Elevation of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) polychlorinated biphenyls. Structure-activity relationships.

Administration of the commercial polychlorinated biphenyl (PCB) Aroclor 1254 to immature male Wistar rats resulted in increased levels (80-110%) of the 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) hepatic cytosolic receptor protein which remained elevated for 14 days. The effects of structure on the activity of individual PCB congeners to modulate hepatic cytosolic receptor levels were compared to the structure-activity relationships (SARs) which have been developed previously for PCBs as inducers of hepatic microsomal monooxygenases. 3,3',4,4'-Tetra- and 3,3',4,4',5-pentachlorobiphenyl induced the cytochrome P-448-dependent monooxygenase, ethoxyresorufin O-deethylase (EROD), and resembled 3-methylcholanthrene in their mode of monooxygenase enzyme induction. These congeners also bound to the receptor protein; however, neither compound increased hepatic cytosolic receptor protein levels. Several PCB congeners which exhibit low binding affinities for the cytosolic receptor protein resembled phenobarbitone (PB) in their mode of monooxygenase enzyme induction and, like PB, elevated cytosolic receptor protein levels. Nevertheless, a comparison of the time course of monooxygenase enzyme induction and receptor protein elevation by 2,2',4,4',5,5'-hexachlorobiphenyl and PB illustrated significant differences in their activities. PB-mediated elevation of receptor levels was maximized 24 hr after the last dose, and 48 hr later the receptor levels decreased to control values. In contrast, 5 days after administration of a single dose of 2,2',4,4',5,5'-hexachlorobiphenyl (300 mumoles/kg) the receptor levels were elevated significantly, and these increased levels (205-127% increases over control) persisted for 14 days. There was no correlation between increased levels of hepatic receptor protein and the induction of the cytochrome P-450-dependent monooxygenases, aldrin epoxidase or 4-dimethylaminoantipyrine N-demethylase. Two PCBs, 2,3,3',4,4',5- and 2,2',3,4,4',5-hexachlorobiphenyl, which resembled Aroclor 1254 in their mode of monooxygenase enzyme induction, also elevated hepatic receptor protein levels but were less active than the PB-type inducers. Thus, the SARs developed for PCBs which elevate cytosolic receptor levels demonstrate that the most active compounds exhibit the lowest affinity for the receptor protein and do not induce EROD. In contrast, the more toxic PCB congeners which are approximate isostereomers of 2,3,7,8-TCDD both induced EROD and bound with high affinity to the receptor protein but did not increase hepatic cytosolic receptor protein levels.

Polychlorinated biphenyls as phenobarbitone-type inducers of microsomal enzymes. Structure-activity relationships for a series of 2,4-dichloro-substituted congeners.

Several polychlorinated biphenyl (PCB) isomers and congeners resemble phenobarbitone (PB) in their mode of induction of the hepatic drug-metabolizing enzymes; however, unlike PCBs which induce aryl hydrocarbon hydroxylase, no apparent structure-activity correlations have been reported. This study examines the effects of structure on the activity of a series of 2,4-dichloro-substituted biphenyls as inducers of several microsomal enzyme activities including dimethylaminoantipyrine N-demethylase, benzo[a]pyrene hydroxylase, aldrin epoxidase, and ethoxyresorufin O-deethylase. The results clearly illustrate a marked effect of structure on activity: all of the 2,4-dichloro-substituted PCBs resembled PB in their mode of induction. However, the potency of the induction response was dependent on the substitution pattern of the second phenyl ring (i.e. 2,3,4,5-tetrachloro greater than or equal to 2,3,4,5,6-pentachloro greater than 2,3,4,6-tetrachloro greater than 2,3,5,6-tetrachloro greater than 2,4,6-trichloro); the structure of the lower chlorinated ring also determined induction potency since the 2,4-dichloro-substituted PCBs were generally more active than their 4-chloro-substituted analogs, whereas the 2-substituted PCB homologs were inactive. The structural factors which typify the most active PB-type inducer, 2,2',3,4,4',5-hexachlorobiphenyl, include the presence of two para-, at least two meta- and two ortho-chloro substituents. In addition to the structure-activity correlations noted for PCBs, the 2,2',3,4,4',5-hexachlorobiphenyl congener also elicited a dose-response induction of two PB-inducible enzymes, aldrin epoxidase and dimethylaminoantipyrine N-demethylase.

