The rising rate of heavy metal contamination due to industrialization, urbanization, and modern agricultural practices has posed unparalleled problems for natural ecosystems and food chains either through direct ingestion or contact with environmental contamination (McLaughlin et al. 1999; Miransari 2011). These heavy metals are non-biodegradable components that frequently concentrate in the root environment due to excessive use of unplanned municipal and industrial wastewater, sewage sludge, pesticides, and chemical fertilizers (Pandey and Pandey 2009; El-Ramady et al. 2015). Some of these heavy metals such as Pb, Cd, Cr, As, and Hg do not take part in any known physiological functions and are very toxic even at very low concentrations (Ernst et al. 2008; Garzón et al. 2011; Chong-qing et al. 2013). However, the essential elements such as Fe, Mn, Ni, Zn, Co, and Cu are required for the normal growth and metabolic processes of plants, but they become toxic when their concentrations exceed their permissible limits (Blaylock and Huang 2000; Sebastiani et al. 2004). The most widespread effect of this metal toxicity on plants is reduction in growth including low biomass accumulation, leaf chlorosis, necrosis, inhibition of seed germination, photosynthesis, altered water balance and nutrient availability, and senescence which ultimately leads to plant death (Carrier et al. 2003; DalCorso et al. 2010). An excess of metals alters various physio-biochemical processes by the stimulation of ROS, enzyme inactivation, blocking functional groups of metabolically important molecules, disrupting membrane integrity, and 70displacing essential metal ions from specific binding sites (Rascio and Navari Izzo 2011; Villiers et al. 2012). Therefore, this review is focused on a physiological and molecular approach to metal toxicity, ROS production, avoidance, and scavenging in the light of heavy metal stress in plants, with special attention on the emrging role of osmoprotectants as antioxidants.