Toxicological evaluation of aerosols of a tobacco extract formulation and nicotine formulation in acute and short-term inhalation studies

Abstract

A formulation of tobacco extract containing 4% nicotine (TE) and similar nicotine formulation containing vehicle and 4% nicotine (NF) were evaluated using animal inhalation assays. Two 4-h inhalation exposures at 1 and 2?mg/L aerosol exposure concentrations, respectively, of the tobacco extract with 4% nicotine formulation showed that the LC₅₀ was greater than 2?mg/L, the maximum concentration tested. All inhalation exposures were conducted using the capillary aerosol generator (CAG). Increasing aerosol TPM concentrations (0, 10, 50, 200, 1000?mg/m³ TE and 0, 50, 200, 500, 1000?mg/m³ NF) were generated via the CAG and used to expose groups of male and female rats for 4-h per day for 14 days. In life monitors for potential effects included clinical observations, weekly body weights and food consumption. Post mortem evaluations included gross tissue findings, hematology, clinical chemistry, serum plasma and nicotine levels, absolute and normalized organ and tissue weights, and histopathology of target organs. Treatment-related changes were observed in body weights, hematology, clinical chemistry, organ weights and histopathological findings for TE at the 200 and 1000?mg/m³ exposure levels, and in the 500 and 1000?mg/m³ exposure groups for NF. Under the conditions of these studies, the no-observed-adverse-effect level in the rat was approximately 50?mg/m³ for the TE aerosol-exposed groups, and approximately 200?mg/m³ in the NF aerosol-exposed groups.     

Investigation of the Effects of Benomyl on Rat Nasal Mucosa

Benomyl [methyl 1-(butylcarbamoyl)-2-benzimidazolecarbamate,CAS Registry No. 17804-35-2] is a widely used agricultural fungicide.Previously, olfactory epithelial lesions were produced followinga 45-day inhalation exposure to 50 and 200 mg/m³ benomyl. Thepresent study, part of a range-finding study for a two-generationreproduction study, was conducted to determine if the previouslyreported effects on the nasal mucosa are the result of systemictoxicity or attributable to the inhalation route of exposure.Groups of 10 7-week-old male Crl:CD BR rats were fed diets containing0, 5000, 10000, or 15000 ppm benomyl for 32 days. Individualbody weights and food consumption were determined weekly andon the last day of the study. After 32 days on test, rats wereeuthanatized by pentobarbital anesthesia and exsanguinationand were examined for gross alterations. The nasal cavity wasprocessed for pathological examination. Mean body weight gainwas statistically significantly decreased during the first weekof treatment and the overall test period (Days 0–32) atthe two highest dose levels. A significant decrease in foodconsumption also was seen during test interval Days 0–7for the two highest dose groups. In addition, statisticallysignificant decreases in food consumption were observed at theDay 7–14 interval for the 15,000 ppm dose group and atthe 21–28 and 28–32 intervals for the two highestdose groups compared with controls. No histopathological lesionswere noted in the nasal epithelium of any of the control orbenomyl-treated rats. These results suggest that the nasal cavityis not a target following dietary administration of benomyland the olfactory epithelial damage reported following inhalationexposure is specific to the route of exposure.     

A 13-week vapor inhalation study of 3,3-dimethyl-2-butanol in Sprague-Dawley rats

Four groups of male and female Sprague-Dawley rats were exposed for 13 weeks to 3,3-dimethyl-2-butanol (PA) at concentrations of 0.00, 0.20, 1.00 or 5.00 mg/l (1 mg/l = 240 ppm). Exposures were for 6 hr per day, 5 days per week with sacrifices at 7 and 13 weeks of exposure, and at 4 weeks after exposure. The test animals were evaluated for abnormalities in physiology, behaviour, clinical laboratory parameters, and gross and microscopic morphology. No abnormalities were detected in electrocardiograms, respiratory indices, spontaneous activity, passive avoidance activity and open-field behaviour. Clinical signs related to PA exposure included alopecia, ataxia and lacrimation. There were no biologically significant between-group differences in body-weights during the study. The clinical laboratory data demonstrated a 30% increase in serum cholesterol and bilirubin at 7 weeks in high-dose males and an increase in urea nitrogen in intermediate and high-dose males at 13 weeks. There were no abnormalities in hematologic or coagulation parameters. At necropsy there were no significant gross abnormalities; however, examination of organ weights revealed enlarged kidneys in high-dose male rats at 13 weeks, enlarged ovaries in high-dose female rats at 13 weeks, and microscopic study of tissue sections revealed minimal to mild renal tubular injury in high and possibly intermediate dose males at several sacrifices. These findings suggest that the primary target organ of PA, when given by inhalation, is the kidney in male rats and possibly the ovary in female rats. The renal changes in the high-dose males were not fully reversible during the recovery period.(ABSTRACT TRUNCATED AT 250 WORDS)     

