SUMMARY SUMMARY Environmental stresses such as salinity, drought, heat, cold, flooding and heavy metal toxicity are major threat to the agricultural productivity worldwide (Gaafar et al., 2012). They are given special attention throughout the world due to their toxic effects even at very low concentrations or at high concentrations (Stevovic, et al., 2010). Today, several cases of human diseases, disorders, malfunction and malformation of organs due to metal toxicity have been reported (Itumoh et al., 2013). Once the heavy metals contaminate the ecosystem, they remain a potential threat for many years. Thus, heavy metal contaminants causing ecological problems are of global concern. Cd is a heavy metal that normally occurs in low concentrations in soils and up to 100-120 mg/kg dry weight was reported by Nwaichi et al. (2010). In plants, the accumulation of Cd can cause numerous morphological and physiological changes. Plants grown in soil containing high levels of Cd show visible symptoms of injury reflected in terms of chlorosis, necrosis, leaf roll, growth inhibition, browning of root tips and finally death (Sanita di Toppi and Gabbrielli, 1999; Wojcik and Tukiendorf, 2004; Benavides et al., 2005; Guo et al., 2008). Generally, chromium is not considered as an essential element for plant growth and development. Devries et al. (2002) reported that chromium is toxic to higher plants at 100 μM kg-1. Moreover, hexavalent chromium compounds due to their high solubility (James, 1996), easy permeability through biological membranes and subsequent interaction with protein components and nucleic acids inside the cell 150 SUMMARY are comparatively more toxic than trivalent chromium. Chromium distribution in crops has a stable character that is independent of the soil properties and content of the element; usually the major concentration of the contaminant element is always found in roots with minimum levels present in the vegetative and reproductive organs (Golovatyj et al., 1999; Iyaka, 2009). Keeping above details in view, this study was aimed to investigate: 1. The effect of heavy metals on seed germination, growth and biomass characteristics of pea and maize plants. 2. The effect of heavy metals (cadmium and chromium) on physiological and biochemical characteristics on pea and maize crop plants. Pisum sativum L. is an annual crop, belongs to family Leguminoseae having significant acceptance as green pea and also as pulses upon seed drying for the masses in North India. Therefore, pea seeds were used to reveal cadmium contaminated inhibition of water affecting seed germination, establishment and growth characteristics in petriplates. Cadmium chloride (CdCl2) irrigation levels arranged from 1 – 16ppm having cadmium contamination on short-term basis (till 15 days). The long-term (upto 60 days) cadmium contaminated irrigation levels were applied in earthern pots under field conditions. Accordingly, effect of cadmium toxicity was elucidated in Pisum sativum to observe its consequences on plant growth, physiological, biochemical and biomass characteristics of Pisum sativum. The plants were grown as per protocol described in material and methods. The seeds were subjected under short-term (till 15 days) to various cadmium concentrations to reveal quick responses of pea seedlings in relation to their growth characteristics. The fast kinetics for hydration/ imbibation found to be getting saturated within 6-8 hrs. It was found that germination percent decreased from 83 to 56%, and 39% incase of 4 and 8 ppm cadmium contaminated water applied during seed germination in petriplates. Almost 67% loss in seed germination reported while applying 16 ppm concentration. The appearance of root, shoot and there biodynamics found to be directelty influenced by the application of cadmium contaminated water irrigation. The appearance of lateral roots also found to be affected depending upon the treatment levels and duration along with loss in their voluminous growth. The root and shoot biomass/ fresh mass found to be significantly correlated with the cadmium treatment levels and duration both. Hence, higher the treatment levels and duration 151 SUMMARY both have affected much in impairing shoot and root fresh biomss. Consequently,it has shown a strong correlation with the loss of photosynthetic pigments sugar and proteins. The bochemical molecules for ex. Sugar did down-regulated in contrast to the stress inducible enzymes, i.e. CAT, POD, MDA and proline found to be up-regulated to extend an ability of seedlings under stress. The amylase and metal tolerance (%) as affected by higher cadmium accumulation gradually reduced. The loss in leaf number, leaf and plant biomass, fruiting and seed yield etc. found to be impaired along with higher levels and durations of the irrigation. Consequently gradual loss in harvest index also found to be 49% (16 ppm). Apart from all these, higher cadmium contamination in irrigation water may also cause necrosis, chlorosis in pea. In conclusion Pisum sativum L. found to be differently susceptible as cadmium contaminated water applied based either on short –long term irrigation duration under laboratory and field conditions or both. Maize (Zea mays L.) is world’s one of the three most popular cereal crops for both livestock feed and human nutrition. With its high content of carbohydrates, fats, proteins, some of the important vitamins and minerals, maize is the main food of the lower-socio-economic populations and in some regions it represents more than 80% of daily food consumption. Maize is widely cultivated throughout the world, and a greater weight of maize is produced each year than any other grain. Therefore, maize