LOW INDUCIBILITY OF CYP1A ACTIVITY BY POLYCHLORINATED-BIPHENYLS (PCBS) IN FLOUNDER (PLATICHTHYS-FLESUS) - CHARACTERIZATION OF THE AH RECEPTOR AND THE ROLE OF CYP1A INHIBITION
Ht. Besselink et al., LOW INDUCIBILITY OF CYP1A ACTIVITY BY POLYCHLORINATED-BIPHENYLS (PCBS) IN FLOUNDER (PLATICHTHYS-FLESUS) - CHARACTERIZATION OF THE AH RECEPTOR AND THE ROLE OF CYP1A INHIBITION, TOXICOLOGICAL SCIENCES, 43(2), 1998, pp. 161-171
Several studies have reported a low inducibility of hepatic cytochrome
P4501A (CYP1A) activity in European flounder (Platichthys flesus) fol
lowing exposure to mixtures of polychlorinated biphenyls (PCBs). Here
we report on mechanistic studies toward understanding this low CYP1A i
nducibility of flounder, involving molecular characterization of the A
h receptor (AhR) pathway as well as inhibition of the CYP1A catalytic
activity by PCB congeners, Hepatic cytosolic AhR levels in flounder we
re determined using hydroxylapatite, protamine sulfate adsorption anal
ysis, or velocity sedimentation on sucrose gradients. AhR levels in fl
ounder (similar to 2-7 fmol/mg protein) were much lower than observed
generally in rodents (similar to 50-300 fmol/mg protein). Molecular ch
aracterization of the flounder AhR was provided by first-strand cDNA s
ynthesis and amplification of flounder hepatic poly(A)(+) RNA using RT
-PCR. A 690-bp product was found, similar in size to a Fundulus AhR cD
NA, The specificity of the 690-bp band was established by Southern blo
tting and hybridization with a degenerate AhR oligonucleotide. The ded
uced amino acid sequence of the flounder AhR fragment was 59-60% ident
ical to mammalian AhR sequences. Although the AhR is present in flound
er cytosol, we were unable to demonstrate detectable amounts of induci
ble TCDD-AhR-DRE complex in gel-retardation assays. High induction lev
els of CYP1A protein and associated EROD activity have been previously
found in flounder following exposure to 2,3,7,8-tetrachlorodibenzo-p-
dioxin (TCDD). In contrast, the induction of CYP1A catalytic activity
by PCB mixtures remains unexpectedly low. Therefore, we further charac
terized the inhibitory potential of PCB congeners on CYP1A activity in
flounder and compared this with inhibitory effects of PCB congeners o
n rat CYP1A activity. Analysis in vitro demonstrated that 3,3',4,4'-te
traCB, 3,3',4,4',5-pentaCB, 2,2',4,4',5,5'-hexaCB, 3,3',4,4',5,5'-hexa
CB, and the commercial PCB mixture Clophen A50 are potent competitive
inhibitors of hepatic microsomal CYP1A catalytic activity in flounder
and rat. The K-m for ethoxyresorufin (0.095 mu M) in flounder is strik
ingly close to K-i's found for the tested PCBs. This emphasizes the po
ssible involvement of PCB congeners in inhibition of EROD activity in
PHAH exposed fish. Finally, our data indicate that flounder CYP1A is m
ore efficient in metabolizing ethoxyresorufin than that of rat CYP1A.
(C) 1998 Society of Toxicology.