Rashmi S. Nair

Subchronic inhalation toxicity of p-nitroaniline and p-nitrochlorobenzene in rats☆

For evaluation of subchronic toxicity of the two single-ring nitroaromatics, p-nitroaniline (PNA) and p-nitrochlorobenzene (PNCB), groups of 10 male and 10 female Sprague-Dawley rats were exposed to an aerosol/vapor of PNA in isopropanol at target concentrations of 0, 10, 30, or 90 mg/m3 or to PNCB vaporized from a solution in ethylene glycol monoethyl ether at target concentrations of 0, 5, 15, or 45 mg/m3 for 6 hr/day, 5 days/week for 4 weeks. Clinical signs of toxicity, body weights, results of ophthalmoscopic exam, hematology and clinical chemistry tests, organ weights, gross and histopathological changes were recorded. Exposure to PNA or PNCB resulted in a dose-related increase in blood methemoglobin levels. Mean red blood cell counts, hematocrit, and hemoglobin were significantly decreased in mid and high level animals exposed to PNCB. Mean spleen weights (absolute and relative to body weight) were significantly increased at the high dose levels in the two studies. A slight increase in spleen weights was also observed at the low concentration level in the PNA study. Absolute and relative liver weights also were increased among animals exposed to 45 mg/m3 PNCB. Microscopic changes were observed mainly in the spleen and included an increase in intensity of extramedullary hematopoiesis and hemosiderosis with both compounds. Spleens of animals exposed to PNCB also exhibited congestion. Neither PNA nor PNCB exhibited significant toxicological effects other than those of methemoglobinemia, anemia, and splenic changes classically associated with nitroaromatics at levels significantly above presently accepted occupational standard. Our data suggest that the current TLV for PNA which is 3 mg/m3 will provide adequate protection to the workers. OSHAs PEL of 1 mg/m3 for PNCB is to be preferred over the current TLV of 3 mg/m3 to provide a comparable margin of safety.

Current Methods for Assessing Safety of Genetically Modified Crops as Exemplified by Data on Roundup Ready 1 Soybeans

Several laboratories have used recombinant DNA technology in plant breeding to improve compositional, processing, and agronomic characteristics of plants. These transformed plants have been extensively tested in fi eld trials, have gained full regulatory approvals and are currently being marketed in a number of countries around the world. This paper briefl y summarizes the approach used to assure the safety of foods and feeds derived from these genetically modified crops, as exemplified by data on Roundup Ready soybeans that has been developed by Monsanto Company using biotechnology in order to confer tolerance to glyphosate, the active ingredient in Roundup herbicide, by the production of the CP4 enolpyruvylshikimate-3-phosphate synthase protein. The results of the studies demonstrate that Roundup Ready soybeans are as safe as traditional soybeans with respect to food and feed safety.

Chronic Toxicity, Oncogenic Potential, and Reproductive Toxicity of p-Nitroaniline in Rats

Dose levels for these studies were selected mainly on the basis of subchronic studies, although consideration was also given to workplace exposure levels and proposed mechanism of tumor formation with structurally similar compounds. For the chronic study, groups of 60 male and 60 female Sprague-Dawley CD (Registered Trademark of Charles River Breeding Laboratories, Portage, MI) rats were given 0, 0.25, 1.5, or 9.0 mg/kg/day paranitroaniline (PNA) by gavage in corn oil for a period of 2 years. Parameters monitored included clinical observations, ophthalmoscopic exams, body weights, food consumption, hematology, clinical chemistry, and urinalysis at regular intervals throughout the study. All gross lesions and over 40 tissues were examined histologically for all control and high-dosage-level animals. Gross lesions, spleens, and livers of low- and mid-dosage groups were also examined histologically. For the reproduction study, groups of 15 male and 30 female rats, designated as F0 generation, were given PNA at the same levels as the chronic study for 14 weeks prior to mating and during mating, gestation, and lactation. Selected groups of 15 male and 30 female rats of the F1 generation received the same dose of PNA for 18 weeks prior to mating and during mating, gestation, and lactation. F2 pups were observed through weaning at which time they were euthanized. Observations made during the study included body weights, food consumption, mating and fertility indices, pup and litter survival indices, and histopathology of selected tissues. In the chronic study, except for a slight decrease in survival of high-dose male rats late in the study, survival in all treated groups was comparable to controls. Blood methemoglobin levels were elevated in the mid- and high-dosage groups, while slight anemia was observed in the high-dosage group also. Spleen weights were significantly increased in the high-dosage groups. An accumulation of brown pigment was observed in the cytoplasm of the sinusoidal macrophages or littoral cells of the liver and in the reticuloendothelial cells of the spleen. No treatment-related increase in tumor incidence was observed. In the reproduction study, no consistent pattern of effect from treatment between the F0 and F1 generation was seen in mating, pregnancy, or fertility indices. Thus, administration of PNA at levels which produced significant methemoglobinemia and low-level anemia in the rat and histological changes in the spleen produced no tumors or reproducible effects on reproductive performance.

