Next Article in Journal
Composite Graph Neural Networks for Molecular Property Prediction
Previous Article in Journal
Involvement of the GH38 Family Exoglycosidase α-Mannosidase in Strawberry Fruit Ripening
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Cadmium Alters the Metabolism and Perception of Abscisic Acid in Pisum sativum Leaves in a Developmentally Specific Manner

by
Edyta Zdunek-Zastocka
*,
Beata Michniewska
,
Angelika Pawlicka
and
Agnieszka Grabowska
Department of Biochemistry and Microbiology, Institute of Biology, Warsaw University of Life Sciences—SGGW, Nowoursynowska 159, 02-776 Warsaw, Poland
*
Author to whom correspondence should be addressed.
Int. J. Mol. Sci. 2024, 25(12), 6582; https://doi.org/10.3390/ijms25126582
Submission received: 13 May 2024 / Revised: 10 June 2024 / Accepted: 11 June 2024 / Published: 14 June 2024
(This article belongs to the Special Issue Role of Abscisic Acid in Plant Stress Response)

Abstract

:
Abscisic acid (ABA) plays a crucial role in plant defense mechanisms under adverse environmental conditions, but its metabolism and perception in response to heavy metals are largely unknown. In Pisum sativum exposed to CdCl2, an accumulation of free ABA was detected in leaves at different developmental stages (A, youngest, unexpanded; B1, youngest, fully expanded; B2, mature; C, old), with the highest content found in A and B1 leaves. In turn, the content of ABA conjugates, which was highest in B2 and C leaves under control conditions, increased only in A leaves and decreased in leaves of later developmental stages after Cd treatment. Based on the expression of PsNCED2, PsNCED3 (9-cis-epoxycarotenoid dioxygenase), PsAO3 (aldehyde oxidase) and PsABAUGT1 (ABA-UDP-glucosyltransferase), and the activity of PsAOγ, B2 and C leaves were found to be the main sites of Cd-induced de novo synthesis of ABA from carotenoids and ABA conjugation with glucose. In turn, β-glucosidase activity and the expression of genes encoding ABA receptors (PsPYL2, PsPYL4, PsPYL8, PsPYL9) suggest that in A and B1 leaves, Cd-induced release of ABA from inactive ABA-glucosyl esters and enhanced ABA perception comes to the forefront when dealing with Cd toxicity. The distinct role of leaves at different developmental stages in defense against the harmful effects of Cd is discussed.

1. Introduction

Environmental pollution, driven mainly by rapid industrialization and extensive agriculture, is a major challenge for the world today. Heavy metals are among the most hazardous pollutants as they are toxic, non-biodegradable and tend to accumulate in living organisms [1]. Cadmium (Cd), a non-essential element with no known biological function in living organisms, is particularly toxic [2]. It is easily absorbed by plants through the roots and transported to the leaves via the xylem [3]. The high affinity of Cd for sulfhydryl groups in proteins and its ability to replace essential metals in the active sites of enzymes make it extremely toxic even at low concentrations. In addition, Cd causes a decrease in chlorophyll content, inhibits the process of photosynthesis and transpiration [4], reduces the uptake of the mineral nutrients and impairs their transport [5]. Although Cd is not a redox-active metal, it can trigger oxidative stress by causing the overproduction and accumulation of reactive oxygen species (ROS), which in turn lead to lipid peroxidation and damage to cell membranes and organelles [6]. Visible symptoms of Cd toxicity include chlorosis, necrosis, growth inhibition and even plant death, at high concentrations [7].
To counteract the harmful effects of stress factors such as cadmium, plants have developed several defense mechanisms, of which abscisic acid (ABA) plays a central role. ABA is a phytohormone involved in plant growth and development, including the promotion of senescence, induction of seed dormancy and closure of stomata [8]. Under appropriate environmental conditions, adequate ABA concentration enables optimal plant growth, while ABA, which rapidly accumulates in plant tissues under various stress factors, plays a protective role [9,10,11]. ABA has been found to increase plant tolerance to cadmium by reducing transpiration and thus reducing Cd uptake from the soil and transport from roots to shoots [3,12,13]. Moreover, ABA promotes the activity of antioxidant enzymes and increases the content of non-enzymatic antioxidants [14]. Furthermore, ABA induces phytochelatin-conjugated vacuolar sequestration of Cd and inhibits the expression of genes encoding metal transporters [15].
Strict control of ABA levels is crucial for proper plant growth and development, and for adaptation to unfavorable environmental conditions. The concentration of ABA is regulated in tissues by its synthesis, degradation, (de)conjugation and transport [9]. In plants, abscisic acid is synthesized de novo via the carotenoid pathway, which starts with the cleavage of β-carotene [16]. A key enzyme of the ABA biosynthetic pathway that determines its rate in response to stress factors is 9-cis-epoxycarotenoid dioxygenase (NCED, EC 1.13.11.51) [16]. Overexpression of the Vitis amurensis gene encoding NCED resulted in increased tolerance to drought and flooding stress [17]. In addition, plants overexpressing VaNCED1 genes also showed increased expression of other genes related to drought stress response, such as ABA-responsive element 1 (ABRE1), ABRE binding factors 2 and ABA-insensitive 5. In peas, increased expression of PsNCED2 and PsNCED3 was observed in both leaves and roots under progressive and rapid-onset drought stress [18]. The final step of the pathway, the oxidation of abscisic aldehyde (ABAld) to abscisic acid, is catalyzed by the molybdenum enzyme aldehyde oxidase (AO, EC 1.2.3.1). AO exhibits a wide range of substrate specificity [19]; however, AO isoforms that oxidize ABAld to ABA are only reported for Arabidopsis (AAOδ) [20], barley (AO3) [21] and pea (PsAOγ) [22]. PsAOγ is a homodimer consisting of subunits encoded by the PsAO3 gene [18]. Importantly, PsAOγ exhibits enhanced activity towards ABAld in both leaves and roots under drought [18], salt and ammonium treatments [22]. The degradation of abscisic acid is based on its conversion to phaseic acid (PA), which is catalyzed by a cytochrome P450 monooxygenase (P450, EC 1.14.14.1) [23]. However, the level of free active ABA is also controlled by its conjugation. ABA-UDP-glucosyltransferase (ABAUGT, EC 2.4.1.163) catalyzes the glucosylation that leads to the formation of the inactive storage form of ABA, ABA-glucose ester (ABA-GE) [24]. In peas, ABAUGT is encoded by PsABAUGT1 and PsABAUGT2, and overexpression of PsABAUGT1 in Arabidopsis thaliana decreases the concentration of free ABA and accelerates cotyledon emergence [25]. Among the conjugates, ABA-GE stands out as the predominant form. When environmental conditions become unfavorable, β-glucosidase (BGLU, ABA-GE hydrolase, EC 3.2.1.175) rapidly converts ABA-GE to its active form [12,26,27]. ABA-GE is also considered as a transport form of abscisic acid for both local and long-distance transport through the xylem [9,28].
The response of plants to abscisic acid depends on the perception of signals mediated mainly through the pyrabactin resistance (PYR), pyrabactin resistance-like (PYL) and regulatory component of ABA receptors (RCAR) [29]. In the presence of ABA, the binding of PYR/PYL/RCAR to phosphatase 2C (PP2C) is enhanced, leading to inhibition of its activity [30,31]. This in turn abolishes PP2C-induced inhibition of sucrose non-fermenting 1-related protein kinase 2 (SnRK2), which subsequently targets specific membrane ion channels and transcription factors that are critical for adaptation to abiotic stress [32]. The Arabidopsis genome encodes 14 small RCAR/PYR1/PYL proteins (159–211 amino acid residues) that have different ABA-binding properties and selectively interact with PP2Cs to jointly regulate the ABA response [33,34]. Overexpression of PYL5, PYL8, PYL9 and PYL11-14 increases drought tolerance [35,36,37], while overexpression of PYL12-13 improves tolerance to heat and cold stress [38]. In addition, the expression of individual PYLs depends on the tissue type, developmental phase and growth stage of the plant, and varies in response to environmental stimuli [39], contributing to the versatility of ABA signaling and functions.
There is still a lack of research focusing on the metabolism and perception of ABA in response to heavy metals, especially in leaves at different developmental stages. In this study, the changes in free ABA and ABA-GE content were investigated in younger and older pea leaves treated with cadmium. Furthermore, the expression of genes involved in the de novo synthesis of ABA and its conjugation with glucose was determined. This study also covered the activity of aldehyde oxidase and β-glucosidase as well as changes in the expression of PYLs in response to cadmium and exogenous ABA. The results obtained provide insight into how leaves prioritize and control their responses to cadmium stress at different developmental stages, which is crucial for the development of targeted strategies to increase plant resistance.

