Toxicological evaluation of ammonium perfluorobutyrate in rats: twenty-eight-day and ninety-day oral gavage studies

Sequential 28-day and 90-day oral toxicity studies were performed in male and female rats with ammonium perfluorobutyrate (NH(4)(+)PFBA) at doses up to 150 and 30mg/kg-d, respectively. Ammonium perfluorooctanoate was used as a comparator at a dose of 30mg/kg-d in the 28-day study. Female rats were unaffected by NH(4)(+)PFBA. Effects in males included: increased liver weight, slight to minimal hepatocellular hypertrophy; decreased serum total cholesterol; and reduced serum thyroxin with no change in serum thyrotropin. During recovery, liver weight, histological, and cholesterol effects were resolved. Results of RT-qPCR were consistent with increased transcriptional expression of the xenosensor nuclear receptors PPARα and CAR as well as the thyroid receptor, and decreased expression of Cyp1A1 (Ah receptor-regulated). No observable adverse effect levels (NOAELs) were 6 and >150mg/kg-d for male and female rats in the 28-day study and 6 and >30mg/kg-d in the 90-dat study, respectively.

A comparison of the pharmacokinetics of perfluorobutanesulfonate (PFBS) in rats, monkeys, and humans

Materials derived from perfluorobutanesulfonyl fluoride (PBSF, C(4)F(9)SO(2)F) have been introduced as replacements for eight-carbon homolog products that were manufactured from perfluorooctanesulfonyl fluoride (POSF, C(8)F(17)SO(2)F). Perfluorobutanesulfonate (PFBS, C(4)F(9)SO(3)(-)) is a surfactant and potential degradation product of PBSF-derived materials. The purpose of this series of studies was to evaluate the pharmacokinetics of PFBS in rats, monkeys, and humans, thereby providing critical information for human health risk assessment. Studies included: (1) intravenous (i.v.) elimination studies in rats and monkeys; (2) oral uptake and elimination studies in rats; and (3) human serum PFBS elimination in a group of workers with occupational exposure to potassium PFBS (K(+)PFBS). PFBS concentrations were determined in serum (all species), liver (rats), urine (all species), and feces (rats). In rats, the mean terminal serum PFBS elimination half-lives, after i.v. administration of 30mg/kg PFBS, were: males 4.51+/-2.22h (standard error) and females 3.96+/-0.21h. In monkeys, the mean terminal serum PFBS elimination half-lives, after i.v. administration of 10mg/kg PFBS, were: males 95.2+/-27.1h and females 83.2+/-41.9h. Although terminal serum half-lives in male and female rats were similar, without statistical significance, clearance (CL) was significantly greater in female rats (469+/-40mL/h) than male rats (119+/-34mL/h) with the area under the curve (AUC) significantly larger in male rats (294+/-77microg.h/mL) than female rats (65+/-5microg.h/mL). These differences were not observed in male and female monkeys. Volume of distribution estimates suggested distribution was primarily extracellular in both rats and monkeys, regardless of sex, and urine appeared to be a major route of elimination. Among 6 human subjects (5 male, 1 female) followed up to 180 days, the geometric mean serum elimination half-life for PFBS was 25.8 days (95% confidence interval 16.6-40.2). Urine was observed to be a pathway of elimination in the human. Although species-specific differences exist, these findings demonstrate that PFBS is eliminated at a greater rate from human serum than the higher chain homologs of perfluorooctanesulfonate (PFOS) and perfluorohexanesulfonate (PFHxS). Thus, compared to PFOS and PFHxS, PFBS has a much lower potential for accumulation in human serum after repeated occupational, non-occupational (e.g., consumer), or environmental exposures.

Toxicological evaluation of potassium perfluorobutanesulfonate in a 90-day oral gavage study with Sprague-Dawley rats

