Plant Physiol. (1998) 116: 1393-1401

Development, Characterization, and Application of a Cadmium-Selective Microelectrode for the Measurement of Cadmium Fluxes in Roots of Thlaspi Species and Wheat¹

Miguel A. Piñeros, Jon E. Shaff, and Leon V. Kochian^*

United States Plant, Soil, and Nutrition Laboratory, United States Department of Agriculture-Agricultural Research Service, Cornell University, Ithaca, New York 14853

	ABSTRACT

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A Cd²⁺-selective vibrating microelectrode was constructed using a neutral carrier-based Cd ionophore to investigate ion-transport processes along the roots of wheat (Triticum aestivum L.) and two species of Thlaspi, one a Zn/Cd hyperaccumulator and the other a related nonaccumulator. In simple Cd(NO₃)₂ solutions, the electrode exhibited a Nernstian response in solutions with Cd²⁺ activities as low as 50 nm. Addition of Ca²⁺ to the calibration solutions did not influence the slope of the calibration curve but reduced the detection limit to a solution activity of 1 µm Cd²⁺. Addition of high concentrations of K⁺ and Mg²⁺ to the calibration solution to mimic the ionic composition of the cytoplasm affected neither the slope nor the sensitivity of the electrode, demonstrating the pH-insensitive electrode's potential for intracellular investigations. The electrode was assayed for selectivity and was shown to be at least 1000 times more selective for Cd²⁺ than for any of those potentially interfering ions tested. Flux measurements along the roots of the two Thlaspi species showed no differences in the pattern or the magnitude of Cd²⁺ uptake within the time frame considered. The Cd²⁺-selective microelectrode will permit detailed investigations of heavy-metal ion transport in plant roots, especially in the area of phytoremediation.

	INTRODUCTION

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Advances in the technologies and methodologies for studying ion transport in higher plant cells have advanced our understanding of the mechanisms by which plants absorb ions from soils and translocate them into the shoots. These advances can be used to increase our understanding of the phytoremediation of metal-contaminated soils. Phytoremediation is a "green technology" with which terrestrial plants are used as an inexpensive, low-technology method to remediate surface soils contaminated with toxic heavy metals. A number of plant species have been identified that are endemic to metalliferrous soils and can tolerate and accumulate high levels of heavy metals such as Zn, Cd, Pb, Cu, and Ni in the shoot (Brooks et al., 1977; Baker et al., 1994). These plants, called hyperaccumulators, can grow in soils contaminated with high levels of heavy metals by translocating and accumulating high concentrations in the shoots. For example, Thlaspi caerulescens, a Zn/Cd hyperaccumulator, can grow in soils containing concentrations as high as 35 µm Cd and 1830 µm Zn (Brown et al., 1994) and can accumulate up to 40,000 µg g¹ Zn in its shoots (Chaney, 1993). By comparison, the normal foliar Zn concentration for hydroponically grown plants is approximately 100 to 200 µg g¹ and 30 µg g¹ is considered adequate. This species also accumulates high levels of Cd in its tissues. These unique aspects of the physiology of T. caerulescens make it an ideal candidate for the study of the mechanisms by which such hyperaccumulator plants can tolerate and accumulate toxic levels of heavy-metal ions. Recent studies have started to reveal some of the fundamental mechanisms by which these plants accumulate heavy metals in shoots (Lasat et al., 1996). Still, there is little known about the fundamental biology concerning plant mechanisms of shoot heavy-metal hyperaccumulation.

Several techniques have been used to obtain estimates and to characterize fluxes of macro- and micronutrient ions in higher plant cells. Intact tissue techniques have often relied on bulk-solution methods, such as radioisotope-flux methods or solution-depletion measurements (Cataldo et al., 1983; Mullins and Sommers, 1986). Such approaches integrate ion uptake over the entire tissue surface, providing an averaged measurement over a period of time. Because these types of techniques are constrained in terms of the spatial and temporal resolution, they are usually used to study ion uptake into entire roots or root systems over fairly long periods. In recent years technological advances have facilitated the fabrication of liquid-membrane ISEs for a number of ions, which has made it possible to map ion-activity gradients (i.e. ion-transport processes) in the unstirred layer along the root surface. Diffusion analysis of these steady-state gradients has, for example, allowed researchers to calculate net K⁺, H⁺, and Ca²⁺ fluxes associated with localized regions of the root surface of maize (Zea mays L.) (Newman et al., 1987; Kochian et al., 1989; Ryan et al., 1990), as well as NH₄⁺ and NO₃ fluxes in barley roots (Henriksen et al., 1990, 1992; McClure et al., 1990), and the effects of other ions (e.g. Al³⁺) on various ion-transport systems in wheat roots (Miyasaka et al., 1989; Huang et al., 1992b; Ryan et al., 1992).