2. Results

2.1. Content of Free ABA and Its Conjugates as Affected by Cd Stress

The concentration of free ABA and its conjugates was analyzed in the leaves of pea plants after 48 h of growth on media containing 50 µM CdCl2. The analyses were performed on leaves at different stages of development.
Under both control and Cd stress conditions, the highest concentration of free ABA was found in the youngest, unexpanded A leaves, while B1, B2 and C leaves contained about 10, 25 and 40% less ABA, respectively (Figure 1A). After 48 h of Cd exposure, an increase in free ABA content was observed in leaves at each developmental stage, and this increase was about 2-fold in A, B1 and B2 leaves, and 1.5-fold in C leaves compared to control plants.
Under control conditions, the concentration of conjugated ABA forms was highest in the oldest C leaves, while B2, B1 and A leaves contained 15, 35 and 50% less ABA-GE, respectively (Figure 1B). This trend changed under Cd stress conditions, where the highest concentration of conjugated ABA forms was observed in A leaves and was 25 and 35% lower in B2, B1 and C leaves, respectively. Cd treatment increased the content of conjugated ABA forms, but only in the youngest A leaves (by 50%), while decreases of 15, 35 and 50% were observed in B1, B2 and C leaves, respectively.

2.2. Expression of Genes Involved in De Novo ABA Synthesis and ABA Conjugation with Glucose as Affected by Cd Stress

The transcript levels of genes encoding enzymes involved in de novo ABA synthesis (PsNCED2, PsNCED3, PsAO3) and ABA conjugation with glucose (PsABAUGT1) were analyzed in the leaves of pea plants after 48 h of growth on media containing 50 µM CdCl2. The analyses were performed on leaves at different stages of development.
Under both control and Cd stress conditions, the mRNA level of all Pisum sativum genes analyzed was highest in the oldest C leaves, lower in B2 and B1 leaves and lowest in A leaves (Figure 2). Under control conditions, the expression of PsNCED2, PsNCED3, PsAO3 and PsABAUGT1 was approximately 4-, 3-, 6- and 13-fold higher in C leaves than in A leaves, respectively, and this trend was also observed in the Cd-treated plants.
Treatment of the plants with CdCl2 resulted in an increase in the mRNA level of all genes analyzed, with the largest increase observed for PsNCED2 (Figure 2). The expression of PsNCED2, PsNCED3 and PsAO3 was 4-, 1.5- and 2-fold higher, respectively, in Cd-treated plants than in control plants in leaves at each developmental stage. Cd also induced the expression of PsABAUGT1, which was increased by 75% in A leaves and 20–25% in the other leaves.

2.3. Activity of Aldehyde Oxidase and ABA-GE Hydrolase as Affected by Cd Stress

The activity of Pisum sativum aldehyde oxidase (PsAO), which catalyzes the final step of de novo ABA synthesis, and Pisum sativum β-glucosidase (PsBGLU, ABA-GE hydrolase), which releases ABA from its glucose conjugates, was investigated in leaves of pea plants after 48 h of growth on media containing 50 µM CdCl2. The analyses were carried out on leaves at different stages of development.
Under both control and Cd stress conditions, the activity of PsAOγ, an isoform previously shown to oxidize abscisic aldehyde to ABA [22] and encoded by PsAO3 [18], was highest in B2 and C leaves (Figure 3A and Figure S2). Under control conditions, the activity of PsAOγ was about 75% higher in B2 and C leaves than in A and B1 leaves. Cd treatment increased the activity of PsAOγ in B2 and C leaves by about 65%, but only by 15% in A leaves. Under Cd stress, the activity of PsAOγ in B2 and C leaves was already 2 and 2.5 times higher, respectively, than in A leaves, suggesting that B2 and C leaves are the major de novo ABA producers.
Under control conditions, the activity of PsBGLU was similar in A, B1 and B2 leaves and about 20% lower in C leaves (Figure 3B). Cd treatment increased PsBGLU activity in leaves of all developmental stages, with the most pronounced changes observed in A leaves and B1 (more than 2-fold increase). In C leaves of Cd-treated plants, PsBGLU activity was only 50% higher than in control plants. The results obtained suggest that Cd-induced ABA release from inactive ABA-glucosyl esters occurs mainly in A and B1 leaves.

2.4. Phylogenetic Analyses and Expression Levels of Genes Encoding ABA Receptors

A database search on the NCBI server yielded five PYL sequences of Pisum sativum: PsPYL1, PsPYL2, PsPYL4, PsPYL8, PsPYL9. Based on the phylogenetic relationships, the PsPYLs were grouped into three PYL subfamilies together with the corresponding sequences of Arabidospsis thaliana and Medicago truncatula. PsPYL1 and PsPYL2 were assigned to subfamily III, PsPYL4 to subfamily II and PsPYL8 and PsPYL9 to subfamily I (Figure 4).
The transcript levels of genes encoding ABA receptors were analyzed in leaves of pea plants after 48 h of growth on media containing 50 µM CdCl2. The analyses were performed on leaves at different stages of development.
Under control conditions, the highest level of PsPYL transcripts was observed in B1 (PsPYL1, 4, 9) and B2 (PsPYL2, 8) leaves (Figure 5). The expression of PsPYLs in A leaves was lower than in B1 or B2 leaves, about 60% for PsPYL1 and PsPYL9, more than 3-fold for PsPYL4 and PsPYL8 and 5-fold for PsPYL2. The expression of PsPYLs in C leaves was also lower than the corresponding highest level observed in B1 or B2 leaves, by 3-fold for PsPYL1 and about 35% for the other PsPYLs.
Under Cd stress, an increase in the mRNA levels of PsPYLs was observed, but only in A leaves, where the expression of PsPYL2, PsPYL4 and PsPYL8 was more than 2-fold higher than in control plants, and in B1 leaves, where an increase of about 40% was observed for PsPYL2 and PsPYL8 (Figure 5). The expression of none of the PsPYL genes examined was increased by Cd in B2 and C leaves. On the contrary, Cd induced a significant decrease in the expression of all PsPYL genes in B2 leaves (by 30–200%), while only a slight decrease or no change in the transcript level of the analyzed genes was observed in C leaves.

2.5. Expression of Genes Encoding ABA Receptors as Affected by ABA Treatment

The transcript levels of genes encoding ABA receptors (PsPYL1, PsPYL2, PsPYL4, PsPYL8, PsPYL9) were analyzed in leaves of pea plants after 24 h of growth on media containing 50 µM ABA. The analyses were performed on leaves at different developmental stages.
ABA treatment increased the content of free ABA more than 3-fold in A leaves, 4- to 5-fold in B1 and B2 leaves and 8-fold in C leaves (Figure S3). At the same time, a down-regulation of the expression of all PsPYLs analyzed was also observed in the leaves of the individual developmental stages (Figure 6). The greatest decrease in mRNA levels was observed for PsPYL4 and PsPYL1, where transcript levels were 5- to 10-fold and 2- to 4-fold lower, respectively, in ABA-treated plants compared to control plants. The least sensitive to ABA treatment was the expression of PYL9, which decreased approximately 2-fold in the youngest A leaves and 5–30% in leaves at other developmental stages.

