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First published online August 7, 2003; 10.1104/pp.103.022178 Plant Physiology 133:307-318 (2003) © 2003 American Society of Plant Biologists Sodium Influx and Accumulation in Arabidopsis1Department of Plant Sciences, University of Cambridge, Cambridge CB2 3EA, United Kingdom
Arabidopsis is frequently used as a genetic model in plant salt tolerance studies, however, its physiological responses to salinity remain poorly characterized. This study presents a characterization of initial Na+ entry and the effects of Ca2+ on plant growth and net Na+ accumulation in saline conditions. Unidirectional Na+ influx was measured carefully using very short influx times in roots of 12-d-old seedlings. Influx showed three components with distinct sensitivities to Ca2+, diethylpyrocarbonate, and osmotic pretreatment. Pharmacological agents and known mutants were used to test the contribution of different transport pathways to Na+ uptake. Influx was stimulated by 4-aminobutyric acid and glutamic acid; was inhibited by flufenamate, quinine, and cGMP; and was insensitive to modulators of K+ and Ca2+ channels. Influx did not differ from wild type in akt1 and hkt1 insertional mutants. These data suggested that influx was mediated by several different types of nonselective cation channels. Na+ accumulation in plants grown in 50 mM NaCl was strongly reduced by increasing Ca2+ activity (from 0.05-3.0 mM), and plant survival was improved. However, plant biomass was not affected by shoot Na+ concentration, suggesting that in Arabidopsis Na+ toxicity is not dependent on shoot Na+ accumulation. These data suggest that Arabidopsis is a good model for investigation of Na+ transport, but may be of limited utility as a model for the study of Na+ toxicity.
Soil salinity reduces yields in a wide variety of crops and affects almost 1,000 million ha of agricultural land globally (Szabolcs, 1994
In many plants, a large component of tolerance to long-term exposure to Na+ can be attributed to the ability of plants to exclude Na+ from the shoot (Munns, 2002
It is proposed that the initial influx step is a key determinant of overall shoot Na+ accumulation (Schubert and Läuchli, 1990
The pathways for initial Na+ influx are still not identified. Tester and Davenport (2003
Interestingly, the relationship observed in many plants between (Ca2+-sensitive) Na+ accumulation and (Ca2+-stimulated) tolerance does not appear to hold for maize or rice. In maize, although Ca2+ alleviates Na+ toxicity, growth inhibition is correlated with the sensitivity of leaf extension to salt-stimulated increases in abscisic acid (ABA) rather than the extent of Na+ accumulation (Cramer and Quarrie, 2002 The aims of this study were (a) to characterize rigorously the unidirectional influx of Na+ with a view to underpinning future molecular studies identifying the pathways for Na+ influx, and (b) to characterize the Na+ sensitivity of growth of Arabidopsis in transpiring conditions and to relate this to shoot Na+ accumulation, with a view to comparing this response to those of other Brassica spp. and the cereals.
Time Course of Na+ Influx The amount of 22Na+ in root tissue increased very rapidly, with uptake being linear for the first 2 min of exposure to the uptake solution and slowing greatly within 5 min (Fig. 1). Thus, an influx time of 2 min was used for subsequent experiments, because longer times would result in an underestimation of unidirectional influx. This influx is unlikely to be due simply to wall binding because influxes occurred after pre-equilibration of wall binding sites for times that were much longer than the influx and rinse times. Furthermore, simple wall binding cannot easily be reconciled with both the elimination of influx in roots that had been boiled (Table I), nor with the significant and repeatable inhibition of influx by submillimolar concentrations of a range of organic compounds (Tables I, II, and III).
A likely consequence of this rapid influx would be a rapid increase of Na+ in root tissue upon changes in external Na+ concentrations. This can be confirmed by directly measuring changes in tissue Na+ concentrations upon changes in external Na+. When roots of Arabidopsis grown and treated in exactly the same way as for 22Na+ influx experiments were placed in 100 mM NaCl plus 3 mM Ca2+ activity for 10 min and then rinsed for 5 min in ice-cold 10 mM CaCl2, tissue Na+ concentration was measured to be 16.5 ± 1.7 µmol g-1 fresh mass (n = 4). Roots analyzed immediately before such a Na+ influx treatment contained 1.6 ± 0.2 µmol Na+ g-1 fresh mass (n = 4), suggesting a net influx into the excised roots of 1.5 µmol g-1 fresh mass min-1, notably similar to that measured using 22Na+. Thus, it is very likely that the influxes measured in this work are not only truly unidirectional but are also occurring across the plasma membrane into living cells within the root.
