The cynomolgus monkey as a model for developmental toxicity studies: variability of pregnancy losses, statistical power estimates, and group size considerations.

BACKGROUND: This work evaluates pregnancy and infant loss in 1,069 vehicle-treated cynomolgus monkeys from 78 embryo-fetal development (EFD) studies and 14 pre-postnatal development (PPND) studies accrued during 1981-2007. METHODS: Losses were analysed by survival function and hazard ratio using logistic regression for influence of year, study type (e.g., dose duration), and test item route of administration (ig, im, iv, sc). RESULTS: Neither study type nor route of dosing affected pregnancy outcome. Losses were higher pre-1990 (104 losses/347 pregnancies) compared to 1990 onwards (94 losses/722 pregnancies). Losses were greatest before gestation day 50 and at parturition. Using post-1989 data, Monte-Carlo simulations of pregnancy outcomes were created. The power associated with the comparison of vehicle survival curves and simulated adverse survival curves was examined. This showed that EFD studies with initial vehicle group sizes of 16 and 20 have an 80% probability of having 13 and 16 ongoing pregnancies at gestational day 100, respectively. For PPND studies with initial vehicle group sizes of 16, 20, or 28, there is an 80% likelihood of having 9, 11, or 16 infants at day 7 post-partum, respectively. A PPND study initiated with group size 20 could detect a threefold increase of test item-related pregnancy or infant loss. CONCLUSIONS: For designing and managing primate developmental toxicity studies, this type of analysis provides an objective tool to facilitate decisions either by supplementing groups with additional pregnant animals or stopping a group because an adverse effect on offspring survival has already been adequately revealed.

Physiology and Endocrinology of the Ovarian Cycle in Macaques.

Macaques provide excellent models for preclinical testing and safety assessment of female reproductive toxicants. Currently, cynomolgus monkeys are the predominant species for (reproductive) toxicity testing. Marmosets and rhesus monkeys are being used occasionally. The authors provide a brief review on physiology and endocrinology of the cynomolgus monkey ovarian cycle, practical guidance on assessment and monitoring of ovarian cyclicity, and new data on effects of social housing on ovarian cyclicity in toxicological studies. In macaques, cycle monitoring is achieved using daily vaginal smears for menstruation combined with cycle-timed frequent sampling for steroid and peptide hormone analysis. Owing to requirements of frequent and timed blood sampling, it is not recommended to incorporate these special evaluations into a general toxicity study design. Marmosets lack external signs of ovarian cyclicity, and cycle monitoring is done by regular determinations of progesterone. Cynomolgus and marmoset monkeys do not exhibit seasonal variations in ovarian activity, whereas such annual rhythm is pronounced in rhesus monkeys. Studies on pair- and group-housed cynomolgus monkeys revealed transient alterations in the duration and endocrinology of the ovarian cycle followed by return to normal cyclicity after approximately six months. This effect is avoided if the animals had contact with each other prior to mingling. These experiments also demonstrated that synchronization of ovarian cycles did not occur.