Open Access Article
Md. Abunasar
Miah
ac,
Yusei
Nakagawa
bd,
Ryo
Tanimoto
be,
Rina
Shinjo
b,
Motohiko
Kondo
b and
Hiroaki
Suzuki
*c
aDepartment of Biotechnology and Genetic Engineering, Faculty of Science, Noakhali Science and Technology University, Noakhali-3814, Bangladesh
bGraduate School of Bioagricultural Sciences, Nagoya University, Furo-cho, Chikusa-ku, Nagoya, Aichi 464-8601, Japan
cGraduate School of Pure and Applied Sciences, University of Tsukuba, 1-1-1 Tennodai, Tsukuba, Ibaraki 305-8573, Japan
dItochu Sugar Co., Ltd., Tamatsu-ura 3, Hekinan, Aichi 447-8506, Japan
eAichi Agricultural Research Center, Susogaeto 11, Inabu, Toyota, Aichi 441-2513, Japan
First published on 25th September 2019
Easily mass-producible needle-type Na+ and K+ ion-selective electrodes (ISEs) were developed for the direct and indirect measurement of Na+ and K+ ion concentrations in live plants. A polyimide strip with a silver layer on one side and Ag/AgCl formed at one end was used to construct two types of ISEs. For the type I ISE, an electrolyte layer was formed on the layer of silver and Ag/AgCl, which was then covered with a protecting layer. Subsequently, an ion-selective membrane (ISM) was formed at the truncated end with Ag/AgCl. For the type II ISE, a syringe needle was used as a container and an ISM was formed at the sharp end. Then, the polyimide strip with Ag/AgCl at one end was inserted and an electrolyte solution was injected to complete the ISE. Reference electrodes (REs) with similar structures were fabricated by forming a liquid junction instead of the ISM. The electrode responses and the relationship between the ISE potential and the Na+/K+ ion concentration agreed with those predicted by the Nernst equation. The Na+ and K+ ion concentrations in different parts of the rice plant (Oryza sativa L.) were measured using the Na+ and K+ ISEs, respectively. The results obtained using these devices agreed well with those obtained using inductively coupled plasma atomic emission spectrometry, thus confirming the practical applicability of the developed ISEs.
To overcome the issues associated with phenotypic field screening, the concentrations of ions have been used as indicators to identify salt-tolerant plants. In most cases, the Na+ and K+ ion concentrations in tissues have been used as indicators for plant breeders.6,7 In most species, Na+ ions are known to accumulate to toxic levels when the roots are exposed to high concentrations of NaCl. By contrast, excess K+ ions are known to suppress increases in the Na+ ion concentration.8 The amounts of Na+ and K+ ions in tissues such as leaves and roots have been measured using techniques such as atomic absorption spectroscopy,9 flame photometry,10 mass spectrometry,11 and inductively coupled plasma mass spectrometry.12 In addition, at the subcellular level, techniques such as X-ray microanalysis have been used.13 These methods are accurate and reliable, even for samples with low ion concentrations. However, these techniques require expensive instruments and cumbersome sample preparation procedures including grinding, ashing, extraction, and filtration using dangerous reagents, such as sulfuric acid, nitric acid, hydrogen chloride, or hydrogen peroxide.14 Therefore, rapid and easy techniques with simple sample preparation procedures are needed to measure ion concentrations in live plant tissues.
To meet these criteria, the ion-selective electrode (ISE) is an attractive device.15,16 ISEs allow ion concentrations to be determined based on the measurement of a potential difference generated at an ion-selective membrane (ISM). To measure ion concentrations in very small regions or small sample volumes, ISEs made with glass capillaries have been used, particularly for physiological research.17,18 However, special care is needed in handling these fragile structures. In addition, such ISEs are not suitable for mass production. To solve these problems, we applied techniques used for the microfabrication of semiconductor chips. Hundreds of thin polyimide strips with Ag/AgCl electrodes were easily mass-produced and then used to construct ISEs of two types. We also used this technique to fabricate needle-type reference electrodes (REs) that can be used in combination with the ISEs. Our technique not only realizes inexpensive disposable ISEs but also enables measurements in sample solutions with very small volumes or directly in plants. These ISEs were successfully applied to measure Na+ and K+ ion concentrations in rice plants.
