当前位置:文档之家› 2009--JME-Exposure of Xenopus laevis tadpoles to finasteride

2009--JME-Exposure of Xenopus laevis tadpoles to finasteride

2009--JME-Exposure of Xenopus laevis tadpoles to finasteride
2009--JME-Exposure of Xenopus laevis tadpoles to finasteride

Page 1 of 31Accepted Preprint first posted on 24 June 2009 as Manuscript JME-09-0058 Exposure of Xenopus laevis tadpoles to finasteride, an inhibitor of 5-alpha reductase activity, 1

impairs spermatogenesis and alters hypophyseal feedback mechanisms

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Abbreviated title: 5-α reductase and spermatogenesis

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Urbatzka, R.1, 4, Watermann, B.2,Lutz, I. 1 and Kloas, W.1, 3

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1IGB, Leibniz-Institute of Freshwater Ecology and Inland Fisheries, Department of Inland Fisheries,

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Mueggelseedamm 301, 12587 Berlin, Germany

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2Limnomar, Bei der Neuen Muenze 11, 22145 Hamburg, Germany

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3Department of Endocrinology, Institute of Biology, Humboldt-University, Invalidenstrasse 43, 10115

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Berlin, Germany

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4present address: Centre of Marine and Environmental Research, Rua dos Bragas 289, 4050-123 Porto,

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Portugal

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Corresponding author:

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Ralph Urbatzka, IGB, Leibniz-Institute of Freshwater Ecology and Inland Fisheries, Department of

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Inland Fisheries, Mueggelseedamm 301, 12587 Berlin, Germany, and Centre of Marine and

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Environmental Research, Rua dos Bragas 289, 4050-123 Porto, Portugal, rurbatzka@ciimar.up.pt,

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Phone: +351 223 401 831, Fax: +351 223 390 608

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Page 2 of 31 Abstract

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Sexual steroids have major regulatory functions in gonadal development, maturation of gametes and

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sexual differentiation in vertebrates. Previous studies in amphibians provided evidence that

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dihydrotestosterone and activity of 5-α reductases might play a significant role in androgen mediated

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reproductive biology. To test involvement of 5-α reductases in maturation of gametes in amphibians,

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X. laevis was exposed to finasteride (FIN), a known inhibitor of 5-α reductase enzyme activity. In a

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long-term exposure from stage 46 to 66, severe disruption of spermatogenesis was observed in

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histological analysis of testes as detected by occurrence of empty spermatocysts, while ovaries

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remained unaffected. Real-time PCR analyses of male and female brain revealed an increase of

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luteinizing hormone (LHβ) mRNA and a decrease in follicle stimulating hormone mRNA in males

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suggesting a signalling on testes that could result in increased steroidogenesis and reduced Sertoli cell

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proliferation. Accordingly, the mRNA expression of P450 side chain cleavage enzyme and of 5-α

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reductase type 2 was increased in testes, while no effects could be observed on steroidogenic genes in

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ovaries. A short-term exposure to testosterone (T), FIN and T + FIN showed that transient effects of

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FIN targeted males selectively and in particular interfered with the hypothalamus-pituitary-gonad axis.

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Furthermore, a negative feedback of T on LHβwas observed on males and females. This study

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provides evidence that exposure of X. laevis to FIN, an inhibitor of 5-αreductases, impaired

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spermatogenesis and involved sex-specific hypophyseal feedback mechanisms.

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Keywords: Xenopus laevis, finasteride, 5-alpha reductase, spermatogenesis, luteinizing hormone,

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follicle stimulating hormone, gonadotropines, hypothalamus-pituitary-gonad axis.

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Page 3 of 31

Introduction

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Synthesis of sexual steroids is a conserved process in vertebrates starting with cholesterol that is 2

converted by actions of multiple enzymes into testosterone (T). T can either exert androgen action by 3

itself or can be further converted into dihydrotestosterone (DHT) or into 17β-estradiol (Payne and 4

Hales 2004). Leydig cells in testis and theca/granulosa cells in ovaries are the main producing cells of 5

sexual steroids that are subsequently released into the blood stream. Biological action in peripheral 6

tissues often needs the conversion of T into DHT that is accomplished by the enzyme 5-α reductase.

