Gama-aminobutyric acid accumulation in Elsholtzia splendens in response to copper toxicity

Gama-aminobutyric acid accumulation in Elsholtzia splendens in response to copper toxicity first-author †E-mail:xyang@zju.edu.cn; penghongyun@zju.edu.cn †E-mail:xyang@zju.edu.cn; penghongyun@zju.edu.cn xyang@zju.edu.cn †E-mail:xyang@zju.edu.cn; penghongyun@zju.edu.cn †E-mail:xyang@zju.edu.cn; penghongyun@zju.edu.cn xyang@zju.edu.cn Ministry of Education Key Lab of Environment, Remediation and Ecosystem Health, School of Natural Resources and Environmental Science, Zhejiang University, Hangzhou 310029, China Ministry of Education Key Lab of Environment, Remediation and Ecosystem Health, School of Natural Resources and Environmental Science, Zhejiang University, Hangzhou 310029, China A solution with different Cu supply levels was cultured to investigate gama-aminobutyric acid (GABA) accumulation in Elsholtzia splendens , a native Chinese Cu-tolerant and accumulating plant species. Increasing Cu from 0.25 to 500 μmol/L significantly enhanced levels of GABA and histidine (His), but considerably decreased levels of aspartate (Asp) and glutamate (Glu) in the leaves. The leaf Asp level negatively correlated with leaf Cu level, while leaf GABA level positively correlated with leaf Cu level. The leaf Glu level negatively correlated with leaf GABA level in Elsholtzia splendens . The depletion of leaf Glu may be related to the enhanced synthesis of leaf GABA under Cu stress. Accumulation Copper toxicity Elsholtzia splendens Gama-aminobutyric acid (GABA) INTRODUCTION 1 Plants have developed metal tolerance traits to adapt to heavy metal contamination in soil by allowing absorption of essential micronutrients to satisfy normal physiological requirements, but avoiding excessive absorption of non-essential or toxic elements in the plant cell (Baker and Proctor, 1990 1990 ; Verkleij and Schat, 1990 1990 ). Elsholtzia splendens growing widely over Cu mining areas along the middle and lower streams of the Changjiang River has been identified as Cu-tolerant and accumulating plant species native to China (Yang et al., 1998 1998 ; Jiang et al., 2002 2002 ). The excess of free Cu ions not only induces generation of free radicals and oxidative stress in cells, but also inactivates enzymes and increases membrane permeability by binding to the sulfhydryl groups of enzymes and cytoplasm membrane proteins, thus destroying metabolic homeostasis (Van Assche and Clijsters, 1990 1990 ). The responses of plants to metal exposure have received considerable attention in toxicological and evolutionary contexts. However, little is known about metal-tolerance mechanisms based on the pathways by which metal “signals” in the environment elicit biochemical responses in E. splendens . GABA levels in plant tissues are typically low, ranging from 0.03 to 2.00 μmol/g fresh weight (FW), but increase several fold in response to various stimuli, including heat shock, mechanical stimulation, hypoxia and phytohormones (Shelp et al., 1999 1999 ). There is some evidence that GABA acts as a long-distance signal in up-regulation of nitrate uptake in Brassica napus L. (Beuve et al., 2004 2004 ). The aim of this study was to determine whether changes in the levels of leaf amino acids are related to Cu supply levels in solution and Cu levels in leaf of E. splendens . MATERIALS AND METHODS 1 Seeds of E. splendens were surface-sterilized and rinsed to establish plant seedlings for 14 d pre-culture in a basal nutrient solution as described by Yang et al.