Responses of hydroponically-grown chickpea to low phosphorus: pH changes, nutrient uptake rates, and root morphological changes Ghiath Alloush To cite this version: Ghiath Alloush. Responses of hydroponically-grown chickpea to low phosphorus: pH changes, nutrient uptake rates, and root morphological changes. Agronomie, EDP Sciences, 2003, 23 (2), pp.123-133. . HAL Id: hal-00886166 https://hal.archives-ouvertes.fr/hal-00886166 Submitted on 1 Jan 2003 HAL is a multi-disciplinary open access archive for the deposit and dissemination of scientific research documents, whether they are published or not. The documents may come from teaching and research institutions in France or abroad, or from public or private research centers. L’archive ouverte pluridisciplinaire HAL, est destinée au dépôt et à la diffusion de documents scientifiques de niveau recherche, publiés ou non, émanant des établissements d’enseignement et de recherche français ou étrangers, des laboratoires publics ou privés. 123 Agronomie 23 (2003) 123–133 © INRA, EDP Sciences, 2003 DOI: 10.1051/agro:2002077 Original article Responses of hydroponically-grown chickpea to low phosphorus: pH changes, nutrient uptake rates, and root morphological changes Ghiath A. ALLOUSH* Department of Soil Science and Land Reclamation, Faculty of Agriculture, Tishreen University, PO Box 1404, Lattakia, Syria (Received 21 January 2002; revised 8 April 2002; accepted 21 May 2002) Abstract – Plants grown in highly weathered or high alkaline soils often experience P stress, but never a P free environment. Thus, applications of mineral P fertilizers are often required to achieve maximum yield. Responses of different plant species or cultivars were the subject of numerous investigations in which P was withheld from the growth media. In this study, chickpea plants (Cicer arietinum L.) grown hydroponically in complete nutrient solution for 17 days (1 mM P) were then maintained at low-P supply for 14 days (0.01 mM). Measurements included dry matter (DM)1, production of shoots and roots, PEP carboxylase, organic acid anion (Org A–), and root morphological responses. Dry matter of shoots and roots were reduced equally in plants subjected to Low-P supply. The uptake rates of all mineral nutrients were reduced soon after low-P was imposed within 1–2 days for Ca2+, Mg2+, and SO42– and within 3–4 days in case of K+ and NO3–. High and low P plants continued to alkalize the nutrient solution, but the rate of OH– released from the roots was considerably reduced in low-P plants. Cumulative values of OH– released from the roots after low P treatment was imposed linearly correlated with the difference of anion–cation uptakes in highP (R2 = 0.9989) and in low-P plants (R2 = 0.9947). Physiological responses to low-P include an enhanced activity of PEPcase in shoots and to a greater extent in roots, which could explain the higher concentrations of Org A– in shoots and roots of low-P plants. Root image analyses showed an enhanced branching density in low-P plants resulting in shorter but slender roots than those in high-P plants. These responses could probably explain the greater inflow rates and SAcR rates of micronutrient cations (Zn, Cu, Mn, and Fe) into the shoots of P-limited plants. chickpea / phosphorus / stress / nutrient uptake / roots morphology Résumé – Réponses du pois chiche en culture hydroponique à une faible alimentation en phosphore : changement de pH, taux d’absorption des minéraux et modifications morphologiques des racines. Les plantes poussant sur des sols fortement altérés ou très alcalins souffrent souvent d’un déficit de phosphore (P), mais ne se trouvent jamais dans un environnement sans P. Les applications d’engrais minéraux phosphoriques sont donc souvent nécessaires pour obtenir un rendement maximum. Les réponses des diverses espèces ou variétés de plantes ont fait l’objet de nombreuses recherches dans lesquelles le P a été enlevé des milieux de culture. Dans cette étude, les plants de pois chiche (Cicer arietinum L.) cultivés hydroponiquement dans une solution nutritive complète pendant 17 jours (1 mM de P), furent ensuite maintenus avec une faible alimentation en P pendant 14 jours (0,01 mM). Les mesures comprenaient la matière sèche des parties aériennes et des racines, la carboxylase PEP, l’anion acide organique (Org A–), et les réponses morphologiques des