Toxicity evaluation of petroleum blending streams: reproductive and developmental effects of light catalytic cracked naphtha distillate in rats

A distillate of light catalytic cracked naphtha (CAS number 64741-55-5, LCCN-D), administered by inhalation, was tested for reproductive and developmental toxicity in Sprague-Dawley rats, following a modified OECD Guideline 421, Reproductive/Developmental Toxicity Screening Protocol. LCCN-D was administered as a vapor, 6 h/d, 7 d/wk at target concentrations of 0, 750, 2500 or 7500 ppm to female rats for approximately 7 wk from 2 wk prior to mating, during mating through gestational d 19, and to males beginning 2 wk prior to mating for 8 consecutive weeks. Dams and litters were sacrificed on postnatal d 4, and males were sacrificed within the following week. Parental systemic effects observed at the 7500 ppm exposure level were increased kidney weights and relative liver weights in males and increased spleen weights in high-dose females. Livers and spleens from rats in the high-dose group were normal in appearance at necropsy. IncreaSed kidney weights in high-dose males were indicative of male-rat-specific light hydrocarbon nephropathy. No test-related microscopic changes were observed in the reproductive organs or nasal turbinate tissues of either sex. Reproductive performance was unaffected by treatment with LCCN-D. Fertility index was > or =90% in all dose groups. There were no exposure-related differences in implantation sites and live pups per litter, and no gross abnormalities were observed. Pups born from treated dams showed comparable body weights and weight gains to controls. The viability index on postpartum d 4 was > or =97%; the high-dose group had more male than female pups at birth and at d 4 postpartum. Under the conditions of this study, the no-observable-adverse-effect level (NOAEL) for exposure to light catalytic cracked naphtha distillate for parental toxicity was 2500 ppm and the NOAEL for reproductive performance and developmental toxicity was 7500 ppm.     

Tissue deposition patterns after chronic inhalation exposures of rats and guinea pigs to aluminum chlorhydrate.

Groups of rats and guinea pigs were exposed to 0.25, 2.5, or 25 mg/m³ aluminum chlorhydrate (ACH), the principle ingredient in antiperspirant deodorants, by inhalation for periods up to 24 months. The tissue deposition pattern of aluminum was determined as well as the effect of ACH on body weight gain and organ/body weight ratios. Decreases in body weight were seen in rats exposed to 2.5 and 25 mg/m³ ACH. Guinea pig weights were unaffected. Increases in lung to body weight ratios were seen in both species. The A1 appeared to be primarily contained in the lung. The only other organs with significant concentration of A1 were the peribronchial lymph nodes in the high dose guinea pigs and the adrenal glands of the medium- and high-dose rats.     

TOXICITY EVALUATION OF PETROLEUM BLENDING STREAMS: REPRODUCTIVE AND DEVELOPMENTAL EFFECTS OF LIGHT CATALYTIC CRACKED NAPHTHA DISTILLATE IN RATS

A distillate of light catalytic cracked naphtha (CAS number 64741-55-5, LCCN-D), administered by inhalation, was tested for reproductive and developmental toxicity in Sprague-Dawley rats, following a modified OECD Guideline 421, Reproductive/ Developmental Toxicity Screening Protocol. LCCN-D was administered as a vapor, 6 h/ d, 7 d/wk at target concentrations of 0, 750, 2500 or 7500 ppm to female rats for approximately 7 wk from 2 wk prior to mating, during mating through gestational d 19, and to males beginning 2 wk prior to mating for 8 consecutive weeks. Dams and litters were sacrificed on postnatal d 4, and males were sacrificed within the following week. Parental systemic effects observed at the 7500 ppm exposure level were increased kidney weights and relative liver weights in males and increased spleen weights in highdose females. Livers and spleens from rats in the high-dose group were normal in appearance at necropsy. Increased kidney weights in high-dose males were indicative of male-rat-specific light hydrocarbon nephropathy. No test-related m icroscopic changes were observed in the reproductive organs or nasal turbinate tissues of either sex. Reproductive performance was unaffected by treatment with LCCN-D. Fertility index was 90% in all dose groups. There were no exposure-related differences in implantation sites and live pups per litter, and no gross abnormalities were observed. Pups born from treated dams showed comparable body weights and weight gains to controls. The viability index on postpartum d 4 was 97% ; the high-dose group had more male than female pups at birth and at d 4 postpartum. Under the conditions of this study, the no-observable-adverse-effect level (NOAEL) for exposure to light catalytic cracked naphtha distillate for parental toxicity was 2500 ppm and the NOAEL for reproductive performance and developmental toxicity was 7500 ppm.     

