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Preclinical imaging technologies are increasingly being applied to developmental toxicology studies in drug development to determine potential compound toxicity. Although most of these studies are conducted in a non-regulatory setting, there is interest in performing these imaging studies under applicable regulations, for example Good Laboratory Practices (GLP), to support regulatory decisions concerning drug safety. This manuscript will describe regulations and processes to consider when bringing an imaging technology into GLP compliance., (Copyright © 2014 Elsevier Inc. All rights reserved.)

This update (version 2) of the Terminology of developmental abnormalities in common laboratory mammals (version 1) by Wise et al. [Wise LD, Beck SL, Beltrame D, Beyer BK, Chahoud I, Clark RL, Clark R, Druga AM, Fueston MH, Guittin P, Henwood SM, Kimmel CA, Lindstrom P, Palmer AK, Petrere JA, Solomon HM, Yasuda M, York RG. Terminology of developmental abnormalities in common laboratory mammals (version 1). Teratology 1997;55:249-92] incorporates improvements and enhancements to both content and organization of the terminology, to enable greater flexibility in its application, while maintaining a consistent approach to the description of findings. The revisions are the result of an international collaboration among interested organizations, advised by individual experts and the outcomes of several workshops. The terminology remains organized into tables under the broad categories of external, visceral, and skeletal observations, following the manner in which data are typically collected and recorded in developmental toxicity studies. This arrangement of the tables, as well as other information provided in appendices, is intended to facilitate the process of specimen evaluation at the laboratory bench level. Only the commonly used laboratory mammals (i.e., rats, mice, rabbits) are addressed in the current terminology tables. The inclusion of other species that are used in developmental toxicity testing, such as primates, is considered outside the scope of the present update. Similarly, categorization of findings as, for example, "malformation" or "variation" remains unaddressed, in accordance with the overall principle that the focus of this document is descriptive terminology and not diagnosis/interpretation. The skeletal terms have been augmented to accommodate cartilage findings.

A subpopulation of the CF-1 mouse strain contains a spontaneous mutation in the P-glycoprotein (Pgp) mdr1a gene, which leads to a lack of mdr1a expression in the placenta as well as brain and intestine. Individual CF-1 mice can be identified according to their Pgp status by a restriction fragment length polymorphism. Male and female mice selected on the basis of Pgp genotype were mated and the pregnant dams exposed during gestation to the known Pgp substrate, L-652,280, the 8,9 Z photoisomer of the naturally occurring avermectin Bla, which is known to produce cleft palate in mice. Fetal examination demonstrated that within individual litters, fetuses deficient in Pgp (-/-) were 100% susceptible to cleft palate, whereas their +/- heterozygote littermates were less sensitive. The homozygous +/+ fetuses with abundant Pgp were totally insensitive at the doses tested. The degree of chemical exposure of fetuses within each litter was inversely related to expression of placental Pgp, which was determined by the fetal genotype. These results demonstrate the importance of placental Pgp in protecting the fetus from potential teratogens and suggest that Pgp inhibitors should be carefully evaluated for their potential to increase susceptibility to chemical-induced teratogenesis.

Rat sperm motility and membrane integrity were compared as endpoints for viability. Sperm motility was measured by computer-assisted semen analysis (CASA), whereas membrane integrity was assessed by flow cytometric analysis of sperm stained with two nucleic acid stains, SYBR-14 and propidium iodide. The two techniques were compared in experiments that examined sperm viability over time and by analysis of known mixtures of control and freeze/thaw-killed sperm. Results from the two approaches were quantitatively very similar. Sperm from rats treated with dibromoacetic acid (600 or 1200 mg/kg) or alpha-chlorhyrin (100 mg/kg) were also analyzed. Neither technique detected a treatment-related effect with dibromoacetic acid. CASA identified a significant decrease in sperm motility in alpha-chlorhyrin-treated rats, whereas flow cytometric analysis did not find a measureable change in sperm membrane integrity. Because decreases in sperm motility would be expected to directly affect fertility, CASA may be a more robust endpoint for risk assessment in reproductive toxicology studies than flow cytometric analysis of membrane integrity.

Reproductive toxicity studies are increasingly including assessments of sperm parameters including motility, morphology, and counts. While these assessments can provide valuable information for the determination of potential reproductive toxicity, the methods for conducting the assessments have not been well developed in all laboratories and are continually evolving. The use of different methods in different laboratories makes comparison of data among laboratories difficult. To address the differences in methods, a working group was convened to discuss methods currently in use, share data, and try to reach consensus about optimal methods for assessing sperm parameters in rats, rabbits, and dogs. This article presents the consensus report, as well as future research needs, with the hope that optimized common methods will aid in the detection of reproductive effects and enhance interlaboratory comparisons.

Finasteride, a 5 alpha-reductase inhibitor, was investigated for its effects on fertility in male rats as part of its preclinical safety assessment. Studies were initiated when the male Sprague-Dawley rats were either young (4 to 6 weeks old) or mature (15 weeks old). Treatment duration ranged from 6 to 32 weeks. Each male was cohabited with two untreated females at various periods during and after treatment. Litter parameters were evaluated on either day 14 or 20 of gestation. Males were necropsied at the end of treatment or 7 to 11 weeks following the end of treatment. The major findings of these studies were that 1) young rats given 20 to 80 mg/kg/day of finasteride first showed mild to moderate decreases in fertility after 12 weeks of treatment, whereas mature males (given only 80 mg/kg/day) did not show a similar decrease until 24 weeks of treatment, 2) fewer copulatory plugs and atrophy of prostates and seminal vesicles were associated with finasteride treatment, 3) the decreased fertility was only partial (ie, fertility index did not decrease below 48% of control in any study) and was not due to decreases in mating, 4) formation of copulatory plugs, organ weights, and fertility returned to normal levels after at least 6 weeks of drug withdrawal, and 5) the testes showed no histologic or weight changes that would explain the effect on fertility. These results show that the decreased fertility in male rats was associated with finasteride-induced inhibition of accessory gland secretions, an expected pharmacologic effect.

Oral administration of 80 mg/kg/day of finasteride, a potent specific inhibitor of 5 alpha-reductase, to sexually mature male Sprague-Dawley rats for 24 to 38 weeks caused an approximate 30% to 40% decrease in fertility. There were no effects on mating indices or implants per pregnant female. From the mating trials, a selected group of treated males with poor reproductive performance was compared to a selected group of control males with good reproductive performance. Observed matings showed no qualitative effects on mating behavior or ejaculation. However, finasteride-treated males did not form or formed small and improperly positioned copulatory plugs, which are required in rats to transport sperm into the uterus. Intrauterine insemination of epididymal sperm from males that were nonfertile by natural mating resulted in similar numbers of embryos and unfertilized oocytes recovered from controls and finasteride-treated males, confirming that there was no effect of finasteride on the ability of sperm to fertilize. Decreased fertility of finasteride-treated males was due to failure to form copulatory plugs and is related to decreased weight of seminal vesicles and prostate, an expected pharmacologic effect. Testes weight was unaffected. Decreased fertility in male rats after finasteride administration is considered a species specific effect. The mechanism of the decrease in rats is not likely to be relevant to species that do not form copulatory plugs.