TY - JOUR
T1 - Effects of dietary exposure to the pyrethroid pesticide esfenvalerate on medaka (Oryzias latipes)
AU - Werner, Ingeborg
AU - Geist, Juergen
AU - Okihiro, Mark
AU - Rosenkranz, Philipp
AU - Hinton, David E.
N1 - Funding Information:
We much appreciate the assistance of Michelle Hornberger and Dan Cain, USGS Menlo Park, CA, in collecting clams, and of Guomin Shan, UC Davis, in chemical analyses. Funding was provided, in part, by EPA contract R826940–01–1.
PY - 2002/9
Y1 - 2002/9
N2 - The pyrethroid insecticide esfenvalerate is widely used on orchard crops throughout California. In the aquatic environment, this compound is likely to accumulate in sediments, food particles and benthic organisms due to its lipophilicity and environmental persistence. This pilot project tested the hypothesis that esfenvalerate is toxic to medaka (Oryzias latipes) when taken up with the diet. For 7 days fish were fed diets, which contained esfenvalerate in three different concentrations (4, 21, 148 mg/kg, measured). Endpoints measured were mortality, fecundity, fertilization and hatching success of embryos, viability of larvae and cellular stress protein (hsp60, hsp70, hsp90) levels. The toxicity of aqueous exposure of medaka to esfenvalerate was also determined. Whereas the 96-h LC50 in the aqueous exposure was <9.4 μg/l, the dietary exposure did not cause mortality. Possible effects of dietary esfenvalerate were seen on fertilization and hatching success and the number of non-viable larvae. Expression of hsp60 and hsp90 showed a dose-dependent response pattern.
AB - The pyrethroid insecticide esfenvalerate is widely used on orchard crops throughout California. In the aquatic environment, this compound is likely to accumulate in sediments, food particles and benthic organisms due to its lipophilicity and environmental persistence. This pilot project tested the hypothesis that esfenvalerate is toxic to medaka (Oryzias latipes) when taken up with the diet. For 7 days fish were fed diets, which contained esfenvalerate in three different concentrations (4, 21, 148 mg/kg, measured). Endpoints measured were mortality, fecundity, fertilization and hatching success of embryos, viability of larvae and cellular stress protein (hsp60, hsp70, hsp90) levels. The toxicity of aqueous exposure of medaka to esfenvalerate was also determined. Whereas the 96-h LC50 in the aqueous exposure was <9.4 μg/l, the dietary exposure did not cause mortality. Possible effects of dietary esfenvalerate were seen on fertilization and hatching success and the number of non-viable larvae. Expression of hsp60 and hsp90 showed a dose-dependent response pattern.
KW - Dietary exposure
KW - Esfenvalerate
KW - Medaka
KW - Pyrethroid pesticides
KW - Reproductive toxicity
KW - Stress proteins
UR - http://www.scopus.com/inward/record.url?scp=0036753398&partnerID=8YFLogxK
U2 - 10.1016/S0141-1136(02)00151-4
DO - 10.1016/S0141-1136(02)00151-4
M3 - Article
C2 - 12408625
AN - SCOPUS:0036753398
SN - 0141-1136
VL - 54
SP - 609
EP - 614
JO - Marine Environmental Research
JF - Marine Environmental Research
IS - 3-5
ER -