Perfluorobutanesulfonate (PFBS) is a surfactant and degradation product of substances synthesized using perfluorobutanesulfonyl fluoride. A 90-day rat oral gavage study has been conducted with potassium PFBS (K+PFBS). Rats were dosed with K+PFBS at doses of 60, 200, and 600mg/kg-day body weight. The following endpoints were evaluated: clinical observations, food consumption, body weight, gross and microscopic pathology, clinical chemistry, and hematology. In addition, functional observation battery and motor activity assessments were made. Histological examination included tissues in control and 600 mg/kg-day groups. Additional histological examinations were performed on nasal cavities and turbinates, stomachs, and kidneys in the 60 and 200 mg/kg-day groups. No treatment-related mortality, body weight, or neurological effects were noted. Chromorhinorrhea (perioral) and urine-stained abdominal fur were observed in males at 600mg/kg-day. Red blood cell counts, hemoglobin, and hematocrit values were reduced in males receiving 200 and 600mg/kg-day; however, there were no adverse histopathological findings in bone marrow. Total protein and albumin were lower in females at 600mg/kg-day. There were no significant changes in clinical chemistry in either sex. All rats appeared normal at sacrifice. Microscopic changes were observed only at the highest dose in the stomach. These changes consisted of hyperplasia with some necrosis of the mucosa with some squamous metaplasia. These effects likely were due to a cumulative direct irritation effect resulting from oral dosing with K+PFBS. Histopathological changes were also observed in the kidneys. The changes observed were minimal-to-mild hyperplasia of the epithelial cells of the medullary and papillary tubules and the ducts in the inner medullary region. There were no corresponding changes in kidney weights. Clinical chemistry parameters related to kidney function were unchanged. These kidney findings are likely due to a response to high concentration of K+PFBS in tubules and ducts and represent a minimal-to-mild effect. Microscopic changes of an equivocal and uncertain nature were observed in the nasal mucosa and were likely attributable to the route of dosing (oral gavage). The NOAEL for the female rat in this study was 600 mg/kg-day (highest dose of study). The NOAEL for the male rat was 60 mg/kg-day based on hematological effects.

Pharmacokinetics of perfluorooctanoate in cynomolgus monkeys

The pharmacokinetics of perfluorooctanoate (PFOA) in cynomolgus monkeys were studied in a six-month oral capsule dosing study of ammonium perfluorooctanoate (APFO) and in a single-dose iv study. In the oral study, samples of serum, urine, and feces were collected every two weeks from monkeys given daily doses of either 0, 3, 10, or 20 mg APFO/kg. Steady-state was reached within four weeks in serum, urine, and feces. Serum PFOA followed first-order elimination kinetics after the last dose, with a half-life of approximately 20 days. Urine was the primary elimination route. Mean serum PFOA concentrations at steady state in the 3, 10, and 20 mg/kg-day dose groups, respectively, were 81, 99, and 156 microg/ml in serum; 53, 166, and 181 microg/ml in urine; and, 7, 28, and 50 microg/g in feces. Mean liver concentrations reached 16, 14, and 50 microg/g in the 3, 10, and 20 mg/kg groups, respectively. In the iv study, three monkeys per sex were given a single dose of 10 mg/kg potassium PFOA. Samples were collected through 123 days. The terminal half-life of PFOA in serum was 13.6, 13.7, and 35.3 days in the three male monkeys and 26.8, 29.3, and 41.7 days in the three females. Volume of distribution at steady state was 181 +/- 12 and 198 +/- 69 ml/kg for males and females, respectively. Based on the result of both the oral and iv studies, the elimination half-life is approximately 14-42 days, and urine is the primary route of excretion.

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.

A novel method to determine uptake and elimination kinetics of volatile chemicals in fish

The development of an exposure system suitable for studying the uptake and elimination kinetics in fish of volatile chemicals is discussed. Static exposure of the fish is in a closed system containing water and air. Automated sampling and analysis of the air provides a concentration-time profile that is then fit to differential equations using numerical integration methods. Assumptions for the mathematical description of the system are a) instantaneous distribution of chemical between water and air and b) a first order one-compartment model describes the kinetics of chemical in fish. Uptake and elimination rate constants in fathead minnows (Pimephales promelas) were determined for a mixture of benzene, toluene, monochlorobenzene, monobromobenzene, and 1,3-dichlorobenzene. No significant biotransformation was observed for any of the compounds. Uptake rate constants increased with increasing octanol-water partition coefficient (Kow), whereas the elimination rate constants were inversely related to Kow.

