Effect of potassium deficiency on antioxidant status and cadmium toxicity in rice seedlings
© Liu et al.; licensee Springer. 2013
Received: 29 May 2013
Accepted: 29 May 2013
Published: 18 July 2013
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© Liu et al.; licensee Springer. 2013
Received: 29 May 2013
Accepted: 29 May 2013
Published: 18 July 2013
Cadmium (Cd) is one of the most toxic heavy metals and inhibits physiological processes of plants. Potassium (K) is an essential macronutrient in plants. K deficiency and Cd stress represent two different abiotic stress conditions that occur in the field simultaneously. In this study, effects of K deficiency on antioxidant status and Cd toxicity in rice seedlings were investigated.
K deficiency significantly decreased K concentration in shoots and roots. However, fresh weight and dry weight of rice seedlings were not affected by K deficiency. The activities of antioxidant enzymes (superoxide dismutase, ascorbate peroxidase, glutathione reductase, and catalase) in K-deficient leaves were higher than respective control leaves. However, K deficiency had no effect on the content of antioxidants (ascorbate and glutathione). Cd toxicity was judged by the decrease in biomass production, chlorosis, and induction of oxidative stress. Based on these criteria, we demonstrated that K deficiency protected rice seedling from Cd stress. Moreover, chlorophyll concentration was higher in K-deficient shoots and roots than their respective control shoots and roots.
Our results indicated that K deficiency protects rice seedlings from Cd toxicity. This protective effect of K deficiency is mainly due to enhanced antioxidant enzyme activities but not inhibition of Cd uptake.
Cadmium is a widespread metal contaminating many areas, either naturally or because of industrial use (Pan et al., 2010). Because of its long biological half-life, Cd is highly toxic. In plants, Cd is easily taken up by roots and translocated into shoots. Once Cd is taken up by plants, many cellular structures and metabolic processes are affected (Sanitá di Toppi and Gabbrielli, 1999; Gratǎo et al., 2005). Cd is a bivalent cation and unable to generate free radicals directly, nevertheless the production of reactive oxygen species (ROS) after Cd exposure has been reported (Sanitá di Toppi and Gabbrielli, 1999; Gratǎo et al., 2005; Cuypers et al., 2010). ROS has to be kept under tight control because their accumulation results in cell death due to oxidative processes such as lipid peroxidation, protein oxidation, and DNA damage (Gill and Tuteja, 2010). Plants use antioxidant enzymes such as superoxide dismutase (SOD), ascorbate peroxidase (APX), glutathione reductase (GR), and catalase (CAT) as well as non-enzymatic antioxidants such as ascorbate (AsA) and glutathione (GSH) to scavenge ROS (Noctor and Foyer 1998; Amudha and Balasubnramani 2011; Foyer and Noctor, 2011).
In agricultural systems, high-density monoculture crops deplete soil minerals quickly and therefore rely on external supplies for most of their nutrients, particularly nitrogen, potassium (K) and phosphorus (Amtmann et al., 2006). A balanced supply of mineral nutrients is crucial for both quantity and quality of the crop, but rarely achieved in the field. Of the mineral nutrients, imbalanced nutrition with K is well known and becoming an important constraint to crop production in many areas (Cakmak, 2010).
Potassium (K) is an essential macronutrient and plays an important role in metabolism as it functions as a cofactor of many enzymes and is required for charge balance and transport of metabolites (Marschner, 1995). It has been shown that the rate of net photosynthesis and the activity of ribulose-1, 5-bisphosphate carboxylase decrease in plants under conditions of K deficiency (Peoples and Koch 1979; Zhao et al., 2001; Cakmak, 2005; Weng et al., 2007). Several lines of evidence have also shown that K deficiency causes a decrease in sucrose export from source leaves (Mengel and Viro, 1974; Cakmak, 2005). Thus, the impairment in photosynthetic CO2 fixation and decrease in sucrose export in K-deficient leaves could lead to enhanced oxygen photoreduction in the chloroplast via the Mehler reaction resulting in the production of ROS. In order to detoxify ROS, increases in the activities/contents of antioxidants are expected in leaves of K-deficient plants. Indeed, enhancement in the activities of antioxidant enzymes has been demonstrated in K-deficient bean leaves (Cakmak, 1994 2005). Ding et al. (2008) also reported that the activities of SOD, CAT and peroxidase in the leaves of rice plants supplied with low K (0.5 mM) were higher than those supplied with high K (6 mM).