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| Fig. 1 Structure of the type I ISE and RE: (a) top view, (b) cross section along the line x–x′, and (c) cross section along the z–z′ line. (d) Photograph of the polyimide strips with a silver layer. | ||
Fig. 2 shows the fabrication steps for the type I ISE. First, to improve the adhesion of silver to the substrate, the surface of a polyimide sheet (80 mm × 60 mm) was roughened by sandblasting and then cleaned by sonication. The sonication step was repeated three times, using fresh acetone every time. A 600 nm thick silver layer was sputter-deposited on one side of the sheet. A positive photoresist was coated on the silver layer for protection. Next, the polyimide sheet with a silver layer was cut into thin strips of 0.5 mm × 50 mm using a dicing machine, and the positive photoresist was removed using acetone. The silver layer on the strip was again coated with the positive photoresist, but both ends were left exposed. One exposed end (∼8 mm) was used to grow AgCl and the other (∼10 mm) was used as a contact pad. AgCl was grown by immersing the exposed end of silver in a 100 mM NaCl solution and applying a constant current (50 nA) for 10 min using a platinum counter electrode and a galvanostat (HA-151, Hokuto Denko, Japan).21
To form the electrolyte layer for type I Na+ ISEs, a 75 wt% PVP solution containing 100 mM NaCl was prepared. The strip with Ag/AgCl was immersed in the PVP solution and then removed immediately. The PVP layer was allowed to dry for 30 min. A 66 wt% PVC solution was then prepared in THF. The electrode with the PVP layer was immersed in the PVC solution, leaving part (∼3 mm) of the PVP layer exposed, and then the PVC layer was allowed to dry for 10 min. The end of the coated strip (∼2 mm) was then truncated using scissors. To form the ISM for type I Na+ ISEs, the truncated end was placed in contact with the PVC solution containing the Na+ ionophore and removed immediately. This step was repeated twice. The ISM was then allowed to dry for at least 24 h before the fabricated ISE was used for measurements. The type I K+ ISEs were fabricated in the same manner, except 100 mM KCl was used to prepare the PVP solution and the solution containing the K+ ionophore was used to form the ISM. The thickness of the ISM was approximately 90 μm.
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| Fig. 3 (a) Structure of the type II ISE and RE. The ISM or liquid junction was formed at the sharp end of the needle. (b) Photograph of the completed ISE. | ||
For the type I RE, the electrolyte layer was formed by dip coating using a solution containing 75 wt% PVP and 3.0 M KCl. The end of the polyimide strip with Ag/AgCl and the electrolyte layer was truncated using scissors. To form the liquid junction, 32.5 mg of poly(HEMA) was dissolved in 500 μL ethanol, and the solution was thoroughly stirred to mix well. The truncated end of the polyimide strip was placed in contact with this solution to seal the open end with a liquid junction. This step was repeated five times and then the membrane was allowed to dry for 24 h.
To fabricate the type II RE, a liquid junction was formed at the sharp end of the syringe needle before introducing the electrolyte solution. The sharp end of the syringe needle was placed in contact with the same poly(HEMA) solution as used for the type I RE. This step was repeated five times and the membrane was allowed to dry for 24 h. After the liquid junction was formed, a polyimide strip with Ag/AgCl was placed inside the syringe needle and a 3.0 M KCl solution was introduced into the interior of the type II RE by evacuation (Fig. S1†). In the KCl solution, a drop of AgNO3 solution was added to suppress the dissolution of AgCl.
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| Fig. 4 Experimental setup for measurements using the type II ISEs: (a) locations of the stem at which the ion concentrations were measured, and the ISE and RE inserted at (b) point A and (c) point B. | ||
000 rpm to remove any debris.
| A (mg kg−1) = a (mg L−1) × b (L kg−1) |
The measurements using the type I ISEs and the subsequent calculations were conducted in the same manner. First, calibration plots for the ISEs were obtained using Na+ or K+ standard solutions. Then, the sensitive area of the ISEs and the liquid junction of the corresponding REs were immersed in the extract solutions. The potential of the ISE with respect to the RE was measured using an electrometer (AutoLab PGSTAT12, Eco Chemie, Utrecht, Netherlands). The concentrations of sodium and potassium in the dry rice samples were then calculated as in the case of ICP-AES.
000 a and grown under low- and high-concentration Na+ and K+ conditions for 54 days. For the low-concentration Na+/K+ treatments, 2.5 mL of 200 mM NaCl/KCl solutions were added, whereas 12.5 mL of 200 mM NaCl/KCl solutions were added for the high-concentration Na+/K+ treatments. On the 10th day after the Na+/K+ treatment, the plant was removed carefully from the soil and immediately used for measurement after cleaning with water and wiping with tissue paper. The locations of the measurements and the experimental setup are shown in Fig. 4.
The measurements using the type II ISEs were conducted in the same manner. The ISEs were immersed in a 100 mM NaCl or KCl solution for 30 min for preconditioning prior to use. Then, the ISE and corresponding RE were inserted directly into point A or point B of the stem of an intact live rice plant (Fig. 4). The potential of the ISE was measured with respect to the RE, as described for the type I ISEs. The same ISE and RE were used for measurements until the ISM or liquid junction broke. The performance of the ISE and RE was checked in a standard solution after every 5th insertion into a plant. For statistical analysis, different rice plants were used, with each rice plant discarded after the measurement. The Na+ and K+ ion concentrations were calculated based on calibration plots constructed using NaCl and KCl standard solutions, respectively. The internal electrolyte solutions of the type II ISEs and REs were replenished with fresh solution prior to each measurement. All the experiments with type I and type II ISEs were conducted at 25 °C.