Sodium influx increased linearly with increasing external Na+ concentration, at least in the range tested, of 1 to 200 mM NaCl (Fig. 2). These fluxes were conducted with a constant Ca2+ activity of 0.2 mM, requiring an increase in Ca2+ concentration from 0.25 to 0.68 mM, due to the effect of NaCl on Ca2+ activity as NaCl increased from 1 to 200 mM (see figure 4 in Tester and Davenport, 2003
The effect of Ca2+ activity on Na+ influx was more complicated (Fig. 3). When roots were not pretreated in sorbitol before uptake, then Na+ influx was significantly inhibited (up to 70%) by increasing extra-cellular Ca2+ activity up to 1 mM. At activities above 1 mM, Ca2+ had no further effect on Na+ influx, i.e. the remaining Na+ influx was Ca2+ insensitive. It should be noted that Ca2+ is being used in this study simply as a pharmacological agent, and no claims are being made to its relevance to Na+/Ca2+ interactions in the soil solution.
In experiments where excised roots were pretreated in sorbitol for 3 h, however, Na+ influx was not affected by differences in external Ca2+ activity (Fig. 3). Pretreatment with sorbitol reduced Na+ influx relative to untreated roots only at low Ca2+ activities (below 1 mM Ca2+ activity), that is, sorbitol pretreatment appeared to affect only Ca2+ sensitivity of influx. Na+ influx at low Na+ concentrations is also Ca2+ sensitive (Essah, 2002
To investigate further the inhibition of the Ca2+-sensitive component of Na+ influx by sorbitol, roots were pretreated with an iso-osmotic concentration of another osmoticum, PEG 8000 (60 mg mL-1), having the same osmotic potential (97 mmol kg-1) as 50 mM NaCl. The results obtained showed that pretreating roots in iso-osmotic PEG led to a significant decrease in the Ca2+-sensitive component of Na+ influx relative to the control (Fig. 5), suggesting that the decrease may be due to the effects of osmotic potential. However, pretreating roots for 3 h in 50 mM NaCl did not reduce the Ca2+ sensitivity of Na+ influx, but rather increased both the Ca2+-sensitive and -insensitive components of Na+ influx by 28% and 38%, respectively (Fig. 5). On the other hand, growing plants on NaCl (phytagel plates supplemented with 50 mM NaCl and 0.2 mM Ca2+ activity) before influx significantly reduced influx compared with control plants, but did not significantly affect the Ca2+ sensitivity of Na+ influx.
To investigate further whether the effects of 3-h pretreatments in iso-osmotic sorbitol and PEG on the Ca2+ sensitivity of Na+ influx were attributable to the osmotic effects of these solutes, Na+ influx was measured in 1 mM NaCl in roots pretreated with sorbitol or PEG at concentrations iso-osmotic with 50 mM NaCl. Sorbitol or PEG was included in the uptake medium, and length of pretreatment was either 10 min or 3 h. Short-term exposure to high concentrations of sorbitol or PEG did not alter Na+ influx relative to controls (10-min pretreatment in 1 mM NaCl and 0.05 or 1 mM Ca2+ activity) (Fig. 4). However, longer exposure (3 h) to sorbitol clearly reduced Ca2+ sensitivity of influx (similar to the level observed in 50 mM NaCl; Fig. 5). This last result is in contrast to the lack of effect of low concentrations of sorbitol on Ca2+ sensitivity of influx at low concentrations of Na+ (reported above). This suggests that influx at lower concentrations of NaCl (1-10 mM) is similar in its characteristics to that at 50 mM and above and that the effect of sorbitol on Ca2+ sensitivity of influx depends on prolonged exposure to fairly high concentrations of sorbitol.