In the field, crops and other plants are routinely subjected to a combination of different abiotic stresses. For this reason, the importance of focusing the research programs in the response of plants to a combination of two different abiotic stresses has been emphasized (Mittler, 2006). Recently, we have revealed that Mg deficiency protects rice seedlings from Cd stress (Chou et al., 2011). In contrast, N deficiency was observed to enhance subsequent toxicity in rice seedlings caused by Cd stress (Lin et al., 2011). K deprivation and Cd stress represent another example of two different abiotic stress conditions that occur in the field simultaneously. However, it is not known whether Cd stress of rice seedlings is influenced by K deficiency. The present study was undertaken with the objective to examine the effect of K deficiency on antioxidant status and subsequent Cd-induced toxicity in rice seedlings.
Rice (Oryza sativa L., cv. Taichung Native 1) seeds were sterilized with 2.5% sodium hypochlorite for 15 min and washed extensively with distilled water. These seeds were then germinated in Petri dishes with wetted filter papers at 37°C in the dark. After 48 h incubation, uniformly germinated seeds were selected and cultivated in a beaker containing half-strength Kimura B nutrient solution with sufficient K supply (control) or deficient K supply (−K). Nutrient solution for the control contains the following macro- and micro-elements: 182.3 μM (NH4)2SO4, 91.6 μM KNO3, 273.9 μM MgSO4, 7H2O, 91.1 μM KH2PO4, 182.5 μM Ca(NO3)2, 30.6 μM Fe-citrate, 0.25 μM H3BO3, 0.2 μM MnSO4 · H2O, 0.2 μM ZnSO4 · 7H2O, 0.05 μM CuSO4 · 5H2O and 0.07 μM H2MoO4 (Kimura, 1931). Sodium nitrate substituted for KNO3 and NaH2PO4 for KH2PO4, respectively, under K-deficient conditions. Kimura B nutrient solution contains the desired nutrients for growing rice plants. Since young rice seedlings were used for the present study, the nutrient solution contained no silicon, although silicon is essential for growth of sturdy rice plants in the field.
Nutrient solution (pH 4.7) were replaced every 3 days. The hydroponically cultivated seedlings were grown in a Phytotron (Agricultural Experimental Station, National Taiwan University, Taipei, Taiwan) with natural sunlight at 30/25°C day/night and 90% relative humidity. Four beakers were used for each treatment, with 20 seedlings in each beaker. Twelve-day-old seedlings with three leaves were then grown with or without CdCl2 (5 μM) for 6 days. Cd toxicity (chlorosis, chlorophyll loss, and lipid peroxidation) was first shown in the second leaves of rice seedlings (Hsu and Kao, 2005). For this reason, unless otherwise indicated the second leaves of rice seedlings were used to perform all the chemical measurements and enzyme assays.
For determination of K and Cd, samples were dried at 65°C for 2 days. Dried material was ashed at 550°C for 4 days. The ash residue was incubated with 70% HNO3 and 30% H2O2 at 72°C for 2 h, and dissolved in distilled water for detection of K and Cd. K and Cd concentrations were then quantified using an atomic absorption spectrophotometer (Model AA-6800, Shimadzu, Kyoto, Japan) and expressed on a dry weight (DW) basis.
At the end of treatment, the seedlings were divided into shoots and roots. For DW estimation, the shoots and roots were dried at 65°C for 48 h, by which time the DW remains constant.
The H2O2 was extracted with sodium phosphate buffer (50 mM, pH 6.8) containing 1 mM hydroxylamine, a catalase inhibitor. The H2O2 content was measured after reaction with TiCl4 (Tsai et al., 2004). The blank reaction consisted of 50 mM phosphate buffer in the absence of leaf extracts. The absorbance was measured at 410 nm. The amount of H2O2 was calculated by using a standard curve prepared with known concentrations of H2O2.