In the same manner, the type I and II K+ ISEs were characterized using KCl standard solutions with respect to the corresponding REs and a commercial Ag/AgCl electrode. Linear relationships were observed for both types of ISEs in the examined concentration range (Fig. 5c and d), and the potential shifted in the positive direction with the increase in K+ ion concentration. The slopes of the calibration plots for the type I K+ ISE with respect to the type I and commercial REs were +52.0 and +55.9 mV per decade, respectively. The slopes of the plots for the type II K+ ISE with respect to the type II and commercial REs were +51.1 and +50.4 mV per decade, respectively. These values were also slightly smaller than those expected based on the Nernst equation.
Fig. 6c and d show the Na+/K+ ion concentrations at points A and B of rice grown under low and high Na+/K+ concentrations, with the results obtained under normal conditions shown for comparison. Overall, the Na+ ion concentration was higher at point A than at point B. Moreover, the Na+ ion concentration at both points increased with the increase in Na+ ion concentration applied during growth (Fig. 6c). By contrast, the K+ ion concentration was higher at point B than at point A. However, as in the case of Na+ ions, the K+ ion concentration increased with the increase in the K+ ion concentration applied during growth. In addition, in all parts of the rice plant, the change with increasing ion concentration was larger for K+ ions than for Na+ ions. Similar tendencies have been reported for the Na+ and K+ ion contents of plants measured by atomic absorption spectroscopy,9 flame photometry,10 mass spectrometry,11 and inductively coupled plasma mass spectrometry.12Table 1 compares the results obtained using the type I Na+ and K+ ISEs with those obtained by the ICP-AES method. Overall, the values obtained using the two methods agreed well. It should be noted that the sample preparation procedure for the type I ISE measurements is much simpler and faster than that for ICP-AES measurements, although the ground parts of rice plants were used for both methods.
| Measured plant part | Treatment | Type I Na+ ISE × 105 (mg kg−1) | ICP-AES × 105 (mg kg−1) | Treatment | Type I K+ ISE × 105 (mg kg−1) | ICP-AES × 105 (mg kg−1) |
|---|---|---|---|---|---|---|
| Roots | Control | 0.037 | 0.025 | Control | 0.013 | 0.016 |
| High Na+ | 0.050 | 0.032 | High K+ | 0.046 | 0.129 | |
| Stem base | Control | 0.020 | 0.030 | Control | 0.027 | 0.022 |
| High Na+ | 0.050 | 0.044 | High K+ | 0.056 | 0.024 | |
| Stem | Control | 0.023 | 0.042 | Control | 0.108 | 0.100 |
| High Na+ | 0.066 | 0.042 | High K+ | 0.142 | 0.113 | |
| Green leaves | Control | 0.003 | 0.004 | Control | 0.094 | 0.108 |
| High Na+ | 0.009 | 0.005 | High K+ | 0.123 | 0.124 | |
| Dead leaves | Control | 0.012 | 0.007 | Control | 0.068 | 0.072 |
| High Na+ | 0.054 | 0.032 | High K+ | 0.085 | 0.091 |
Depending on the case, it may be better to measure the ion concentrations by inserting the ISEs directly into the plant part of interest. To this end, we used the type II ISEs, which were inserted into points A and B of 64 days old seedlings of rice plants (cv. Nipponbare) grown under low and high Na+/K+ ion concentrations. As shown in Fig. 7, the Na+ ion concentration was higher at point A than at point B, whereas the K+ ion concentration was higher at point B than at point A. Furthermore, the Na+ and K+ ion concentrations in these parts increased with the increase in the salt concentration in the root during growth. This tendency agrees with the results obtained using the type I ISEs (Fig. 6c and d). In addition, the Na+ ion concentration was higher than the K+ ion concentration at point A, whereas the opposite tendency was observed at point B, indicating K+, an essential element for plants, and Na+ exhibit different dynamics. Overall, the distributions of the ions measured using the type II ISEs were similar to those obtained using the type I ISEs and ICP-AES. These results also agree with those obtained previously by another group.26 Thus, the type II ISEs can be used for the direct measurement of ion concentrations and their localization in live intact rice plants.
In using the ISEs for real sample analyses, there are two points to be considered. One is the initial drift of the ISE potential after placing the ISM in contact with the internal and external solutions. The other is storage and user-friendliness. Because thin-film Ag/AgCl electrodes are easily damaged,27 the ISEs should be stored in a dry state until use. Furthermore, long preconditioning times are not beneficial and users should be able to use the ISEs immediately after preparation. To promote widespread use of the ISEs, further optimization will be needed to address these issues.
Footnote |
| † Electronic supplementary information (ESI) available. See DOI: 10.1039/c9ra05477d |
| This journal is © The Royal Society of Chemistry 2019 |