly higher in the offspring from the PCB-administered groups than in the offspring from the control group. The administration of PCB126 reduced the number of stage XII seminiferous tubules, whereas the administration of PCB169 reduced the numbers of stage I, V, and VI seminiferous tubules and increased the numbers of stage II/III and VII seminiferous tubules. Pathologic changes, such as pyknotic nuclei and the occurrence of cell debris, were not detected in the testis from PCB-treated groups at 6 and 15 weeks (Figure 1).



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Figure 1. Photomicrographs showing spermatogenesis in testicular seminiferous epithelium of rats exposed to polychlorinated biphenyls (PCBs) at 6 (a, b) and 15 (c-h) weeks after birth. Roman numerals indicate the stage in the cycle of spermatogenesis. At 6 weeks, the administration of 3,3',4,4',5,5'-hexachlorobiphenyl (PCB169) reduced the number of stage VI (a) and increased the number of stage VII (b) tubules. Matured spermatids had not yet appeared in the lumen of seminiferous tubules (a, b). At 15 weeks, the administration of PCB169 reduced the number of stage I (c), V (e), and VI (f) seminiferous tubules and increased the numbers of stage II/III (d) and VII tubules. In the stage VIII tubules (g), the release of spermatids was observed. Meiosis was detected in stage XIV tubules (h). M indicates meiotic figures; S, spermatogonia; Pl, preleptene spermatocyte; P, pachytene spermatocyte; arrows, elongating spermatids; arrowheads, round spermatids; and Rb, residual bodies. (a, c-h) PCB169 groups; (b) control group. Magnification, 657x.

 

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Table 6. Effects of polychlorinated biphenyls (PCBs) on spermatogenesis{dagger}
 

Expression Levels of StAR, Steroidogenic Enzymes (P450scc, 3ß-HSD, P45017{alpha}), and 5{alpha}-Reductase 1 Mitochondrial RNAs

The expression levels of StAR, P450scc, 3ß-HSD, P45017{alpha}, and 5{alpha}-reductase 1 mitochondrial RNAs (mRNAs) were semiquantitatively analyzed by RT-PCR (Figure 2). The expression levels of StAR did not change in the 3- and 15-week-old offspring from the PCB-administered groups but were significantly higher in the 6-week-old offspring from the PCB126-administered group than in the PCB169-administered group. The expression levels of P450scc mRNA in the testis did not change in all experimental periods. The expression levels of 3ß-HSD mRNA in the testis did not change in the 3- and 6-week-old offspring from the PCB-administered groups, but were significantly higher in the 15-week-old offspring from the PCB-administered groups than in the control offspring. The expression levels of P45017{alpha} mRNA were also unaffected by PCB administration in the 3- and 6-week-old offspring but were significantly increased in the 15-week-old offspring from the PCB169-administered group. The levels of 5{alpha}-reductase 1 mRNA expression were significantly higher in the 6-week-old offspring from the PCB126-administered group, significantly lower in the 15-week-old offspring from the PCB126-administered group, and still lower in the 15-week-old offspring from the PCB169-administered group compared with those in the control offspring.



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Figure 2. Effects of maternal exposure to 3,3',4,4',5-pentachlorobiphenyl (PCB126) or 3,3',4,4',5,5'-hexachlorobiphenyl (PCB169) on mRNA levels of StAR (steroidogenic acute regulatory protein) and steroidogenic enzymes in testis measured by semiquantitative reverse transcription-PCR. Values are given as means ± SEM of 3 determinations. Significant difference from * control group (P < .05), a indicates PCB169-administered group (P < .05).

 


   Discussion
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 Abstract
 Materials and Methods
 Results
 Discussion
 References
 
The principal experimental protocol for studying the perinatal TCDD effect on the male reproductive system was dosing pregnant rats on gestational day 15 (GD 15) on the basis of reports by Peterson and coworkers (Mably et al, 1992a,b,c). However, Faqi (1998b) reported that a single PCB126 oral dose of 10 µg/kg on GD 15 did not induce any decrease in testicular weight, sperm count, and serum testosterone on postnatal day 65. Furthermore, there were few reports that the effects of in utero, lactational, or both kinds of exposure to PCB congeners have an effect on the male reproductive system (Lundvist, 1990; Faqi et al, 1998b; Kuriyama and Chahoud, 2004; Meerts et al, in press). Therefore, we administered PCBs to pregnant rats from GD 7 to GD 21 during organogenesis and the period when the fetal endocrine organs begin to function.