Assessment of Toxicity of o-Nitrochlorobenzene in Rats following a 4-Week Inhalation Exposure

Assessment of Toxicity of o-Nitrochlorobenzene in Rats followinga 4-Week Inhalation Exposure. NAIR, R.S., JOHANNSEN, F.R., LEVINSKAS,G.J., AND TERRILL, J.B. (1986). Fundam. Appl. Toxicol. 7, 609-614.o-Nitrochlorobenzene (ONCB) is a chemical intermediate usedfor the synthesis of various industrial chemicals. To evaluatethe subchronic toxicity of this compound, three groups of 15male and 15 female Sprague-Dawley rats were exposed to ONCBvapor 6 hr/day, 5 days/week for 4 weeks at target concentrationsof 10, 30, or 60 mg/m³. A control group of 15 animals/sex wasexposed to room air in a separate inhalation chamber. Concentrationsof ONCB in the chambers were determined at least three timesa day using a uv spectrophotometer. Parameters monitored inthis study included observation for signs of toxicity, bodyweights, ophthalmoscopic exam, hematology, and clinical chemistry.At necropsy, selected organ weights were recorded and over 35tissues/animal were examined microscopically for all controland high-exposure level animals. No mortality was observed inthis study. Mean body weights of all groups were comparableto controls. Animals exposed to the mid and high concentrationsof ONCB showed a significant increase in blood methemoglobinand a significant decrease in hemoglobin, hematocrit, and redblood cell counts. Spleen and liver weights (absolute and relativeto body weight) were significantly increased for these two groups.Microscopic changes, observed only in the spleen, included increaseddegree of extramedullary hematopoiesis and hemosiderosis. Thesedata suggest that the toxicity of ONCB is comparable to thatof its structural analog, p-nitrochlorobenzene. Thus these twocompounds should have similar workplace exposure limits.     

Evaluation of subchronic inhalation toxicity of dimethyl disulfide in rats

This study was carried out to investigate the potential subchronic inhalation toxicity of dimethyl disulfide (DMDS) via whole-body exposure in F344 rats. Groups of 10 rats of each sex were exposed to DMDS vapor by whole-body exposure at concentrations of 0, 5, 25, or 125 ppm for 6 h/day, 5 days/wk for 13 wk. All the rats were sacrificed at the end of treatment period. During the test period, clinical signs, mortality, body weights, food consumption, ophthalmoscopy, urinalysis, hematology, serum biochemistry, gross findings, organ weights, and histopathology were examined. At 25 ppm, a decrease in the body weight gain, food intake, aspartate aminotransferase (AST), alanine aminotransferase (ALT), and blood urea nitrogen (BUN) was observed in the males, but not in the females. However, at 125 ppm, a decrease in the body weight gain, food intake, and thymus weight and an increase in the weights of adrenal glands were observed in both genders. Serum biochemical investigations revealed a decrease in the AST, ALT, BUN, creatine phosphokinase (CPK), and triglyceride levels and an increase in the glucose level. In contrast, no treatment-related effects were observed in the 5 ppm group. The toxic potency of DMDS was slightly higher in males than that in females. In these experimental conditions, the target organ was not determined in rats. The no-observed-adverse-effect concentration (NOAEC) was found to be 5 ppm, 6 h/day for male rats and 25 ppm, 6 h/day for female rats.     

Evaluation of Subchronic Inhalation Toxicity of Dimethyl Disulfide in Rats

This study was carried out to investigate the potential subchronic inhalation toxicity of dimethyl disulfide (DMDS) via whole-body exposure in F344 rats. Groups of 10 rats of each sex were exposed to DMDS vapor by whole-body exposure at concentrations of 0, 5, 25, or 125 ppm for 6 h/day, 5 days/wk for 13 wk. All the rats were sacrificed at the end of treatment period. During the test period, clinical signs, mortality, body weights, food consumption, ophthalmoscopy, urinalysis, hematology, serum biochemistry, gross findings, organ weights, and histopathology were examined. At 25 ppm, a decrease in the body weight gain, food intake, aspartate aminotransferase (AST), alanine aminotransferase (ALT), and blood urea nitrogen (BUN) was observed in the males, but not in the females. However, at 125 ppm, a decrease in the body weight gain, food intake, and thymus weight and an increase in the weights of adrenal glands were observed in both genders. Serum biochemical investigations revealed a decrease in the AST, ALT, BUN, creatine phosphokinase (CPK), and triglyceride levels and an increase in the glucose level. In contrast, no treatment-related effects were observed in the 5 ppm group. The toxic potency of DMDS was slightly higher in males than that in females. In these experimental conditions, the target organ was not determined in rats. The no-observed-adverse-effect concentration (NOAEC) was found to be 5 ppm, 6 h/day for male rats and 25 ppm, 6 h/day for female rats.     

