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First published online May 12, 2006; 10.1104/pp.105.076240 Plant Physiology 141:1138-1148 (2006) © 2006 American Society of Plant Biologists Heavy Metal Stress and Sulfate Uptake in Maize Roots1Dipartimento di Produzione Vegetale, Università degli Studi di Milano, 20133 Milan, Italy (F.F.N., C.L., B.C., G.A.S.); and Biochimie and Physiologie Moléculaire des Plantes, Institut National de la Recherche Agronomique (Unité 386), Centre National de la Recherche Scientifique (Unité Mixte de Recherche 5004), Ecole Nationale Supérieure Agronomique de Montpellier, Université Montpellier 2, 34060 Montpellier, cedex 1, France (P.F., J.-C.D.)
ZmST1;1, a putative high-affinity sulfate transporter gene expressed in maize (Zea mays) roots, was functionally characterized and its expression patterns were analyzed in roots of plants exposed to different heavy metals (Cd, Zn, and Cu) interfering with thiol metabolism. The ZmST1;1 cDNA was expressed in the yeast (Saccharomyces cerevisiae) sulfate transporter mutant CP154-7A. Kinetic analysis of sulfate uptake isotherm, determined on complemented yeast cells, revealed that ZmST1;1 has a high affinity for sulfate (Km value of 14.6 ± 0.4 µM). Cd, Zn, and Cu exposure increased both ZmST1;1 expression and root sulfate uptake capacity. The metal-induced sulfate uptakes were accompanied by deep alterations in both thiol metabolism and levels of compounds such as reduced glutathione (GSH), probably involved as signals in sulfate uptake modulation. Cd and Zn exposure strongly increased the level of nonprotein thiols of the roots, indicating the induction of additional sinks for reduced sulfur, but differently affected root GSH contents that decreased or increased following Cd or Zn stress, respectively. Moreover, during Cd stress a clear relation between the ZmST1;1 mRNA abundance increment and the entity of the GSH decrement was impossible to evince. Conversely, Cu stress did not affect nonprotein thiol levels, but resulted in a deep contraction of GSH pools. Our data suggest that during heavy metal stress sulfate uptake by roots may be controlled by both GSH-dependent or -independent signaling pathways. Finally, some evidence suggesting that root sulfate availability in Cd-stressed plants may limit GSH biosynthesis and thus Cd tolerance are discussed.
To minimize the detrimental effects of heavy metal accumulation, plants have evolved detoxification mechanisms, mainly based on chelation and subcellular compartmentalization (Clemens, 2001
Chelation of heavy metals is a ubiquitous detoxification strategy described in a wide variety of plants (Zenk, 1996
The mechanism of heavy metal detoxification based on PC biosynthesis is well described in the case of Cd; the isolation of the Arabidopsis (Arabidopsis thaliana) cad1 mutant, which is defective in PCS activity and consequently Cd hypersensitive, has underlined the significance of this mechanism for plant survival in polluted soils (Howden et al., 1995
It has been shown that Cd exposure and accumulation induce a transient depletion of GSH, which is used as substrate for a massive PC production (Tukendorf and Rauser, 1990
In a previous work we showed that in Cd-stressed maize (Zea mays) plants the need for maintaining a high rate of PC biosynthesis and adequate GSH levels may be also met by increasing the sulfate uptake capacity of the roots probably by the up-regulation of HAST, a gene encoding a putative high-affinity sulfate transporter (Nocito et al., 2002
The activity of sulfate transporters has been extensively shown to be transcriptionally regulated by signals, such as the GSH level, reflecting the sulfur nutritional status of the plants (Hawkesford, 2000
To thoroughly understand the effect of Cd on sulfate uptake regulation in maize roots we present a study aimed at analyzing the transcriptional regulation of ZmST1;1, the putative high-affinity sulfate transporter gene previously named ZmST1-701, HAST, or ZmST1 (Bolchi et al.,1999
Cloning and Functional Characterization of ZmST1;1
The ZmST1;1 (accession no. AF355602) coding sequence was amplified by reverse transcription (RT)-PCR from total RNA isolated from maize roots. Sequence analysis confirmed the identity of the cloned PCR product as the cDNA encoding the putative high-affinity sulfate transporter described by Hopkins et al. (2004)