3. Discussion

3.1. Cd Stress Increases the Concentration of Free ABA and Its Conjugates Mainly in the Youngest Leaves of Pea Plants

Under stress conditions, plants prioritize the protection of the youngest leaves, which are thought to make a greater contribution to plant fitness due to their relatively higher photosynthetic potential as a result of an unimpaired photosynthetic apparatus [40,41,42] and higher nitrogen content [43]. Younger leaves of Barbarea have been shown to contain higher concentrations of protective glucosinolates and saponins than older leaves when exposed to the herbivore Plutella xylostella [44]. It has also been reported that young leaves of Arabidopsis show a stronger antioxidant response than older leaves when exposed to drought [45] and herbicides [46]. Previous studies have also shown increased levels of other protective compounds, such as proline, especially in the youngest pea leaves when exposed to cadmium [47]. In monocotyledonous plants, the deleterious effects of Cd were observed to be less severe in the younger part of the leaves of rye [48] and maize [49].
Cadmium, an element known for its toxicity even at trace amounts, poses a significant threat to plants, forcing them to develop defense mechanisms to counter its negative effects. Abscisic acid is the main phytohormone involved in the plant’s response and tolerance to stress. Under Cd conditions, exogenous ABA significantly improves the growth characteristics of Brassica napus and Lactuca sativa plants, as measured by the accumulation of fresh biomass and the length of shoots and roots [50,51]. Exogenous ABA also mitigates the negative effects of Cd toxicity by increasing the content of chlorophyll a, chlorophyll b and carotenoids, improving gas exchange in the leaf and regulating the expression of genes encoding antioxidant enzymes and Cd stress-related genes [50,51]. In addition, ABA is known to reduce the transpiration rate by closing stomata and ultimately inhibiting Cd translocation into shoots [15].
An increase in the content of free endogenous ABA in leaves in response to cadmium exposure has been found in several plant species, including Oryza sativa [52], Zea mays [53], Phaseolus vulgaris [54] and Mentha crispa [55]. However, the changes in ABA content related to its metabolism in response to Cd in leaves at different developmental stages have not been investigated so far. In this study, it was observed that in the control plants, the highest free ABA content occurred in the youngest leaves, and gradually decreased with the stage of leaf development (Figure 1A). After a 48 h treatment with 50 µM cadmium, the ABA content doubled in the youngest A leaves and the fully developed B1 and B2 leaves, while a less pronounced increase was observed in the oldest C leaves. Similar results were obtained in previous studies on pea plants exposed to a 12 h treatment with Cd [47], where the highest free ABA content was also observed in young A and B1 leaves, both under control and stress conditions. The content of ABA conjugates showed an inverse trend, with the lowest levels found in the youngest A leaves and the highest levels in the oldest leaves of the control plants (Figure 1B). In turn, after Cd treatment, the content of ABA conjugates increased only in the youngest unexpanded A leaves and decreased in the leaves of later developmental stages, especially in the oldest C leaves. An increase in ABA-GE content in leaves of Betula pendula [56], Cistus albidus [57] and Hordeum vulgare [58] was found in response to drought; however, the response to stress in tissues at different developmental stages was not investigated. In this study, older leaves after Cd treatment showed a remarkable decrease in the content of ABA conjugates without a corresponding sharp increase in free ABA content, whereas younger leaves showed a marked increase in both ABA conjugate and free ABA content. As is commonly understood, the vast majority of ABA conjugates are ABA-GE, which serves as a storage and transport form of ABA, so that a transport of ABA-GE from the older to the younger leaves cannot be excluded.

3.2. Cd-Induced De Novo Synthesis of ABA and Its Conjugation with Glucose Occurs Mainly in Mature B2 and Old C Leaves, Whereas Its Release from Conjugates Occurs in Young A and B1 Leaves

To gain a deeper insight into the rationale behind the increase in free ABA, the expression of genes specific for de novo ABA synthesis was examined (Figure 2). Interestingly, the increase in free ABA in response to Cd was highest in the youngest leaves, while the transcript levels of PsNCED2, PsNCED3 and PsAO3 genes, which encode key enzymes for de novo ABA synthesis, were lowest in these leaves, even in response to Cd. The expression of all genes tested showed a positive correlation with the stage of leaf development, with a further increase in transcript levels observed in response to Cd treatment. Furthermore, expression of PsNCED2 increased more than 3-fold in mature B2 leaves and the oldest C leaves in response to cadmium. An increase in endogenous ABA levels associated with the up-regulation of SaNCED and BnNCED3 was previously reported for roots of the non-hyperaccumulating ecotype Sedum alfredii [59] and leaves of Boehmeria nivea [60], respectively, after Cd exposure. In turn, an increase in OsNCED4 expression was observed in Oryza sativa under Cd stress [61], while arsenic treatment strongly increased OsNCED2 and OsNCED3 expression [62]. In pea plants exposed to Cd, the highest expression of PsNCEDs and PsAO3 observed in B2 and C leaves was accompanied by the highest activity of the PsAOγ isoform (Figure 3A). Indeed, the activity of the PsAOγ isoform, whose subunits are encoded by PsAO3, increased more in older leaves than in younger leaves in response to Cd exposure. It is noteworthy that, the observed increase in PsAOγ activity in the A leaves was comparatively modest. In previous studies, the most significant increase in PsAOγ activity was also observed in the oldest leaves of pea plants under gradually induced drought [18] and under prolonged treatments with salinity, low nitrogen and ammonium [22,63]. Since de novo ABA synthesis occurs predominantly in the B2 and C leaves of pea plants exposed to Cd, it is very likely that the remarkable increase in ABA concentration in the youngest A leaves is due to its transport from the older leaves. In addition, analysis of ABA-GE hydrolase activity (Figure 3B) revealed that under cadmium exposure, the release of ABA from ABA-GE occurs predominantly in the youngest A leaves. There are two isoforms of BGLU in Arabidopsis. One of them, known as BG1 or BGLU18, is localized in the ER and undergoes dehydration-induced post-translational activation involving polymerization into high molecular weight complexes [26,64,65]. In contrast, the BG2 or BGLU33 isoform is localized in the vacuole, where under normal growth conditions it functions as an active, stable multimer whose level increases after dehydration [27]. Currently, there is no biochemical confirmation of which BGLU gene encodes the enzyme that can hydrolyze ABA-GE in pea plants. Therefore, to accurately assess the changes in the deconjugation of ABA-GE, it is essential to study the activity of the enzyme rather than focusing on the expression of the genes encoding it. In the oldest leaves, the observed increase in PsBGLU activity in response to Cd was the lowest compared to the other leaf developmental stages. Moreover, the expression of PsABAUGT1 increased the most in the oldest leaves under Cd treatment, suggesting the formation of ABA-GE conjugates and consequently leading to a decrease in the concentration of free ABA in these leaves. In contrast, the expression of PsABAUGT1 increased the least in the youngest leaves (Figure 3B), where the greatest increase in ABA-GE concentration was observed upon Cd treatment (Figure 1B). Therefore, based on the analysis of transcript levels, it is likely that ABA-GE is primarily synthesized in the oldest leaves in response to Cd stress and subsequently transported to the youngest leaves, where it undergoes hydrolysis to ABA.

3.3. The Expression of PYLs Increases Only in Young A and B1 Leaves under Cd Treatment

The phylogenetic relationship of the PYLs (Figure 4) revealed that the ABA receptors of Pisum sativum belong to the same subfamilies as those of Arabidopsis thaliana, Citrus sinensis, Glycine max, Medicago truncatula, Oryza sativa, Triticum aestivum or Zea mays [66]. PsPYL8 and PsPYL9 were assigned to subfamily I, PsPYL4 to subfamily II and PsPYL1 and PsPYL2 to subfamily III (Figure 4). However, the expression of the PYLs of the individual subfamilies in response to stress factors is generally not related to phylogenetic relationships. The expression of each ABA receptor varies according to plant species, tissue type, type of stress, duration and intensity of stress, resulting in a different scenario under different stress conditions. For example, under salinity, the transcript level of TaPYL1 is induced in roots while it decreases in shoots, while a decrease in the TaPYL1 transcript level was observed after dehydration in both leaves and roots [67]. In roots of Zea mays, the expression of ZmPYLs, with the exception of ZmPYL6, was activated by osmotic stress induced by polyethylene glycol (PEG); however, the response was time-dependent [66]. Time course analyses showed that ZmPYL8-9 are early response genes, and ZmPYL1-7 and ZmPYL10-11 are late response genes. In turn, in maize leaves ZmPYL1-3, ZmPYL5-6 and ZmPYL9-11 were down-regulated by dehydration, while ZmPYL4 and ZmPYL7-8 were significantly up-regulated. With the exception of ZmPYL4, which has been shown to belong to the group of late-responding genes together with ZmPP2C and ZmSnRK2, the other ZmPYL genes responded rapidly to water deprivation in maize leaves [68].
In pea plants, the expression of PsPYLs increases in response to cadmium in young A and B1 leaves and consistently decreases in mature B2 leaves and old C leaves, with the exception of PsPYL1, whose transcript level decreases in leaves at all developmental stages (Figure 5). The results indicate enhanced ABA perception in young leaves, where free ABA content was highest, suggesting a possible link between ABA content and perception mechanisms. In addition, the increased sensitivity to ABA could contribute to better protection of the youngest leaves. Similarly, in maize, sensitivity to herbivore-induced volatiles such as (Z)-3-hexenyl acetate varied with leaf age, resulting in high and persistent activation of jasmonate-mediated defenses exclusively in young leaves [69]. In older pea leaves, Cd-induced de novo ABA synthesis (Figure 2 and Figure 3) and ABA release from inactive conjugates are most pronounced, while the expression of PsPYLs genes is decreased (Figure 5). Therefore, the question arose whether a higher level of free ABA in older leaves would also increase the expression of PsPYLs as in A leaves. To clarify this uncertainty, plants were treated exogenously with 50 µM ABA for 24 h. It was found that the level of free ABA in the oldest C leaves increased approximately 7-fold after treatment, reaching a level almost equal to that of the youngest A leaves (Figure S3). Interestingly, the expression of all PsPYLs analyzed consistently decreased after ABA treatment at every developmental stage, including A leaves (Figure 6). The different expression profiles of ZmPYL4 and ZmPYL5 were also observed in maize roots and leaves, respectively, when the plants were exposed to ABA treatment and osmotic (PEG) or dehydration stress [68]. Interestingly, the transcript level of OsPYL10 was down-regulated by abscisic acid in shoots and up-regulated in roots [70]. The observations made for PsPYLs may suggest that plants control the perception of ABA signaling to avoid undesirable effects, such as stunted growth, when ABA levels are too high. In this study, PsPYL4 expression was found to be the most sensitive to changes in ABA concentration, while PsPYL9 was the least sensitive. Studies in Arabidopsis and rice have shown that overexpression of PYL9 genes promotes senescence of mature leaves in response to ABA treatment [37]. Therefore, it can be hypothesized that reduced PsPYLs transcription prevents the capture of de novo synthesized ABA before it is transported to the youngest leaves in the form of ABA-GE. Consequently, reducing the expression of PYLs may prevent the plant from triggering an exaggerated and prolonged stress response and premature senescence. However, further studies are needed to confirm this assumption.