For this study, Na+ influx for 2 min from a 50 mM NaCl solution was conducted without the 3-h sorbitol pretreatment and with 0.2 mM Ca2+ activity to enable measurement of the effects of the pharmacological agents on both the Ca2+-sensitive and -insensitive components of Na+ influx.
Diethylpyrocarbonate (DEPC), a reagent that modifies His and Tyr residues in proteins (Mankelow and Henderson, 2001 The partial effects of Ca2+ and DEPC on Na+ influx suggests that there were three components (although not necessarily three separate mechanisms) of Na+ influx: a Ca2+-sensitive, DEPC-sensitive component; a Ca2+-insensitive, DEPC-sensitive component; and a component that was insensitive to both Ca2+ and DEPC. The mechanisms underlying these components were investigated using biochemical modifiers of known transport mechanisms. In the conditions used for these Na+ influx assays (no sorbitol pretreatment and 0.2 mM Ca2+ activity), the three components of Na+ influx were of approximately equal magnitudes (approximately 0.6 µmol g-1 min-1 each).
The monovalent cations Cs+ and tetraethyl-ammonium-Cl (TEA-Cl; K+ channel blockers) did not have any significant effect on influx (Table IV), suggesting that Na+ influx was not via TEA+ and Cs+-sensitive K+-selective channels. Among the divalent cations tested, Ba2+ (and Ca2+) significantly inhibited Na+ influx, whereas Zn2+ caused a nonsignificant reduction in Na+ influx. Although the effects of these divalent cations suggest that there could be a charge effect involved in the inhibition of Na+ influx into the roots, this is unlikely given the effects of the trivalent cations, Gd3+ and La3+. Gd3+ had no effect on Na+ influx, irrespective of the concentration used (0.01- 1.0 mM). La3+ inhibited influx at low concentrations (0.01 and 0.1 mM: data not shown), but significantly increased influx when higher concentrations were applied (Table IV). Amiloride (an inhibitor of Na+/H+ antiporters) and verapamil (a Ca2+ channel blocker) had no significant effects on Na+ influx. Taken together, these results suggest that Na+ uptake into the roots was not via K+ channels, Na+/H+ antiporters, and/or Ca2+ channels. The stimulation of Na+ influx by high concentrations of La3+ may be an indirect effect due to the cytotoxicity of these concentrations. Evidence consistent with cytotoxicity of millimolar concentrations of La3+ has been observed in Arabidopsis (J. Love, A.N. Dodd, and A.A.R. Webb, unpublished data), and the membrane depolarization of Neurospora crassa by 1 mM La3+ observed by Corzo and Sanders (1992
Flufenamate (an inhibitor of nonselective cation channels in animals) and quinine (a non-specific cation channel blocker) significantly reduced the influx of Na+ with 0.2 mM Ca2+ (Table II). Influxes were therefore conducted at low (0.05 mM) and high (3.0 mM) Ca2+ activities to further investigate the effects of these compounds. The results indicated that flufenamate was (partially) inhibiting only the Ca2+-sensitive portion of Na+ influx, whereas quinine inhibited both the Ca2+-sensitive and -insensitive components (Table II).
The application of H2O2 (an agonist of plant plasma membrane Ca2+-permeable cation channels; Demidchik et al., 2002 To investigate further what type of nonselective cation channels could be operating in Na+ uptake, the effects of bromocyclic monophosphates and aminobutyric acids on Na+ influx were tested. The bromocyclic monophosphates (Na+ salts) tested reduced influx, although only the inhibition by 8-bromoguanine 3',5'-cyclic monophosphate was statistically significant at P < 0.05 (Table III). The rapid reduction in Na+ influx by external application of membrane-permeable analogs of cGMP and cAMP (to a lesser extent) suggests a down-regulation of the channel proteins responsible for the uptake, probably through direct binding.
Addition of l and 10 mM DL- The effects of Glu, an agonist of neuronal nonselective cation channels, were also tested. This required slight modifications to the general procedure for influx assays, in that there was just a 5-min pretreatment in Glu-containing solutions, and both the pretreatment and the labeled influx solutions contained 2 mM MES. To this was added 2 or 10 mM Na-Glu, and the pH was adjusted to 5.6 with Tris base. The concentration of NaCl was reduced to 40 mM in solutions containing 10 mM Na-Glu. Under these conditions, the influx of Na+ into excised roots was increased by 25% in 2 mM Na-Glu and by 17% in 10 mM Na-Glu (Table III).
