Comparative pulmonary toxicity inhalation and instillation studies with different TiO2 particle formulations: impact of surface treatments on particle toxicity.

Most pigment-grade titanium dioxide (TiO(2)) samples that have been tested in pulmonary toxicity tests have been of a generic variety-i.e., generally either uncoated particles or TiO(2) particles containing slightly hydrophilic surface treatments/coatings (i.e., base TiO(2)). The objectives of these studies were to assess in rats, the pulmonary toxicity of inhaled or intratracheally instilled TiO(2) particle formulations with various surface treatments, ranging from 0-6% alumina (Al(2)O(3)) or alumina and 0-11% amorphous silica (SiO(2)). The pulmonary effects induced by TiO(2) particles with different surface treatments were compared to reference base TiO(2) particles and controls. In the first study, groups of rats were exposed to high exposure (dose) concentrations of TiO(2) particle formulations for 4 weeks at aerosol concentrations ranging from 1130-1300 mg/m(3) and lung tissues were evaluated by histopathology immediately after exposure, as well as at 2 weeks and 3, 6, and 12 months postexposure. In the second study, groups of rats were intratracheally instilled with nearly identical TiO(2) particle formulations (when compared to the inhalation study) at doses of 2 and 10 mg/kg. Subsequently, the lungs of saline-instilled and TiO(2)-exposed rats were assessed using both bronchoalveolar (BAL) biomarkers and by histopathology/cell proliferation assessment of lung tissues at 24 h, 1 week, 1 and 3 months postexposure. The results from these studies demonstrated that for both inhalation and instillation, only the TiO(2) particle formulations with the largest components of both alumina and amorphous silica surface treatments produced mildly adverse pulmonary effects when compared to the base reference control particles. In summary, two major conclusions can be drawn from these studies: (1) surface treatments can influence the toxicity of TiO(2) particles in the lung; and (2) the intratracheal instillation-derived, pulmonary bioassay studies represent an effective preliminary screening tool for inhalation studies with the identical particle-types used in this study.

Developmental toxicity and genotoxicity studies of 1,1,1,3,3,3-hexachloropropane (HCC-230fa) in rats.

The potential developmental toxicity and the in vitro and in vivo genotoxicity of HCC-230fa were assessed. In the developmental toxicity study, groups of 25 mated Crl:CD(R)(SD)BR rats were exposed (whole body) by inhalation to HCC-230fa over days 7-21 of gestation; the day of confirmed mating was designated as gestation day 1 (GD1). Exposures were 6 h per day at concentrations of 0, 0.5, 2.5, or 25 ppm. Body weight, food consumption, and clinical observation data were collected during the study. On day 22 of gestation, the dams were euthanized and examined grossly. The fetuses were removed and subsequently weighed, sexed, and examined for external, visceral, head, and skeletal alterations. Evidence of maternal and developmental toxicity was observed at 25 ppm and was noted as significant, compound-related reductions in mean maternal body weight, weight change, and food consumption. Significant fetal effects also were observed at 25 ppm as compound-related reductions in mean fetal weight and increased fetal malformations (filamentous tail, situs inversus, absent vertebrae) and variations (rudimentary cervical ribs, delayed sternebral ossification). There was no evidence of either maternal or developmental toxicity at 0.5 or 2.5 ppm. The genotoxicity of HCC-230fa was examined in a bacterial reversion assay and in erythrocyte micronucleus studies in two species by different routes of administration. No increases in the number of revertants were observed in the bacterial reversion assay. In one micronucleus study, HCC-230fa was administered by inhalation to rats as part of a 90-day study at doses indicated above. For the second study, ICR mice were given a single ip dose at 0, 166, 330, or 660 mg/kg. In both micronucleus studies, a significant increase in micronucleated erythrocytes was observed. The results of these studies suggest that HCC-230fa affects rapidly dividing cells and may have long-term consequences for occupational exposures.

Effects of HCFC-123 exposure to maternal and infant rhesus monkeys on hepatic biochemistry, lactational parameters and postnatal growth.

