Factors involved in increased protein synthesis in rat kidney after administration of DDT

Homogenates of kidney cortex obtained from control rats and rats treated with DDT have been separated into microsomes or ribosomes, and into postmicrosomal (S105) supernatant fraction or pH 5 supernatant fraction. The incorporation of [¹⁴C]phenylalanyl-tRNA into peptide was increased when microsomes derived from kidneys of DDT-treated rats were incubated with pH 5 supernatant fraction from control rats. Elongation factors (EF) 1 and 2, necessary for the binding of aminoacyltRNA to ribosomes and for translocation of peptidyl-tRNA from the A site to the P site of ribosomes, were present in the pH 5 supernatant fractions of kidney of control and DDT-treated rats and these fractions were incubated with KCl-washed ribosomes obtained from livers of control rats. The results provided evidence that the increased incorporation observed with the pH 5 supernatant fraction obtained from the DDT-treated animals could not be attributed to decreased ribonuclease activity or to increased elongation factor 2 activity but was due to an increase in elongation factor l activity.     

Object Discrimination Reversal As a Method to Assess Cognitive Impairment in Nonhuman Primate Enhanced Pre‐ and Postnatal Developmental (ePPND) Studies: Statistical Power Analysis

An important aspect of the enhanced pre‐ and postnatal developmental (ePPND) toxicity study in nonhuman primates (NHP) is that it combines in utero and postnatal assessments in a single study. However, it is unclear if NHP ePPND studies are suitable to perform all of the evaluations incorporated into rodent PPND studies. To understand the value of including cognitive assessment in a NHP ePPND toxicity study, we performed a power analysis of object discrimination reversal task data using a modified Wisconsin General Testing Apparatus (ODR‐WGTA) from two NHP ePPND studies. ODR‐WGTA endpoints evaluated were days to learning and to first reversal, and number of reversals. With α = 0.05 and a one‐sided t‐test, a sample of seven provided 80% power to predict a 100% increase in all three of the ODR‐WGTA endpoints; a sample of 25 provided 80% power to predict a 50% increase. Similar power analyses were performed with data from the Cincinnati Water Maze (CWM) and passive avoidance tests from three rat PPND toxicity studies. Groups of 5 and 15 in the CWM and passive avoidance test, respectively, provided 80% power to detect a 100% change. While the power of the CWM is not far superior to the NHP ODR‐WGTA, a clear advantage is the routine use of larger sample size, with a group of 20 rats the CWM provides ～90% power to detect a 50% change. Due to the limitations on the number of animals, the ODR‐WGTA may not be suitable for assessing cognitive impairment in NHP ePPND studies.     

Reproductive traits of the freshwater oyster Etheria elliptica (Bivalvia: Etheriidae) in the Pendjari River,Benin: implications for conservation

The African freshwater oyster Etheria elliptica, which is of great economic importance throughout the continent, is facing overharvesting in many fisheries in West Africa. Its reproductive traits (sex ratio, size at sexual maturity, oocyte diameter and fecundity) were studied at four stations located along the Pendjari River, northern Benin, in April 2013. Histological techniques were implemented to identify sex and gonad development stages. Oocyte sizes were measured based on the histological images and mean oocyte diameter was 38 µm. Fecundity, estimated by counting the developing eggs, averaged 106 724 eggs and increased significantly with shell size. The average sex ratio was approximately 1:1. Hermaphrodites were rare. Males reached sexual maturity at 57.6 mm dorsoventral height, earlier than females at 64.7 mm. The majority of the oyster specimens were in ripe-spawning stages, indicating that reproductive activities partly took place towards the end of the dry season. Both mature and immature individuals were subjected to harvesting at all the investigated fishing sites. The mean size of exploited oysters was 60.6 mm, lower than the size of females at maturity. Management strategies must enforce the minimum size of 65 mm required for harvesting, particularly in open access sites where juveniles are mostly harvested.