Gail D. Bellward

Comparison of polychlorinated dibenzodioxin levels with hepatic mixed‐function oxidase induction in great blue herons

As part of the Canadian Wildlife Service monitoring of great blue herons in British Columbia, eggs were collected from three colonies with low, intermediate, and high levels of PCDD and PCDF contamination: Nicomekl, Vancouver, and Crofton, respectively. One egg from each nest was used for chemical analysis by GC-MS; the others were hatched. Liver microsomes were prepared from the heron chicks and used for determination of cytochrome P-450-dependent activities. No erythromycin N-demethylase activity was found in any sample. Ethoxyresorufin O-dealkylase activity in the Nicomekl group was similar to that in pigeons, a control altricial species. The ethoxyresorufin activity in the herons from the Crofton colony was 2.6-fold higher than in the Nicomekl group. The Vancouver colony was intermediate. No difference among the three heron colonies was found in pentoxyresorufin O-dealkylase activity, although levels were 20-33 times that in the pigeon. Chemical analysis was carried out on paired heron eggs. Vancouver and Crofton eggs contained 13.5 and 21 times the levels of 2,3,7,8-TCDD compared to the Nicomekl group. The Crofton eggs contained higher levels of several other contaminants also. A highly significant correlation (p less than .001) was found between ethoxyresorufin O-dealkylase and 2,3,7,8-TCDD concentrations. The correlation coefficient did not change when ethoxyresorufin O-dealkylase was compared to total chemical contamination using several toxic equivalency factors. Multiple regression analysis resulted in only one predictor variable for ethoxyresorufin O-dealkylase: 2,3,7,8-TCDD.

Monitoring biological effects of polychlorinated dibenzo‐p‐dioxins, dibenzofurans, and biphenyls in great blue heron chicks (Ardea herodias) in British Columbia

The Canadian Wildlife Service monitors levels of polychlorinated aromatic hydrocarbons in great blue heron (Ardea herodias) eggs in British Columbia as indicators of environmental contamination. The present project assessed the temporal effects of environmental contamination with 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and other polychlorinated dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and biphenyls (PCBs) on hepatic microsomal ethoxyresorufin O-deethylase (EROD) activities and several morphological parameters in heron hatchlings. Between 1990 and 1992, eggs were collected from two great blue heron colonies in British Columbia that had elevated levels of contamination in 1988: Vancouver in 1990 and 1992, and Crofton in 1991. Biological parameters in the hatchlings and chemical contaminant levels in matched eggs from the same clutch were measured and compared with the findings from the same colonies studied in 1988. Levels of TCDD and other PCDDs and PCDFs had decreased significantly in both colonies since 1988. A concomitant decrease in EROD activity and incidence of chick edema, increase in body weight, and improvement of the reproductive success of the Crofton colony was observed. Body, yolk-free body, stomach, and intestine weights, tibia wet, dry, and ash weights, and tibia length regressed negatively on TCDD level (p < .01; n = 54). Hepatic EROD activity regressed positively on TCDD level (r2 = .49; p = .00005; n = 54). Regression of these parameters on the sum of TCDD toxic equivalents (TEQ) resulted in similar relationships. The reduction in severity of the effects observed in the contaminated colonies in the recent collections, accompanied by the declines in levels of PCDDs and PCDFs, was consistent with the dose-response relationships determined in 1988.

Dioxin contamination and growth and development in great blue heron embryos

A great blue heron colony located near a pulp mill in British Columbia failed to fledge young in 1987, with a concurrent sharp increase in polychlorinated dibenzo-p-dioxin (PCDD) and polychlorinated dibenzofuran (PCDF) levels in their eggs. In 1988 we tested the hypothesis that the PCDD and PCDF contamination caused reproductive failure by increasing mortality of the heron embryos in ovo. Pairs of great blue heron eggs were collected from three British Columbia colonies with low, intermediate, and high levels of dioxin contamination: Nicomekl, Vancouver, and Crofton, respectively. One egg of each pair was incubated under laboratory conditions at the University of British Columbia (UBC) while the other egg was analyzed for PCDDs and PCDFs. All incubated eggs were fertile. All eggs from the Nicomekl colony hatched, while 13 of 14 eggs from Vancouver and 12 of 13 eggs from Crofton hatched. Subcutaneous edema was observed in 4 of 12 chicks from Crofton and 2 of 13 chicks from Vancouver. No edema was seen in the chicks from Nicomekl. There was a small, but significant, negative regression of plasma calcium concentration, yolk-free body weight, tibia length, wet, dry, and ash weight, beak length, and kidney and stomach weight of the hatched chicks on the tetrachlorodibenzo-p-dioxin (TCDD) level of the paired eggs. Fewer down follicles were present on the heads of TCDD-contaminated chicks. Hence while dioxins did not cause mortality of the heron embryos in ovo, the depression of growth and the presence of edema are suggestive that dioxins at the levels found in the environment have an adverse effect on the development of great blue heron embryos.