Effects of structure on binding to the 2,3,7,8-TCDD receptor protein and AHH induction--halogenated biphenyls.

The quantitative structure-activity relationships (QSARs) for polychlorinated biphenyl (PCB) congeners have been determined by comparing the EC50 values for three in vitro test systems, namely, aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) induction in rat hepatoma H-4-II-E cells and competitive binding avidities to the rat cytosolic receptor protein (using 2,3,7,8-tetrachlorodibenzo-p-dioxin as a radioligand). For several PCB congeners that are in vivo inducers of rat hepatic microsomal AHH, there was a linear correlation between the -log EC50 values for receptor and the -log EC50 values for AHH (or EROD) induction; moreover, a comparable linear relationship was observed between the -log EC50 values for AHH and EROD induction. Previous in vivo studies have shown that the most active PCB congeners 3,3',4,4'-tetra-, 3,4,4',5-tetra-, 3,3',4,4',5-penta-, and 3,3',4,4',5,5'-hexachlorobiphenyl, cause many of the biologic and toxic effects reported for the highly toxic halogenated aryl hydrocarbon, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Moreover, the monoortho-substituted homologs of the four coplanar PCBs also elicit comparable in vivo biologic and toxic responses. It was evident from the QSARs for PCBs that there was an excellent correspondence between the in vivo and in vitro potencies of the individual PCB congeners. The effects of substituents on both receptor binding and AHH/EROD induction was determined for a series of 4'-substituted (X)-2,3,4,5-tetrachlorobiphenyls (where X = H, Cl, Br, I, OH, OCH3, NO2, COCH3, F, CF3, CH3, C2H5, i-C3H7, n-C4H9 and t-C4H9). Not unexpectedly, there was a linear relationship between the -log EC50 values for AHH and EROD induction, and these results confirm that both enzymatic oxidations are catalyzed by the same cytochrome P-450 isozyme(s). The effects of substituent structure on receptor binding for 12 substituents was subjected to multiple regression analysis which correlates the relative binding affinities of the compounds with the physical chemical characteristics of the substituents. The analysis gave the following equation: log (1/EC50) = 1.53 sigma + 1.47 pi + 1.09 HB + 4.08 for n = 12, s = 0.18, r = 0.978; where n is the number of substituents, s is the standard deviation, r is the correlation coefficient, and sigma = electronegativity, pi = hydrophobicity (log P) and HB = hydrogen bonding capacity for the substituent groups.(ABSTRACT TRUNCATED AT 400 WORDS)

Polybrominated dibenzo-p-dioxins and related compounds: quantitative in vivo and in vitro structure-activity relationships.