The expression of ZmST1;1 in the yeast (Saccharomyces cerevisiae) double sulfate transporter mutant CP154-7A (Cherest et al., 1997
Effect of Different Cd Concentrations on Thiol Compounds, Sulfate Uptake Capacity, and ZmST1;1 Transcript Levels in Maize Roots To further investigate the role of GSH as putative signal involved in modulating sulfate uptake during Cd stress, we performed experiments on maize plants grown for 48 h in complete nutrient solutions in the absence (0 µM) or presence of CdCl2 at different concentrations (1, 5, or 10 µM). The analyses of thiol compounds showed that the NPT contents of the roots, expressed as GSH equivalents (Fig. 3A ), progressively increased up to 5.5-fold with respect to the control, while at the same time a significant contraction of total glutathione pools (reduced + oxidized form) of the root (Fig. 3B) was observed under all Cd-exposure conditions (about 50% as compared to the control). Moreover, Cd exposure significantly decreased the GSH pools but at the same time slightly increased the levels of glutathione disulfide (GSSG), affecting thus the GSH/GSSG ratio that in Cd-stressed roots had lower results than in the control (Fig. 3B). Northern-blot analysis, carried out on total RNA extracted from roots revealed that, upon Cd treatment, the ZmST1;1 transcript relative abundance significantly increased in relation to Cd concentration in the nutrient solution (Fig. 3C). Such a last response was positively correlated to an enhancement in the sulfate uptake capacity of the roots (Fig. 3D). The rate of 35S-sulfate uptake, measured at 0.2 mM SO42 external concentration, increased up to 1.6-fold with respect to the control at the highest Cd external concentration (10 µM).
Cd Stress Versus Sulfate Deprivation
Since the above-reported data resulted from a long-term equilibrium between metabolite levels and gene expression, to better understand the relationship existing between Cd stress, sulfate transport, and thiol metabolism, we performed experiments aimed at comparing the short-term (
In the same conditions NPT, GSH, GSSG, Cys, and -EC levels of the root were analyzed (Table I
). Results showed that sulfate deprivation did not affect NPT levels during the first 6 h from sulfate withdrawal; a significant effect appeared only after 12 h of sulfur starvation, when the level of these compounds decreased by 50% with respect to the control (Table I). Differently, following Cd exposure the level of NPTs progressively increased over time resulting, in all conditions, higher than that of the control (Table I). During the first 6 h from sulfate withdrawal, no effects on both GSH and GSSG levels were detectable; at the 12th h the total glutathione concentration fell down to 0.48-fold the value of the control. Nevertheless, even in this last condition the GSH/GSSG ratio remained constant (Table I). Differently, after 3 h of Cd treatment the total glutathione level dramatically decreased with respect to the control (49%), remaining constant during the entire observation period (Table I); in the same conditions a significant decrement of the GSH/GSSG ratio was observed with respect to the control (Table I). Moreover, sulfate deprivation did not affect the levels of Cys and -EC into the root, which was different from Cd exposure that resulted in a progressive accumulation of these compounds (Table I).
Effect of Zn and Cu on Thiol Compounds, Sulfate Uptake Capacity, and ZmST1;1 Transcript Levels in Maize Roots
The relationship between sulfur metabolism and ZmST1;1 expression pattern was also investigated in the roots of maize plants exposed to other heavy metals, Zn and Cu, which have been previously shown as affecting thiol metabolism and/or PC biosynthesis (Tukendorf, 1996 The analysis of thiol compounds of the root revealed that Zn and Cu had different effects on NPTs, GSH, and GSSG. In fact, compared to the control, the NPT levels dramatically increased following Zn exposure (+257% and +361% at 100 and 250 µM ZnCl2, respectively) but were not affected by Cu (Fig. 5A ). Moreover, a significant effect on total glutathione was evident only in the roots of plants exposed to 250 µM ZnCl2 (+31% with respect to the control). Conversely, the GSH/GSSG ratio was significantly affected only by Cu exposure, which moved its value from 4.3 (control) to 0.2 (10 µM CuCl2). Such a behavior was related to a dramatic decrease in the GSH level of the roots (Fig. 5B).