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Two isozymes exist for 5-αreductase, named type 1 (Srd5a1) and type 2 (Srd5a2), which are 8

differentially distributed in many tissues. In rats, Srd5a2 is confined to androgen-dependent tissues 9

while Srd5a1 is present in various tissues (Torres et al. 2003). Especially Srd5a2 activity is believed to

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play a key role in androgen regulated reproductive biology.

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In mammals as in amphibians the more potent androgen is DHT unlike in fish, where 11-

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ketotestosterone is the most potent androgen (Norris 1997). DHT promotes in humans and mammals

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the development of external genitalia, or androgenic tissues like prostate while T is responsible for the

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development of male internal genitalia. Finasteride (FIN), a well-known inhibitor of 5-αreductase

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activity with higher potency to Srd5a2 than to Srd5a1 (George et al.1989; Prahalada et al., 1997;

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Ellsworth et al.1998), was frequently used to experimentally unravel functions of 5-αreductases

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being involved in male pattern hair loss (Kawashima et al. 2004) or benign prostate hyperplasia or

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prostate cancer (Luo et al. 2003). If administered in utero, external genitalia were feminized in rats

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(Imperato-McGinley et al.1992) or developed abnormalities in rhesus monkeys (Prahalada et al.

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1997). Humans with deficiency of Srd5a2 developed feminized genitalia (Imperato-McGinley et al.

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1981) and polymorphisms in Srd5a2 gene were associated with differences in sperm concentration and

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motility (Elzanaty et al. 2006).

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In the Srd5a2 gene promoter region a progesterone and androgen response element (PRE/ARE) was

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identified in mouse suggesting that different androgens might be able to regulate gene expression of

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Srd5a2 (Matsui et al.2002). T regulated enzyme activity of 5-αreductase in an in vitro system

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Page 4 of 31 (Andersson et al. 1989), mRNA expression of Srd5a2 in prostate of intact and castrated rats in vivo

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(Torres et al. 2003) and in rat brain in vivo and in vitro (Poletti et al. 1998). However, also DHT is

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described to induce 5-αreductase activity in rats (George et al.1991). Effects of T and DHT are

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mediated both via the androgen receptor and it is known that some genes are differentially regulated

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by T and DHT, respectively (Avila et al.1998). The mechanism for this is still unclear, but it is

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proposed that especially in peripheral tissues with low T level, specific action of 5-αreduced

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androgens are needed.

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In amphibians, some studies provided evidence that DHT is a decisive androgen for sexual

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differentiation in Xenopus laevis: DHT but not T at a concentration of 10-8 M induced sex reversal in

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an exposure experiment (B?gi et al.2002; Kloas 2002) and sex-specific pattern of Srd5a2 mRNA

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expression during ontogeny suggested an important function in male gamete maturation (Urbatzka et

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al. 2007). The aim of the present study was to analyse the effect of FIN on the development of gonads

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in X. laevis and to gain insights into the physiological function of 5-αreductases in regulating

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reproductive biology of amphibians. Therefore tadpoles of X. laevis were exposed to FIN during their

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sensitive phase of gonadal development and sexual differentiation with the intention to decrease the

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activities of 5-α reductase enzymes in X. laevis. The effects of FIN on gonad histology of X. laevis

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were monitored at stage 66, just after completion of metamorphosis. Additionally, the expression of

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LH and FSH mRNA was analysed in brain samples and the expression of selected steroidogenic genes

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(P450scc, StAR, Srd5a1, Srd5a2 and Aro) in gonad samples. In complement to the analysis of long

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term effects of FIN, a short term exposure was conducted to analyse the transient effects of FIN. The

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short-term exposure included three treatment groups, T, FIN, and T + FIN to address the question of a

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potential regulation of 5-α reductase by T in amphibians, a regulation that was frequently observed in

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mammalian model species. In this study, X. laevis was used for the first time as a comparative model

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to unravel the potential function of 5-α reductases on spermatogenesis in lower vertebrates.

