ic and lusitropic effects on contractile function (KC2) and increased ventricular systolic pressure (Silva et al. 2015). Occupational exposure induced electrocardiogram disturbances, possibly associated to decreased RyR1 expression (Xie et al. 2019). Lead replaces calcium in cellular signaling and might bring about hypertension by PDE3 drug inhibiting the calmodulin-dependent synthesis of NO (KC5) (Vaziri 2008). Lead exposures have also been linked to dyslipidemia (KC7) (Dudka et al. 2014; Xu et al. 2017). Altered cardiac mitochondrial activity (KC8), including increased oxidant and malondialdehyde generation, was associated with lead exposure in animals (Basha et al. 2012; Davuljigari and Gottipolu 2020; Roshan et al. 2011). Lead-exposed male workers had dysfunctional ANS activity (KC9), manifest as a significant reduce of R-R interval variation for the duration of deep breathing (Teruya et al. 1991) and chronic exposure in rats triggered sympathovagal imbalance and decreased baroreflex PAR2 Storage & Stability sensitivity (Shvachiy et al. 2020; Sim s et al. 2017). Lead can enhance oxidative pressure (KC10) by altering cardiac mitochondrial activity (KC8) (Basha et al. 2012; Davuljigari and Gottipolu 2020; Roshan et al. 2011) and129(9) SeptemberArsenicArsenic is usually a unique example of a CV toxicant that may be both an authorized human therapeutic and an environmental contaminant. Arsenic exhibits a number of KCs, depending on dose and variety of exposure. Acute lethality benefits from mitochondrial collapse in several tissues, like blood vessels plus the myocardium (KC8). Arsenic trioxide is also utilized to treat leukemia and as an adjuvant in treating some strong tumors, but it is regarded amongst the most hazardous anticancer drugs for growing cardiac QTc prolongation and danger of torsade de pointes arrhythmias, potentially through direct inhibition of hERG present (Drolet et al. 2004) and altered channel expression (KC1) (Alexandre et al. 2018; Dennis et al. 2007). Arsenic trioxide also exhibits KCs 2, eight, and ten (Varga et al. 2015). In contrast towards the toxicities from arsenic therapies, chronic environmental arsenic exposure is closely linked with increased threat of coronary heart disease at exposures of one hundred lg=L in drinking water (Moon et al. 2018; Wu et al. 2014) and occlusive peripheral vascular disease at higher exposure levels (Newman et al. 2016). Chronic exposure from contaminated drinking water was linked to ventricular wall thickness and hypertrophy in young adults (Pichler et al. 2019). There is well-documented evidence that chronic environmental arsenic exposure exhibits KCs 5, six, 7, ten, and 11 (Cosselman et al. 2015; Moon et al. 2018; Straub et al. 2008, 2009; Wu et al. 2014).Environmental Health Perspectives095001-Figure 4. Important traits (KCs) associated with doxorubicin cardiotoxicity. A summary of how distinctive KCs of doxorubicin could impact the heart as well as the vasculature. Some detailed mechanisms are given, also as some clinical outcomes. Note: APAF1, apoptotic protease activating element 1; Undesirable, Bcl-2-associated agonist of cell death; Bax, Bcl-associated X; BclXL, B-cell lymphoma-extra massive; Ca2+ calcium ion; CASP3, caspase 3; CASP9, caspase 9; CytoC, cytochrome complex; ECG, electrocardiogram; eNOS, endothelial nitric oxide synthase; ER, estrogen receptor; Fe2+ , iron ion; LV, left ventricular; NADPH, nicotinamide adenine dinucleotide phosphate; ROS, reactive oxygen species; Topo II, topoisomerase II; UPS, ubiquitin-proteasome system.inhibiting glutathione synthesis and SOD (Navas-A