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559 Advances in Environmental Biology, 5(4): 559-565, 2011 ISSN 1995-0756 This is a refereed journal and all articles are professionally screened and reviewed ORIGINAL ARTICLE Phytotoxicity of Cadmium on Seed Germination, Early Growth, Proline and Carbohydrate Content in Two Wheat Verities 1 M.R. Asgharipour, 2M. Khatamipour and 3M. Razavi-Omrani 1 University of Zabol, Zabol, Iran. University of Zabol 3 Islamic Azad University-Quchan Branch 2 M.R. Asgharipour, M. Khatamipour and M. Razavi-Omrani; Phytotoxicity of Cadmium on Seed Germination, Early Growth, Proline and Carbohydrate Content in Two Wheat Verities ABSTRACT Human activities all over the earth have increased environmental pollution by heavy metals in agricultural soil. The present study was designed to examine the toxicological effects of different concentrations of cadmium (Cd) on the germination, early-growth parameters, and accumulation of Proline and carbohydrates in two wheat varieties, namely Roshan and Omid. Seeds of these plants were exposed to five different concentrations of Cd in an increasing fashion (5, 20, 50, 100 and 200 mg L-1 of Cadmium Chloride). The endpoints of wheat seedlings, including seed germination percentage, mean germination time, seedling dry weight, root length and shoot height, all decreased along with increasing the Cd concentrations. Cd-treated seedlings, on the contrary, showed an increase in Proline and carbohydrate when compared to control. Significant differences in seed germination, biomass, root length, shoot height and the accumulation of Proline and carbohydrates were observed through the treatments and between the two varieties. In the two varieties, Roshan was found to be more resistant to Cd phytotoxicity. The sensitivity of wheat early-growth to the toxicity of the Cd contamination was in the following sequence: root elongation > shoot elongation > germination. Key words: Toxicology; Cadmium; Wheat Triticum aestivum, Varieties, seedling. Introduction The ever-increasing environmental pollution in agricultural soil caused by heavy metals due to application of sewage sludge, city refuse, and heavy metals containing fertilizers or pesticides, is becoming a major problem in modern agriculture [30,5]. Cadmium is one of the toxic heavy metals in contaminated crop environments. In natural soils, Cd concentration in soil solution is estimated to be around 0.04–0.32 mM. Nevertheless, the soil solution with 0.32 to nearly 1 mM Cd can be considered polluted or toxic[8]. The mobility of this metal in soil–plant system allows its easy take-up in excess by plant so that it will directly or indirectly inhibit the physiological processes like respiration, photosynthesis, transpiration, cell elongation, plantwater relationship, mineral nutrition, nitrogen, and carbohydrate metabolism, leading to poor growth and low biomass[15,28]. The seed germination and early-seedling growth are important stages in the whole process of plantgrowth and due to being the most sensitive stage in the plants changing of their environment, have been widely used in environmental bio-monitoring. In this study, we looked at the ecotoxicological effects of Cd in small-scale toxicity tests using seed germination assay of wheat (Triticum aestivum L.) as a model crop. Not only is wheat one of the most Corresponding Author M.R. Asgharipour, University of Zabol, Zabol, Iran, Phone No.: +989153167234 Email: [email protected]. Adv. Environ. Biol., 5(4): 559-565, 2011 important food crops, it is also easier to culture, to maintain in the laboratory conditions, and even to use in toxicity tests for examining the effects of cadmium, especially on the germination of seeds and the growth of early seedlings which are more sensitive to heavy metals [26,23]. Many plants at seed germination and seedling stages are sensitive to environmental factors. Therefore, the change of plant growth at the germination and seedling stage under heavy metal stress is often regarded as an important index to evaluate plant tolerance to heavy metals[29]. Cd stress leads to protein degradation and increased levels of Proline [32,12]. Therefore, Proline accumulation, accepted as an indicator of environmental stresses [2]. Proline is also considered to have