A 90-Day Inhalation Toxicity Study with Benomyl in Rats

A 90-Day Inhalation Toxiaty Study with Benomyl in Rats. WARHEIT,D. B., KELLY, D. P., CARAKOSTAS, M. C., AND SINGER, A. W. (1989).Fundam Appl Toxicol./ 12, 333-345. Benomyl [methyl 1-(butylcarbamoyl)-2-benzimidazolecarbamate,CAS Registry No. 17804-35-2] is a fungicide and the possibilityfor inhalation exposure exists for field workers. To assessthe toxicity of benomyl, groups of 20 male and 20 female CDrats were exposed nose-only 6 hr a day, 5 days a week, to concentrationsof 0, 10, 50 or 200 mg/m³ of a benomyl atmosphere. At the midpoint(approximately 45 days on test) and at the end of the exposureperiod, blood and urine samples for clinical evaluation werecollected from 10 rats/group/sex, and these animals were sacrificedfor pathological examination. Similar evaluations were performadon all remaining rats at the end of the 90-day test period.After approximately 45 days on test, compoundrelated degenerationof the olfactory epithelium was observed in all males and in8 of 10 female rats exposed to 200 mg/m³ benomyl. Two male ratsexposed to 50 mg/m³ had similar, although less severe, areasof olfactory epithelial degeneration. After approximately 90days of exposure, the remaining 10 rats/group/sex were sacrificedand examined. Of these rats, all of the males and females exposedto 200 mg/m³ had olfactory degeneration, along with 3 malesexposed to 50 mg/m³ of benomyl. No other observed lesions wereinterpreted to have been caused by the benomyl exposure. Inaddition, male rats exposed to 200 mg/m³ benomyl had depressedmean body weights compared to controls and this finding correlatedwith a reduction in food consumption. Based on pathologicalobservations, 10 mg/m³ represents the no-observable-effect level(NOEL) for the male rats, and 50 mg/m³ is the NOEL for the femalerats.     

Oral (drinking water) two-generation reproductive toxicity study of dibromoacetic acid (DBA) in rats

In a two-generation study of dibromoacetic acid (DBA), Crl SD rats (30 rats/sex/group/generation) were provided DBA in drinking water at 0 (reverse osmosis-deionized water), 50, 250, and 650 ppm (0, 4.4 to 11.6, 22.4 to 55.6, and 52.4 to 132.0 mg/kg/day, respectively; human intake approximates 0.1 microg/kg/day [0.0001 mg/kg/day]). Observations included viability, clinical signs, water and feed consumption, body and organ weights, histopathology, and reproductive parameters (mating, fertility, abortions, premature deliveries, durations of gestation, litter sizes, sex ratios and viabilities, maternal behaviors, reproductive organ weights, sperm parameters and implantation sites, sexual maturation). Histopathological evaluations were performed on at least 10 P and F1 rats/sex at 0 and 650 ppm (gross lesions, testes, intact epididymis; 10 F1 dams at 0, 250, and 650 ppm for primordial follicles). Developmental observations included implantations, pup numbers, sexes, viabilities, body weights, morphology, and reproductive performance. At 50 ppm and higher, both sexes and generations had increased absolute and relative liver and kidneys weights, and female rats in both generations had reduced absolute and relative adrenal weights; adrenal changes were probably associated with physiological changes in water balance. The livers and kidneys (10/sex/group/generation) had no histopathological changes. Other minimal effects at 50 ppm were reduced water consumption and a transient reduction in body weight. At 250 and 650 ppm, DBA reduced parental water consumption, body weight gains, body weights, feed consumption, and pup body weights. P and F1 generation male rats at 250 and 650 ppm had altered sperm production (retained step 19 spermatids in stages IX and X tubules sometimes associated with residual bodies) and some epididymal tubule changes (increased amounts of exfoliated spermatogenic cells/residual bodies in epididymal tubules, atrophy, and hypospermia), although inconsistently and at much lower incidences. Unilateral abnormalities of the epididymis (small or absent epididymis) at 650 ppm in four F1 generation male rats were considered reproductive tract malformations. The no-observable-adverse-effect level (NOAEL) and reproductive and developmental NOAELs for DBA were at least 50 ppm (4.5 to 11.6 mg/kg/day), 45,000 to 116,000 times the human adult exposure level. Reproductive and developmental effects did not occur in female rats exposed to DBA concentrations as high as 650 ppm. Based on the high multiples of human exposure required to produce effects in male rats, DBA should not be identified as a human reproductive or developmental risk.     

