Only monoamine neurotransmitters

www.selleckchem.com/products/pci-32765.html were assessed and in only three brain regions. Mn may affect other neurotransmitter, neurotrophins, receptors, transporters, or morphology that were not examined here. As noted above, this experiment did not include assessments of the permanence of the changes observed or test for their effects on cognitive or other behavioral functions. We fostered 1-2 pups into litters short 1 or 2 pups; across the study this amounted to 2.6% of pups in-fostered, a proportion unlikely to impact the findings (see [64]). It is also worth mentioning that rats were weaned on P28 and the last samples were taken on P29, only 24 h post-weaning which could conceivably be an added stressor. A comparison of the P19 baseline levels of corticosterone and the P29 baseline levels in controls shows that corticosterone levels were lower on P29 than on P19, suggesting that weaning was not a stressor. Despite limitations, the data demonstrate that developmental Mn alters brain neurotransmitters in several brain regions important for behavior and the effects were age- and sex-dependent. The data suggest that developmental Mn exposure should be investigated further for possible Selleckchem Apitolisib long-term effects. The authors declare no conflict of interest, financial or otherwise. “
“The state of Baja California Sur (BCS), Mexico, is geographically bounded by the Sea

of Cortes (east) and the Pacific Ocean (west), and has the largest coastline of any state in Mexico. Fish and shellfish are important dietary components for women of child-bearing age in BCS [1]. Fish consumption is particularly advantageous for pregnant women as it contains high concentrations of omega 3 (ω3) polyunsaturated fatty acids (PUFA), and amino acids that are essential for the developing fetal brain ([2] and [3]). However, a diet rich in finfish may be reasonably regarded as a major pathway of exposure to mercury

(Hg) [4] and [5] and other contaminants. Mercury exists in three general forms with different bioavailability and toxicity profiles: elemental (Hg0), inorganic (typically divalent, Hg+2), and PAK6 organic Hg (e.g., monomethyl mercury, MeHg+) as discussed in Trasande et al. [6]. It is well known that MeHg+ concentration can increase with increasing trophic level, a phenomenon referred to as biomagnification [5]. Several reports have described the Hg concentrations in BCS coastal sediments [7], [8] and [9]. Total Hg concentration ([THg]) has been reported for biological samples from BCS coast predators such as blue sharks and yellowfin tuna with [THg] up to 1.69 ± 0.18 μg g−1 and 0.15 ± 0.10 μg g−1, respectively, in muscle of the largest specimens [10] and [11]. Exposure to MeHg+ from a diet rich in fish, or any other sources, during the pre-natal stage could be associated with serious effects on the central nervous system [12].