3.4. Perspectives for the Development of ABA-Mediated Strategies to Increase Plant Resistance to Cadmium

The results of this study not only shed light on how leaves prioritize and control their responses to Cd stress at different developmental stages, but by identifying genes involved in the regulation of ABA content and ABA perception, they also open up possibilities for their application in the development of strategies to improve plant stress resistance. The possibility of using genes encoding enzymes involved in de novo ABA synthesis (PsNCED2, PsAO3) and release from conjugates with glucose (PsBGLU) to generate transgenic plants seems particularly promising. Although studies have already been conducted in which ABA metabolism has been modified to improve resistance of plants to Cd stress, there are still too few studies to fully understand the complex and interlinked molecular mechanisms behind this resistance. Transgenic lines of Arabidopsis thaliana obtained by ectopic expression of Malus hupehensis NCED3 showed increased ABA accumulation, higher seed germination rate, better growth and lower water loss under Cd stress [71]. They also exhibited higher antioxidant enzyme activity, which was probably responsible for the reduction in oxidative damage and apoptosis compared to wild-type plants [71]. Moreover, ectopic expression of MhNCED3 in transgenic Arabidopsis thaliana and apple calli showed reduced expression of genes related to Cd2+ uptake (NRAMP, natural resistance-associated macrophage protein, and IRT, iron-regulated transporter) as well as reduced Cd2+ influx and Cd content [13]. In turn, knocking down BGLU10 or BGLU18 reduced endogenous ABA levels, resulting in higher NRT1.5 (nitrate transporter 1.5) levels and lower vacuolar H+-ATPase activity, which in turn led to higher Cd accumulation and sensitivity [72]. When generating transgenic plants with elevated ABA content, the possible undesirable physiological effects of these genetic modifications, such as growth inhibition, premature senescence or reduced photosynthetic efficiency due to prolonged stomatal closure, should also be considered. On the other hand, as highlighted in the discussion, the expression of genes encoding ABA receptors is regulated by the plant, presumably to avoid these undesirable physiological effects of long-term elevated ABA concentrations. In this way, the complex network that regulates the plant’s response to the current ABA concentration becomes as important as the ABA concentration itself and should also be taken into account when developing strategies to increase plant resistance to stress factors such as heavy metals.

4. Materials and Methods

4.1. Plant Material and Experimental Conditions

Seeds of Pisum sativum L. (cv. Iłówiecki) were germinated in moist vermiculite and 12-day-old seedlings were transferred to containers filled with aerated 1/2 Hoagland medium [73]. Nitrogen was added in the form of 4 mM NaNO3. After seven days, the medium was supplemented with CdCl2 (50 µM) or ABA (50 µM). Plants grown in a medium without CdCl2 and ABA served as a control. After 48 h of treatment, the plants (twelve plants per treatment) were harvested and separated into roots and leaves (leaflets plus stipule). The leaves were bulked according to their stage of development (Figure S1). The oldest true leaves were taken from the first and second node from the bottom and labeled as C leaves. Leaves from the third to fifth node were termed B2 leaves. The youngest fully expanded leaves were taken from the sixth node and labeled as B1 leaves, while the youngest unexpanded leaves were labeled as A leaves. Leaf samples were frozen in liquid N2 immediately after harvest and stored at −80 °C until use.
The experiments were carried out in a growth chamber at a humidity of about 60% and light intensity of 250 µE m−1 s−1. The air temperature was 22 °C (16 h) during the day and 19 °C (8 h) at night. The experiment was repeated three times independently, resulting in three independent biological replicates.

4.2. Determination of ABA and Its Conjugates

Free and conjugated forms of ABA were extracted and determined as previously described by Sauter and Hartung [74], Dietz et al. [75] and Watanabe et al. [65] with some modifications. In brief, tissue pulverized in liquid nitrogen was extracted with 10 mM CaCl2 for 24 h in the dark at 4 °C. The ratio of tissue to buffer was 1:7 (w:v). The homogenate was centrifuged at 16,000× g for 30 min at 4 °C. The resulting supernatant was acidified with 0.1 M HCl to pH 3.0 and partitioned three times against equal volumes of ethyl acetate. The combined upper organic fractions containing free ABA were evaporated to dryness using a vacuum centrifuge and taken up in TBS buffer (Tris-buffered saline, 50 mM Tris-HCl, pH 7.8, 0.1 mM MgCl2 and 0.15 M NaCl). The lower aqueous fractions, containing ABA conjugates, were hydrolyzed with 1 M NaOH at 60 °C for 1 h in the dark. After alkaline hydrolysis, the samples were adjusted to pH 3.0 with 1 M HCl, partitioned three times against ethyl acetate, dried and taken up in TBS buffer. The levels of free ABA and ABA released from the conjugates were measured using the Phytodetek enzyme linked immunosorbent assay (ELISA) kit (Agdia, Inc., Elkhart, IN, USA) according to the protocol provided.

4.3. Determination of Aldehyde Oxidase Activity and Protein Content

Extraction of soluble plant proteins was performed in an ice-cold extraction medium containing 250 mM Tris–HCl, pH 8.5, 1 mM EDTA, 10 mM GSH and 2 mM DTT. A ratio of 1 g tissue to 3 mL buffer (1:3, w/v) was used. The homogenate was centrifuged at 16,000× g at 4 °C for 20 min. The resulting supernatant was subjected to native polyacrylamide gel electrophoresis (PAGE) on 7.5% separating gels in a Laemmli buffer system without SDS [76]. After electrophoresis, AO activity was stained as previously described [18] using indole-3-aldehyde as substrate. The relative intensity of the AO activity bands was quantified using NIH Image 1.62 software (Research Services Branch, National Institutes of Health). The total soluble protein content was determined using the Bradford method [77].

4.4. ABA-GE Hydrolyzing Activity Assay

The activity releasing free ABA from its glucose conjugates was determined as previously described [26,65] with slight modifications. In brief, 1 g of frozen tissue was homogenized with 5 mL of lysis buffer (25 mM HEPES, pH 7.0, 250 mM sucrose, 1 mM DTT, 10 mM MgCl2) and centrifuged at 10,000× g at 4 °C for 5 min to remove debris. Subsequently, the resulting supernatant was centrifuged at 100,000× g at 4 °C for 1 h. The microsomal fraction was then resuspended in 0.5 mL of lysis buffer containing 1% (v/v) Triton X-100 and incubated on ice for 30 min. Samples were then diluted 10-fold with lysis buffer, and 0.4 mL aliquots were then used to assay ABA-GE hydrolyzing activity in a 1 mL reaction mixture containing 100 pmol ABA-GE (OlChemim Ltd., Olomouc, Czech Republic) at 37 °C for 1 h. After incubation, the mixtures were diluted 20-fold in TBS buffer, and the amount of ABA released was determined by ELISA as described above.