This experiment produced a new finding, showing that the administration of PCB169 to pregnant rats tended to decrease plasma testosterone levels in their offspring up to 6 weeks after birth but significantly increased the levels in the 15-week-old offspring. We demonstrated that maternally administered PCB126 or PCB169 passed through the placenta in absolute form. Although, PCB126 was detected in fetal livers from the PCB169-administered group, the purity of administered PCB126 was approximately 99%, so PCB126 might have contained PCB169. Because the amounts of PCB126 found in PCB169 were approximately 5% in terms of TEF, these amounts might have resulted in an unconsidered effect on the PCB169-induced changes in this study. The highly chlorinated (14C) PCBs (Aroclor 1260) that accumulated in the maternal rats transferred to the fetuses and sucklings, and the PCB concentration in the milk increased gradually for 16 days after delivery and then decreased (Takagi et al, 1986). In this study, the administered PCBs were transferred to the fetuses during pregnancy and were transported to the offspring postnatally via milk; therefore, mother-derived PCBs decreased the plasma testosterone levels in the 3- and 6-week-old offspring. It appears that PCB169 influences testosterone levels more strongly than PCB126. The highly chlorinated congeners had a longer retention time in rat tissues (Shain et al, 1986). Because the dose of PCB169 was determined such that it was equal to the toxicity equivalence factor of PCB126, the higher inhibitory effect of PCB169 on testicular function might be a result of its structure.

Testosterone is the predominant androgen involved in the regulation of normal spermatogenesis in the rat because of its high intratesticular concentration (Wright and Frankel, 1979). It is known to preferentially induce the conversion of round spermatids between stages VII and VIII (O'Donnel et al, 1994, 1996). The content of androgen receptors (AR) is maximal in Sertoli cells at stages VII and VIII (Shan et al, 1997). We speculate that the increase in the number of stage VI seminiferous tubules and the decrease in stage VII seminiferous tubules in the 6-week-old offspring from the PCB169-administered group were because of the decrease in the concentration of plasma testosterone, resulting in the inhibition of the conversion of round spermatids between stages VII and VIII. Conversely, the concentration of plasma testosterone in the 15-week-old offspring from the PCB169-administered group was increased, but the ratio of the number of stage VIII seminiferous tubules to that of stage VII seminiferous tubules, which indicates an accelerated conversion of round spermatids, remained unchanged. However, the decreases in stage V and VI seminiferous tubules could be proof that the development of stage VII round spermatids was promoted. Meachem et al (1998) concluded that FSH acts on stages XIV through I (type A3 and A4 spermatogonia) of spermatogenesis on the basis of the number of FSH receptors (Kangasniemi et al, 1990) and the level of FSH receptor mRNA expression (Heckert and Griswold, 1991). Therefore, we speculate that the decrease in the number of stage I seminiferous tubules and the increases in those of stage II and III in the 15-week-old offspring from the PCB169-administered group were caused by an increase in the concentration of FSH, resulting in the stimulation of stage XIV and I spermatogonia, thereby promoting the progression from stage I to stages II and III.

It is still a matter of controversy whether maternal exposure to TCDD affects spermatogenesis in offspring. Mably et al (1992c) reported that perinatal exposure to a low TCDD dose significantly reduced testis weight and daily sperm production, whereas Gray et al (1997) and Ohsako et al (2001) failed to find this. On the other hand, Faqi et al (1998a) found a slight decrease of daily sperm production with no changes in testicular weight by administering female rats an initial loading dose 2 weeks before mating, followed by a weekly maintenance dose. Furthermore, there were no reports that maternal exposure to the PCB congeners altered the steroidogenesis or spermatogenesis of male offspring, especially an increase in plasma testosterone concentrations in male offspring after puberty, born to TCDD- or PCB congeners-exposed dams, although lactational exposure to Archor 1242 increased daily sperm production and testicular weight (Kim, 2001). We showed for the first time that maternal exposure to PCB169 affects steroidogenesis, resulting to alterations of the spermatogenesis in male offspring.