Plants with reduced activity of K+ channels involved in K+ influx into roots (akt1; Hirsch et al., 1998
Na+ influx was also measured in the salt-sensitive sos3-1 mutant (Liu and Zhu, 1997
The scr2 mutant, which shows altered root development and endodermal function (Scheres et al., 1995
The rss (for reduced salt sensitivity; Werner and Finkelstein, 1995
Growing plants in 50 mM NaCl inhibited plant growth, reducing the fresh and dry mass by 30% to 50% when compared with control plants grown in 1 mM NaCl (data not shown). Increasing the Ca2+ activity from 0.05 to 0.2 or 3 mM improved survival of plants. Only 14 of 24 plants survived 3 weeks of 50 mM NaCl treatment at 0.05 mM Ca2+ activity, compared with 24 of 24 and 21 of 24 plants surviving at 0.2 and 3 mM Ca2+ activities, respectively. However, there were only very small differences in the fresh and dry mass of the surviving plants, and their overall appearance was also very similar. Increasing the Ca2+ activity from 0.05 to 0.2 or 3 mM had a small effect on fresh and dry shoot masses of the surviving 50 mM NaCl-treated plants, but this effect was not statistically significant (Fig. 6a). The data in Fig. 6a were multiplied by a "survival factor" to take into account the differential survival in the three treatments and tend in fact to exaggerate the effect of Ca2+ in enhancing growth. The water content as well as fresh and dry root mass ratios (i.e. root mass divided by total plant mass) did not differ significantly for control and 50 mM NaCl-treated plants, and their values remained constant with higher Ca2+ (Essah, 2002
Relationship of Influx to Net Accumulation
Unidirectional influx of 22Na+ into roots of Arabidopsis plants could only be measured over a few minutes before the cytosol became fully labeled with 22Na and significant efflux contributed to the measurements. In 50 mM external NaCl, influx was around 1.8 µmol g-1 root fresh mass min-1. This is within the range measured in wheat (Davenport and Tester, 2000
The suggestion from our data that cytosolic Na+ turns over at very high rates is strongly supported by the thorough work of Cheeseman (1982
The very high rates of exchange of Na+ between the external solution and the cytosol would also explain the difference between the values we measure using 50 mM Na+ (around 1.8 µmol g-1 min-1) and the smaller fluxes found in Arabidopsis roots by other workers (of 0.1-0.15 µmol g-1 min-1) whose measurements were made with either longer influx times (Maathuis and Sanders, 2001 These rapid rates of influx imply high rates of Na+ efflux to the soil solution. Arabidopsis plants grown in 50 mM NaCl accumulated 335 to 1,281 µmol Na+ per gram of root fresh mass (depending on the Ca2+ activity) over 3 weeks (Table VI). These amounts would be accumulated within 3 to 12 h at measured rates of unidirectional influx (assuming a constant influx rate during growth). The disparity between unidirectional and net Na+ uptake implies high rates of Na+ efflux.
Measurements of unidirectional influx into roots of Arabidopsis seedlings indicated that there were three components of influx: a DEPC-insensitive component (which was not affected by extracellular Ca2+), and two components, which were inhibited by DEPC and were sensitive or insensitive to inhibition by extracellular Ca2+. In the following discussion, we attempt to relate these components to transport mechanisms. It must be emphasized that the components we distinguish are purely phenomenological, and it is possible that all are due to the activity of a single transporter or that more than one transporter type contributes to each component.