racines. La matière sèche des parties aériennes et des racines fut réduite de manière égale pour les plantes carencées. Les taux de prélèvement de tous les minéraux furent réduits rapidement après l’imposition d’une faible alimentation en P, en 1–2 jours pour le Ca2+, le Mg2+ et le SO42– et en 3–4 jours dans le cas du K+ et du NO3–. Les plantes, cultivées avec un fort ou un faible taux de P, ont continué d’alcaliniser la solution nutritive, mais le taux de OH– relâché par les racines a été considérablement réduit pour les plantes carencées. Les valeurs cumulatives de OH– libérés par les racines après que les deux doses de P aient été imposées, sont corrélées linéairement avec la différence « anion–cation » absorbés dans les plantes pour la forte (R2 = 0,9989) et la faible (R2 = 0,9947) concentration en P. Les réponses physiologiques à une faible concentration en P comportent un accroissement d’activité de la carboxylase PEP dans les parties aériennes et dans une plus grande mesure dans les racines, ce qui peut expliquer les fortes concentrations de Org A– dans les parties aériennes et les racines des plantes carencées en P. Les analyses d’images de racines ont montré, de plus, un accroissement de la densité de ramification pour les plantes carencées en P, induisant des racines plus courtes et plus fines que celles des plantes non carencées. Ces réponses pourraient probablement expliquer les plus grands taux d’absorption et d’accumulation spécifique pour les macro et les micronutriments (Zn, Cu, Mn et Fe) dans les parties aériennes des plantes stressées. pois chiche / carence / phosphore / absorption racinaire / morphologie des racines Communicated by Gérard Guyot (Avignon, France) * Correspondence and reprints [email protected] 1 Abbreviations: DM, dry matter; RL, root length; PEPcase, phosphoenolpyruvate carboxylase; Org A–, organic acid anion; I, inflow rate; SAcR, specific accumulation rate. 124 G.A. Alloush 1. INTRODUCTION Plant acquisition of nutrients of low mobility, such as phosphorus, is often determined by their concentration in the soil. This is especially important in highly weathered or alkaline soils in which plants often experience P stress [24]. Annual application of P fertilizers may be required for plants to produce reasonable growth and yield. The ability of plants to acquire P from such soils is strongly influenced by root morphological and physiological properties [27]. Root morphology changes markedly in response to phosphorus deficiency. It has been demonstrated for many plant species (rape, bean, maize, buckwheat) that P-deficient plants have more extensive root systems, which are characterized by more rapid development, higher root/shoot ratios, and finer and longer roots, as well as more root hairs [3, 7, 9, 31]. These changes in the root structure under P-stress allowed more efficient acquisition of P, which was attributed to a greater ability to explore the soil, and hence improve P recovery [24]. Similarly, there are a number of functional changes in the roots that result from P deficiency, which also enhance the uptake of soil P. P-fixation in the soil [24]. Therefore, depending on soil management, soil type, and environmental factors, plants may experience low-P availability in the soil later in the growing season rather than absolutely P-free soil solution. In this study, non-nodulated chickpea plants were grown initially with high rate of P supply (1 mM P) to establish relatively sizable plants, and then subjected to low-P supply (0.01 mM P), rather than complete P-starvation [12, 14, 20, 25, 27]. The Rhizobium symbiosis with chickpea roots was intentionally avoided in this study as may alter root physiological and morphological responses [24]. The overall objectives were to investigate: (i) the extent of growth reduction and mineral nutrient uptakes due to low-P supply; (ii) the speed response to low-P stress in acidifying the growth media; (iii) the occurrence of root morphological changes; and (iv) chickpea physiological responses with special reference to activity of PEP carboxylase enzyme and subsequent accumulation of organic acids in plant tissues. 