The chlorophyll content was determined according to Wintermans and De Mots (1965) after extraction in 96% (v/v) ethanol. For protein determination, leaves were homogenized in a 50 mM sodium phosphate buffer (pH 6.8). The extracts were centrifuged at 17,600 g for 20 min, and the supernatants were used for determination of protein by the method of Bradford (1976). Malondialdehyde (MDA), routinely used as an indicator of lipid peroxidation, was extracted with 5% (w/v) trichloroacetic acid and determined by the thiobarbituric acid reaction as described by Heath and Packer (1968). The contents of H2O2, chlorophyll, and MDA were expressed on the basis of fresh weight (FW) of the second leaves prior to Cd treatment.
Ascorbic acid (AsA) and DHA contents in 5% (w/v) trichloroacetic acid were determined as described by Law et al. (1983). The assay is based on the reduction of Fe3+ to Fe2+ by AsA. The Fe2+ then forms complexes with bipyridyl, giving a pink color that absorbs at 525 nm. GSH and GSSG contents in 3% sulfosalicylic acid extract were determined by the method of Smith (1985). The content of GSH was spectrophotometrically determined with an enzyme-recycling assay at 412 nm. The assay is based on sequential oxidation of GSH by 5, 5-dithiobis-(2-nitrobenzoic acid) and reduction by NADPH in the presence of known amount of GR. The contents of AsA, DHA, GSH and GSSG were expressed on the basis of FW of the second leaves prior to Cd treatment.
Leaf samples were excised and immediately used for enzyme extraction. All operations were carried out at 4°C. For extraction of enzymes, leaf tissues (about 70 mg FW) were homogenized with 0.1 M sodium phosphate buffer (pH 6.8) in a chilled pestle and mortar. For analysis of APX activity, 2 mM AsA was added to the extraction buffer. The homogenate was centrifuged at 12,000 g. SOD activity was determined according to Paoletti et al. (1986). This method, originally used for animal material (liver), has been used to determine SOD activity in rice (Dey and Kar, 1995), maize (Bennicelli et al., 1998), cucumber (Piacentini et al., 2001), wheat (Goggin and Colmer, 2005), and potato (Agrawal et al., 2008). The reaction mixture (2.73 mL) contained 100 mM triethanolamine-diethanolamine buffer (pH 7.4), 7.5 mM NADH, EDTA/MnCl2 (100 mM/50 mM, pH 7.4), 10 mM 2-mercaptoethanol, and enzyme extract (0.2 mL). The reaction was started by the addition of NADH. The reaction was allowed to proceed for 10 min. The absorbance was measured at 340 nm. One unit of SOD was defined as the amount of enzyme that inhibited by 50% the rate of NADH oxidation observed in blank sample. CAT activity was assayed according to Kato and Shimizu (1987). The decrease in H2O2 was followed as the decline in the absorbance at 240 nm, and the activity was calculated using the extinction coefficient (40 mM-1 cm-1 at 240 nm) for H2O2. One unit of CAT was defined as the amount of enzyme which degraded 1 μmol H2O2 per min. APX activity was determined according to Nakano and Asada (1981). The decrease in AsA concentration was followed as a decline in the absorbance at 290 nm and activity was calculated using the extinction coefficient (2.8 mM-1 cm-1 at 290 nm) for AsA. One unit of activity for APX was defined as the amount of enzyme that degraded 1 μmol of AsA per min. GR was defined as the amount of enzyme of Foster and Hess (1980). One unit of GR was defined as the amount of enzyme that decreased 1 optical density min-1 at 340 nm. Enzyme activities were expressed on the basis of mg protein.
To test if the protection effect of K deficiency against Cd toxicity is due to enhanced protection against oxidative stress, the second leaves were detached from 12-day-old rice seedlings grown under K-sufficient and -deficient nutrition solutions. Ten detached leaves were then floated on Petri dish containing 10 μM paraquat (PQ) at 27°C for 24 h in the light (40 μmol m-2 s-1). After incubation, 10 detached leaves per treatment (four replicates) were analyzed for chlorophyll.
Data were analyzed by Student’s t-test or Duncan’s multiple range test. P < 0.05 was considered statistically significant.