The influx experiments were designed to measure Na+ influx across the plasma membrane, with rinse conditions designed to displace apoplastic Na+. However, the discovery of a DEPC-insensitive component of Na+ influx raised the possibility that some of the Na+ influx was not protein-mediated and represented apoplastic Na+ binding. We think that the DEPC-insensitive component of influx was not due to apoplastic binding or apoplastic transport for several reasons. First, influx into boiled roots was negligible, indicating that rinse conditions were sufficient to displace most of the labeled extracellular Na+. Although boiled roots lack some of the complexity of intact roots, in particular the endodermal barrier, uptake of labeled Na+ into intact roots saturated rapidly, and so it was considered likely that any component of uptake due to leak of Na+ across the endodermis into the apoplast of the inner half of the root would exchange equally rapidly during rinsing. Second, DEPC only partially inhibited Na+ currents in isolated protoplasts from Arabidopsis roots, and was only effective in 56% of protoplasts (Demidchik and Tester, 2002
The scarecrow (scr) mutant has altered endodermal development and did show slightly higher influx, suggesting that in these plants, some of the influx measured was due to greater apoplastic leak across the endodermis (which could then result in higher uptake into stelar cells and so would be included in the influx measurement). This study did not attempt to measure apoplastic leak, except to attempt to exclude it from measurements, and the lack of transpiration would also reduce any apoplastic component. However, any Na+ that did leak across the endodermis and was taken up into stelar cells would be included in the measurement. The strong effect of Ca2+ in reducing net Na+ uptake suggests that bypass leak does not contribute significantly to uptake to the shoot (given that bypass flow, at least in rice, is Ca2+ insensitive; Yeo and Flowers, 1985
AtHKT1 has been demonstrated to act as a Na+ uniporter when expressed in Xenopus sp. oocytes, and both AtHKT1 and the wheat homolog TaHKT1 have been implicated in plant Na+ uptake (Rus et al., 2001
Influx of K+ into Arabidopsis roots is partially via the K+ transporters, AKT1 and AtKC (Hirsch et al., 1998
NSCCs are generally considered to constitute the major pathway for Na+ influx (Amtmann and Sanders, 1999
The main NSCC candidates in Arabidopsis are cyclic nucleotide-gated channels and Glu receptors. Both cAMP and cGMP inhibited Na+ influx (although this was statistically significant only in the case of cGMP). This is in accordance with a cyclic nucleotide inhibition of cation currents in Arabidopsis root protoplasts (Maathuis and Sanders, 2001
Recently, a number of hyperpolarization-activated Ca2+ conductances (HACCs) have been characterized in Arabidopsis, and in at least some cases, these appear to be carried by Ca2+-permeable NSCCs (Demidchik et al., 2002 It is not possible from the data presented here to attribute Na+ influx to a specific transport pathway. These data agree with other studies in identifying NSCCs as the most likely route of Na+ influx, however, much of this evidence is negative (based on lack of effect of modifiers of more selective channels). Plant NSCCs have proven difficult to characterize due to lack of specific blockers and effective agonists, and so we could not use rigorous diagnostic tests to confirm NSCC involvement. Moreover, our data suggested that several independent mechanisms probably operate in Na+ influx. For instance, the effect of sorbitol pretreatment in inhibiting only the Ca2+-sensitive portion of influx suggests that the Ca2+-sensitive pathway is discrete from the Ca2+-insensitive components. Alternatively, sorbitol pretreatment could cause modification of the properties of a single transporter type. At present, we do not have the tools to distinguish these possibilities.
Sodium influx was responsive to osmotic conditions. Growth in NaCl reduced Na+ influx to approximately one-half of that of control plants (pretreated for only 10 min in NaCl before measurement) but did not affect Ca2+ sensitivity of influx, suggesting either a uniform down-regulation of multiple pathways or reduction in activity of a single transporter type with partial Ca2+ sensitivity. However, a short (3-h) exposure to 50 mM NaCl increased Na+ influx (again without affecting Ca2+ sensitivity), suggesting a transient up-regulation of transport activity (or some effect of, for example, a change in membrane potential). In contrast to the effect of short pretreatment in NaCl, in plants pretreated in osmotica with low membrane permeability (PEG and sorbitol) for 3 h, Na+ influx was reduced to the Ca2+-insensitive component of influx. One explanation of this difference is that NaCl and the other osmotica had opposite effects on the ability of the plants to adjust to the sudden change in osmotic potential of the solution. NaCl uptake would provide a rapid means of turgor adjustment, whereas (relatively impermeant) sorbitol and PEG may induce synthesis of organic intracellular osmotica and a reduction in activity of NSCCs (which could leak cellular solutes in the low-salt conditions in which sorbitol and PEG were applied). Interestingly, the incubation of roots in high osmolarity enzyme solutions for several hours during protoplasting did not seem to affect Ca2+ sensitivity of Na+ currents in Arabidopsis root protoplasts (Demidchik and Tester, 2002
In wheat, the characteristics of Na+ influx have been shown to correlate reasonably well with both net uptake and toxicity (Davenport and Tester, 2000
Although transport characteristics in Arabidopsis and wheat appeared to be comparable, there was an interesting difference in the effect of Ca2+ on growth. Although increasing Ca2+ increased survival of Arabidopsis plants exposed to high NaCl concentrations, it had little effect on the growth of surviving plants. This was surprising because plants grown in 0.05 mM Ca2+ activity accumulated dramatically higher shoot Na concentrations than plants grown in 3.0 mM Ca2+ activity, yet there was no difference in biomass or water content between these plants. Liu and Zhu (1997
These results with Arabidopsis generally accord with a range of observations made with several Brassica spp. (He and Cramer, 1993 We suggest that Arabidopsis provides a reasonable model for the study of Na+ transport processes in other salt-sensitive species, but it probably should not be used as a general model for studies of Na+ tolerance, because the bases of toxicity may differ between Arabidopsis and species such as wheat.