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Page 5 of 31

Material and Methods

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Exposure

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Xenopus laevis were taken from the breeding stock of the Institute of Freshwater Ecology and Inland 4

Fisheries, Berlin, Germany. Adult X. laevis were injected with human chorionic gonadotropin 5

(SIGMA, Deisenhofen, Germany) into the dorsal lymph sac to induce spawning as described 6

previously (Kloas et al.1999). Fertilized eggs and tadpoles were reared in 50 L tanks containing 7

reconstituted tap water using deionised water supplemented with 2.5 g marine salt (Tropic Marin 8

Meersalz, Tagis, Dreieich, Germany) per 10 L. Tanks were aerated and temperature was adjusted to 22 9

± 1°C. The light:dark cycle was 12:12 h and tadpoles were fed daily with Sera Micron (Sera GmbH,

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Heinsberg, Germany). The developmental stages of the tadpoles were determined according to the

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Normal Table of X. laevis (Nieuwkoop and Faber 1994).

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For a long-term exposure, tadpoles at stage 46 were transferred to 10 L aerated glass aquaria at a

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density of 30 tadpoles per tank containing 7 L of reconstituted tap water. Tadpoles were exposed to

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FIN (APIN Chemicals LTD, a gift of Dr. John Ashby, Central Toxicology Laboratory, Cheshire,

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Syngenta, UK), a known 5-αreductase enzyme inhibitor. FIN was dissolved in dimethylsulfoxide

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(DMSO, SIGMA) and the highest soluble concentration was chosen for exposure that did not re-

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crystallize if added to the water. The final concentration of FIN was 7 x 10-6M (2.66 mg/L) and

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DMSO concentration was 0.0286%. Exposure was conducted in duplicate tanks (total n = 60) and

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included a solvent control. Water and chemicals were renewed every Monday, Wednesday and Friday.

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Tadpoles were sampled after completion of metamorphosis (stage 66). Sex of tadpoles was determined

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by gross morphology of the gonads using a stereo microscope before gonads were fixed in bouin′s

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solution for 24 h. Fixed gonads were transferred to 80% EtOH for 24 h and then stored in fresh 80%

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EtOH until further processing for histological analyses. Further gonad and brain samples of male and

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female tadpoles were dissected, immediately snap-frozen in liquid nitrogen and stored at -80°C until

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further analyses.

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Page 6 of 31 In the short-term exposure, tadpoles were reared in aerated glass aquaria until they reached stage 58.

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At this stage, tadpoles were transferred to the exposure tanks in a density of 18 tadpoles per tank

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containing 7 L of reconstituted tap water. Tadpoles were exposed to T at a supra-physiological

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concentration of 10-7 M, to FIN at a concentration of 7 x 10-6M and to a combination of both. A

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solvent control (DMSO 0.0867%) and a control without solvent were included in the experimental

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setup. Exposure lasted 4 days and water and chemicals were changed daily. Brain and gonads of six

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male and female tadpoles were dissected at day 5, directly snap-frozen in liquid nitrogen and stored at

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-80°C until further analyses.

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Histology

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From the long-term exposure, 6 males and 6 females of the control and of the FIN treatment were

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analysed for histological alterations of the gonads. 3 – 4 μm sections from paraffin blocks were cut

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using a microtome. Tissue sections were deparaffinized in xylene for 15 min, washed sequentially in

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96%, 90%, 70%, 50%, 30% EtOH (2 min each) and in aqua dest. for 5 min. Subsequently, one set of

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sections was stained with hematoxylin-eosin (H-E), while another set was stained by

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immunocytochemistry for the proliferating cell nuclear antigen (PCNA) as indication for cell

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proliferation. Heat-induced epitope retrieval was performed by transfer of the slides into a jar

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containing S?rensen’s citrate buffer (pH 6) on a hot water bath (96°C to 99°C) for 30 min. After

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cooling down the slides for 20 min at room temperature, the slides were washed with phosphate

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buffered saline (PBS) and aqua dest. Endogenous peroxidase was quenched in 3% hydrogen peroxide

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for 5 min with subsequent rinsing in PBS. 100 μL of anti-PCNA were applied to the slide, incubated at

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room temperature in a humidity chamber for 30 min and rinsed in PBS. The working concentration of

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anti-PCNA was 1:200, diluted in PBS. Next, 100 μL of peroxidase was added to the slide, followed by

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incubation of the slide for 30 min in a humidity chamber and rinsing with PBS. The final step

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comprised the application of the chromagen solution NovaRED, incubation in a humidity chamber for

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15 min, washing in aqua dest. for 5 min and counterstaining of the slides with hematoxylin.