Previous work demonstrated that Cd induces oxidative stress in rice leaves, characterized by an increase in the contents of MDA (an indicator of lipid peroxidation) and H2O2 (Kuo and Kao, 2004; Hsu and Kao, 2007). It was observed that the increase in the contents of MDA and H2O2 caused by 5 μM CdCl2 was less pronounced in K-deficient leaves than in control leaves (Figure 4B, C).
In the present study, rice seedlings were grown under K-sufficient and -deficient conditions for 12 days, by which time the third leaves of both K-sufficient and -deficient rice seedlings were fully grown. K deficiency significantly decreased K concentrations in shoots and roots of rice seedlings (Figure 1C, F). However, neither DW nor FW in shoots and roots was affected by K deficiency (Figure 1A, B, D, E). These results suggest that plant biomass is not effective for diagnosis of K deficiency in the early stage. It appears that K analysis rather than plant biomass is the most accurate tool to diagnose K deficiency.
In this study, Na salt substituted for K salt under K-deficient conditions. Elimination of K in this study by Na gives not only elimination of K but also leads to increase in Na concentration. It has been shown that NaCl inhibited growth of rice seedlings (Lin and Kao, 1995). Since growth of rice seedlings was not affected by K deficiency (Figure 1A, B, D, E), thus, Na taken up by rice seedlings does not seem to raise the concentration of the Na in the tissue to the levels that are toxic to rice growth under K deficiency conditions.
In the present study, Cd toxicity was evaluated by the decrease in biomass production, chlorosis, and induction of oxidative stress. On the basis of these criteria, it was demonstrated that K deficiency protected rice seedlings from the toxicity caused by 5 μM CdCl2 (Figures 3–6). PQ is an herbicide widely used in agriculture and a well known ROS-generating chemical. Treatment of detached rice leaves with 10 μM PQ for 24 h in the light caused marked chlorophyll loss. This chlorophyll destruction caused by PQ was higher in K-sufficient than K-deficient leaves (Figure 7). Clearly, K deficiency is able to protect rice seedlings from ROS damage caused by Cd or PQ. Thus, the K nutritional status of plants should be taken into consideration not only in evaluation of Cd toxicity but also in screening studies for PQ resistance. It is well known that PQ resistant plants also posses a higher resistance to O3 and SO2 (Shaalitiel et al., 1988; Tanaka et al., 1988). Based on the data shown in this study, it might be assumed that K-deficient leaf tissues are also more resistant to other ROS activating stress factors such as O3 and SO2.
It has been established that the increase in the activities of antioxidant enzymes and /or the contents of antioxidants is important for the improvement of stress tolerance (Gill and Tuteja, 2010). Cho and Seo (2005) demonstrated that seedlings of Cd-resistant Arabidopsis had higher activities of SOD, APX and GR and experienced lower oxidative stress from Cd exposure. The results of this study show that K-deficient rice leaves have higher activities of antioxidant enzymes, SOD, APX, GR, and CAT than K-sufficient leaves (Figure 2A-D). Enhanced activities of antioxidant enzymes have also been described in K-deficient bean leaves (Cakmak, 1994) and rice plants (Ding et al., 2008).
Irrespective of K supply, Cd treatment resulted in an increase in Cd concentration in rice roots and shoots (Figure 8A, B). The Cd concentration was lower in shoots than in roots (Figure 8A, B), indicating that a higher proportion of the Cd taken up by rice remained in the roots. This is in agreement with previous reports (Jalil et al., 1994; Wu and Zhang, 2002; Ueno et al., 2010). Figure 8 showed that Cd concentration was higher in K-deficient shoots and roots than their respective control shoots and roots. Thus, the protective effect of K deficiency against Cd toxicity is mainly due to enhanced antioxidant status but not inhibition of Cd uptake. It appears that K-deficient leaves experienced lower oxidative stress. In this study, the total shoot and root Cd concentrations were measured. It is not known whether K deficiency alters Cd distribution between vacuolar compartment and the rest of the cell. In future studies, it will be important to determine the effect of K deficiency on Cd concentration in different cellular compartments.
In conclusion, our results indicated that K deficiency protects rice seedlings from Cd toxicity. This protective effect of K deficiency is mainly due to enhanced antioxidant enzyme activities but not inhibition of Cd uptake.
Reactive oxygen species
This work was supported financially by the National Science Council of the Republic of China (NSC 99-2628-B-002-001).
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