Gary M. Hoffman

Role of the Renal Cysteine Conjugate β-Lyase Pathway in Inhaled Compound A Nephrotoxicity in Rats

BACKGROUND The sevoflurane degradation product compound A is nephrotoxic in rats and undergoes metabolism to glutathione and cysteine S-conjugates, with further metabolism by renal cysteine conjugate beta-lyase to reactive intermediates. Evidence suggests that toxicity is mediated by renal uptake of compound A S-conjugates and metabolism by beta-lyase. Previously, inhibitors of the beta-lyase pathway (aminooxyacetic acid and probenecid) diminished the nephrotoxicity of intraperitoneal compound A. This investigation determined inhibitor effects on the toxicity of inhaled compound A. METHODS Fischer 344 rats underwent 3 h of nose-only exposure to compound A (0-220 ppm in initial dose-response experiments and 100-109 ppm in subsequent inhibitor experiments). The inhibitors (and targets) were probenecid (renal organic anion transport mediating S-conjugate uptake), acivicin (gamma-glutamyl transferase), aminooxyacetic acid (renal beta-lyase), and aminobenzotriazole (cytochrome P450). Urine was collected for 24 h, and the animals were killed. Nephrotoxicity was assessed by histology and biochemical markers (serum BUN and creatinine; urine volume; and excretion of protein, glucose, and alpha-glutathione-S-transferase, a predominantly proximal tubular cell protein). RESULTS Compound A caused dose-related proximal tubular cell necrosis, diuresis, proteinuria, glucosuria, and increased alpha-glutathione-S-transferase excretion. The threshold for toxicity was 98-109 ppm (294-327 ppm-h). Probenecid diminished (P < 0.05) compound A-induced glucosuria and excretion of alpha-glutathione-S-transferase and completely prevented necrosis. Aminooxyacetic acid diminished compound A-dependent proteinuria and glucosuria but did not decrease necrosis. Acivicin increased nephrotoxicity of compound A, and aminobenzotriazole had no consistent effect on nephrotoxicity of compound A. CONCLUSIONS Nephrotoxicity of inhaled compound A in rats was associated with renal uptake of compound A S-conjugates and cysteine conjugates metabolism by renal beta-lyase. Manipulation of the beta-lyase pathway elicited similar results, whether compound A was administered by inhalation or intraperitoneal injection. Route of administration does not apparently influence nephrotoxicity of compound A in rats.

Inhalation toxicity studies with boron trifluoride

An acute study of boron trifluoride (BF3) in rats indicated the 4-hr LC50 to be 1.21 mg/liter. In a 2-week study, all animals exposed to 180 mg/m3 died prior to the sixth exposure, rats exposed at concentrations of 66 and 24 mg/m3 showed clinical signs of respiratory irritation, body weight gain depressions, increased lung weights, and depressed liver weights. Histopathology showed necrosis and pyknosis of the proximal tubular epithelium of the kidneys. This effect was limited to the high-concentration exposure group. Based on the results of these studies, Fischer 344 rats were exposed 6 hr/day, 5 days/week for 13 weeks to a respirable, liquid aerosol of BF3 at concentrations of 0, 2.0, 6.0, and 17 mg/m3. One rat in the high exposure group died. The most significant finding in this group was necrosis of the proximal tubular epithelium of the kidneys. Other observations noted during the study included dried material around the nose and mouth, rales and excessive lacrimation, reversible depression of serum total protein and globulin concentrations, and increases in urinary, serum, and bone fluoride amounts. In the lower exposure groups, findings of respiratory irritation were minimal. All observations occurred in a dose-related pattern. Based on this study, exposure to BF3 at 17 mg/m3 resulted in renal toxicity, while exposure at 6 mg/m3, although showing elevations of fluoride amounts, did not result in a toxic response.

The toxicological properties of petroleum gases.