The effects of structure on the in vitro receptor binding affinities, aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) induction potencies in rat hepatoma cells were determined for the following compounds: 2-bromo-, 2,7/2,8-dibromo-, 2,3,7-tribromo-, 2,4,6,8/1,3,7,9-tetrabromo-, 2,3,7,8-tetrabromo-, 1,3,7,8-tetrabromo-, 1,2,3,7,8-pentabromo-, 1,2,4,7,8-pentabromo-, 2,3-dibromo-7,8-dichloro-, 2,8-dibromo-3,7-dichloro- and 2-bromo-3,7,8-trichlorodibenzo-p-dioxin. The structure-activity relationships (SARs) for the polybrominated dibenzo-p-dioxins (PBDDs) were comparable for both in vitro responses: the most active compounds were substituted only in the lateral 2,3,7 and 8 position and the addition of non-lateral or removal of lateral halogen substituents reduced the activity of the resultant compound. The biologic and toxic effects of 2,3,7,8-tetrabromo-, 1,3,7,8-tetrabromo-, 1,2,4,7,8-pentabromo-1,2,3,7,8-pentabromo-, 2-bromo-3,7,8-trichloro- and 2,3-dibromo-7,8-dichlorodibenzo-p-dioxin on several receptor-mediated responses (thymic atrophy, body weight loss, hepatic microsomal AHH and EROD induction) were determined in a dose-response fashion in immature male Wistar rats. A comparison of the ED50 values for the in vivo responses demonstrated that the SARs for the PBDDs and brominated polychlorinated dibenzo-p-dioxins were comparable to those observed for in vitro receptor binding and AHH induction. Moreover, there was an excellent linear correlation between the -log EC50 (in vitro AHH induction) vs. the in vivo -log ED50 (thymic atrophy) and -log ED50 (body wt loss) correlation coefficient, r = 0.97 for all 2 correlations).

Substituted polychlorinated dibenzofuran receptor binding affinities and aryl hydrocarbon hydroxylase induction potencies--a QSAR analysis.

The rat hepatic cytosolic receptor binding affinities of 8-substituted 2,3-dichlorodibenzofurans and 8-substituted 2,3,4-trichlorodibenzofurans have been measured. The EC50-value for each compound was determined by dose-response competitive displacement of 2,3,7,8-[3H] tetrachlorodibenzo-p-dioxin (TCDD). Multiple parameter linear regression analysis of the data using several substituent parameters [lipophilicity (pi), hydrogen bonding (HB), electronegativity (sigma op), STERIMOL (delta B5)] demonstrated that for both sets of ligands, the binding affinities were dependent on substituent pi-values. The equations derived for the 8-substituted 2,3,4-trichlorodibenzofurans (a) and 8-substituted 2,3-dichlorodibenzofurans (b) were (Formula: see text) remarkably similar, moreover the relatively bulky t-butyl substituent was treated as an outlier for both calculations. The in vitro induction of aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) in rat hepatoma H-4-II E cells by both sets of ligands demonstrated that there was not a rank order correlation between induction potencies and receptor binding affinities for these compounds. Analysis of the data for the 8-substituted 2,3-dichlorodibenofurans demonstrated that the monooxygenase enzyme induction was dependent on substituent lipophilicity and a STERIMOL (delta B5) factor which is related to (Formula: see text) substituent width. In contrast, the equation for the 8-substituted 2,3,4-trichlorodibenzofurans also included a substituent sigma op Hammett constant. The results indicate that although the binding affinities of the two sets of ligands are dependent only on substituent pi-values, their enzyme induction activities are both substituent and chlorine substitution pattern-dependent.

Pyrethroid insecticide residues on vegetable crops.

Pyrethroid insecticides were applied on various vegetable crops as foliar treatments to determine dissipation rates. On Chinese broccoli (Guy Lon), Chinese mustard (Pak Choi) and Chinese cabbage (Kasumi, napa), fenvalerate was persistent with residues of 0.10, 0.14 and 0.11 mg kg-1, respectively, by day 21. Cypermethrin residues on head lettuce were below 0.1 mg kg-1 by day 10 but on the leafier romaine and endive varieties it was more persistent and required 14-19 days to dissipate below this concentration. After three applications, residues of cypermethrin in harvested carrots and of permethrin in eggplant were not detected on the day of application. On asparagus, deltamethrin and cypermethrin residues declined to less than 0.1 mg kg-1 by days 1 and 2, respectively; permethrin was more persistent, requiring more than 2 days to decline to less than 0.1 mg kg-1. Deltamethrin on dry (cooking) and Spanish onions was not detected on the day of application. On tomatoes, the concentration of permethrin was 0.093 mg kg-1 on the day of application and declined to about 0.05 mg kg-1 after 2-4 days. In general, permethrin, cypermethrin and deltamethrin residues declined to acceptable concentrations within an acceptable pre-harvest interval. Fenvalerate may be too persistent on these speciality crops unless a maximum residue limit > 0.1 mg kg-1 is permitted.