2. MATERIALS AND METHODS 2.1. Plant cultivation Evidence for acidification of the substrate has been observed for many plant species in response to P deficiency. Moorby et al. [25] demonstrated using rape plants (Brassica napus L.), that acidification was the results of net H+ excretion from the roots consequent to the shift in cation/anion uptake ratio, although the uptake of anion remained slightly higher than cation. Such acidification has also been observed (though NO3− was the main source of nitrogen supply) for chickpea plants (Cicer arietinum L.) grown in nutrient solution [20], and for tomato plants [12]. The supply of NO3−-N normally increases anion over cation uptake and nitrate may represent approximately 80% of the total anion uptake by tomato plants [18]. In all cases, the observed acidification of substrate by different plant species coincided with accumulation and/or release of organic acid anions [12, 20, 25, 27]. Hoffland et al. [15] concluded that acidification of the rhizosphere resulted from the release of organic acids, which was matched by an increase in activity of PEP carboxylase enzyme in rape plants. Organic acids also play an important role in plant physiology and maintain intercellular pH and electrochemical charge [19]. An enhanced activity of the enzyme PEP carboxylase was reported in several plant species subjected to P stress such as rape, tomato, and lupin [15, 16, 27]. Some other plant species, such as white clover and buckwheat, were shown to accumulate sufficient P during periods of high supply to maintain growth through times without adequate availability of P [3, 6]. However, conclusions regarding the importance of each of these P-deficiency response mechanisms have been contradictory. The complete nutrient solution (H-P) consisted of Ca(NO3)2, 1.5 mM; KH2PO4, 1.0 mM; and MgSO4, 0.5 mM. The L-P nutrient solution consisted of Ca(NO3)2, 1.5 mM; KH2PO4, 0.01 mM; MgSO4, 0.5 mM and K2SO4, 0.495 mM to compensate for K. The concentration of sulfate, an anion known to have little effect on the uptake of other macronutrients was thus varied in the two P nutrient solutions. To both nutrient solutions (Low and High P), micronutrients were supplied according to the Long Ashton formula [13]. The extent of these response mechanisms is probably important when plants are subjected to P-free growth substrates [12, 20, 25, 27]. It is most unlikely for plants growing in soils to experience absolute P-free environment and therefore, it is a matter of speculation on the extent appearance of these functional responses if plants do not experience absolute P starvation. The availability of P in the soil is mainly determined by the initial plant uptake and simultaneously occurring Every 24 hours at the beginning of each light cycle, the circulation pumps were stopped for 5 min to allow the used nutrient solutions to drain into the reservoir tanks, after which they were replaced with 10 L fresh low or high P solutions (pH = 6.0) according to treatments. At the beginning and end of each cycle, 50 ml samples from each tank were taken for mineral nutrient concentration analyses. The volumes of used nutrient solutions, and pH, were measured. Using 1-L of the Chickpea (Cicer arietinum L. cv. UC 27) seeds were surface sterilized (4 min in 10% sodium hypochlorite, with 5 drops of teepol followed by 5 rinses in deionized water) and germinated in a moist peat-perlite mixture. Eighty seedlings (0.74 ± 0.04 fresh wt.basis) were selected and transferred to plastic troughs, along which nutrient solution was circulated from reservoir tanks. Each trough supported 10 seedlings and each reservoir tank held 10 L of nutrient solution, which was fed into four troughs at a flow rate of 2 L·min−1. After a 7-day pre-culturing period, during which half-strength, complete nutrient solution was circulated, 2 seedlings from each trough were harvested to begin the experiment (t0). Plants in all troughs (8 in each trough) were subsequently supplied with full-strength, complete nutrient solutions for 13 days. One of two treatment regimes was then imposed: (1) in four troughs, 24 plants continued to receive the complete nutrient solution containing 1 mM P (H-P, high-P treatment), and (2) 24 plants were P-limited by reducing the P concentration in the nutrient solution to 0.01 mM P (L-P, low-P treatment). Responses of hydroponically-grown chickpea to low P used nutrient solutions, the pH was titrated back to the starting pH (6.0) using 0.5 mM HCl. The quantities of acid necessary to correct the pH of the nutrient solutions at each cycle were recorded and results expressed as rate (meq·plant−1 ·day−1) and cumulative OH− released (meq·plant−1) from the roots. 