Biological effects of polychlorinated dibenzo-p-dioxins, dibenzofurans, and biphenyls in double-crested cormorant chicks (Phalacrocorax auritus)

The present project assessed the effect of environmental contamination with polychlorinated dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and biphenyls (PCBs) on hepatic microsomal ethoxyresorufin O-deethylase (EROD) activities and morphological parameters in matched double-crested cormorant (Phalacrocorax auritus) hatchlings from egg clutches chosen for chemical analysis. Double-crested cormorant eggs were collected from five colonies across Canada, with differing levels of contamination. Levels of contamination expressed in sum of 2,3,7,8-tetrachlorodibenzo-p-dioxin-toxic equivalents (TCDD-toxic equivalents or TEQ, ng/kg egg; mean +/- SEM) were: Saskatchewan, 250 +/- 50; Chain Islands, 672 +/- 73; Christy Islet, 276 +/- 14; Crofton, 131, n = 1; and Lake Ontario, 1606 +/- 118. In the hatchlings, hepatic EROD activities (pmol/min/mg protein; mean +/- SEM) were: Saskatchewan, 283 +/- 42; Chain Islands, 516 +/- 98; Christy Islet, 564 +/- 91; Crofton, 391 +/- 52; and Lake Ontario, 2250 +/- 156. Hepatic microsomal EROD activity (pmol/min/mg protein) regressed positively on TEQ (r2 = .69; p < .00005; n = 25). Yolk weight (g) regressed negatively on TEQ (r2 = .44; p = .00005). Wing length (mm) regressed negatively on PCB-169 (r2 = .28; p = .007). Monospecific antibodies raised against rat cytochrome P-450 1A1 recognized a protein in the hepatic microsomes of the double-crested cormorant, and also in those of the great blue heron (Ardea herodias), using immunoblotting. The intensity of the stained band increased with increased EROD activity, supporting the assumption that ethoxyresorufin is a suitable substrate for avian cytochrome P-450 1A1. These results validate the use of avian hepatic microsomal EROD activity as an index of cytochrome P-450 1A1 induction by environmental levels of polychlorinated aromatic hydrocarbons and as a useful screening tool to determine the extent of exposure to such chemicals. Furthermore, the induction of cytochrome P-450 1A1 observed in the cormorant indicates that the Ah receptor-mediated process, by which TCDD and related chemicals exert many of their toxicities, has been activated.

Methadone maintenance: Effect of urinary pH on renal clearance in chronic high and low doses

The subjects were 12 male patients stabilized on methadone for many months or years. A comparison was made of the plasma levels and renal clearance of methadone between patients on “high” doses (80 to 110 mg/day) and those on “low” doses (15 to 40 mg/day). A general trend to higher renal clearance was seen in the “high”‐dose group, but on more detailed examination there was a direct correlation only when the patients were categorized by urinary pH. At low pHs, there was nearly a 3‐fold increase in renal clearance which was associated with a decreased major metabolite to methadone ratio. No evidence for a difference in rate of metabolism between the two groups was found nor were there differences in hepatic function. It was concluded that urinary pH was a major factor in renal clearance of methadone.

Differential effects of diabetes on microsomal metabolism of various substrates: Comparison of streptozotocin and spontaneously diabetic wistar rats

We have examined the effect of recent onset diabetes on several aspects of hepatic microsomal metabolism in both streptozotocin (STZ)-induced and spontaneously diabetic BioBreeding (BB) male and female Wistar rats. Differential alterations of the diabetic state on hepatic microsomal enzyme activities were observed. Female diabetic rats exhibited no change in benzo [a]pyrene (BP) hydroxylase activity, a decrease in testosterone delta 4-hydrogenase, and an increase in aniline hydroxylase. On the other hand, male diabetic rats demonstrated a decrease in hepatic BP hydroxylase activity, no change in testosterone delta 4-hydrogenase, and an increase in aniline hydroxylase. Insulin treatment corrected these effects. No change in kidney BP hydroxylase activity was apparent in either female or male diabetics. There were no marked differences between the chemically induced and genetic models of diabetes with respect to the metabolism studies. Serum testosterone levels were significantly lower than control in male BB diabetics, whereas no change was apparent in female diabetics. Light microscopy and serum insulin determinations indicated that the spontaneously diabetic animals we examined were not severely diabetic. From electrophoresis of hepatic microsomal proteins we determined that spontaneous diabetes of short duration does alter the protein distribution in the cytochrome P-450 region. We conclude that the acute effects of STZ-induced and spontaneous diabetes on hepatic microsomal metabolism are quantitatively and qualitatively similar, despite probable differences in etiology of the diabetic state.

Studies on phosphorylase b kinase from neutral tissues.

Abstract— Phosphorylase b kinase (ATP: phosphorylase phosphotransferase; EC 2.7.1.38), the enzyme which converts phosphorylase b to phosphorylase a (α‐1,4‐glucan: orthophosphate glucosyltransferase; EC2.4.1.1) was examined in nerve tissue. Both phosphorylase and phosphorylase kinase were present in all nerve tissues tested, with central tissues about ten times as active as peripheral nerve. Exceptions were the superior cervical and stellate ganglia, tissues rich in synapses, which displayed activity similar to brain. Phosphorylase kinase in brain had properties similar to those of the enzyme in skeletal and cardiac muscle; it was activated in vitro by ATP and adenosine 3′,5′‐monophosphate (cyclic AMP) and by Ca2+. Subconvulsive doses of insulin or of amphetamine administered to mice produced some activation of the enzyme. It is concluded that the mechanism for activation of phosphorylase in nerve tissue is similar to that in muscle.

