Ralph Gingell

Two-Generation Reproduction Study and Immunotoxicity Screen in Rats Dosed with Phenol via the Drinking Water

This study evaluated the potential reproductive toxicity of phenol in a rat two-generation reproduction study, which included additional study endpoints, such as sperm count and motility, developmental landmarks, histological evaluation of suspect target organs (liver, kidneys, spleen, and thymus), weanling reproductive organ weights, and an immunotoxicity screening plaque assay. Phenol was administered to 30 Sprague-Dawley rats/sex/group in the drinking water at concentrations of 0, 200, 1000, or 5000 ppm. Parental (P1) animals were treated for 10 weeks prior to mating, during mating, gestation, lactation, and until sacrifice. The F1 generation (P1 offspring) was treated using a similar regimen, while the F2 generation was not treated. After mating, 10 P1 males/group were evaluated using standard clinical pathology parameters and an immunotoxicity screening plaque assay. Significant reductions in water and food consumption were observed in the 5000-ppm group in both generations; corollary reductions in body weight/body weight gain were also observed. Mating performance and fertility in both generations were similar to controls, and no adverse effects on vaginal cytology or male reproductive function were observed. Vaginal opening and preputial separation were delayed in the 5000-ppm group, and were considered to be secondary to the reduction in F1 body weight. Litter survival of both generations was reduced in the 5000-ppm group. Absolute uterus and prostate weights were decreased in the F1 generation at all dose levels; however, no underlying pathology was observed and there was no functional deficit in reproductive performance. Therefore, these findings were not considered to be adverse. No evidence of immunotoxicity was noted in the 5000-ppm group. The effects noted at the high concentration were presumed to be associated with flavor aversion to phenol in the drinking water. Based on a comprehensive examination of all parameters, the no-observable-adverse-effect level (NOAEL) for reproductive toxicity of phenol administered in drinking water to rats is 1000 ppm. The corresponding daily intake of phenol for an adult rat at the NOAEL of 1000 ppm is equivalent to about 70 mg/kg/day for males and 93 mg/kg/day for females.

Inhalation Two-Generation Reproductive Toxicity Study of Methyl Isobutyl Ketone in Rats

To evaluate whether methyl isobutyl ketone (MIBK) affects reproductive performance, a two-generation reproduction study was conducted. MIBK was administered to 30 Sprague-Dawley rats/sex/group via whole-body inhalation at concentrations of 0, 500, 1000, or 2000 ppm, 6 h daily, for 70 days prior to mating. F0 and F1 females were exposed from mating through gestation day 20 and from postnatal day 5; F2 litters were maintained through post-natal day 21. No treatment-related mortality of adult animals occurred. There was a dose-related increase in adult animals with no or a decreased response to a sound stimulus at 1000 and 2000 ppm; however, no adverse clinical signs occurred 1 h after exposure, suggesting this was a transient sedative effect. Clinical signs of central nervous system (CNS) depression in the pups were observed and one F1 pup died after initial exposure to 2000 ppm on postnatal day 22; subsequently exposure was delayed until postnatal day 28. Decreased body weight gain and slight decreased food consumption were observed during the first 2 weeks of exposure in both generations at 2000 ppm. There were no adverse effects on male and female reproductive function or landmarks of sexual maturation. Increased F0 and F1 liver weights with associated centrilobular hypertrophy occurred in rats at 2000 ppm, indicative of an adaptive response. Increased male kidney weights at all exposure concentrations, associated with hyaline droplets, were indicative of male rat-specific nephropathy. Other than acute sedative effects, the no-observed-adverse-effect level (NOAEL) for parental systemic effects (excluding male rat kidney) was 1000 ppm, based on transient decreased body weight and food consumption; for reproductive effects, 2000 ppm, the highest concentration tested; and for neonatal toxicity, 1000 ppm (based on acute CNS depressive effects).

Subchronic Dermal Toxicity and Oral Neurotoxicity of Triethylene Glycol Monomethyl Ether in Cd Rats