More recently, the development of a vibrating ISE system has proven to be a substantial improvement over the static ISE described above (Smith et al., 1994). By way of comparison, the sensitivity of the static liquid-membrane ISE is limited by the voltage drift due to the inherent high resistance (10¹⁰ ) of these electrodes, such that ion fluxes can be measured only as long as the background concentration is kept below approximately 0.3 mm. Likewise, smaller fluxes, such as Ca²⁺ influx into mature regions of the root, are very hard to detect, even at low background concentrations. Kühtreiber and Jaffe (1990) overcame these system limitations by developing a vibrating Ca²⁺-selective microelectrode that exhibited a greatly improved sensitivity over static electrodes. It allowed them to measure small extracellular Ca²⁺ gradients associated with Ca²⁺ fluxes in single cells such as fucoid eggs, pollen tubes, and moving amoebae. Vibrating ion-selective electrodes have subsequently been used to characterize root ion-transport processes with a high degree of spatial and temporal resolution (Huang et al., 1992a; Ryan and Kochian, 1993; Jones et al., 1995). Kochian et al. (1992) conducted a detailed comparison of static and vibrating ISE techniques to quantify K⁺, H⁺, and Ca²⁺ transport in intact maize roots and suspension cells. This study showed that the vibrating electrodes were approximately 50 times more sensitive than static microelectrodes, making vibrating electrodes the technique of choice when studying root-ion fluxes of small magnitude or ion-transport processes in single cells.

In the present work we have taken advantage of the vibrating-electrode technology, along with the synthesis of a Cd²⁺ ionophore (Schneider et al., 1980), to develop and characterize a Cd²⁺-selective electrode and to demonstrate its potential in studying Cd²⁺ transport in roots of nonaccumulator and hyperaccumulator plant species.

	MATERIALS AND METHODS

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Construction of Cd²⁺-Selective Microelectrodes

N,N,N,N

Vibrating-Microelectrode System

The system was mounted on the stage of an inverted microscope (IM 35, Zeiss) equipped with a video camera. A 486-PC computer running DVIS6 software (Biocurrents Research Center, Marine Biology Lab, Woods Hole, MA) controlled the movement of the microelectrode between the two preset positions (i.e. vibration amplitude) such that the excursion of the electrode was damped. Generally, the vibration amplitude is set at 30 µm for most experiments but can be shortened for smaller voltage gradients. The software also allows for the visual display of the voltage difference, which is calculated by measuring the microelectrode output at each extreme position of the vibration excursion (1000 data points/s), pooling these data into two separate buffers representing the two extremes of vibration, and then subtracting the averaged data of one buffer from the other. The sensitivity of the system permits the measurement of voltage differences in the microvolt range. These voltage gradients are translated into the ion-activity gradient by using the calibration curve of the microelectrode, which relates the voltage output of the microelectrode to specific ion activities in solution.

Selectivity Measurements

The second approach used the MPM (Gadzekpo and Christian, 1984; Umezawa et al., 1995), which is the method of choice for calculating selectivity coefficients when the electrode does not exhibit a Nernstian response to changes in interfering ion activity. This method involved adding a specific activity of the primary ion, Cd²⁺, to a reference solution already containing a defined Cd²⁺ activity and then measuring the millivolt output. In a separate test, interfering ions were added to an identical Cd²⁺ reference solution until the change in membrane potential matched the previous one obtained by adding primary ions (Cd²⁺) to the reference solution. The matched potential selectivity coefficient was then calculated from the ratio of the activity of the primary ion to that of the interfering ion: where I and J represent the interfering and primary ions, respectively, K^MPM_IJ is the selectivity coefficient, and a is the ion activity.

