Chronic kidney disease (CKD) is a common progressive disease that is typically characterized by the permanent loss of functional nephrons. As injured nephrons become sclerotic and die, the remaining healthy nephrons undergo numerous structural, molecular, and functional changes in an attempt to compensate for the loss of diseased nephrons. These compensatory changes enable the kidney to maintain fluid and solute homeostasis until approximately 75% of nephrons are lost. As CKD continues to progress, glomerular filtration rate decreases, and remaining nephrons are unable to effectively eliminate metabolic wastes and environmental toxicants from the body. This inability may enhance mortality and/or morbidity of an individual. Environmental toxicants of particular concern are arsenic, cadmium, lead, and mercury. Since these metals are present throughout the environment and exposure to one or more of these metals is unavoidable, it is important that the way in which these metals are handled by target organs in normal and disease states is understood completely.
The effect of limbic forebrain stimulation on pituitary-adrenal function was assessed by evaluating plasma corticosterone obtained prior to and following sham or electrical stimulation of urethane (1.20 g/kg) anesthetized female rats. Cortical electroencephalogram (EEG), electrocardiogram (ECG), heart rate (HR), mean arterial blood pressure (MAP), and respiration were routinely monitored. Timed blood samples (0.25 ml) were obtained from a catheterized femoral artery. The HR (Bts/min), MAP (mm of Hg), and corticosterone levels (microgram/dl) for 7 non-stimulated rats averaged over 6 sampling periods were 385 +/- 19,95 +/- 6, and 70.3 +/- 5.8 respectively. In electrically or sham stimulated rats, blood samples were taken just prior to stimulation (biphasic square waves, 100 microA, 50 or 60 Hz, 1 ms, 1 s on/1 s off for 15 or 30 min) and 5, 10, 15, and 30 min after initiation of stimulation. Significant changes in plasma corticosterone levels were obtained following stimulation of hippocampal and amygdaloid areas. In contrast, no change in corticosterone concentration was observed following stimulation of cortex, corpus callosum, fornix and a variety of other CNS areas. Detailed analysis of hippocampal influence on urethane stimulated plasma corticosterone levels showed increased plasma corticosterone levels following stimulation of CA1. In contrast, stimulation of CA3, dentate (includes CA4) and the subiculum produced significant decreases in plasma corticosterone levels. No change in corticosterone levels was observed following sham stimulation. Collectively, these data indicate that consideration must be given to the possibility that differential neuroendocrine regulatory mechanisms reside within various limbic forebrain complexes and that electrical stimulation of limbic forebrain sites of urethane anesthetized rats may provide information regarding sites inhibitory to pituitary-adrenal activity.
Background Silver ions from silver nanoparticles (AgNP) or AgNPs themselves itself that are ingested from consumer health care products or indirectly from absorbed food contact material can interact with the gastrointestinal tract (GIT). The permeability of the GIT is strictly regulated to maintain barrier function and proper nutrient absorption. The single layer intestinal epithelium adheres and communicates actively to neighboring cells and the extracellular matrix through different cell junctions. In the current study, we hypothesized that oral exposure to AgNPs may alter the intestinal permeability and expression of genes controlling cell junctions. Changes in cell junction gene expression in the ileum of male and female rats administered different sizes of AgNP for 13-weeks were assessed using qPCR. Results The results of this study indicate that AgNPs have an altering effect on cell junctions that are known to dictate intestinal permeability. mRNA expression of genes representing tight junction ( Cldn1, Cldn5, Cldn6 , Cldn10 and Pecam1 ), focal adhesion ( Cav1, Cav2 , and Itgb2 ), adherens junction ( Pvrl1, Notch1 , and Notch2 ), and hemidesmosome ( Dst ) groups were upregulated significantly in females treated with 10 nm AgNP, while no change or downregulation of same genes was detected in male animals. In addition, a higher concentration of pro-inflammatory cytokine, TNF-α, was noticed in AgNP-treated female animals as compared to controls. Conclusions This study proposes that interaction of silver with GIT could potentially initiate an inflammatory process that could lead to changes in the gastrointestinal permeability and/or nutrient deficiencies in sex-specific manner. Fully understanding the mechanistic consequences of oral AgNP exposure may lead to stricter regulation for the commercial usage of AgNPs and/or improved clinical therapy in the future.
Consumer products manufactured with antimicrobial silver nanoparticles (AgNPs) may affect the gastrointestinal (GI) system. The human GI-tract is complex and there are physiological and anatomical differences between human and animal models that limit comparisons between species. Thus, assessment of AgNP toxicity on the human GI-tract may require tools that allow for the examination of subtle changes in inflammatory markers and indicators of epithelial perturbation. Fresh tissues were excised from the GI-tract of human male and female subjects to evaluate the effects of AgNPs on the GI-system. The purpose of this study was to perform an assessment on the ability of the ex vivo model to evaluate changes in levels of pro-/anti-inflammatory cytokines/chemokines and mRNA expression of intestinal permeability related genes induced by AgNPs in ileal tissues. The ex vivo model preserved the structural and biological functions of the in-situ organ. Analysis of cytokine expression data indicated that intestinal tissue of male and female subjects responded differently to AgNP treatment, with male samples showing significantly elevated Granulocyte-macrophage colony-stimulating factor (GM-CSF) after treatment with 10 nm and 20 nm AgNPs for 2 h and significantly elevated RANTES after treatment with 20 nm AgNPs for 24 h. In contrast, tissues of female showed no significant effects of AgNP treatment at 2 h and significantly decreased RANTES (20 nm), TNF-α (10 nm), and IFN-γ (10 nm) at 24 h. Smaller size AgNPs (10 nm) perturbed more permeability-related genes in samples of male subjects, than in samples from female subjects. In contrast, exposure to 20 nm AgNPs resulted in upregulation of a greater number of genes in female-derived samples (36 genes) than in male-derived samples (8 genes). The ex vivo tissue model can distinguish sex dependent effects of AgNP and could serve as a translational non-animal model to assess the impacts of xenobiotics on human intestinal mucosa.
Elemental mercury (Hg 0 ) contamination in artisanal and small-scale gold mining (ASGM) communities is widespread, and Hg 0 -contaminated tailings are often reprocessed with cyanide ( − CN) to extract residual gold remaining after amalgamation. Hg 0 reacts with − CN under aerobic conditions to produce Hg(CN) 4 2− and other Hg(CN) n n−2 complexes. The production of solvated Hg(CN) n n−2 complexes increases upon agitation in the presence of synthetic and authentic Hg 0 -contaminated tailings that aid in dispersing the Hg 0 , increasing its reactive surface area. Adult rats were exposed to various concentrations of Hg(CN) 2 , and accumulation in organs and tissues was quantified using direct mercury analysis. The primary site of Hg(CN) 2 accumulation was the kidney, although accumulation was also detected in the liver, spleen, and blood. Little accumulation was observed in the brain, suggesting that Hg(CN) 2 complexes do not cross the blood−brain barrier. Renal tissue was particularly sensitive to the effects of Hg(CN) 2 , with pathological changes observed at low concentrations. Hg(CN) 2 complexes are handled by mammalian systems in a manner similar to other inorganic species of Hg, yet appear to be more toxic to organ systems. The findings from this study are the first to show that Hg(CN) 2 complexes are highly stable complexes that can lead to cellular injury and death in mammalian organ systems.
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