Mechanism-based inhibition of mouse P4502b-10 by selected arylalkynes.

Suicide inhibitors of cytochrome P450 families are excellent tools to predict which isoforms mediate the metabolism/activation of a variety of chemical agents. We compared the inhibitory effects of several arylalkynes on mouse cytochromes P450 with published data for the rat model. The inhibition of P4502b specific dealkylation of benzyloxyresorufin by 2-ethynylnaphthalene (2-EN), 5-phenyl-1-pentyne (PPY), 4-phenyl-1-butyne (PBY), and 9-ethynylphenanthrene (9-EPh) was measured in hepatic microsomes from male mice treated with 1,4-bis[2-(3,5-dichloropyridyloxy)]-benzene (TCPOBOP) to induce cytochrome P4502b. Pulmonary microsomes were prepared from untreated mice. 9-EPh, 2-EN, and PPY caused a time-, concentration-, and NADPH-dependent loss in P4502b activity in both tissues. PBY, however, demonstrated this type of inhibition only in liver microsomes. The IC50 was calculated for both liver and lung microsomes and compared with published Ki (concentration required for half-maximal inhibition) or KI (concentration required for half-maximal inactivation) values for the rat. PPY, PBY, and 9-EPh were equally effective inhibitors of mouse P4502b and rat P4502B1. 2-EN was a 5- to 10-fold less potent inhibitor of mouse P4502b, as compared with the rat, even though it was shown to bind to the active site of the mouse isoform as demonstrated by its metabolism to 2-naphthylacetic acid. These data suggest that the active site of the mouse P4502b enzyme is functionally similar to the rat P4502B isoform, with the exception of the disparity in its susceptibility to inactivation by 2-EN as measured by the Ki values.

Relationship between CYP1A enzyme activities and protein levels in rats treated with 2,3,7,8-tetrachlorodibenzo-p-dioxin.

Induction of CYP1A1 is one of the best characterized responses to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). EROD activity has been used as an enzymatic marker for CYP1A1 following TCDD treatment. Enzymatic markers for the induction of CYP1A2 by TCDD are not as well characterized. The present study examines the relationship between CYP1A1 and CYP1A2 protein and the corresponding enzymatic markers. Induction of hepatic ethoxyresorufin O-deethylase (EROD) activity and methoxyresorufin O-demethylase (MEROD) and acetanilide 4-hydroxylase (ACOH) activity (both markers for CYP1A2) were analyzed in 8-wk-old male and female Fischer 344 rats treated orally with either 0, 0.1, 0.3, 1.0, or 3.0 micrograms TCDD/kg. There were no sex differences in basal EROD or ACOH activity. MEROD activity was significantly greater in control males than in control females. Significant induction of EROD activity in females occurred at slightly lower doses of TCDD compared to males (0.1 vs. 0.3 micrograms/kg, respectively); however, a greater absolute and a larger fold induction of EROD activity was seen in males compared to females at all doses tested except 0.1 micrograms/kg. EROD activity did not attain a maximum in either sex. Similarly, MEROD activity was induced at lower doses of TCDD in females than in males (0.1 vs. 0.3 micrograms/kg, respectively). MEROD activity was maximally induced at 0.3 micrograms/kg in males. In females, MEROD did not attain maximum induction at the doses tested. ACOH activity was induced at doses as low as 0.3 micrograms/kg in both sexes, and the dose-dependent increases in activity were equivalent in males and females. Both ACOH and MEROD activity correlated well with CYP1A2 levels as determined by Western blot analysis, although there was a greater fold induction of protein than either MEROD or ACOH. Although MEROD and ACOH are both markers for the same response, MEROD activity may be a more useful marker because it is the quicker and more sensitive of the two assays.

Promotion of N-nitrosodiethylamine-initiated hepatocellular tumors and hepatoblastomas by 2,3,7,8-tetrachlorodibenzo-p-dioxin or Aroclor 1254 in C57BL/6, DBA/2, and B6D2F1 mice.