Fluoroacetate-mediated toxicity of fluorinated ethanes

A series of 1-(di)halo-2-fluoroethanes reported in the literature to be nontoxic or of low toxicity were found to be highly toxic by the inhalation route. Experiments were performed that showed the compounds, 1,2-difluoroethane, 1-chloro-2-fluoroethane, 1-chloro-1,2-difluoroethane, and 1-bromo-2-fluoroethane to be highly toxic to rats upon inhalation for 4 hr. All four compounds had 4-hr approximate lethal concentrations of < or = 100 ppm in rats. In contrast, 1,1-difluoroethane (commonly referred to as HFC-152a) has very low acute toxicity with a 4-hr LC50 of > 400,000 ppm in rats. Rats exposed to the selected toxic fluoroethanes showed clinical signs of fluoroacetate toxicity (lethargy, hunched posture, convulsions). 1,2-Difluoroethane, 1-chloro-2-fluoroethane, 1-chloro-1,2-difluoroethane, and 1-bromo-2-fluoroethane were shown to increase concentrations of citrate in serum and heart tissue, a hallmark of fluoroacetate intoxication. 19F NMR analysis confirmed that fluoroacetate was present in the urine of rats exposed to each toxic compound. Fluorocitrate, a condensation product of fluoroacetate and oxaloacetate, was identified in the kidney of rats exposed to 1,2-difluoroethane. There was a concentration-related elevation of serum and heart citrate in rats exposed to 0-1000 ppm 1,2-fluoroethane. Serum citrate was increased up to 5-fold and heart citrate was increased up to 11-fold over control citrate levels. Metabolism of 1,2-difluoroethane by cytochrome P450 (most likely CYP2E1) is suspected because pretreatment of rats or mice with SKF-525F, disulfiram, or dimethyl sulfoxide prevented or delayed the toxicity observed in rats not pretreated. Experimental evidence indicates that the metabolism of the toxic fluoroethanes is initiated at the carbon-hydrogen bond, with metabolism to fluoroacetate via an aldehyde or an acyl fluoride. The results of these studies show that 1-(di)halo-2-fluoroethanes are highly toxic to rats and should be considered a hazard to humans unless demonstrated otherwise.

Development of a biomonitoring assay for ortho-toluidine or its metabolites in human urine

We describe a method for the measurement of a metabolite of ortho-toluidine in urine. The method uses capillary gas chromatographic separation with mass spectrometric detection to quantitate the metabolite, and it requires no derivatization or extraction of the urine sample prior to analysis. Quantitation is accomplished by comparison with a control spiked with a standard of the metabolite. The coefficient of variation for day-to-day reproducibility of the assay was 9.7%. The limit of quantitation was 10 micrograms/L (10 parts per billion).

Dimethylacetamide pharmacokinetics following inhalation exposures to rats and mice

Whole-body inhalation exposures to N,N-dimethylacetamide (DMAC) were conducted with male rats (Crl:CD BR) and mice (Crl:CD-1 (ICR)BR). Exposure concentrations were 50, 150, 300 and 500 ppm. The exposure routines consisted of single 1-, 3-, or 6-h exposures and ten 6-h exposures (10 exposure days in 2 weeks). Area under the plasma concentration curve (AUC) values were determined for DMAC and its metabolite N-methylacetamide (NMAC), following 6-h exposures (single exposure or last in a series of 10 exposures). The range of exposures was chosen to assess the exposure-dependent nature of DMAC pharmacokinetics in rats and mice. Plasma profiles indicated mice metabolized DMAC rapidly with plasma half-lives from 0.3 to 0.5 h for DMAC. The DMAC AUC values from mice were underestimated due to the required time (< 30 min) between termination of exposure and the initial blood sample. DMAC plasma half-life in rats ranged from 0.6 to 1.5 h. The AUC values for DMAC in rats increased approximately 5-fold and 3-fold as exposure concentrations increased from 150 to 300 ppm and 300 to 500 ppm, respectively. NMAC persisted in plasma for at least 24 h after the 150, 300 and 500 ppm exposures to rats. NMAC was not detected in plasma from mice beyond the 12-h post-exposure timepoint for the 300 and 500 ppm exposures. Regardless of exposure level, repeated DMAC exposures to both rats and mice resulted in plasma profiles of DMAC and NMAC similar to those from a single exposure. The dose-dependent nature of the DMAC AUC data and the absence of effects of repeated 300 and 500 ppm DMAC exposures supported a toxicity-driven upper limit of 350 ppm for a chronic inhalation study.