Growth hormone regulation and developmental expression of rat hepatic CYP3A18, CYP3A9, and CYP3A2

The present study investigated the role of growth hormone (GH) in hepatic CYP3A18 and CYP3A9 expression in prepubertal and adult male rats. For comparison, the effects of GH on CYP3A2 expression were also measured. Initial experiments demonstrated that CYP3A18 mRNA levels were greater during puberty and adulthood than during the prepubertal period, CYP3A9 mRNA was not expressed until puberty and its expression increased in adulthood, and CYP3A2 mRNA levels were relatively constant from prepuberty to adult life. Hypophysectomy, which results in the loss of multiple pituitary factors including GH, increased CYP3A2 and CYP3A18 mRNA expression 3- to 4-fold, but it did not affect CYP3A9 mRNA levels or CYP3A-mediated testosterone 2beta- or 6beta-hydroxylase activity in adult rats. GH administered as twice daily s.c. injections (0.12 microg/g body weight) to hypophysectomized or intact adult rats did not affect CYP3A18 or CYP3A9 mRNA expression. The same treatment decreased CYP3A2 mRNA and protein and testosterone 2beta- and 6beta-hydroxylase activity levels in intact but not hypophysectomized rats. However, in intact prepubertal rats, intermittent GH administration decreased CYP3A18 and CYP3A2 mRNA levels, but a higher dosage (3.6 microg/g) was required to suppress CYP3A2. Overall, the present study demonstrated that: (a) the constitutive expression of CYP3A18, CYP3A9, and CYP3A2 does not require the presence of GH, (b) CYP3A18 is more sensitive than CYP3A9 to GH modulation in adult rats; and (c) CYP3A2 is less sensitive to the suppressive influence of GH during the prepubertal period than during adult life.

Endocrine mediation of psychosocial stressor effects on mouse mammary tumor growth

We have demonstrated that differential housing alters the growth rate of the androgen-responsive Shionogi mouse mammary carcinoma (SC115). In the present study we wished to determine if changes in plasma levels of hormones or a shift in the responsiveness of the tumor cells to hormones was responsible for the differential tumor growth rates observed. Plasma testosterone and corticosterone levels were assayed 24 h, 3 days and 1 week post tumor cell/vehicle injection. Also 3 weeks post injection androgen and glucocorticoid receptor binding capacity (Bmax) and binding affinity (Kd) and the in vitro responsiveness of tumor cells to dihydrotestosterone and hydrocortisone were measured. At 24 h post injection, plasma testosterone levels were significantly increased in mice with large tumors, but remained low in mice with small tumors. Plasma corticosterone levels were significantly elevated in mice with small tumors compared to those of mice with large tumors at all time points measured. Androgen and glucocorticoid receptor binding capacity and binding affinity of tumor cells did not differ among groups. Further, all groups tested had the ability to respond to dihydrotestosterone and hydrocortisone in vitro. These data indicate that an effect of housing condition on plasma levels of steroid hormones may, in part, mediate the differential tumor growth rates observed in this model.

Elevation of Brain GABA Content by Chronic Low-Dosage Administration of Hydrazine, a Metabolite of Isoniazid

Abstract: When γ‐aminobutyric acid aminotransferase (GABA‐T) activity was measured in vitro in rat brain, neither isoniazid (INH) nor four of its known metabolites (isonicotinic acid, acetylisoniazid, acetylhydrazine, diacetylhydrazine) inhibited the enzyme in concentrations (5 mM) far higher than those likely to be achieved when INH is administered to man. In contrast, hydrazine (5 μM) caused a 50% inhibition of GABA‐T without inhibiting glutamic acid decarboxylase (GAD). Rats were injected daily for 109 days with hydrazine (0.08 or 0.16 mmol/kg/day), after which amino acid contents and enzyme activities were measured in their brains. Both hydrazine doses caused significant elevations of whole brain GABA content and reductions of GABA‐T activity, but did not affect GAD activity. Chronic administration of hydrazine at thee doses did not reduce weight gain or alter rat behavior, nor did it produce any irreversible pathologic changes in liver or alterations in hepatic aryl hydrocarbon hydroxylase activity. However, hydrazine treatment caused changes in the contents of many brain amino acids besides GABA, and markedly increased concentrations of ornithine, tyrosine, and α‐aminoadipic acid in rat plasma. Inhibition of GABA‐T activity and the other biochemical alterations observed in patients given high doses of INH probably result from hydrazine formed in the metabolic degradation of INH. Thus administration of hydrazine might be a more direct means of elevating brain GABA content in patients where this seems indicated, and might not entail a greater risk of adverse effects.