To characterize the toxicological hazards of petroleum gases, 90-day inhalation toxicity (Organization for Economic Cooperation and Development [OECD] 413) and developmental toxicity (OECD 414) tests were conducted with liquefied propane gas (LPG) at concentrations of 1000, 5000, or 10 000 ppm. A micronucleus test (OECD 474) of LPG was also conducted. No systemic or developmental effects were observed; the overall no observed adverse effect concentration (NOAEC) was 10 000 ppm. Further, there was no effect of LPG exposure at levels up to 10 000 ppm on micronucleus induction and no evidence of bone marrow toxicity. Other alkane gases (ethane, propane, n-butane, and isobutane) were then evaluated in combined repeated exposure studies with reproduction/development toxicity screening tests (OECD 422). There were no toxicologically important changes in parameters relating to systemic toxicity or neurotoxicity for any of these gases at concentrations ranging from 9000 to 16 000 ppm. There was no evidence of effects on developmental or reproductive toxicity in the studies of ethane, propane, or n-butane at the highest concentrations tested. However, there was a reduction in mating in the high-exposure group (9000 ppm) of the isobutane study, which although not significantly different was outside the range previously observed in the testing laboratory. Assuming the reduction in mating to have been toxicologically significant, the NOAEC for the isobutane reproductive toxicity screening test was 3000 ppm (7125 mg/m3). A method is proposed by which the toxicity of any of the 106 complex petroleum gas streams can be estimated from its composition.

Health assessment of gasoline and fuel oxygenate vapors: reproductive toxicity assessment.

Vapor condensates of baseline gasoline (BGVC), or gasoline-blended with methyl tertiary butyl ether (G/MTBE), ethyl t-butyl ether (G/ETBE), t-amyl methyl ether (G/TAME), diisopropyl ether (G/DIPE), ethanol (G/EtOH), or t-butyl alcohol (G/TBA) were evaluated for reproductive toxicity in rats at target concentrations of 2000, 10,000, or 20,000 mg/m3, 6 h/day, 7 days/week. BGVC and G/MTBE were assessed over two generations, the others for one generation. BGVC and G/MTBE F1 offspring were evaluated for neuropathology and changes in regional brain glial fibrillary acidic protein content. No neurotoxicity was observed. Male kidney weight was increased consistent with light hydrocarbon nephropathy. In adult rats, decreased body weight gain and increased liver weight were seen. Spleen weight decreased in adults and pups exposed to G/TBA. No pathological changes to reproductive organs occurred in any study. Decreased food consumption was seen in G/TAME lactating females. Transient decreases in G/TAME off-spring weights were observed during lactation. Except for a minor increase in time to mating in G/TBA which did not affect other reproductive parameters, there were no adverse reproductive findings. The NOAEL for reproductive and offspring parameters was 20,000 mg/m3 for all vapor condensates except for lower offspring NOAELs of 10,000 mg/m3 for G/TBA and 2000 mg/m3 for G/TAME.

Health assessment of gasoline and fuel oxygenate vapors: micronucleus and sister chromatid exchange evaluations.

Micronucleus and sister chromatid exchange (SCE) tests were performed for vapor condensate of baseline gasoline (BGVC), or gasoline with oxygenates, methyl tert-butyl ether (G/MTBE), ethyl tert butyl ether (G/ETBE), t-amyl methyl ether (G/TAME), diisopropyl ether (G/DIPE), t-butyl alcohol (TBA), or ethanol (G/EtOH). Sprague Dawley rats (the same 5/sex/group for both endpoints) were exposed to 0, 2000, 10,000, or 20,000mg/m(3) of each condensate, 6h/day, 5days/week over 4weeks. Positive controls (5/sex/test) were given cyclophosphamide IP, 24h prior to sacrifice at 5mg/kg (SCE test) and 40mg/kg (micronucleus test). Blood was collected from the abdominal aorta for the SCE test and femurs removed for the micronucleus test. Blood cell cultures were treated with 5μg/ml bromodeoxyuridine (BrdU) for SCE evaluation. No significant increases in micronucleated immature erythrocytes were observed for any test material. Statistically significant increases in SCE were observed in rats given BGVC alone or in female rats given G/MTBE. G/TAME induced increased SCE in both sexes at the highest dose only. Although DNA perturbation was observed for several samples, DNA damage was not expressed as increased micronuclei in bone marrow cells. Inclusion of oxygenates in gasoline did not increase the effects of gasoline alone or produce a cytogenetic hazard.