Peroxisome proliferators are a class of nongenotoxic rodent hepatocarcinogens that cause peroxisome proliferation and liver tumors when administered to rats and mice; but other species, including guinea pigs, dogs, and primates are less sensitive or refractory to the induction of peroxisome proliferation. Therefore, rodent peroxisome proliferators are not believed to pose a hepatocarcinogenic hazard to humans. Some peroxisome proliferators produce developmental toxicity in rats that is expressed as suppressed postnatal growth. To evaluate the relevance of the rat developmental effect to primates, groups of 4 lactating female Rhesus monkeys and their infants were exposed for 6 h/day, 7 days/week for 3 weeks to air or 1000 ppm HCFC-123. Animals were evaluated for clinical signs, body weights, clinical pathology parameters, and biochemical and pathological evaluations of liver biopsy samples. The effect of HCFC-123 exposure on milk quality (protein and fat concentration) was evaluated. The concentrations of HCFC-123 and the major metabolite, trifluoroacetic acid (TFA), were measured in the blood of the mothers and infants and in the milk. Exposure of monkeys to 1000 ppm HCFC-123 did not result in exposure-related clinical observations, or changes in body weight, appetence and behavior. There were no exposure-related effects on serum triglycerides, cholesterol, or glucose levels. HCFC-123 and TFA were present in milk, although maternal HCFC-123 exposure did not affect milk protein and fat content. In general, HCFC-123 was not detected in maternal or infant blood. TFA was detected in the majority of the mothers and TFA levels in infants ranged from 2 to 6 times higher than levels in the corresponding maternal blood. A pharmacokinetic analysis in a maternal animal indicated a peak concentration of TFA at approximately 1 h post-exposure, with a half-life of approximately 20 h. Liver microsomal P450 and peroxisome oxidase activities showed exposure-related decreases in CYP4A1 and CYP2E1 and acyl-CoA oxidase for animals exposed to HCFC-123. Microscopic evaluation of maternal liver from HCFC-123 exposed animals revealed mild to moderate centrilobular hepatocyte vacuolation, trace to mild centrilobular necrosis, and trace to mild subacute inflammation. The histopathological damage and altered hepatic biochemical activities produced by HCFC-123 in monkeys are not consistent with the HCFC-123 peroxisome proliferation response observed in rat livers. These findings demonstrate that HCFC-123 is not a peroxisome proliferator in adult Rhesus monkeys and postnatal exposure to HCFC-123 does not affect body weight of nursing infant monkeys.

Subchronic inhalation toxicity of the chlorinated propane 1,1,1,3,3,3-hexachloropropane (HCC-230fa).

Male and female rats were exposed by inhalation (whole body) to HCC-230fa (1,1,1,3,3,3-hexachloropropane) for 6 h/day, 5 days/week over a 15-week period. Concentrations of 0, 0.50, 2.5, and 25 ppm were studied. A total of eight groups/sex were exposed. Four groups of male and four groups of female rats were used to measure clinical signs and growth, clinical pathology, and tissue pathology. The remaining four groups of male rats were used for immunotoxicological and sperm assessment evaluations, and the remaining four groups of female rats were used for immunotoxicological evaluation. Following the exposure period, surviving male rats were kept for a 1- or 3-month recovery period. Male and female rats exposed to 25 ppm had lower mean body weights, mean body weight gains, and food consumption during the exposure period. Male and female rats exposed to 25 ppm and sacrificed immediately after the exposure period had minimally decreased total leukocyte and lymphocyte counts. These changes were considered to be marginally adverse. Pathologic examination revealed hepatocellular hypertrophy in 0-day recovery males and an increased incidence and/or severity in chronic progressive nephropathy in 0-day, 1-month recovery, and 3-month recovery males at 25 ppm. No other pathological changes, including the testis, epididymis, and other accessory sex organs, were noted in rats during the study. Evaluation of sperm parameters at the end of the exposure period showed statistically significant decreases in epididymal sperm number per cauda epididymis, percent motile sperm, and percent normal sperm morphology at 25 ppm. The biological significance of the slight changes observed in the sperm parameters in the absence of histopathological changes is unclear. After a 1-month recovery period, no biologically significant differences in sperm parameters were noted at 25 ppm compared with controls. Exposure to HCC-230fa did not significantly alter the primary humoral immune response to sheep red blood cell (SRBC). Under the conditions of this study, the no-observed-adverse-effect level (NOAEL) was considered to be 2.5 ppm.

