Reprint of “Current perspectives on the androgen 5 alpha-dihydrotestosterone (DHT) and 5 alpha-reductases in teleost fishes and amphibians”,☆☆

https://doi.org/10.1016/j.ygcen.2014.06.011Get rights and content

Highlights

  • The androgen dihydrotestosterone (DHT) is not well studied in non-mammalian species.

  • DHT can masculinize female fish and frogs.

  • DHT can also induce estrogenic-like effects in teleost fish.

  • 5 alpha-reductase isoforms are expressed early in fish and frog development.

  • 5 alpha-reductases show sex and tissue-specific expression patterns.

Abstract

The androgen 5 alpha-dihydrotestosterone (DHT) is a steroidogenic metabolite that has received little attention in non-mammalian species. DHT is produced by the reduction of the double-bond of testosterone by a group of enzymes called 5 alpha-reductases of which there can be multiple isoforms (i.e., srd5a1, srd5a2, and srd5a3). Data from amphibians suggest that the expression of the srd5a genes occurs in early development, and continues until adulthood; however insufficient data exist in fish species, where DHT is thought to be relatively biologically inactive. Here, we demonstrate that fathead minnow (FHM; Pimephales promelas) developing embryos and adults express srd5a enzyme isoforms. During FHM embryogenesis, both srd5a1 and srd5a3 mRNA levels were significantly correlated in expression levels while srd5a2 showed a more unique pattern of expression. In adult FHMs, males had significantly higher levels of srd5a2 in the liver and gonad compared to females. In the male and female liver, transcript levels for srd5a2 were more abundant compared to srd5a1 and srd5a3, suggesting a prominent role for srd5a2 in this tissue. Interestingly, the ovary expressed higher mRNA levels of srd5a3 than the testis. Thus, data suggest that srd5a isoforms can show sexually dimorphic expression patterns in fish. We also conducted a literature review of the biological effects observed in embryonic and adult fish and amphibians after treatments with DHT and DHT-related compounds. Treatments with DHT in teleost fishes and amphibians have resulted in unexpected biological responses that are characteristic of both androgens and anti-androgens. For example, in fish DHT can induce vitellogenin in vitro from male and female hepatocytes and can increase 17β-estradiol production from the teleost ovary. We propose, that to generate further understanding of the roles of DHT in non-mammals, studies are needed that (1) address how DHT is synthesized within tissues of fish and amphibians; (2) examine the full range of biological responses to endogenous DHT, and its interactions with other signaling pathways; and (3) investigate how DHT production varies with reproductive stage. Lastly, we suggest that the Srd5a enzymes can be targets of endocrine disruptors in fish and frogs, which may result in disruptions in the estrogen:androgen balance in aquatic organisms.

Introduction

The interest in the effects of endocrine disrupting chemicals (EDCs) in the aquatic environment continues to increase over the past decade, specifically those that act on steroidogenic pathways. EDCs that include synthetic androgenic and estrogenic compounds can severely affect endocrine systems in wildlife and exert significant impacts on their reproduction, development and sexual behavior (reviewed in Colborn et al., 1993, Söffker and Tyler, 2012). For example, the pharmaceutical androgen 17β-trenbolone is used as a growth promoter in beef cattle farming and it has been shown to masculinize female fish (Ankley et al., 2003). This occurs because it is found in the aquatic environment predominantly in runoff, feedlot surface soils and manure on animal farming facilities. Hence, characterizing the range and magnitude of effects of androgens on development and reproduction is crucial for understanding how EDCs perturb androgen receptor signaling in aquatic organisms.

In many teleost fishes, androgens have been shown to be involved in a broad range of biological functions, including reproduction, development, and behavior. Furthermore, androgens have also been shown to be involved in growth and osmoregulation in several teleost species (Sparks et al., 2003, Sangiao-Alvarellos et al., 2006). Recently, it has been suggested that androgens also have an important role in immune responses. For example, Àguila et al. (2013) discovered that two dominant androgens, testosterone and 11-ketotestosterone (11KT), are involved in regulating the response of professional phagocytes in gilthead seabream (Sparus aurata). In addition to modulation of the immune response, other androgen related functions based upon transcriptomics and proteomics data in fish include apoptosis, transport and oxidation of lipids, synthesis and transport of hormones, protein metabolism, and cell proliferation (Martyniuk and Denslow, 2012). Thus, androgens are involved in diverse functions in teleostean species.

The sex hormone testosterone is perhaps the most well studied androgen in vertebrate taxa and it has important functions in both male and female mammals (Konkle and McCarthy, 2011), birds (Goymann, 2009), amphibians (Eikenaar et al., 2012), reptiles (Eikenaar et al., 2012), and fish (Borg, 1994). Testosterone is a metabolic precursor for estrogens and other androgenic steroids such as 11KT, which has more potent androgenic characteristics in fish. Testosterone is not only involved in the development of male sexual characteristics but is also involved in the production of estrogens via aromatization, carbohydrate, fat and protein metabolism, and osmoregulation (Sangiao-Alvarellos et al., 2006, Kelly and Jones, 2013). Testosterone is synthesized from either androstenediol or androstenedione by 3β-HSD and 17β-HSD, respectively, and has several metabolic pathways involving a range of different enzymes as shown in Fig. 1.