Desaulniers et al (1999) speculated that PCB126 administration inhibits LH release from the pituitary gland and damages the hypothalamus because they found that the twice-daily administration of high doses (100 or 400 µg/kg/d) of PCB126 to adult male rats reduced plasma LH levels and increased LH levels in the pituitary gland. However, a single dose of TCDD on GD 15 to pregnant rats did not change the plasma LH concentrations in male offspring (Mably et al, 1992c). In this study, although testosterone levels were decreased in the 3-week-old offspring from PCB126-administered dams and in the 3- and 6-week-old offspring from PCB169-administered dams, LH levels were unchanged or decreased. Therefore, we consider that maternally administered PCBs exert inhibitory effects on the interrelationship of the hypothalamus-pituitary-testis system in the offspring.

We investigated whether PCBs exert direct inhibitory effects on the testosterone-synthesizing ability of the testis. In all species, the rate-limiting step in androgen biosynthesis is the conversion of cholesterol to pregnenolone by P450scc. In addition to this important enzyme, another protein, steroidogenic acute regulatory (StAR) protein, appears to transfer cholesterol from cellular stores to the inner mitochondrial membrane, where cholesterol is enzymatically converted to pregnenolone by cytochrome P450scc (Clark et al, 1994; Stocco and Clark, 1996). Few experimental studies involving the administration of endocrine disruptors have focused on StAR. A study has reported that the long-term administration of a plant estrogen (soy-phytoestrogen)-containing diet to adult rats reduces the concentration of testosterone, but not that of StAR (Weber et al, 2001). However, in this study, the level of StAR mRNA expression was increased in the 6-week-old offspring from the PCB126-administered group. The plasma testosterone level in the 3-week-old offspring from the PCB126-administered group was decreased, but that in the 6-week-old offspring did not differ from that in the control offspring, suggesting that the increase in the level of StAR mRNA expression was involved in the restoration of testosterone. When newborn mouse testes were cultured with PCB126, P450scc mRNA expression was significantly down-regulated by PCB126 (Fukuzawa et al, 2003). However, in this study, the administration of each PCB did not change the level of testicular P450scc mRNA expression, suggesting that the testosterone concentration changes observed after the transplacental passage of PCB to embryos and newborns were not because of the changes in the early stages of steroidogenesis.

We measured the expression levels of the mRNAs of hormone-synthesizing enzymes 3ß-HSD and P45017{alpha} and found that the expression levels of these mRNAs were unchanged at 3 and 6 weeks after birth, when testosterone levels should normally have been decreased. Leydig cells bear androgen receptors (Bremner et al, 1994), whose expression is inhibited at puberty (Shan et al, 1995). In immature animals, testosterone is an important autocrine regulator in the differentiation of Leydig cells. Treatment of undifferentiated Leydig cells with androgen and LH in vitro increases their testosterone-synthesizing ability (Hardy et al, 1990). An increase in endogenous LH exerts a positive control on the membrane receptor and steroid synthesis in Leydig cells (Dufau, 1988; Nishihara et al, 1988; Tang et al, 1998). In contrast, in the mature testes, androgen is believed to limit the biosynthesis of androgen by inhibiting the activity of steroid-synthesizing enzymes and their gene expression. In an in vitro study with mature Leydig cells, testosterone treatment inhibited the activity of 3ß-HSD (Ruiz de Galarreta et al, 1983) and P45017{alpha} (Darney et al, 1996). Plasma testosterone levels rose rapidly until 45 days postnatally, thereafter increasing gradually or flattening out (Mack et al, 2000). Daily injection of Aroclor 1242 to mothers during days 0 through 21 after parturition caused a lower volume of Leydig cells and a lower level of LH in pups (Kim et al, 2001). In this study, maternal PCB administration decreased the area ratio of Leydig cells/testis in the testes of 3-week-old offspring. When plasma testosterone levels were decreased in the 3- and 6-week-old offspring from PCB169-administered rats, LH levels were decreased compared with controls. These low levels of testosterone and LH presumably retarded the differentiation of Leydig cells. However, it is also possible that, at 15 weeks after birth, the Leydig cells in the offspring from PCB169-administered rats had undergone differentiation to some extent and had acquired the ability to secrete large amounts of testosterone with increased expression levels of 3ß-HSD and P45017{alpha}.

