Rat two-generation reproduction and dominant lethal study of acrylamide in drinking water.

Fischer 344 (F344) F(0) weanling rats, 30/sex/group, were exposed to acrylamide in drinking water at 0.0, 0.5, 2.0, or 5.0 mg/kg/day for 10 weeks and then mated. Exposure of F(0) females continued through gestation and lactation of F(1) litters. F(0) males, after F(0) mating, were removed from exposure and mated (one male: two untreated females) for the dominant lethal (DL) assay. Thirty F(l) weanlings/sex/group were exposed for 11 weeks to the same dose levels as their parents, and then mated to produce F(2) offspring. F(0) and F(l) parents and F(1) and F(2) weanlings were necropsied. Prebreeding exposure of F(0) and F(l) animals resulted in systemic toxicity at 2.0 to 5.0 mg/kg/day, with head tilt and/or foot splay increased at 0.5 to 5.0 mg/kg/day. F(0) and F(l) reproductive indices and gestational length were unaffected. Implantations and live pups/litter at birth were reduced at 5.0 mg/kg/day. Survival of F(l) and F(2) pups was reduced at 5.0 mg/kg/day for PND 0 through 4 only. In the DL assay, total and live implants were reduced, pre- and postimplantation loss was increased, and the frequency of DL factors (F(L)%) was increased at 5.0 mg/kg/day. At 5.0 mg/kg/day, adult F(l) male peripheral nerves exhibited axonal fragmentation and/or swelling; F(l) female spinal cord sections were unremarkable. The NOEL for prenatal DL was 2.0 mg/kg/day; the NOEL for adult systemic toxicity, including neurotoxicity, was < or = 0.5 mg/kg/day. Therefore, neurotoxicity and DL were differentially affected.

CT imaging of intrathoracic lymph nodes in dogs with bronchoscopically administered iodinated nanoparticles.

RATIONALE AND OBJECTIVES: The purpose of the study was to determine if airway instillation of iodinated nanoparticles results in contrast material enhancement of tracheobronchial lymph nodes in dogs. MATERIALS AND METHODS: Eight dogs underwent intrabronchial instillation of iodinated nanoparticles; six dogs received 900 mg each, and two dogs received 450 mg each. Spiral computed tomography (CT) was then performed 2-34 days later. RESULTS: CT scans obtained 2 days after instillation showed the presence of contrast material within the lung parenchyma but no nodal enhancement. Scans obtained 6-34 days after instillation showed enhancement of the right, left, and middle tracheobronchial lymph nodes (analogous to the mediastinal nodes in humans). Mean nodal attenuation on CT images was 117 HU +/- 43, and the mean nodal volume was 129 mm3 +/- 113. Histologic specimens of the nodes showed macrophage hyperplasia. CONCLUSION: Iodinated nanoparticles instilled into small airways are transported to the tracheobronchial lymph nodes, where they result in contrast enhancement.

Developmental toxicity evaluation of inhaled toluene diisocyanate vapor in CD rats.

Mated female CD (Sprague-Dawley) rats, 25/group, were exposed to toluene diisocyanate (TDI) vapor, for six h/day on gestational days (gd) 6 through 15, at 0.00, 0.02, 0.10, or 0.50 p.p.m.. Maternal clinical signs, body weights, and feed and water consumption were recorded throughout gestation. At termination (gd 21), maternal body, gravid uterine, and liver weights were recorded. Corpora lutea were counted, and implantation sites were identified: resorptions and dead and live fetuses. All live fetuses were examined for external alterations. One-half of the live fetuses/litter were examined for visceral (including craniofacial) alterations. The remaining intact fetuses/litter were stained with alizarin red S and examined for ossified skeletal alterations. Maternal toxicity at 0.50 ppm consisted of reduced body weights, body weight gains, feed consumption, and clinical signs of toxicity. Water consumption was unaffected. Gestational parameters exhibited no significant treatment-related changes, including pre- and postimplantation loss, sex ratio/litter, or fetal body weights/litter. Incidences of individual malformations, malformations by category (external, visceral, and skeletal), total malformations, individual external and visceral variations, variations by category, and total variations were unaffected. Of 111 skeletal variants observed, only 1, incidence of poorly ossified cervical centrum 5, was increased at 0.50 ppm, indicating possible minimal fetotoxicity, although it occurred in the absence of any other indications of developmental toxicity. Therefore, exposure to TDI vapor by inhalation, during major organogenesis in CD rats, resulted in maternal toxicity and minimal fetotoxicity at 0.50 ppm no observed adverse effect level (NOAEL) for maternal and developmental toxicity was 0.10 ppm. No treatment-related embryotoxicity or teratogenicity was observed.

