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J L Parrott

Publications and source records attributed to J L Parrott.

2 recordsLinked to original sources

Isolation of MFO inducers from tissues of white suckers caged in bleached kraft mill effluent.

White sucker (Catostomus commersoni) caged for 3 days in a bleached kraft mill effluent (BKME) stream had elevated mixed function oxygenase (MFO) activities 15-90 fold those of fish caged in a reference stream. Liver composites of male and female fish were ground and extracted with dichloromethane (DCM), methanol or 50% DCM/methanol, and tested for MFO activity in rat hepatoma cells (H4IIE). There was no difference in the potency of H4IIE EROD induction among the three solvents, so DCM extracts were split into 31 fractions using reverse phase high pressure liquid chromatography (HPLC). H4IIE MFO activity was elevated in several fractions, with three early peaks and several later peaks of induction, indicating several classes or compounds causing MFO induction were present in the fish livers. Polychlorinated dibenzo-p-dioxins (PCDDs), polychlorinated dibenzofurans (PCDFs) and chlorinated diphenylethers (CDPEs) were detected in several late-eluting fractions, but concentrations were not high enough for these compounds to be solely responsible for the observed induction. Induction by liver extracts decreased as cell exposure times increased (24, 48 or 72 h), suggesting that some inducers were more easily metabolized and eliminated from the H4IIE cells. In contrast, 2,3,7,8-tetrachlorodibenzo-p-dioxin (2378-TCDD) had similar potency over 24, 48 and 72 h, as it was relatively resistant to metabolism.

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Rainbow trout hepatic mixed-function oxygenase induction by polychlorinated dibenzo-p-dioxins (PCDDs) as a function of time and tissue concentration.

Rainbow trout, dosed orally with 0.060-84 micrograms/kg of [3H]-2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), [14C]-1,2,3,4,7,8-hexachlorodibenzo-p-dioxin (HxCDD), or [14C]-1,2,3,4,6,7,8-heptachlorodibenzo-p-dioxin (HpCDD) showed dose-dependent increases in hepatic ethoxyresorufin O-deethylase (EROD) activity, up to 250-fold, after 2-16 d. Induction of EROD activity was a sensitive and rapid indicator of exposure to PCDDs. The effects of time after exposure were not dramatic, but generally EROD activity after 2 d was lower than EROD activity after 16 d. Slopes of dose-response curves relating EROD activity to hepatic concentrations of PCDDs significantly decreased and intercepts significantly increased with increasing time of exposure. When fish were grouped by oral doses, only the low doses of TCDD and HpCDD exhibited time-dependent EROD induction, with significantly greater activity 16 d after dosing compared to 2 d. In most cases, hepatic and muscle concentrations of PCDDs did not significantly change over time. Concentrations of PCDDs in liver and muscle accounted for up to 7% of the orally administered dose. Hepatic levels of PCDDs ranged from 20-100 pg/g at the lowest doses to about 1000 pg TCDD/g, 2000 pg HxCDD/g, or 40,000 pg HpCDD/g at the highest doses. Of the PCDD in the liver, approximately one-third to one-half was associated with the postmitochondrial supernatant (PMS). PCDD concentrations in muscle did not span as wide a range of concentrations as did PCDD in liver; fish given low doses had 10 pg/g in muscle whereas fish given high doses had several hundred picograms per gram in muscle for all three PCDDs.

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