To investigate the hypothesis that tumor promotion by chlorinated aromatic hydrocarbons involves Ah receptor occupation and subsequent induction of cytochromes P-450 1a-1, effects of Aroclor 1254 or 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) were examined in N-nitrosodiethylamine-initiated mice with different Ah receptor phenotype. Levels of cytochromes P-450 1a and 2b were measured by enzyme assay and Western immunoblots. Males of the C57BL/6, DBA/2, or (C57BL/6 x DBA/2)F1 (hereafter referred to as "B6D2F1") strain were initiated with a single i.p. dose of N-nitrosodiethylamine (90 mg/kg body weight), followed by either multiple doses of TCDD (0.05 micrograms/kg) weekly or Aroclor 1254 chronically in the diet (100 ppm) for 20 weeks, and then no treatment for 24 weeks. Lung tumor incidence or multiplicity was not altered by either of the promoters. Liver tumor incidence was similar among the three strains after N-nitrosodiethylamine alone (14, 21, and 21%, respectively). In DBA/2 mice, TCDD neither induced Cyp 1a nor promoted liver tumors. Aroclor caused an 8-fold induction of hepatic Cyp 2b, which was its maximum at the 12-week time point but did not promote tumors. Inductions of hepatic Cyp 1a by TCDD and 1a and 2b by Aroclor were similar in C57BL/6 and B6D2F1 mice, but tumor promotion responses were quite different. Dietary Aroclor significantly promoted liver tumors in C57BL/6 mice (59 versus 14%) but not in B6D2F1 mice (24 versus 21%). Repeated TCDD promoted only in B6D2F1 mice (52 versus 21%) and not in C57BL/6 mice (19 versus 14%). Thus, whereas these data confirm that a functional Ah receptor is required for liver tumor promotion, the degree of activation as measured by induction of Cyp 1a is not directly related to the degree of tumor-promoting capability. Other genetic factors must play a role in mediating the final tumor outcome.

Effect of dietary Aroclor 1254 exposure on lung and kidney cytochromes P450 in female rats: evidence for P4501A2 expression in kidney.

In this report, we have investigated the effect of dietary exposure to Aroclor 1254 (1-100 ppm) given chronically or discontinuously over an 84-day time interval to the female F344 rat. Cytochrome P4501A was quantified in lung and kidney by measuring the dealkylation of ethoxyresorufin substrate and by Western immunoblotting. P4501A displayed a dose- and time-dependent increase in both extrahepatic organs. The kidney appeared to be more responsive to induction than lung at all doses (maximum of 500-fold induction following 84 days exposure to 100 ppm). Further, there was evidence by enzymatic activity, immunoblotting and Northern analysis of total RNA for the presence of 1A2 in the most highly induced kidneys. The decline in 1A induction observed following discontinuous exposure was more prominent in the kidney than in the lung. These data demonstrate the sensitivity of kidney to P4501A induction capacity as compared to lung, although the persistence of the induction response was evident in lung and not kidney.

Promotion of N-nitrosodimethylamine-initiated mouse lung tumors following single or multiple low dose exposure to 2,3,7,8-tetrachlorodibenzo-p-dioxin.

The environmental contaminant, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), is highly toxic to several rodent species and may have adverse health effects in exposed human populations. Further, TCDD has been shown to be a potent liver tumor promoter in the rat after repeated administration. These studies were conducted to determine the tumor promoting capability of TCDD in the Swiss mouse following single or multiple exposures. Following tumor initiation with N-nitrosodimethylamine (NDMA; 25 mg/kg), animals were given either a single dose (1.6, 16 or 48 micrograms/kg) or repeated injections (0.05 microgram/kg/week for 20 weeks) of TCDD and sacrificed at 52 weeks of age. Neither NDMA nor TCDD caused an increase in incidence of liver tumors. NDMA induced lung tumors in 100% of animals, with 12 +/- 0.1 tumors/mouse. The multiplicity of lung tumors was significantly increased by low dose TCDD treatment, with 20 +/- 2.6 tumors/mouse following a single 1.6 micrograms/kg dose (P = 0.016) and 18 +/- 1.7 (P = 0.031) following repeated 0.05 microgram/kg doses (x 20). Higher doses of TCDD did not increase multiplicity of lung tumors and, in fact, may have been toxic to the lungs of NDMA-treated mice, as evidenced by the infiltration of pigmented macrophages. These data demonstrate the potent tumor promoting capability of TCDD in mouse lung.