Dimethylformamide pharmacokinetics following inhalation exposure in monkeys

Male and female cynomolgus monkeys received whole-body inhalation exposures to dimethylformamide (DMF) at concentrations of 30, 100, and 500 ppm for 6 hours a day, 5 days a week over a 13-week period. Serial blood samples were drawn at the conclusion of the first day of exposure and following 15, 29, 57, and 85 days of testing. Area under the plasma concentration curve (AUC) values were determined for DMF and "NMF" [N-methylformamide (NMF) plus N-(hydroxymethyl)-N-methylformamide (DMF-OH)]. Urine samples were also collected and assayed for DMF, NMF and DMF-OH. The systemic exposure to DMF increased disproportionately as the airborne DMF concentrations increased. DMF AUC values increased 19- to 37-fold in male and 35- to 54-fold in female monkeys as the inhalation concentrations increased 5-fold (100 to 500 ppm). These data are consistent with saturation of DMF metabolism as inhaled DMF concentrations increased from 100 to 500 ppm. AUC values, peak plasma concentrations, and plasma half-lives were essentially unaltered over the duration of the study within each exposure concentration tested. Estimated plasma half-lives ranged from 1 to 2 hours and 4 to 15 hours for DMF and "NMF" respectively. DMF was rapidly converted to "NMF" following 30 ppm exposures, with "NMF" plasma concentrations higher than DMF plasma concentrations at the 0.5 hour time-point. In plasma samples simultaneously assayed for DMF-OH and NMF, the concentration of DMF-OH exceeded, was equal to, or was less than NMF concentrations depending upon the plasma sample. DMF-OH was always the main urinary metabolite (56 to 95 percent) regardless of exposure level or time on study.

Dimethylformamide pharmacokinetics following inhalation exposures to rats and mice

Whole-body inhalation exposures to N,N-dimethylformamide (DMF) were conducted with rats and mice. The exposure concentrations were 10, 250, and 500 ppm DMF. The exposure routines consisted of single 1-, 3-, or 6-hour exposures and ten 6-hour exposures (ten exposure days in 2 weeks). Area under the plasma concentration curve (AUC) values were determined following exposure for DMF and "N-methylformamide" ["NMF" represented N-methylformamide plus N-(hydroxymethyl)-N-methylformamide (DMF-OH)]. The DMF AUC values increased 8- and 29-fold for rats and mice, respectively, following single six-hour exposures to 250 and 500 ppm DMF. These data are indicative of saturation of DMF metabolism. Peak "NMF" plasma concentrations for rats and mice, following single 6-hour exposures, did not increase as DMF exposure concentrations increased from 250 to 500 ppm. In addition, the "NMF" plasma levels in rats following a single 6-hour 500 ppm DMF exposure did not decay by 24 hours post exposure. These "NMF" plasma data also indicate saturation of DMF metabolism. Multiple exposures to 500 ppm DMF resulted in a 3- and 4-fold reduction in DMF AUC values for rats and mice, respectively, compared to AUC values following a single six-hour 500 ppm DMF exposure. This indicates enhanced metabolism of DMF resulting from multiple 500 ppm DMF exposures and together with saturation of DMF metabolism suggest using exposure levels below 500 ppm in a chronic bioassay. Selected plasma samples were simultaneously assayed for NMF and DMF-OH. The "NMF" values consisted of between 30 to 60 percent DMF-OH depending upon the exposure group (conversely NMF represented 30 to 60 percent of the "NMF" levels). Urinary analysis of all samples revealed DMF-OH represented over 90 percent of the summed DMF, DMF-OH and NMF quantities.

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.

Effect of diethyldithiocarbamate rescue on tumor response to cis-platinum in a rat model

The nephrotoxic effects of cis-dichlorodiamineplatinum(II) (NSC-119875) (DDP) in female F344 rats were effectively inhibited by administration of sodium diethyldithiocarbamate (DDTC) in doses of 750 mg/kg intraperitoneally or 100 mg/kg intravenously 2 hr after administration of DDP. Rats were inoculated with mammary tumor 13762 and treated after 10 days with DDP (2.0 or 8.0 mg/kg) with or without DDTC rescue (750 mg/kg intraperitoneally or 100 mg/kg intravenously). Initial reductions in tumor size were identical with or without rescue in all experiments. High-dose intraperitoneal rescue, however, resulted in earlier relapse and more rapid progressions at both DDP doses than was observed in the absence of rescue. Low-dose intravenous rescue led to a tumor response identical to that observed without rescue. Urinary excretion of free DDTC was increased by prior administration of acetazolamide; however, this combination was more toxic to rats after DDP administration than was DDTC alone. Intravenous administration of DDTC appeared to be the most effective route for delivery of this ligand to the kidney. These results support our earlier mechanistic hypothesis and demonstrate the feasibility of inhibition of cis-platinum toxicity by DDTC without inhibition of the antitumor effect.