Two-generation reproductive toxicity study of inhaled toluene diisocyanate vapor in CD rats.

Twenty-eight 42-day-old pups/sex/group (F0) were exposed to toluene diisocyanate vapor (TDI; 80% 2,4-TDI, 20% 2,6-TDI) by inhalation at 0.0, 0.02, 0.08, or 0.3 ppm, 6 h/day, 5 days/week, for 10 weeks, then mated within groups for 3 weeks, with exposure 7 days/week during mating, gestation, and lactation. F0 maternal animals were not exposed from gestational day (gd) 20 through postnatal day (pnd) 4; maternal exposures resumed on pnd 5. Twenty-eight weanlings/sex/group continued exposure for 12 weeks (starting on pnd 28) and were bred as described above. F0 and F1 parents and ten F1 and F2 weanlings/sex/group were necropsied, and adult reproductive organs, pituitary, liver, kidneys, and upper respiratory tract (target organs) were evaluated histologically in ten/sex/group. Adult toxicity was observed in both sexes and generations at 0.08 and 0.3 ppm, including occasional reductions in body weights and weight gain, clinical signs of toxicity at 0.08 and 0.3 ppm, and histologic changes in the nasal cavities at 0.02, 0.08, and 0.3 ppm (including rhinitis, a nonspecific response to an irritating vapor, at all concentrations). There was no reproductive toxicity, reproductive organ pathology, or effect on gestation or lactation at any exposure concentration. Postnatal toxicity and reduced body weights and weight gains during lactation occurred only in F2 litters at 0.08 and 0.3 ppm. Therefore, under the conditions of this study, a no observed adverse effect level (NOAEL) was not determined for adult toxicity; the NOAEL for reproductive toxicity was at least 0.3 ppm, and the NOAEL for postnatal toxicity was 0.02 ppm.

Pulmonary delivery of nanoparticles of insoluble, iodinated CT X-ray contrast agents to lung draining lymph nodes in dogs.

Lung cancer continues to be a leading cause of death around the world. Staging of this disease is critically dependent upon the involvement or noninvolvement of the lymph nodes which drain the region of lung containing the lesion/tumor. Palpation, unenhanced CT, and lymph node excision (i.e., mediastinectomy) are currently used to ascertain the status of these regional draining lymph nodes. The work reported herein details the first efforts toward the pulmonary instillation of iodinated nanoparticles for contrast-enhanced CT of lung draining lymph nodes. The data reflect the impact of dose, time post instillation, and formulation (surfactant) upon the observed CT enhancement of the tracheobronchial lymph nodes of beagle dogs. In addition, initial safety is discussed with both macroscopic and microscopic observations. The results indicate that pulmonary instillation of small volumes of iodinated nanoparticles could be successfully used to aid staging of lung cancer by CT imaging.

Short-term and subchronic repeated exposure studies with 5-ethylidene-2-norbornene vapor in the rat.

