Impact of polychlorinated naphthalenes (PCNs) in juvenile Baltic salmon, Salmo salar: Evaluation of estrogenic effects, development, and CYP1A induction
N. Akerblom et al., Impact of polychlorinated naphthalenes (PCNs) in juvenile Baltic salmon, Salmo salar: Evaluation of estrogenic effects, development, and CYP1A induction, ARCH ENV C, 38(2), 2000, pp. 225-233
Citations number
46
Categorie Soggetti
Environment/Ecology,"Pharmacology & Toxicology
Journal title
ARCHIVES OF ENVIRONMENTAL CONTAMINATION AND TOXICOLOGY
Juvenile Baltic salmon, Salmo saint; were fed commercial salmon food contam
inated with different concentrations of polychlorinated naphthalenes (PCNs;
0.1, 1, 2, or 10 mu g PCN/g food). Among other effects, possible estrogeni
c impact caused by PCNs were evaluated. Fish were therefore fed a diet cont
aminated with 17 beta-estradiol (E2; 0.94 or 9.4 mu g E2/g food), as a posi
tive control. After 8, 13, 17, and 41 weeks, sampling took place. Growth, L
iver somatic index (LSI), EROD activity, and vitellogenin content in blood
plasma were measured along with morphological studies of gonads and chemica
l analyses to determine the effects caused by PCNs. Exposure to PCNs did no
t seem to have any effects on body weight gain, since the group fed the hig
h dose followed the growth in the control group during the entirely experim
ental period. After 41 weeks of exposure the groups fed 2 and 10 mu g PCN/g
food had significantly lower LSIs compared with the control, indicating li
ver toxic effects of PCNs. Furthermore, a dose-dependent induction of EROD
activity was found. At week 41, the control group had an activity of 4.9 +/
- 4.8 pmol/mg prot/min, whereas it was between 69 +/- 21 and 720 +/- 320 pm
ol/mg prot/min in the exposed groups, respectively. Examination of gonadal
morphology showed that PCNs also had negative effects on ovaries in Baltic
salmon, including delayed development. The distribution between females and
males, gonadal morphology, and vitellogenin content in blood plasma did, h
owever, indicate that PCNs are not capable of causing effects similar to E2
or xenoestrogens. Exposure to both of the concentrations of E2 resulted in
decreased body weight gain, increased LSI, and feminization of the gonads.
E2 did, however, not induce any EROD activity.