Setting safe acute exposure limits for halon replacement chemicals using physiologically based pharmacokinetic modeling.

Most proposed replacements for Halon 1301 as a fire suppressant are halogenated hydrocarbons. The acute toxic endpoint of concern for these agents is cardiac sensitization. An approach is described that links the cardiac endpoint as assessed in dogs to a target arterial concentration in humans. Linkage was made using a physiologically based pharmacokinetic (PBPK) model. Monte Carlo simulations, which account for population variability, were used to establish safe exposure times at different exposure concentrations for Halon 1301 (bromotrifluoromethane), CF(3)I (trifluoroiodomethane), HFC-125 (pentafluoroethane), HFC-227ea (1,1,1,2,3,3,3-heptafluoropropane), and HFC-236fa (1,1,1,3,3,3-hexafluoropropane). Application of the modeling technique described here not only makes use of the conservative cardiac sensitization endpoint, but also uses an understanding of the pharmacokinetics of the chemical agents to better establish standards for safe exposure. The combined application of cardiac sensitization data and physiologically based modeling provides a quantitative approach, which can facilitate the selection and effective use of halon replacement candidates.

Inhalation toxicity and genotoxicity of hydrochlorofluorocarbon (HCFC)-225ca and HCFC-225cb.

The acute, subchronic and genetic toxicity of the hydrochlorofluorocarbons HCFC-225ca and HCFC-225cb were evaluated to assist in establishing proper handling guides. In acute inhalation studies, rats were exposed for 4 h to various concentrations of each isomer. Based on the mortality incidence, the LC50 value for HCFC-225cb for males and females (combined) was 36800 ppm. For HCFC-225ca, the LC50 for males and females (combined) was 37300 ppm. Narcotic-like effects, e.g. prostration, incoordination and reduced motor activity, were observed during exposure to either isomer, but these signs were not evident 15 min after termination of exposure. Histopathological examination of the liver revealed an increase in mitotic figures with vacuolation of hepatocytes and fluid-filled, congested hepatic sinusoids. In cardiac sensitization studies, HCFC-225cb induced a cardiac sensitization response at 20000 ppm, with one fatal response, whereas a blend of the two isomers (45% HCFC-225ca/55% HCFC-225cb) produced a cardiac sensitization response at 15000 ppm. In 4-week subchronic inhalation studies, male and female rats were whole-body exposed to HCFC-225cb at concentrations of 0, 1000, 5000 or 15000 ppm for 6 h a day, 5 days per week. Similarly, male and female rats were whole-body exposed to HCFC-225ca concentrations of 0, 50, 500 or 5000 ppm for 6 h a day, 5 days per week. During exposure, narcotic-like and irritant effects were observed. A dose-related decrease in cholesterol and triglycerides was observed in the treated rats, with males being affected more than females. Increases in liver weight were observed in most male and female rats exposed to either isomer. The increase in liver weight was consistent in male rats with microscopic evidence of hepatocyte hypertrophy. Although liver weight was increased in female rats, no hepatocyte enlargement was observed in treated female rats. Increases in cytochrome P-450 and beta-oxidation activities were also observed in male and female rats exposed to either isomer. Neither of the HCFC-225 isomers was mutagenic in the Ames reverse mutation assay, or clastogenic in the chromosomal aberration assay with Chinese hamster lung cells. Also, neither isomer induced unscheduled DNA synthesis in liver cells. However, both isomers were clastogenic in the chromosomal aberration assay with human lymphocytes in the absence of S-9. No increases in aberrant cells were observed in activated cells exposed to either isomer.

1,1,1-Trifluoro-2,2-dichloroethane (HCFC-123) and 1,1,1-trifluoro-2-bromo-2-chloroethane (halothane) cause similar biochemical effects in rats exposed by inhalation for five days.