5-Ethylidene-2-norbornene (ENB) is an industrial chemical whose physical properties indicate a likelihood for vapor exposure to humans. The potential for target organ or cumulative toxicity was investigated in rats exposed for 6 h per day for 9 days over an 11-day period, or 66 or 67 days over 14 weeks; 4- week recovery animals were added to the 14-week study. Mean analytically measured ENB vapor concentrations (+/-SD) were 52 +/- 1.5, 148 +/- 2.3 and 359 +/- 4.2 ppm for the 9-day study and 4.9 +/- 0.14, 24.8 +/- 1.23 and 149 +/- 4.40 ppm for the subchronic study. There were no mortalities, and clinical signs were limited to periocular swelling and/or encrustation, and urogenital area wetness. Body weight gain was decreased in the 9-day 359 ppm females and in the subchronic 24.8 and 149 ppm males. A minimal macrocytic anemia was present in subchronically exposed males, which resolved during the recovery period. In the 9-day study increased liver weight was associated with minimal centrilobular hepatocytomegaly and cytoplasmic basophilia with no degenerative or serum biochemical liver function changes, suggesting an adaptive response. Only relative liver weights were increased in the subchronic 149 ppm males, and no histopathological findings were observed. Principal target organ effects were to the thyroid gland, which showed an exposure concentration-related, but not exposure time-related, depletion of follicular colloid that resolved during the recovery period, together with light microscopic evidence for a hypertrophic and hyperplastic response in the follicular epithelium that resolved more slowly. The thyroid colloid depletion was a graded effect without a clear no-effect concentration, but was not accompanied by any clinical or clear biochemical evidence for thyroid dysfunction. A no-effect concentration of 4.9 ppm was established for the follicular cytological effects.

Dental dysplasia in rats and mice.

Malformations of the maxillary incisors, diagnosed as dental dysplasia, were observed as a spontaneous background lesion in 3% (females) to 9% (males) of CD-1 mice and 14.5% (females) to 10.5% (males) of CD (Sprague-Dawley) rats in a chronic inhalation study. Lesions were reported grossly as overgrown, maloccluded, or malformed incisors. Microscopic findings included tooth pulp and periodontal abscesses, fractured and necrotic teeth, periodontal cysts, malformations of the incisor roots, and expansile masses, including odontomas, of the incisor roots. Development of lesions followed a pattern of tooth pulp necrosis and/or traumatic disruption of the epithelial root sheath at the base of the tooth. Feeding a powdered ration, which reduced the normal wearing of the incisors, and repeated clipping of overgrown incisors were believed to contribute to the incidence of disease.

Assessment of the developmental toxicity of ethylene glycol applied cutaneously to CD-1 mice.

Ethylene glycol (EG; CAS No. 107-21-1) is teratogenic to mice by whole-body exposure to an aerosol at high concentrations, but results were confounded by possible exposure from ingestion after grooming and/or from percutaneous absorption. Therefore, CD-1 mice were exposed to EG on Gestational Days (GD) 6 through 15, 6 hr/day by occluded cutaneous application at 0, 12.5, 50, or 100% (undiluted) EG (0.1 ml/animal, equivalent to approximately 0, 404, 1677, or 3549 mg/kg/day [10 ml/kg, positive control gavage (PCGG)], 30 females/group. Dams were weighed and evaluated daily (including application site) for clinical signs and water consumption throughout gestation. On GD 18, maternal uterus, liver, and paired kidneys were weighed; kidneys of 0 and 100% and the PCGG were examined microscopically. Corpora lutea and implantation sites were recorded. Live fetuses were weighed, sexed, and examined for structural alterations. For cutaneously exposed dams, there was no treatment-related maternal, no differences in pre- or postimplantation loss in fetal body weights/litter, and no increased incidences of any fetal malformations. Two skeletal variations, increased at 100% may represent effects of restraint stress and/or findings due to chance. In the PCGG, 8 females (26.7%) died, water consumption was increased, fetal body weights/litter were reduced, and fetal malformations and variations were increased. PCGG kidneys exhibited tubular nephrosis and tubular cell degeneration, with no oxalate crystals, documenting renal toxicity at this oral dose in mice. Minimal-grade renal tubular lesions observed in 3 mice (of 30) at 100% EG may represent treatment-related or incidental findings. Therefore, exposure of pregnant CD-1 to 0, 12.5, 50 or 100% EG during organogenesis by occluded cutaneous application resulted in minimal or no observable maternal or developmental toxicity at 100% (approximately 3549 mg/kg/day), the NOEL.