( 2002 2002 ). Cu at treatment concentrations of 0.25, 12.5, 50, 100 and 500 μmol/L was added as CuSO 4 ·5H 2 O. The experiment was set up in a completely randomized design with six replicates for each treatment. The culture solution was continuously aerated and maintained at pH 5.5±0.3, and adjusted daily with 0.1 mol/L NaOH or 0.1 mol/L HCl, and was renewed every 4 d during the 12 d experiment in a greenhouse with temperature ranging from (28±2) °C (day) to (15±2) °C (night), without supplementary light. At harvest, leaf samples were collected, and rinsed thoroughly with deionized water, blotted dry. For amino acid detection, the 4th leaf sample from the top of the plant were frozen immediately in liquid N 2 , lyophilized under vacuum and kept at −60 °C. Amino acids were assayed following the methods of Schaeffer and Sharpe ( 1997 1997 ), and determined by HPLC with an PE LS-50B fluorescence detector and an AccQ-Taq amino acid column by using AccQ-Taq Amino acids quantitation methods (Waters Alliance 2690). Plant leaves were dried at 65 °C, ground and passed through a 60-mesh sieve for elemental analyses by an Inductively Coupled Plasma-Optical Emission Spectroscopy (ICP-OES, Model IRAS-AP, TJA). All data were presented as mean values of at least six replicates. SPSS statistical software package (Version 11.0) was used for one-way Analysis of variance (ANOVA) to evaluate whether the means were significantly different at P ≤0.05. RESULTS AND DISCUSSION 1 Results in Table 1 1 show drastic increase of leaf Cu with the addition of 100 and 500 μmol/L Cu as compared to 0.25 μmol/L Cu. Yang et al.( 2002 2002 ) has observed the stimulated growth of E. splendens at 50 μmol/L Cu, but that significantly inhibited at 100 and 500 μmol/L Cu. Amino acids are involved in immobilization and detoxification of heavy metals in plant cells, which is attributed mainly to its carboxyl, amido, sulphydryl and phenol groups that can be bonded with heavy metals in cytosol. Xylem Ni accumulation in a Ni hyperaccumulator Alyssum lesbiacum was positively correlated with xylem His level when exposed to 10 −3 ~10 mmol/L Ni. EXAFS technique detected the binding of xylem Ni with xylem His (Krämer et al., 1996 1996 ). 2 Element 5 Leaf Cu concentration (μmol/L) 2 LSD 0.05 0.25 12.5 50 100 500 Ca (g/kg) 3.2 3.4 3.2 3.3 3.2 0.17 K (g/kg) 20 22 19 19 17 1.20 Mg (g/kg) 2.9 3.4 3.0 3.2 2.6 0.20 P (g/kg) 6.5 6.9 5.3 5.7 4.7 0.20 S (g/kg) 4.1 3.8 3.3 4.3 4.6 0.18 Cu (μg/g) 48.1 52.2 55.1 84.8 274.1 3.87 Zn (μg/g) 72 136 335 235 105 15.3 Fe (μg/g) 817 830 834 754 606 39.1 Mn (μg/g) 78 101 183 143 53 4.1 In this study, of 18 amino acids, Asp, Ser, Glu, His, Val and GABA constituted 80%–92% of the total amino acids in the leaves of E. splendens , each with the proportion of > 5% at different Cu supply levels. The levels of both leaf Ser and leaf Val were not correlated with the leaf Cu level or the Cu level in solution, and their proportion changed slightly as Cu increased from 0.25 to 500 μmol/L (Fig. 1 1 ). Leaf Asp was negatively correlated with both the leaf Cu level and Cu level in solution (Table 2 2 ). The fast degradation of Asp might decrease leaf Asp level when E. splendens accumulated high levels of Cu in the leaves. The leaf His levels were positively related to both the leaf Cu level and the Cu level in solution (Table 2 2 ). For example, leaf His increased 3.4-fold with the increase in Cu from 50 to 500 μmol/L. The positive correlation between leaf His levels with leaf Cu levels indicated that His accumulation in the plant might be involved in Cu uptake and accumulation in the plants. In both the vacuole and cytoplasm of Ni hyperaccumulator Thlaspi goesingense , Ni was mainly bonded with citric acid and His detected by X-ray Absorption Spectroscopy (XAS) techniques (Krämer et