Abstract

Environmental estrogens are ubiquitous in the environment and can cause detrimental effects on male reproduction. In fish, a multitude of effects from environmental estrogens have been observed including altered courting behavior and fertility, sex reversal, and gonadal histopathology. However, few studies in fish assess the impacts of estrogenic exposure on a physiological endpoint, such as reproduction, as well as the associated morphologic response and underlying global gene expression changes. This study assessed the implications of a 14 day sub-chronic exposure of ethinylestradiol (EE2; 1.0 or 10.0 µg/L EE2) on male medaka fertility, testicular histology and testicular gene expression. The findings demonstrate that a 14 day exposure to EE2 induced impaired male reproductive capacity and time- and dose-dependent alterations in testicular morphology and gene expression. The average fertilization rate/day following the exposure for control, 1.0 and 10.0 µg/L EE2 was 91.3% (±4.4), 62.8% (±8.3) and 28.8% (±5.8), respectively. The testicular morphologic alterations included increased germ cell apoptosis, decreased germinal epithelium and thickening of the interstitium. These changes were highly associated with testicular gene expression changes using a medaka-specific microarray. A pathway analysis of the differentially expressed genes emphasized genes and pathways associated with apoptosis, cell cycle and proliferation, collagen production/extracellular matrix organization, hormone signaling, male reproduction and protein ubiquitination among others. These findings highlight the importance of anchoring global gonadal gene expression changes with morphology and ultimately with tissue/organ function.

Highlights

  • Endocrine disrupting chemicals (EDCs) impair reproductive function in diverse wildlife populations [1,2]

  • In male fish exposed to estrogenic EDCs, gene expression is altered and reproductive physiology and morphology are subsequently impacted as evidenced by: synthesis of the yolk protein, vitellogenin; altered spermatogenesis; testicular fibrosis; development of testicular oocytes; decreased sperm counts and eventually reduced fertility [7,10,11,12,13]

  • Males were exposed to dimethyl sulfoxide (DMSO), 1.0 mg/L EE2 or 10.0 mg/L EE2 for 14 days

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Summary

Introduction

Endocrine disrupting chemicals (EDCs) impair reproductive function in diverse wildlife populations [1,2]. Multiple wild fish populations with altered gonads, in particular testicular oocytes, have been observed around the world including: roach (Rutilus rutilus), gudgeon (Gobio gobio) and flounder (Platichthys flesus) from rivers in the United Kingdom, barbel (Barbus plebejus) from Italy, grey mullet (Mugil cephalus) in coastal waters of Japan and Korea, shovelnose sturgeon (Scaphirhynchus platyornchus) from the Mississippi River and bass species from rivers within the United States [3,4,5,6,7,8,9] Many of these gonadal alterations have been attributed to EDC exposures, which are often associated with agricultural practices and municipal effluents. There was a collapse of the fathead minnow population after the second year due to loss of young-of-the-year individuals [19]

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