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RNA-Isolation and reverse transcription (RT)

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Page 7 of 31

Extraction of total RNA of brain samples of tadpoles from the long-term exposure and of brain and 1

gonad samples of tadpoles from the short-term exposure was performed by using RNA extraction kits 2

of Qiagen (RNeasy Micro Kit, RNeasy Mini Kit, Hilden, Germany) according to the instructions of 3

the manufacturer and included on-column DNAse ingestion (Qiagen). Transcription of RNA into 4

cDNA was accomplished by reverse transcriptase reaction (RT) and was performed with 1 μg total 5

RNA for the brain samples and with 200 ng total RNA for the gonad samples. For RT of brain samples 6

7.5 pM poly (dT) primer (Biometra, G?ttingen, Germany), 10 mM dNTP (Qbiogene, Heidelberg,

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Germany) and 10 U AMV reverse transcriptase (Finnzymes, Finnland) were applied in a 30 μl 8

reaction while for RT of gonad samples 10 U AffinityScript reverse transcriptase (Stratagene, 9

Amsterdam, The Netherlands) were used in a 20 μL reaction.

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Real-time RT-PCR

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Amplifications of cDNA specific for luteinizing hormone (LHβ), follicle stimulating hormone (FSHβ),

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P450 side chain cleavage enzyme (P450scc), steroidogenic acute regulatory protein (StAR), 5-α

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reductase type 1 (Srd5a1), 5-α reductase type 2 (Srd5a2), aromatase (Aro) and elongation factor 1-α

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(EF) as housekeeping gene of X. laevis were carried out by using real-time RT-PCR. Amplification

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was carried out in a thermal cycler (Stratagene, Mx3000P) using SYBR green. The following thermal

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cycling conditions were applied: 7 min 40 sec at 95°C followed by 40 cycles of 17 s at 95°C, 25 s at

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62°C, 25 s at 72°C. Melting curve analyses were performed with the following setting, 40 sec at 95°C,

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30 sec at 55°C and 30 sec at 95°C. For all PCR reactions, cDNA was diluted 1:5 (brain samples) or

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1:10 (gonad samples) and 3 μl of diluted cDNA were mixed in a 25 μl reaction with 10 mM dNTP′s

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(Qbiogene), 1:40.000 SYBR (Invitrogen), 1:200 ROX (Invitrogen), 2 mM MgCl2, 100 - 400 pM

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forward and reverse primer and 1 U of Platinum Taq-Polymerase (Invitrogen).

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Primers were designed according to sequences published in the National Centre for Biotechnology

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Information (NCBI). All sequences were derived from X. laevis with the exception of Srd5a1 and

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Srd5a2 that were deduced from X. tropicalis. Table 1 lists the sequences of the designed primers. To

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test specificity of the PCR products the bands were run on an agarose gel, extracted (QIAquick, Gel

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Page 8 of 31 extraction kit, Qiagen, Hilden, Germany) and forwarded to automated sequencing (SeqLab, Sequence

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Laboratories, G?ttingen, Germany). Sequence comparisons by BLAST and sequence alignments

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(BioEdit) confirmed the specificity of amplified PCR products.

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Data analysis and statistics

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MxPro software (Stratagene) was used to analyse real-time PCR data using the ??Ct-method

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including the PCR efficiencies of the genes (ranging from 91.6 % to 104.5 %). Values of the mRNA

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expressions of the target genes were normalized by the values of the house-keeping gene. After testing

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normal distribution, data of long-term exposure was analysed with unpaired t-tests. For data of short-

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term exposure, one-way ANOVA was used to examine significant differences between the mRNA

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expressions of the treatments. Either Tukey′s test or Dunnet-T3 test was applied depending on the

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outcome of testing equality of variance by the Levene-test. Histological data were analysed by using

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Mann-Whitney U-test. For all statistical analyses, differences were regarded to be significant if p was

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< 0.05.

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Page 9 of 31

Results

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Long-term exposure

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Mortality of tadpoles during exposure was very low and was 2% in control tanks (one individual) and 3

0% in finasteride (FIN) treatment tanks. No differences between control and FIN treatment groups 4

were observed regarding the time needed to complete metamorphosis, and their total length at stage 5

66. Tadpoles developed from stage 46 to stage 66 in about six weeks and the mean length was 1.8 ±

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0.2 cm. Exposure of X. laevis tadpoles during ontogeny to FIN did not affect the sex ratio of tadpoles.