Pesticide residues on fruits and vegetables from Ontario, Canada, 1991-1995.

For the 5-year period 1991 to 1995, 1536 vegetable and 802 fruit samples were analyzed. The purpose of this study was to determine if pesticides were present on Ontario-produced fruits and vegetables, and if so, to determine if residues violated maximum residue limits (MRLs). Overall, 31.5% of the samples had no detectable pesticide residues, whereas 68.5% contained one or more residues. Most of the residues were present at very low concentrations; 48% of the detections were < 0.1 parts per million (ppm), and 86% were < 1 ppm. However, violations of MRL were observed in only 3.2% of the vegetables samples and 3.1% of the fruit samples. In addition, 4.8% of the samples contained a "technical" violation, that is, there was no specified MRL for the pesticide-commodity combination and the residues exceeded 0.1 ppm. Of the detectable residues, 63% were < 10% of the MRL, whereas 89% were < 50% of the MRL. More fruit samples (91.4%) had a detectable residue, compared with vegetable samples (56.6%). Fruit is often treated close to harvest or post harvest to ensure that wholesome produce reaches the consumer. Forty-six percent of the samples contained 2 or more residues, and 2% of all samples had more than 5 different pesticides detected; fruit samples tended to have more multiple residues. The most frequently found pesticides were captan, the dithiocarbamate fungicides, endosulfan, azinphos-methyl, phosmet, parathion, and iprodione. These pesticides were also used in the greatest quantity for crop production. Overall, the data agree fairly closely with those reported for the U.S. Department of Agriculture Pesticide Data Program because the 2 programs have similar analytical goals and objectives.

Nonadditive interactive effects of polychlorinated biphenyl congeners in rats: role of the 2,3,7,8-tetrachlorodibenzo-p-dioxin receptor.

Administration of 3,3',4,4',5,5'-hexa-,3,3',4,4',5-penta-, and 2,3,3'4,4'5-hexa-chlorobiphenyl to immature male Wistar rats caused a thymic atrophy at high dose levels (1.25, 1.0, and 100 mumol/kg, respectively) and induced the hepatic cytochrome P-448 dependent monooxygenases (benzo[a]pyrene hydroxylase and ethoxyresorufin O-deethylase) at both high and low (0.25, 0.01, and 5 mumol/kg, respectively) doses. In contrast, 2,2',4,4',5,5'-hexachlorobiphenyl (HCBP) (300 mumol/kg) did not elicit any of these effects but elevated hepatic 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) cytosolic receptor protein levels (threefold) as previously reported. The effects of hepatic receptor modulation by 2,2',4,4',5,5'-HCBP (300 mumol/kg) on the enzyme induction activities of 3,3'4,4',5-penta-, 3,3'4,4',5,5'-hexa-, and 2,3,3',4,4',5-hexa-chlorobiphenyl were dose-dependent; no interactive effects were observed at high (toxic) doses of these compounds, whereas apparent synergistically increased hepatic microsomal monooxygenase induction activities were noted at the lower submaximal induction doses. It was concluded that the increased responsiveness of the rats was due to elevated hepatic 2,3,7,8-TCDD receptor levels.

Polychlorinated benzene and phenol congeners as inducers of rat hepatic drug-metabolizing enzymes in immature male Wistar rats.