Testosterone and its 5{alpha}-reduced metabolite, 5{alpha}-dihydrotestosterone (DHT), both interact with the AR to promote androgen-dependent gene transcription. However, DHT is a more potent androgen than testosterone because of its increased affinity for the AR; therefore, DHT is assumed to amplify the androgen response when testosterone levels are low (Grino et al, 1990; Zhou et al, 1995). 5{alpha}-Reductase 1, one of the isoforms of 5{alpha}-reductase, was the predominant isoform in the pubertal and adult rat testis, with both isoforms being lower in the adult testis (Pratis et al, 2000). Pratis et al (2003) concluded that testosterone negatively regulated 5{alpha}-reductase 1 mRNA, resulting in an increase in the metabolism of testosterone to a more potent metabolite, DHT. In this study, in the 6-week-old offspring from the PCB169-administered group, the plasma testosterone level was decreased, but the level of 5{alpha}-reductase 1 mRNA expression remained unchanged, whereas, in the 15-week-old offspring, the plasma testosterone level was increased, and the level of 5{alpha}-reductase 1 mRNA expression was decreased. Thus, we speculate that the high plasma testosterone level in the 15-week-old offspring from the PCB169-administered group was because of the decrease in 5{alpha}-reductase 1 mRNA, resulting in the inhibition of the conversion of testosterone to DHT and the recovery of spermatogenesis.

In utero and lactational exposure of rats to 2 kinds of PCB exerted different inhibitory effects. PCB126 reduced the testosterone concentration at 3 weeks after birth, mainly through the inhibitory effect on the higher central nervous system, but exerted little or no inhibitory effects at 6 weeks after birth. On the other hand, PCB169 reduced the testosterone concentration at 3 and 6 weeks after birth, indicating a stronger inhibitory effect on spermatogenesis, via the inhibition of the pituitary-testicular axis; however, at 15 weeks after birth, the mRNA for testicular steroid-synthesizing enzymes had undergone changes, resulting in increased testosterone levels. The 2 PCBs reduced the percentage of testicular Leydig cells at 3 weeks after birth, indicating the inhibition of Leydig cell differentiation. These results indicate that PCB169 has a stronger inhibitory effect on testicular function than PCB126.


   Acknowledgments
 
The authors thank Dr Masaru Murakami for his useful technical information.


   Footnotes
 
This work was supported by a Grant-in-Aid for High-Tech Research Center Projects from the Ministry of Education, Science, Sports, and Culture of Japan.


   References
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 Abstract
 Materials and Methods
 Results
 Discussion
 References
 
Backlin A, Bergman A. Histopathology of postpartum placental sites in mink (Mustela vison) exposed to polychlorinated biphenyls and fractions thereof. APMIS. 1992; 103: 845 -854.

Bremner WJ, Millar MR, Sharpe RM, Saunders PTK. Immunohistochemical localization of androgen receptors in the rat testis: evidence for stage-dependent expression and regulation by androgen. Endocrinology. 1994; 135: 1227 -1234.[Abstract]

Brezner E, Terkel J, Perry AS. The effect of aroclor 1254(PCB) on the physiology of reproduction in the female rat. Comp Biochem Physiol C. 1984;77: 65 -70.

Clark BJ, Wells J, King SR, Stocco DM. The purification, cloning and expression of a novel LH-induced mitochondrial protein in MA-10 mouse Leydig tumor cells: characterization of the steroidogenic acute regulatory protein (StAR). J Biol Chem. 1994; 269: 28314 -28322.[Abstract/Free Full Text]

Colborn T, Clement C. Chemically Induced Alterations in Sexual and Functional Development: The Wildlife/Human Connection. Princeton, NJ: Princeton Scientific Publishing; 1992.

Colborn T, vom Saal FS, Soto AM. Developmental effects of endocrine-disrupting chemicals in wildlife and humans. Environ Health Perspect. 1993;101: 378 -384.[Medline]

Crisp TM, Clegg ED, Cooper RL, et al. Environmental endocrine disruption: an effects assessment and analysis. Environ Health Perspect. 1998;106(suppl 1): 11 -56.