important protective roles through osmotic adjustment [2]. Different plant species and varieties show a wide range of plasticity in Cd tolerance, varying from the high degrees of sensitivity to the hyper accumulating phenotype of some tolerant higher plants [40,21]. It, moreover, brings the possibility to develop crop varieties with low accumulation and high tolerance of heavy metals, which could be planted in slightly to moderately contaminated soils. Two popular wheat varieties, Roshan and Omid, are being widely cultivated all over Iran. Therefore they were chosen for examining the toxicological effects of Cd on seed germination, and root and shoot elongation. Yet, most of the experiments so far have mainly concentrated on oxidative stress only in adult plants during Cd toxicity [34,39] and only a limited number of studies has been dedicated to the germinating stage of plants exposed to Cd stress [42]. Previous experiments indicated that Cd can cause significant reduction in the germination rate in Triticum and Cucumis [27] or will serve to inhibit the germination and growth of Arabidopsis embryos [20]. There is little information available about the sensitivity and physiological responses of wheat seedlings to Cd toxicity, eventhough wheat ranks as the third most important cereal in terms of planting area and production (FAO "Faostat", 2007). The main objective of the present study is to examine the effects of cadmium on the seed germination, early seedlings biomass, and root and shoot elongation of two wheat seedling varieties differing in Cd toxicity resistance by a laboratory experiment. The availability of carbohydrates (soluble sugars, glucose and fructose) and Proline changes occurring in germinating seeds following cadmium exposure to achieve a better understanding of the Cd toxicity has been investigated as well. Materials and Methods The experiment was carried out in April 2010 at the Biotech Research Center of the University of Zabol, Zabol, I.R. Iran. Two wheat (Triticum 560 aestivum) varieties, Roshan and Omid, being widely planted all over Iran, were used in this study. Seeds were kindly provided by Zabol Agricultural Research Center. Prior to germination, the seeds of wheat were surface-sterilized with 3% Formaldehyde for 10 minutes and washed 3 times with re-distilled water. The seeds were then germinated in sterilized Petri dishes, 100mm in diameter, on Whatmann filter-paper moistened with 10 mL of either double-distilled water (control) or Cadmium test solution. The test was performed on 25 wheat seeds exposed to increasing concentrations (5, 20, 50, 100 and 200 mg L-1) of Cadmium Chloride (Sigma, St. Louis, MO). Concentration in terms of weight-by-volume is defined in the reference protocol of the Inter calibration Action in molar terms, 200 mg L!1 corresponds to 1.1 mM of Cadmium. Petri dishes were subsequently kept in the dark, at 25 NC, for a span of 7 days. The solutions were renewed after 3 days. The experiment was laid out as a split-plot design with Cd concentration as the main plot and verities as the sub-plot, together with four replicates. After 7 days, 10 seedlings of each petri were sampled with an aim to measure the root length and shoot height using a ruler (against a black background). Dry weight was also evaluated after drying the specimens (10 seeds) for 72 hours at 76 NC. During the experiment, germinated seeds were counted on a daily. Seed germinability was assessed by the final cumulative percentage of germination at the end of the tests. Here, germination was considered only when the radicles were longer than 2 mm. FGP and D 50 germination was calculated based on Soltani et al. [38]. Proline content was determined using a colorimetric method modified from Li [19] with minor modifications. The fine powder of freeze-dried plant tissues (0.2 g) was treated with 5ml of 3% Sulphosalicylic acid and maintained at 100 NC for 10 minutes. The supernatant (2ml) was added to a solution of 2 ml of glacial Acetic plus 2 ml of 2.5% (w/v) acidic Ninhydrin, and kept at 100 NC for 25 minutes. After the liquid was cooled down, it was added to 4 ml of Toluene. The photometric absorbance of the Toluene extract was read at 520 nm. Contents were calculated to ηg g-1 dry matter. For determination of soluble Carbohydrate contents, embryonic tissues were ground in 80% Ethanol, boiled for 30vminutes at70 °C, and then centrifuged at 8000g for 10 minutes at 41°C. The supernatants were used as samples to determine total soluble Carbohydrate glucose and Fructose [9]. Calibration curves were obtained using Sigma standards. The experiments were repeated twice and the pooled mean values were separated on the basis of Duncan Multiple Range Test (DMRT) at a probability level of 0.01. 