seeds were used to reveal chromium contaminated inhibition of water affecting seed germination, establishment and growth characteristics in petriplates. Chromium trioxide (CrO3) irrigation levels arranged from 1 – 16ppm having chromium contamination on short-term basis (till 15 days). The long-term (upto 90 days) chromium contaminated irrigation levels (upto 16 ppm) were applied in earthen pots under field conditions. Accordingly, effect of chromium toxicity was elucidated in Zea mays to observe its consequences on plant growth, physiological, biochemical and biomass characteristics of Zea mays. The seeds were subjected under short-term (till 15 days) to various chromium concentrations to reveal quick responses of maize seedlings in relation to their growth characteristics. The fast kinetics for hydration/ imbibation found to be getting saturated within 6-8 hrs. It was found that germination percent decreased from 87 to 57%, and 43% incase of 4 and 8ppm chromium contaminated water applied during seed germination in petriplates. Almost 57% loss in seed germination reported while applying 16 ppm 152 SUMMARY concentration. The morphological appearance such as root, shoot length,leaves per plant and there biodynamics found to be down regulated parallel by the application of chromium contaminated water irrigation. The appearance of roots also found to be affected depending upon the treatment levels and duration along with loss in their voluminous growth. The root and shoot biomass/ fresh mass found to be significantly correlated with the chromium treatment levels and duration both. Hence, higher the treatment levels and duration both have affected much in impairing shoot and root fresh biomss. The morphological appearance based on retention/biogenesis of photosynthetic pigments (chlorophylls and carotenoids) also found to be directly down regulated with chromium levels and durations. The biochemical molecules for example sugar did get down regulated in contrast to the stress inducible enzymes, i.e. CAT, POD, MDA and proline found to be up-regulated to extend an ability of seedlings under chromium stress. The amylaseand metal tolerance (%) as affected by higher chromium accumulation gradually reduced. The loss in flower, cobs and seed yield etc. were found to be impaired along with higher levels and durations of the irrigation. Consequently gradual loss in harvest index also found ca. 52% (16 ppm). Apart from all these, higher chromium contamination in irrigation water may also cause necrosis and chlorosis in maize. Thus it can be concluded that chromium irrigation had negative impact over maize cultivar starting from seed germination to seedlings establishment their growth and development processes. It may be due to adverse effects of chromium over plant, based either on short-long term irrigation duration under laboratory and field conditions or both. The biochemical molecules for example protein did get down-regulated in contrast to the stress inducible enzymes for example lipid peroxidase, proline, catalase and peroxidase as observed up-regulated under the influence of cadmium and chromium treatments may be helping affected plants intrinsically to support them for their viability. The flower, pods and seed characteristics have also been reported and found progressively reduced parallel with increasing levels of cadmium and chromium irrigation. Consequently, biomass and harvest characteristics both found to be impaired under the influence of cadmium and chromium as reported in the study. Consequently, it is concluded that cadmium and chromium irrigation had negative impact over pea and maize cultivars starting from seed germination to seedling establishment their growth and development processes may be due to adverse effects 153 SUMMARY of cadmium and chromium over plants’ water holding capacity to retain ionic balance coupled with osmotic stress or ion cytotoxicity due to excess heavy metals in plant cell and its related functioning. A long term exposure to heavy metals such as cadmium and chromium produces oxidative stress in roots as already reported earlier. This s is being confirmed through enzymatic and non enzymatic antioxidant defense system. Our study also confirms that the cadmium and chromium disturbs the uptake and distribution of essential nutrients such as nitrogen (N), iron (Fe) and zinc (Zn) due to which certain essential metabolic processes are being disturbed in our experimental plants i.e. pea and maize. It appears that sugar and chlorophyll concentrations were adversely affected by the interference of cadmium and chromium in the Fe metabolism in the plants. The disturbance in the protein synthesis in the studied plants might have occurred due to the disturbance in the nitrogen metabolism of the plants, caused by cadmium and chromium. The activities of antioxidative enzymes specially Fe containing enzymes were also adversely affected by the toxic amount of two studied heavy metals. As, these heavy metals might have interfered with Fe metabolism in the plants. So far as the plant growth is concerned, it might have adversely affected due to the interference of availability of two studied heavy metals. Consequently our findings as reported have extended an overview about pea and maize cultivation under the influence of differential levels of the cadmium and chromium. It is found that pea and maize may be preferred to be cultivated in agroclimate areas either free from cadmium and chromium or may be less affected to ensure crop improvement and crop productivity in relation to national economy (socio-economy) and food safety security for the masses. 154
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