Developmental effects of estrogen and PCBs in the reproductive tract of BALB/C mice

Many of the tumorigenic effects that result from neonatal exposure to both natural and synthetic estrogens resemble those found in humans exposed to diethylstilbestrol (DES) in utero. Using this established DES neonatal mouse model, my goal was to investigate long-term molecular and morphological effects of certain polychlorinated biphenyls (PCBs) that are weakly estrogenic in adult mice. Focusing on the cervicovaginal (CV) tract, since this is where tumors develop in the BALB/c mouse, I first assessed the 17β-estradiol (E2) dose-response for expression of lactoferrin (LTF). LTF is a highly inducible estrogen biomarker that is permanently altered in uteri from neonatally treated mice. Treatments were administered via 5 subcutaneous injections beginning within 16 hrs after birth, days 1–5. ^ The ontogeny of LTF expression from mouse CV tracts was determined by examining three different stages of life: pups, immature, and mature mice. Northern RNA analysis and immunohistochemistry showed that neonatal E 2 treatment both increases and decreases LTF expression. Early expression of LTF in the CV tract at all doses occurred in pups. In both immature and adult mice, increased LTF expression was dependent on whether E2 induced ovary-dependent or ovary-independent persistent vaginal cornification. ^ Next, I studied biological responses from neonatally PCB exposed adult mice. As expected, using a neonatal uterine bioassay I showed that 2 ′4′6′-trichloro-4-biphenylol (OH-PCB-30), 2′3′4′ 5-tetrachloro-4-biphenyloI (OH-PCB-61), and OH-PCB-30/61 (50/50 mixture), were estrogenic causing a dose-dependent increase in uterine weight. ^ Long-term effects of OH-PCB 30 [200 μg/pup/day] were most similar to E2 as seen by an increased uterine wet weight in day 50 mice similar to E2 [5 μg/pup/day] (141% and 140% of control, respectively). Another similarity between OH-PCB 30 and E2 neonatally treated mice was found in those sacrificed at 20 months of age. At these same doses CV tract squamous cell carcinoma induction was 43% of E2 treated mice and 47% of OH-PCB 30 treated mice. Differences were noted in adenoaquamous; cell carcinoma development, where 16% of OH-PCB-30 neonatally treated mice developed tumors versus 8% for E2. Based on these results using the neonatal mouse model, I conclude that the OH-PCBs tested are strongly estrogenic and tumorigenic showing dose-response relationships when exposure occurs during development of the reproductive tract in mice. These results may have important implications for risk assessment in determining the effects of xenoestrogens exposure early versus later in life. ^

CYTOCHROME P450 MEDIATED REDUCTIVE DEHALOGENATION OF HEXACHLOROBENZENE

The role of the cytochrome (CYT) P-450 mixed-function oxidase (MFO) in the biotransformation of hexachlorobenzene (HCB) was investigated, since in vivo interaction between this enzyme and chemical is very probable. HCB is a type I substrate with (Fe('3+)) CYT P-450 isozymes present in untreated, b-naphthoflavone (BNF) and phenobarbital (PB) induced rat liver microsomes. HCB dependent and saturable type I binding titrations yield spectral dissociation constants (K(,s)) of 180 and 83 uM for the isozymes present in untreated and PB induced microsomes, respectively. Purified CYT P-450b, the major isozyme induced by PB, produces HCB dependent and saturable type I spectra with a K(,s) of 0.38 uM.^ CYT P-450 mediated reductive dehalogenation occurs in microsomes and purified/reconstituted MFO systems and produces pentachlorobenzene (PCB) as the initial and major metabolite under both aerobic and anaerobic conditions. In microsomal reactions secondary metabolism of PCB occurs in the presence of oxygen. Pentachlorophenol (PCP) is produced only in aerobic reactions with PB induced microsomes with a concomitant decrease in PCB production. PCP is not detected in aerobic reactions with BNF induced microsomes, although PCB production is decreased compared to anaerobic conditions. A reaction scheme for the production of phenolic metabolities from PCB is deduced.^ CYT P-450 dependent and NADPH independent modes of PCB production occur with purified/reconstituted MFO systems and are consistent with dehalogenation pathways observed with microsomal experiments. The NADPH independent production of PCB requires native microsomal or purified MFO protein components and may be the result of nucleophilic displacement of a chlorine atom from HCB mediated or coupled with redox active functions (primary, secondary, tertiary and quarternary structures) of the proteins. CYT P-450 dependent production of PCB from HCB is isozyme dependent: CYT P-450c = CYT P-450d > CYT P-450a > CYT 450b. The low apparent specific activity may be due to non-optimal reconstitution conditions (e.g., isozyme choice and requirement of other microsomal elecron transport components) and secondary metabolism of PCB and the phenols derived from PCB. CYT P-450 mediated dehalogenation may be catalyzed through attack, by the iron oxene (postulated intermediate of CYT P-450 monooxygenations), at the chlorines of HCB instead of the aromatic nucleus. (Abstract shortened with permission of author.) ^