The detection of biomarkers of genotoxin exposure in the European flounder (Platichthys flesus) collected from the River Tyne Estuary.
The Tyne Estuary (North East England) is known to contain elevated levels of polycyclic aromatic hydrocarbons (PAH), compared with other less industrialised English waterways. Previous studies suggest that such contamination is responsible for the toxicity detected in invertebrate bioassays conducted on water and sediment samples collected from the Tyne. Here we present data from a biomonitoring study using hepatic DNA adducts (32P-postlabelling assay) and bile metabolites (synchronous fluorescence spectrometry) to investigate genotoxic exposure in flounder (Platichthys flesus) collected from three sites (Scotswood, Newcastle and Redheugh) along the Tyne Estuary. Flounder were also collected from a clean reference site, the Alde Estuary. Levels of bile metabolites (microgram kg-1 wet weight 1-OH pyrene equivalents) were elevated in flounder caught from the Tyne (Scotswood = 22,247 +/- 3408; Newcastle = 14,572 +/- 1888; Redheugh = 21,872 +/- 2935) compared with those collected from the Alde (632 +/- 56). The levels of DNA adducts (adducted nucleotides per 10(8) normal nucleotides) were also elevated in Tyne flounder (Scotswood = 24.6 +/- 3.2; Newcastle = 34.4 +/- 3.7; Redheugh = 27.6 +/- 6.3) compared with fish collected from the Alde (10.1 +/- 4.8), suggesting that a proportion of the bioavailable PAH was being converted into genotoxic metabolites. All DNA adduct profiles in flounder collected from the Tyne consisted of diagonal radioactive zones of radiolabelled adducts, which were not present in fish sampled from the Alde. The in vivo dosing of flounder with benzo[a]pyrene (BaP) to produced DNA adducts in similar chromatographic positions to the diagonal radioactive zones in the Tyne caught flounder are also described.
Lyons
B P
BP
Centre for Environment Fisheries and Aquaculture Sciences (CEFAS), Lowestoft Laboratory, Suffolk, UK. b.p.lyons@cefas.co.uk
Stewart
C
C
Kirby
M F
MF
D000818:Animals; D001564:Benzo(a)pyrene / Q000633:toxicity; D001646:Bile / Q000737:chemistry / Q000378:metabolism; D018736:DNA Adducts / Q000032:analysis* / Q000187:drug effects; D004781:Environmental Exposure / Q000032:analysis*; D004784:Environmental Monitoring / Q000379:methods; D005432:Flounder / Q000235:genetics* / Q000378:metabolism; D005618:Fresh Water; D005819:Genetic Markers; D008099:Liver / Q000737:chemistry / Q000187:drug effects / Q000378:metabolism; D009153:Mutagens / Q000378:metabolism / Q000633:toxicity*; D010761:Phosphorus Radioisotopes; D013050:Spectrometry, Fluorescence; D006113:United Kingdom; D014874:Water Pollutants, Chemical / Q000378:metabolism / Q000633:toxicity*
D018736:DNA Adducts; D005819:Genetic Markers; D009153:Mutagens; D010761:Phosphorus Radioisotopes; D014874:Water Pollutants, Chemical; D001564:Benzo(a)pyrene