Assessment of the Delayed Neurotoxicity of Tributyl Phosphate, Tributoxyethyl Phosphate, and Dibutylphenyl Phosphate:

There industrial organophosphorus compounds were tested for their ability to cause organophosphorus compound-induced delayed neurotoxicity (OPIDN) in the adult hen. The compounds tested were tributyl phosphate (TBP), tributoxyethyl phosphate (TBEP), and dibutylphenyl phosphate (DBPP). The acute oral LD50 of TBP and DBPP were estimated to be 1,863 and 1,500 mg/kg, respectively, and the dose equal to the LD50 was used as a test dose. The acute oral LD50 of TBEP was greater than 5,000 mg/kg and 5,000 mg/kg was used as a test dose. An oral dose of 750 mg tri-o-cresyl phosphate (TOCP) was used as a positive control. For the acute delayed neurotoxicity test, hens were given two test doses of the test materials 21 days apart and killed 21 days after the second dose. None of the hens given TBP, TBEP, or DBPP exhibited nerve damage or clinical signs which distinguished them from untreated control animals. A single dose of TOCP resulted in paralysis and a histopathological profile typical of a distal neuropathy. For the assay of the inhibition of esterases, hens were killed 24 hours after a single dose equal to the greater of either the LD50 or 5000 mg/kg. TOCP administration resulted in over 90% inhibition of brain neurotoxic esterase (NTE), but none of the other three compounds inhibited NTE to an extent (<70%) which would be expected to result in OPIDN. Administration of TOCP, TBEP, or DBPP resulted in approximately a 70% decrease in plasma butyrylchol-inesterase (BuChE) activity. TBP caused a 2–3 fold increase in BuChE activity. TBEP administration resulted in about 45% inhibition of acetycholinesterase (AChE) in brain. These results indicate that TBP, TBEP, and DBPP are all unlikely to cause OPIDN with any single sublethal dose.

Assessment of toxicity of o-nitrochlorobenzene in rats following a 4-week inhalation exposure☆

o-Nitrochlorobenzene (ONCB) is a chemical intermediate used for the synthesis of various industrial chemicals. To evaluate the subchronic toxicity of this compound, three groups of 15 male and 15 female Sprague-Dawley rats were exposed to ONCB vapor 6 hr/day, 5 days/week for 4 weeks at target concentrations of 10, 30, or 60 mg/m3. A control group of 15 animals/sex was exposed to room air in a separate inhalation chamber. Concentrations of ONCB in the chambers were determined at least three times a day using a uv spectrophotometer. Parameters monitored in this study included observation for signs of toxicity, body weights, ophthalmoscopic exam, hematology, and clinical chemistry. At necropsy, selected organ weights were recorded and over 35 tissues/animal were examined microscopically for all control and high-exposure level animals. No mortality was observed in this study. Mean body weights of all groups were comparable to controls. Animals exposed to the mid and high concentrations of ONCB showed a significant increase in blood methemoglobin and a significant decrease in hemoglobin, hematocrit, and red blood cell counts. Spleen and liver weights (absolute and relative to body weight) were significantly increased for these two groups. Microscopic changes, observed only in the spleen, included increased degree of extramedullary hematopoiesis and hemosiderosis. These data suggest that the toxicity of ONCB is comparable to that of its structural analog, p-nitrochlorobenzene. Thus these two compounds should have similar work-place exposure limits.

The Genotoxic Potential of Linear Alkylbenzene Mixtures in a Short-Term Test Battery

Alkylate 215 (A-215), Alkylate 225 (A-225), and Alkylate 230 (A-230) are mixtures of C10-C14 linear alkylbenzenes used as intermediates for the manufacture of detergents. These products were evaluated for genotoxic activity in the Ames bacterial mutagenesis assay (strains TA98, 100, 1535, and 1537), the CHO/HGPRT mammalian cell forward gene mutation assay, and the in vivo rat bone marrow chromosome assay. The Ames and CHO/HGPRT assays were conducted both with and without the addition of Aroclor-induced rat liver S9. The maximum concentrations evaluated were 10 mg/plate (A-215) and 3 mg/plate (A-225 and A-230) for the Ames test, and 1.5 mg/ml (A-215 and A-225) and 2.0 mg/ml (A-230) for the CHO/HGPRT assay. In each case, the highest concentrations produced evidence of either toxicity or insolubility. The highest dose in the bone marrow cytogenetics assay was 12,700 mg/kg, a level which produced significant weight loss. The results of all tests were negative, indicating a lack of genotoxic activity as measured by the battery of tests used.