Preparation of Seedlings Seeds of Arabidopsis ecotype C 24 were surface-sterilized in 3% (v/v) sodium hypochlorite containing 0.02% Triton X-100 for 15 min and rinsed six times with sterile de-ionized water. Approximately 20 surface sterilized seeds were grown in vertical 10-cm-wide square sterile plates containing 50 mL of medium per plate. The medium was composed of Murashige and Skoog basal salts (Duchefa, Haarlem, Netherlands), 1% (w/v) Suc, and 0.25% phytagel (Sigma-Aldrich, St. Louis), and pH adjusted to 5.7 with KOH before autoclaving. After planting, seeds were vernalized for 2 d at 4°C to break any residual dormancy and to ensure uniform germination. Plates were then transferred to a growth room with a temperature of 22°C, an approximate photon flux density of 100 m mol m-2 s-1 supplied by 30-W Grolux and 30-W warm white fluorescent tubes, and a 16-h photoperiod. Seedlings were used 12 d after the end of the vernalization, when roots were 8 to 9 cm long.
In most experiments, entire root systems were excised from the shoot (to eliminate potential complications arising from transpiration) and were pretreated in 15 mL of unlabeled uptake solution for 10 min, with solutions changed after 5 min. This was to equilibrate cell wall-bound Ca2+ and Na+ with that of the external solution, eliminating binding of 22Na+ to extracellular sites in a manner that could not be reversed with the rinses used. Channel blockers or modulators were also included during this pretreatment when tested. However, in some experiments, excised roots were pretreated for 3 h (instead of 10 min) in concentrations of sorbitol, PEG, or NaCl iso-osmotic with the uptake solution (plus 0.2 mM Ca2+ activity), to reduce the effects of osmotic shock on influx measurements. A longer recovery time after removal from the Phytagel and shoot excision was not used, to reduce long-term consequences arising from the removal of the photosynthate supply of the root. Recovery for up to 3 h had no effect on rates of influx, suggesting that any damage to roots arising from removal from the Phytagel did not have a large impact on influxes. In contrast, we found that removing roots from agar plates appeared to damage root function. Likewise, it was found that influx into roots excised from plants grown in solution culture was very similar to influx into roots grown on solid medium, suggesting that the damage to root hairs inevitable with the removal of plants from the solid medium did not significantly affect influx (P. Essah, unpublished data). As such, the most experimentally convenient protocol was selected. Uptake was measured in 15 mL of unbuffered uptake solution containing various concentrations of NaCl and CaCl2, 37 to 185 kBq L-1 of 22Na+, and channel blockers or modulators as indicated. Unless otherwise stated, influx solutions contained 50 mM NaCl and a Ca2+ activity of 0.2 mM, and influxes were measured over 2 min. Solutions were unbuffered, because the pH was found to remain unchanged after several 2-min uptake periods. There was no significant depletion of solutions during the course of up to 30 influx periods (monitored by measurements of the radioactivity of the solutions). To reduce effects of plant-to-plant variation and errors in both counting and weighing, 10 root systems were used for each influx assay.