Ion Gradient Sources for Efficiency Determination

Measurement of Ion Fluxes

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For the transport studies, root seedlings were set in a plastic Petri dish containing 50 µm Ca(NO₃)₂ solution, and the primary root (for wheat [Triticum aestivum L. cv Grandin]) or a single root from the root system (for the two Thlaspi spp.) was anchored to the bottom of the dish with notched Plexiglas blocks that straddled the root and were attached to the dish bottom with silicone grease. For wheat, this solution was exchanged with a solution consisting of 50 µm Ca(NO₃)₂ plus 5 µm Cd(NO₃)₂ 10 min before starting the flux measurements. For Thlaspi caerulescens and Thlaspi arvense seedlings we found it necessary to allow the plant to be exposed overnight to the 50 µm Ca(NO₃)₂ plus 5 µm Cd(NO₃)₂ solution to detect significant Cd²⁺ fluxes. Flux measurements were carried out at different positions along the root. Microelectrodes were vibrated perpendicularly to the root with an amplitude of 30 µm such that the extremes of the vibration were between 30 and 60 µm from the root surface. Experiments were performed at 22°C ± 2°C. Ionic activities were calculated using the GEOCHEM PC program (Parker et al., 1995).

Plant Material

T. caerulescens and T. arvense seeds were placed in a drop of 0.7% (w/v) low-temperature-gelling agarose, which sat on nylon mesh circles (1-mm mesh openings) and, in turn, were positioned on a coarser mesh support covering a 5-L black plastic tub. The nylon mesh was covered with black polyethylene beads. Seeds were germinated for 5 d in the dark in deionized water. Subsequently, deionized water was replaced with a nutrient solution containing the following macronutrients (in mm): Ca, 0.8; K, 1.2; Mg, 0.2; NH₄, 0.1; NO₃, 2.0; PO₄, 0.1; and SO₄, 0.2; and micronutrients (in µm): BO₃, 12.5; Cl, 50; Cu, 0.5; Fe-N,N-ethylenebis(2-[2-hydroxyphenyl]-Gly), 10.0; MoO₄, 0.1; Mn, 1.0; Ni, 0.1; and Zn, 1.0. The solution was buffered at pH 5.5 with 1 mm Mes-Tris. Seedlings were grown in a growth chamber at 25/15°C (light:dark, 16:8 h) under a light intensity of 300 µmol photons m² s¹. Plants were grown for 2 to 3 weeks before being used for the flux studies. The length of the whole root system was about 5 to 10 cm.

	RESULTS

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Calibration of the Cd²⁺-Selective Microelectrode

View larger version (16K): [in this window] [in a new window]   Figure 1. Calibration curve for the Cd2+ microelectrode in Cd(NO3)2 solutions varying in activity. The electrode's output was arbitrarily defined as 0 for the reading taken when its Cd2+ activity was 784 µm, which corresponds to a 1 mm Cd(NO3)2 solution. The output of electrode potential (relative to the potential of the reference electrode) for the different calibration solutions was then referred to this 0 level. The solid line is the linear regression for the experimental points. The sensitivity (slope) is equal to 32 mV/dec (r2= 0.992). The dotted line represents the Cd2+ electrode's ideal Nernstian change in potential for an electrode that is selective only for Cd2+. ses are shown when they are bigger than the symbol. Data points represent the average responses of four different electrodes.

Because a defined Ca²⁺ activity in the uptake solution is required for normal root growth and function, we evaluated the Cd²⁺-electrode sensitivity with a constant Ca²⁺ background. The electrode response over a large range of Cd²⁺ activities with a constant Ca²⁺ background is shown in Figure 2. At the two Ca²⁺ background concentrations tested (50 and 200 µm Ca²⁺), the sensitivity of the electrode for Cd²⁺ (29 and 27 mV/dec, respectively), was close to that predicted theoretically (28.5 mV) by the Nernst equation. The electrode maintained a high Cd²⁺ sensitivity over a 10⁵-fold range of Cd²⁺ activities in the presence of 50 and 200 µm Ca²⁺. The electrode showed a linear Nernstian response down to Cd²⁺ activities as low as 1 µm. We also assessed the ability of the electrode to measure Cd²⁺ activities under conditions approximating the cell cytoplasm and vacuole, where the activities of potentially interfering background cations are high. Thus, we tested the sensitivity of the electrode in an artificial cytoplasm containing 100 mm K⁺ and 2 mm Mg²⁺. The sensitivity of the electrode under these conditions is shown in Figure 3. The slope of the calibration curve (29 mV/dec) is close to that predicted theoretically (28.5 mV/dec) by the Nernst equation. Thus, the electrode remains highly sensitive and selective for Cd²⁺ under conditions that mimic the plant cell cytoplasm. Below Cd²⁺ solution activities of 1 µm, the electrode response was still linear but exhibited sub-Nernstian behavior (19 mV/dec between 50 nm and 1 µm Cd²⁺ concentrations).