125 the PEP was followed in a spectrophotometer at 340 nm. Protein concentrations were determined by the methods of Bradford [5]. 2.3. Root digital image analyses 2.2. Procedure at harvest and measurements Four plants from each treatment, selected randomly, were harvested at 0, 9, 13, 17, 21, and 27 days. At each harvest, roots were cut from shoots and fresh weights were recorded. A known fresh weight from shoots and roots was taken for PEP carboxylase activity, and from roots for total root length (RL), determined using the RL scanner (Comair Model TM0001, Melbourne, Australia). The remaining fresh matter of shoots and roots were oven-dried at 70 °C for at least 48 h, and total dry matter (DM) of shoots and roots was then calculated. Shoots and roots were ground to pass a 0.5-mm screen and kept in sealed plastic bags for total and soluble mineral ion concentration determinations. Between 50−100 mg of plant samples were weighed into teflon containers, after which 1.0 mL of 15.8 M HNO3 was added. The samples were then digested using the microwave procedure [16]. Digested samples were brought to a final volume of 10.0 mL, filtered, and analysed for total mineral elements (P, S, K, Ca, Mg, and Na) using Inductive Couple Plasma (ICP, Jobin Yvon Model JY 46P ICP, Longjumeau, France). Total nitrogen contents in shoot and root tissues were determined by using a Carlo Erba analyzer (EA 1108 CHNSO, Milan, Italy). Soluble NO3− and Cl− were determined from hot water extracts using an ion chromatograph [2] with suppressed conductivity (Dionex DX 500 ion chromatography, AS 14 4 mm anion column and CS 14 4mm cation column). Alkalinity of the tissues [34] was determined by ashing subsamples (250–500 mg) in porcelain crucibles at 500 °C for 6 h. Samples were then allowed to cool and the ash dissolved in 10 mL of 1 M standardized HCl, followed by back titration to pH 7.0 using 1 M NaOH solution. The calculated difference in volume between the two standard solutions (acid–alkaline) represents the alkalinity of the ash and is taken as a good estimator of the organic acid content of the plant tissues. Xylem sap was collected from additional three plants from L-P and H-P treatments at day 27. Collection of sap was made over a period of 5 minutes from each plant using a pressure bomb (Soil Moisture Equipment Crop, USA) at 2–4 psi. Sap samples were analyzed for mineral nutrient concentrations using ICP for (P, S, K, Ca, and Mg) and using Dionex chromatography for anions (NO3−, Cl–, SO4−2, and H2PO4−). The extraction and assay of PEPcase was performed according to Marques et al. [23], and as modified by Schweizer and Erismann [32]. Desalted extracts of shoots and roots were incubated with PEP, malate dehydrogenase [EC1.1.1.37] and NADH, and the disappearance of NADH during the conversion to malate of oxalacetate formed from 2 Mention of trademark does not imply endorsement by USDA over comparable products. Two plants were taken from Low and High-P treatments at each harvest after P-stress was imposed (17, 21, and 27 days). Triplicates of basal roots were teased from the main root axes of each chickpea plant, arranged using a small paint brush in a glass tray partially filled with distilled water and placed on top of a light box (Aristo model DA-10, Rosyln NY, USA). A digital image of the entire root was recorded using a Dage 72S CCD (charge coupled device) camera (Dage-MTI Inc., Michigan City, IN, USA), fitted with a Minolta 50/1.7 lens. Image capture was controlled by a Power Macintosh 7200/ 120PC compatible computer equipped with an AG-5 frame grabber board (Scion Inc., Frederick, MD, USA) and NIHImage (version 1.60 adapted by Scion, Inc. from public domain software). In order to investigate the effects of P-stress on lateral root branching, density, length, branch root characteristics were recorded from a 12–15 cm region of the root where branches first appeared from the apical meristem. 