Verónica Castañeda1, Esther M González1. 1. Department of Sciences, Institute for Multidisciplinary Research in Applied Biology, Public University of Navarra, E-31006 Pamplona, Spain.
Abstract
Water-deficit stresses such as drought and salinity are the most important factors limiting crop productivity. Hence, understanding the plant responses to these stresses is key for the improvement of their tolerance and yield. In this study M. truncatula plants were subjected to 250 mM NaCl as well as reduced irrigation (No-W) and 250 g/L polyethylene glycol (PEG)-6000 to induce salinity and drought stress, respectively, provoking a drop to -1.7 MPa in leaf water potential. The whole plant physiology and metabolism was explored by characterizing the stress responses at root, phloem sap and leaf organ level. PEG treatment led to some typical responses of plants to drought stress, but in addition to PEG uptake, an important impairment of nutrient uptake and a different regulation of carbon metabolism could be observed compared to No-W plants. No-W plants showed an important redistribution of antioxidants and assimilates to the root tissue, with a distinctive increase in root proline degradation and alkaline invertase activity. On the contrary, salinity provoked an increase in leaf starch and isocitrate dehydrogenase activity, suggesting key roles in the plant response to this stress. Overall, results suggest higher protection of salt-stressed shoots and non-irrigated roots through different mechanisms, including the regulation of proline and carbon metabolism, while discarding PEG as safe mimicker of drought. This raises the need to understand the effect at the whole plant level of the different strategies employed to apply water-deficit stress.
n class="Disease">Water-deficit stresses such as drought and salinity are the most important factors limiting crop n class="Chemical">productivity. Hence, understanding the plant responses to these stresses is key for the improvement of their tolerance and yield. In this study M. truncatula plants were subjected to 250 mM NaCl as well as reduced irrigation (No-W) and 250 g/L polyethylene glycol (PEG)-6000 to induce salinity and drought stress, respectively, provoking a drop to -1.7 MPa in leaf water potential. The whole plant physiology and metabolism was explored by characterizing the stress responses at root, phloem sap and leaf organ level. PEG treatment led to some typical responses of plants to drought stress, but in addition to PEG uptake, an important impairment of nutrient uptake and a different regulation of carbon metabolism could be observed compared to No-W plants. No-W plants showed an important redistribution of antioxidants and assimilates to the root tissue, with a distinctive increase in root proline degradation and alkaline invertase activity. On the contrary, salinity provoked an increase in leaf starch and isocitrate dehydrogenase activity, suggesting key roles in the plant response to this stress. Overall, results suggest higher protection of salt-stressed shoots and non-irrigated roots through different mechanisms, including the regulation of proline and carbon metabolism, while discarding PEG as safe mimicker of drought. This raises the need to understand the effect at the whole plant level of the different strategies employed to apply water-deficit stress.
Entities:
Keywords:
PEG; Water stress; carbon metabolism; glutathione; ionome; phloem sap; proline; salt stress
Plant gron class="Chemical">wth, development and productivity are adversely affected by various abiotic stress factors, drought and soil salinity being the major problems, reducing crop productivity by more than 50% [1]. It is then of outmost importance to breed crops capable of tolerating or resisting these stresses without a significant impact on their yield. However, the knowledge about drought and salinity stress resistance is still limited, partly due to the complexity of the trait, involving important metabolic and physiological changes at the whole plant level. Water deficit can be defined as any water content of a tissue or cell below the highest water content exhibited in the most hydrated state. Hence, although the terms “drought stress” and “water-deficit stress” are usually employed indistinctively, water does not only become limiting for plant communities as a result of inadequate rainfall but also due to other environmental conditions like excessive salinity in the soil solution. Both drought and salinity cause osmotic stress by lowering the water potential of plant cells, which can lead to cell turgor loss, membrane disorganization, protein denaturation, inhibition of photosynthesis and oxidative damage, and thus both stresses share many plant responses [2]. However, in addition to the cellular water deficit provoked by the presence of salts, salinity stress also has an ionic component that further alters plant ion homeostasis through Na+ and Cl− toxicity.
Both n class="Disease">water-deficit stresses affect plant growth and development through changes in the plant biochemistry, physiology and morphology which have been investigated independently in many plant species, including Medicago truncatula [3,4]. Studies comparing different osmotic stresses are much less common, with a few done in some crop plants such as M. falcate [5] and rice [6]. In M. truncatula, Staudinger et al. observed significant differences in the degree and strategy of early drought, as compared to saltstress response, concluding that N-nutrition seems of crucial importance for plant stress acclimation [7]. However, more studies are needed in order to better understand the plant response to different water-deficit stresses. It is not surprising that no irrigation and salinity stress lead to a severe alteration of the carbon and nitrogen metabolism of the plant, which are the main providers of energy and nutrients of the plant [8] The coordination of carbon and nitrogen assimilation ensures the availability of amino acids and carbon skeletons, building blocks of biomass production and important compounds associated with increased water-stress tolerance, at the required amounts and moment [9]. However, despite their high relevance on plant growth and stress tolerance, their response to water-deficit stress is still not fully understood.
The transport of n class="Chemical">carbon and n class="Chemical">nitrogen assimilates occurs in the phloem, a part of the vascular system that connects all plant parts and directs the movement of these metabolites from their sites of synthesis (“sources”, such as mature leaves) to the sites of utilization or “sinks” (heterotrophic organs such as roots or growing leaves) [10]. The most accepted mechanism for phloem transport drive is explained by an osmotic pressure differential between the source and sink tissues. This implies that changes in the sink and/or source tissues such as those triggered by abiotic stresses can alter phloem transport and, hence, vital aspects such as growth, stress tolerance and reproduction [11,12]. Despite the crucial role of the phloem as essential metabolite transporter and its impact on plant–environment interactions, little research has been done on how its potential function alteration influences plant response to stress [13]. However, compelling studies suggest that the response of the phloem sap to stress conditions such as drought might predict plant survival and recovery capacity and can, in any case, help us better understand the response to stress at a whole-plant level [14]. To our knowledge and up to this date, only one study has been conducted in M. truncatula considering the phloem sap and its response to water-deficit stress [15]. In this proteomics study, Castañeda et al. described the existence of a core stress responsive proteome in M. truncatula across different tissues including the phloem sap, suggesting a major role of the phloem in stressprotection and antioxidant activity, especially by linking below and above ground communication in order to fine-tune stress response [15]. Other studies considering the phloem sap and different water-deficit stresses have been made in tomato [16,17], Plantago major [18], white clover [19], Ricinus communis [20], maize [21] and alfalfa [22].
Many authors have studied the effect of n class="Disease">water-deficit stress in leaves [23] or roots [24,25], but not many have simultaneously addressed the response in both organs [26,27], and even less at the whole-plant level including the phloem sap [15,19], even though the study of a plant as a whole can give us a unique and valuable information and understanding of its response to stress. We hypothesize that the impact of different osmotic treatments frequently applied to simulate water-deficit stress is markedly different at the whole-plant level. Here we assess the effect of different treatments (250 mM NaCl, 250 g/L polyethylene glycol (PEG)-6000 and reduced irrigation (No-W)) in roots, leaves and phloem sap of M. truncatula plants to better understand the response to different kinds of water-deficit mimickers. Overall, results suggest a higher protection of shoots in saltstressed plants while roots are the major responding organ under no-irrigation conditions. On the other hand, PEG caused an important impairment of nutrient uptake, which dismisses a confident use to mimic water-deficit stress.
