We examined effects of dietary methylmercury (MeH
g) onreproduction of fathead minnows (
Pimephales promelas).Juvenile fish were fed one of four diets until sexual maturity(phase 1): a control diet (0.06
ges/entities/m
gr.
gif">
g H
g g-1 dry wei
ght)and three diets contaminated with MeH
g at 0.88 (low),4.11 (medium), and 8.46
ges/entities/m
gr.
gif">
g H
g g-1 dry wei
ght (hi
gh). At sexualmaturity, male and female fish were paired, a
gain fedone of the four diets, and allowed to reproduce (phase 2).To assess effects of MeH
g durin
g gameto
genesis, somefish were fed diets durin
g phase 2 that differed from thosedurin
g phase 1. Spawnin
g success of pairs fed the samediet durin
g phases 1 and 2 was 75% for controls and 46%,50%, and 36% for the low-, medium-, and hi
gh-MeH
gtreatments, respectively. Spawnin
g success of pairs fed acontaminated diet durin
g phase 1 and a control dietdurin
g phase 2 was 63%, 40%, and 14% for the low-, medium-,and hi
gh-MeH
g treatments, respectively, whereasexposure to dietary MeH
g only durin
g phase 2 did notreduce spawnin
g success. Dietary MeH
g delayed spawnin
g,and days to spawnin
g was positively correlated withconcentration of total mercury in the carcasses of testfish. MeH
g reduced the instantaneous rate of reproductionof fish fed the same diets durin
g phases 1 and 2. Boththe
gonadosomatic index and reproductive effort of femalefish were inversely correlated with mercury in carcasses,whereas developmental and hatchin
g success ofembryos, 7-d survival, and 7-d
growth of larvae wereunrelated to mercury concentrations in parental fish ortheir diets. MeH
g decreased reproduction of adult fatheadminnows at dietary concentrations encountered bypredatory fishes in aquatic systems with MeH
g-contaminatedfood webs, implyin
g that exposed fish populations couldbe adversely affected by this widespread contaminant.