4.5. RNA Extraction and Gene Expression Analysis

Total RNA was isolated according to Chomczynski and Sacchi [78]. The isolated RNA was treated with DNase I and a total of 4 µg of RNA was reverse transcribed using the Transcriptor First Strand cDNA Synthesis Kit (Roche Diagnostics, Mannheim, Germany) according to the manufacturer’s protocol. Gene expression was analyzed by real-time PCR using a LightCycler® 96 instrument (Roche Diagnostics, Mannheim, Germany). The reaction mixture contained 5 μL SYBR Green I Master Mix (Roche Diagnostics, Mannheim, Germany), 3 μL cDNA template (equivalent to 10 ng total RNA) and 0.5 μM of each primer in a total volume of 10 μL. The thermocycling conditions were as follows: 10 min at 95 °C, 40 cycles of 15 s at 95 °C, 15 s at 62 °C and 15 s at 72 °C. Melting curves (95 °C for 10 s, 65 °C for 1 min and 97 °C for 1 s) were generated for each reaction to ensure the specificity of amplification. The relative expression level of target genes was calculated using the 2−ΔΔCt method [79]. The gene coding for actin was used as an internal control. All primers used for real-time PCR are listed in Table S1. All reactions were performed in at least triplicate for each of the three biological replicates.

4.6. Bioinformatics Analysis of PYL Sequences

A database search of the National Center for Biotechnology Information (http://www.ncbi.nlm.nih.gov; accessed on 3 February 2023) for Pisum sativum PYL-like sequences was performed using the BLAST algorithm. The maximum likelihood tree was constructed using the program PhyML 3.0 and the Shimodaira-Hasegawa-like (SH-like) approximate likelihood ratio test [80].

4.7. Statistical Analyses

Statistical analyses were based on three independent experiments (biological replicates) with three technical replicates for each experiment and are presented as mean  ±  SD. Data were analyzed by a two-way analysis of variance (ANOVA) using leaf development stage and treatment as two parameters. The conformity of the data to a normal distribution was checked using the Shapiro–Wilk test, and the homogeneity of variances in the data sets was confirmed using the Levene test. The significance of the differences between the group means was assessed using the parametric Tukey test. All statistical analyses were performed using Statistica ver. 9.1 software.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/ijms25126582/s1.

Author Contributions

Conceptualization, E.Z.-Z.; methodology, E.Z.-Z. and A.G.; validation, E.Z.-Z.; investigation, E.Z.-Z., A.G. and B.M.; data curation, E.Z.-Z.; writing—original draft preparation, E.Z.-Z. and A.P.; writing—review and editing, E.Z.-Z.; visualization, E.Z.-Z.; supervision, E.Z.-Z. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data are contained within the article and Supplementary Materials.

