No abstract

Estrogen hormones interact with cellular ERs to exert their biological effects in vertebrate animals. Similar to other animals, fishes have two distinct ER subtypes, ERalpha (NR3A1) and ERbeta (NR3A2). The ERbeta subtype is found as two different isoforms in several fish species because of a gene duplication event. Although predicted, two different isoforms of ERalpha have not been demonstrated in any fish species. In the rainbow trout (Oncorhynchus mykiss), the only ER described is an isoform of the ERalpha subtype (i.e. ERalpha1, NR3A1a). The purpose of this study was to determine whether the gene for the other ERalpha isoform, ERalpha2 (i.e., NR3A1b), exists in the rainbow trout. A RT-PCR and cloning strategy, followed by screening a rainbow trout BAC library yielded a unique DNA sequence coding for 558 amino acids. The deduced amino acid sequence had a 75.4% overall similarity to ERalpha1. Both the rainbow trout ERbeta subtypes, ERbeta1 [NR3A2a] and ERbeta2, [NR3A2b] which were previously unknown in this species, were also sequenced as part of this study, and the amino acid sequences were found to be very different from the ERalphas (approximately 40% similarity). ERbeta1 and ERbeta2 had 594 and 604 amino acids, respectively, and had 57.6% sequence similarity when compared to one another. This information provides what we expect to be the first complete nuclear ER gene family in a fish. A comprehensive phylogenetic analysis with all other known fish ER gene sequences was undertaken to understand the evolution of fish ERs. The results show a single ERalpha subtype clade, with the closest relative to rainbow trout ERalpha2 being rainbow trout ERalpha1, suggesting a recent, unique duplication event to create these two isoforms. For the ERbeta subtype there are two distinct subclades, one represented by the ERbeta1 isoform and the other by the ERbeta2 isoform. The rainbow trout ERbeta1 and ERbeta2 are not closely associated with each other, but instead fall into their respective ERbeta subclades with other known fish species. Real-time RT-PCR was used to measure the mRNA levels of all four ER isoforms (ERalpha1, ERalpha2, ERbeta1, and ERbeta2) in stomach, spleen, heart, brain, pituitary, muscle, anterior kidney, posterior kidney, liver, gill, testis and ovary samples from rainbow trout. The mRNAs for each of the four ERs were detected in every tissue examined. The liver tended to have the highest ER mRNA levels along with the testes, while the lowest levels were generally found in the stomach or heart. The nuclear ERs have a significant and ubiquitous distribution in the rainbow trout providing the potential for complex interactions that involve the functioning of many organ systems.

The synthetic estrogen 17 alpha-ethynylestradiol (EE2) is a commonly used oral contraceptive that has been increasingly detected in sewage effluents. This study determined whether EE2 exposure adversely affected reproduction in sexually maturing male rainbow trout (Oncorhynchus mykiss). We exposed male trout to graded water concentrations of EE2 (10, 100, and 1,000 ng/ L) for 62 d leading up to the time of spawning. Semen and blood plasma samples were removed from each fish. Semen was used to fertilize groups of eggs from one nonexposed female. As a measure of fertility, eggs were incubated for 28 d after fertilization to determine the proportion that attained the eyed stage of embryonic development. Additional endpoints also measured included sperm motility, spermatocrit, gonadosomatic and hepatosomatic indices, testis histology, and circulating plasma levels of the sex steroids 17 alpha, 20 beta-dihydroxyprogesterone (17,20-DHP) and 11-ketotestosterone (11-KT). Exposure to 1,000 ng/L of EE2 caused complete mortality of the treatment group by day 57. Exposure to lower EE2 water concentrations (10 and 100 ng/L) caused an increase in sperm density, while a significant reduction in testis mass was observed only in the 100-ng/L exposure group. Most significantly, semen harvested from fish exposed to 10 and 100 ng/L EE2 caused an approximately 50% reduction in the number of eggs attaining the eyed stage of embryonic development. Plasma levels of 17,20-DHP in exposed fish were roughly twice the level of the controls, while levels of 11-KT were significantly reduced in fish exposed to 100 ng/L EE2. These results suggest that sexually maturing male rainbow trout are susceptible to detrimental reproductive effects of short-term exposures to environmentally relevant levels of EE2.

Sex is determined genetically in most fishes, but the gene responsible for sex determination is not known for the vast majority of fish species, including Chinook Salmon Oncorhynchus tshawytscha. The purpose of this study was to characterize a putative sex‐determining gene (“sexually dimorphic on the Y‐chromosome” [sdY] gene) in Chinook Salmon and develop a method to test genomic DNA (gDNA) samples for genetic sex assignment. Using next‐generation sequencing and salmonid DNA sequence data from GenBank, the entire genomic organization of Chinook Salmon sdY was described. The corresponding full‐length complementary DNA (cDNA) sequence generated from total RNA was determined by using a combination of genomic‐based primers and “rapid amplification of cDNA ends” (RACE) PCR assays. A phylogenic analysis was conducted by comparing the Chinook Salmon sdY cDNA sequence with sdY sequences (GenBank) from 10 other teleost species. A multisequence alignment was performed, and a phylogenetic tree was inferred from the alignment, providing evidence for sdY identity. Based upon a TaqMan real‐time PCR assay, a genetic test for male sex using sdY was developed and tested on gDNA isolated from phenotypic female and male Chinook Salmon representing populations in Alaska, Idaho, and Washington. The results provide compelling evidence that sdY is the sex‐determining gene in Chinook Salmon. We developed a reliable assay for sdY that can be used for genetic sex assignment in this species. However, discordance between phenotype and genotype was noted in 13 of 107 phenotypic female Chinook Salmon from Alaska and Washington. Several explanations for this discordance are discussed.Received January 14, 2014; accepted November 25, 2014