2. Results
2.1. Physiological Measurements
n class="Chemical">NaCl, no-n class="Chemical">watering (No-W) and PEG-6000stresswere applied to provoke a drop in the leaf water potential similar to a moderate water-deficit level. Selected treatments were based on results of previous studies, in which the addition of 250 mM NaCl and 250 g/L PEG-6000 led to an average drop to Ψleaf −1.7 MPa after 7 days. Visually, salt-treated and No-W plants showed a vigorous and turgid appearance in the shoots, but some yellowing could be observed in the oldest leaves of salt-treated plants. On the other hand, PEG treated plants showed a less leafy appearance and a whitish discoloration in the leaves (Figure S1). Regarding plant biomass, the imposition of water-deficit stress did not significantly impact total, shoot or root dry biomasses except for a higher root/shoot ratio in No-W plants compared to the other treatments (Table 1).
Table 1
Physiological responses under different iso-osmotical conditions.
Control
NaCl
No-W
PEG-6000
Total biomass (g DW)
16.7 ± 0.7 a
15.6 ± 1.0 a
17.0 ± 1.4 a
14.8 ± 0.9 a
Shoot biomass (g DW)
8.8 ± 0.3 a
8.4 ± 0.5 a
8.2 ± 0.6 a
7.82 ± 0.7 a
Root biomass (g DW)
7.5 ± 0.4 a
7.3 ± 0.4 a
8.8 ± 0.8 a
7.0 ± 0.3 a
Root-to-shoot ratio
0.81 ± 0.03 b
0.88 ± 0.03 b
1.07 ± 0.02 a
0.92 ± 0.08 ab
Leaf water potential (MPa)
−0.50 ± 0.00 a
−1.67 ± 0.02 b
−1.68 ± 0.02 b
−1.68 ± 0.02 b
Stomatal conductance (cm s−1)
0.087 ± 0.005 a
0.021 ± 0.003 b
0.000 ± 0.000 c
0.000 ± 0.000 c
Transpiration (g H2O day−1 plant−1)
174.1 ± 4.7 a
69.2 ± 8.7 b
50.5 ± 6.9 b
50.2 ± 5.0 b
Chlorophyll content (SPAD units)
64.0 ± 0.5 a
63.2 ± 1.0 a
63.4 ± 0.9 a
58.8 ± 0.4 b
Leaf water content (%)
81.7 ± 0.4 a
80.4 ± 0.8 ab
77.9 ± 0.7 b
68.6 ± 1.2 c
Root water content (%)
82.5 ± 0.8 a
80.2 ± 1.9 a
65.2 ± 1.8 b
83.5 ± 1.6 a
Values represent the means ± SE (n = 5–10). Letters represent statistical differences (Tukey’s test, p < 0.05) between treatments. No-W, no irrigation.
Control plants exhibited a Ψleaf value of −0.50 ± 0.00 MPa, while the NaCl, PEG and No-Wstresses led to drops in the Ψleaf to an average value of −1.70 ± 0.02 MPa. The stomatal conductance was severely reduced under NaClstress, while this parameter reached values close to zero in No-W and PEG treated plants. Accordingly, transpiration rates were also markedly decreased under all stress treatments, with no significant differences among them. On the other hand, the chlorophyll content, measured in the second expanded leaf, decreased only slightly in the PEG treatment. It should be noted that no measurements were made in the oldest leaves. Leaf water content (WC) did not significantly decrease in neither salt nor No-W treatments, while dropping around 13.6% in the PEG treatment. Conversely, the No-Wstresswas the only treatment significantly reducing from 82.4% to around 65% the root water content (Table 1). On the other hand, the average PEG concentration measured in leaves and roots of PEG treated plants was 8.24 ± 1.33 and 152.88 ± 16.49 mg g dry weight (DW−1), respectively.
2.2. Carbon Metabolites
The concentration of n class="Chemical">starch and soluble n class="Chemical">sugars was differently affected by the stress treatments in the leaf, root and phloem sap of Medicago truncatula (Table 2). Under NaClstressstarch and sucrose accumulated markedly in leaves, being mostly unaffected or slightly modified in roots and phloem. However, in PEG-treated plants, starchwas fully depleted in leaves and significantly reduced in roots, whilesucrose accumulated markedly in leaves and roots without any change at phloem sap level. A significant decrease in starchwas observed in the No-W treated plants concomitant with a moderate accumulation of sucrose. Both salt and PEG treatments led to a depletion of glucose and fructose at root level, being unaffected at the leaf level. Conversely, No-W treatment showed a marked hexose increase in leaves and roots.
Table 2
Effect of the different water-stress treatments on the carbohydrate content.
Control
NaCl
No-W
PEG-6000
Leaves
Starch
147.2 ± 29.1 b
330.1 ± 24.0 a
60.4 ± 16.2 c
0.000 ± 0.000 c
Sucrose
11.5 ± 1.8 d
50.5 ± 4.9 b
25.6 ± 4.1 c
82.8 ± 16.6 ab
Glucose
4.3 ± 1.0 b
6.6 ± 2.4 b
21.2 ± 5.4 a
9.1 ± 2.1 ab
Fructose
6.1 ± 1.7 b
5.5 ± 1.5 b
15.5 ± 3.1 a
8.9 ± 2.2 ab
Phloem
Sucrose
17.8 ± 2.0 a
16.1 ± 3.8 a
18.0 ± 1.4 a
17.4 ± 1.6 a
Roots
Starch
10.4 ± 1.7 a
8.0 ± 2.1 ab
3.3 ± 0.4 b
6.0 ± 1.1 ab
Sucrose
16.1 ± 1.8 c
28.0 ± 2.3 b
43.2 ± 1.9 a
45.3 ± 4.3 a
Glucose
16.3 ± 2.6 b
4.3 ± 0.5 c
62.6 ± 9.8 a
8.2 ± 1.8 bc
Fructose
26.8 ± 5.3 b
4.1 ± 0.8 c
74.4 ± 12.7 a
7.0 ± 1.4 c
Leaves
Malate
4.62 ± 1.45 a
5.61 ± 1.17 a
4.76 ± 0.39 a
2.90 ± 0.17 a
Citrate
2.30 ± 0.93 ab
3.72 ± 0.65 a
1.04 ± 0.26 b
0.49 ± 0.05 b
Succinate
0.12 ± 0.02 a
0.12 ± 0.01 a
0.11 ± 0.01 a
0.080 ± 0.006 a
α-KG
0.040 ± 0.002 b
0.083 ± 0.006 a
0.031 ± 0.005 b
0.032 ± 0.002 b
Roots
Malate
1.21 ± 0.42 a
0.40 ± 0.06 a
1.51 ± 0.41 a
0.84 ± 0.09 a
Citrate
0.59 ± 0.07 a
0.46 ± 0.10 a
0.47 ± 0.03 a
0.32 ± 0.02 a
Succinate
0.095 ± 0.010 a
0.065 ± 0.005 ab
0.060 ± 0.008 b
0.55 ± 0.07 c
α-KG
0.027 ± 0.003 a
0.012 ± 0.001 b
0.035 ± 0.002 a
0.030 ± 0.004 a
Effect of different treatments on the starch (measured as glucose units released after starch enzymatic breakdown) and various soluble sugars and organic acids (in µmol g dry weight (DW)−1) in leaf, root and phloem sap of M. truncatula plants. Values represent the means ± SE (n = 5). Letters represent statistical differences (Tukey’s test, p < 0.05) between treatments. α-KG, α-ketoglutarate; No-W, no-watering.
Regarding n class="Chemical">organic acids, n class="Chemical">malate and citratewere more abundant than succinate and α-ketoglutarate (α-KG), both in leaves and roots. NaClstress significantly affected malate, citrate and succinate content in leaves, whileprovoking an overall decrease in the malate content on the root tissue. In salt-stressed plants, the α-KG level also decreased in the root tissue, whilst it accumulated significantly in leaves. No-Wstress had a minor impact on organic acids: the more abundant organic acids, malate and citrate, were not significantly affected in either leaves or roots, while α-KG increased slightly in the latter. PEG treatment led to a decline in citrate and succinate levels in the shoots, while a significant decrease in citratewas observed in roots togetherwith an up to six-fold accumulation of succinate levels (Table 2).