At the end of the influx, roots were blotted and then transferred into 200 mL of ice-cold 200 mM NaCl plus 10 mM CaCl2 for two successive rinses of 2 min and then 3 min. The aim of these rinses was to displace apoplastic 22Na+ while inhibiting efflux from the root cells. Similar rates of influx were found if roots were rinsed in (iso-osmotic) 50 mM NaCl plus 10 mM CaCl2, but the higher concentration was used to increase confidence that all apoplastic 22Na+ was being removed in all treatments. Solutions were stirred on gently moving shakers (45 rpm). Roots were finally blotted gently, weighed rapidly, and transferred into plastic vials with 2.5 mL of scintillation cocktail (Optiphase Hisafe, Fisher Chemicals, Loughborough, UK). Samples were counted on a liquid scintillation counter (Beckman Instruments, Fullerton, CA). All chemicals used were analytical grade, except PEG 8000, which was ultra-pure and low in aluminum (catalog no. P-2139, Sigma-Aldrich). Ca2+ activities were calculated using GEOCHEM-PC v2.0 (Parker et al., 1995
For the growth experiment, 12-d-old seedlings (see "Preparation of Seedlings") were transferred onto plastic supports with holes placed over hydroponic growth solution in deep trays. The nutrient solution contained 2.5 L of: 5.0 mM KNO3, 0.25 mM KH2PO4, 2.0 mM MgSO4, 0.1 mM Ca(NO3)2, 0.05 mM FeEDTA, plus micronutrients (70 µM H3BO3, 14 µM MnCl2, 0.5 µM CuSO4, 1 µM ZnSO4, 0.2 µM Na2MoO4, 10 µM NaCl, and 0.01 µM CoCl2). This was similar to Hoagland solution, but with the phosphate concentration reduced to one-tenth of that in the original Hoagland solution because phosphate toxicity can sometimes be observed in saline conditions (Grattan and Maas, 1984 An aquarium pump fitted with an air stone gently aerated the solution. A propagator cover was placed over the top, and its vents were opened after 2 d, by which time the plants should have largely recovered from the shock of their transplantation. Plants were grown in this solution for 4 d, after which the solution was changed, and treatments were applied. Treatments consisted of two NaCl concentrations of 1 and 50 mM and three Ca2+ activities (0.05, 0.2, and 3.0 mM, supplied as 0.1 mM Ca(NO3)2 and supplemental CaCl2). For the 50 mM NaCl treatment, NaCl was supplied in two steps of 25 mM separated by a 2-d interval. This gradual increase enabled plants to adapt to the change in osmotic pressure. Solutions were topped up to 2.5 L daily with de-ionized water. Hydroponically grown plants were exposed to a temperature of 22°C, relative humidity of approximately 70%, and photoperiod of 10 h with a photon flux density of approximately 120 m mol m-2 s-1.
Plants were harvested 4 weeks after transplanting (and hence 6 weeks after planting). For each plant, the root and base of the stem were rinsed in de-ionized water for a few seconds to reduce surface contamination by Na+ from the growth solution. Roots (i.e. all tissue below the hypocotyl) and shoots were separated and blotted, and fresh masses were determined quickly. Plant tissues were then oven-dried for 48 h at 70°C, and their dry masses determined. Water content (WC) of tissues was calculated as a percentage according to the following equation:
To determine tissue Na+ and K+ concentrations, the dried plant material was boiled for 20 min in 10 mL of 100 mM nitric acid, made up to volume with de-ionized water, and analyzed for Na+ and K+ using a flame photometer (M410, Corning, Palo Alto, CA). Tissue Ca2+ concentration was determined using an atomic absorption spectrophotometer (Baird Alpha 1, Cambridge, UK).
We thank Vadim Demidchik for helpful discussions, John Banfield for technical assistance, Ana Rus and Mike Hasegawa for hkt1/sos3 mutants, and the Nottingham Arabidopsis Stock Centre for supplying other seeds. Received February 14, 2003; returned for revision March 19, 2003; accepted June 11, 2003.