Suppression of pulmonary P4502b and induction of hepatic, intestinal and kidney P4501a-1 and 1a-2 in the Ah-responsive and non-responsive mouse by Aroclor 1254.

1. Investigations in our laboratory have demonstrated a rapid suppression of the P4502b isoform in mouse lung, concomitant with significant induction of this enzyme in liver from these same animals. The current study was designed to determine whether the suppression by polychlorinated biphenyls of pulmonary P4502b required the presence of a functional Ah receptor, and additionally to delineate the time course of the induction responses to Aroclor 1254 in the liver, kidney, and intestine of the AH-responsive and non-responsive mouse. 2. P450s were quantified by specific enzyme assay and immunoblot in liver (1a-1, 1a-2, 2b), lung (1a-1, 1a-2), kidney (1a-1, 1a-2, 2b) and small intestine (1a-1, 2b) of C57 and DBA animals at varying times (48 h-12 weeks) following a single intraperitoneal dose of Aroclor 1254 (250 mg/kg). 3. The suppression of constitutive P4502b in the lung by Aroclor was observed in both strains, but was more prominent over a longer time course in the non-responsive animals. P4502b enzyme activity was increased in the liver and intestine of both strains of mouse; however, there was a significantly greater response to Aroclor in the C57 animals. These data indicate that the AH receptor does not participate in the suppression of pulmonary P4502b, and suggests that the regulation of inducible P4502b in liver and intestine is quantitatively different between these two strains of mouse. 4. P4501a was predictably induced in all tissues examined from the C57 animal, but was largely unaffected by PCBs in the DBA strain. P4501a-2, which is also regulated by the Ah receptor, was highly induced in the liver of the responsive strain, and also increased approximately two-fold in the liver of the non-responsive animals. Kidney P4501a-2 was also modestly increased by Aroclor, only in the responsive mouse.

Subchronic dietary exposure to Aroclor 1254 in rats: accumulation of PCBs in liver, blood, and adipose tissue and its relationship to induction of various hepatic drug-metabolizing enzymes.

Female F344/NCr rats were exposed continuously (7-84 days) or discontinuously (7 days exposure/21 days control diet or 28 days exposure/56 days control diet) to various dietary concentrations (1-100 ppm) of Aroclor 1254. There were dose- and time-dependent increases in PCB levels in liver, blood, and adipose tissue. Following removal of the rats from diet containing Aroclor 1254, there was a relatively rapid decrease in PCB levels, particularly in rats exposed to higher concentrations of Aroclor 1254. In parallel with the alterations in PCB levels observed, the rats showed striking dose- and time-dependent increases in hepatic levels of CYP1A1 and CYP1A2, as determined by various methods [RNA analysis, immunochemical detection, or measurement of the O-dealkylation of methoxyresorufin (CYP1A2) or ethoxyresorufin (CYP1A1)]. In rats removed from the Aroclor 1254 diet, catalytic activity for CYP1A1 as well as RNA levels for both CYP1A1 and CYP1A2 rapidly diminished. In contrast to the high levels of induction of CYP1A1 and CYP1A2 observed, limited induction (< 5-fold) of epoxide hydrolase, quinone oxidoreductase, and aldehyde dehydrogenase was detected, even in rats exposed to the highest concentration of Aroclor (100 ppm) for up to 84 days. Furthermore, induction of these non-CYP hepatic drug-metabolizing genes exhibited distinctly different concentration-response curves. The ratios of hepatic CYP1A1 activity to hepatic PCB burden were similar for rats exposed continuously to Aroclor in the diet for 7, 28, or 84 days, and for rats exposed discontinuously (7 days Aroclor/21 days control diet or 28 days Aroclor/56 days control diet). Thus, hepatic PCB levels alone appeared to be reasonably predictive of CYP1A1 levels under a variety of modes of exposure. When the ratio of CYP1A1 activity to adipose or blood PCB concentration was determined, similar ratios were observed for rats exposed continuously for 7, 28, or 84 days. However, lower ratios were observed for rats discontinuously exposed to Aroclor in the diet. These results have important implications with respect to: (a) employing PCB levels in various tissues to predict biological effects, and (b) determining different concentration-response curves for the various biological effects induced by PCBs.