2.4. Calculations and statistical analyses Uptake of macronutrient elements over a 24-h period was calculated from differences between concentrations at the start and end of each 24-h depletion cycle, multiplied by the volume of the solution in each trough system and reservoir tank. The results of these calculations give the uptake rates of nutrients (mg·plant−1 ·day−1), when divided by number of plants remaining in each trough system and tank. The sum of uptake rates yield the cumulative uptake of nutrient elements (mg·plant−1) and are average values and statistical analyses could not be performed. Inflow rates (I, µg nutrient·m−1 RL·d−1) for macro- and micro-nutrient elements were calculated, using the equation of Williams [35], between harvest dates 13 and 27 days. These values provide average accumulation rates over 14 days from the time P-stress was imposed. The inflow equation is: I = (N4-N1)/(T2-T1) × Ln(L4/L1)/(L4-L1) (1) where N4 and N1 are total macro- and micro-nutrient contents of plants, L4 and L1 are total root length, and T2 and T1 are time (d) for plants at harvest dates 27 and 13. Specific accumulation rates for macro- and micro-nutrient elements (SAcR, µg nutrient·g−1 DM·d−1) were calculated using also the equation of Williams [35], over the same period of time using mineral nutrient contents of shoots and shoots DM. Data for mineral nutrient contents of plants, PEPcase, organic acid contents, and root data (branching, density and length) were subjected to analysis of variance using the ANOVA procedures [29]. 126 G.A. Alloush thereafter pH values were similar in both L-P and H-P solutions. However, the rate of OH− released from the roots of L-P plants was smaller than that from H-P plants, the reduction being apparent 24-h after the initiation of P-stress. Cumulative amounts of OH− released by the roots were higher in H-P plants, compared to L-P plants (10.43 meq·plant−1 in H-P plants vs. 6.955 meq·plant−1 in L-P plants at day 27). Cumulative quantities of OH− released from the roots correlated linearly with differences between total anion-cation taken up by the plants (R2 = 0.9987 in H-P treatment and R2 = 0.9894 in L-P treatment), the slope, however, being greater in case of H-P plants (Fig. 4). Generally, the uptake of cation and anions correlated linearly irrespective of P nutritional status (Fig. 4). Figure 1. Shoot and root dry matter production of chickpea as influenced by high and low P supply. Bars are standard errors of means (n = 4). 3. RESULTS 3.1. Dry matter and nutrient uptakes Shoot and root growth was significantly reduced (P ≤ 0.01) after 8 days from the time P-stress was imposed at day 13 from the start of the experiment (Fig. 1). The reduction in shoot growth (23%) was similar to the reduction in root growth (22%), by the end of the experiment. The reduction in growth of shoots and roots was paralleled by the reduction in the uptake rates of NO3− and K (Fig. 2), which became apparent by day 18. Uptake rates of Ca and P were reduced right after the stress was imposed. The reduction of Mg and S uptake was not apparent until day 23 (10 days from initiating P-stress). Cumulative uptake rates of all nutrients were reduced in L-P plants (Fig. 2), the reduction being greater for P and Ca, compared to N, K, Mg, and S. Both H-P and L-P plants increased the pH of the nutrient solution (Fig. 3) throughout the entire length of the experiment. After P-stress was introduced at day 13, the pH of the nutrient solution in L-P plants was higher after 24-h by about 0.5 units, compared to the H-P nutrient solution. The higher pH in L-P solution remained until day 23, and Average inflow rates into roots (I, µg·m−1 RL·day−1) and specific accumulation rates into shoots (SAcR, µg·g−1 DM·day−1) of plants over the period of P-stress (between 13 and 27 days) are presented in Table I for macro- and micronutrients. The inflow rates of all macronutrients (N, P, S, K, Ca, and Mg) into the roots of L-P plants were reduced compared to H-P plants. P-stress reduced significantly (P < 0.05) anion inflow rates by 17, 26, and 27% for N, P, and S respectively, whereas the reductions in K and Mg inflow rates (6 and 10%) were not significant. Inflow of Ca was reduced by 47%, and to a lesser extent its translocation to the shoots as SAcR was reduced by 27%. Translocation of N, P, S, K into shoots showed similar pattern to inflow rates and Mg SAcR was not reduced. For B and Mo, inflow rates were reduced by P-stress by 10 and 22% with slightly lesser reduction in their SAcR values (13 and 17%). Mn and Fe inflows were reduced similarly (about 18%), but their translocation to the shoots was enhanced by 14 and 38%, whereas the