Abstract. Benign proliferative fibro-osseous lesions of the rostral mandible in six young horses are classified as equine juvenile mandibular ossifying fibroma. Histologically there is a characteristic abrupt transition from subgingival fibroblastic stroma to a zone of proliferating osteoblasts that form irregular spicules of osteoid. The layer of proliferating osteoblasts blends with a deeper zone of bony trabeculae rimmed by osteoblasts and separated by intertrabecular spaces of moderate cellular density. Incomplete surgical excision resulted in local recurrence, while rostral mandibulectomies resulted in no recurrence. The predilection for the rostral mandible of young horses coupled with the similar clinical, radiographic, and histological characteristics supports the classification of this lesion as a distinct entity.

The safety profile of afoxolaner, a new isoxazoline molecule, was evaluated following the regulatory requirements when administered six times orally in a soft chewable formulation at a dose of at least 1×, 3× or 5× the maximum exposure dose (6.3mg/kg) in 8-week-old Beagle dogs. Thirty-two healthy puppies (16 males and 16 females) were enrolled and allocated randomly to one of four treatment groups. Treatments were administered at three, one-month dose intervals (Days 0, 28 and 56) followed by three, 2-week dose intervals (Days 84, 98 and 112). The study ended at Day 126. The groups were: Group 1: non-treated control; Group 2: afoxolaner chews administered at a dosage of at least 6.3mg/kg (1×); Group 3: afoxolaner chews administered at a dosage of at least 18.9 mg/kg (3×); and Group 4: afoxolaner chews administered at a dosage of at least 31.5mg/kg (5×). All dogs were examined for general health twice a day beginning on at least Day-14. Physical examinations, and blood collections for clinical pathology analysis and afoxolaner plasma concentrations, were performed throughout the study. On Day 126, 2 weeks following the last treatment, all dogs were humanely euthanized prior to the conduction of a full necropsy with tissue collection. No afoxolaner-related changes were observed in growth, physical variables, clinical pathology variables, or tissues examined histologically. No clinically or statistically significant health abnormalities related to the administration of afoxolaner were observed. Vomiting and diarrhea were observed sporadically across all groups including the controls. The kinetics of afoxolaner plasma concentrations was linear following 6 doses of 6.3, 18.9 and 31.5mg/kg and dose proportionality was demonstrated. There were no statistical differences (p<0.05) between samples taken on Days 55 and 83 when compared to Day 27. Based upon the results of this study, afoxolaner was shown to be safe when administered repeatedly in a soft chewable formulation at up to 5× the maximum exposure dose in dogs as young as 8 weeks of age.

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An adult male pigeon (Columba livia) was presented to the Wildlife Service at the University of Pennsylvania School of Veterinary Medicine for depression, cachexia, and diarrhea. Five days after the initial presentation, the bird died and was necropsied. Gross lesions included opaque air sacs and multiple 1-mm yellow-white foci on the epicardial surface of the heart. Histopathologic lesions included a pericarditis, epicarditis, and multifocal hepatic necrosis accompanied by eosinophilic inclusion bodies. Ultrastructural examination of the hepatic inclusions revealed viral particles consistent with a herpesvirus. The gross, light microscopic, and electron microscopic findings are consistent with pigeon herpesvirus infection.

The safety profile of afoxolaner (an isoxazoline molecule) when combined with milbemycin oxime (a macrocyclic lactone) was evaluated according to the regulatory requirements when administered six times orally in a soft chewable formulation at a dose of at least 1×, 3×, or 5× the maximum exposure dose in 8-week-old Beagle dogs. Thirty-two healthy puppies (16 males and 16 females) were enrolled and allocated randomly to one of four treatment groups. Three doses were administered at 28-day intervals (Days 0, 28, and 56), followed by three additional doses administered with 14-day intervals (Days 84, 98, and 112). The study ended on Day 126. Treatment groups were as follows: Group 1: untreated, sham-dosed control; Group 2: afoxolaner/milbemycin oxime chews administered at a dose of at least 5 and 1 mg/kg, respectively (1×); Group 3: afoxolaner/milbemycin oxime chews administered at a dose of at least 15 and 3 mg/kg, respectively (3); and Group 4: afoxolaner/milbemycin oxime chews administered at a dose of at least 25 and 5 mg/kg, respectively (5×). All dogs were examined for general health twice a day beginning on Day -14. Physical examinations, and blood collections for clinical pathology analysis and afoxolaner and milbemycin oxime plasma concentrations, were performed throughout the study. No afoxolaner/milbemycin oxime treatment-related changes were observed in growth, physical variables, clinical pathology variables, or tissues examined histologically. No clinically relevant or statistically significant health abnormalities related to the administration of afoxolaner/milbemycin oxime were observed. No signs of macrocyclic lactone sensitivity were observed at any time during the study. Vomiting and diarrhea were observed sporadically across all groups including the controls. Based upon the results of this study, afoxolaner/milbemycin oxime soft chewables were shown to be safe when administered repeatedly at up to 5× the maximum exposure dose in dogs as young as 8 weeks of age.

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The reproductive and developmental toxicity of cyclohexane was assessed in a two-generation reproduction study with Crl:CD BR rats and in developmental toxicity studies with Crl:CD BR rats and Hra:(NZW)SPF rabbits. The animals were exposed whole-body to atmospheric concentrations of 0, 500, 2000, or 7000 ppm cyclohexane. In the two-generation reproduction study, parental effects included statistically significantly lower mean body weight, overall mean body weight gain, and overall mean food efficiency for P1 and F1 females of the 7000 ppm level and statistically significantly lower mean body weight for F1 males of that level. Adult rats exposed to 2000 ppm cyclohexane and above exhibited a transient diminished or absent response to a sound stimulus while in the chambers during exposure. Mean pup weight was statistically significantly lower than control from lactation day 7 throughout the remainder of the 25-day lactation period for both F1 and F2 7000 ppm litters. Changes observed at 500 ppm were either considered not to be compound related or not adverse. Therefore, the systemic-toxicity no-observed-effect level (NOEL) was 500 ppm and the reproductive NOEL was 2000 ppm. The reproductive NOEL was based solely on the decreased pup weights in both the F1 and F2 generations observed at 7000 ppm. In the developmental toxicity studies, only the rats showed evidence of maternal toxicity. For rats in the 7000 ppm group, statistically significant reductions were observed in overall maternal body weight gain and overall maternal food consumption for the treatment period. Rats exposed to 2000 ppm cyclohexane and above again exhibited a transient diminished or absent response to a sound stimulus while in the chambers during exposure. Therefore, for rats, the maternal no-observed-effect level (NOEL) was 500 ppm. In the rabbit developmental toxicity study, no compound-related maternal effects were observed at concentration levels of 7000 ppm and below. Therefore, the maternal NOEL for rabbits was 7000 ppm. No compound-related evidence of developmental toxicity was observed at any test concentration in either species. Therefore, the developmental NOEL for both species was 7000 ppm, the highest concentration tested.