The effects of the higher chlorinated benzene and phenol congeners as inducers of the hepatic microsomal drug-metabolizing enzymes have been determined in the immature male Wistar rat by comparing the enzymic, electrophoretic, and spectral properties of the microsomes. 3,4,5-Trichlorophenol, 1,2,4,5-tetrachlorobenzene, 1,2,3,5-tetrachlorobenzene, 1,2,4-trichlorobenzene, and pentachlorobenzene induced 4-dimethylaminoantipyrine (DMAP) N-demethylase, an enzyme induced by phenobarbitone (PB) and several PB-type inducers. Hexachlorobenzene induced DMAP N-demethylase and aldrin epoxidase, two PB-inducible enzymes, and benzo[a]pyrene hydroxylase and ethoxyresorufin O-deethylase, two enzymes induced by 3-methylcholanthrene (MC). This mixed-type induction pattern has been previously reported for hexachlorobenzene. The remaining higher chlorinated benzene and phenol congeners were inactive as inducers of the drug-metabolizing enzymes in the immature male Wistar rats.

Polychlorinated biphenyls: correlation between in vivo and in vitro quantitative structure-activity relationships (QSARs).

The in vivo quantitative structure-activity relationships (QSARs) for several polychlorinated biphenyls (PCBs) were determined in the immature male Wistar rat. The ED25 and ED50 values for hepatic microsomal aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD) induction as well as for body weight loss and for thymic atrophy were determined for nine PCB congeners and 4'-bromo-2,3,4,5-tetrachlorobiphenyl. The most active compounds were the coplanar PCB congeners, 3,3',4,4',5-penta- and 3,3',4,4',5,5'-hexachlorobiphenyl; for example, their ED50 values for body weight loss were 3.25 and 15.1 mumol/kg, respectively. The in vivo toxicity of the coplanar PCB, 3,3',4,4'-tetrachlorobiphenyl, was significantly lower (ED50 for body weight loss = 730 mumol/kg) than the values observed for the more highly chlorinated homologs, and this was consistent with the more rapid metabolism of the lower chlorinated congener. The dose-response biologic and toxic effects of several mono-ortho-chloro-substituted analogs of the coplanar PCBs, including 2,3,4,4'5-, 2,3,3',4,4'-, 2',3,4,4',5- and 2,3',4,4',5-penta-, 2,3,3',4,4',5- and 2,3,3',4,4',5'-hexachlorobiphenyl were also determined, and members of this group of compounds were all less toxic than 3,3',4,4',5-penta and 3,3',4,4',5,5'-hexachlorobiphenyl. There was a good rank order correlation between the in vivo QSAR data and the in vitro QSARs for PCBs that were developed from their relative receptor binding affinities and potencies as inducers of AHH and EROD in rat hepatoma H-4-II E cells in culture. These results are consistent with the proposed receptor-mediated mechanism of action for PCBs. In addition, for this series of halogenated biphenyls there was a linear correlation between their in vivo toxicity in rats and their in vitro monooxygenase enzyme induction results. Assuming that the in vivo toxic responses in the rat are representative toxic responses to PCBs, then these results support the predictive utility of the in vitro bioassay with rat hepatoma H-4-II E cells as a short-term test system for the potential toxicity of this class of halogenated aryl hydrocarbons.

Reconstituted halogenated hydrocarbon pesticide and pollutant mixtures found in human tissues: effects on the immature male Wistar rat after short-term exposure.