1,1,1-Trifluoro-2,2-dichloroethane (HCFC-123) and 1,1,1-trifluoro-2-bromo-2 chloroethane (halothane) are gases with anesthetic properties. HCFC-123 is used as a refrigerant, fire extinquishing agent, and solvent, while halothane is a clinical anesthetic. Much information is available on chronic toxicity of HCFC-123 in animals, while the information available for halothane is from short-term animal exposures or chronic, low level human exposures. Thus, there is little biochemical information available on similar endpoints for these two chemicals, which share common metabolites. In the present study, male rats were exposed to 5000 ppm HCFC-123, 5000 ppm halothane, or room air for 6 hr per day for 5 consecutive days. Rats exposed to both test compounds gained little or no weight during the study. Liver weights were slightly decreased in the rats exposed to HCFC-123 and halothane compared to controls. The serum triglycerides were decreased to approximately 20% of control level in rats exposed to both HCFC-123 and halothane, and serum cholesterol was decreased to less than 80% of control by both compounds. Both test compounds increased hepatic beta-oxidation by approximately 3-fold over control, and HCFC-123 caused a significant increase in hepatic cytochrome P450 content, while the increase in cytochrome P450 was not statistically significant in the halothane-treated rats. The results indicate that HCFC-123 and halothane share not only common metabolic pathways, but also several common biological effects, specifically those associated with peroxisome proliferation. These data indicate that human experience with halothane may be useful in the risk assessment of HCFC-123.

Chronic toxicity, oncogenicity, and mutagenicity studies with chlorotetrafluoroethane (HCFC-124).

The chronic toxicity, oncogenicity, and mutagenicity of chlorotetrafluoroethane (HCFC-124) were evaluated. In the chronic toxicity/oncogenicity study, male and female rats were exposed to 0, 2000, 10,000, or 50,000 ppm HCFC-124 for 6 hr/day, 5 days/week, for 2 years. Body weights were obtained weekly during the first three months of the study and every other week for the remainder of the study. Food consumption was determined weekly. Clinical signs of toxicity were monitored throughout the study. An ophthalmological examination was performed on all animals prior to study start, and all surviving rats were examined at approximately 3, 12, and 24 months after study start. Clinical pathology was evaluated at 3, 6, 12, 18, and 24 months. An interim termination was conducted at 12 months. All surviving rats were necropsied at 24 months. A complete set of tissues was collected for microscopic examination, and selected tissues were weighed. There were no compound-related, adverse effects on body weight, food consumption, survival, clinical signs of toxicity, ophthalmoscopically observable ocular lesions, serum hormone concentrations, or clinical pathology parameters at any exposure concentration in either male or female rats. Compared to controls, urine fluoride was increased in males and females at all exposure concentrations, and plasma fluoride was increased in females at all exposure concentrations. Excretion of fluoride represents conversion of the parent molecule, and as such is not considered to be an adverse effect. There were no toxicologically significant, compound-related organ weight changes or gross or microscopic findings in male or female rats at any of the exposure concentrations tested. HCFC-124 was not toxic or carcinogenic in rats of either sex after inhalation exposure at concentrations of up to 50,000 ppm in this two-year chronic toxicity/oncogenicity study. After exposure to HCFC-124 for six hours per day, five days per week, for 24 months, the no-observed-adverse-effect level for male and female rats was 50,000 ppm. HCFC-124 was not mutagenic in Salmonella typhimurium strains TA1535, TA97, TA98, and TA100 with and without activation when evaluated at concentrations up to 60% HCFC-124 for 48 hours. No evidence of clastogenic activity was observed in cultured human lymphocytes at atmospheric concentrations up to 100% HCFC-124 for 3 hours, with and without metabolic activation. In vivo, no micronuclei were induced in mouse bone marrow cells following exposure of mice to concentrations of 99,000 ppm HCFC-124 6 hours/day for 2 days.

Acute, subchronic, and developmental toxicity and genotoxicity of 1,1,1-trifluoroethane (HFC-143a).