inflows Zn and Cu were enhanced by 56 and 17% and to a lesser extent, their translocation to the shoots (17 and 13%, respectively). The mineral composition of xylem sap collected at day 27 is shown in Table II. Concentration of all macronutrient anions and cations in xylem sap was higher in H-P plants compared to L-P plants and the reverse was true for micronutrients. Irrespective of P nutritional status, total anion concentration exceeded cation, the excess negative charge being –9.3 for H-P plant sap vs. –3.1 for L-P plant sap. 3.2. Root morphology and characteristics Total root length (RL) was similar in low and high P treatments until 21 days and became significantly (P ≤ 0.05) smaller in L-P treatment at the last harvest, 14 days after lowP treatment was imposed (Fig. 5). However, the distribution of root branches between the different length categories was strikingly different (Fig. 6). Almost all the lateral root branches in the L-P root system fell in the 0–4 cm category. In H-P plants, lateral roots were longer, up to 28–32 cm. Such long lateral root branches were nonexistent in the L-P root system. The density of lateral root branching along the root system of L-P treatment was significantly greater (P ≤ 0.01) than in H-P treatment (Fig. 7). Branching density (number of Responses of hydroponically-grown chickpea to low P 127 Figure 2. Rate and cumulative uptake of macronutrient element uptake every 24-h in chickpea as influenced by high and low P supply. branches·cm−1 RL) in L-P root system was almost twice that of H-P root system. The overall average of lateral root branches was longer in H-P root system, compared to L-P, although average length decreased with time in both H-P and L-P root (Fig. 7). 3.3. PEPcase activity and organic acids The specific activity of PEP carboxylase (PEPcase) in shoots and roots is shown in Figure 8. Enzyme PEPcase activity, while decreasing with time towards the end of the 128 G.A. Alloush Figure 4. Correlation of OH– released from roots and (anion-cation) difference, and correlation between anion and cation uptakes by chickpea after low P treatment was imposed. Figure 3. pH values reached every 24-h in solutions, rate and cumulative OH– released by the roots of chickpea plants as influenced by high and low P supply. experiment, was 10-folds higher in roots than in shoots irrespective of P nutritional status. Both in shoots and in roots, PEPcase activity was significantly (P ≤ 0.01) enhanced by P-stress. The difference between L-P and H-P plants in PEPcase activity was higher in roots than shoots. Concentrations of organic acids in the roots decreased slightly with time but remained almost at constant concentrations in the shoots irrespective of P treatment (Fig. 9). Both shoots and Figure 5. Total root length of chickpea plants as influenced by high and low P supply. Bars are standard errors of means (n = 4). roots of L-P plants had significantly higher organic acid concentrations (P ≤ 0.01), compared to H-P plants during the 14 days of the treatment. Responses of hydroponically-grown chickpea to low P 129 Figure 6. Distribution of lateral root length of chickpea as influenced by high and low P supply. Note that the scale of L-P graph is three times greater than the scale of H-P graph. 4. DISCUSSION The acquisition of phosphorus by plant roots growing in soil depends on its concentration in the soil solution and on the buffering capacity of the soil to replenish the depleted soil solution with P due to absorption by plant roots [24]. The adsorption and subsequent fixation of P is high in acid and calcareous soils, so crops may experience P deficiency later in the growing season, even if P-fertilizers were applied before sowing. It is therefore unlikely for soil growing plants to experience P-free soil solution. Chickpea cultivated in the field is normally nodulated and fixes N2, leading to acidification of the rhizosphere, which increases the availability of P in the soil [20]. Under the condition of the present experiment, however, the growth of non-nodulated chickpea plants supplied with NO3-N was reduced after 8 days of low P supply (Fig. 1). The uptake of cations and anions were reduced (Fig. 2), the effect being greater on anions, compared to cations. However, anion uptake remained greater than cation so L-P plants continued to alkaline the nutrient