Comparison of transplacental and neonatal initiation of mouse lung and liver tumors by N-nitrosodimethylamine (NDMA) and 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone (NNK) and promotability by a polychlorinated biphenyls mixture (Aroclor 1254).

We have previously shown a positive tumor-promoting effect of a single dose of Aroclor 1254 on lung and liver tumors initiated neonatally in the mouse by N-nitrosodimethylamine (NDMA). In this study, we have confirmed and extended this observation with NDMA and the tobacco-specific nitrosamine, 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone (NNK) given either transplacentally or postnatally, followed by a single dose of Aroclor 1254 on day 56. This polychlorinated biphenyl (PCB) mixture was an effective promoter of both lung and liver tumors; however, there were specific initiator and sex-related differences in this response. Aroclor administration significantly increased the incidence of lung tumors initiated transplacentally by NDMA or NNK in male mice. Neither nitrosamine initiated tumors transplacentally in females, but lung tumors initiated with NNK and liver tumors caused by NDMA in neonatal females were promoted by PCBs. Both liver and lung tumors initiated neonatally by NDMA in male animals, but not NNK-initiated tumors, were promoted by PCBs. These data confirm that PCBs are able to promote both NDMA- and NNK-initiated tumors, but with chemical-, sex- and age-dependent difference; this suggests influences of both quantitative and qualitative factors in susceptibility to tumor promotion.

Induction of hepatic CYP1A in male F344/NCr rats by dietary exposure to Aroclor 1254: examination of immunochemical, RNA, catalytic, and pharmacokinetic endpoints.

Male F344/NCr rats were exposed to low dietary concentrations of Aroclor 1254 (0-33 ppm) for 7 days, following which the induction of selected hepatic drug metabolizing enzymes was monitored. CYP1A1, measured indirectly by assaying the O-dealkylation of ethoxyresorufin in 9000 g supernatants, was increased 1.5-, 3-, 8-, and 37-fold following 7 days of exposure to 1.0, 3.3, 10, and 33 ppm Aroclor, respectively. In contrast, the O-dealkylation of benzyloxyresorufin, an indirect measure of CYP2B1 activity, was increased approximately 4-fold following exposure to 33 ppm dietary Aroclor. Measurement of the non-P450-mediated activities epoxide hydrolase, DT-diaphorase, and aldehyde dehydrogenase (NADP+, benzaldehyde) revealed < 4-fold inductions following feeding of 33 ppm Aroclor. In view of the relatively high sensitivity of the CYP1A-specific catalytic endpoint as a biomarker for Aroclor exposure, alternative endpoints for detecting induction of this subfamily of P450 were also examined. The extent of in vivo CYP1A induction was assessed by measuring serum concentrations of zoxazolamine 150 min following an intraperitoneal dose of 100 mg/kg body wt. Slight decreases in serum zoxazolamine concentration were observed in rats exposed to as little as 1.0 ppm dietary Aroclor 1254, while profound decreases were seen in rats exposed to > or = to 10 ppm Aroclor. Immunodetection of CYP1A1 protein, with a monoclonal antibody directed against this cytochrome, revealed a 2.9-fold increase in rats exposed to as little as 1.0 ppm Aroclor, and approximately 10- and 44-fold increases following exposure to 3.3 and 10 ppm dietary Aroclor, respectively. Increases in total hepatocellular RNA coding for CYP1A1 and CYP1A2, quantified by hybridization to specific oligonucleotide probes, corresponded well to the increases in hepatic O-dealkylase activity for ethoxyresorufin (CYP1A1) and methoxyresorufin (CYP1A2), respectively. Thus, CYP1A induction, directly or indirectly measured with a variety of endpoints, represents a highly sensitive biomarker for exposure to relatively low doses of Aroclor 1254 in the rat.