Numerous populations of anadromous salmonids in the northwestern United States have been declining for many years, resulting in Endangered Species Act listings and in some cases extinction. The degradation of river ecosystems has been proposed as one of the major reasons for the inability of salmon to maintain their populations. However, the specific factors interfering with the reproduction and survival of salmon during the freshwater phase of their life cycle have not been fully described. This study was initiated to determine the incidence of phenotypic sex reversal in wild, fall chinook salmon (Oncorhynchus tshawytcha) that returned to spawn in the Columbia River. Fish were sampled at different locations within this watershed to determine whether they were faithfully expressing their genotype. We report a high incidence (84%) of a genetic marker for the Y chromosome in phenotypic females sampled from the wild, which was not observed in female fish raised in hatcheries. It appears likely that female salmon with a male genotype have been sex reversed, creating the potential for an abnormal YY genotype in the wild that would produce all-male offspring and alter sex ratios significantly.

Estrogens are critical hormones involved in reproduction and need to bind to estrogen receptors in target organs for biological activity. Fishes have two distinct estrogen receptor subtypes, alpha (α) and beta (β), with variable combinations of additional isoforms of each subtype dependent on the history of genome duplication within a taxon. The comparative expression patterns of estrogen receptor isoforms during the female reproductive cycle will provide important insights into the unique function and importance of each. The purpose of this study was to measure the mRNAs for the four estrogen receptor isoforms (erα1, erα2, erβ1, erβ2) in the liver and ovary of adult, female rainbow trout over the course of an annual reproductive cycle. The expression of estrogen receptor mRNA isoforms was measured by quantitative real-time RT-PCR. Several reproductive indices (gonadosomatic index, maximum oocyte diameter, plasma estradiol-17β, plasma vitellogenin, and ovulation) were also quantified for comparison and used in a correlation analysis to examine any inter-relationships. Of the four isoforms, the expression of erα1 was highest in the liver, and had a significant positive correlation with liver erβ1 expression. Liver expression of erα2 mRNA was the lowest, but showed a significant positive correlation with maximum oocyte diameter in the ovary. The pattern of the erβ isoforms in liver was one of initially elevated mRNA expression followed by a gradual decrease as reproductive development proceeded. In the ovary the erβ1 isoform had the highest mRNA expression of all estrogen receptor isoforms, at the beginning of the reproductive cycle, but then decreased afterward. Both ovarian erβ isoforms had a significant positive correlation with one another. In contrast, erα2 mRNA expression showed a high maximum level in the ovary near the end of the cycle along with a significant positive correlation with plasma estradiol-17β levels; the highest gonadosomatic indices, maximum oocyte diameter, and vitellogenin levels occurred then too.

Exposure of fishes to environmental estrogens is known to affect sexual development and spawning, but little information exists regarding effects on gametes. This study evaluated embryonic survival of offspring from male rainbow trout (Oncorhynchus mykiss) exposed to 17a-ethynylestradiol (EE 2 ) using an in vitro fertilization protocol. Males were exposed at either 1800 or 6700 degree days (8d) (i.e. 161 or 587 days post-fertilization (dpf)) to test for effects on testes linked to reproductive ontogeny. At 18008d, fish were beginning testicular differentiation and were exposed to 109 ng EE 2 /l for 21 days. At 67008d, fish have testes containing spermatocytes and spermatids and were exposed for 56 days to either 0.8, 8.3, or 65 ng EE 2 /l. Semen was collected at full sexual maturity in each group and used to fertilize eggs pooled from several non-exposed females. Significant decreases in embryonic survival were observed only with the 67008d exposure. In 0.8 and 8.3 ng EE 2 /l treatments, embryo survival was significantly reduced at 19 dpf when compared with the control. In contrast, an immediate decrease in embryonic survival at 0.5 dpf was observed in the 65 ng EE 2 /l treatment. Blood samples collected at spawning from 67008d exposed males revealed a significant decrease in 11-ketotestosterone and a significant increase in luteinizing hormone levels for the 65 ng EE 2 /l treatment when compared with the other treatment groups. Results indicate that sexually maturing male rainbow trout are susceptible to EE 2 exposure with these fish exhibiting two possible mechanisms of reduced embryonic survival through sperm varying dependant on EE 2 exposure concentrations experienced.

A linear relationship exists between increasing levels of the indirect indicators serum total phosphoprotein phosphorus (TPP), alkali-labile phosphoprotein phosphorus (ALPP), and total calcium (Ca) and increasing levels of serum vitellogenin (Vg) in mature female rainbow trout (Salmo gairdneri) during active vitellogenesis. A similar result was observed with TPP, Ca, and Vg in immature rainbow trout injected with 17β-estradiol (E2). Although TPP, ALPP, and Ca could be utilized to distinguish vitellogenic from nonvitellogenic fish, the phosphoprotein phosphorus measures TPP and ALPP emerged as the most reliable indirect indicators of serum Vg levels. Linear regression equations developed from the data allow the estimation of Vg levels from TPP or Ca values for both highly vitellogenic mature female and E2-injected immature rainbow trout when a direct assay for vitellogenin is not available.