solution, thus no acidification was observed (Fig. 3). In fact, pH values were higher in L-P, compared to H-P nutrient solution, although rates of OH− release were lower in L-P Figure 7. Lateral roots branching density and length of chickpea plants as influenced by high and low P supply. Bars are standard errors of means (n = 6). plants (Fig. 3). This is due the lower buffering capacity of the L-P nutrient solution, where a smaller quantity of OH– released shifted pH values higher than those recorded for H-P plants. The quantities of OH− released from the roots did not match the difference between anion minus cation although the two were linearly correlated (Fig. 4). The slope, however, in L-P treatment was lower than in H-P plants, indicating that the rate of OH− released was lesser than expected by the difference in anions minus cations. It is a matter of speculation whether organic anions were actively released from the roots of L-P plants and contributed to charge balance at the root plasma membrane. Measurement of organic acid anion was not performed in nutrient solutions and therefore, no firm conclusion could be drawn. However, the lower rate of OH− released from L-P roots coincided with greater concentrations 130 G.A. Alloush Figure 8. Activity of PEP carboxylase in leaves and roots of chickpea plants as influenced by high and low P supply. Bars are standard errors of means (n = 4). Figure 9. Concentration of organic acid anions estimated from the alkalinity of ash in shoots and roots of chickpea plants as influenced by high and low P supply. Bars are standard errors of means (n = 4). of organic acid anion in the shoots and roots (Fig. 9). It is likely that higher organic acid concentrations in the tissues resulted from the enhanced enzyme activity of PEPcase (Fig. 8). Accumulation of organic acids in chickpea plants was shown to accumulate in substantial quantities in shoot and root tissues even when no nutrient stresses were imposed [1]. Moreover, chickpea has been shown to excrete organic acid anions into the rhizosphere and their quantities were greater when plants were subjected to iron stress [1, 26]. However, for tomato plants, fed with NO3-N [27], PEPcase activity increases in the roots within 2 days of P withdrawal, by which time the rate of alkalization of the growth medium is already decreasing. By 8 days after withdrawal of P, PEPcase activity in the roots can be up to four times higher than in P-sufficient plants, and the growth medium is noticeably acidified by this time [27]. Certainly this was not the case with chickpea grown under condition of low P supply. The rate of OH− released was reduced within 24 h. Chickpea did not switch to acidification, or four-fold increase in PEPcase activity even after 14 days of P-stress (Figs. 2, 3, 8). Acidification of the P-free nutrient solution, even when supplied with NO3-N, was attributed to an excess cation over anion uptake [11, 20] or the release of organic acids (malic and citric) from the roots [10, 14]. Accumulation of organic acids in plant tissues arising from enhanced PEPcase activity provide the source of H+ ions for extrusion, as well as for a considerable internal anion charge, possibly acting as counter ion in cation uptake (thus depressing NO3− uptake) and transport from roots to shoots [21]. Calculations of inflow and SAcR rates (Tab. I) and analysis of xylem sap (Tab. II) support this hypothesis in which NO3− was considerably reduced compared to cations. Such organic acids may act as chelating agents in the soil, exchanging with bound phosphate, and thus rendering P available to plants [23]. Organic acids, such as citric and malic, have been seen to increase the availability and uptake of Fe and Mn in the soil by a chelation reaction facilitating their movement in the soil and across roots plasma membrane [24]. This mechanism may explain the enhanced uptake and translocation of micronutrient cations (Zn, Cu, Fe, Responses of hydroponically-grown chickpea to low P 131 Table I. Average inflow rates (I, mg/µg·m–1 RL·day–1) and specific accumulation rates (SAcR, mg/µg·g−1 DM·day−1) of macro- and micronutrients in chickpea plants over 14 days of Low-P stress (between harvest 3 and 5). Inflow rates of macronutrients (µg·m–1 RL·day−1) N P S K Ca Mg H-P 211 ± 8 31 ± 2 26 ± 2 182 ± 21 109 ± 36 19 ± 1 L-P 175 ± 18 23 ± 2 19 ± 3 170 ± 16 58 ± 