2.3. Nitrogen Status
The soluble n class="Chemical">protein content (Table 3) was not significantly affected by any treatment in leaves while it showed a decreasing trend in roots. A significant increase in total free amino acid concentration was found in leaves and roots of the PEG and No-W treatments whilst this parameter was not significantly affected by salinity (Table 3). The amino acid content of the phloem sap exhibited a marked increase in NaCl and PEG treatments. Although the No-W treatment significantly altered the total amino acid concentration of leaves and, above all, roots, it did not show any changes at phloem level. Proline (Pro) accumulated in all the treatments and organs, including the phloem sap. In NaCl-treated plants, Pro increased around 14-fold in leaves and roots with a remarkable accumulation at the phloem level (24-fold). Pro accumulation was much less marked in the leaves of No-W treated plants, while the highest increase (29-fold) was observed at the root level. PEGprovoked a similar Pro accumulation in leaves and roots (30-fold) with a more moderate increase at the phloem level. Complete data of individual amino acids are shown in Table S1. In general, the concentration of leaf amino acids, except for Pro, was not markedly affected by any stress, the leaves of No-W treated plants being the most affected tissue. No-W also showed the most altered root amino acid content, even though PEG showed an important alteration too, including the accumulation of the branched-chain amino acids (BCAA) Leu, Ile and Val. Conversely, the higher phloem sap alteration occurred under saltstress, where Pro, GABA, Ser, Gln and Ala showed significant increments and Val declined.
Table 3
Effect of the different water-stress treatments on the soluble protein and amino acid content.
Control
NaCl
No-W
PEG-6000
Leaf soluble protein
150.3 ± 6.5 a
137.7 ± 4.5 a
140.4 ± 12.7 a
152.1 ± 15.9 a
Root soluble protein
27.8 ± 1.1 a
24.8 ± 1.4 ab
22.7 ± 1.2 ab
21.2 ± 1.6 b
Leaves
Pro
1.9 ± 0.1 d
24.4 ± 0.8 (13) b
16.1 ± 0.8 (9) c
56.7 ± 5.4 (30) a
aa
85.2 ± 12.7 b
97.6 ± 14.8 b
118.6 ± 8.1 b
136.9 ± 8.5 (2) a
Phloem
Pro
0.17 ± 0.03 c
4.09 ± 0.68 (24) a
1.27 ± 0.13 (8) b
2.20 ± 0.48 (13) ab
aa
8.8 ± 1.1 c
17.7 ± 1.7 (2) a
10.4 ± 0.7 b
17.6 ± 2.8 (2) a
Roots
Pro
0.47 ± 0.07 c
6.86 ± 1.20 (14) b
13.56 ± 0.92 (29) a
14.25 ± 1.21 (30) a
aa
23.5 ± 4.3 c
30.3 ± 5.2 bc
78.0 ± 3.2 (3) a
63.1 ± 11.4 (3) ab
Response of M. truncatula leaves, phloem sap and roots to NaCl, no-watering (No-W) and polyethylene glycol (PEG) treatments regarding soluble protein (as mg g DW−1) and total soluble amino acid content (µmol g DW−1). Values represent the means ± SE (n = 5), while numbers in brackets represent the fold change of each treatment compared to control conditions when statistically significant according to t-Student’s test (p < 0.05). Letters represent statistical differences (Tukey’s test, p < 0.05) between treatments. aa, Total amino acids; Pro, Proline.
2.4. Inorganic Ions
Figure 1A,B shon class="Chemical">w the treatment:control fold change for each ion in leaves and roots in response to the different treatments. n class="Chemical">NaCl stressprovoked a marked accumulation of both ions in leaves and roots, Na+ being preferentially accumulated in leaves and Cl− in roots. However, irrigation with NaCl also lead to a decrease in K+, Mg2+, Ca2+ and SO42− levels in the roots. PEGprovoked an ion alteration mostly at the root level, leading to a decline in the Na+, K+, Mg2+, Ca2+ and SO42− concentrations. Lastly, No-W did not significantly modify the inorganic ions levels in any tissue, and only NO3− and SO42− exhibited a significant accumulation in roots. The absolute ion content under all stresses and both leaves and roots can be found in Table S2. In addition to the already stated changes in the ionic content, a remarkable increase in total ion content could be observed in both tissues in response to salinity stress, while the total ion content was decreased under PEG-6000.
Figure 1
Representation of the inorganic ion content response to water-deficit stress. Bars represent the means (n = 5) of the treatment/control ratios fold change in leaves (A) and roots (B). Asterisks represent statistical differences (Student’s t-test, p < 0.05) between control and treatments. No-W, no-watering.
2.5. Antioxidant Content
n class="Chemical">Ascorbate, n class="Chemical">glutathione and homoglutathione total contents in the different tissues and treatments are shown in Table 4, while complete data including their respective reduced and oxidized forms can be found in Table S3. The antioxidant metabolites’ concentration in the phloem sapwas below the detection limit of our analytical system (5 ppm). Saltstress did not significantly modify the total glutathione or homoglutathione pools but provoked a significant decrease in the total ascorbate pool. Similarly, in leaves of No-W treated plants, total glutathione and homoglutathione levels were maintained stable but the ascorbate pool decreased significantly, although less than under salinity. Conversely, in roots, total glutathione and homoglutathione significantly increased concomitantly with the decrease in the ascorbate pool. PEGprovoked an overall decrease in the ascorbate pool in leaves and roots, while the glutathione and homoglutathione pools remained unaffected. Since the total ascorbate level was near the detection level of our analytical method in the root tissue, it was not possible to discern between both antioxidant forms in this tissue in those treatments provoking a decrease in the ascorbate pool such as No-W or PEG, and this metabolite could then only be measured as the whole pool. Regarding the ratio reduced form/total pool for each metabolite, the ascorbate and glutathione ratios in leaves showed a decreasing trend, while the reduced homoglutathione/total homoglutathione ratio showed an increasing trend in response to all treatments. Conversely, in roots, the glutathione ratio showed a decreasing trend, while the homoglutathione ratio remained unaffected under all conditions.
Table 4
Effect of the different water-stress treatments on the antioxidant composition of M. truncatula. As well as their reduced/total antioxidant content ratios in leaves and roots under control, NaCl, no watering (No-W) and PEG-6000 treatments.
Control
NaCl
No-W
PEG
Leaves
Total Asc
3.41 ± 0.09 a
2.43 ± 0.08 b
3.00 ± 0.11 a
2.38 ± 0.11 b
ASC/Total Asc
0.79 ± 0.06 a
0.74 ± 0.03 a
0.69 ± 0.02 a
0.63 ± 0.02 a
Total Glut
0.70 ± 0.13 a
0.54 ± 0.03 a
0.67 ± 0.12 a
0.75 ± 0.07 a
GSH/Total Glut
0.52 ± 0.03 a
0.44 ± 0.04 a
0.47 ± 0.01 a
0.30 ± 0.02 b
Total hGlut
0.29 ± 0.03 a
0.31 ± 0.04 a
0.27 ± 0.06 a
0.18 ± 0.00 a
hGSH/Total hGlut
0.44 ± 0.04 a
0.66 ± 0.07 a
0.51 ± 0.06 a
0.62 ± 0.08 a
Roots
Total Asc
0.58 ± 0.01 a
0.36 ± 0.05 b
0.23 ± 0.02 c
0.25 ± 0.03 bc
ASC/Total Asc
0.36 ± 0.05 a
0.39 ± 0.01 a
n.d.
n.d.