561 Adv. Environ. Biol., 5(4): 559-565, 2011 Results: Two-way ANOVA exhibited that all assessed parameters were significantly affected by Cd concentration and verities (Table 1). It was also confirmed that statistically significant differences of Cd treatment by verities exist on these parameters. Toxicity of Cd on Wheat Seed Germination and Early Developmental Stages: The response of final germination percentage (FGP), days to 50% germination (D 50), seedling dry weight, radicle length, shoot height, and ratio of radicle length to shoot height to Cd levels are summarized in Table 2. The mean FGP (i.e. the average of both varieties) over control (without Cd) decreased significantly along with increasing the concentrations of Cd. The FGP was 96.0, 64.7, 48.0, 32.0 and 26.0% at 0, 5, 20, 100 and 200 mg L-1 of Cd, respectively. One the other hand, the effect of Cd on D 50 germination is dependent on its concentration and the D 50 was 18.7, 21.1, 28.6, 35.0 and 37.6 hour at 0, 5, 20, 100 and 200 mg L-1 of Cd, respectively. There were significant differences in FGP and D 50 for different wheat varieties with the treatments of Cd. In both varieties, the FGP and D 50 decreased with increasing the Cd. Seed germination in Omid showed more resistance to the highest concentration of Cd (200 mg L-1). For the treatment with 200 mg L-1 of Cd, the FGP was 30.7 and 21.3% while the D 50 was 34.0 and 41.3 hours for Roshan and Omid, respectively. The seedling dry weight of both verieties decreased significantly with increasing the concentration of Cd. The mean seedlings dry weight was 0.191, 0.117, 0.094, 0.073 and 0.058 g at 0, 5, 20, 100 and 200 mg L-1 of Cd, respectively. Differential responses were observed among the varieties in terms of seedling dry weight; Omid showed more resistance to Cd contamination, so that the seedling dry weight for Roshan and Omid at 200 mg L-1 of Cd were 0.054 and 0.062 g, respectively. The mean radicle length was 6.02, 0.93, 0.65, 0.30, and 0.10 at the Cd concentrations of 0, 5, 20, 100, and 200 mg L-1 of Cd, respectively. The radicle length for both varieties decreased significantly with the increase of Cd concentrations. Differential responses in radicle length were noted for different Cd concentrations and between the two varieties. The radicle lengths in Roshan and Omid for the treatment with 200 mg L-1 of Cd were 0.11 and 0.10, respectively. Significant reduction in shoot height was observed with the increase of Cd concentrations. The mean shoot height was 12.17, 5.94, 4.94, 3.15, and 2.17 cm at the treatments with 0, 5, 20, 100, and 200 mg L-1 of Cd, respectively. The shoot heights in Roshan and Omid, for the treatment with 200 mg L-1 of Cd were 2.07 and 2.27, respectively. The difference in radicle and shoot height indicated that the resistance of wheat varieties to Cd was greater in Omid compared with that of Roshan. In our experiments, radicle length was more affected than radicle length and shoot height. On an average of two genotypes, radicle length was reduced by 84, 89, 95 and 98% in 0, 5, 20, 100, and 200 mg L -1 of Cd treatments, respectively, while, correspondingly, the reductions in shoot height were 11, 45, 59, 74, and 82%, respectively. Thus, the increase in the ratio of radicle length to shoot height observed in the treated plants was mainly due to a decrease of the radicle length while the shoot height was less affected. The effect of Cd on ratio of radicle length to shoot height was dependent on its concentration and differed with genotypes. Toxicity of Cd on Proline and Carbohydrate Content: Proline content and total Carbohydrates in germinated seeds with different concentrations of Cd treatment are presented in Table 3. The Proline content was higher in the seedlings treated with Cd than in the control (Table 3). Therefore, the Proline contents