These studies were conducted to evaluate the potential for repeated subchronic administration of triethylene glycol monomethyl ether (TGME) to produce systemic toxicity in the rat following dermal application, and neurotoxicity in the rat following peroral administration. The route of administration and maximum dose levels for these studies were specified by the U.S. Environmental Protection Agency (EPA) in a testing consent order for TGME. In the subchronic dermal toxicity study, TGME (undiluted) was applied to the clipped backs of CD rats (10 rats/sex/group) for 6 h/day (occluded), 5 days/wk or 13 wk at dose levels of 0, 0.4, 1.2, and 4.0 g/kg/day. Four groups of satellite animals (5 rats/sex/group) employed for interim hematology and clinical chemistry measurements were dosed in the same manner for 31 days. Experimental evaluations included clinical examinations, food consumption, body weight, ophthalmology, estrous cyclicity, hematology, clinical chemistry, urinalysis, and necropsy for all animals and microscopic examination of a complete set of tissues (including bone marrow smears) for animals in the control and high-dose treatment groups. In addition, the testes and epididymides were processed for examination of spermatocyte development. None of the experimental endpoints included in this study to evaluate the potential for systemic toxicity were affected by treatment with TGME. For the neurotoxicity study, TGME was mixed in the drinking water and administered ad libitum to rats

Acute toxicity of ethylene glycol mono-n-butyl ether in the guinea pig.

Acute toxicity values, such as oral and percutaneous LD50s, are often used as the basis for classifying chemicals into toxicity categories, and their subsequent regulation. Such values obtained for ethylene glycol mono-n-butyl ether (EGBE; 2-butoxyethanol) in rats and rabbits indicate that it is moderately toxic. However, the cause of death in these acute studies appeared to be secondary to acute intravascular haemolysis, an effect for which guinea pigs and humans are much less sensitive than rats, mice and rabbits. Recently-conducted acute toxicity studies in the guinea pig resulted in an acute oral LD50 of 1400 mg/kg, an acute percutaneous LD50 of greater than 2000 mg/kg, and a 1-hr LC50 greater than 633 ppm. These data are compared with published acute toxicity values, and indicate that the predicted acute toxicity of EGBE in humans, based on data from the guinea pig, would be less than that observed in other animal species. Based in part on the guinea pig data, EBGE is no longer classified as a poisonous substance by either the United Nations or US Department of Transportation.

Comparative metabolism of methyl isobutyl carbinol and methyl isobutyl ketone in male rats

Methyl isobutyl carbinol (MIBC) is an oxygenated solvent that is metabolized to methylisobutyl ketone (MIBK) and then to 4-hydroxymethyl-4-methyl-2-pentanone (HMP). Plasma levels of MIBC, MIBK and HMP were determined up to 12 h after a single oral 5 mmol/kg dose of MIBC or MIBK to male rats. The major material in the plasma in both cases was HMP, with similar areas-under-the-curve (AUC) and C(max) at 9 h after dosing. MIBK plasma levels and AUC were also comparable after MIBK or MIBC administration. MIBC AUC was only about 6% of the total material in the blood after MIBC, and insignificant after MIBK administration. No other metabolites were detected in the plasma under the analytical conditions used. The extent of metabolism of MIBC to MIBK, by comparing combined AUCs for MIBK and HMP, was at least 73%. The limited systemic toxicity data for MIBC are consistent with those for MIBK, which has been well studied. The metabolic equivalency of MIBC with MIBK indicates that MIBC will have a low potential for toxicity similar to that of MIBK, and reduces the need for additional animal studies.

Subchronic toxicity study of 1,3-propanediol administered orally to rats

1,3-Propanediol was a specialty chemical that, due to a novel manufacturing process, is now commercially available in large quantities. Its subchronic toxicity has been evaluated in rats, with special emphasis on potential male reproductive effects. 1,3-Propanediol in deionized water was administered orally by gavage to three groups of 10 male and 10 female Crl:CD(SD)BR rats for a period of 90 consecutive days. Dosage levels were 100, 300, and 1000 mg/kg/day, and a control group received water at a constant volume of 10 ml/kg/day. All animals survived to the scheduled necropsy, and there were no effects on the clinical condition of the animals, body weights, body weight gains, food consumption or organ weights. There were no effects on hematology or serum chemistry parameters. Spermatogenic endpoints were unaffected in all treated males. No treatment-related changes were observed on macroscopic or microscopic examinations of selected organs. Under the conditions of the study, the no-observed-effect level (NOEL) for systemic toxicity of 1,3-propanediol administered orally via gavage to male and female rats for 90 consecutive days was 1000 mg/kg/day, the highest dose tested.