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Sex ratio in the FIN treatment group was not significantly different from the solvent control group 8

with 60% males and 40% females.

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Histological analyses of gonads revealed that male X. laevis from the solvent control group had

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relatively immature testes containing mainly spermatogonia and spermatocytes in numerous

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spermatocysts (Figure 1, panel A). A further maturation to spermatids or spermatozoa was not

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observed in these animals. Proliferation activity of spermatogonia and spermatocytes was high as

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indicated by PCNA staining (Figure 1, panel B). FIN exposed male X. laevis possessed comparable

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maturation stages as in the solvent control group, namely spermatogonia and spermatocytes but not

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spermatids or spermatozoa. In 5 of 6 analysed FIN treated males, empty cavities were observed in the

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tubules and this likely corresponded to former spermatocysts with secondary spermatogonia (Figure 1,

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panel C). Quantitative analyses of male gonadal sections revealed a statistically significant occurrence

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of empty spermatocysts (p < 0.01). While there was no significant difference, FIN treated male

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animals seemed to have a lower number of tubuli, spermatogonia and spermatocytes (Table 2).

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Intensity of proliferation was dramatically reduced in all FIN treated males compared to the solvent

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control group indicated by the lower number of visible mitoses and reduced PCNA staining (Figure 1,

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panel D).

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In female X. laevis from the solvent control group ovaries were in the maturation stage in that ovarian

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cavities were formed or expanded. In the cortical region numerous germ cells and primary oocytes

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arranged in nests were observed (Figure 1, panel E). Proliferation activity indicated by PCNA staining

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was moderate in germ cells and high in primary oocytes (Figure 1, panel F). Stages of maturation and

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structure of gonads of FIN treated female X. laevis were similar compared to females from the solvent

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Page 10 of 31 control (Figure 1, panel G) and also proliferation activity was about the same (Figure 1, panel H). The

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development of an ovarian cavity was not observed in one ovary.

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In brain samples of male X. laevis, LH mRNA expression was about 9-fold increased in the FIN

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treatment group (p < 0.001), while FSH mRNA expression was decreased in FIN-treated males (p <

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0.05) (Figure 2). In testes, P450scc and Srd5a2 mRNA were significantly increased (p < 0.01), while

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no effects were observed for StAR, Srd5a1 and Aro mRNA expression (Figure 2).

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In brain of female X. laevis, the expression of both gonadotropins was not altered by waterborne

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exposure to FIN (Figure 3). In ovaries, no different expression was observed in the FIN treatment

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group relative to the solvent control for all analysed steroidogenic genes.

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Short-term exposure

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In male tadpoles from the four day exposure, LHβ mRNA in the brain was significant decreased by T

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as well as by the combined exposure to T and FIN. In contrast, exposure to FIN alone led to a

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significant increase of LHβ mRNA expression and was about 8-fold higher than in the control and in

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the solvent control (Figure 4). FSH mRNA expression was not changed by any treatment. In the

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gonads, P450scc mRNA expression was 2-fold elevated in response to FIN while the other treatments

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had no effect. StAR, Srd5a1, Srd5a2, and Aro mRNA expression stayed at the same expression levels

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compared to both control groups.

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In female tadpoles, LHβmRNA in the brain was significantly decreased by T and the combined

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exposure to T and FIN compared to the solvent control corresponding to the results obtained in male

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tadpoles (Figure 5). FIN alone did not change LHβmRNA expression in females. No significant

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changes of mRNA expression were observed in the other analysed genes (FSHβ, P450scc, StAR,

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Srd5a1, Srd5a2, and Aro) relative to control and solvent control.

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Page 11 of 31

Discussion

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Tadpoles of X. laevis were exposed to FIN, a known inhibitor of 5-α-reductase enzyme activity 2

(George et al. 1989; Ellsworth et al. 1998), during their sensitive phase of gonadal development and 3

sexual differentiation. In a previous study an important function of 5-αreduced metabolites was 4

suggested for spermatogenesis, observing sex-specific mRNA expression pattern of Srd5a2 in X.

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laevis tadpoles during their ontogeny at the beginning of gamete maturation (Urbatzka et al. 2007).

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The present study demonstrated that FIN affected specifically males and not females leading to a 7

disruption of spermatogenesis and to altered mRNA expression of gonadotropins in the brain and of 8

steroidogenic genes in the gonads.

