Heavy metal pollution was of considerable importance and relevant to the present scenario due to the increasing levels of pollution and its obvious impact on human health through the food chain [1]. It is a known fact that the widespread accumulation of metals in the environment is increasingly becoming a problem for organisms of every kind. The main sources of elevated heavy metals concentration in soils were agricultural, manufacturing, mining, waste disposal practices, and the use of sewage sludge as fertilizer in agricultural fields. Metal contamination of agricultural soil has increased parallel to industrialization. Heavy metals concentration was introduced due to the application of metals containing agrochemicals such as pesticides and fertilizers. Previous studies had showed that Hg, Zn, Cd, Co, Pb, Cu, As, Al, Cr, and Ni reduce the germination of many kinds of seeds [2][3][4][5][6][7][8][9][10][11][12][13][14][15][16].Cadmium pollution was increasing in the environment due to mining, industrial usage, and many anthropogenic activities. Irrigation with polluted water had induced heavy metal accumulation not only in the soil but also in plant parts, including seeds and tissues [17]. Excess Cd caused a number of toxic symptoms in plant growth retardation and inhibition of photosynthesis. Cadmium could also enter the soil or water from spills or leaks at hazardous waste sites if Pol. J. Environ. Stud. Vol. 24, No. 1 (2015), [295][296][297][298][299]
AbstractThe ecotoxicological effects of Cd 2+ on germination and early seedling growth of six pulses were investigated. Seeds of these plants were exposed to seven different concentrations of Cd (0, 0.1, 0.2, 0.4, 0.8, 1.6, and 3.2 mM). The results indicated that root and coleoptile growth of six pulse plants were more sensitive than seed germination for measurement of toxic Cd 2+ pollution. Different species show different levels of tolerance to Cd 2+ pollution. V. angularis and Dumasia villosa are the most sensitive to Cd
2+, and their germination percentage, and root and coleoptile growth were significantly lower than other tested species. By contrast, Vigna radiata and Lablab purpureus are the most resistant species, their germination and seedling growth almost were not influenced by Cd 2+ pollution significantly compared to control. There were significantly negative correlations between seedling growth and increasing concentrations of Cd 2+ for V. angularis. V. angularis and Dumasia villosa are the most sensitive to Cd 2+ . By contrast, Vigna radiata and Lablab purpureus are the most resistant species.