The contamination of the environment by heavy metals is currently a major
global environmental problem threatening the health of vegetation, wildlife and humans (Salt
et al., 1995). Various industrial activities, including battery production, metals products,
metal smelting and cable industries, mining, vehicular emissions, agricultural waste
disposal technologies and atmospheric emissions contribute to the increasing levels of heavy
metals in the environment. Besides anthropogenic activities, geothermal streams and
volcanic eruptions also contribute to heavy metal accumulation in the environment (Foy
et al., 1978). Eventually, these metals find entry into the food chain and tend to biomagnify at
subsequent trophic levels (Woolhouse, 1983). Heavy metals like arsenic (As), cadmium (Cd), lead
(Pb) and mercury (Hg), which form a part of the present study, have no role to play in
plant metabolic activities and thus altogether are nonessential.
Brassica is an important oil seed crop which is being grown in heavy
metal-contaminated sites (Tickoo et al., 2007). Earlier studies have reported the positive effects of toxic
metals on Brassica (Inoue and Saeki, 2004; Qadir
et al., 2004; and Tickoo et al., 2007). The
relative sensitivity of Brassica cv to Cd, Pb and Hg was reported previously. In this study, we
have assessed the effects of various concentrations of Hg on seed germination, seedling
growth and related physiological changes in the Indian mustard genotypes for their response to
Hg accumulation and tolerance.
The seeds of Brassica juncea genotype P Bold and Vasundhra were procured from
Mustard Rape Research Institute. The healthy seeds were surface-sterilized with 1%
sodium hypochloride solution for 2 min and washed thoroughly with distilled water. Seeds
were germinated in petridishes of 15 cm diameter having blotting papers moistened with
distilled water and respective metal solutions. For imposing heavy metal stress, mercuric
chloride (HgCl2) at 0.5, 1.5 and 10 mM concentrations were used. The seeds were allowed to
grow into seedlings under these conditions. The experiments were terminated on the
10th day and data on germination and growth of seedlings were recorded on the
5th and 10th day as length of shoots and roots. Root Growth Rate (RGR) was determined by dividing the difference
of root length on the 10th day and
5th day by number of days. Similarly, the Shoot
Growth Rate (SGR) was determined. The
10th day-old seedlings were analyzed for chlorophyll
content, Relative Leaf Water Content (RLWC), Electrolyte Leakage (EL) and proline that were
estimated at 5 mM concentration of this metal. |