were respectively 0.082, 0.092, 0.106, 0.126, and 0.244 at 0, 5, 20, 100, and 200 mg L-1 of Cd which, in comparison to the control, increased by respectively 12, 28, 54 and 198%, In addition, the treatment of wheat seedlings with Cd significantly increased the content of Carbohydrate reserves in seeds from which the seedlings had developed. Cadmium-treated seedlings with 200 Cd mg L-1 exhibited the greatest Carbohydrate content, while the seedlings in control had the least Carbohydrate content. On an average of the two genotypes, the Carbohydrate contents of 0, 5, 20, 100, and 200 mg L-1 of Cd treatments were 1.035, 1.249, 1.421, 1.552, and 1.725, respectively. Between the two varieties, distinct differences existed regarding the response of Proline and Carbohydrate contents to Cd treatment and the accumulation of Proline was always greater in Roshan than in Omid regarding the response to Cd stress, while Carbohydrates content was crelatively greater in Omid. Discussion: Germination and Early Seedling Growth: Germination and early seedling development assay has been regarded as a basic experiment for evaluating the toxicity effect of any kind of metal or chemical on plants [1,25,24]. Germination inhibition is among the best-known effects of toxic impact of Adv. Environ. Biol., 5(4): 559-565, 2011 562 Table 1: Results of ANOVA testing the effect of Cd concentration and varieties on final germination percentage (FGP), days to 50% germination (D 50), Seedling dry weight, Radicle length, Shoot height, ratio of radicle length to shoot height, Proline and Total soluble carbohydrate content. SS SOV df FGP D 50 Seedling dry Radicle Shoot ratio of radicle Proline Total soluble (hour) weight length height length to shoot content carbohydrate height (mg g-1 DW) content (mg g-1 DW) Conc. 4 **21.594 **0.0024 **0.0163 **37.269 **92.187 **319.863 **0.0261 **0.427 1st Error 10 0.0328 0.00002 0.000021 0.078 0.097 1.323 0.0000068 0.00018 Var. 1 1.659** **0.00023 **0.0099 **1.81 **25.502 *8.945 **0.00215 **0.43 Var. × Conc. 4 0.14* 0.000057ns **0.0015 *0.31 **2.835 **7.903 **0.00008 **0.0173 Error 10 0.342 0.0002 0.000051 0.0682 3.384 1.045 0.0000038 0.00015 Errorns: not significant; (*) and (**) represent significant difference over control at p<0.05 and p<0.01, respectively. Table 2: Influence of various Cd concentrations on Final germination percentage (FGP), Days to 50% (D 50) mean, Seedling dry weight, Radicle length, Shoot height and ratio of radicle length to shoot height of two wheat varieties. Concentrations FGP (%) D 50 (hour) Seedlings dry Radicle length Shoot height ratio of radicle of Cd (mg L-1) weight (g) (cm) (cm) length to shoot height ---------------------- --------------------------------------------------------------- --------------------- -----------------Roshan Omid Roshan Omid Roshan Omid Roshan Omid Roshan Omid Roshan Omid 0 94.7a 97.3a 18.7c 18.7c 0.236a 0.146a 6.60a 5.45a 14.07a 10.27a 1.95d 1.88e 5 62.7b 66.7b 20.6b 21.7c 0.138b 0.096b 1.25b 0.61b 7.13b 4.77b 5.68c 7.80d 20 44.0c 52.0c 23.6b 33.7b 0.106c 0.082c 0.92bc 0.39bc 5.88c 4.00b 6.38c 9.49c 100 29.3d 34.7d 36.7a 33.3b 0.082d 0.064d 0.37cd 0.23cd 3.63d 2.66c 9.80b 11.47c 200 21.3e 30.7e 34a 41.3a 0.062e 0.054e 0.10d 0.10d 2.07c 2.27e 22.67a 20.67a * Values followed by the same letter within the same columns do not differ significantly at p =1% according to DMRT. Table 3: Influence of various Cd concentrations on Proline and Total soluble carbohydrate content of two wheat varieties. Concentrations of Cd (mg L-1) Proline content (mg g-1 DW) Total soluble carbohydrate content (mg g-1 DW) ---------------------------------------------------------------------------------------------------------Roshan Omid Roshan Omid 0 0.086e 0.078e 0.967e 1.103e 5 0.100d 0.084d 1.127d 1.372d 20 0.115c 0.096c 1.350c 1.493c 100 0.133b 0.119b 1.414b 1.690b 200 0.258a 0.231a 1.526a 1.924a * Values followed by the same letter within the same columns do not differ significantly at p =1% according to DMRT. heavy metals [10]. Under heavy metal stress, the processes of germination, like embryo growth, will be depressed [1]. Some researchers [31] have reported the reduction of germination rate and seedling growth of different crops by heavy metals toxicity. The present research also showed that the wheat