Repeated exposure inhalation study of pentane in rats

Pentane (CAS No. 109-66-0) is a chemical being used as a co-solvent in a polymer production facility with potential for inhalation exposure in humans. To assess the toxicity of pentane, groups of 10 male rats each were exposed by inhalation, 6 hr/day, 5 days/week for 2 weeks to either 0 (control), 1,000, 3,000 or 10,000 ppm. Five rats per group were killed following the 10th exposure; the remaining 5/group were killed after a 14-day post-exposure recovery period. Parameters investigated were clinical signs of toxicity, functional behavior, body weights, clinical pathology, and gross and microscopic pathology including organ weights. No unusual clinical observations were seen in the pentane-treated rats, and body weights were not altered. Test rats generally exhibited normal behavioral responses in the functional observational battery. Increases in serum calcium and phosphorus concentrations were seen in rats exposed to either 3,000 or 10,000 ppm. These were reversible during the 2-week recovery period. No other clinical pathology changes were observed and no pentane-related tissue pathology was seen in any of the groups. The no-observed-adverse-effect level was 1,000 ppm with reversible clinical pathology changes produced at 3,000 and 10,000 ppm.     

REPEATED EXPOSURE INHALATION STUDY OF PENTANE IN RATS

Pentane (CAS No. 109-66-0) is a chemical being used as a co-solvent in a polymer production facility with potential for inhalation exposure in humans. To assess the toxicity of pentane, groups of 10 male rats each were exposed by inhalation, 6 hr/day, 5 days/week for 2 weeks to either 0 (control), 1,000, 3,000 or 10,000 ppm. Five rats per group were killed following the 10th exposure; the remaining 5/group were killed after a 14-day post-exposure recovery period. Parameters investigated were clinical signs of toxicity, functional behavior, body weights, clinical pathology, and gross and microscopic pathology including organ weights. No unusual clinical observations were seen in the pentane-treated rats, and body weights were not altered. Test rats generally exhibited normal behavioral responses in the functional observational battery. Increases in serum calcium and phosphorus concentrations were seen in rats exposed to either 3,000 or 10,000 ppm. These were reversible during the 2-week recovery period. No other clinical pathology changes were observed and no pentane-related tissue pathology was seen in any of the groups. The no-observed-adverse-effect level was 1,000 ppm with reversible clinical pathology changes produced at 3,000 and 10,000 ppm.     

Subchronic Inhalation Toxicity of Methyl Isoamyl Ketone in Rats

Subchronic Inhalation Toxicity of Methyl Isoamyl Ketone in Rats.KATZ, G. V., RENNER, E. R., JR., AND TERHAAR, C. J. (1986).Fundam. Appl. Toxicol. 6, 498–505. Rats were exposed byinhalation, 6 hr/day, 5 days/week, to target vapor concentrationsof 2000, 1000, or 0 ppm of methyl isoamyl ketone (MIAK) for12 exposures spanning 16 days, and 2000, 1000, 200, or 0 ppmfor 69 exposures spanning 96 days. Body weights, hematology,and serum clinical chemistry determinations were comparableto controls in both inhalation studies. Clinical signs of toxicitywere lethargy and decreased aural response (2000 ppm, 2-weekstudy; 2000 and 1000 ppm, 90-day study) and nasal and eye irritation(2000 and 1000 ppm, 90-day study). In addition, the excretionof gel-like casts in seminal fluid was seen in males exposedto 2000 and 1000 ppm in both studies. increases in absoluteand relative liver and kidney weights were observed in bothsexes following exposure to 2000 and 1000 ppm in the 2-weekand 90-day studies. Liver weight increases were exposure dependentand in the 90-day study reflected hepatocyte hypertrophy observedon microscopic examination. Microscopic kidney changes werehyalin degeneration or hyalin droplet formation in males inthe 2-week (2000 and 1000 ppm) and 90-day (2000 ppm) studies;and minor to moderate regeneration of tubular epithelium (2000and 1000 ppm) in both studies. Minor tubular epithelium regenerationwas seen in females exposed to 2000 ppm for 90 days. The toxicityof MIAK following inhalation exposure was not as extensive orsevere as that resulting from a prior study in which male ratswere dosed orally with 2000 mg/kg/day (a dose comparable to2000 ppm) for 13 weeks. The 90-day inhalation exposure no-observed-effectlevel for toxicity was 200 ppm MIAK.     

Evaluation of the Developmental Toxicity of Ethylene Glycol Aerosol in the CD Rat and CD-1 Mouse by Whole-Body Exposure