Health assessment of gasoline and fuel oxygenate vapors: developmental toxicity in mice.

CD-1 mice were exposed to baseline gasoline vapor condensate (BGVC) alone or to vapors of gasoline blended with methyl tertiary butyl ether (G/MTBE). Inhalation exposures were 6h/d on GD 5-17 at levels of 0, 2000, 10,000, and 20,000mg/m(3). Dams were evaluated for evidence of maternal toxicity, and fetuses were weighed, sexed, and evaluated for external, visceral, and skeletal anomalies. Exposure to 20,000mg/m(3) of BGVC produced slight reductions in maternal body weight/gain and decreased fetal body weight. G/MTBE exposure did not produce statistically significant maternal or developmental effects; however, two uncommon ventral wall closure defects occurred: gastroschisis (1 fetus at 10,000mg/m(3)) and ectopia cordis (1 fetus at 2000mg/m(3); 2 fetuses/1 litter at 10,000mg/m(3)). A second study (G/MTBE-2) evaluated similar exposure levels on GD 5-16 and an additional group exposed to 30,000mg/m(3) from GD 5-10. An increased incidence of cleft palate was observed at 30,000mg/m(3) G/MTBE. No ectopia cordis occurred in the replicate study, but a single observation of gastroschisis was observed at 30,000mg/m(3). The no observed adverse effect levels for maternal/developmental toxicity in the BGVC study were 10,000/2000mg/m(3), 20,000/20,000 for the G/MTBE study, and 10,000/20,000 for the G/MTBE-2 study.

TOXICITY EVALUATION OF PETROLEUM BLENDING STREAMS: INHALATION SUBCHRONIC TOXICITY/NEUROTOXICITY STUDY OF A LIGHT CATALYTIC REFORMED NAPHTHA DISTILLATE IN RATS