The toxicity potential of 1,1,1-trifluoroethane (HFC-143a), a CFC alternative, was evaluated in several acute, subchronic, and developmental toxicity studies by the inhalation route and in genotoxicity studies. HFC-143a has a very low acute inhalation toxicity potential as shown by a 4-hr LC50 of > 540,000 ppm in rats. HFC-143A has a low potential to induce cardiac sensitization in experimental screening studies in dogs; only the highest concentration tested--300,000 ppm--elicited a cardiac sensitization response. In an initial 4-week nose-only inhalation study, male and female rats were exposed 6 hr/day, 5 days/week at concentrations of 0, 2000, 10,000, or 40,000 ppm. Females showed no evidence of toxicity at any exposure level; male rats did exhibit degenerative changes only in the tests at all exposure levels. However, because of exposure system irregularities, which resulted in excessive temperature conditions and stress in the HFC-143a-exposed groups, the study was repeated in male rats exposed by whole-body inhalation. In this repeat study no toxicity was observed at < or = 40,000 ppm. Moreover, a subsequent 90-day whole-body inhalation study in rats exposed 6 hr/day, 5 days/week at 0, 2000, 10,000, or 40,000 ppm resulted in no evidence of toxicity at any exposure concentration. The results of the second 4-week and the 90-day studies using whole-body exposures indicate that the findings from the first 4-week study were related to the stress induced by excessive temperatures and nose-only restraint. Therefore, the no-observed-effect level (NOEL) for rats repeatedly exposed up to 90 days was considered to be 40,000 ppm. In developmental toxicity studies with rats and rabbits, an increase in visceral variations or skeletal malformations was observed, respectively, at HFC-143a concentrations of 2000, 10,000 or 40,000 ppm (rat) or at the low and high concentrations (rabbit). Because of the unusually low control incidence of variations (1.6% per litter in the control versus 6.8-16.8% for historical control values), the lack of a clear dose-response relationship, and the lack of other developmental effects, these findings were not considered related to HFC-143a exposure. In addition, results from genotoxicity studies (Ames, chromosomal aberration with human lymphocytes, mouse micronucleus) demonstrated that HFC-143a was not mutagenic.

Acute and subchronic toxicity of 1,1-dichloro-1-fluoroethane (HCFC-141b).

The acute and subchronic toxicity of 1,1-dichloro-1-fluoroethane (HCFC-141b), a CFC alternative, was evaluated in several acute and subchronic studies to assist in establishing proper handling guides. Data from acute toxicity studies in rats and rabbits demonstrated that HCFC-141b has very low acute toxicity. HCFC-141b was not a skin irritant, but was a mild eye irritant, in rabbits and was not a skin sensitizer in guinea pigs. Skin application of HCFC-141b to rabbits at 2000 mg/kg body weight produced no adverse effects. Oral administration at 5000 mg/kg body weight did not cause any deaths or clinical signs of toxicity in rats. The 4-hr LC50 for HCFC-141b was about 62,000 ppm in rats. Repeated exposures of rats for 6 hr/day, 5 days/wk for up to 90 days at concentrations of 2000, 8000 or 20,000 ppm did not result in significant adverse effects. Minor, but dose-dependent, reductions in body weight were observed in male and female rats during the 90-day study. Decreased responsiveness was also observed in rats but only at 20,000 ppm. An increase in serum cholesterol or triglycerides was observed in male and female rats at 20,000 ppm, and in males at 8000 ppm. No specific organ pathology was noted in these subchronic inhalation studies. The no-observable-adverse-effect level (NOAEL) from these studies was 8000 ppm. Results from other studies demonstrate that HCFC-141b was not neurotoxic in rats. As with trichlorofluoroethane (CFC-11), a cardiac sensitization response to an intravenous epinephrine challenge occurred in dogs with HCFC-141b at 5000 ppm and higher concentrations in experimental screening studies.

Hepatic macromolecular binding and tissue distribution of ortho- and para-toluidine in rats.