Ethylene glycol (EG) is a major industrial chemical, shown tobe teratogenic at high doses by gavage in rodents. Since oneroute of industrial exposure is to the aerosol at high concentrations,timed-pregnant CD rats and CD-1 mice were exposed, whole-body,to a respirable aerosol of EG (mass median aerodynamic diameter,2.3 µm) on Gestational Days (GD) 6 through 15 for 6 hrper day at target exposure concentrations of 0, 150, 1000, or2500 mg/m³ (analytical concentrations of 0, 119 ± 13,888 ± 149, and 2090 ± 244 mg/m³, respectively),with 25 plug-positive animals per species per group. Clinicalobservations and maternal body weights were documented throughoutgestation for both species. Maternal food and water consumptionwas measured in rats only throughout gestation. At schedulednecropsy (GD 21 for rats, GD 18 for mice), maternal animalswere evaluated for body weight, liver weight, kidney weight,gravid uterine weight, number of ovarian corpora lutea, andstatus of implantation sites, i.e., resorptions, dead fetuses,live fetuses. Fetuses were dissected from the uterus, counted,weighed, sexed, and examined for external, visceral, and skeletalmalformations and variations. All rat dams survived to scheduledtermination. Minimal maternal toxicity was indicated by a significantincrease in absolute and relative liver weight at 2500 mg/m³.Food and water consumption, maternal body weights and weightgain, and maternal organ weights (other than liver) were unaffectedby exposure. Gestational parameters were unaffected by exposure,including pre- and post-implantation loss, live fetuses/litter,sex ratio, and fetal body weight/litter. There was no treatment-relatedincrease in the incidence of any individual malformation, inthe incidence of pooled external, visceral, or skeletal malformations,or in the incidence of total malformations by fetus or by litter.There were no increases in the incidence of external or visceralvariations. Evidence of fetotoxicity, expressed as reduced ossificationin the humerus, the zygomatic arch, and the metatarsals andproximal phalanges of the hind-limb, was observed at 1000 and2500 mg/m³. All mouse dams survived to scheduled termination.One dam at 2500 mg/m³ was carrying a totally resorbed litterat termination. Maternal toxicity was observed at 1000 and 2500mg/m³, expressed as reduced body weight and weight gain duringand after the exposure period, and reduced gravid uterine weight.(Maternal effects may have been due, in part or in whole, toeffects on the conceptuses; see below.) Embryo/fetal toxicitywas also observed at 1000 and 2500 mg/m³, expressed as an increasein nonviable implantations/litter, a reduction in viable implantations/litter,and reduced fetal body weights (male, female, and total)/litter.The incidences of individual and pooled external, visceral,and skeletal malformations were increased at 1000 and 2500 mg/m³,as was the incidence of total malformations. Malformations werefound in the head (exencephaly), face (cleft palate, foreshortenedand abnormal face, and abnormal facial bones), and skeleton(vertebral fusions, and fused, forked, and missing ribs). Theincidences of many fetal variations were also increased at 1000and 2500 mg/m³ (and only a few at 150 mg/m³). The no observableadverse effect level (NOAEL) for maternal toxicity in rats was1000 mg/m³ (analytical concentration 888 mg/m³) and in micewas 150 mg/m³ (analytical concentration 119 mg/m³). The NOAELfor development toxicity in rats was 150 mg/m³ and in mice wasat or below 150 mg/m³, under the conditions of this study. Analysisof EG on the fur of rats and mice during and after the exposureperiod at 2500 mg/m³ indicated that much of the EG "dose" (65–95%)was potentially derived from ingestion after grooming and/orpercutaneous absorption. This contribution of the ingested and/orabsorbed chemical could have been sufficient, per se, to producethe teratogenic effects observed in mice. The definitive evaluationof the possible role of inhaled EG aerosol alone in teratogenesisrequires an exposure regimen which limits or precludes exposureby any other route.     

Biochemical toxicology and disposition of Therminol 66 heat transfer fluid after inhalation or after dietary administration to male Sprague-Dawley rats.

The objectives of this study were to determine the disposition of Therminol 66 in rats and to determine the effects of this heat-transfer fluid on liver and kidney microsomal drug-metabolizing enzymes. Therminol 66 was administered to male Sprague-Dawley rats at various doses as either a single oral administration at 0, 100, or 300 mg/kg, or as a single 6-h inhalation exposure at 0 or 350 mg/m3. Animals were killed 48 h after gavage or after termination of inhalation exposure. Additional groups of animals were exposed to Therminol 66 via the diet at 0, 100, 500, or 5000 ppm for 14 d, or via repeated inhalation exposure at 0, 25, 250, or 1200 mg/m3 for 6 h/d for 14 d. These exposure scenarios represent approximately equivalent doses of Therminol 66 by the different routes of administration. No change in body weight was observed after acute oral or inhalation exposure, and little change in body weight was observed in animals administered Therminol 66 via the diet except at the highest dose. There was no change in kidney weight, and liver weights were increased only at the higher doses of Therminol 66. The body weight gain of animals exposed to Therminol 66 via inhalation decreased in a dose-dependent manner over the 2-wk exposure period. Results from the disposition study indicated that Therminol 66 did not appear to accumulate in the tissues examined and did not appear to be extensively absorbed after a single oral dose of 300 mg/kg. The whole-body elimination half-life was approximately 14 h and occurred primarily via the feces. There was no significant induction of hepatic aryl hydrocarbon hydroxylase (AHH) activity after single oral or inhalation exposures to Therminol 66. Ethoxycoumarin O-deethylase (ECOD) was significantly induced only in animals exposed to 350 mg/m3 via inhalation. Repeated dietary and inhalation exposures resulted in AHH and ECOD induction only at the highest doses, and the kidney appeared to be less sensitive than the liver. Animals exposed via inhalation demonstrated a greater hepatic inductive effect than did animals exposed via the diet, which may be due to absorption differences.(ABSTRACT TRUNCATED AT 400 WORDS)     