Darney KJ Jr, Zirlin BR, Ewing LL. Testosterone autoregulation of its biosynthesis in the rat testis: inhibition of 17alpha-hydroxylase activity. J Androl. 1996; 17: 137 -142.[Abstract/Free Full Text]

Desaulniers D, Leingartner K, Wade M, Fintelman E, Yagminas A, Foster WG. Effects of acute exposure to PCBs 126 and 153 on anterior pituitary and thyroid hormones and FSH isoforms in adult Sprague Dawley male rats. Toxicol Sci. 1999; 47: 158 -169.[Abstract/Free Full Text]

Dufau ML. Endocrine regulation and communicating functions of the Leydig cell. Annu Rev Physiol. 1988; 50: 483 -508.[Medline]

Faqi AS, Dalsenter PR, Merker H-J, Chahoud I. Reproductive toxicity and tissue concentrations of low doses of 2,3,7,8-tetrachlorodibenzo-p-dioxin in male offspring rats exposed throughout pregnancy and lactation. Toxicol Appl Pharmacol. 1998a;150: 383 -392.[Medline]

Faqi AS, Dalsenter PR, Merker H-J, Chahoud I. Effects on developmental landmarks and reproductive capability of 3,3',4,4'-tetrachlorobiphenyl and 3,3',4,4',5-pentachlorobiphenyl in offspring of rats exposed during pregnancy. Hum Exp Toxicol. 1998b; 17: 365 -372.[Abstract/Free Full Text]

Fukazawa NH, Ohsako S, Nagano R, Sakaue M, Baba T, Aoki Y, Tohyama C. Effects of 3,3',4,4',5-pentachlorobiphenyl, a coplanar polychlorinated biphenyl congener, on cultured neonatal mouse testis. Toxicol In Vitro. 2003; 17: 259 -269.[Medline]

Goldman D, Yawetz A. The interference of polychlorinated biphenyls (Aroclor 1254) with membrane regulation of the activities of cytochromes P-450C21 and P-450(17) alpha, lyase in guinea-pig adrenal. J Steroid Biochem Mol Biol. 1992; 42: 37 -47.[Medline]

Gray LE, Ostby JS Jr, Kelce WR. A dose-response analysis of the reproductive effects of a single gestational dose of 2,3,7,8-tetrachlorodibenzo-p-dioxin in male Long Evans hooded rat offspring. Toxicol Appl Pharmacol. 1997; 146: 11 -20.[Medline]

Grino PB, Griffin JE, Wilson JD. Testosterone at high concentrations interacts with the human androgen receptor similarly to dihydrotestosterone. Endocrinology. 1990; 126: 1165 -1172.[Abstract]

Hansen LG. Stepping backward to improve assessment of PCB congener toxicities. Environ Health Perspect. 1998; 106: 171 -189.

Hardy MP, Kelce WR, Klinefelter GR, Ewing LL. Differentiation of Leydig cell precursors in vitro: a role for androgen. Endocrinology. 1990; 127: 488 -490.[Abstract]

Heckert LL, Griswold MD. Expression of follicle-stimulating hormone receptor mRNA in rat testes and Sertoli cells. Mol Endocrinol. 1991;5: 670 -677.[Medline]

Hess RA. Quantitative and qualitative characteristics of the stages and transitions in the cycle of the rat seminiferous epithelium: light microscopic observations of perfusion-fixed and plastic-embedded testes. Biol Reprod. 1990; 43: 525 -542.[Abstract]

Hess RA, Schaeffer DJ, Eroschenko VP, Keen JE. Frequency of the stages in the cycle of the seminiferous epithelium in the rat. Biol Reprod. 1990;43: 517 -524.[Abstract]

Kangasniemi M, Kapia A, Toppari J, Perheentupa A, Huhtaniemi IT, Parvinen M. Cellular regulation of FSH binding in rat seminiferous tubules. J Androl. 1990;11: 336 -343.[Abstract/Free Full Text]

Kim IS. Effects of exposure of lactating female rats to polychlorinated biphenyls (PCBs) on testis weight, sperm production and Sertoli cell numbers in the adult male offspring. J Vet Med Sci. 2001;63: 5 -9.[Medline]

Kim IS, Ariyaratne HB, Chamindrani Mendis-Handagama SM. Effects of continuous and intermittent exposure of lactating mothers to Aroclor 1242 on testicular steroidogenic function in the adult male offspring. Tissue Cell. 2001; 33: 169 -177.[Medline]

Kovacevic R, Vojinovic-Miloradov M, Teodorovic I, Andric S. Effect of PCBs on androgen production by suspension of adult rat Leydig cells in vitro. J Steroid Biochem Mol Biol. 1995; 52: 595 -597.[Medline]

Kuriyama SN, Chahoud I. In utero exposure to low-dose 2,3',4,4',5-pentachlorobiphenyl (PCB118) impairs male fertility and alters neurobehavior in rat offspring. Toxicology. 2004; 202: 185 -197.[Medline]

Levy H, Deane HW, Rubin BL. Visualization of steroid-3-ß-ol-dehydrogenase activity in tissue of intact and hypophysectomized rats. Endocrinology. 1959; 65: 932 -943.