Determination of a no-observed-effect level for developmental toxicity of ethylene glycol administered by gavage to CD rats and CD-1 mice.

Previous studies have indicated that ethylene glycol (EG) is a developmental toxicant in rats and mice primarily when ingested. This study was designed to establish no-observed-effect levels (NOELs) for developmental toxicity of EG administered by gavage in both rodent species. Dams were administered EG on Gestation Days 6-15; rats were given 0, 150, 500, 1000, or 2500 mg EG/kg/day; mice were dosed with 0, 50, 150, 500, or 1500 mg EG/kg/day. In rat dams given 2500 mg EG/kg/day, water consumption was increased during treatment and body weights were reduced throughout gestation; liver and kidney weights were increased at euthanization (Gestation Day 21). Relative liver weights were also increased at 1000 mg/kg/day. Effects observed in rat fetuses at 2500 mg/kg/day included the following: hydrocephaly; gastroschisis; umbilical hernia; fused, duplicated, or missing arches, centra, and ribs; poor ossification in thoracic and lumbar regions; and reduced body weights. Reduced body weights, duplicated or missing ribs, centra, and arches, and poor ossification were also observed in rat fetuses at 1000 mg/kg/day. In mice, there was no apparent treatment-related maternal toxicity. In mouse fetuses (Gestation Day 18), effects were observed at 1500 mg/kg/day and included reduced body weights, fused ribs and arches, poor ossification in thoracic and lumbar centra, and increased occurrence of an extra 14th rib. At 500 mg/kg/day, slight reductions in fetal body weight and increased incidences of extra ribs were observed. Under conditions of these studies, NOELs for developmental toxicity were 500 mg/kg/day for rats and 150 mg/kg/day for mice, indicating that mice were more susceptible than rats to the teratogenic effects of EG.

Evaluation of the developmental toxicity of ethylene glycol aerosol in CD-1 mice by nose-only exposure.

Ethylene glycol (EG; CAS No. 107-21-1) is teratogenic to mice by whole-body (WB) exposure to aerosol (1000-2500 mg/m3). The WB results were confounded by possible exposure from ingestion after grooming and/or from percutaneous absorption. Therefore, CD-1 mice were exposed to EG aerosol (MMAD 2.6 +/- 1.7 microns) on Gestational Days (GD) 6 through 15, 6 hr/day, by nose-only (NO) (0, 500, 1000, or 2500 mg/m3) or WB exposures (0 or 2100 mg/m3, as positive control), 30/group. Five additional "satellite" females each at 2500 mg/m3 NO and 2100 mg/m3 WB were exposed on GD 6 for measurement of EG on fur. Control environments were water aerosol (4200 mg/m3 for NO; 2700 mg/m3 for WB). Females were weighed and evaluated for clinical signs and water consumption throughout gestation. On GD 18, maternal uterus, liver, and kidneys (2) were weighed, with kidneys examined microscopically. Corpora lutea and implantation sites were recorded. Live fetuses were weighed, sexed, and examined for structural alterations. For NO dams, kidney weights were increased at 1000 and 2500 mg/m3; no renal lesions and no other treatment-related maternal toxicity were observed. There were no effects on pre- or postimplantation loss; fetal body weights/litter were reduced at 2500 mg/m3. At 2500 mg/m3, incidences of fused ribs and skeletal variations were increased. The 2500 mg/m3 NO satellite animals had approximately 330 mg/kg extractable EG. The WB group exhibited maternal and developmental toxicity including increased fetal skeletal malformations and variations, confirming previous results, with 1390 mg/kg extractable EG on fur. Therefore, exposure of CD-1 mice to a respirable EG aerosol during organogenesis by NO inhalation resulted in minimal maternal toxicity at 1000 and 2500 mg/m3 and developmental toxicity at 2500 mg/m3. The NOAEL was 500 mg/m3 NO for maternal and 1000 mg/m3 NO for developmental toxicity. This study supports the interpretation of the initial EG WB results as due to systemic exposure from noninhalation routes since limiting noninhalation routes prevented almost all of the effects (including teratogenicity) observed in mice after WB exposure.