Total Glut
0.19 ± 0.02 b
0.17 ± 0.02 b
0.45 ± 0.04 a
0.21 ± 0.08 b
GSH/Total Glut
0.65 ± 0.09 a
0.39 ± 0.04 a
0.36 ± 0.09 a
0.38 ± 0.09 a
Total hGlut
0.52 ± 0.11 b
0.28 ± 0.03 b
1.23 ± 0.23 a
0.32 ± 0.06 b
hGSH/Total hGlut
0.36 ± 0.06 a
0.42 ± 0.06 a
0.32 ± 0.04 a
0.38 ± 0.07 a
Values represent the means ± SE (n = 5). Letters represent statistical differences (Tukey’s test, p ≤ 0.05) between treatments. No reduced nor oxidized ascorbate data could be measured in the root tissue. Asc, ascorbate; ASC, reduced ascorbate; Glut, glutathione; GSH, reduced glutathione; hGlut, homoglutathione; hGSH, reduced homoglutathione; n.d., not detected.
2.6. Carbon and Nitrogen Enzymatic Activities
Several enzymatic activities related to the n class="Chemical">carbon [alkaline invertase (alkINV), n class="Chemical">glucose-6-phosphate dehydrogenase (G6PDH), isocitrate dehydrogenase (IDH), sucrose synthase (SuSy)], nitrogen metabolism [aspartate aminotransferase (AAT), glutamate dehydrogenase (GDH), glutamate synthase (GOGAT) and glutamine synthase (GS)] and proline [ornithine aminotransferase (OAT), Δ1-1-pyrroline-5-carboxylate synthase (P5CS) and proline dehydrogenase (ProDH)] metabolism were measured in leaves and roots of M. truncatula (Table 5).
Table 5
Effect of the different water-stress treatments on several enzymatic activities.
Control
NaCl
No-W
PEG-6000
Leaves
G6PDH
0.12 ± 0.01 a
0.12 ± 0.02 a
0.18 ± 0.03 a
0.11 ± 0.03 a
IDH
1.67 ± 0.10 b
2.38 ± 0.18 a
2.06 ± 0.31 ab
1.86 ± 0.14 ab
Roots
AlkINV
2.7 ± 0.2 ab
2.1 ± 0.5 b
3.7 ± 0.2 a
1.6 ± 0.4 b
G6PDH
4.2 ± 0.1 b
6.1 ± 0.5 a
2.7 ± 0.1 b
2.6 ± 0.6 b
IDH
7.6 ± 0.7 a
7.6 ± 0.6 a
6.3 ± 0.4 a
7.3 ± 1.2 a
SuSy
2.7 ± 0.2 a
1.3 ± 0.3 b
1.0 ± 0.4 b
1.2 ± 0.5 ab
Leaves
AAT
3.3 ± 0.3 a
3.1 ± 0.4 a
3.2 ± 0.2 a
3.8 ± 0.3 a
GDH
0.82 ± 0.06 a
0.83 ± 0.11 a
0.80 ± 0.04 a
0.85 ± 0.08 a
GOGAT
0.063 ± 0.005 a
0.068 ± 0.014 a
0.040 ± 0.006 a
0.053 ± 0.009 a
GS
0.027 ± 0.000 a
0.027 ± 0.001 a
0.030 ± 0.001 a
0.028 ± 0.003 a
Roots
AAT
15.1 ± 0.3 a
9.6 ± 1.3 b
7.7 ± 1.4 b
9.2 ± 1.2 b
GDH
11.8 ± 1.5 a
16.8 ± 2.5 a
11.7 ± 1.6 a
13.0 ± 1.8 a
GOGAT
0.25 ± 0.05 a
0.29 ± 0.06 a
0.20 ± 0.04 a
0.17 ± 0.03 a
Leaves
OAT
0.34 ± 0.04 a
0.55 ± 0.10 a
0.42 ± 0.03 a
0.15 ± 0.01 b
P5CS
0.41 ± 0.03 b
0.59 ± 0.05 a
0.45 ± 0.03 ab
0.44 ± 0.02 ab
ProDH
0.26 ± 0.03 a
0.17 ± 0.02 a
0.20 ± 0.01 a
0.24 ± 0.02 a
Roots
OAT
1.6 ± 0.1 b
2.6 ± 0.2 a
2.2 ± 0.1 ab
2.5 ± 0.2 a
P5CS
0.64 ± 0.06 c
0.78 ± 0.09 bc
1.04 ± 0.09 ab
1.16 ± 0.05 a
ProDH
0.52 ± 0.03 b
0.59 ± 0.03 b
0.91 ± 0.09 a
0.91 ± 0.05 a
Enzymatic activities of various carbon [alkaline invertase (alkINV), glucose-6-phosphate dehydrogenase (G6PDH), isocitrate dehydrogenase (IDH) and sucrose synthase (SuSy)], nitrogen [aspartate aminotransferase (AAT), glutamate dehydrogenase (GDH), glutamate synthase (GOGAT) and glutamine synthase (GS)] and proline metabolism [ornithine aminotransferase (OAT), Δ1-1-pyrroline-5-carboxylate synthase (P5CS) and proline dehydrogenase (ProDH)] (as nmol NADH min−1 µg prot−1) under control, NaCl, no-irrigation (No-W) and PEG stress in leaves and roots. Values represent the means ± SE (n = 5–10). Letters represent statistical differences (Tukey’s test, p < 0.05) between treatments.
Overall, the measured n class="Chemical">carbon and n class="Chemical">nitrogen-related enzyme activities were not significantly affected in leaves, except for an increase in the IDH activity under salinity stress. On the contrary, the root tissue showed a generalized response at enzymatic activity level: AAT and SuSy activities showed a general down-regulation in all treatments. Conversely, alkINV showed a significant enhancement in the No-W treatment while it decreased in the PEG-treated roots. Root GOGAT, GDH and IDH activities did not significantly change in response to any treatment.
n class="Chemical">Proline synthesis-related P5CS and OAT enzymes increased significantly in leaves and roots of n class="Chemical">salt-stressed plants, while the proline-degrading ProDHwas slightly inhibited in the leaves (Table 5). However, in leaves of No-W treated plants proline metabolism was not affected while the three enzymatic activities increased significantly in roots. This Pro metabolism activation occurred also in roots of PEG-treated plants, while OAT was negatively affected in leaves.
2.7. Principal Component Analysis
A Principal Component Analysis (PCA) was performed with all measured parameters in order to further confirm the differences between the treatments. All treatments were compared in Figure S2, in which a clear differentiation between samples, above all between control and drought treatments, could be observed. Indeed, No-W- and PEG-treated plants showed different scores along the first PC axis (Figure 2A), with the variables with the most weight responsible for the separation of both treatments being leaf starch, root fructose and glucose contents, root succinate, root Na+, Ca2+, Mg2+, NO3−, SO42− and total ion contents, as well as root oxidized, reduced and total homoglutathione, root reduced glutathione and leaf proline contents (Figure 2B). A very obvious sample separation occurred when NaCl and No-W treated plants were analyzed (Figure 3A), with the most responsible variables being leaf stomatal conductance, root fructose and glucose contents, leaf and root Na+ and Cl− contents, leaf starch and citrate, root SO42−, NO3− and Ca2+ contents, root Ile and root oxidized and total homoglutathione contents (Figure 3B). The statistical significance of the cited parameters was further acknowledged by Student’s t-test (p < 0.05), while the complete list of loading values for each PCA is shown in Table S4. All measurements in performed in this study and used for the PCA analyses can be found in Table S5.