Two-Week (Ten-Day) Inhalation Toxicity and Two-Week Recovery Study of Phenol Vapor in the Rat

The toxicity of phenol vapor was evaluated in male and female Fischer 344 rats (20/sex/group) via flow-past nose-only inhalation exposure. The test animals were exposed to target concentrations of 0 (air control), 0.5, 5.0, or 25 parts per million (ppm) of phenol in air for 6 hours/day, 5 days/week, for 2 weeks. High pressure liquid chromatography (HPLC) measurement of phenol test atmospheres determined mean (± standard deviation) analytical concentrations of 0.0 ± 0.0, 0.52 ± 0.078, 4.9 ± 0.57, and 25 ± 2.2 ppm, respectively. After 2 weeks of exposure, 10 test animals/sex/group were sampled for clinical chemistry and hematology parameters, and then sacrificed. Histopathological examination included the nasopharyngeal tissues, larynx, trachea, lungs with mainstem bronchi, kidney, fiver, and spleen. The remaining 10 animals/sex/group were retained for a 2-week recovery period. Recovery groups of animals were evaluated as described previously and then sacrificed. No signs of toxicity in clinical observations (including overt neurological signs), body weights, food consumption, clinical pathology, organ weights, macroscopic pathology or microscopic pathology were seen during the exposures or at either sacrifice interval. In conclusion, 2-week inhalation exposures to phenol vapor at concentrations up to and including 25 ppm did not produce any adverse effects.

Reproduction/developmental toxicity screening test in rats with orally-administered 1-hexene.

This study was conducted to provide screening information concerning the potential systemic, reproductive and developmental toxicity of 1-hexene when administered orally, by gavage, to male and female rats using a modified OECD 421 protocol. 1-Hexene was administered at doses of 100, 500, and 1000 mg/kg/day in corn oil; the control group received the vehicle at an equivalent volume. The males were treated for 28 days prior to mating and until euthanasia (44 days of dosing). The females were treated for 14 days prior to mating and during mating, gestation, and lactation until euthanasia (41–55 total days of dosing). Females were allowed to deliver and rear their offspring until lactation day 4. The parental rats were subject to a gross and microscopic examination. Viability and development of the pups were followed through lactation day 4. There was no mortality, and there were no clinical signs of toxicity or differences in body weights, weight gain, feed consumption or organ weights. Copulation and fertility indices, precoital intervals, gestation lengths and pregnancy rates were comparable among the groups, and no signs of prolonged delivery or unusual nesting behaviors were noted. Pup viability, body weights, external observations and necropsy data were comparable among the groups. Pitted kidneys were observed at necropsy for two parental males in the 500 mg/kg/day group and three males in the 1000 mg/kg/day group. Microscopic changes in the kidneys of some male rats from the 100, 500, and 1000 mg/kg/day groups consisted of dose-related accumulations of hyaline droplets in the epithelial cells of the proximal convoluted tubules of the kidneys. In summary, the only treatment-related effect noted in this study was hydrocarbon nephropathy in male rats, which is not considered relevant for human health. The NOAEL for systemic and reproductive toxicity was 1000 mg/kg/day, excluding the finding of male rat hydrocarbon nephropathy.

Subchronic inhalation study of 1-hexene in Fischer 344 rats.

The objective of this study was to evaluate the toxicity of 1-hexene following repeated inhalation exposures in male and female Fischer 344 rats. Groups of 40 male and 40 female rats were exposed for 6 hours per day, 5 days per week, over a 13-week period. Treatment groups consisted of air-exposed control (0 ppm) and three test groups of 300, 1000, and 3000 ppm 1-hexene. During the treatment period, the rats were observed daily for clinical signs of toxicity; body weights and neuromuscular coordination [females only] were measured at 7-day intervals. After 7 weeks of exposure and at the end of the treatment period, the rats were subject to macroscopic and microscopic pathology, clinical chemistry, hematology, urinalysis, and sperm counts. No mortalities were observed during the course of the study. No clinical signs of toxicity attributable to 1-hexene exposure were observed. Female rats exposed to 3000 ppm had significantly lower body weights compared to control rats from exposure day 5 persisting throughout the treatment period. Male rats exposed to 3000 ppm had slightly but not statistically significant lower body weights in comparison to controls. Male rats exhibited slightly increased absolute and relative testicular weights, and female rats had slightly decreased absolute [but not relative] liver and kidney weights, at 3000 ppm. There were no gross or microscopic morphological findings attributed to treatment. Exposure to 1-hexene did not affect neuromuscular coordination in females as determined using the Rotarod, nor sperm counts in male rats. Several statistically significant effects in hematology, clinical chemistry, and urinalysis evaluations were observed, but were either of small magnitude or did not correlate with histopathological findings, and thus did not appear to be of biological significance. In summary, the no-adverse-effect-level for this study was determined to be 1000 ppm, based on decreased weight gain in female rats, and on slight organ weight changes in both sexes at 3000 ppm.