Halogenated hydrocarbon insecticides and polychlorinated biphenyl (PCB) mixtures are routinely detected as residues in human adipose tissue, serum, and milk. Based on average values observed in analytical studies, reconstituted halogenated hydrocarbon pesticide mixtures and PCB mixtures were prepared and administered to immature male Wistar rats. The mixtures were administered at dose levels which approximate the concentrations which would be absorbed by an infant suckling for 180 days (low dose, L), and at three higher dose levels (2 X L, 10 X L, and 100 X L). The pesticide mixture contained isomeric hexachlorocyclohexanes, dieldrin, heptachlor epoxide, oxychlordane, trans-nonachlor, hexachlorobenzene, 1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane, 1,1-dichloro-2,2-bis(p-chlorophenyl)ethane, and 1,1-dichloro-2,2-bis(p-chlorophenyl)ethylene; the reconstituted PCB mixture contained 13 of the major congeners which have been identified in human milk samples. Administration of the L dose level of the pesticide (0.95 mg/kg), PCB (0.45 mg/kg), and pesticide plus PCB mixture (0.95 + 0.45 mg/kg, respectively) in corn oil on days 1 and 3 did not significantly alter hepatic drug-metabolizing enzyme activities or elicit any observable pathological damage 6 days after the first exposure. In contrast, administration of the higher dose levels of this mixture elicited a dose-dependent induction of several hepatic drug-metabolizing enzymes. Moreover, despite the short duration of exposure to these chemicals, the rats treated with the higher doses (10 X L and 100 X L) of these mixtures exhibited mild alterations in thyroid architecture, changes in hepatocellular nuclei including variations in chromatin distribution, vesiculation of larger nuclei, and frequent appearance of pyknotic shrunken nuclei.(ABSTRACT TRUNCATED AT 250 WORDS)

Effects of substituents on the cytosolic receptor-binding avidities and aryl hydrocarbon hydroxylase induction potencies of 7-substituted 2,3-dichlorodibenzo-p-dioxins. A quantitative structure-activity relationship analysis.

The binding affinities of 16 7-substituted 2,3-dichlorodibenzo-p-dioxins for the 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) cytosolic receptor protein from male Wistar rats have been determined. The EC50 value for each compound was estimated by competitive displacement of [3H]TCDD and the data illustrated that the differences between competitive ligands were dependent on the substituent (X) group. The EC50 value for 7-trifluoromethyl-2,3-dichlorodibenzo-p-dioxin was 1.95 X 10(-8) M and was greater than 1000-fold more active than 7-amino-2,3-dichlorodibenzo-p-dioxin (EC50 = 2.88 X 10(-5) M). Multiple parameter linear regression analysis of the data for 14 different compounds gave the following equation: log (1/EC50) = 1.24 pi + 6.11. This demonstrated that the binding affinity was linearly dependent on the lipophilicity (pi) of the 7-X-group. This contrasted with a comparable analysis of the substituent effects on the binding of 13 4'-substituted 2,3,4,5-tetrachlorobiphenyls to the cytosolic receptor which showed that the lipophilicity, electronegativity, and hydrogen-bonding capacity were important physicochemical determinants which facilitated binding to the receptor protein. These data suggest that the halogenated dibenzo-p-dioxins and biphenyls may interact with different binding sites on the receptor or they may bind to the same site but exert different conformational effects on the receptor protein. For the 7-X-2,3,-dichlorodibenzo-p-dioxins, there was not a rank order correlation between receptor-binding EC50 values and the induction of aryl hydrocarbon hydroxylase (AHH) or ethoxyresorufin O-deethylase in rat hepatoma H-4-II E cells in culture. However, the data could be correlated with an estimate of substituent width, the STERIMOL factor (B5), i.e., log (AHH) = 1.29 log (binding) + 2.19 delta B5 - 1.31 (delta B5)2 - 1.48. The importance of a steric factor in the correlation between receptor binding and AHH induction for substituted dibenzo-p-dioxins and halogenated biphenyls is consistent with a structure-dependent conformational change(s) in the receptor protein:ligand complex after the initial binding event. Presumably, this latter process is associated with the steps involving interactions between the ligand:receptor complex and nuclear binding sites.

Hexachlorobenzene and substituted pentachlorobenzenes (X-C6Cl5) as inducers of hepatic cytochrome P-450-dependent mono-oxygenases.