Figure 2
Principal Component Analysis (PCA) conducted with all measured parameters in No-W and PEG-6000 treated plants. (A) PCA scores plot showing the non-irrigated (No-W) and PEG-6000 cases. (B) Loading values of all variables in PC1 separating both treatments. GSH, reduced glutathione; hGlut, homoglutathione; hGSH, reduced homoglutathione; hGSSG, oxidized homoglutathione; L, leaves; R, roots. Bar key: yellow, carbohydrates; blue, inorganic ions; pink, antioxidants; red, amino acids.
Figure 3
Principal Component Analysis conducted with all measured parameters in NaCl and No-W treated plants. (A) PCA plot showing the NaCl and non-irrigated (No-W) cases. (B) Loading values of all variables in PC1 separating both treatments. gs, stomatal conductance; hGlut, homoglutathione; hGSSG, oxidized homoglutathione; L, leaves; R, roots. Bar key: green, physiological measurements; yellow, carbohydrates; blue, inorganic ions; pink, antioxidants; red, amino acids.
3. Discussion
3.1. PEG: A False Mimetic of Drought
n class="Chemical">PEG is a n class="Chemical">polymer widely employed to mimic drought stress. One of the advantages of using this osmotic agent versus water-deficit imposition through withholding irrigation is the possibility to adjust precisely the stress level in the hydroponic solution, yielding a more uniform and controlled stress [28]. However, even though PEG-6000 molecules are usually described as too large to be taken up by intact roots, several studies have observed PEG uptake by both leaves and roots [29,30,31,32]. This, togetherwith the hypoxic nature of the highly-viscous PEG solution, can lead to additional stresses in plants subjected to PEG irrigation [33].
For this study, n class="Chemical">PEG treated plants exhibiting a Ψleaf ≈ −1.7 MPa were selected in order to perform a comparative analysis with No-W treated plants at an equal level of water-deficit stress. In this context, we found some common physiological and metabolic responses such as the reduced transpiration and stomatal conductance (Table 1) and root soluble protein content, as well as the general amino acid accumulation, particularly proline (Table 3). These responses are in agreement with previous studies with plants subjected to drought stress as part of their drought stress response [34]. However, PEG treated plants’ water content behaved in a completely opposite way compared to No-W treated plants, with a lower leaf and higher root water content under PEG (Table 1). This is in agreement with Fan and Blake, who observed a higher decline in leaf RWC of 5-month-old seedlings of jack pine, black spruce and flooded gum treated with PEG compared to those subjected to no irrigation [35]. This could be a sign of PEG uptake and/or hypoxia, which have been reported to disturb leaf water relations by blocking the water conducting channels and possibly exert a toxic response [31,33,35,36].
One of the most divergent aspects differentiating no irrigation and n class="Chemical">PEG treatment was the carbohydrate content (Table 2, Figure 2). Indeed, even though starch depletion has been a long time described phenomenon under drought stress that serves as energy and carbon supply when photosynthesis may be limited [37], its decline was more dramatic under PEG conditions. In addition, sucrose accumulation was especially remarkable in leaves of PEG-treated plants, whilehexoses concentration only increased in No-W leaves (Table 2, Figure 2). This increase in leaf soluble sugars has been described as a common behavior in drought-stressed plants due to their role in osmoregulation, amongst others [34]. Darko et al. also reported a different pattern of soluble sugars accumulation in leaves and roots of wheat seedlings depending on the studied stress even under iso-osmotic conditions [38], which could have a role in the signaling process of the regulation of plant metabolism and developmental processes [38,39,40].
n class="Chemical">Proline accumulation is another drought n class="Disease">stress response that is observed early in the onset of osmotic stress [34]. In our study, both PEG and No-W treated plants showed a marked increase in this compatible solute, with a much higher accumulation in PEG treated leaves and phloem sap (Table 3, Figure 2). Cui et al. observed a similar accumulation of proline under soil drought and PEGstress consistent with the increases in the content of key enzymes involved in proline metabolism [40]. However, like in our study, a differential activation of proline metabolism-related enzymes was observed (Table 5), suggesting that PEG and No-W affect carbon and proline metabolism through different mechanisms.
An additional and very marked difference between both n class="Chemical">water-deficit treatments was the depletion of inorganic nutrients under PEG treatment (Figure 1 and Figure 2, Table S2). This phenomenon was also observed in wheat leaves subjected to PEGstress [41,42]. However, waterwithholding did not alter leaf ion content in Limonium species either [43], suggesting a lack of nutrient deficiency under these conditions. Maintaining appropriate nutrient levels is key for plant function and growth, and it is of special relevance under drought stress, where the decrease in transpiration and water uptake can lower K+ influx to the roots [44]. Considering the special importance of this nutrient, its decline, togetherwith the decline in other essential nutrients suggest a higher plant metabolic and physiologic alteration and lower tolerance towards PEG treatment. These lower nutrient levels upon PEG exposure could be another consequence of lowoxygen availability due to the highly viscous nature of the PEG solution, which could impair ion transport and uptake processes [33,45]. The presence of hypoxic conditions could also explain the vast increase in succinate and alanine levels in PEG-treated roots (Table 2 and Table 3) due to a shift in the primary carbon metabolism under these conditions [46].
3.2. Salinity and Drought: Differences in the Metabolic Response at the Whole-Plant Level
Although n class="Chemical">salt and drought n class="Disease">stress trigger some common responses in plants, especially at early stages, salinity implies an important ionic stress by high intracellular sodium and chloride concentrations, which is absent in drought-stressed plants [47], thus affecting plant metabolism in a different way than no-irrigation stress.
The closure of stomata is a common phenomenon under n class="Disease">water-deficit stress, aimed at decreasing n class="Chemical">water loss through transpiration and driven by a “hydroactive feedback” mechanism involving the leaf water status. This could explain why, despite the similar leaf water potential achieved by No-W and NaCl-stressed plants, drought stress led to a lower stomatal conductance, which correlated well with the lower leaf water content in the soil-drying experiment (Table 1, Figure 3). However, whilesaltstress did not significantly affect the roots’ water content, No-W conditions led to a significant decrease in this parameter (Table 1). This could mean that while the lack of irrigation led to an obvious decrease in the soil water content, the presence of NaCl and consequent increase in the soil osmotic potential was not enough to fully inhibit root water absorption under these conditions. Despite these physiological differences, it was at the metabolism level where the disparities between both treatments became more evident.
3.2.1. Drought Stress Modulates Carbon and Antioxidant Metabolism in the Roots, While Salinity Does So in the Shoots
The differential response exerted by both n class="Chemical">water-deficit treatments n class="Chemical">was also visible when analyzing the carbohydrate content (Table 2, Figure 3). In leaves, the starch content increased in response to saltstress but decreased dramatically upon drought, whilesucrose accumulated under both stresses, above all in response to NaCl, as observed in rice leaves [48]. The increase in leaf starch content is often observed in salinity experiments, and could be a means to scavenge excess sodium [37,49]. Additionally, this sugar partitioning into starch under NaClstress could help avoid metabolic alterations derived by excessive accumulation of sucrose, which can act as a feedback inhibitor of processes such as photosynthesis [49]. On the other hand, soluble sugars, including fructose and, especially, sucrose and glucose, play a crucial role in plant metabolism and in the defense of plants against stress, serving as osmoprotectants, source of energy and carbon as well as signaling molecules involved in the up-regulation of genes involved in plant defense [39,49,50,51]. Hence, the accumulation of these molecules under abiotic stress has been widely reported in the literature [52].
