Journal of Microbiology and Biotechnology Research Scholars Research Library J. Microbiol. Biotech. Res., 2011, 1 (4): 124-130 (http://scholarsresearchlibrary.com/archive.html) ISSN : 2231 –3168 CODEN (USA) : JMBRB4 Phenols and their antioxidant activity in Brassica juncea seedlings growing under HgCl2 stress Yaksha Singh and C P Malik School of Life Sciences, Jaipur National University, Jaipur _____________________________________________________________________________ ABSTRACT Lab experiments were conducted to investigate the relationship between Hg-induced phytotoxicity and oxidative stress and the ameliorative effects of total phenols and putrescine. Seedlings were treated with HgCl2 at the seedling stage. Seeds were prehardened with putrescine (0.5mM). Reactive oxygen species (ROS) accumulation enhanced. Putrescine was effective in decreasing the superoxide anion content and H2O2 content. The decrease was concentration specific. Lipid peroxidation enhanced by % with HgCl2 which caused increased leakage. Putrescine decreased lipid peroxidation and hence electrolyte leakage. The activities of SOD, ascorbate peroxidase and catalase increased with treatments. Hg had a deleterious effect on most parameters but putrescine was markedly effective in overcoming the toxic effect of Hg. Enhancement in total phenols as a response to heavy metal stress is reported. The role of phenolics in acting as metal chelators and scavenging molecular species of active oxygen is proposed. Keywords: Phenol, SOD, ascorbate peroxidase and catalase. INTRODUCTION Crop plants are affected by a variety of abiotic stresses like salinity, drought, low and high temperature and heavy-metal as well as biotic stresses like pathogens. These stresses result in significant loss of crop yield and quality. Heavy metals are important environment pollutants and many of them are toxic even at very low concentrations. Toxic metal contamination of soil, aqueous waste streams and groundwater poses a major environmental and human health problem. The influence of metals on development and reproduction of plants can be firstly quantified by determining the germination traits of seeds and growth performance of seedling. In the presence of high concentrations of some heavy metals, most of plant species performed the reduction of seed germination and seedling growth. Different industrial and other anthropogenic 124 Available online at www.scholarsresearchlibrary.com Yaksha Singh et al J. Microbiol. Biotech. Res., 2011, 1 (4):124-130 ______________________________________________________________________________ activities have increased the levels of heavy metals in the environment. The metals contamination restricts the plant growth, threatening the human life. Germination of seed is a crucial step in seedling establishment and crop productivity. Seed priming is a controlled hydration treatment of seeds sufficient to permit pre-germinative metabolic events to take place but insufficient to allow radical emergence and are followed by drying back of the seeds to their original moisture content. Seed priming is a technique which involves uptake of water by the seed followed by drying to initiate the early events of germination up to the point of radical emergence. Its benefits include rapid, uniform and increased germination, improved seedling vigour and growth under a broad range of environments resulting in better establishment and alleviation of phytochrome-induced dormancy in some crops. The polyamines (PAs) are small aliphatic amines that are ubiquitous in all living organisms. In plants, the most common PAs are diamine putrescine, triamine spermidine and tetramine spermine which have been implicated in a wide range of plant growth and developmental processes including cell division, embryogenesis, morphogenesis, fruit development, fruit ripening, leaf senescence and response to environmental stresses [1,2,3,4]. In this study we have used putrescine as a pre hardening agent. MATERIALS AND METHODS The seeds of Vasundhra were obtained from National Research Center on Rape Seed and Mustard, (Indian Council of Agriculture Research) Bharatpur - 321303, Rajasthan. Uniformly selected seeds were sterilized with 0.1 % HgCl2 for 1 min and subsequently repeatedly washed under running tap water followed by distilled water. Seeds were presoaked in putrescine (1 mM) for 8 hrs. Thereafter, these were dried and brought to original weight, Seeds were germinated in Petri dishes lined with blotting paper and irrigated with heavy metal solution. For imposing HgCl2 stress 1 mM concentration was used in each Petri dish. Nearly 20 seeds were sown in each Petri dish and incubated in BOD