View larger version (15K): [in this window] [in a new window]   Figure 2. Calibration curves for the Cd2+ microelectrode in Cd(NO3)2 solutions containing either 200 µm Ca(SO4)2 (top) or 50 µm Ca(NO3)2 (bottom). The electrode response (in millivolts) was arbitrarily defined as 0, as described in Figure 1. The solid line in both cases is the linear regression for the experimental points. The sensitivity (slope) is equal to 29 mV/dec (r2= 0.995 excluding the lowest point) for the calibration in 200 µm Ca(SO4)2 and 27 mV/dec (r2 = 0.999) for the calibration in 50 µm Ca(NO3)2. ses are given if bigger than the symbol. Points represent, respectively, the averages of three and five different electrodes for the 200 µm Ca(SO4)2 (top) and 50 µm Ca(NO3)2 (bottom) background. The dashed line represents the theoretical change in potential for an electrode with ideal Cd2+ selectivity, as calculated by the Nernst equation.

View larger version (14K): [in this window] [in a new window]   Figure 3. Calibration curve for the Cd2+ microelectrode in Cd(NO3)2 solutions containing a background of 100 mm KNO3 and 2 mm Mg(NO3)2 (i.e. artificial cytoplasm). The electrode response (in millivolts) was arbitrarily defined as 0, as described in Figure 1. The solid line is the linear regression for the experimental points. The sensitivity (slope) is equal to 29 mV/dec (r2= 0.995 excluding the two lowest activity points). The dotted line represents the theoretically expected response for a Cd2+-selective microelectrode with an ideal Cd2+ selectivity, as calculated by the Nernst equation.

Ion Selectivity

Based on this lack of consistency in the SSM technique we adopted two approaches to assess the selectivity of the electrode. The first technique, the MPM, is prescribed for those electrode systems in which interfering ions and/or the primary ion do not satisfy Nernstian conditions (Umezawa et al., 1995). We used this technique because the lack of interference by K⁺ and Mg²⁺ in the "artificial cytoplasm" and the minimal interference by Ca²⁺ suggested that the Cd²⁺ microelectrode was insensitive to a number of potentially interfering cations, and thus, these cations would display non-Nernstian responses. Using this technique we were able to calculate selectivity coefficients only for Cu²⁺ (0.0465) and for Pb²⁺ (0.27) ions. These values indicate that the Cd²⁺ electrode is 21 and 4 times more selective for Cd²⁺ than for Cu²⁺ and Pb²⁺, respectively. Addition of any of the other interfering ions resulted in the reduction of the electrical output (data not shown). This reduction in potential could be accounted for by the dilution of the Cd²⁺ activity in the solution, suggesting that the interfering ions had no direct effect on the electrode.

A novel technique for measuring the Cd²⁺ electrode's true response to interfering cations, first proposed by Bakker (1996), was then used. The selectivity coefficients of the Cd²⁺ microelectrode obtained for eight divalent cations and for three monovalent cations using this technique are summarized in Table I. The convention for these selectivity coefficients is such that a log value of 0 indicates that the microelectrode cannot discriminate between the ion of interest, Cd²⁺, and an interfering ion. Values less than 0 indicate that the microelectrode preferentially responds to the ion of interest over the interfering ion. Again, these results show that the microelectrode was highly selective for Cd²⁺ over other cations. From the selectivity coefficients presented in Table I, the electrode is between 800 and 10¹² times more selective for Cd²⁺ over the other cations tested.

pH Effects on the Electrode

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View larger version (8K): [in this window] [in a new window]   Figure 4. Effect of pH on Cd2+ microelectrode performance. The pH of five different 50 µm Cd(NO3)2 solutions were adjusted over a range spanning from pH 4.0 to 8.0, using a series of buffers consisting of 10 mm Homopipes and 10 mm Tris added in the appropriate proportions to achieve the desired pH. The electrical output of the electrode was measured and then referenced to a 0 level, as described in Figure 1.