In this study, phloem n class="Chemical">sucrose concentration was not altered under NaCl or No-W conditions (Table 2), suggesting that plant metabolism was not severely affected by these stresses, with enough starch available to sustain plant metabolism even at night [53]. Considering the fact that phloem translocation depends on source and sink strengths, the maintenance of the sucrose phloem transport despite the inhibition of photosynthesis under No-W conditions (Table 1), suggests an increased sink strength. This is in agreement with the significant increase in the root-to-shoot ratio under No-W (Table 1), a commonly observed phenomenon under drought stress linked to the lower growth inhibition of the root compared to the shoots, allowing better water uptake from the soil [54]. This increase in root strength under No-W could be linked to the increase in alkINV observed in this organ, which could compensate for the decrease in the SuSy activity (Table 5), as observed previously in arabidopsis [55]. The decrease in root SuSy activity in response to abiotic stress has been already reported for roots of salt-stressed maize [56] and drought-stressed sorghum [57] and M. truncatula [25], being described as one of the main and faster markers of abiotic stress [25]. In our study, the decrease in root sink strength due to a decrease in both SuSy and INV under salinity stress might indicate a redistribution of assimilates to the shoots rather than to the roots in NaCl-stressed M. truncatula plants. These responses suggest a key role of alkINV in the regulation of assimilate partitioning and plant response to drought stress, allowing sucrose transportation, unloading and its degradation in the root tissue for its use in root growth and/or osmoprotection under adverse conditions.
In our study, the levels of leaf n class="Chemical">organic acids remained constant under n class="Chemical">No-W stress, while α-ketoglutarate and citrate increased significantly under salinity stress, reflecting the subtle differences in the management of the different osmotic stresses (Table 2, Figure 3). The observed activation of IDH in salt-treated leaves (Table 5), in agreement with previous studies [58], not only could allow for this α-ketoglutarate (α-KG) build-up, but also for net glutamate biosynthesis via the GS/GOGAT cycle, thus playing a key role in the synthesis of amino acids as well as in the linkage between carbon and nitrogen metabolism [59]. In addition, the reaction catalyzed by IDH provides the cytosol with NADPH, which can be used in the reduction of NO3− and many other biosynthetic processes such as proline biosynthesis or glutathione regeneration, allowing ROS scavenging [60]. This could explain why its over-expression increased salt tolerance in transgenic A. thaliana plants [61], hence suggesting an important role in M. truncatula tolerance to NaCl.
Interestingly, total n class="Chemical">glutathione and n class="Chemical">homoglutathione levels were lower in salt-stressed roots compared to those of No-W treated plants (Table 4, Figure 3). Glutathione is one of the main plant polar antioxidants and plays a central role in reactive oxygen species (ROS) scavenging through the glutathione–ascorbate cycle and as an electron donor to glutathione peroxidase, whilehomoglutathione is a glutathione homologue with similar functions and characteristic of legumes, usually being accumulated under various stresses, including drought [62]. The inherent ROS detoxifying properties of α-KG and its accumulation under NaClstress togetherwith the decreased ROS formation as a result of inhibited respiration due to lower NADH availability (through the potential inhibition of α-KGDH) confer a unique strategy to modulate the cellular redox environment [63]. Hence, the higher accumulation of α-KG in salt-treated leaves and drought-stressed-roots may reflect the higher need of these tissues for ROS detoxification. This apparently higher sensitivity of leaves to NaClstress than roots was also reported for maize plants and switchgrass, with one of the responses being a higher antioxidant content in leaves than roots [64,65].
3.2.2. Drought Elicits an Overall Accumulation of Amino Acids in Roots While Only Proline Metabolism Is Modulated under Salt Stress
Attending to n class="Chemical">nitrogen compounds, the response to n class="Chemical">salt and drought stresswas also different (Table 3). Protein degradation is a common phenomenon observed under stress conditions contributing to the amino acid pool build-up [2]. In addition, the increased protein catabolism could also be linked to the provision of carbon sources for respiration [66]. In our study, soluble protein and total amino acid contents were not relevantly affected at either shoot or root level under saltstress. However, the lack of irrigation provoked an important accumulation of amino acids in the roots accompanied by a non-significant decrease in the protein content (Table 3) in agreement with previous studies [27,67]. In addition, the lack of phloem amino acid accumulation under drought stress opposed to the increase in leaves and roots suggests an in situ amino acid synthesis or protein recycling rather than import from the shoots. This is in agreement with the observed proteomic changes in M. truncatula [27], where drought stressprovoked an accumulation of protein degradation and amino acid synthesis-related proteins in roots while decreasing in shoots, as suggested by our enzymatic studies (Table 5). In addition, the increased BCAA levels (Table S1), as previously observed [25], could be used as alternative electron donors for respiration, reinforcing their role on water-deficit tolerance [68].
Even though drought n class="Disease">stress did not increase the phloem n class="Gene">sap total amino acid content, Prowas significantly increased in agreement with studies in white clover [19] and arabidopsis [69]. Lee et al. concluded that Pro loading to the phloem sap has a significant influence on the down-regulation of N uptake and assimilation [19], which could imply a means of avoiding further ammonium build-up due to the down-regulation of growth and protein synthesis [70]. Indeed, the increased proline phloem loading in white cloverwas closely related to the decrease in nitrogen reductase in roots, nitrogen uptake and its assimilation [19].
Contrary to drought, n class="Chemical">salt n class="Disease">stress did exert significant changes in the phloem sap amino acid content, with a significant increase in total and several individual amino acid contents, above all Pro and less significantly Gln, Ser, Ala and GABA (Table 3 and Table S1). The increase in total phloem sap amino acids was also observed in tomato plants [16], but the lack of increase in NaCl roots suggests their redistribution to older leaves, as previously observed for sucrose [71]. In addition, the increase in amino acid flow in the phloem could also be considered a nitrogen source, correlating well with the decrease in the NO3− levels in the roots of NaCl plants (Figure 1), which further highlights the different response and adaptations of M. truncatula to both stresses. On the other hand, Cuin and Shabala suggested that certain amino acids such as GABA, Pro, Gln and Ser can mitigate the NaCl-induced K+ efflux, while others such as Val can enhance the detrimental effects of salinity on K+ homeostasis [72]. This is in agreement with the amino acid changes observed in the salt-stressed phloem sap, indicating that increases in free amino acids under abiotic stress might have a key role in plant salinity tolerance [72].
The overall accumulation of n class="Chemical">proline at the whole-plant level in response to both stresses was remarkable (Table 3), which is a widely accepted response of plants to abiotic stress. Proline is a compatible solute which acts as osmolyte, molecular chaperone and hydroxyl radical scavenger, protecting cells from stress-induced damage [2,73]. In our study, Pro synthesis was increased in both leaves and roots in NaCl-treated plants, while no-irrigation only altered Pro synthesis-related enzymes in the root tissue, correlating with Pro levels in each tissue (Table 3 and Table 5). On the contrary, Pro root degradation was only activated upon drought stress, possibly as a mechanism for energy and reducing equivalents generation under stressful conditions [74]. These results are in agreement with Verdoy et al., who observed an increased Pro degradation and activation of OAT activity in osmotic stressed M. truncatula roots, thus remarking the importance of the ornithine pathway under stressful conditions in this plant species [75].
3.2.3. Salt Stress Provokes a Nutrient Deficiency Which Does Not Occur in Drought-Stressed Plants
The most notorious differential effect of both n class="Disease">stresses n class="Chemical">was observed in the M. truncatula ionome (Figure 1 and Figure 3). Thus, while drought stress did not significantly alter the ion content of leaves and roots, saltstress led to massive ion alterations in both leaves and, above all, roots. NaCl irrigation led to a very important Na+ and Cl− ion accumulation in both organs, as previously reported for alfalfa plants [76]. These ions’ transport to the shoot and vacuole sequestration is an extensively described salt tolerance mechanism for the maintenance of a healthy high K+/Na+ ratio [77]. The decrease in Ca2+ ions in the root tissue has also been previously observed in alfalfa plants under salinity stress [78], possibly related to a decreased uptake due to a reduced calcium activity in NaCl-rich soil solutions. Indeed, Na+ and Cl− ions compete with other ions such as K+, Ca2+, Mg2+ and NH4+ as well as SO42− and NO3−, respectively, for the ion transporters during root uptake and translocation in plant shoots as well as during their use in biochemical processes such as enzymatic reactions [79].