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Histological analyses of gonads of male X. laevis tadpoles exposed to FIN revealed a severe disruption

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of spermatogenesis. Emptied cavities were observed in the analysed gonads that corresponded to

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former spermatocysts with secondary spermatogonia (Figure 1) and a reduced proliferation activity in

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FIN treated males. According to these results, it was shown in male rats during puberty that a peak of

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5-αreductases and 5-αreduced metabolites coincided with the first wave of spermatogenesis

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suggesting a role for 5-α reductases in the initiation of spermatogenesis (Killian et al. 2003). In studies

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during adulthood, no effects of FIN on testicular histomorphology were found in rats (George et al.

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1989; Rhoden et al. 2002) and dogs (Juniewicz et al. 1993). In contrast, a study performed in adult rats

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showed that administration of FIN suppressed the T induced restoration of spermatogenesis and

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demonstrated clearly a role for 5-αreduced androgens in adult spermatogenesis (O′Donnell et al.

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1996). In contrast to the specific mode of action of FIN, the antiandrogen flutamide (FLU) inhibits the

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action of various androgens at the androgen receptor and exposure experiments demonstrated the

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importance of androgens in spermatogenesis in different vertebrates. If rats were exposed in utero to

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FLU, the death of testicular germ cells was observed in a concentration-dependent way mediated by

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apoptotic gene expression (Bozec et al.2004). Fish exposed to FLUexperienced spermatocyte

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degeneration in fathead minnow (Jensen et al. 2004) or reduced numbers of spermatogenic cysts in

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male guppies (Kinnberg and Toft 2003).

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In contrast to the results obtained in male tadpoles, histological analyses of ovaries demonstrated no

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alterations in the FIN treatment group compared to the control group. The single finding of one female

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Page 12 of 31 gonad without the forming of an ovarian cavity may be an effect of FIN, but has to be verified in

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future experiments. In tadpoles of Bufo bufo and of Rana dalmatina, the inhibition of 5-α reductase

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activity accelerated the ovarian differentiation in females suggesting an inhibiting role for 5-α reduced

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metabolites regarding the timing of ovarian differentiation and maybe also for inhibiting oocyte

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maturation in females (Zaccanti et al. 1994; Petrini and Zaccanti 1998). However, this finding could

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not be confirmed in the present study.

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The analysis of gonadotropin mRNA expression in male and female X. laevis from the long-term

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exposure revealed a sex-specific hypophyseal feedback mechanism. Selectively in males, LH mRNA

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was strongly increased in the FIN treatment group while FSH mRNA was decreased (Figure 2). LH is

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known to act mainly on steroidogenesis in gonads while FSH is essential for Sertoli cell proliferation

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(Weltzien et al.2004). Therefore, this observed regulation pattern could signal an increased

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steroidogenesis in testes and a reduced Sertoli cell proliferation that could potentially have caused the

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observed impairment of spermatogonia maturation considering the central role of Sertoli cells in germ

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cell development. Mitotic activity of Sertoli cells in fish was highest during spermatogonial

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proliferation and considered as an important factor determining testis size and sperm production

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(Schulz et al. 2005). The modulatory effect of FIN on gonadotropin mRNA expression in male X.

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laevis is shown for the first time and demonstrated an involvement of a physiological regulation of the

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H-P-G axis. This finding fits to a study in rats, where a high dose of FIN (250 mg/kg/day) increased

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the plasma LH level that correlated with Leydig cell hyperplasia (Prahalada et al.1994), while in

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another study plasma LH level remained unchanged in a concentration of 20 mg/kg/day (Ribeiro and

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Pereira 2005). The contrary regulation of LH and FSH mRNA expression in response to sexual

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steroids was confirmed in further experiments from our workgroup, even if the mechanism remains

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unclear (Urbatzka et al., 2008). From studies in fish it is known that sexual steroids can regulate

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gonadotropins differently, inhibiting one gene and stimulating the other (Sohn et al., 2001; Mateos et

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al., 2002).