germination percentage and time are considerably affected by Cd. With the increasing the concentrations of Cd in the growth media, the root length reduced more significantly than the other parameters and the reduction was in the following order: root length > shoot height > seedling dry weight > germination. More sensitivity of root length to Cd could be described by the fact that a plant root is the first point to contact with the toxicants in the growth media. Cadmium can easily penetrate the root cortex [41], consequently the roots are more likely to experience the Cd damage before any other part [8]. The previous work by Blum [6] also showed that root was the most sensitive part to Cd treatment. The wheat varieties showed different levels of sensitivity to Cd toxicity. The data of inhibition rates of germination, seedling dry weight, root length, and shoot height all showed that Omid was more tolerant to Cd contamination. High resistance to Cd could be achieved by: 1) complexated the Cd by such peptides as SH-groups [25]; 2) enhanced the production of antioxidants that detoxify free reactive oxygen species (ROS) produced in response to Cd [14]; and 3) depressed the total ion activity in the solution caused by the Cd [22]. Toxicity of Cd on Proline and Carbohydrate Content: As shown in table 3, increasing the concentrations of Cd in the growth medium resulted in a pronounced increase in Proline. In many plants, unfavorable environmental effects bring about the accumulation of Proline, which is, by itself, one of the most universal poly-functional stress-protective substances [3]. Proline is known to accumulate under heavy metal exposure and is considered to be involved in the particular stress resistance [7,11]. The Proline accumulation in Cd- treated seedlings can be regarded as one of the most sensitive responses to water deficiency and osmotic stress [4]. The capability of plants for a heavy-metal induced Proline accumulation could be brought about not only by a direct effect of Cd ions, but also by water deficiency 563 Adv. Environ. Biol., 5(4): 559-565, 2011 [36]. This deficiency develops in the plant tissues under the conditions of Cd stress due to damage to the water-absorbing capacity of roots. Schat et al. [33] considered that Proline accumulation is mainly induced by the water stress component of Cd toxicity while Kastori et al. [18] argued that Proline accumulation occurred as a result of Cd toxicity independent of any water-stress component. From an experimental point of view, however, causes and consequences are quite difficult to distinguish. Besides its putative impact on osmotic adjustment processes, Proline was shown to protect enzymes and cellular structures against heavy metal damages as a consequence of the formation of Cd–Proline complexes [35] or against maintenance of the glutathione redox state, thus indirectly acting as an antioxidant [37]. So, greater Proline content in Omid may be a major factor involved in the comparatively higher degree of resistance of this variety. Heavy metals also modified the Carbohydrate accumulation in wheat seedlings (Tables 3). Increasing the Cd significantly increased the Carbohydrate levels measured in the seedlings. The present results contrast with those of Greger and Bertell [13] since they found that Cd decreased the Carbohydrate levels in both shoots and roots from sugar beet whereas the nutrient medium and the metal ion were supplied in a similar manner to those of ours. However, the same authors observed that Cd increased the carbohydrate levels when plants were cultivated with an exponential supply of nutrients. Seed germination relies almost exclusively on seed reserves for the supply of metabolites for respiration as well as other anabolic reactions. Starch is quantitatively the most abundant storage material in seeds and available evidence indicates that, in germinating seed, starch is degraded predominantly via the amylolytic pathway [17]. Our results showed that Cd treatments reduce the seedling growth corroborating the results previously found by others [8,31,1]. The higher Carbohydrate levels observed in the Cd-treated plants can be explained by less utilization of Carbohydrate for growth subjected to Cd stress. study that Roshan is more suitable for cultivation in soils with Cd contaminations. References 1. 