Lundkvist U. Clinical and reproductive effects of clophen A50 (PCB) administered during gestation on pregnant guinea pigs and their offspring. Toxicology. 1990; 61: 249 -257.[Medline]

Mably TA, Bjerke DL, Moore RW, Gendron-Fitzpatrick A, Peterson RE. In utero and lactational exposure of male rats to 2,3,7,8-tetrachlorodibenzo-p-dioxin. 3. Effects on spermatogenesis and reproductive capability. Toxicol Appl Pharmacol. 1992a; 114: 118 -126.[Medline]

Mably TA, Moore RW, Goy RW, Peterson RE. In utero and lactional exposure of male rats to 2,3,7,8-tetrachlorodibenzo-p-dioxin. 2. Effects on sexual behavior and the regulation of luteinizing hormone secretion in adulthood. Toxicol Appl Pharmacol. 1992b; 114: 108 -117.[Medline]

Mably TA, Moore RW, Peterson RE. In utero and lactional exposure of male rats to 2,3,7,8-tetrachlorodibenzo-p-dioxin. 1. Effects on androgenic status. Toxicol Appl Pharmacol. 1992c; 114: 97 -102.[Medline]

Mack SO, Garrett WM, Guthrie HD. Absence of correlation between in situ expression of cytochrome P450 17{alpha} hydroxylase/lyase and 3ß-hydroxysteroid dehydrogenase/{Delta}5-4 isomerase messenger ribonucleic acids and steroidogenesis during pubertal development in the rat testis. J Steroid Biochem Mol Biol. 2000; 73: 19 -28.[Medline]

Meachem SJ, Wreford NG, Stanton PG, Robertson DM, McLachlan RI. Follocle-stimulating hormone is required for the initial phase of spermatogenic restoration in adult rats following gonadotropin suppression. J Androl. 1998;19: 725 -735.[Abstract/Free Full Text]

Meerts IA, Hoving S, Van Den Berg JH, et al. Effects of in utero exposure to 4-hydroxy-2,3,3',4',5-pentachlorobiphenyl (4-OH-CB107) on developmental landmarks, steroid hormone levels and female estrous cyclicity in rats. Toxicol Sci. 2004; 82: 259 -267.[Abstract/Free Full Text]

Nishihara M, Winters CA, Buzko E, Waterman MR, Dufau, ML. Hormonal regulation of rat Leydig cell cytochrome P-45017 alpha mRNA levels and characterization of a partial length rat P-45017 alpha cDNA. Biochem Biophys Res Commun. 1988; 154: 151 -158.[Medline]

O'Donnel L, McLachlan RI, Wreford NG, de Kretser DM, Robertson DM. Testosterone withdrawal promotes stage-specific detachment of round spermatids from the rat seminiferous epithelium. Biol Reprod. 1996; 55: 895 -901.[Abstract]

O'Donnel L, McLachlan RI, Wreford NG, Robertson DM. Testosterone promotes the conversion of round spermatid between stages VII and VIII of the rat spermatogenic cycles. Endocrinology. 1994; 135: 2608 -2614.[Abstract]

Ohsako S, Miyabara Y, Nishimura N, et al. Maternal exposure to a low dose of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) suppressed the development of reproductive organs of male rats: dose-dependent increase of mRNA levels of 5{alpha}-reductase type 2 in contrast to decrease of androgen receptor in the pubertal ventral prostate. Toxicol Sci. 2001;60: 132 -143.[Abstract/Free Full Text]

Pflieger-Bruss S, Hanf V, Behnisch P, Hagenmaier H, Rune GM. Effects of single polychlorinated biphenyls on the morphology of cultured rat tubuli seminiferi. Anrologia. 1999; 31: 77 -82.

Pratis K, O'Donnel L, Ooi GT, McLachlan RI, Robertson DM. Enzyme assay for 5{alpha}-reductase type 2 activity in the presence of 5{alpha}-reductase type 1 activity in rat testis. J Steroid Biochem Mol Biol. 2000;75: 75 -82.[Medline]

Pratis K, O'Donnel L, Ooi GT, Stanton PG, McLachlan RI, Robertson DM. Differential regulation of rat testicular 5{alpha}-reductase type 1 and 2 isoforms by testosterone and FSH. J Endcrinol. 2003; 176: 393 -403.