A 13-wk whole-body inhalation study was conducted with Sprague-Dawley CD rats (16/sex/group) exposed to a light catalytic reformed naphtha distillate (LCRN-D, CAS number 64741-63-5) at target concentrations of 0, 750, 2500, and 7500 ppm for 6 h/d, 5 d/wk. Sixteen rats per sex in the control and high-dose groups were maintained after final exposure for a 4-wk recovery period. The highest exposure concentration was 75% of the lower explosive limit. Standard parameters of subchronic toxicity were measured throughout the study; at necropsy, organs were weighed and tissues processed for microscopic evaluation. Neurotoxicity evaluations consisted of motor activity (MA) and a functional operational battery (FOB) measured pretest, throughout exposure and after the recovery period. Neuropathology was evaluated at termination. No test-related mortality or effects on physical signs, body weight, food consumption, or clinical chemistry were observed. In males exposed to 7500-ppm LCRN-D, a statistically significant decrease in white blood cell counts and lymphocyte counts was observed at the termination of exposure that was not present in animals after the 4-wk recovery period. However, mean corpuscular volume was slightly decreased in high-dose males after the recovery period. Statistically significant increases in kidney weights relative to body weights in 7500-ppm male rats correlated with microscopically observed hyaline droplet formation and renal tubule dilation, indicative of light hydrocarbon nephropathy, a condition in male rats that is not toxicologically significant for humans. Statistically significant decrease in absolute and relative spleen weights in 7500-ppm male rats correlated with decreases in hematologic parameters but had no microscopic correlate and was not observed in animals after 4 wk of recovery. This mild, reversible effect in white blood cell populations may relate to the presence of aromatics in the distillate. The only effect of LCRN-D on neurobehavioral parameters was significantly higher motor activity counts among high-dose (7500 ppm) males after the 4-wk recovery period, suggesting a possible delayed effect of LCRN-D. However, there was no evidence of hyperactivity or abnormal behavior from the functional observational battery evaluations, and there were no microscopic changes in neural tissue to support this observation. The no-observed-adverse-effects level (NOAEL) for LCRN-D was 2500 ppm for both subchronic toxicity and neurotoxicity. The no-observed-effects level (NOEL) was 750 ppm.A 13-wk whole-body inhalation study was conducted with Sprague-Dawley CD rats (16/sex/group) exposed to a light catalytic reformed naphtha distillate (LCRN-D, CAS number 64741-63-5) at target concentrations of 0, 750, 2500, and 7500 ppm for 6 h/d, 5 d/wk. Sixteen rats per sex in the control and high-dose groups were maintained after final exposure for a 4-wk recovery period. The highest exposure concentration was 75% of the lower explosive limit. Standard parameters of subchronic toxicity were measured throughout the study; at necropsy, organs were weighed and tissues processed for microscopic evaluation. Neurotoxicity evaluations consisted of motor activity (MA) and a functional operational battery (FOB) measured pretest, throughout exposure and after the recovery period. Neuropathology was evaluated at termination. No test-related mortality or effects on physical signs, body weight, food consumption, or clinical chemistry were observed. In males exposed to 7500-ppm LCRN-D, a statistically significant decrease in white blood cell counts and lymphocyte counts was observed at the termination of exposure that was not present in animals after the 4-wk recovery period. However, mean corpuscular volume was slightly decreased in high-dose males after the recovery period. Statistically significant increases in kidney weights relative to body weights in 7500-ppm male rats correlated with microscopically observed hyaline droplet formation and renal tubule dilation, indicative of light hydrocarbon nephropathy, a condition in male rats that is not toxicologically significant for humans. Statistically significant decrease in absolute and relative spleen weights in 7500-ppm male rats correlated with decreases in hematologic parameters but had no microscopic correlate and was not observed in animals after 4 wk of recovery. This mild, reversible effect in white blood cell populations may relate to the presence of aromatics in the distillate. The only effect of LCRN-D on neurobehavioral parameters was significantly higher motor activity counts among high-dose (7500 ppm) males after the 4-wk recovery period, suggesting a possible delayed effect of LCRN-D. However, there was no evidence of hyperactivity or abnormal behavior from the functional observational battery evaluations, and there were no microscopic changes in neural tissue to support this observation. The no-observed-adverse-effects level (NOAEL) for LCRN-D was 2500 ppm for both subchronic toxicity and neurotoxicity. The no-observed-effects level (NOEL) was 750 ppm.

Inhalation toxicity of hexafluoroisobutylene

An acute study of hexafluoroisobutylene (HFIB) determined its 4-hr LC50 in rats to be 1425 ppm. In a 2-week study, all animals exposed to 215 ppm for 4 days died or were sacrificed in extremis, while those exposed to the lowest level tested, 53 ppm, showed respiratory and renal effects. Based on the results of these studies, Fischer-344 rats were exposed 6 hr a day, 5 days a week, for 13 weeks to average HFIB concentrations of 3, 10, 30, and 90 ppm. No animals died due to the HFIB exposures. However, at the highest exposure level tested there were numerous marked signs of systemic toxicity in males and females. At all exposure levels, males were more affected than females. The lungs and kidneys were clearly target organs for HFIB, the kidneys being more sensitive in this study (having increased absolute and relative weights, alterations in relevant clinical chemistry parameters, and alterations in microscopic structure). A clear dose-response pattern for the above toxic effects was evident with 10 ppm in the males being an effect level. Male rats exposed to 30 ppm of HFIB had decreased body weights and significantly increased kidney weights. A satellite group of animals was maintained for 2 weeks after the completion of exposure. These animals showed some remission from the observed toxic effects, indicating recovery could be expected in rats from at least most of the toxic effects associated with exposure to HFIB. All effects observed in 3 ppm males disappeared by the end of the recovery period.