al., 1997 1997 ). But whether and how Cu is bonded with His in leaf cells of E. splendens is unknown. Correlation is significant at the 0.05 levels. Regression coefficients were tested with the analysis of covariance by SPSS statistical software package (Version 11.0) Leaf amino acid level Cu levels Regression equation Correlation coefficient ( R 2 ) Leaf Asp Cu in solution Y =31.06−0.04 X 0.912 * * Leaf Asp Leaf Cu Y =34.42−0.09 X 0.967 * * Leaf His Cu in solution Y =3.89 X +0.13 0.962 * * Leaf His Leaf Cu Y =3.89 X +0.13 0.962 * * Leaf Glu Leaf Cu Y =103.25−2.87 X +0.22 X 2 0.978 * * Leaf GABA Cu in solution Y =26.99+0.23 X −3.07 X 2 0.879 * * Leaf GABA Leaf Cu Y =17.91+0.35 X −6.33 X 2 0.842 * * As compared to 0.25 μmol/L Cu, leaf Glu level did not significantly change at 50 μmol/L Cu, but considerably decreased at 100 and 500 μmol/L Cu (Fig. 1 1 ). Significantly quadratic and negative correlations between the leaf Glu level and the leaf Cu level were observed (Table 2 2 ), and the leaf Glu level had considerably negative correlation with the leaf GABA level ( Y =61.84−0.85 X , R 2 =0.929, X and Y represent leaf GABA level and leaf Glu level, respectively). The leaf GABA level was increased pronouncedly at 100 and 500 μmol/L Cu, whereas no marked difference was observed at 50 μmol/L Cu as compared with 0.25 μmol/L Cu (Fig. 1 1 ). Positively quadratic relations were found between the leaf GABA levels and the leaf Cu level or the Cu level in solution (Table 2 2 ). It has been suggested that in plant cell stress-induced GABA synthesis is the result of cytosolic acidosis and the consequent stimulation of glutamate decarboxylase (GAD) (Snedden et al., 1992 1992 ). GAD activity catalysing the formation of GABA from Glu is regulated by Glu levels as well as Ca 2+ /calmodulin and H + , which result from the stresses of mechanical damage, heat shock, cold shock, hypoxia, and drought stimulation. In this study, the decreased Glu level in the plant may be due to the increased conversion of Glu to GABA under Cu toxicity, which inhibits glutamine synthesis or reduces protein synthesis (Satyanarayan and Nair, 1990 1990 ; Scott-Taggart et al., 1999 1999 ). The levels of macro- and micronutrients in E. splendens at different Cu supply levels were listed in Table 1 1 . Compared to 0.25 μmol/L Cu, for macronutrients, Ca was not changed, while K, Mg and P were decreased, and S was increased at Cu supply level of 500 μmol/L, whereas for micronutrients, Cu and Zn were enhanced but Fe and Mn were decreased at 500 μmol/L Cu. 500 μmol/L Cu was observed toxic to plant growth and considerably decreased levels of leaf Fe. At 100 μmol/L Cu, no marked change was found for macronutrients uptake, but increased uptake of Cu, Zn and Mn and minimum uptake for Fe were observed as compared to 0.25 μmol/L Cu. Kinnersley and Fang ( 2000 2000 ) reported that the increase in biomass of Lemna was accompanied by an increase in mineral content of GABA-treated plants, except for the decrease in Fe 2+ levels, as GABA levels increased from 1 to 10 mmol/L. However, the function of GABA in the plant is unclear. Beuve et al.( 2004 2004 ) demonstrated that N stress or critical N-demand for sustaining shoot growth during bolting period could result in accumulation of GABA, which in turn would induce increase of nitrate uptake. In our experiment, the increased accumulation of GABA in E. splendens at 100 and 500 μmol/L Cu was observed. But the metabolite or signal transduction functions of GABA accumulation in E. splendens in response to Cu toxicity need to be further investigated. References AJM Baker , J Proctor . 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