The in vivo covalent binding of ortho- and para-toluidine (OT and PT) to rat hepatic macromolecules was investigated to determine if a relationship exists between the degree of binding for each isomer and its carcinogenic potency. The ortho-isomer has been shown to be a more potent hepatocarcinogen than the para-isomer. In addition to the macromolecular binding, the tissue distribution of each isomer was also measured. The degree of binding to hepatic macromolecules appeared to be at maximum for both at 24 28 h following dosing. At 24 h following dosing, the level of DNA binding of OT was approximately 1.2-fold lower than that of PT. The binding to RNA and protein was also lower for OT than PT, although the differences were not as great as that observed for DNA binding. There were subtle differences in tissue distribution for each isomer. However, in contrast to the macromolecular binding data, the area under the plasma concentration curve for OT was approximately 1.8-fold greater than that for PT. Based on the results of these studies, there was no direct correlation between the degree of macromolecular binding and carcinogenic potency.

Characterization of covalent binding of N'-nitrosonornicotine in rat liver microsomes.

The metabolism of the carcinogenic nitrosamine, N'-nitrosonornicotine (NNN), to reactive intermediates which bind covalently was assessed using male Sprague-Dawley rat liver microsomes. The NADPH-dependent covalent binding of [14C]NNN was linear with time up to 90 min and protein concentration up to 3.0 mg/ml. The apparent Km and Vmax of the binding were determined from the initial velocities and found to be 0.91 mM and 4.7 pmol/min/mg protein, respectively. Although NNN is not a hepatocarcinogen, this amount of NADPH-dependent covalent binding is 7-fold greater than that reported for dimethylnitrosamine, a potent hepatocarcinogen. Extensive covalent binding of [14C]NNN to liver and muscle microsomal protein was also present in the absence of an NADPH-generating system and in the presence of 50% methanol, indicating a non-enzymatically mediated reaction. Addition of the nucleophiles glutathione, cysteine and N-acetylcysteine significantly decreased (p less than 0.01) the non-NADPH-dependent binding, but did not affect NADPH-dependent binding. In vitro addition of the cytochrome P-450 inhibitors metyrapone, piperonyl butoxide and SKF-525A significantly decreased (p less than 0.05) NADPH-dependent binding of [14C]NNN by 27-40%. NADH did not replace NADPH in supporting covalent binding. Replacement of an air atmosphere with nitrogen or CO:O2 (8:2) significantly decreased (p less than 0.05) NADPH-dependent binding of [14C]NNN by 40 and 27%, respectively. Aroclor 1254 pre-treatment of the rats did not enhance the NADPH-dependent binding of [14C]NNN. These data indicate that cytochrome P-450 is at least in part responsible for the metabolic activation of the carcinogen NNN but also suggest additional mechanisms of activation.

The effect of pregnancy and treatment with 17 beta-estradiol on the transport of organic anions into isolated rat hepatocytes.

The uptake of the bile acid taurocholate (TC), and the organic anions, estradiol-17 beta (beta-D-glucuronide) (E217G), estradiol-3-(beta-D-glucuronide) (E23G), estriol-16 alpha (beta-D-glucuronide) (E316G), and morphine glucuronide (MG) were evaluated in hepatocytes isolated from nonpregnant female, pregnant (19-21 days of gestation) and E2-treated (1 mg/kg/day sc for 14 days) rats. Pregnancy significantly decreased the uptake of TC, E217G, E23G, and MG whereas E2 treatment decreased only the uptake of E217G. The Vmax (nmol/min/mg protein) for E217G uptake was significantly decreased from 1.45 +/- 0.2 (mean +/- SE) in hepatocytes from nonpregnant female rats to 0.70 +/- 0.11 and 0.64 +/- 0.13 in cells from pregnant and E2-treated rats, respectively. The Vmax for uptake of TC was decreased, but not significantly, from 0.56 +/- 0.16 in hepatocytes from nonpregnant female rats to 0.34 +/- 0.08 in cells from pregnant rats.

Characterization of the interaction between estrogen metabolites and taurocholate for uptake into isolated hepatocytes. Lack of correlation between cholestasis and inhibition of taurocholate uptake.