Northern-blot analysis showed that both heavy metals modulated the ZmST1;1 transcript levels. Following 48 h of ZnCl2 (100 and 250 µM) or CuCl2 (10 µM) exposure the ZmST1;1 mRNA relative abundances were significantly higher in the roots of Zn- and, although to a lesser extent, Cu-treated plants than in those of the controls (Fig. 5C). Also in these cases, the root sulfate uptake capacity was modulated by the heavy metal exposure. In the presence of Zn the rate of sulfate uptake by roots had significantly higher results (+42% and +71% at 100 and 250 µM ZnCl2, respectively) than in the control (Fig. 5D); a similar effect was detected in Cu-treated roots, in which sulfate uptake was increased (+37%) by the presence of the heavy metal in the nutrient solution (Fig. 5D).
To establish whether Cd tolerance may be affected by the sulfate contents of the roots, we performed experiments on maize plants pregrown for 72 h at different sulfate concentrations (0, 0.2, and 2 mM) and then exposed for 48 h to 10 µM CdCl2 in a complete nutrient solution containing 0.2 mM SO42. The 72 h pregrowing period allowed us to modulate the total amount of sulfate stored in root tissues, which increased with sulfate concentration in the pregrowing solution (Table II ). Table II also reports the effect of Cd on the relative growth of both shoots and roots, calculated referring to the growth of control plants not exposed to the heavy metal. Plant relative growth was closely dependent on the sulfate concentration in the pregrowing solution. In fact, the inhibitory effect exerted by Cd on plant growth diminished as sulfate external concentration increased; the growth of both shoots and roots of plants pregrown in the solution containing 2 mM SO42 was not affected by Cd exposure. The concentration of Cd in shoot and root tissues, measured at the end of the Cd-exposure period, was not influenced by the pregrowth at different sulfate concentrations (Table II). However, the amount of Cd removed by the plants from the nutrient solution, calculated considering the total biomass and the tissue Cd concentrations, increased as the sulfate concentration of the pregrowing solution increased (Table II). The plants pregrown in the solution containing 2 mM SO42 were more efficient in Cd extraction (0.77 ± 0.02 µmol plant1) than those pregrown in the solutions containing 0.2 mM or no sulfate (0.50 ± 0.02 and 0.38 ± 0.01 µmol plant1, respectively).
The pregrowth treatment influenced the total glutathione content of the roots, which increased with sulfate availability in the pregrowing solution (Fig. 6 ). Following Cd exposure, the total glutathione levels decreased in all conditions analyzed. However, at the end of the 48 h Cd-exposure period, a similar relation was still observed between the total glutathione levels of the roots and the sulfate concentration in the pregrowing solution (Fig. 6).
In a previous work we hypothesized that sulfate transporter genes are involved in Cd-detoxification mechanisms based on PCs (Nocito et al., 2002
The activity of sulfate transporters is transcriptionally regulated by signals reflecting the nutritional status of the plants (Hawkesford, 2000
Following Cd stress, a deep alteration of the sulfur nutritional status of maize plants occurs, mainly as a consequence of the Cd-induced PC biosynthesis. In fact, the levels of NPTs dramatically increase because of the massive biosynthesis of PCs, which rapidly become the most abundant class of thiols in the root cells with a consequent transient depletion of the GSH pools (Tukendorf and Rauser, 1990 With the aim to investigate the role of GSH in modulating sulfate transport activity during Cd stress we carried out a set of experiments with plants exposed to different Cd concentrations, to induce additional sinks for thiol compounds with different strength, and then GSH-consuming activities that could result in different GSH levels. Results suggest that the extent of the Cd-induced sulfate uptake is closely related to the strength of the Cd-induced additional sink for thiol compounds, which increases with the heavy metal concentration in the nutrient solution. In fact, a progressive enhancement in the NPT and ZmST1;1 mRNA levels and in the rate of sulfate uptake occurred as the external Cd concentration increased (Fig. 3). These responses were accompanied by a contraction of the root total glutathione contents, whose values do not seem clearly related to the strength of the additional sinks for thiols induced by Cd stress. In fact, as shown in Figure 3, moving from 1 to 10 µM Cd2+ external concentration, the NPT levels of the root increased from 78% to 454% with respect to the control, while the total glutathione levels fell down to about 0.5-fold the value of the control at the lower concentration analyzed and then remained constant as Cd concentration increases. A similar behavior was evident also considering the levels of GSH, a putative signal involved in sulfate transport modulation; in fact, the GSH/GSSG ratio in all Cd-exposure conditions, although lower than that of the control, remained constant.