Oral (drinking water) two-generation reproductive toxicity study of bromodichloromethane (BDCM) in rats

Bromodichloromethane (BDCM) was tested for reproductive toxicity in a two-generation study in CRL SD rats. Thirty rats/sex/ group/generation were continuously provided BDCM in drinking water at 0 (control carrier, reverse osmosis membrane-processed water), 50,150, and 450 ppm (0, 4.1 to 12.6, 11.6 to 40.2, and 29.5 to 109.0 mg/kg/day, respectively). Adult human intake approximates 0.8 microg/kg/day (0.0008 mg/kg/day). P and F1 rats were observed for general toxicity (viability, clinical signs, water and feed consumption, body weights, organ weights [also three weanling Fl and F2 pups/sex/litter], histopathology [10/sex, 0- and 450-ppm exposure groups]) and reproduction (mating, fertility, abortions, premature deliveries, durations of gestation, litter sizes, sex ratios, viabilities, maternal behaviors, reproductive organ weights [also three weanling Fl and F2 pups/sex/ litter], sperm parameters, and implantations. F1 rats were evaluated for age at vaginal patency or preputial separation. Ten P and F1 rats/sex from the 0- and 450-ppm exposure groups and rats at 50 and 150 ppm with reduced fertility were evaluated for histopathology (gross lesions, testes, intact epididymis, all F1 dams for number of primordial follicles). Developmental parameters in offspring included implantation and pup numbers, sexes, viabilities, body weights, gross external alterations, and reproductive parameters (Fl adults). Toxicologically important, statistically significant effects at 150 and/or 450 ppm included mortality and clinical signs associated with reduced absolute and relative water consumption, reduced body weights and weight gains, and reduced absolute and relative feed consumption (P and F1 rats). Significantly reduced body weights at 150 and 450 ppm were associated with reduced organ weights and increased organ weight ratios (% body and/or brain weight). Histopathology did not identify abnormalities. Small delays in sexual maturation (preputial separation, vaginal patency) and more Fl rats with prolonged diestrus were also attributable to severely reduced pup body weights. Mating, fertility, sperm parameters, and primordial ovarian follicular counts were unaffected. The no-observable-adverse-effect level (NOAEL) and the reproductive and developmental NOAELs for BDCM were at least 50 ppm (4.1 to 12.6 mg/kg/day), 5125 to 15,750 times the human adult exposure level, if delayed sexual maturational associated with severely reduced body weights is considered reproductive toxicity. If considered general toxicity, reproductive and developmental NOAELs for BDCM are greater than 450 ppm (29.5 to 109.0 mg/kg/day), or 36,875 to 136,250 times the human adult exposure level. Regardless, these data indicate that BDCM should not be identified as a risk to human reproductive performance or development of human conceptuses.     

Repeat oral dose toxicity studies of melamine in rats and monkeys

Melamine is an important and widely used organic industrial chemical. Recently, clinical findings of renal failure and kidney stones in infants have been associated with ingestion of melamine-contaminated infant formula. To understand the toxicity and clinical outcome of melamine exposure, repeated oral dose studies in rats and monkeys were performed to characterize the subchronic toxicity of melamine. Assessment of toxicity was based on mortality, clinical signs, body weights, ophthalmic findings, clinical pathology, gross pathology, organ weights, and microscopic observations. The first rat study was intended to be a 14-day oral study followed by an 8-day recovery period. The dose levels were 140, 700, and 1,400 mg/kg/day (lowered to 1,000 mg/kg/day subsequently due to mortality). Oral administration of melamine at 700 mg/kg/day for 14 consecutive days in rats produced compound-related clinical signs (red urine), decreased body weights, and changes in clinical pathology (increased serum urea nitrogen and creatinine) and anatomical pathology (renal tubular cell debris, crystal deposition, and hyperactive regeneration of renal tubular epithelium). The kidney was identified as the target organ. Oral administration at 1,400 mg/kg/day (subsequently lowered to 1,000 mg/kg/day) resulted in animal death and moribundity. There were no treatment-related findings in the 140 mg/kg/day group. There were no compound-related findings in the high-dose recovery animals. The second rat study was a 5-day oral toxicity study with genomic biomarkers assayed in the kidney tissues. At the top dose of 1,050 mg/kg/day, similar clinical and anatomical pathology findings as described above were observed. The genes measured, Kim-1, Clu, Spp1, A2m, Lcn2, Tcfrsf12a, Gpnmb, and CD44, were significantly up-regulated (fivefold to 550-fold), while Tff3 was significantly down-regulated (fivefold). These results indicated that genomic markers could sensitively diagnose melamine-induced kidney injury. A 3-month oral study with 4-week recovery in monkeys was also conducted. In this monkey study, the animals were treated with melamine at doses of 60, 200, or 700 mg/kg/day. The administration of 700 mg/kg/day melamine by nasal-gastric gavage to monkeys resulted in test article-related clinical signs including turbid and whitish urine, urine crystals, red blood cell changes, increased serum alanine aminotransferase and kidney and/or liver weights, and microscopic findings including nephrotoxicity, pericarditis, and increased hematopoiesis. Nephrotoxicity was also noted at 200 mg/kg/day. It was concluded that the kidney is the primary target organ and the NOAEL was estimated to be 140 mg/kg/day in rats following a 14-day oral administration and 60 mg/kg/day in the monkey study.     