2. 3. 4. 5. 6. 7. 8. 9. 10. 11. Conclusions: As a well-known pollutant, Cd had an obvious toxic effect on the seed germination percentage and time, seedling dry weight, root length, shoot height and ratio of shoot height to root length, as well as Proline and Carbohydrate content. Among the two varieties, Roshan was found to be the more resistant to Cd. The different resistances among the varieties could be ascribed to the more synthesis of Proline by Roshan seedlings. It can be concluded from this 12. 13. Ahsan, N., D.G. Lee, S.H. Lee, K.Y. Kang, J.J. Lee, P.J. Kim, H.S. Yoon, J.S. Kim and B.H. Lee, 2007. Excess copper induced physiological and proteomic changes in germinating rice seeds. Chemosphere, 67: 1182-1193. Alia-Saradhi, P.P., 1991. Proline accumulation under heavy metal stress. Journal of Plant Physiology, 138: 554-558. Ashraf, M. and M.R. Foolad, 2007. Roles of glycine betaine and proline in improving plant abiotic stress resistance. Environmental and Experimental Botany, 59: 206-216. Ashraf, M. and P.J.C. Harris, 2004. Potential biochemical indicators of salinity tolerance in plants. Plant Science, 166: 3-16. Baker, D.E., M.C. Amacher and R.M. Leach, 1979. Sewage sludge as a source of cadmium in soil-plant-animal systems. Environ Health Perss, 28: 45-49. Blum, W.H., 1997. Cadmium uptake by higher plants. In: Proceedings of Extended Abstracts from the Fourth International Conference on the Biogeochemistry of Trace Elements. University of California, Berkeley, USA, pp: 109-110. Chen, C.T., T.H. Chen, K.F. Lo and C.Y. Chiu, 2004. Effects of proline on copper transport in rice seedlings under excess copper stress. Plant Science, 166: 103-111. di Toppi, L.S. and R. Gabbrielli, 1999. Response to cadmium in higher plants. Environmental and Experimental Botany, 41: 105-130. Dishe, Z. and E. Borenfreund, 1951. A new spectrophotometric method for the detection and determination of keta sugar and trioses. The Journal of Biological Chemistry, 192: 583-7. Ernst, W.H.O., 1998. Effects of heavy metals in plants at the cellular and organismic level ecotoxicology. In: Bioaccumulation and Biological Effects of Chemicals, Eds., Gerrit, S. and M.Bernd. W iley and Spektrum Akademischer Verlag, pp. 587-620. Gouia, H., A. Suzuki, J. Brulfert and M.H. Ghorbal, 2003. Effects of cadmium on the coordination of nitrogen and carbon metabolism in bean seedlings. Journal of Plant Physiology, 160: 367-376. Gowrinathan, K.P. and V.N.R. Rao, 1992. Reversal of heavy metal toxicity by ascorbic acid in micro algae. Journal of Swamy Botany, 9: 27-29. Greger, M. and G. Bertell, 1992. Effects of Ca2+ and Cd2+ on the carbohydrate metabolism in sugar beet (Beta vulgaris). Journal of Experimental Botany, 43: 167-173. Adv. Environ. Biol., 5(4): 559-565, 2011 14. Hartley-Whitaker, J., G. Ainsworth and A.A. Meharg, 2001. Copper and As induced oxidative stress in Holcus lanatus L. clones with different sensitivity. Plant Cell Environment, 24: 713-722. 15. Herna´ndez, L.E., R. Carpena-Ruiz and A. Ga´rate, 1996. Alterations in the mineral nutrition of pea seedlings exposed to cadmium. Journal of Plant Nutrient, 19: 1581-1598. 16. http://faostat.fao.org/site/526/default.aspx. Retrieved 2009-05-05. 17. Juliano, B.O. and J.E. Varner, 1969. Enzyme degradation of starch granules in the cotyledons of germinating peas. Plant Physiology, 44: 886892. 18. Kastori, R., M. Petrovic, and N. Petrovic, 1992. Effect of excess lead, cadmium, copper and zinc on water relations in sunflower. Journal of Plant Nutrient, 15: 2427-2439. 19. Li, H.S., 2000. Principle and Techniques of Botanic, Chemical and Physiological Experiments, Senior Education Press, Beijing, pp. 164-169. 20. Li, W., M.A. Khan, S. Yamaguchi and Y. Kamiya, 2005. Effects of heavy metals on seed germination and early seedling growth of Arabidopsis thaliana. Plant Growth Regulation, 46: 45-50. 21. Liu, J.G., J.S. Liang, K.Q. Li, Z.J. Zhang, B.Y. Yu, X.L. Lu, J.C. Yang and Q.S. Zhu, 2003. Correlations between cadmium and mineral nutrients in absorption and accumulation in various genotypes of rice under cadmium stress. Chemosphere, 52: 1467-1473. 22. Liu, X.L. and S.Z. Zhang, 2007. Intraspecific differences in effects of co-contamination of cadmium and arsenate on early seedling growth and metal uptake by wheat. Journal of Environmental Sciences, 19: 1221-1227. 