Repeated exposure toxicity of 2-ethyl-1,3-hexanediol by cutaneous applications to the rat for 9 and 90 days.

2-Ethyl-1,3-hexanediol (EHD; CASRN 94-96-2), an industrial chemical and insect repellent, has a high potential for recurrent skin contact. Short-term (9 d) and subchronic (13 w) repeated epicutaneous contact studies were conducted to determine the potential for cumulative local skin irritation and systemic toxicity in Fischer 344 rats. Doses were 0.5, 2.0 or 4.0 ml/kg/d of undiluted EHD. There were no clinical signs and no treatment-related effects on hematology, clinical chemistry or histology of a large number of organs and tissues including the treated skin. The only effects where slight decreases in body weight gain for the high-dose males in the 9-d study and males and females of the high-dose group in the subchronic study; slight decreases in food consumption for females of all treatment groups in the subchronic study; and slight increases in relative liver weight for high-dose females in the 9-d study and high-dose males in the subchronic study, which is probably a compensatory hypertrophy for the metabolism of EHD. Thus, recurrent epicutaneous applications of undiluted EHD to the rat did not cause any local skin irritation or cumulative or organ-specific toxicity.

Two-week aerosol inhalation study on polyethylene glycol (PEG) 3350 in F-344 rats.

PEGs in the 3000 to 4000 MW range are used in many pharmaceutical and cosmetic applications; they produce little ocular or dermal irritation and have extremely low acute and subchronic toxicity by oral and dermal routes of administration. However, little information exists on the potential of aerosols of these materials to produce adverse health effects. F-344 rats were exposed to aerosols of PEG 3350 (20% w:w in water) at 0, 109, 567, or 1008 (highest attainable) mg/m3 for 6 hr/d, 5 d/wk for 2 wk. No exposure-related toxicity was found with regard to clinical signs, ophthalmology, serum chemistry, urinalysis, or gross pathology. Exposure-related effects included: a 50% increase in the neutrophil count (males only) at 1008 mg/m3; decreased body weight gain (16%) for both the 567 and 1008 mg/m3 groups (males only); absolute lung weights of both sexes were increased 10 and 18% for the 567 and 1008 mg/m3 groups, respectively. A slight increase in the number of macrophages in the alveoli was the only change observed histologically in all PEG 3350-exposed groups. Therefore, inhalation of aerosols of PEG 3350 at concentrations up to 1008 mg/m3 produced relatively little toxicity in rats, the lung was the target organ, and the no-observable-effect-level was between 109 to 567 mg/m3.

Corneal dystrophy in Fischer 344 rats.

A spontaneous degenerative lesion of the cornea resembling calcific band keratopathy in man has been observed in 10-15% of the F-344 rats (aged 35-300 days) purchased from a private vendor's closed breeding colony. The lesion appears clinically as punctuate to linear superficial corneal opacities located in the interpalpebral fissure of one or both eyes. Occasional roughening, bleb formation, or pitting of the corneal surface resembling superficial ulcers may be observed. The lesion occurs in both sexes. It is rarely associated with inflammation or irritation. Histologically, it consists of mineral deposits along the epithelial basement membrane and Bowman's space, some of which are large enough to disrupt or destroy portions of the basilar epithelium. Energy dispersive X-ray analysis of the deposits proved them to be composed of calcium and phosphorus. Electron microscopic examination revealed a variety of extracellular laminated and crystalline arrays similar to those seen in humans with band keratopathy. The etiology of the lesion is as yet undetermined. A genetic-associated susceptibility due to hypercalcemia may be involved.

Pulmonary fibrosis produced in F-344 rats by subchronic inhalation of aerosols of a 4000 molecular weight ethylene oxide/propylene oxide polymer.