incubator set at 25°C. Petri dishes were watered with a desired concentration of heavy metal and left to germinate. Following parameters were studied after 15 days of sowing (DAS). Different seed, seedling, physical and biochemical characters were analyzed. Each treatment was replicated thrice and the data represented as average values. Data on seed germination and seedling growth shall be published elsewhere. Total Phenolic Content The colorimetric method [5] was used for the determination of total phenols. Aliquote of 0.5 ml extract was diluted with distilled water. To this was added 0.5 ml of Folin-Ciocalteu reagent and content shaken vigorously. After three minutes 1 ml of saturated sodium carbonate solution was mixed and final volume was made to 10 ml with distilled water. The test tubes were kept in dark for one hour after which absorbance was measured at 725 nm and for standard curve stock solution of gallic acid was made by dissolving gallic acid (50 mg) in 50 ml of methanol. Chlorophylls and carotenoid content 200 mg of fresh leaves were taken and homogenized thoroughly in 80 per cent (v/v) acetone using a glass-in-glass homogenizer. The material was centrifuged at 3000 g for 10 min in dark 125 Available online at www.scholarsresearchlibrary.com Yaksha Singh et al J. Microbiol. Biotech. Res., 2011, 1 (4):124-130 ______________________________________________________________________________ and clear supernatant was collected in a test tube. The pellet was extracted again with 2 ml of 80 per cent acetone and recentrifuged. The two supernatants were pooled and the final volume was adjusted to 10 ml. The absorbance was read at 647 and 664 nm respectively [6]. 80 per cent aqueous acetone solution served as a blank. The absorbance of the solution was recorded at 480 nm respectively [7]. Malonaldehyde (MDA) The level of lipid per oxidation was measured in term of malondialdehyde (MDA) content, a product of lipid per oxidation by the method of Heath and Packer [8]. Plant tissue was homogenized in 0.1 % TCA. The homogenate was centrifuged at 10,000 rpm for 10 min. Supernatant was treated as extract. To 1 ml aliquot of supernatant, 4 ml of 0.5 % of TBA in 20 % TCA was added. The mixture was heated at 95ºC for 30 min and cooled in ice bath. After centrifugation at 10,000 rpm for 10 min, the absorbance of supernatant was recorded at 532 nm. MDA content was calculated by extinction coefficient of 155 mM-1 cm-1 expressed as per gram of fresh weight. Hydrogen peroxide (H2O2) It was estimated by method of Mukherji and Chaudhary [9]. 0.5 g Plant material was homogenized in 5 ml chilled acetone (80 %) and filtered through Whatman No 1 filter paper. To the above 5 ml of extract, added 4ml of titanium reagent followed by the addition of 5 ml of ammonia solution. The mixture was centrifuged at 10,000 rpm and supernatant was discarded. The residue was dissolved with 1 M H2SO4. Absorbance was recorded at 410 nm. Calculations were made with standard curve plotted with pure H2O2. Concentration of H2O2 was determined using standard curve plotted with known concentrations of H2O2. Proline content The proline content was determined by the method of Bates and Waldren [10]. Fresh material of seedlings was homogenized in 3 % aqueous sulfosalicylic acid and the homogenate was centrifuged to 10,000 rpm. Supernatant was estimated for proline. The reaction mixture consisting of 2 ml supernatant, 2 ml acid ninhydrin and 2 ml of glacial acetic acid was boiled at 100°C for 1 hr. After termination of the reaction in ice bath, the reaction mixture was extracted with 4 ml toluene and the absorbance was read at 520 nm. The amount of proline was calculated from the standard curve plotted with known concentrations of proline. Superoxide dismutase (SOD) (EC1.15.1.1) The activity of SOD was assayed following the method of Dhindsa and Dhindsa [11].The fresh plant material was homogenized in 50 mM chilled / ice cold phosphate buffer pH 7.0, 0.25 % triton X-100 (m/v) and 1 % poly vinyl pyrrolidone (PVP and 10 % w/v glycerol) and centrifuged centrifuged at 10,000 rpm for 10 min at 4ºC and supernatant was treated as enzyme extract. The reaction mixture (3 ml) contained 13 mM methionine, 25 mM NBT, 0.1 mM EDTA, 50 mM sodium bicarbonate, 50 mM phosphate buffer pH 7.8 and 0.1 ml of enzyme extract. The reaction was started by addition of 2 mM riboflavin and exposed to 15 W fluorescent lights for 10 min. The Photo – reduction of NBT resulted in the formation of purple formazon. The absorbance was read at 560 nm and the total SOD activity of the samples was assayed by measuring its ability to inhibit the photochemical reduction of nitro-blue-tetrazolium (NBT). 