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. Ali, H.; Khan, E.; Ilahi, I. Environmental chemistry and ecotoxicology of hazardous heavy metals: Environmental persistence, toxicity, and bioaccumulation. J. Chem. 2019, 2019, 6730305. [Google Scholar] [CrossRef]
  2. Singh, V.; Singh, N.; Rai, S.N.; Kumar, A.; Singh, A.K.; Singh, M.P.; Sahoo, A.; Shekhar, S.; Vamanu, E.; Mishra, V. Heavy metalcontamination in the aquatic ecosystem: Toxicity and its remediation using eco-friendly approaches. Toxics 2023, 11, 147. [Google Scholar] [CrossRef] [PubMed]
  3. Uraguchi, S.; Mori, S.; Kuramata, M.; Kawasaki, A.; Arao, T.; Ishikawa, S. Root-to-shoot Cd translocation via the xylem is the major process determining shoot and grain cadmium accumulation in rice. J. Exp. Bot. 2009, 60, 2677–2688. [Google Scholar] [CrossRef] [PubMed]
  4. Parmar, P.; Kumari, N.; Sharma, V. Structural and functional alterations in photosynthetic apparatus of plants under cadmium stress. Bot. Stud. 2013, 54, 45. [Google Scholar] [CrossRef] [PubMed]
  5. Qin, S.; Liu, H.; Nie, Z.; Rengel, Z.; Gao, W.; Li, C.; Zhao, P. Toxicity of cadmium and its competition with mineral nutrients for uptake by plants: A review. Pedosphere 2020, 30, 168–180. [Google Scholar] [CrossRef]
  6. Baruah, N.; Subham, C.M.; Farooq, M.; Gogoi, N. Influence of heavy metals on seed germination and seedling growth of wheat, pea, and tomato. Wat. Air and Soil Poll. 2019, 230, 273–288. [Google Scholar] [CrossRef]
  7. Shanying, H.E.; Yang, X.; Zhenli, H.E.; Baligar, V.C. Morphological and physiological responses of plants to cadmium toxicity: A review. Pedosphere 2017, 27, 421–438. [Google Scholar] [CrossRef]
  8. Ma, Y.; Cao, J.; He, J.; Chen, Q.; Li, X.; Yang, Y. Molecular mechanism for the regulation of ABA homeostasis during plant development and stress responses. Int. J. Mol. Sci. 2018, 19, 3643. [Google Scholar] [CrossRef] [PubMed]
  9. Chen, K.; Li, G.J.; Bressan, R.A.; Song, C.P.; Zhu, J.K.; Zhao, Y. Abscisic acid dynamics, signaling, and functions in plants. J. Integr. Plant Biol. 2020, 62, 25–54. [Google Scholar] [CrossRef]
  10. Kumar, S.; Shah, S.H.; Vimala, Y.; Jatav, H.S.; Ahmad, P.; Chen, Y.; Siddique, K.H.M. Abscisic acid: Metabolism, transport, crosstalk with other plant growth regulators, and its role in heavy metal stress mitigation. Front. Plant Sci. 2022, 13, 972856. [Google Scholar] [CrossRef]
  11. Zhao, Y.; Wang, J.; Huang, W.; Zhang, D.; Wu, J.; Li, B.; Li, M.; Liu, L.; Yan, M. Abscisic-acid-regulated responses to alleviate cadmium toxicity in plants. Plants 2023, 12, 1023. [Google Scholar] [CrossRef] [PubMed]
  12. Han, Y.; Wang, S.; Zhao, N.; Deng, S.; Zhao, C.; Li, N.; Sun, J.; Zhao, R.; Yi, H.; Shen, X.; et al. Exogenous abscisic acid alleviates cadmium toxicity by restricting Cd2+ influx in Populus euphratica cells. J. Plant Growth Regul. 2016, 35, 827–837. [Google Scholar] [CrossRef]
  13. Zhang, W.; Wang, Z.; Song, J.; Yue, S.; Yang, H. Cd2+ uptake inhibited by MhNCED3 from Malus hupehensis alleviates Cd-induced cell death. Environ. Exp. Bot. 2019, 166, 103802. [Google Scholar] [CrossRef]
  14. Leng, Y.; Li, Y.; Ma, Y.H.; He, L.F.; Li, S.W. Abscisic acid modulates differential physiological and biochemical responses of roots, stems, and leaves in mung bean seedlings to cadmium stress. Environ. Sci. Pollut. Res. 2020, 28, 6030–6043. [Google Scholar] [CrossRef] [PubMed]
  15. Hu, B.; Deng, F.; Chen, G.; Chen, X.; Gao, W.; Long, L.; Xia, J.; Chen, Z.H. Evolution of abscisic acid signaling for stress responses to toxic metals and metalloids. Front. Plant Sci. 2020, 11, 909. [Google Scholar] [CrossRef] [PubMed]
  16. Nambara, E.; Marion-Poll, A. Abscisic acid biosynthesis and catabolism. Annu. Rev. Plant Biol. 2005, 56, 165–185. [Google Scholar] [CrossRef] [PubMed]
  17. He, R.; Zhuang, Y.; Cai, Y.; Agüero, C.B.; Liu, S.; Wu, J.; Deng, S.; Walker, M.A.; Lu, J.; Zhang, Y. Overexpression of 9-cis-epoxycarotenoid dioxygenase cisgene in grapevine increases drought tolerance and results in pleiotropic effects. Front Plant Sci. 2018, 9, 970. [Google Scholar] [CrossRef]
  18. Zdunek-Zastocka, E.; Sobczak, M. Expression of Pisum sativum PsAO3 gene, which encodes an aldehyde oxidase utilizing abscisic aldehyde, is induced under progressively but not rapidly imposed drought stress. Plant Physiol. Biochem. 2013, 71, 57–66. [Google Scholar] [CrossRef] [PubMed]
  19. Zdunek-Zastocka, E.; Lips, H.S. Plant molybdoenzymes and their response to stress. Acta Physiol. Plant. 2003, 25, 437–452. [Google Scholar] [CrossRef]
  20. Seo, M.; Koiwai, H.; Akaba, S.; Komano, T.; Oritani, T.; Kamiya, Y.; Koshiba, T. Abscisic aldehyde oxidase in leaves of Arabidopsis thaliana. Plant J. 2000, 23, 481–488. [Google Scholar] [CrossRef]
  21. Omarov, R.; Dräger, D.; Tischner, R.; Lips, H. Aldehyde oxidase isoforms and subunit composition in roots of barley as affected by ammonium and nitrate. Physiol. Plant. 2003, 117, 337–342. [Google Scholar] [CrossRef] [PubMed]
  22. Zdunek-Zastocka, E.; Omarov, R.T.; Koshiba, T.; Lips, H.S. Activity and protein level of AO isoforms in pea plants (Pisum sativum L.) during vegetative development and in response to stress conditions. J. Exp. Bot. 2004, 55, 1361–1369. [Google Scholar] [CrossRef] [PubMed]
  23. Kushiro, T.; Okamoto, M.; Nakabayashi, K.; Yamagishi, K.; Kitamura, S.; Asami, T.; Hirai, N.; Koshiba, T.; Kamiya, Y.; Nambara, E. The Arabidopsis cytochrome P450 CYP707A encodes ABA 8′-hydroxylases: Key enzymes in ABA catabolism. EMBO J. 2004, 23, 1647–1656. [Google Scholar] [CrossRef] [PubMed]
  24. Xu, Z.J.; Nakajima, M.; Suzuki, Y.; Yamaguchi, I. Cloning and characterization of the abscisic acid-specific glucosyltransferase gene from adzuki bean seedlings. Plant Physiol. 2002, 129, 1285–1295. [Google Scholar] [CrossRef]
  25. Zdunek-Zastocka, E.; Grabowska, A. The interplay of PsABAUGT1 with other abscisic acid metabolic genes in the regulation of ABA homeostasis during the development of pea seeds and germination in the presence of H2O2. Plant Sci. 2019, 285, 79–90. [Google Scholar] [CrossRef]
  26. Lee, K.H.; Piao, H.L.; Kim, H.Y.; Choi, S.M.; Jiang, F.; Hartung, W.; Hwang, I.; Kwak, J.M.; Lee, I.J.; Hwang, I. Activation of glucosidase via stress-induced polymerization rapidly increases active pools of abscisic acid. Cell 2006, 126, 1109–1120. [Google Scholar] [CrossRef] [PubMed]
  27. Xu, Z.Y.; Lee, K.H.; Dong, T.; Jeong, J.C.; Jin, J.B.; Kanno, Y.; Kim, D.H.; Kim, S.Y.; Seo, M.; Bressan, R.A.; et al. A vacuolar β-glucosidase homolog that possesses glucose-conjugated abscisic acid hydrolyzing activity plays an important role in osmotic stress responses in Arabidopsis. Plant Cell 2012, 24, 2184–2199. [Google Scholar] [CrossRef]
  28. Burla, B.; Pfrunder, S.; Nagy, R.; Francisco, R.M.; Lee, Y.; Martinoia, E. Vacuolar transport of abscisic acid glucosyl ester is mediated by ATP-binding cassette and proton-antiport mechanisms in Arabidopsis. Plant Physiol. 2013, 163, 1446–1458. [Google Scholar] [CrossRef]
  29. Ng, L.M.; Melcher, K.; Teh, B.T.; Xu, H.E. Abscisic acid perception and signaling: Structural mechanisms and applications. Acta Pharmacol. Sin. 2014, 35, 567–584. [Google Scholar] [CrossRef]
  30. Ma, Y.; Szostkiewicz, I.; Korte, A.; Moes, D.; Yang, Y.; Christmann, A.; Grill, E. Regulators of PP2C phosphatase activity function as abscisic acid sensors. Science 2009, 324, 1064–1068. [Google Scholar] [CrossRef]
  31. Bai, G.; Yang, D.H.; Zhao, Y.; Ha, S.; Yang, F.; Ma, J.; Gao, X.S.; Wang, Z.M.; Zhu, J.K. Interactions between soybean ABA receptors and type 2C protein phosphatases. Plant Mol. Biol. 2013, 83, 651–664. [Google Scholar] [CrossRef]
  32. Fujii, H.; Zhu, J.K. Arabidopsis mutant deficient in 3 abscisic acid activated protein kinases reveals critical roles in growth, reproduction, and stress. Proc. Natl. Acad. Sci. USA 2009, 106, 8380–8385. [Google Scholar] [CrossRef] [PubMed]
  33. Szostkiewicz, I.; Richter, K.; Kepka, M.; Demmel, S.; Ma, Y.; Korte, A.; Assaad, F.E.; Christmann, A.; Grill, E. Closely related receptor complexes differ in their ABA selectivity and sensitivity. Plant J. 2010, 61, 25–35. [Google Scholar] [CrossRef] [PubMed]
  34. Tischer, S.V.; Wunschel, C.; Papacek, M.; Kleigrewe, K.; Hofmann, T.; Christmann, A.; Grilla, E. Combinatorial interaction network of abscisic acid receptors and coreceptors from Arabidopsis thaliana. Proc. Natl. Acad. Sci. USA 2017, 114, 10280–10285. [Google Scholar] [CrossRef] [PubMed]