SUBCHRONIC RAT INHALATION STUDY WITH SKYDROL® 500B-4 FIRE RESISTANT HYDRAULIC FLUID

Skydrol 500B-4 fire resistant hydraulic fluid, a proprietary phosphate ester mixture composed principally of dibutyl phenyl phosphate (DBPP) and tributyl phosphate (TBP) and used as a commercial airline hydraulic fluid, was evaluated in an inhalation toxicity study of Sprague-Dawley rats. Target exposure levels used in the study were 0, 5, 100, and 300 mg/m3, and exposures were maintained for 6 hr/day, 5 days/week. Mass median aerodynamic diameters determined for particles in the mid- and high-exposure inhalation chambers were 2.85 microns and 3.31 microns, with geometric standard deviations of 1.99 microns and 1.92 microns, respectively. The percentage of particles less than 10 microns in diameter were 96.4% in the mid-exposure chamber and 95.5% in the high-exposure chamber. After 6 weeks of Skydrol exposure, 10 rats/sex/group were euthanized and then assessed for indications of possible chemical toxicity. Another 15 rats/sex/group were studied for a total of 13 weeks of exposure. The only clinical sign of chemical toxicity was the observation of a reddish nasal discharge with accompanying oral salivation in mid- and high-exposure animals of both sexes, indicative of an irritant response. Statistically significant reduced body weights; increased absolute and relative liver weights; and decreased erythrocyte counts, hemoglobin levels, and hematocrit values were observed in high-exposure female rats euthanized after 13 weeks of Skydrol exposure. High-exposure male rats also had increased absolute and relative liver weights and decreased hematocrit values after 13 weeks. Plasma cholinesterase levels were decreased in high-exposure female rats both 6 and 13 weeks after the study was initiated.(ABSTRACT TRUNCATED AT 250 WORDS)

Selecting a more realistic uncertainty factor: Reducing compounding effects of multiple uncertainties

Available toxicology datasets provide a unique opportunity to validate some of the currently used Uncertainty Factors in the development of acceptable exposure levels for noncancer effects. Toxicit...

Mixture risk assessment: A case study of monsanto experiences

Monsanto employs several pragmatic approaches for evaluating the toxicity of mixtures. These approaches are similar to those recommended by many national and international agencies. When conducting hazard and risk assessments, priority is always given to using data collected directly on the mixture of concern. To provide an example of the first tier of evaluation, actual data on acute respiratory irritation studies on mixtures were evaluated to determine whether the principle of additivity was applicable to the mixture evaluated. If actual data on the mixture are unavailable, extrapolation across similar mixtures is considered. Because many formulations are quite similar in composition, the toxicity data from one mixture can be extended to a closely related mixture in a scientifically justifiable manner. An example of a family of products where such extrapolations have been made is presented to exemplify this second approach. Lastly, if data on similar mixtures are unavailable, data on component fractions are used to predict the toxicity of the mixture. In this third approach, process knowledge and scientific judgement are used to determine how the known toxicological properties of the individual fractions affect toxicity of the mixture. Three examples of plant effluents where toxicological data on fractions were used to predict the toxicity of the mixture are discussed. The results of the analysis are used to discuss the predictive value of each of the above mentioned toxicological approaches for evaluating chemical mixtures.

A two-generation reproduction study with monochlorobenzene vapor in rats.

Groups of 30 male and 30 female Sprague-Dawley CD rats, designated as the F0 generation, were exposed to vapor of monochlorobenzene (MCB) at target concentrations of 0, 50, 150, or 450 ppm for 10 weeks prior to mating and during mating, gestation, and lactation. The progeny of the F0 generation was designated as the F1 generation and groups of 30 male and 30 female F1 animals were exposed to the same concentrations of MCB as the F0 parents. Exposure of F1 animals was initiated 1 week postweaning and lasted 11 weeks prior to mating and through mating, gestation, and lactation. All F2 pups were observed through weaning at which time they were killed. Observations made during the study included body weights, food consumption, mating and fertility indices, pup and litter survival indices, and histopathology of selected tissues. No mortality was observed during the course of this study. Body weights and food consumption for all treated groups were comparable to controls during the growth period. Maternal body weight data during gestation and lactation were also comparable between the control and treated groups. Mating and fertility indices for males and females for both generations appeared unaffected by treatment. Pup and litter survival indices for all treated groups were comparable to those of controls. Hepatocellular hypertrophy and renal changes (tubular dilation with eosinophilic material, interstitial nephritis, and foci of regenerative epithelium) were observed among F0 and F1 male rats exposed to 150 and 450 ppm MCB.(ABSTRACT TRUNCATED AT 250 WORDS)