Biotransformation of 2,3,3,3-tetrafluoropropene (HFO-1234yf) in male, pregnant and non-pregnant female rabbits after single high dose inhalation exposure.

2,3,3,3-Tetrafluoropropene (HFO-1234yf) is a novel refrigerant intended for use in mobile air conditioning. It showed a low potential for toxicity in rodents studies with most NOAELs well above 10,000 ppm in guideline compliant toxicity studies. However, a developmental toxicity study in rabbits showed mortality at exposure levels of 5,500 ppm and above. No lethality was observed at exposure levels of 2,500 and 4,000 ppm. Nevertheless, increased subacute inflammatory heart lesions were observed in rabbits at all exposure levels. Since the lethality in pregnant animals may be due to altered biotransformation of HFO-1234yf and to evaluate the potential risk to pregnant women facing a car crash, this study compared the acute toxicity and biotransformation of HFO-1234yf in male, female and pregnant female rabbits. Animals were exposed to 50,000 ppm and 100,000 ppm for 1h. For metabolite identification by (19)F NMR and LC/MS-MS, urine was collected for 48 h after inhalation exposure. In all samples, the predominant metabolites were S-(3,3,3-trifluoro-2-hydroxypropanyl)-mercaptolactic acid and N-acetyl-S-(3,3,3-trifluoro-2-hydroxypropanyl)-L-cysteine. Since no major differences in urinary metabolite pattern were observed between the groups, only N-acetyl-S-(3,3,3-trifluoro-2-hydroxypropanyl)-L-cysteine excretion was quantified. No significant differences in recovery between non-pregnant (43.10 ± 22.35 μmol) and pregnant female (50.47 ± 19.72 μmol) rabbits were observed, male rabbits exposed to 100,000 ppm for one hour excreted 86.40 ± 38.87 μmol. Lethality and clinical signs of toxicity were not observed in any group. The results suggest that the lethality of HFO-1234yf in pregnant rabbits unlikely is due to changes in biotransformation patterns or capacity in pregnant rabbits.

Toxicity Evaluation of Petroleum Blending Streams: Inhalation Subchronic Toxicity/Neurotoxicity Study of a Light Catalytic Cracked Naphtha Distillate in Rats

A 15-week, whole-body inhalation study of the vapors of a distillate (LCCN-D) of light catalytic cracked naphtha (CAS no. 64741–55–5, LCCN) was conducted with Sprague-Dawley rats. Target exposure concentrations were 0, 750, 2500, and 7500 ppm for 6 hours/day, 5 days/week. Over the course of the study, animals received at least 65 exposures. For a portion of the control and 7500-ppm groups, a 4-week postexposure period was included in the study. Subchronic toxicity was evaluated using standard parameters. During life, neurotoxicity was evaluated by motor activity assessment and a functional observational battery. Selected tissues from animals in all exposure groups were examined microscopically. Neuropathologic examination of selected neuronal tissues from animals in the control and high-exposure groups was also conducted. No compound-related effects were seen on survival, clinical chemistry, food consumption, or physical signs. No evidence of neurotoxicity was seen at any exposure level. Slight decreases in hematocrit and hemoglobin concentrations were seen in male rats at the end of exposure to 7500 ppm LCCN-D. However, values were within normal physiological ranges and recovery occurred. Slight decreases in mean body weights and body weight gain were observed in high-exposure females during the first 7 weeks of exposure, but this decrease was not seen during the second half of the study. Male rat nephropathy involving hyaline droplet formation and alpha-2μ-globulin accumulation was seen in mid-and high-exposure males, an effect not relevant to humans. The incidence and severity of goblet cell hypertrophy/hyperplasia and respiratory epithelium hyperplasia in nasoturbinal tissues were greater in high-exposure animals, but recovery occurred. None of the effects observed were considered toxicologically significant. The no-observable-adverse-effect level (NOAEL) for subchronic and neurotoxicity of LCCN-D was ≥7500 ppm.