  35. Li, X.; Li, G.; Li, Y.; Kong, X.; Zhang, L.; Wang, J.; Li, X.; Yang, Y. ABA receptor subfamily III enhances abscisic acid sensitivity and improves the drought tolerance of Arabidopsis. Int. J. Mol. Sci. 2018, 19, 1938. [Google Scholar] [CrossRef] [PubMed]
  36. Santiago, J.; Rodrigues, A.; Saez, A.; Rubio, S.; Antoni, R.; Dupeux, F.; Park, S.Y.; Márquez, J.A.; Cutler, S.R.; Rodriguez, P.L. Modulation of drought resistance by the abscisic acid receptor PYL5 through inhibition of clade A PP2Cs. Plant J. 2009, 60, 575–588. [Google Scholar] [CrossRef] [PubMed]
  37. Zhao, Y.; Chan, Z.; Gao, J.; Xing, L.; Cao, M.; Yu, C.; Hu, Y.; You, J.; Shi, H.; Zhu, Y.; et al. ABA receptor PYL9 promotes drought resistance and leaf senescence. Proc. Natl. Acad. Sci. USA 2016, 113, 1949–1954. [Google Scholar] [CrossRef] [PubMed]
  38. Lee, H.Y.; Jang, G.; Um, T.; Kim, J.K.; Lee, J.S.; Choi, Y.D. The soluble ABA receptor PYL8 regulates drought resistance by controlling ABA signaling in Arabidopsis. Plant Biotechnol. Rep. 2015, 9, 319–330. [Google Scholar] [CrossRef]
  39. Sun, S.; Fan, W.; Mu, Z. The spatio-temporal specificity of PYR1/PYL/RCAR ABA receptors in response to developmental and environmental cues. Plant Signal. Behav. 2017, 12, e1214793. [Google Scholar] [CrossRef] [PubMed]
  40. Harper, J.L. The value of a leaf. Oecologia 1989, 80, 53–58. [Google Scholar] [CrossRef]
  41. Hensel, L.L.; Grbić, V.; Baumgarten, D.A.; Bleecker, A.B. Developmental and age-related processes that influence the longevity and senescence of photosynthetic tissues in Arabidopsis. Plant Cell 1993, 5, 553–564. [Google Scholar] [CrossRef] [PubMed]
  42. Berens, M.L.; Wolinska, K.W.; Spaepen, S.; Ziegler, J.; Nobori, T.; Nair, A.; Krüler, V.; Winkelmüller, T.M.; Wang, Y.; Mine, A.; et al. Balancing trade-offs between biotic and abiotic stress responses through leaf age-dependent variation in stress hormone cross-talk. Proc. Natl. Acad. Sci. USA 2019, 116, 2364–2373. [Google Scholar] [CrossRef] [PubMed]
  43. Kursar, T.A.; Coley, P.D. Nitrogen content and expansion rate of young leaves of rain forest species: Implications for herbivory. Biotropica 1991, 14, 141–150. [Google Scholar] [CrossRef]
  44. Badenes-Perez, F.R.; Gershenzon, J.; Heckel, D.G. Insect attraction versus plant defense: Young leaves high in glucosinolates stimulate oviposition by a specialist herbivore despite poor larval survival due to high saponin content. PLoS ONE 2014, 9, e95766. [Google Scholar] [CrossRef] [PubMed]
  45. Sperdouli, I.; Moustaka, J.; Ouzounidou, G.; Moustakas, M. Leaf age-dependent photosystem II photochemistry and oxidative stress responses to drought stress in Arabidopsis thaliana are modulated by flavonoid accumulation. Molecules 2021, 26, 4157. [Google Scholar] [CrossRef] [PubMed]
  46. Moustaka, J.; Tanou, G.; Adamakis, I.D.; Eleftheriou, E.P.; Moustakas, M. Leaf age-dependent photoprotective and antioxidative response mechanisms to paraquat-induced oxidative stress in Arabidopsis thaliana. Int. J. Mol. Sci. 2015, 16, 13989–14006. [Google Scholar] [CrossRef] [PubMed]
  47. Zdunek-Zastocka, E.; Grabowska, A.; Michniewska, B.; Orzechowski, S. Proline concentration and its metabolism are regulated in a leaf age dependent manner but not by abscisic acid in pea plants exposed to cadmium stress. Cells 2021, 10, 946. [Google Scholar] [CrossRef] [PubMed]
  48. Krupa, Z.; Moniak, M. The stage of leaf maturity implicates the response of the photosynthetic apparatus to cadmium toxicity. Plant Sci. 1998, 138, 149–156. [Google Scholar] [CrossRef]
  49. Drążkiewicz, M.; Tukendorf, A.; Baszyński, T. Age-dependent response of maize leaf segments to cadmium treatment: Effect on chlorophyll fluorescence and phytochelatin accumulation. J. Plant Physiol. 2003, 160, 247–254. [Google Scholar] [CrossRef]
  50. Tang, Y.; Wang, L.; Xie, Y.; Yu, X.; Li, H.; Lin, L.; Liao, M.; Wang, Z.; Sun, G.; Wang, X.; et al. Effects of exogenous abscisic acid on the growth and cadmium accumulation of lettuce under cadmium-stress conditions. J. Environ. Anal. Chem. 2019, 100, 720–731. [Google Scholar] [CrossRef]
  51. Liao, Y.; Tang, Y.; Wang, S.; Su, H.; Chen, J.; Zhang, D.; Wu, J.; Zhou, D.; Yan, M.; Liu, L. Abscisic acid modulates differential physiological and biochemical responses to cadmium stress in Brassica napus. Environ. Pollut. Bioavailab. 2023, 35, 2168216. [Google Scholar] [CrossRef]
  52. Huybrechts, M.; Hendrix, S.; Kyndt, T.; Demeestere, K.; Vandamme, D.; Cuypers, A. Short-term effects of cadmium on leaf growth and nutrient transport in rice plants. Plant Sci. 2021, 313, 111054. [Google Scholar] [CrossRef] [PubMed]
  53. Shah, T.; Khan, Z.; Khan, S.R.; Imran, A.; Muhammad, A.; Ahmad, A.; Ahmad, P. Silicon inhibits cadmium uptake by regulating the genes associated with the lignin biosynthetic pathway and plant hormone signal transduction in maize plants. Environ. Sci. Pollut. Res. 2023, 30, 123996–124009. [Google Scholar] [CrossRef] [PubMed]
  54. Poschenrieder, C.; Gunsé, B.; Barceló, J. Influence of cadmium on water relations, stomatal resistance, and abscisic acid content in expanding bean leaves. Plant Physiol. 1989, 90, 1365–1371. [Google Scholar] [CrossRef] [PubMed]
  55. Farhangi-Abriz, S.; Ghassemi-Golezani, K. The modified biochars influence nutrient and osmotic statuses and hormonal signaling of mint plants under fluoride and cadmium toxicities. Front. Plant Sci. 2022, 13, 1064409. [Google Scholar] [CrossRef] [PubMed]
  56. Sauter, A.; Dietz, K.J.; Hartung, W.A. A possible stress physiological role of abscisic acid conjugates in root-to-shoot signaling. Plant Cell Environ. 2002, 25, 223–228. [Google Scholar] [CrossRef]
  57. Brossa, R.; Pintó-Marijuan, M.; Francisco, R.; López-Carbonell, M.; Chaves, M.M.; Alegre, L. Redox proteomics and physiological responses in Cistus albidus shrubs subjected to long-term summer drought followed by recovery. Planta 2015, 241, 803–822. [Google Scholar] [CrossRef] [PubMed]
  58. Thameur, A.; Ferchichi, A.; López-Carbonell, M. Quantification of free and conjugated abscisic acid in five genotypes of barley (Hordeum vulgare L.) under water stress conditions. S. Afr. J. Bot. 2011, 77, 222–228. [Google Scholar] [CrossRef]
  59. Tao, Q.; Jupa, R.; Liu, Y.; Luo, J.; Li, J.; Kováč, J.; Li, B.; Li, Q.; Wu, K.; Liang, Y.; et al. Abscisic acid-mediated modifications of radial apoplastic transport pathway play a key role in cadmium uptake in hyperaccumulator Sedum alfredii. Plant Cell Environ. 2019, 42, 1425–1440. [Google Scholar] [CrossRef]
  60. Chen, K.; Chen, P.; Qiu, X.; Chen, J.; Gao, G.; Wang, X.; Zhu, A.; Yu, C. Regulating role of abscisic acid on cadmium enrichment in ramie (Boehmeria nivea L.). Sci. Rep. 2021, 11, 22045. [Google Scholar] [CrossRef]
  61. Tan, M.; Cheng, D.; Yang, Y.; Zhang, G.; Qin, M.; Chen, J.; Chen, Y.; Jiang, M. Co-expression network analysis of the transcriptomes of rice roots exposed to various cadmium stresses reveals universal cadmium-responsive genes. BMC Plant Biol. 2017, 17, 194. [Google Scholar] [CrossRef]
  62. Huang, T.L.; Nguyen, Q.T.; Fu, S.F.; Lin, C.Y.; Chen, Y.C.; Huang, H.J. Transcriptomic changes and signaling pathways induced by arsenic stress in rice roots. Plant Mol. Biol. 2012, 80, 587–608. [Google Scholar] [CrossRef]
  63. Zdunek, E.; Lips, S.H. Transport and accumulation rates of abscisic acid and aldehyde oxidase activity in Pisum sativum L. in response to suboptimal growth conditions. J. Exp. Bot. 2001, 52, 1269–1276. [Google Scholar] [CrossRef] [PubMed]
  64. Han, Y.; Watanabe, S.; Shimada, H.; Sakamoto, A. Dynamics of the leaf endoplasmic reticulum modulate β-glucosidase-mediated stress-activated ABA production from its glucosyl ester. J. Exp Bot. 2020, 71, 2058–2071. [Google Scholar] [CrossRef] [PubMed]
  65. Watanabe, S.; Matsumoto, M.; Hakomori, Y.; Takagi, H.; Shimada, H.; Sakamoto, A. The purine metabolite allantoin enhances abiotic stress tolerance through synergistic activation of abscisic acid metabolism. Plant Cell Environ. 2014, 37, 1022–1036. [Google Scholar] [CrossRef]
  66. Ruiz-Partida, R.; Rosario, S.M.; Lozano-Juste, J. An Update on Crop ABA Receptors. Plants 2021, 10, 1087. [Google Scholar] [CrossRef] [PubMed]
  67. Mega, R.F.; Abe, J.S.; Kim, Y.; Tsuboi, K.; Tanaka, H.; Kobayashi, Y.; Sakata, K.; Hanada, H.; Tsujimoto, J.; Kikuchi, S.R.; et al. Tuning water-use efficiency and drought tolerance in wheat using abscisic acid receptors. Nat. Plants 2019, 5, 153–159. [Google Scholar] [CrossRef]
  68. Fan, W.; Zhao, M.; Li, S.; Bai, X.; Li, J.; Meng, H.; Mu, Z. Contrasting transcriptional responses of PYR1/PYL/RCAR ABA receptors to ABA or dehydration stress between maize seedling leaves and roots. BMC Plant Biol. 2016, 16, 99. [Google Scholar] [CrossRef] [PubMed]