Hexachlorobenzene (HCB) and 2,3,4,4',5-pentachlorobiphenyl induced a similar spectrum of cytochrome-P-450-dependent mono-oxygenase activities in the rat, including 4-dimethylaminoantipyrine N-demethylase, aryl hydrocarbon hydroxylase (AHH) and ethoxyresorufin O-deethylase (EROD). Levels of individual cytochrome P-450 isozymes and various mono-oxygenase activities in liver microsomes from rats treated with substituted pentachlorobenzene (X-C6Cl5) and 4'-substituted-2,3,4,5-tetrachlorobiphenyl (X-C12 H5Cl4) analogues demonstrated the remarkable effects of substituent structure on induction activities. The chloro- and bromopentachlorobenzenes induced hepatic microsomal 4-dimethylaminoantipyrine N-demethylase, AHH and EROD; the iodo-, fluoro-, acetamino- and nitropentachlorobenzene analogues together with pentachlorobenzene weakly induced both AHH and EROD (approximately 2-fold or less); and the remaining substituted pentachlorobenzenes tested (X = CH3, OCH3 and OH) were relatively inactive as inducers of microsomal mono-oxygenases. Substituent effects were observed for the induction of liver microsomal cytochromes P-450a, P-450b + e, P-450c, P-450d and total cytochrome P-450 by the X-C6Cl5 and X-C12H5Cl4 analogues. The chloro- and bromopentachlorobenzene analogues in both series induced total cytochrome P-450 and cytochromes P-450a to P-450d, whereas the hydroxy-, methyl- and methoxy-substituted analogues in both series were relatively inactive as inducers of cytochrome P-450. Iodo-, fluoro- and nitropentachlorobenzene were weak 3-methylcholanthrene-type inducers and, in contrast to the corresponding biphenyl analogues, had little or no effect on the induction of cytochromes P-450a, P-450c and P-450d.(ABSTRACT TRUNCATED AT 250 WORDS)

Effects of individual terphenyls and polychlorinated terphenyls on rat hepatic microsomal cytochrome P-450-dependent monooxygenases: structure-activity relationships.

The effects of o-, m- and p-terphenyl, 2,4-dichloro-, 2,4,6-trichloro-, 2,3,5,6-tetrachloro-, 2,3,4,6-tetrachloro-, 2,4,4''',6- tetrachloro- and 2,3,4,5-tetrachloro-p-terphenyl, 2,3,4,5-tetrachloro-m- and o-terphenyl as inducers of hepatic drug-metabolizing enzymes were determined in immature male Wistar rats. o-Terphenyl, 2,4-dichloro-, 2,4,6-trichloro-p-terphenyl and 2,3,4,5-tetrachloro-o-terphenyl induced 4,4'-dimethylamino antipyrine N-demethylase at total dose levels of 300 mumol/kg and the 2,3,4,5-tetrachloro-p-terphenyl induced ethoxyresorufin O-deethylase (EROD). In contrast, none of the other terphenyls or polychlorinated terphenyls (PCTs) induced these enzyme activities. Previous studies have demonstrated that 2,3,4,5-tetrachloro-p-terphenyl did not exhibit a high affinity for the 2,3,7,8-tetrachlorodibenzo-p-trachlorodibenzo-p-dioxin (TCDD) receptor protein (EC50 = 6.6 X 10(-6) M). In contrast, this study showed that 2,3,4,5-tetrachloro-p-terphenyl was more active than either 2,3,4,5-tetrachloro-o- or m-terphenyl as an inducer of EROD. Moreover, the competitive receptor binding EC50 values for the latter two isomers were greater than 10(-5) M and this result was also consistent with their lack of EROD induction activity. Previous studies showed that analysis of the data for a series of 4'-substituted-2,3,4,5-tetrachlorobiphenyls indicated that the p-terphenyl structural moiety (i.e. 4'-substituent = phenyl) did not interact with high affinity with the receptor protein binding site. Since the 2,3,4,5-tetrachloro o- and m-terphenyls are also poor ligands for the receptor protein, this data and results from other studies indicate that PCT congeners (and commercial mixtures) are therefore unlikely to elicit significant 2,3,7,8-TCDD-like biologic or toxic effects in target species.