Efficiency Measurements

View larger version (26K): [in this window] [in a new window]   Figure 5. Theoretical () and experimental () measurements of a Cd2+ gradient as a function of distance from the artificial Cd2+ gradient source. Theoretical values were calculated according to the following equation: V = S([Ur]/[Cbr2 + Ur])/2.3, where V is the change in millivolts over the vibration excursion, S is the slope of the electrode, r is the distance from the source, r is the amplitude of vibration, Cb is the background activity of Cd2+, and U is an empirical constant. Experimental measurements were made by vibrating the electrode through a 10-µm amplitude at different distances from the Cd2+ source. Inset, Calculation of the empirical constant, U. Static measurements were made at a series of distances from the source and then the millivolt outputs were converted to activity values. A plot of these activity (C) values versus the inverse of the distance from the Cd2+ source (1/r) yields a line with a slope of U, according to the equation: C = Cb + U/r, where Cb is the background activity of Cd2+ (0.09 mm), and U (in micromoles per square centimeter) defines the diffusion characteristics of the gradient source (r2=0.992).

Measurement of Cd²⁺ Fluxes in Intact Root Systems

View larger version (19K): [in this window] [in a new window]   Figure 6. Diagram illustrating the Cd2+ flux profile along the longest seminal root of a 4-d-old wheat seedling. Flux measurements were carried out in 50 µm Ca(NO3)2 plus 5 µm Cd(NO3)2 at different positions along the root. The position and the magnitude of the fluxes are indicated by arrows, such that arrows directed toward the root indicate influx and arrows directed away from the root denote efflux. Scaling bars correspond to the distance along the root and the flux magnitude. Microelectrodes were vibrated perpendicularly to the root with an amplitude of 30 µm such that the extremes of the vibration were between 30 and 60 µm from the root surface.

View larger version (30K): [in this window] [in a new window]   Figure 7. Diagram illustrating the Cd2+ flux profile along a single root of the Zn/Cd hyperaccumulator T. caerulescens and the nonaccumulator T. arvense. Seedlings were exposed overnight to the 50 µm Ca(NO3)2 plus 5 µm Cd(NO3)2 solution. Flux measurements were carried out in 50 µm Ca(NO3)2 plus 5 µm Cd(NO3)2 at different positions along the root. The position and the magnitude of the fluxes are indicated by arrows, such that arrows directed toward the root indicate influx and arrows directed away from the root denote efflux. Scaling bars correspond to the distance along the root and the flux magnitude. Microelectrodes were vibrated perpendicularly to the root with an amplitude of 30 µm, such that the extremes of the vibration were between 30 and 60 µm from the root surface.

	DISCUSSION

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In the present work we have provided results that demonstrate the utility of an ion-selective Cd²⁺ microelectrode as a research tool to study heavy-metal transport in biological systems. To our knowledge, this is the first report of the use of Cd²⁺-selective microelectrodes for any biological application. The ionophore cocktail provides a highly sensitive Cd²⁺ electrode over a wide range of activities, with a Cd²⁺ detection limit (in simple Cd²⁺ solutions) below 1 µm (Fig. 1). Thus, the electrode remains highly sensitive to Cd²⁺ in the range of activities that are relevant to ion transport in plants growing on heavy-metal-contaminated soils (Brown et al., 1994; Jopony and Young, 1994).

Complications from potentially interfering cations were assessed using a variety of techniques and found to be minimal. The addition of Ca²⁺ to the experimental solutions had negligible effects on the response of the microelectrode (Fig. 2). Moreover, this electrode showed a high sensitivity when calibrated in an "artificial cytoplasm solution" (Fig. 3), despite the very high K⁺ and Mg²⁺ activities in the test medium. The slopes of the calibration curves obtained under different ionic conditions were Nernstian and indicate that this type of electrode system can be used to estimate intracellular Cd²⁺ activities. Furthermore, the electrode was shown to be pH insensitive (Fig. 4), further supporting its usefulness in intracellular and extracellular applications. Estimates of intracellular ion activities using ISEs, taking into account total ion interference, have been extensively reviewed (Steiner et al., 1979; Croxton and Armstrong, 1992). The development of this Cd²⁺ microelectrode will allow us to simultaneously monitor the uptake and accumulation of Cd²⁺ into plant roots, allowing for detailed studies into the mechanism and regulation of Cd²⁺ uptake into roots and other plant tissues.