The only significant effect of drought n class="Disease">stress in the plant ionome was the accumulation of nitrate and, to a lesser extent, sulphate in the root tissue (Figure 1). Nitrate is the main nitrogen source in agricultural soils and the mineral nutrient that most frequently limits plant growth. This nitrate accumulation has been previously observed in Spartina alterniflora plants under drought stress [80] and could be due to a reduction in the nitrate reductase activity, the first and rate-limiting step enzyme in the nitrate assimilation pathway, which has been observed to decline in many species even under mild water-stress [81]. The decline in root AAT activity (Table 5), another nitrogen metabolism-related enzyme, also agrees with this decrease in root nitrogen metabolism under water-deficit conditions. However, despite the decrease in the primary assimilation of nitrogen, the increase in nitrogen compounds such as amino acids rules out a deficit in nitrogen under this stress.
4. Materials and Methods
4.1. Plant Materials and Stress Treatments
n class="Species">Medicago truncatula seeds were scarified with sulfuric acid 98% for 7 min, washed and then sterilized with 3.5% sodium hypochloride for 90 s. After a thorough wash, the seeds were soaked in water and left shaking in the dark for 6 h. When the seeds were hydrated, they were transferred to 7‰ agar plates at 4 °C for one day in the dark, and then incubated at 20 °C for two days. The seedlingswere then planted in 1-L brown plastic pots with perlite:vermiculite (1:3, v/v) and grown for 11 weeks in a controlled chamber (22/18 °C day/night temperature, 70% relative humidity, 500 µmol m−2 s−1 (PPFD), 12-h photoperiod) and irrigated with Evans medium supplemented with 5 mM NH4NO3 [82].
n class="Chemical">NaCl, no-watering (No-W) and PEG-6000stresswere applied to provoke a drop of the leaf water potential (Ψleaf) similar to a moderate water-deficit level. Saltstresswas applied by watering plants with 0.25 M NaCl, which generated an osmolarity of 450 mmol Kg−1 in the solution. The No-W treatment was applied by limiting water irrigation to 2/3 of the daily-transpired water. Lastly, 250 g L−1 PEG-6000were dissolved in water to reach the same osmolarity than the above-described salt solution. Control plants were watered daily with dH2O. All treatments were applied for 7 days. In addition to physiological measurements, different aliquots of leaf and lateral root tissue were collected and stored at −80 °C for further analysis. In the case of PEG-treated plants a large variation in the Ψleaf response was observed and only the ones with Ψleaf ≈ −1.7 MPa were selected for further experiments.
4.2. Physiological Measurements
Plant transpiration was gravimetrically determined on a daily basis by weighting the pots one hour after the beginning of the photoperiod. Ψleaf was measured at this time point in the second fully expanded leaf using a pressure chamber (Soil Moisture Equipment, Santa Barbara, CA, USA) as earlier described [83]. Stomatal conductance was measured with a dynamic diffusion porometer (AP4; Delta-T devices, Cambridge, UK) in leaflets of the second-fully expanded leaf. Chlorophyll content was measured in five leaflets of the second-fully expanded leaf per plant using a SPAD-502 m (Konica-Minolta, Osaka, Japan). Water content (WC) was determined in base to the fresh weight (FW) and the dry weight (DW) obtained after 48 h drying at 70 °C using the following formula (1):
4.3. Phloem Sap Exudation
Phloem n class="Gene">sap exudation was performed as indicated by Rahmat and Turnbull with minor modifications [84]. Petioles were cut with razor blades in buffer containing 10 mM EDTA, 10 mM HEPES pH 7. After gently drying the cut with paper, 10 leaves per plant were arranged and soaked in Eppendorf tubes containing 1.5 mL of the above-mentioned buffer. Phloem sapwas exudated in the dark at 21 °C with the opening of the tube sealed with scotch tape and in saturated humidity conditions. After exudating for 22 h, the leaves were carefully removed from the tube and exudate extracts were frozen in liquid nitrogen and stored at −80 °C for further use.
4.4. PEG Uptake Measurement
The following n class="Chemical">procedure was adapted from the method described by Hyden [85]. Frozen leaves and roots aliquots (≈0.15 g) of all PEG-treated plants were homogenized in 1 mL extraction buffer (50 mM MOPS pH 7.5, 10 mM MgCl2, 20 mM KCl) and samples were centrifuged for 5 min at 11,500× g. The supernatant was then pipetted into a centrifuge tube, and 0.6 mL of 10% (w/v) BaCl·2H20, 0.6 mL of saturated Ba(OH)2, and 0.6 mL of 5% (w/v) ZnSO4·7H2Owere added with shaking between each addition. The tubes were allowed to stand for at least 5 min and then were centrifuged at 7600× g. The supernatant was mixed with 3 mL TCA solution (450 g TCA and 50 g BaCl2·2H2O in 1LH2O) and left for 5 min. The turbidity was then measured as the percentage of light absorbed at 600 nm, and the PEG content was calculated using a calibration curve [32]. The measured turbidity value in control plants was considered as zero.
4.5. Determination of Soluble Sugar and Starch Content
Frozen samples were extracted three times in boiling n class="Chemical">ethanol (80%, v/v) and once at RT for 30 s. The aqueous phase of the ethanol extract was evaporated at 40 °C and then the dry residue was resuspended in ddH2O by vigorous vortexing. A sample cleaning was then performed by centrifugation at 2330× g for 10 min and the supernatants were stored at −20 °C for further soluble sugar analysis.
The remaining tissue after n class="Chemical">ethanol soluble compounds extraction was dried at 70 °C for 48 h. Dry samples were homogenized in ddH2O and further boiled for one hour for starch grain breakage. After cooling down, 1 mL of desalted amiloglucosidase solution (EC 3.2.1.3, 0.5 units/mL in acetate buffer pH 4.5) was added to each tube and incubated under shaking at 55 °C for starch digestion. Extractions were centrifuged at 2330× g for 10 min and the supernatants were stored at −20 °C for further glucose quantification. The soluble sugar analysis in the phloem sapwas performed directly using the exudates. Sucrose, glucose and fructosewere determined by capillary electrophoresis (CE) in a Coulter P/ACE system 5500 (Beckman Coulter Inc., Fullerton, CA, USA) coupled to a diode array detector [86]. Concentrations were calculated from peak heights using commercial standards (Sigma-Aldrich, Steinheim, Germany).
4.6. Determination of Organic Acids and Inorganic Ions
Frozen samples (≈100 mg) were homogenized to a fine pon class="Chemical">wder in liquid N2 using a mortar and pestle. For organic and inorganic anions, 1.5 mL of 10% (w/v) TCAwere added and the homogenate was centrifuged for 10 min at 1750× g and 4 °C. The aqueous phase was washed three times with ethyl ether saturated with water. The upper ether solution was discarded and the aqueous phase was purged with nitrogen gas for 2 min and subsequently filtered (0.45 nm pore size). For cations, finely-ground leaf and root material was extracted with 1 mL ddH2O for 30 min at 90 °C. After centrifugation (12,500× g, 10 min), the supernatant was collected and centrifuged again for 5 min. Ion levels were determined by ion chromatography in a DX-500 system (Dionex Ltd., Sunnvale, CA, USA). Cations were analyzed by isocratic separation (CS12A columns) and anions by gradient separation (AS11 column; 2.5 mM NaOH/18% methanol to 45 mM NaOH/18% methanol in 13 min) according to the manufacturer’s instructions.