1 unit of SOD activity was defined as the amount of enzyme, which causes 505 inhibition of the photochemical reduction of NBT. 126 Available online at www.scholarsresearchlibrary.com Yaksha Singh et al J. Microbiol. Biotech. Res., 2011, 1 (4):124-130 ______________________________________________________________________________ Catalase (CAT) (EC 1.11.1.6) Catalase activity was determined by the method of Aebi [12]. The reaction mixture in final volume of 3 ml comprised 0.1 M phosphate buffer (pH 7.0). The reaction mixture was initiated by adding H2O2 and enzyme activity was determined following degradation of at H2O2 at 240 nm for 2 min. The catalase activity was measured using the extinction coefficient 0.0394. Ascorbate peroxidase (APX) (EC 1.11.1.11) APX activity was determined by following oxidation of ascorbate as a decrease in absorbance at 290 nm [13]. Ascorbate (2 mM) was added to extraction medium to the inactivation of enzyme. Plant material was homogenized in ice cold. 50 mM phosphate buffer pH 7.0, 0.1 mM EDTA, 0.5 mM ascorbic acid, and enzyme extract. The change in A290 was recorded at 30 seconds intervals after addition of H2O2. The rate constant was calculated using the extinction coefficient of 2.8 mM-1cm-1. Reactive oxygen species (ROS) ROS production was measured as described by Able et al., [14] by monitoring the reduction of 2, 3-bis (2-methoxy-4-nitro-5-sulfophenyl)-2H-tetrazolium-5- carboxanilide-inner salt (XTT) in presence of ROS, with some modifications. Leaves (250 mg) were homogenized with 1.5 ml of 50 mM K-phosphate buffer (pH 7.8) and centrifuged at 5000 rpm for 10 min. The reaction mixture (1 ml) contained 50 mM K-phosphate buffer (pH7.8), 500 µl of 0.5 mm XTT. The reaction of XTT was determined at 470 nm for 3 min. Corrections were made for the absorbance of chlorophyll. ROS production was calculated by using extinction coefficient of 2.163104M-1 cm-1. RESULTS AND DISCUSSION Figure 1. Effect of HgCl2 on total phenols (left) and ROS accumulation ( right) in leaves of B.juncea after 15 days of treatment Total Phenols 12 µM g-1 FW µ g-1 FW 10 8 6 4 2 0 Control 1 mM Hg Put Treatments 1 mM Hg + Put ROS 450 400 350 300 250 200 150 100 50 0 Control 1 mM Hg Put Treatments 1 mM Hg + Put Figure 1 shows increase level of total phenols with mercury and putrescine. When both were used the phenolic contents enhanced. Enhanced ROS accumulation was observed with Hg. Hg + putrescine were effective in decreasing the level of ROS. 127 Available online at www.scholarsresearchlibrary.com Yaksha Singh et al J. Microbiol. Biotech. Res., 2011, 1 (4):124-130 ______________________________________________________________________________ Table 1 Effect of HgCl2, putrescine (1mM) on different traits in leaves of Brassica juncea after 15 days of treatment Treatments Level of lipid peroxidation (MDA µM g-1 FW) H2O2 (µM g-1 FW) Total chlorophyll (mg g-1 FW) Carotenoids (mg g-1 FW) Proline (µM g-1 FW) SOD (IU) CAT (µM min-1 g-1 FW) APX (µM min-1 g-1 FW) Control 1.85 375.00 0.300 0.126 1.76 0.40 32.84 9.24 1 mM Hg 2.01 551.28 0.230 0.106 4.36 0.80 49.61 10.00 Put 1.79 221.15 0.336 0.145 2.16 0.66 43.71 11.72 1 mM Hg + Put 1.93 416.66 0.261 0.141 5.10 1.06 58.39 16.55 Antioxidant enzymes SOD, CAT and APX SOD activity enhanced two fold with Hg treatment and putrescine + Hg further enhanced the activity several fold (Table 1). Catalase activity showed similar trend. A small enhancement in APX activity was noticed with Hg and putrescine. Hg and putrescine further enhanced the APX activity (Table 1). Chlorophyll and carotenoid content There was a significant difference in amount of chlorophylls between the treated and non treated samples. The content of total chlorophyll decreased with the increasing concentration of Hg on the 10th and 15th day. In our investigations, it was observed that in Brassica, mercury showed decreasing effect on Hill activity. Hg treatments also caused decline in carotenoid content but putrescine exhibited promontory effect. MDA Hg stress adversely affected the membrane integrity. The MDA content indicated the degree of lipid peroxidation. Enhanced levels of lipid peroxidation resulted in membrane injury. Putrescine effectively alleviated the toxic effect of Hg (table 1). Proline The proline content increased markedly in hardened seedlings over the NHS. In fact proline contents in the 15th days old seedlings were invariably more in the NHS compared with non hardened control. As the concentration of metal increased the proline content also enhanced. It seems that during heavy metal stress, accumulation of nitrogen compounds like proline as well as proteins increase. It is pertinent to state that with NHS the situation