A number of techniques were used to assess the electrode sensitivity for Cd²⁺ in the presence of other interfering cations. In the case of the MPM, we found that only Pb²⁺ and Cu²⁺ influenced the electrical output of the electrode. Other interfering ions tested had no direct effect on the electrode's output. It was possible to only crudely estimate the selectivity of the electrode for Cd²⁺ over other interfering cations using the MPM. From the data we can estimate that the electrode was between 250 and 500 times more selective for Cd²⁺ over other cations. The selectivity values calculated by the MPM are specific to the experimental conditions (Bakker, 1997a) imposed on the test solution. These MPM-selectivity coefficients should only serve as an indication of an ion's potential to be an interferent. We were able to calculate more general selectivity coefficients using the technique of Bakker (1996, 1997a, 1997b), which involved preconditioning the electrode in a solution containing the interfering cation prior to any Cd²⁺ exposure. The selectivity coefficients calculated using this technique confirm that there is minimal interference by any of the 11 divalent and monovalent cations tested (Table I). In fact, our Cd²⁺ microelectrode exhibited a greater Cd²⁺ selectivity than was previously reported when the ionophore was first synthesized (Schneider et al., 1980). This lack of interference is an important requirement for the measurement of Cd²⁺ fluxes along the root. If other cations interfere with the operation of the electrode and their fluxes are substantial, then the operation of the system and the ease of measurement would be compromised. In addition, the ability of the system to operate in the presence of other cations without interference allows for studies in which the competitive aspects of uptake can be assessed.

The vibrating microelectrode system provides the advantages of having a high degree of both spatial and temporal resolution. The system is capable of measuring very small Cd²⁺ gradients, as well as measuring fluxes at specific locations along the root. We were able to measure Cd²⁺ fluxes in both wheat and T. caerulescens and T. arvense roots. The flux profile observed along the roots had a distinct spatial organization, with a much higher Cd²⁺ influx in the few first millimeters back from the root apex and significantly smaller fluxes in the root zones behind this apical region. Similar flux profiles have been reported for Ca²⁺ and Mg²⁺ fluxes. Ryan et al. (1990) found no significant Ca²⁺ influxes beyond 3 mm back from the maize root apex. Huang et al. (1992a) found that Ca²⁺ influx measured 1 and 2 mm back from the root apex was 4 times larger than Ca²⁺ uptake measured farther back from the root apex, although the Ca²⁺ influx in the root cap and meristem region of wheat roots was smaller than the Ca²⁺ flux entering the root just behind this region. Grunes et al. (1993) found an identical spatial pattern for Mg²⁺ influx along wheat roots. Likewise, Ca²⁺ influx into Limnobium stoloniferum root hairs was found to be localized to the root hair apex (Jones et al., 1995). Our preliminary results indicate that there was no difference in either the magnitude or the spatial aspects of the Cd²⁺ flux profile among the two species of Thlaspi that we tested. This is despite the fact that these two species have been shown to vary in the tolerance and accumulation of both Cd²⁺ and Zn²⁺.

Previous studies (Vasquez et al., 1992; Brown et al., 1995) have demonstrated that T. caerulescens can accumulate significant levels of Cd in both roots and shoots. Perhaps differences between these two species would have been noted had the experiments been carried out over a much longer time. Cd²⁺ fluxes were not observed until the root system was exposed overnight to a solution containing Cd²⁺, suggesting that some type of transport "activation" is induced by the presence of the ion. Such observations encourage research characterizing Cd²⁺ fluxes from the two Thlaspi spp. grown under different nutrient regimens, as well as measuring intracellular Cd²⁺ activities in root and leaf cells. Investigators have also shown that Brassica juncea, a high-biomass crop plant, can accumulate substantial amounts of Cd in its shoots and roots (Salt et al., 1995). A comparison of Cd²⁺ uptake in the roots of the two Thlaspi spp. and of Brassica juncea would also be quite interesting. All of these studies are now possible given the development of a highly sensitive Cd²⁺-selective microelectrode. Indeed, it should be a useful tool to further our understanding of the physiology of heavy-metal uptake and accumulation in plants.

	FOOTNOTES

   Received July 15, 1997; accepted December 17, 1997.

	ABBREVIATIONS

Abbreviations: ISE, ion-selective microelectrode. MPM, matched potential method. mV/dec, millivolts per decade change in ion activity. SSM, separate solution method.

	ACKNOWLEDGMENTS

The authors would like to thank Dr. Eric Bakker (Auburn University, Auburn, AL) and Dr. Ernö Pretsch (Eidgenössiche Technische Hochschule, Zurich, Switzerland) for their invaluable assistance with the technical aspects of ionophore chemistry and selectivity.

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