Since this picture resulted from the establishment of a long-term equilibrium between metabolite levels, enzyme activities, and gene expression, speculating on the nature of GSH depletion and then on putative signals involved in ZmST1;1 gene expression appears difficult. In fact, the above-described behavior is consistent with the induction of GSH-consuming activities such as PC biosynthesis (Zenk, 1996
To thoroughly analyze the putative role of GSH in controlling ZmST1;1 expression, we performed short-term experiments aimed at comparing Cd-treated and sulfate-starved roots; both conditions are indeed able to positively modulate ZmST1;1 transcription (Bolchi et al., 1999
Such a behavior may reflect any difficulties in maintaining GSH homeostasis during Cd stress and could be ascribed to a direct effect of Cd on GS activity, as previously reported by Schneider and Bergmann (1995)
Concerning the mechanisms of sulfate transport regulation some physiological considerations need to be taken into account. Our knowledge of sulfate transport regulation mainly arises from extensive studies conducted on sulfur-starved plants. As expected, in this condition the absence or the reduced availability of sulfate in the external medium limits the sulfur flux through the assimilatory pathway with a consequent GSH biosynthesis impairment, which in turn may act as a signal in promoting the up-regulation of high-affinity sulfate transporters. Several works have shown the strength of these responses to be related to the entity of the decrement in the levels of GSH and Cys, which, in these conditions, represent the principal NPTs in plant tissues (Smith et al., 1997
Taken as a whole, our data suggest that during heavy metal-induced stress, sulfate uptake by roots may be controlled through GSH-dependent or -independent signaling pathways. However, the nature of these last signals needs to be further investigated. Several works have shown that other metabolic intermediates along the pathways of sulfate reductive assimilation and GSH biosynthesis, such as O-acetyl-serine (OAS), the carbon skeleton used for S2 assimilation, may play a role as signals in controlling both sulfate transporter and sulfur-responsive gene expression (Hawkesford, 2000
Considering the effect of Cd on sulfate uptake and thiol metabolism, a natural question arises: May sulfate acquisition limit GSH biosynthesis and thus Cd tolerance and accumulation? The experiments conducted with plants pregrown at different sulfate concentrations suggested that the toxic effects exerted by Cd accumulation can be alleviated maintaining high sulfate concentrations in the root tissues. In fact, following 48 h of Cd exposure, the total biomass produced by plants increased with sulfate concentration in the pregrowing solution (Table II). Such a behavior was likely due to an effect of root sulfate stores on the synthesis of GSH, since the levels of this metabolite were positively related to those of sulfate in the pregrowing solutions (Fig. 6). Similar results have been obtained in plants of Brassica juncea overexpressing GS, which maintain, in the absence or presence of Cd, GSH levels higher than those of the wild type (Zhu et al., 1999a
Our results suggest that root sulfate availability could represent a limiting factor for GSH biosynthesis and for plant Cd tolerance. Moreover, since other genes encoding high- and low-affinity sulfate transporters have been shown to be modulated in their expression following Cd exposure and accumulation (Heiss et al., 1999