Embryotoxicity Study of Monomeric 4,4'-Methylenediphenyl Diisocyanate (MDI) Aerosol after Inhalation Exposure in Wistar Rats

One of the uses of MDI is as an alternative to formaldehydein the manufacture of furniture, its main route of exposureto humans being by inhalation. There have been no previous studieson the potential prenatal toxic effects of this compound. Toclose this gap in information, gravid Wistar rats, Crl:(WI)BR,were exposed by whole-body inhalation to clean air (control)and to 1, 3, and 9 mg/m3 MDI, respectively, for 6 hr per dayfrom Days 6 to 15 post conception (p.c). Rats were killed onDay 20 p.c. and the following results were obtained: Treatmentcaused a dose-dependent decrease in food consumption in allsubstance-treated groups during exposure, returning to normalvalues after cessation of treatment. The lung weights in thehigh-dose group were significantly increased compared to thesham-treated control animals. Treatment did not influence anyother maternal and/or fetal parameters investigated (maternalweight gain, number of corpora lutea, implantation sites, pre–and postimplantation loss, fetal and placental weights, grossand visceral anomalies, degree of ossification), although aslight but significant increase in litters with fetuses displayingasymmetric sternebra(e) was observed after treatment with thehighest dose of 9 mg/m³. Although the relevance of an increaseof this minor anomaly in doses which cause toxic effects indams (reduced food consumption, increased lung weights) is limitedand the number observed is within the limits of biological variability,a substance-induced effect in the high-dose group cannot beexcluded with certainty. Consequently, a no embryotoxic effectlevel of 3 mg/m³ was determined.     

Prechronic Inhalation Toxicity Studies of 2-Mercaptobenzimidazole (2-MBI)in F344/N Rats

2-Mercaptobenzimidazole (2-MBI), used in rubber processing,is a suspect carcinogen structurally related to ethylene thiourea.The inhalation toxicity of 2-MBI was evaluated in male and femaleF344/N rats exposed 6 hr/day, 5 days/week to respirable aerosolsgenerated by spray atomization of aqueous suspensions of the2-MBI powder and subsequent drying of the resulting aerosols.Twelve exposures at target concentrations of 0, 6.3, 12.5, 25.0,50.0, or 100 mg/m³ of 2-MBI produced a dose-related reductionin body weight gains, thyroid follicular cell hyperplasia, adrenalcortex fatty change, and pituitary atrophy. Sub-chronic exposureswere conducted at target concentrations of 0, 3.1, 6.2, 12.5,25.0, and 50.0 mg/m³ of 2-MBI. Rats at 25 mg/m³ displayed hunchedposture, hypoactivity, and reduced body weight gain, with compoundrelated mortality at the highest exposure level. Anemia; increasedSGPT, SGOT, alkaline phosphatase, sorbitol dehydrogenase, BUN,and cholesterol; and reduced free fatty acid were seen in ratsat 25 mg/m³. Increased thyroid weight and thyroid follicularcell hyperplasia were noted in both sexes at 6.2 mg/m³, withreduced triiodothyronine and thyroxine levels in both sexesat > 12.5 mg/m³. Thyroid follicular cell hyperplasia wasalso seen in rats at 3.1 mg/m³. Thymus weights were significantlyreduced in both sexes at all exposure levels with liver weightincreases at 6.2 mg/m³. Exposure-related histopathologic changesincluded pituitary cytoplasmic vacuolization, adrenal cortexnecrosis, lymphoid depletion, thymic atrophy, liver cell hypertrophy,renal mineralization and tubular atrophy, and hypocellularityof the bone marrow.