Induction of hepatic CYP1A activity as a biomarker for environmental exposure to Aroclor 1254 in feral rodents.

Specimens of the feral mouse species Reithrodontomys fulvescens trapped from a polychlorinated biphenyl (PCB)-contaminated field location had hepatic ethoxyresorufin (ETR) O-dealkylase activities and immunoreactive CYP1A protein contents which were two- to threefold higher than those measured in animals of the same species and sex collected from non PCB-contaminated reference sites. Specimens with hepatic ETR O-dealkylase activities differing by as little as 50% could readily be assigned as originating from the PCB or reference sites by the use of a specific chemical inhibitor of cytochrome P450IA (CYP1A). The relative levels of ETR O-dealkylase activity in R. fulvescens significantly correlated with hepatic PCB burdens (r = 0.819, P less than 0.01). When the magnitudes of the induced ETR O-dealkylase activities corresponding to given hepatic PCB burdens were compared between the feral animals, F344/NCr rats (Rattus norvegicus) or B6C3F1 mice (Mus musculus) exposed in the laboratory to dietary Aroclor 1254, the order of sensitivity to the inducing effects of PCBs were F344/NCr rat greater than B6C3F1 mouse greater than R. fulvescens.

Promotion of mouse lung tumors by bioaccumulated polychlorinated aromatic hydrocarbons.

Lung tumors initiated in infant Swiss mice by N-nitrosodimethylamine (NDMA) were promoted by a single dose of a mixture of polychlorinated biphenyls (PCBs), Aroclor 1254 (250 or 500 mg/kg) given 4 days later. The tumors were typical alveologenic adenomas, and their number increased gradually over the course of 1 year to a maximum 4-fold enhancement in average tumor number compared with those given NDMA alone. The time course pattern suggested continuous tumor stimulation by the nonmetabolized PCB congeners retained in the tissues. Content of the nine major bioretained PCB congeners in carcass, liver, and lung was determined at intervals after treatment. Several showed tissue-specific retention patterns: 2,3,3',4,4'-PCB was selectively retained in lung and liver, and 2,2',3,4,4', 5'-HCB in lung. In tests of the tumor-promoting ability of individual congeners, the 2,2',3,4,4',5'-HCB, an Ah receptor agonist, promoted lung tumors when given singly, whereas another prominent bioretained congener, the 2,2',4,4',5,5'-HCB, an Ah receptor antagonist, did not promote, and in fact abrogated the positive effect of the 2,2',3,4,4',5'-HCB. In a parallel examination of persistent biochemical effects, a single low dose of 2,3,7,8-tetrachlorodibenzo-p-dioxin (5 nmole/kg) resulted in significant elevation of immunochemically detected protein and enzymatic activity of cytochrome P450 IA1 in lung for at least 12 weeks; these parameters were elevated for at least 30 weeks after a single dose of Aroclor 1254 (500 mg/kg). Taken together these results suggest that Ah-receptor-dependent induction of cytochrome P450 IA1 in mouse lung is correlated with and possibly causally involved in promotion of tumors by retained congeners.