Plant Material, Growth Conditions, and Experimental Design Maize (Zea mays L. cv Dekalb DK 300) caryopses were sown on filter paper saturated with distilled water and incubated at 26°C in the dark. Three days later, seedlings selected for uniform growth were transplanted into 5 L plastic tanks (18 seedlings per tank) containing an aerated complete nutrient solution [200 µM KNO3, 200 µM Ca(NO3)2, 40 µM KH2PO4, 200 µM MgSO4, 25 µM Fe-tartrate, 30 µM H3BO3, 5 µM MnCl2, 1 µM CuCl2, 1 µM ZnCl2, and 0.1 µM (NH4)6Mo7O24, pH 6.5] and kept for 3 d in a growth chamber maintained at 26°C and 80% relative humidity during the 16-h light period and at 22°C and 70% relative humidity during the 8-h dark period. Two experimental systems were used to study the involvement of GSH as metabolic signal in promoting ZmST1;1 derepression or the role of sulfate acquisition in Cd tolerance and accumulation. In the first, 3 d after seedling transplanting, the complete nutrient solution was supplemented with CdCl2, ZnCl2, or CuCl2 at different concentrations, or substituted with a minus-sulfate solution, where MgSO4 was replaced by an equimolar amount of MgCl2. The treatment period varied from 3 to 48 h. Plants were then sampled and frozen in liquid nitrogen or immediately used for further experiments (see sulfate influxes assay). In the second experimental system, 3 d after transplanting, seedlings were pregrown for an additional 72-h period in a nutrient solution (see above) containing different sulfate concentrations (0, 0.2, and 2 mM); in the 0 mM SO42 pregrowing solution MgSO4 was replaced by an equimolar amount of MgCl2. Plants were then exposed to 10 µM CdCl2 for 48 h in the complete nutrient solution containing 0.2 mM MgSO4. Relative growths of both shoots and roots were calculated referring to the growth of control plants not exposed to CdCl2. All hydroponic solutions were renewed daily to minimize nutrient depletion.
The ZmST1;1 cDNA was amplified by RT-PCR from maize total RNA isolated by roots. PCR primers ZmST1;1-for (5'-CAGCGAATTCATGCCGCCGCGAACGGTGTCC-3') and ZmST1;1-rev (5'-GCGCGAATTCTCAGACATTATCGACCATCTTAGGAGC-3') were designed to amplify the entire coding sequence of ZmST1;1, according to the nucleotide sequence (National Center for Biotechnology Information/GenBank accession no. AF355602) reported by Hopkins et al. (2004) Total RNA was extracted from roots of 5-d sulfur-starved plants using Trizol Reagent (Invitrogen) and first-strand cDNA synthesis was carried out using SuperScript first-strand synthesis system for RT-PCR (Invitrogen) according to the manufacturer's instructions. PCR was carried out on the first-strand cDNA using Pfu DNA polymerase (Promega) and the amplified EcoRI-ended fragment was cloned into the EcoRI site of pBluescriptII KS vector (Stratagene). The identity of the PCR product was verified by sequencing both the strands.
The EcoRI-ended fragment of ZmST1;1 cDNA was subcloned in the EcoRI site of the yeast (Saccharomyces cerevisiae) expression vector pESC-TRP (Stratagene) under the control of GAL10 promoter. The chimeric vector was used to transform the yeast double sulfate transporter mutant CP154-7A (MAT For the complementation test, Trp+ cells were grown to approximately 1 A600 unit in a Trp-free rich medium containing yeast nitrogen base and required amino acids. Yeast cells were then washed twice with sterile distilled water and resuspended to a final absorbance of 1 A600 unit in a selective synthetic minimal medium, named B medium, containing 15 mM NH4Cl, 6.6 mM KH2PO4, 0.5 mM K2HPO4, 2 mM MgCl2, 1.7 mM NaCl, 0.68 mM CaCl2, 80 µM H3BO3, 6 µM KI, 4 µM ZnCl2, 2 µM CuCl2, 1.8 µM FeCl3, 2% (w/v) Gal, 200 mg L1 His, 40 mg L1 adenine, 20 mg L1 inositol, 2 mg L1 calcium panthotenate, 2 mg L1 thiamine HCl, 2 mg L1 pyridoxine HCl, and 0.02 mg L1 biotine. Ten microliters of drops of the final cell suspension were dropped on B media, containing either 0.1 mM Na2SO4 or 0.1 mM D-L-homo-Cys as the sole sulfur sources, solidified with 1% (w/v) low sulfate-containing agarose (Invitrogen). Yeast cells were incubated at 28°C for 3 d and then analyzed for the growth.
