The antioxidant or pro-oxidant actions and their involvement in the epigenome regulation by the phytochemical phenolic antioxidants should be at least established in the cellular models under normal and pathophysiological states. The current review discusses the mechanisms of modulation of the mammalian cellular epigenome by the phytochemical phenolic antioxidants with implications in human diseases.
The actin crosslinking domain (ACD) is an actin-specific toxin produced by several pathogens, including life-threatening spp. of Vibrio cholerae, Vibrio vulnificus, and Aeromonas hydrophila. Actin crosslinking by ACD is thought to lead to slow cytoskeleton failure owing to a gradual sequestration of actin in the form of nonfunctional oligomers. Here we found that ACD converted cytoplasmic actin into highly toxic oligomers that potently "poisoned" the ability of major actin assembly proteins, formins, to sustain actin polymerization. Thus, ACD can target the most abundant cellular protein by employing actin oligomers as secondary toxins to efficiently subvert cellular functions of actin while functioning at very low doses. Author Manuscript Author ManuscriptAuthor Manuscript Author ManuscriptBacterial toxins are the deadliest compounds on the planet. As little as a single molecule of a delivered toxin can compromise vital functions or even kill an affected host cell (1, 2). This is achieved by amplification of a toxin enzymatic activity via signaling cascades (e.g. by cholera, pertussis, and anthrax toxins) or via enzymatic inhibition of vital host complexes present in relatively few copies (e.g. Shiga and diphtheria toxins acting on ribosomes). Such efficiency is crucial because i) the amount of a toxin produced early upon infection is limited by an initially small number of bacterial cells; ii) the host is protected by commensal bacteria; and iii) the host immune system efficiently neutralizes toxins by means of adaptive (antibodies) and innate (e.g. defensins) (3) humoral defense factors.Owing to its importance in multiple cellular processes, actin is a common target for bacterium-and parasite-produced toxins. Upon delivery to the cytoplasm of host cells via Type I (as part of MARTX toxin) (4) or Type VI (within VgrG1 toxin) (5) secretion systems, the actin crosslinking domain toxin (ACD) catalyzes the covalent crosslinking of K50 in subdomain 2 of one actin monomer with E270 in subdomain 3 of another actin monomer via an amide bond, resulting in the formation of actin oligomers (6, 7). The actin subunits in the oligomers are oriented similar to short-pitch subunits in the filament, except that a major twist of the subdomain-2, required to accommodate such orientation, disrupts the normal inter-subunit interface and precludes polymerization (6).The currently accepted mechanism of ACD toxicity, via sequestering of bulk amounts of actin as non-functional oligomers, is compromised owing to the high concentration (hundreds of micromolar) of actin in a typical animal cell. Extrapolation of in vitro determined rates of the ACD activity (7) to cellular conditions suggests that a single ACD molecule per cell (i.e. ~ 1 pM) would require over six months to covalently crosslink half of all cytoplasmic actin.In contrast to these estimations, the integrity of the intestinal cell monolayers was disrupted when only a small fraction of cellular actin (2-6%) was crosslinked by ACD ( Fig. 1A-C; fig. S1). To account fo...
BackgroundMechanisms of cardiovascular injuries from exposure to gas and particulate air pollutants are unknown.ObjectiveWe sought to determine whether episodic exposure of rats to ozone or diesel exhaust particles (DEP) causes differential cardiovascular impairments that are exacerbated by ozone plus DEP.Methods and resultsMale Wistar Kyoto rats (10–12 weeks of age) were exposed to air, ozone (0.4 ppm), DEP (2.1 mg/m3), or ozone (0.38 ppm) + DEP (2.2 mg/m3) for 5 hr/day, 1 day/week for 16 weeks, or to air, ozone (0.51 or 1.0 ppm), or DEP (1.9 mg/m3) for 5 hr/day for 2 days. At the end of each exposure period, we examined pulmonary and cardiovascular biomarkers of injury. In the 16-week study, we observed mild pulmonary pathology in the ozone, DEP, and ozone + DEP exposure groups, a slight decrease in circulating lymphocytes in the ozone and DEP groups, and decreased platelets in the DEP group. After 16 weeks of exposure, mRNA biomarkers of oxidative stress (hemeoxygenase-1), thrombosis (tissue factor, plasminogen activator inhibitor-1, tissue plasminogen activator, and von Willebrand factor), vasoconstriction (endothelin-1, endothelin receptors A and B, endothelial NO synthase) and proteolysis [matrix metalloprotease (MMP)-2, MMP-3, and tissue inhibitor of matrix metalloprotease-2] were increased by DEP and/or ozone in the aorta, but not in the heart. Aortic LOX-1 (lectin-like oxidized low-density lipoprotein receptor-1) mRNA and protein increased after ozone exposure, and LOX-1 protein increased after exposure to ozone + DEP. RAGE (receptor for advanced glycation end products) mRNA increased in the ozone + DEP group. Exposure to ozone or DEP depleted cardiac mitochondrial phospholipid fatty acids (DEP > ozone). The combined effect of ozone and DEP exposure was less pronounced than exposure to either pollutant alone. Exposure to ozone or DEP for 2 days (acute) caused mild changes in the aorta.ConclusionsIn animals exposed to ozone or DEP alone for 16 weeks, we observed elevated biomarkers of vascular impairments in the aorta, with the loss of phospholipid fatty acids in myocardial mitochondria. We conclude that there is a possible role of oxidized lipids and protein through LOX-1 and/or RAGE signaling.
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