was altered with heavy metal stress and proline contents increased markedly. Brassica juncea (Brassicaceae), Indian mustard, is a very important oil crop which is a fast growing plant and produces a high biomass even in heavy metal polluted soils. Thus, this plant could be a potential candidate for phytofiltration or phytostabilzation of heavy metal contaminated waste water. Heavy metals in soils are an increasing concern of environmental pollution. These are continuously being added to agricultural land with sludge, fertilizers, lime and manure. It causes deleterious effects to plants in two ways: by inactivating several enzymes by binding with SH128 Available online at www.scholarsresearchlibrary.com Yaksha Singh et al J. Microbiol. Biotech. Res., 2011, 1 (4):124-130 ______________________________________________________________________________ groups, and second by intensifying the processes of production of reactive oxygen species (ROS) leading to oxidative stress. There are several anti oxidative systems operating within the plants to combat such toxic effects. These include antioxidants (non-enzymatic and enzymatic). Additionally, exogenous applications of putrescine also decrease oxidative stress. Polyamines have been reportedly concerned with responses to several stresses e.g. salt stress, water stress and heavy metal stress. For details one may refer to the review by Sairam and Tyagi [15] Polyamines are shown to function as metal chelators, decrease lipid peroxidation and hence delay senescence, scavenge ROS, etc. [16]. Several stress factors e.g. potassium deficiency, osmotic stress, low pH are shown to stimulate the accumulation of polyamines especially putrescine in plants. In the present investigation we have employed putrescine as an antioxidant to ameliorate the effect of Hg toxicity by scavenging ROS. The precise role of exogenously added putrescine on plant resistance to Hg toxicity has not been described so far. Hence, the present investigation was undertaken to demonstrate its effect on Brassica juncea var. vasundhra. Generally when the level of antioxidants processes and detoxification mechanisms are lesser than the level of ROS accumulation, damages to the plant occurs. Most plants have evolved complex protecting systems against ROS. These comprise non enzymatic and enzymatic antioxidants. Such systems act as defensive systems against oxidation of biomolecules and block the process of oxidative chain reactions [18]. The present investigation provides evidence of induction of phenolic metabolism as a response to metal stress. Phenolic compounds are shown to have strong antioxidant activity in plants growing under heavy metal stress [17]. It has been suggested that their antioxidant act resides chiefly in their chemical structure. Phenols are oxidized by peroxidase and contribute in scavenging H2O2. REFERENCES [1] A.Bouchereau, A. Aziz Larher, F. Martin-Tanguy, J. Plant Science., 1999, 140, 103-125. [2] N. Babini, A. Tassoni, Amino Acids., 2001, 20, 301-317. [3] R. Kaur-Sawhney, A.F. Tiburcio T. Altabella, A. Galston, Journal of Cell and Molecular Biology., 2003, 2, 1-12. [4] N. Babini, A. Tassoni, Floriculture, Ornamental and Plants Biotechnology: Avances and Topical Issues , Global Scince Book, London, 2006, 88 -95. [5] T. Swain, W.E.Hillis, J. Sci. Food. Agric., 1959. 10, 63-68. [6] J.D. Coombs, O. Hall, S.P. Long, and J.M.O. Scunlacki, Techniques in Bioproductivity and Photosynthesis Π edition Pergamon Press., 1985, 223-224. [7] A.R. Wellburn, J. Plant Physiol., 1994, 144, 307-313. [8] R.L. Heath, and L. Packer, Arch. Biochemistry Biophysics., 1968, 125, 189-198. [9] S.P. Mukharji and M.A. Chaudhary, Plant Physiology., 1983, 58, 166-170. [10] L.S. Bates, R.P. Waldren, J.D. Teare, Plant Soil., 1973, 39, 205-207. [11] R.S. Dhindsa, P.P. Dhindsa and T.A. Thorpe, Journal of Experimental Botany., 1981, 32, 93–101. 129 Available online at www.scholarsresearchlibrary.com Yaksha Singh et al J. Microbiol. Biotech. Res., 2011, 1 (4):124-130 ______________________________________________________________________________ [12] H. Aebi, Methods Enymol., 1984, 105, 121-126. [13] Nakano Yoshiyuki and Asada Kozi, Plant Physiol ., 1980, 22, 867-880. [14] A.J. Able, D.I. Guest and M.W. Suterland, Plant Physiol., 1998, 117, 491-499. [15] R.K. Sairam and A. Tyagi, Current science., 2009, 86, 407-421. [16] T. Takahashi and Kakehi Jun-Ichi, Annals of Botany., 2010, 105, (1) 1-6. [17] A . Michalak Polish J of Environ Study 2006 15 (4) 523-530. [18] C.Sgherri,E.Cosi and F. Navari-Izzo, Physiol. Plant 2003 118, 21. 130 Available online at www.scholarsresearchlibrary.com
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