Sulfate uptake kinetic was determined on complemented yeast cells by measuring the rate of sulfate uptake in a range of low sulfate external concentrations. To this purpose the complemented cells were grown in B medium containing 0.1 mM D-L-homo-Cys as sole sulfur source up to reach an absorbance of 0.9 A600 units. At the end of the growing period cells were washed twice with sterile distilled water and then resuspended to a final absorbance of 0.7 A600 units in a sulfurless B medium. The uptake assay was performed by adding 0.5 mL of cell suspension to 0.5 mL of B medium containing different Na2SO4 concentrations and labeled with 37 kBq Na235SO4. The mixture was incubated at 28°C for 30 and 210 s; for each time the incubation was stopped by the addition of 10 mL of ice-cold 0.1 mM Na2SO4, cells were filtered on a GF/C glass filter (Whatman), and then washed three times with 10 mL of ice-cold 0.1 mM Na2SO4. Radioactivity retained on each filter was measured by liquid scintillation counting in a
Roots of heavy metal-exposed, sulfur-starved, and control plants were pulverized using mortar and pestle in liquid nitrogen and total RNA was extracted using Trizol Reagent (Invitrogen). Thirty micrograms of total RNA per lane were separated by electrophoresis at 5 V cm1 in a 1.3% (w/v) agarose gel containing 6% (v/v) formaldehyde, transferred to Hybond-N+ nylon membrane (Amersham Bioscience) by capillary blotting in 20x SSC and then fixed by UV cross-linking. The blot was hybridized with 32P-labeled cDNA probe for the entire coding sequence of the high-affinity sulfate transporter ZmST1;1. Prehybridization and hybridization were conducted according to the nylon membrane manufacturer's instructions. Membrane was washed for 10 min with 2x SSC in 0.1% (w/v) SDS at room temperature, with 1x SSC in 0.1% (w/v) SDS at 65°C for 20 min and then for 10 min with 0.1x SSC in 0.1% (w/v) SDS at 65°C.
Sulfate influxes into the roots were measured by determining the rates of 35S uptake, over a 15 min pulse in incubation solutions labeled with the radiotracer. Three plants were placed onto 400 mL of a fresh complete nutrient solution, containing 200 µM MgSO4, supplemented or not with CdCl2, ZnCl2, or CuCl2 at different concentrations, aerated and thermoregulated at 26°C. Radioactive pulses were started by adding 35S-labeled Na2SO4 to the uptake solutions. Specific activity was 4.7 kBq µmol1. At the end of the pulse period, roots were excised from shoots, rinsed twice for 1 min in 400 mL of a 4 mM CaSO4 nonradioactive solution at 4°C, blotted with paper towels, and then heated for 20 min at 80°C in 0.1 N HNO3 (10 mL g1 fresh weight). Radioactivity was measured on aliquots of the extracting solution by liquid scintillation counting in a
Roots were pulverized using mortar and pestle in liquid nitrogen and stored frozen in a cryogenic tank. For Cys,
Roots were rinsed three times in distilled water and blotted with paper towels. Sulfate was extracted by homogenizing the samples in 1:10 (w/v) ice-cold 0.1 N HNO3. After heating at 80°C for 40 min, the extracts were filtered and the sulfate contents were then determined according to the turbidimetric method described by Tabatabai and Bremner (1970)
Plants were harvested and roots were washed for 10 min in ice-cold 5 mM CaCl2 solution to displace extracellular Cd (Rauser, 1987
ANOVA, Bonferroni's, and Student's t tests were calculated using SigmaStat for Windows (Version 3.11). Sequence data from this article can be found in the GenBank/EMBL data libraries under accession number AF355602. Received December 23, 2005; returned for revision April 28, 2006; accepted May 2, 2006.
1 This work was supported by grants from the Italian Ministry of Education, University, and Research (Ministero dell'Istruzione, dell'Università e della Ricerca Progetti di Ricerca di Interesse Nazionale 2004) and from French Research Institutes (Institut National de la Recherche Agronomique and Centre National de la Recherche Scientifique). The author responsible for the distribution of materials integral to the finding presented in this article in accordance with the policy described in the Instructions for Authors (www.plantphysiol.org) is: Gian Attilio Sacchi (gianattilio.sacchi@unimi.it). Article, publication date, and citation information can be found at www.plantphysiol.org/cgi/doi/10.1104/pp.105.076240. * Corresponding author; e-mail gianattilio.sacchi{at}unimi.it; fax 390250316521.
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