Roman BL, Timms BG, Prins GS, Peterson RE. In utero and lactational exposure on male rats to 2,3,7,8-tetrachlorodibenzo-p-dioxin impairs prostate development. 2. Effects on growth and cytodifferentiation. Toxicol Appl Pharmacol. 1998; 150: 254 -270.[Medline]

Ruiz de Galarreta CM, Fanjul LF, Median R, Hsueh AJ. Regulation of 3 beta-hydroxysteroid dehydrogenase activity by human chorionic gonadotropin, androgens, and anti-androgens in cultured testicular cells. J Biol Chem. 1983;258: 10988 -10996.[Abstract/Free Full Text]

Safe S. Polychlorinated biphenyls (PCBs), dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and related compounds: environmental and mechanistic considerations, which support the development of toxic equivalency factors (TEFs). Crit Rev Toxicol. 1990;21: 51 -88.[Medline]

Sager DB. Effects of postnatal exposure to polychlorinated biphenyls on adult male reproductive function. Environ Res. 1983;31: 76 -94.[Medline]

Sager DB, Girard D, Nelson D. Early postnatal exposure to PCBs: sperm function in rats. Environ Toxicol Chem. 1991; 10: 737 -746.

Sager DB, Shin-Schroeder W, Girard D. Effects of early postnatal exposure to polychlorinated biphenyls (PCBs) on fertility in male rats. Bull Environ Contam Toxicol. 1987; 28: 946 -953.

Shain W, Overmann SR, Wilson LR, Kostas J, Bush B. A congener analysis of polychlorinated biphenyls accumulating in rat pups after perinatal exposure. Arch Environ Contam Toxicol. 1986; 15: 687 -707.[Medline]

Shan LX, Bardin CW, Hardy MP. Immunohistochemical analysis of androgen effects on androgen receptor expression in developing Leydig and Sertoli cells. Endocrinology. 1997; 138: 1256 -1266.

Shan LX, Hardy JF, Catterall MP. Effects of luteinizing hormone (LH) and androgen on steady state levels of messenger ribonucleic acid for LH receptors, androgen receptors, and steroidogenic enzymes in rat Leydig cell progenitors in vivo. Endocrinology. 1995; 136: 1686 -1693.[Abstract]

Stocco DM, Clark BJ. Role of the steroidogenic acute regulatory protein (StAR) in steroidogenesis. Biochem Pharmacol. 1996; 51: 197 -205.[Medline]

Takagi Y, Aburada S, Hashimoto K, Kitamura T. Transfer and distribution of accumulated (14C)polychlorinated biphenyls from maternal to fetal and suckling rats. Arch Environ Contam Toxicol. 1986; 15: 709 -715.[Medline]

Tang PZ, Tsai-Morris VH, Dufau ML. Regulation of 3beta-hydroxysteroid dehydrogenase in gonadotropin-induced steroidogenic desensitization of Leydig cells. Endocrinology. 1998; 139: 4496 -4505.[Abstract/Free Full Text]

Van den Berg M, Birnbaum L, Bosveld ATC, et al. Toxic equivalency factors (TEFs) for PCBs, PCDDs, PCDFs for human. Environ Health Perspect. 1998;106: 775 -792.[Medline]

Weber KS, Setchell KDR, Stocco DM, Lephart ED. Dietary soy-phytoestrogens decrease testosterone levels and prostate weight without altering LH, prostate 5{alpha}-reductase or testicular steroidogenic acute regulatory peptide levels in adult male Sprague-Dawley rats. J Endocrinol. 2001;170: 591 -599.[Abstract]

Wilker C, Johnson L, Safe S. Effects of developmental exposure to indol-3-carbinol or 2,3,7,8-tetrachlorodibenzo-p-dioxin on reproductive potential of male rat offspring. Toxicol Appl Pharmacol. 1996;141: 68 -75.[Medline]

Wright WW, Frankel AI. Endogeneous androgen concentrations in nuclei isolated from seminiferous tubules of mature rat testes. J Steroid Biochem. 1979;10: 633 -640.[Medline]

Zhou Z, Lane MV, Kemppainen JA, French FS, Wilson EM. Specifity of ligand-dependent androgen receptor stabilization: receptor domain interactions influence ligand dissociation and receptor stability. Mol Endocrinol. 1995;9: 208 -218.[Abstract]





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