Inhalation of aerosols of the ethylene oxide/propylene oxide polymer (U-5100) evaluated in this study has previously been shown in acute and 2-week studies to produce toxicologic effects on the lungs, with increased lung weights and microscopic findings of congestion and hemorrhage of pulmonary alveolar capillaries and necrosis of alveolar epithelial cells (D. R. Klonne, D.J. Nachreiner, D. E. Dodd, P. E. Losco, and T.R. Tyler, 1987, Fundam. Appl. Toxicol. 9, 773-784). In the present studies, F-344 rats were exposed 6 hr/day, 5 day/week for 2 weeks to aerosols at mean concentrations of 0, 0.9, or 5.0 mg/m3 or for 13 weeks to mean concentrations of 0, 0.3, 1.1, or 5.2 mg/m3. Following the 2-week study, minimal multifocal hemorrhage and eosinophilic proteinaceous debris in alveoli were observed in the 0.9 mg/m3 group; similar lesions plus alveolar cell necrosis were found in the 5 mg/m3 group. In the 13-week study, the 5.2 mg/m3 group had a slight decrease in body weight gain, while increases in absolute and/or relative lung weights occurred for both the 1.1 and 5.2 mg/m3 groups at the end of the exposure regimen and at the end of a 5-week recovery period. Histologic lesions of the lungs occurred in all U-5100-exposed groups and consisted of hemorrhage, alveolar histocytosis, interstitial pneumonia, and multifocal fibrosis. The incidence and severity of the pulmonary lesions were concentration related.(ABSTRACT TRUNCATED AT 250 WORDS)

The acute toxicity and primary irritancy of 1-propoxy-2-propanol.

1-Propoxy-2-propanol, a widely used industrial chemical, was found to have acute peroral LD50 values in the rat of 4.92 ml/kg (males) and 2.83 ml/kg (females), with the signs of systemic toxicity being principally related to narcosis. Acute percutaneous LD50 values in the rabbit (24-hr occluded) were 4.29 ml/kg (males) and 4.92 ml/kg (females); signs of systemic toxicity were related to narcosis, and local effects were severe inflammation and corrosion. There were signs of sensory irritation of the eye during a 6-hr exposure to a dynamically generated saturated vapor atmosphere, but no signs of toxicity during exposure or in a 14-hr day postexposure observation period. A 4-hr occluded cutaneous application with 0.5 ml PP in rabbits produced mild to moderate erythema and edema of about 3 days duration, but no signs of corrosion. Contamination of the eye (0.005 to 0.1 ml PP) produced moderate to severe conjunctivitis (hyperaemia and chemosis), with mild iritis and diffuse mild keratitis; spontaneously healing occurred within 3 days (0.005 ml) to 7 days (0.1 ml). The major acute hazards with PP are by swallowing, splash contamination of the eye, and sustained skin contact.

Hyalin droplet nephrosis in male Fischer-344 rats following inhalation of diisobutyl ketone.

Four groups, each consisting of 10 male and 10 female Fischer-344 rats, were exposed 6 h/day, 5 days/week, for 9 days to diisobutyl ketone (DIBK) vapor at concentrations of 905, 300, 98, or 0 (control) ppm. An additional 10 rats/sex were assigned to the 905 and 0 ppm groups and allowed two weeks recovery prior to sacrifice. Rats exposed to 905 ppm had mild ocular irritation (lacrimation) and evidence of kidney toxicity, manifested as: 1) an increase in absolute and relative (as a percentage of body weight) kidney weights, 2) an increase in urine volume (and water intake) with a concomitant decrease in urine osmolality (males only), and 3) an increase in severity of hyalin droplet nephrosis in the proximal tubules (males only). Absolute and relative liver weights were also increased in both male and female rats of the 905 and 300 ppm groups. These effects either disappeared or lessened in severity following the 2-week recovery period. Male rats exposed to 300 ppm had similar renal alterations to the males of the 905 ppm group, although the alterations were fewer in number and smaller in magnitude. Kidney weights and renal histology of the males of the 98 ppm group were similar to the control male rats, although an increase in urine volume with a decrease in urine osmolality was observed. The kidney findings in this study were not surprising because of the chemical relationship of DIBK with other aliphatic ketones (e.g., methyl isobutyl ketone, methyl isoamyl ketone) which, after repeated inhalation exposure, cause hyalin droplet nephropathy in male rats. The significance of this male rat nephrosis with regard to human exposure is unknown.