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Page 13 of 31

In gonads of long-term exposed animals, steroidogenic gene expression was changed in males, but not 1

in females (Fig. 2 and 3). FIN treatment increased P450scc and Srd5a2 mRNA expression in testes, 2

while StAR, Srd5a1 and Aro mRNA expression was not affected. It is well known that steroidogenesis 3

is under control of gonadotropins (Weltzien et al., 2004) and therefore it is likely that increased LH 4

mRNA in brain stimulated the transcription of P450scc. Interestingly, StAR mRNA expression was 5

only slightly, but not significant increased. StAR is the enzyme responsible for cholesterol transport 6

into the mitochondria where it is converted by P450scc to pregnenolone (Arukwe, 2008). Studies in 7

fish showed that StAR and P450scc mRNA expression pattern were different under some 8

experimental conditions regarding to exposure time, compounds and their concentration (Arukwe 9

2005, Kortner et al., 2009a, Kortner et al., 2009b). The increase of Srd5a2 mRNA in testis in FIN

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treated animals is suggested to be a counter-regulation to the inhibition of 5-αreductase enzyme

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activities and indicated the presence of a regulatory feedback loop. Thereby, the counter-regulation

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could be driven directly by the assumed lower DHT level or by the observed feedback on LH mRNA

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expression. The Srd5a1 mRNA expression was only slightly increased, but not significant, and could

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be associated to the fact that FIN inhibits 5-α reductase type 2 enzyme with higher potency than 5-α

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reductase type 1 enzyme (Prahalada et al., 1997; Ellsworth et al., 1998). Aro mRNA expression stayed

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at the same expression level indicating no interference of FIN with estrogen synthesis.

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Male and female tadpoles at stage 58 were exposed to T, FIN and a combination of both in a short-

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term exposure to analyse transient effects on gonadotropin mRNA expression in the brain and on

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steroidogenic gene expression in the gonads. T was chosen as androgen since its stimulatory function

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on 5-α reductase mRNA expression and enzyme activity in peripheral tissues (Andersson et al. 1989;

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Poletti et al. 1998; Torres et al. 2003). LHβ mRNA expression was significantly reduced by T and T +

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FIN in males and females, but no effects were observed on FSH mRNA expression or on

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steroidogenic gene expression in the gonads. The negative feedback of androgens on the H-P-G axis is

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known from previous studies in mature amphibians. DHT reduced the plasma LH level in male, adult

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Rana pipiens (Tsai et al. 2005) and MDHT decreased the LHβ mRNA expression in male, adult X.

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laevis (Urbatzka et al. 2006). Thus, it is suggested that decreased LHβ mRNA levels in T and T + FIN

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Page 14 of 31 treatment are due to negative feedback of T. A regulation of Srd5a2 by T like in mammals or in vitro

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(Andersson et al. 1989; George et al. 1991; Poletti et al. 1998; Torres et al. 2003) was not observed in

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this study for X. laevis. In accordance to the long-term exposure, the effect of FIN was restricted to

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males and included an increase of LHβmRNA and of P450scc mRNA indicating an increase in

4

steroidogenesis mediated by feedback on LH. FIN treatment in rat resulted in an increase of T and

5

androstenedione, in a decrease of DHT (George 1997), and additionally increased estradiol in humans

6

(Castro-Magana et al., 1996). If a similar effect of FIN on steroids is assumed in this study, the

7

increased LHβ mRNA expression in the FIN treatment group is unlikely to be induced by the increase

8

of T or estrogens since exposure to T was demonstrated in this study to inhibit LHβmRNA

9

expression, an effect also known for exposure of amphibians to estrogens (Urbatzka et al., 2006).

10

Furthermore, androstenedione is known to have only a low affinity to the androgen receptor and is

11

therefore an improbable candidate for steroidal feedback. In contrary, we suggest that the increase of

12

LHβ in the FIN treatment could be due to the assumed lower DHT levels, a regulation thatwould fit to

13

another experiment where exposure to FLU, an androgen receptor antagonist, increased LHβ mRNA

14

expression in males (Urbatzka et al., 2008). A decrease in FSH mRNA and a increase in Srd5a2

15

mRNA as detected in males from the long-term exposure, could only slightly be observed in the short-

16

term exposure and was not significant different from the control. Therefore it may indicate that these

17

effects are time-dependent. Some effects may be unmasked only after a prolonged exposure time.

18

Furthermore, transient effects could be mediated by altered enzyme levels, while long term effects

19

involve de novo synthesis of mRNA.

20

Interestingly, no effect of FIN was observed in females in the short- and long-term exposures either on

21

gonadotropin expression in the brain or on steroidogenic gene expression in ovaries. The reasons for

22

these results remain speculative and may be owed to a differential regulation of feedback mechanisms

23

in the brain.