4.7. Determination of Free Amino Acid Content
Frozen leaves (≈70 mg Fn class="Chemical">W) and roots (≈150 mg Fn class="Chemical">W) were ground to powder under liquid N2 and subsequently homogenized with 3 mL 1 M HCl. Homogenates were incubated on ice for 10 min and, subsequently, extracts were centrifuged twice at 20,000× g and 4 °C for 10 min. Supernatants were neutralized using NaOH, and internal standards norvaline and homoglutamic acidwere spiked. In the case of the phloem sap, internal standards were directly added to the samples. Samples were then derivatized with 1 mM fluorescein isothiocyanate dissolved in acetone at RT for 15 h in 20 mM borate buffer pH 10. The content of free amino acidswas determined using a Beckman Coulter capillary electrophoresis (CE) PA-800 (Beckman Coulter Inc., Brea, CA, USA) coupled to laser-induced fluorescence detection (argon laser at 488 nm), as described by Arlt et al. [87] and Takizawa and Nakamura [88], with minor modifications.
A fused-silica capillary, 43/53.2 cm long and 50 µm internal diameter (Beckman Coulter Inc., Brea, CA, USA), was employed. For amino acid separation, 45 mM α-cyclodextrin in 80 mM n class="Chemical">borax buffer pH 9.2 was used. Analyses were performed at 20 °C and at a voltage of 30 kV (110 µA). Total amino acid content is presented as the summation of single amino acids for each sample and expressed on a DW basis.
4.8. Small Antioxidant Determination
Frozen samples (≈130 mg Fn class="Chemical">W leaves and ≈180 mg Fn class="Chemical">W roots) were ground to powder in liquid nitrogen and subsequently homogenized with 1 mL of ice-cold 2% metaphosphoric acid. The homogenate was centrifuged at 4400× g and 4 °C for 2 min. Antioxidants were analyzed by high-performance CE in a Beckman Coulter P/ACE system 5500 (Beckman coulter Inc., Fullerton, CA, USA.) associated with a diode array detector, as described by Herrero-Martínez et al. [89]. The CE instrument was equipped with the P/ACE station software for instrument control and data handling. The background buffer was 60 mM NaH2PO4 pH 7 containing 60 mM NaCl and 0.0001% hexadimethrine bromide. The applied potential was 15 kV, and the capillary tubing (50 μM) was 30/37 cm long. The indirect UV detection wavelength was set at 200 and 265 nm. Reduced ascorbate (ASC) glutathione (GSH) and homoglutathione (hGSH) were determined directly by injecting a plant extract aliquot in the CE as described above. Total ascorbate, glutathione and homoglutathione levels were directly analyzed by CE after sample reduction with DTT. Dehydroascorbate (DHA) and oxidized glutathione (GSSG) and homoglutathione (hGSSG) levels were determined as the difference between total ascorbate, glutathione and homoglutathione and their respective reduced form levels.
4.9. Enzymatic Activities and Total Soluble Protein Content
Leaf and root samples were ground into a fine pon class="Chemical">wder with liquid nitrogen and homogenized with extraction buffer (50 mM MOPS pH 7.5, 0.1% (v/v) Triton X-100, 10 mM MgCl2, 1 mM EDTA, 20 mM KCl, 10 mM DTT, 10 mM β-mercaptoethanol, 2.5% (w/v) PVPP, 2 mM PMSF and a protease inhibition cocktail tablet) and centrifuged at 24,000× g and 4 °C for 20 min. The protein content of the supernatant was determined by the Bradford assay in the crude extract, while an aliquot was desalted through BioGel P-6 DG desalting gel for some enzymatic determinations. Enzymatic activities for aspartate aminotransferase (AAT), glutamate synthase (GOGAT), glutamine synthase (GS), glucose-6-phospate dehydrogenase (G6PDH), sucrose synthase (SuSy), NADP-isocitrate dehydrogenase (IDH), glutamate dehydrogenase (GDH), alkaline invertase (AlkINV), Δ1-1-pyrroline-5-carboxylate synthase (P5CS), ornithine aminotransferase (OAT) and proline dehydrogenase (ProDH) were performed as described previously [25].
4.10. Statistical Analysis
All data are reported as the mean ± standard error (SE) of 5 to 10 independent biological replicates. Multiple comparison analyses were performed with SPSS using analysis of variance (ANOVA, p < 0.05) and Tukey’s HSD test, while comparisons between treatment and control (when needed) were analyzed by Student’s t-test (p < 0.05). All mentioned correlations were statistically tested with XLSTAT 2020.5 (https://www.xlstat.com/en/, accessed on 23 December 2020) using Pearson’s correlation coefficient. Principal Component Analyses (PCA) were performed in log-transformed data using MetaboAnalyst 5.0 (https://www.metaboanalyst.ca/, accessed on 23 December 2020) and MetaGeneAlyse v1.7.1 (https://metagenealyse.mpimp-golm.mpg.de/, accessed on 23 December 2020).
5. Conclusions
Generally, n class="Species">M. truncatula is considered a relatively drought tolerant legume compared to others like pea or n class="Species">soybean [90]. However, regarding salinity stressM. truncatula Jemalong A17 cultivar is considered salt sensitive by some authors [24] and salt tolerant by others [91]. Our study suggests a similar tolerance to both drought and saltstress, with even some parameters such as higher stomatal conductance and leaf water content suggesting slightly better coping with NaCl at similar leaf water potentials. Nonetheless, M. truncatula responses to both stresses differed notably (Figure 4), with a marked defensive response of NaCl shoots and droughted-roots through the accumulation of soluble sugars and amino acids under both stresses. In addition, the most relevant differences in the plant’s response to stresswas the increased starch content in plants under NaCl, possibly as a mechanism of ion sequestration and avoidance of photosynthesis inhibition, as well as the increase in IDH activity and α-KG content. On the other hand, root proline catabolism, BCAA accumulation as well as the increased root sink strength via invertase could play key roles in M. truncatula response to no-irrigation stress. Regarding the use of PEG as a drought mimicker, even though the presence of typical drought stress markers such as proline accumulation could suggest PEG as an adequate drought simulator, the important impairment on nutrient uptake and the differential regulation of carbon and proline metabolism upon PEG treatment does not suggest that conclusions based on PEG studies may be directly extrapolated to the understanding of drought stress responses. Thus, results suggest a higher protection of shoots in saltstressed plants and roots in non-irrigated plants through different mechanisms including the regulation of proline and carbon metabolism, while discarding PEG as safe mimicker of drought. The conclusions derived from this work highlight the importance of the study of the response to abiotic stress in plants as whole systems and open the doors to future studies that research the relevance of the analyzed traits for water-deficit tolerance.
Figure 4
Summary of the most relevant M. truncatula responses to salinity and drought stress. This image depicts the increases and decreases in physiological parameters as well as enzymatic activities and metabolite and nutrient concentrations in leaves, roots and phloem sap under NaCl and no-irrigation (No-W) compared to control conditions. Bolded text indicates a higher increase or decrease in the studied parameter compared to the other stress. aa, amino acids; glut, glutathione; G6PDH, glucose-6-phosphate dehydrogenase; gs, stomatal conductance; hglut, homoglutathione; IDH, isocitrate dehydrogenase; α-KG, α-ketoglutarate; OAT, ornithine aminotransferase; P5CS, Δ1-1-pyrroline-5-carboxylate synthase; ProDH, proline dehydrogenase; Suc, sucrose; SuSy, sucrose synthase; WC, water content; Ψleaf, leaf water potential. (Created with BioRender.com, accessed on 23 December 2020).
Figure 1
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Figure 3
Figure 4