7 17 ± 3 Specific accumulation rates of macronutrients (µg·g–1 DM·day–1) H-P 4763 ± 28 544 ± 33 341 ± 13 3100 ± 354 2367 ± 241 303 ± 32 L-P 3850 ± 354 412 ± 38 264 ± 29 2937 ± 157 1723 ± 228 316 ± 23 Inflow rates of micronutrients (µg·m–1 RL·day–1) Zn Cu Mn Fe B Mo H-P 0.16 ± 0.01 0.06 ± 0.01 2.83 ± 0.24 3.45 ± 0.24 0.29 ± 0.02 0.09 ± 0.01 L-P 0.25 ± 0.05 0.07 ± 0.01 2.33 ± 0.46 2.80 ± 0.07 0.26 ± 0.02 0.07 ± 0.01 Specific accumulation rates of micronutrients (µg·g–1 DM·day–1) H-P 3.24 ± 0.25 0.98 ± 0.06 21.70 ± 6.28 8.48 ± 1.11 8.14 ± 0.38 2.36 ± 0.30 L-P 3.80 ± 0.30 1.11 ± 0.06 24.73 ± 3.71 11.69 ± 1.55 7.04 ± 0.54 1.95 ± 0.19 ± is standard errors of mean. Table II. Mineral nutrient concentrations in the xylem sap of chickpea plant collected 14 days after the Low-P stress was imposed. Treatment Anions NO3– H2PO4 –† Cations SO4 2– † Total A ___________________________________ – K + Ca2+ Mg2+ Total C+ A-C meq·L–1 __________________________________ H-P 9.1 ± 2.7 2.4 ± 0.4 4.6 ± 1.1 16.1 18.8 ± 4.0 4.6 ± 1.3 2.0 ± 0.4 25.4 –9.3 L-P 3.8 ± 1.1 0.6 ± 0.1 1.4 ± 0.4 5.8 7.1 ± 1.6 1.2 ± 0.4 0.6 ± 0.1 8.9 –3.1 Micronutrients (mg·L–1) Zn Cu Mn Fe B Mo H-P 2.2 ± 0.7 2.1 ± 0.6 7.6 ± 1.6 5.8 ± 1.1 1.0 ± 0.5 0.2 ± 0.06 L-P 3.1 ± 0.5 3.2 ± 0.8 24.5 ± 5.0 18.0 ± 3.4 1.5 ± 0.2 0.3 ± 0.05 ± is standard errors of mean. † Calculated from total concentration of S and P, assuming all is in the form of SO42– and H2PO4–, respectively. 132 G.A. Alloush and Mn) into the shoots of chickpea (Tab. I). The higher rate of SAcR for micronutrient cation into the shoots of L-P chickpea, compared to H-P plants, was also confirmed by the higher concentrations of Zn, Cu, Fe, and Mn in the xylem sap collected from H-P and L-P plants (Tab. II). Chickpea has a restricted root system with fewer root hairs [33]. It consists primarily of the main apex and branching roots from the first and second degree lateral roots. Root mass and total length were slightly reduced under low P supply (Figs. 1, 5). However, morphological changes did occur under P-stress condition. Branching density was significantly increased in response to P-stress compared to P-sufficient plants (Fig. 7). Most of lateral root branches were shorter (0–4 cm), compared to lateral roots in H-P plants and increased in number as P-stress continues (Fig. 6). This enhanced branching and slandering may insure a greater root surface contact with soil, and thus enhancing the immobilization of P from soil deficient in P [4, 8]. Recently, Malinowski et al. [22], using the same root imaging technique, reported a decline in root diameter and increased root hair length in endophyte infected tall fescue in response to P deficiency, which may be one of responsible mechanisms for the mineral stress tolerance in tall fescue. The information about root morphological changes in P-deficient chickpea grown in the field and under different cropping system is lacking, and no conclusion could be made to the extent existence of these changes under field condition. There are however, indications to some environmental factor such as drought, temperature, and salinity to have the reverse effect of low-P supply on roots in which inhibits the development of root hairs [28]. If these root morphological changes occur in the field, they would enhance the acquisition of P and water. This is important as chickpea is mostly grown in poor semidry areas in which the availability of fertilizers is limited. Striking differences occur however, between chickpea genotypes that make screening for tolerance to nutritional and environmental stresses important [28]. These results suggest that chickpea plants respond to P-stress in a variety of ways. They reduce alkalinization/ acidification of the rhizosphere, accumulate organic acids in their tissues, and modify their root morphology. Modifications of the root system occur as increase in density of lateral root branching affecting surface area for mineral acquisition. Rootinduced changes in the rhizosphere along with the possible release of organic acids increase P mobility in the soil. In field conditions, chickpea is usually nodulated and acidification of the rhizosphere may occur which could increase P availability [24]. These responses to low P supply probably enable chickpea to mine P from sparingly soluble sources. 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