Effects of terbuthylazine on early life stages of common carp
Language English Country Sweden Media print
Document type Journal Article, Research Support, Non-U.S. Gov't
PubMed
26757117
PII: NEL360915A21
Knihovny.cz E-resources
- MeSH
- Water Pollutants, Chemical toxicity MeSH
- Embryo, Nonmammalian drug effects MeSH
- Carps embryology MeSH
- Kidney drug effects embryology MeSH
- Pesticides toxicity MeSH
- Toxicity Tests, Chronic MeSH
- Triazines toxicity MeSH
- Animals MeSH
- Zygote drug effects MeSH
- Check Tag
- Animals MeSH
- Publication type
- Journal Article MeSH
- Research Support, Non-U.S. Gov't MeSH
- Names of Substances
- Water Pollutants, Chemical MeSH
- Pesticides MeSH
- terbutylazine MeSH Browser
- Triazines MeSH
OBJECTIVES: The aim of this study was to assess the toxicity of terbuthylazine in different developmental stages of common carp (Cyprinus carpio) on the basis of mortality, early ontogeny, occurrence of morphological anomalies, growth rate, and Fulton's condition factor during and at the conclusion of the test. DESIGN: The toxicity tests were performed on carp according to OECD 210 methodology. The developmental stages of carp were exposed to terbuthylazine at four concentrations, 2.9 (reported environmental concentration in Czech rivers); 70; 1,400; and 3,500 µg.L(-1) for 35 days and compared to carps in a non-treated control group. RESULTS: Terbuthylazine in concentration 1,400 and 3,000 µg.L(-1) caused significant (p<0.01) decrease of mass, total length and delayed in development of carp. Fish exposed to terbuthylazine showed alteration of tubular system of caudal kidney. On the basis of histopathological changes the values of LOEC=2.9 µg.L(-1) terbuthylazine were estimated. CONCLUSIONS: Chronic terbuthylazine exposure of early-life stages of common carp affected their growth rate, early ontogeny and histology. Some of the changes were observed only at higher exposures, but change founded in caudal kidney was affected in fish exposed to the real environmental concentration tested (i.e., 2.9 µg.L(-1)).