23. Smirk, M., A. Chaoui and E. El-Ferjani, 2009. Respiratory metabolism in the embryonic axis of germinating pea seed exposed to cadmium. Journal of Plant Physiology, 166: 259-269. 24. Wang, M. and Q. Zhou, 2005. Single and joint toxicity of chlorimuronethyl, cadmium, and copper acting on wheat Triticum aestivum. Ecotoxicology and Environmental Safety, 60: 169-175. 25. Maitani, T., H. Kubota, K. Sato and T. Yamada, 1996. The composition of metals bound to class III metallothioein (phytochelatin and its desglycyl peptide) induced by various metals in root cultures of Rubia tinctorum. Plant Physiology, 110: 1145-1150. 26. Mihoub, Ch.A. and E. El-Ferjani, 2005. Biochemical changes associated with cadmium and copper stress in germinating pea seeds (Pisum sativum L.). Comptes Rendus Biologies, 328: 33-41. 564 27. Munzuroglu, O. and H. Geckil, 2002. Effects of metals on seed germination, root elongation, and coleoptile and hypocotyl growth in Triticum aestivum and Cucumis sativus. Archives of Environmental Contamination and Toxicology, 43: 203-213. 28. Obata, H., N. Inoue and M. Umebayashi, 1996. Effect of Cd on plasma membrane ATPase from plant roots differing in tolerance to Cd. Soil Science & Plant Nutrition, 42: 361-366. 29. Peralta-Videa, J.R., J.L. Gardea-Torresdey, E. Gomez, K.J. Tiermann, J.G. Parsons and G. Carrillo, 2002. Effect of mixed cadmium, copper, nickel and zinc at different pHs upon alfalfa growth and heavy metal uptake. Environmental Pollution, 119: 291-301. 30. Qadir, A.M., G. Ghafoor and G. Murtaza, 2000. Cadmium concentration in vegetables grown on urban soils irrigated with untreated municipal sewage. Environment, Development and Sustainability, 2: 11-19. 31. Rahul, S., A. Chaoui and E. El-Ferjani, 2008. Differential sensitivity to cadmium in germinating seeds of three cultivars of faba bean (Vicia faba L.). Acta Physiologiae Plantarum, 30: 451-456. 32. Rai, L.C. and M. Raizada, 1988. Impact of chromium and lead on Nostoc muscorum: Regulation of toxicity by ascorbic acid, glutathione and sulphur-containing amino acids. Ecotoxicology and environmental safety, 15: 195-205. 33. Schat, H., S.S. Sharma and R. Vooijs, 1997. Heavy metal-induced accumulation of free proline in a metal-tolerant and a non-tolerant ecotype of Silene vulgaris. Plant Physiology, 101: 477-482. 34. Schutzendubel, A., A. Polle, 2002. Plant responses to abiotic stresses: heavy metal induced oxidative stress and protection by mycorrhization. Journal of Experimental Botany, 53: 1351-1365. 35. Sharma, S.S. and K.J. Dietz, 2006. The significance of amino acids and amino acidderived molecules in plant responses and adaptation to heavy metal stress. Journal of Experimental Botany, 57: 711-726. 36. Shevyakova, N.I., I.A. Netronina, E.E. Aronova and V.V. Kuznetsov, 2003. Compartmentation of cadmium and iron in Mesembryanthemum crystallinum plants during the adaptation to cadmium stress. Russian Journal of Plant Physiology, 50: 678-685. 37. Siripornadulsil, S., S. Traina, D.P. Verma and R.T. Sayre, 2002. Molecular mechanisms of proline-mediated tolerance to toxic heavy metals in transgenic microalgae. Plant Cell, 14: 28372847. Adv. Environ. Biol., 5(4): 559-565, 2011 38. Soltani, A., M. Gholipoor, E. Zeinali, 2006. Seed reserve utilization and seedling growth of wheat as affected by drought and salinity. Environmental and Experimental Botany, 45: 195-200. 39. Wang, S.H., Z.M. Yang, H. Yang, B. Lu, S.Q. Li and Y.P. Lu, 2004. Copper-induced stress and antioxidative responses in roots of Brassica juncea L. Botanical Bulletin of Academia Sinica, 45: 203-212. 40. Yang, Y.Y., J.Y. Jung, W.Y. Song, H.S. Sun and Y. Lee, 2000. Identification of rice varieties with high tolerance or sensitivity to lead and characterization of the mechanism of tolerance. Plant Physiology, 124: 1019-1027. 565 41. Yang, M.G., X.Y. Lin and X.E. Yang, 1998. Impact of Cd on growth and nutrient accumulation of different plant species. Chinese Journal of Applied Ecology, 19: 89-94. 42. Zhu, Y.L., E.A.H. Pilon-Smits, A.S. Tarun, S.U. Weber, L. Jouanin and N. Terry, 1999. Cadmium tolerance and accumulation in Indian mustard is enhanced by overexpressing gglutamyl cysteine synthetase. Plant Physiology, 121: 1169-1177.