The cholestasis induced by estrogen metabolites has been postulated to be due to an inhibition of bile acid transport. Therefore, the uptake of [3H]taurocholate (TC) into isolated hepatocytes was examined in the presence of known cholestatic steroid glucuronides. The cholestatic D-ring glucuronide conjugates of estradiol, estriol, ethynylestradiol and dihydrotestosterone did not inhibit the uptake of TC suggesting that these organic anions are transported by different carrier systems. Estrone sulfate inhibited TC uptake 65% but did not decrease bile flow following i.v. administration to the rat (22 mumol/kg), under conditions which the steroid glucuronide estradiol-17 beta-(beta-D-glucuronide) ( E217G ) decreased bile flow 100%. The hepatocytic uptake of [3H] E217G (100 microM) was inhibited by estriol-16 alpha-(beta-D-glucuronide) (200 microM, 40%) and estradiol-17 beta-3-(beta-D-glucuronide) (200 microM, 22%) as well as by the organic anions bromosulfophthalein (150 microM, 57%), dibromosulfophthalein (150 microM, 59%), indocyanine green (150 microM, 62%), rose bengal (150 microM, 56%) and bilirubin (50 microM, 40%). Thus, the bile acids and steroid glucuronides are transported into the hepatocyte by different carrier systems so that the cholestasis induced by the steroid D-ring glucuronides cannot be explained by an inhibition of bile acid uptake. Furthermore, the hepatocytic uptake of E217G occurs by a carrier system similar to that for the other steroid glucuronides and organic anions.

Characterization of uptake of steroid glucuronides into isolated male and female rat hepatocytes.

The uptake of estradiol-17 beta(beta-D-glucuronide) (E(2)17G), estriol-16 alpha(beta-D-glucuronide (E(3)16G), estradiol-17 beta-3-(beta-D-glucuronide) (E(2)3G) and taurocholate (TC) into hepatocytes isolated from male and female rats was examined and found to be linear for at least 75 sec and to exhibit Michaelis-Menten kinetics. The Vmax (nanomoles per minute per milligram of protein) for uptake in female rat hepatocytes ranged from 0.56 for TC to 2.32 for E(3)16G and from 0.89 for TC to 1.62 for E(2)17G in males. For TC, E(2)17G and E(2)3G, the Vmax for uptake was the same or higher in males, whereas for E(3)16G the Vmax was approximately 2-fold higher in females. The Km for TC was approximately equal in males and females, whereas for E(2)17G and E(3)16G, males exhibited a 3- to 9-fold lower Km. The rate of uptake of E(2)17G (100 microM) was decreased in the presence of carbonylcyanide-m-chlorophenylhydrazone (23%), 2,4-dinitrophenol (54%), potassium cyanide (38%), iodoacetic acid (46%) and rotenone (50%) and was reduced by 30 to 40% when sodium was replaced with lithium or choline or in the presence of ouabain. The rate of uptake of all the organic anions was reduced by 80 to 85% at 0-4 degrees C and the cell/medium concentration ratios at 75 sec (37 degrees C) exceeded 1. Thus, the steroid glucuronides are taken up by the hepatocyte by a saturable process; E(2)17G uptake was found to be partially dependent upon metabolic energy and an intact sodium gradient. Substrate-dependent differences in the rate of uptake between male and female rat hepatocytes were also seen.

Hepatic morphine and estrone glucuronyltransferase activity and morphine biliary excretion in the isolated perfused rat liver. Effect of pregnancy and estradiol-17 beta treatment.

Hepatic microsomal estrone and morphine glucuronyltransferase activity and the biliary excretion of morphine in the isolated perfused liver were examined in nonpregnant, pregnant (19-21 days of gestation), and estradiol-17 beta-treated (E2; 1.0 mg/kg/day sc for 14 days) rats. Pregnancy decreased estrone and morphine glucuronyltransferase activity 20%, whereas E2 treatment increased activity 50%. Treatment of nonpregnant and pregnant rats with 2,3,7,8-tetrachlorodibenzo-p-dioxin (3 micrograms/kg po) increased estrone glucuronyltransferase activity 1.3- and 2.8-fold respectively, but such treatment had no effect in E2-treated rats. In the isolated perfused liver, E2 treatment, but not pregnancy, decreased the biliary excretion of morphine 3-glucuronide. Bile flow (microliter/min/g of liver) was slightly decreased by pregnancy but not by E2 treatment. Maximal bile/perfusate concentration ratios of morphine glucuronide were 175, 325, and 90 in livers from nonpregnant, pregnant, and E2-treated rats, respectively.