In teleost fishes, 11KT is considered to be the predominant androgen and has been shown to stimulate secondary sexual characteristics, spermatogenesis, reproductive behavior as well as the masculinization of female genotypes to a higher degree than testosterone (reviewed in Borg, 1994). Testosterone is converted to 11β-hydroxytestosterone by the enzyme cytochrome P450 11β-hydroxylase (P45011β) and then converted to 11KT by the enzyme 11β-hydroxysteroid dehydrogenase (11βHSD). 11KT circulates in male teleost species at a higher plasma concentration than in their female counterparts and undergoes a seasonal cycle with the highest plasma concentration occurring during the pre-spawning season in some species (Borg, 1994). The abundance of 11KT in female plasma is generally not as high as testosterone, but in contrast to testosterone, the physiological actions of 11KT have not yet been fully described in female fishes (Lokman et al., 2002). Currently, most research with teleost fishes focuses on the biological functions of 11KT and testosterone; however other androgens with potentially important roles such as 5 alpha-dihydrotestosterone (DHT) have been understudied in fishes.

In mammals, birds, reptiles, and amphibians the most potent androgen is considered to be DHT. Although 11KT is considered the major androgen in teleost fishes, it has been demonstrated by Asahina et al. (1985) that in urohaze goby (Glossogobius olivaceus), the main product of testosterone conversion was DHT and not 11KT, suggesting that some teleost species could show unexpected patterns in androgen biosynthesis. DHT is produced from testosterone by an enzyme class called the 5 alpha-reductases (srd5a1, srd5a2, and srd5a3; reviewed in Langlois et al., 2010a). These enzymes were previously found to be active in the teleostean central nervous system, indicating the potential for localized conversion of testosterone into DHT in the brain (Callard et al., 1980). Recent exposure of fathead minnows (Pimephales promelas; FHMs) to DHT revealed that both DHT and 11KT can induce androgenic responses in fish (Margiotta-Casaluci and Sumpter, 2011), suggesting that DHT may also have important physiological roles in male and female fishes similar to 11KT.

To better clarify some of the potential roles of DHT in non-mammalian species we (1) generated a developmental profile of 5 alpha-reductase transcripts during early embryogenesis in the FHM; (2) investigated the distribution of the three srd5a isoforms in both male and female brain, liver, ovary, and testis; (3) reviewed studies that investigate the effects of DHT during fish and amphibian development; and (4) synthesized evidence to suggest that DHT can be a biologically active androgen in fish and amphibians.

Section snippets

Dihydrotestosterone and 5 alpha-reductase in early development

Androgens are present in early vertebrate development and have been detected in oocytes and in unfertilized and fertilized eggs. Testosterone is present in Japanese rice fish (Oryzias latipes) female fully grown oocytes (4–5 pg), then decreases in concentration in unfertilized eggs (2–3 pg) until after ∼1 d incubation (1–2 pg) (Iwamatsu et al., 2006a). After fertilization, testosterone concentration remains between 0.2 and 1.0 pg/animal (up to 10 dpf) which suggests roles for testosterone metabolites

Tissue distributions of DHT synthesizing enzymes in non-mammals

We were also interested in whether or not the srd5a isoforms showed tissue specific or sexually dimorphic expression patterns in reproductive female and male FHMs. A tissue distribution revealed that all three srd5a isoforms were expressed in the whole brain, liver, ovary, and testis of FHMs (Fig. 3). There were no differences in the mRNA levels of srd5a1, srd5a2, or srd5a3 between male and female whole brain (i.e., no sex difference in expression), however srd5a2 mRNA appeared to be expressed

New perspectives and next directions

Similar to other androgens, DHT can modulate reproductive endpoints in both fish and amphibians. However, predicting the effects of DHT can be challenging, as reproductive homeostasis is dependent upon the balance between estrogenic and androgenic hormones in addition to many other signaling molecules. We have summarized the documented effects of DHT in fish and frogs (Fig. 4) as an initial framework for uncovering the molecular mechanisms of action of DHT in aquatic vertebrates. In male fish,

Funding

This research was supported by NSERC Discovery Grants to C.J.M. and V.S.L., and a Canada Research Chair to C.J.M. The authors have no conflict of interest to declare.

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    A publisher’s error resulted in this article appearing in the wrong issue. The article is reprinted here for the reader’s convenience and for the continuity of the special issue. For citation purposes, please use the original publication details; General and Comparative Endocrinology, 194, pp. 264–274.

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