Acute and 2-week inhalation toxicity studies on aerosols of selected ethylene oxide/propylene oxide polymers in rats.

The ethylene oxide/propylene oxide (EO/PO) polymers evaluated in this study have previously been shown to have a low order of toxicity and/or irritancy by ocular, dermal, or oral routes of administration. These studies evaluated the acute inhalation toxicity of respirable aerosols of three EO/PO compounds (U-660, U-2000, and U-5100) that differ in chain length, molecular weight, and viscosity. The respective 4-hr LC50 values (95% confidence limits) for U-660, U-2000, and U-5100 in Wistar albino rats were 4670 (4090-5320), 330 (227-480), and 106 (45-245) mg/m3. Occasionally, slight increases in respiration rate and slight hyperactivity were observed during the postexposure period. All deaths were delayed for 2-5 days postexposure. Body weight gains were transiently depressed in rats exposed to U-2000 and U-5100. Discolored lungs and livers occurred in animals which died during the 14-day postexposure period. Subsequently, a repeated-exposure study was conducted on U-5100 in F-344 rats exposed for 6 hr/day, 5 days/week, for 9 exposures at mean concentrations of 0, 5, 26, and 50 mg/m3. Portions of the control and 50 mg/m3 groups were maintained for an additional 2-week recovery period. Exposure-related effects included transient urogenital wetness in 50 mg/m3 group females; decreased body weight gain (7-29%) in all U-5100 groups except the 5 mg/m3 group females; increases in absolute (17-52%) and relative lung weights in all U-5100 groups; macroscopic red foci in the lungs; and microscopic findings of congestion and hemorrhage of pulmonary alveolar capillaries and necrosis of alveolar epithelial cells. Lung weights remained elevated after the 2-week recovery period, but the severity of the microscopic lesions was noticeably less, indicating partial reversibility of the lesions. In conclusion, EO/PO polymers have a higher order of toxicity by inhalation in comparison to other routes of administration, vary considerably in their acute lethal toxicity as a function of chain length/molecular weight, and induce pulmonary hemorrhage, and possibly edema, following repeated aerosol exposures at concentrations as low as 5 mg/m3.

Influence of housing conditions for mice on the results of a dermal oncogenicity bioassay.

Male C3H/HeJ mice were thrice weekly given 25 microliter applications of 0.25, 0.05, or 0.01% (w/w) benzo(a)pyrene (BaP) in acetone, or acetone alone, to clipped dorsal skin from 12 to 14 weeks of age for the remainder of their life spans. There were two groups of 40 mice for each treatment regimen, one group being housed in conventional stainless-steel wire mesh cages and the other in polycarbonate cages with wood shavings held in an enclosed ventilated cabinet. Under both housing conditions, tumor incidence was directly related and latency inversely related to BaP concentration. The time-adjusted incidence of epidermal neoplasms was significantly greater for the groups housed in polycarbonate cages. Mortality rates were directly related to BaP concentration and were significantly enhanced by the polycarbonate-cage housing conditions for the high and intermediate concentrations. Survival patterns for the two acetone control groups were similar. These findings indicate that differences in housing conditions can influence both the incidence and the latency of local neoplasms produced in response to the chronic application of a carcinogen in dermal oncogenesis bioassays.

Canine multilobular osteosarcoma of the skull with metastasis.

A 6-year-old crossbreed dog had recurring nodular masses on the dorsum of the head which were diagnosed as multilobular osteosarcoma. At necropsy, metastases were present throughout the lungs. Histological features of the masses included multiple islands of cartilage and bone separated by a dense fibrovascular stroma. These tumours are slow growing malignant neoplasms which may metastasize.