24

25

The presented study provided clear evidence that FIN affected the expression of gonadotropin mRNA

26

in long-term and short-term exposures. However, the effect of FIN on gonadotropins could be

27

potentially mediated by inhibition of 5-αreductase activity or by a direct effect. The present data

28

Page 15 of 31

indicated an increased Srd5a2 mRNA expression in the long-term exposure as counter-regulation to 1

the assumed inhibition of 5-α reductase enzyme activity. This result is in line with the fact that FIN is 2

a specific inhibitor of 5-αreductase type 2 enzyme activity in mammals (Prahalada et al., 1997;

3

Ellsworth et al., 1998). Accordingly, specific inhibition of 5-α reductase enzyme activity was reported 4

in sea urchins (Wasson and Watts, 1998) suggesting that FIN is acting specifically in vertebrates and 5

non-vertebrates. An assumed lower DHT level in the FIN treatment group could affect the 6

gonadotropin mRNA expression in the pituitary, since it is well known that sexual steroids feedback 7

on the hypothalamus and pituitary. In further experiments of our workgroup, it was demonstrated that 8

LHβmRNA expression in male X. laevis was increased in an exposure to the androgen receptor 9

antagonist flutamide (Urbatzka et al., 2008) providing further indications for this hypothesis.

10

Nevertheless, both hypotheses are suggested to be possible until a proof of decreased enzymatic levels

11

of 5-α reductase or DHT levels is shown in response to FIN treatment in amphibians.

12

13

Summarizing, it was shown that exposure of X. laevis tadpoles to FIN, an inhibitor of 5-α reductase

14

activity, during the phase of gonadal development and sexual differentiation affected only the males

15

and impaired spermatogenesis in testes of metamorphosed frogs. The long-term and short-term

16

exposures to FIN demonstrated a potential involvement of sex-specific hypophyseal feedback

17

mechanisms, in particular an elevation of LHβ mRNA in brain and of P450scc mRNA in gonads. Only

18

the long-term exposure revealed an additional decrease of FSH mRNA in brain and an increase of

19

Srd5a2 mRNA in gonads. Decreased FSH mRNA expression may have caused a reduced Sertoli cell

20

proliferation, important cells for germ cell development, while increased LH mRNA expression was

21

suggested to stimulate steroidogenesis as counter-regulation to FIN.

22

23

24

25

Declaration of interest

26

The authors declare that there is no conflict of interest that could be perceived as prejudicing the

27

impartiality of the research reported.

28

Page 16 of 31

1

Funding

2

This research was funded in part by the European Union within the EU-project EASYRING, contract

3

Nr. QLK4-CT-2002-02286.

4

5

6

Acknowledgment

7

We thank Dr. John Ashby (Central Toxicology Laboratory, Cheshire, Syngenta, UK) for the gift of

8

Finasteride.

9

10

11

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如何写先进个人事迹 篇一:如何写先进事迹材料 如何写先进事迹材料 一般有两种情况:一是先进个人,如先进工作者、优秀党员、劳动模范等;一是先进集体或先进单位,如先进党支部、先进车间或科室,抗洪抢险先进集体等。无论是先进个人还是先进集体,他们的先进事迹,内容各不相同,因此要整理材料,不可能固定一个模式。一般来说,可大体从以下方面进行整理。 (1)要拟定恰当的标题。先进事迹材料的标题,有两部分内容必不可少,一是要写明先进个人姓名和先进集体的名称,使人一眼便看出是哪个人或哪个集体、哪个单位的先进事迹。二是要概括标明先进事迹的主要内容或材料的用途。例如《王鬃同志端正党风的先进事迹》、《关于评选张鬃同志为全国新长征突击手的材料》、《关于评选鬃处党支部为省直机关先进党支部的材料》等。 (2)正文。正文的开头,要写明先进个人的简要情况,包括:姓名、性别、年龄、工作单位、职务、是否党团员等。此外,还要写明有关单位准备授予他(她)什么荣誉称号,或给予哪种形式的奖励。对先进集体、先进单位,要根据其先进事迹的主要内容,寥寥数语即应写明,不须用更多的文字。 然后,要写先进人物或先进集体的主要事迹。这部分内容是全篇材料

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