1 This work was supported by a studentship from Churchill College (Cambridge) and an Overseas Research Scholarship (to P.A.E.), by a Royal Society Dorothy Hodgkin Research Fellowship (to R.D.), and by a Biotechnology and Biological Science Research Council Research Development Fellowship (to M.T.). * Corresponding author; e-mail mat10{at}cam.ac.uk; fax 44 -1223-333953.
Alberico GJ, Cramer GR (1993) Is the salt tolerance of maize related to sodium exclusion? I. Preliminary screening of 7 cultivars. J Plant Nutr 16: 2289-2303 Al-Mansour N (1996) Sodium accumulation in maize cultivars differing in their Na+ tolerance. M. Phil. thesis. University of Cambridge, Cambridge
Amtmann A, Fischer M, Marsh EL, Stefanovic A, Sanders D, Schachtman DP (2001) The wheat cDNA LCT1 generates hypersensitivity to sodium in a salt-sensitive yeast strain. Plant Physiol 126: 1061-1071 Amtmann A, Sanders D (1999) Mechanisms of Na+ uptake by plant cells. Adv Bot Res 29: 75-112 Ashraf M, Naqvi MI (1992) Growth and ion uptake of four Brassica spp. as affected by Na/Ca ratio in saline sand culture. Z Pflanzenphysiol Bodenkense 155: 101-108
Balagué C, Lin BQ, Alcon C, Flottes G, Malmström S, Köhler C, Neuhaus G, Pelletier G, Gaymard F, Roby D (2003) HLM1, an essential signaling component in the hypersensitive response, is a member of the cyclic nucleotide-gated channel ion channel family. Plant Cell 15: 365-379 Berthomieu P, Conéjéro G, Nublat A, Brackenbury WJ, Lambert C, Savio C, Uozumi N, Oiki S, Yamada K, Cellier F et al. (2003) Functional analysis of AtHKT1 in Arabidopsis shows that Na+ recirculation by the phloem is crucial for salt tolerance. EMBO J 22: 2004-2014[CrossRef][ISI][Medline] Cheeseman JM (1982) Pump-leak sodium fluxes in low salt corn roots. J Membr Biol 70: 157-164[CrossRef][ISI] Cheffings C (2001) Calcium channel activity of a plant glutamate receptor homologue. Twelfth International Workshop on Plant Membrane Biology, Madison, WI, October, 2001 Corzo A, Sanders D (1992) Inhibition of Ca2+ uptake in Neurospora crassa by La3+: a mechanistic study. J Gen Microbiol 138: 1791-1795 Cramer GR (2002) Sodium-calcium interactions under salinity stress. In A Läuchli, U Lüttge, eds, Salinity. Environment-Plants-Molecules. Kluwer Academic Publishers, Dordrecht, The Netherlands, pp 205-227 Cramer GR, Alberico GJ, Schmidt C (1994) Salt tolerance is not associated with the sodium accumulation of 2 maize hybrids. Aust J Plant Physiol 21: 675-692 Cramer GR, Quarrie SA (2002) Abscisic acid is correlated with the leaf growth inhibition of four genotypes of maize differing in their response to salinity. Funct Plant Biol 29: 111-115
Davenport R (2002) Glutamate receptors in plants. Ann Bot 90: 549-557
Davenport RJ, Tester M (2000) A weakly voltage-dependent, nonselective cation channel mediates toxic sodium influx in wheat. Plant Physiol 122: 823-834 Demidchik V, Davenport RJ, Tester M (2002) Nonselective cation channels. Annu Rev Plant Biol 53: 67-107[CrossRef][Medline]
Demidchik V, Shabala SN, Coutts KB, Tester MA, Davies JM (2003) Free oxygen radicals regulate plasma membrane Ca2+- and K+-permeable channels in plant root cells. J Cell Sci 116: 81-88
Demidchik V, Tester M (2002) Sodium fluxes through non-selective cation channels in the plasma membrane of protoplasts from Arabidopsis thaliana roots. Plant Physiol 128: 379-387 Di Laurenzio L, Wysocka-Diller J, Malamy JE, Pysh L, Helariutta Y, Freshour G, Hahn MG, Feldmann KA, Benfey PN (1996) The SCARECROW gene regulates an asymmetric cell division that is essential for generating the radial organization of the Arabidopsis root. Cell 86: 423-433[CrossRef] |