  69. Wang, L.; Jäggi, S.; Cofer, T.M.; Waterman, J.M.; Walthert, M.; Glauser, G.; Erb, M. Immature leaves are the dominant volatile-sensing organs of maize. Curr. Biol. 2023, 33, 3679–3689. [Google Scholar] [CrossRef] [PubMed]
  70. Yadav, S.K.; Kumar, V.V.S.; Verma, R.K.; Yadav, P.; Saroha, A.; Wankhede, D.P.; Chaudhary, B.; Chinnusamy, V. Genome-wide identification and characterization of ABA receptor PYL gene family in rice. BMC Genomics 2020, 21, 676. [Google Scholar] [CrossRef]
  71. Zhang, W.; Yang, H.; You, S.; Xu, Y.; Ran, K.; Fan, S. Cloning, characterization and functional analysis of the role MhNCED3, a gene encoding 9-cis-epoxycarotenoid dioxygenase in Malus hupehensis Rehd., plays in plant tolerance to osmotic and Cd2+ stresses. Plant Soil 2014, 381, 143–160. [Google Scholar] [CrossRef]
  72. Wang, T.; Hua, Y.; Chen, M.; Zhang, J.; Guan, C.; Zhang, Z. Mechanism enhancing Arabidopsis resistance to cadmium: The role of NRT1.5 and proton pump. Front. Plant Sci. 2018, 9, 1892. [Google Scholar] [CrossRef] [PubMed]
  73. Hoagland, D.R.; Arnon, D.I. The water culture method for growing plants without soil. Univ. Calif. Agric. Exp. Stn. Circ. 1938, 347, 1–39. [Google Scholar]
  74. Sauter, A.; Hartung, W. Radial transport of abscisic acid conjugates in maize roots: Its implication for long distance stress signals. J. Exp. Bot. 2000, 346, 929–935. [Google Scholar] [CrossRef]
  75. Dietz, K.J.; Sauter, A.; Wichert, K.; Messdaghi, D.; Hartung, W. Extracellular β-glucosidase activity in barley involved in the hydrolysis of ABA glucose conjugate in leaves. J. Exp. Bot. 2000, 346, 937–944. [Google Scholar] [CrossRef]
  76. Laemmli, U.K. Cleavage of structural proteins during the assembly of the head of bacteriophage T4. Nature 1970, 227, 680–685. [Google Scholar] [CrossRef] [PubMed]
  77. Bradford, M.M. A rapid and sensitive method for the quantitation of microgram quantities of protein utilizing the principle of protein dye-binding. Anal. Biochem. 1976, 72, 248–254. [Google Scholar] [CrossRef] [PubMed]
  78. Chomczynski, P.; Sacchi, N. Single-step method of total RNA isolation by a single extraction with an acid guanidinium thiocyanate-phenol-chloroform extraction. Anal. Biochem. 1987, 162, 156–159. [Google Scholar] [CrossRef] [PubMed]
  79. Livak, K.J.; Schmittgen, T.D. Analysis of relative gene expression data using real-time quantitative PCR and the 2−ΔΔ CT method. Methods 2001, 25, 402–408. [Google Scholar] [CrossRef]
  80. Dereeper, A.; Guignon, V.; Blanc, G.; Audic, S.; Buffet, S.; Chevenet, F.; Dufayard, J.F.; Guindon, S.; Lefort, V.; Lescot, M.; et al. Phylogeny.fr: Robust phylogenetic analysis for the non-specialist. Nucleic Acids Res. 2008, 36, W465–W469. [Google Scholar] [CrossRef] [PubMed]
Figure 1. Changes in the concentration of free abscisic acid (A) and its conjugates (B) after 48 h of Cd treatment. Cadmium was applied as 50 µM CdCl2. A, the youngest unexpanded leaves; B1, the youngest fully expanded leaves; B2, fully expanded mature leaves; C, the oldest leaves. Results are the means (±SD) of three biological replicates. Different letters above the columns indicate significant differences between the means (p < 0.05).
Figure 1. Changes in the concentration of free abscisic acid (A) and its conjugates (B) after 48 h of Cd treatment. Cadmium was applied as 50 µM CdCl2. A, the youngest unexpanded leaves; B1, the youngest fully expanded leaves; B2, fully expanded mature leaves; C, the oldest leaves. Results are the means (±SD) of three biological replicates. Different letters above the columns indicate significant differences between the means (p < 0.05).
Ijms 25 06582 g001
Figure 2. Changes in transcript levels of genes involved in ABA metabolism after 48 h of Cd treatment. (A) PsNCED1, (B) PsNCED2, (C) PsAO3, (D) PsABAUGT1. Cadmium was applied as 50 µM CdCl2. The relative mRNA level in each group of leaves was expressed relative to that in A leaves from control plants, which were set to 1 after normalizing to the reference gene. A, the youngest unexpanded leaves; B1, the youngest fully expanded leaves; B2, fully expanded mature leaves; C, the oldest leaves. Results are the means (±SD) of three biological replicates. Different letters above the columns indicate significant differences between the means (p < 0.05).
Figure 2. Changes in transcript levels of genes involved in ABA metabolism after 48 h of Cd treatment. (A) PsNCED1, (B) PsNCED2, (C) PsAO3, (D) PsABAUGT1. Cadmium was applied as 50 µM CdCl2. The relative mRNA level in each group of leaves was expressed relative to that in A leaves from control plants, which were set to 1 after normalizing to the reference gene. A, the youngest unexpanded leaves; B1, the youngest fully expanded leaves; B2, fully expanded mature leaves; C, the oldest leaves. Results are the means (±SD) of three biological replicates. Different letters above the columns indicate significant differences between the means (p < 0.05).
Ijms 25 06582 g002
Figure 3. Activity of Pisum sativim aldehyde oxidase (PsAOγ) and β-glucosidase (PsBGLU, ABA-GE hydrolase) in leaves of the pea plants after 48 h of Cd treatment. Cadmium was applied as 50 µM CdCl2. (A) AO activity was assayed after native PAGE with indole-3-aldehyde as substrate. Each lane of the gel was loaded with 100 µg of proteins. The relative intensity of the PsAOγ isoform activity band in each group of leaves was quantified using ImageJ 1.53e software and expressed relative to that in A leaves from control plants set to 1. A representative zymogram is shown in Figure S2. (B) ABA-GE hydrolase activity was assayed using ABA-GE as substrate. A, the youngest unexpanded leaves; B1, the youngest fully expanded leaves; B2, fully expanded mature leaves; C, the oldest leaves. Results are the means (±SD) of three biological replicates. Different letters above the columns indicate significant differences between the means (p < 0.05).
Figure 3. Activity of Pisum sativim aldehyde oxidase (PsAOγ) and β-glucosidase (PsBGLU, ABA-GE hydrolase) in leaves of the pea plants after 48 h of Cd treatment. Cadmium was applied as 50 µM CdCl2. (A) AO activity was assayed after native PAGE with indole-3-aldehyde as substrate. Each lane of the gel was loaded with 100 µg of proteins. The relative intensity of the PsAOγ isoform activity band in each group of leaves was quantified using ImageJ 1.53e software and expressed relative to that in A leaves from control plants set to 1. A representative zymogram is shown in Figure S2. (B) ABA-GE hydrolase activity was assayed using ABA-GE as substrate. A, the youngest unexpanded leaves; B1, the youngest fully expanded leaves; B2, fully expanded mature leaves; C, the oldest leaves. Results are the means (±SD) of three biological replicates. Different letters above the columns indicate significant differences between the means (p < 0.05).
Ijms 25 06582 g003
Figure 4. The phylogenetic relationship between the PYLs of Arabidopsis thaliana (At), Medicago truncatula (Mt) and Pisum sativum (Ps). The maximum likelihood tree was constructed using PhyML 3.0 software and the Shimodaira-Hasegawa-like (SH-like) test. The tree was displayed using TreeDyn. Numbers above branches indicate bootstrap support values after 100 replicates.
Figure 4. The phylogenetic relationship between the PYLs of Arabidopsis thaliana (At), Medicago truncatula (Mt) and Pisum sativum (Ps). The maximum likelihood tree was constructed using PhyML 3.0 software and the Shimodaira-Hasegawa-like (SH-like) test. The tree was displayed using TreeDyn. Numbers above branches indicate bootstrap support values after 100 replicates.
Ijms 25 06582 g004
Figure 5. Changes in the transcript level of PsPYLs after 48 h of Cd treatment. Cadmium was applied as 50 µM CdCl2. (A) PsPYL1, (B) PsPYL2, (C) PsPYL4, (D) PsPYL8, (E) PsPYL9. The relative mRNA level in individual leaves was expressed relative to that in A leaves of control plants set to 1 after being normalized to the reference gene. A, the youngest unexpanded leaves; B1, the youngest fully expanded leaves; B2, fully expanded mature leaves; C, the oldest leaves. Results are the means (±SD) of three biological replicates. Different letters above the columns indicate significant differences between the means (p < 0.05).
Figure 5. Changes in the transcript level of PsPYLs after 48 h of Cd treatment. Cadmium was applied as 50 µM CdCl2. (A) PsPYL1, (B) PsPYL2, (C) PsPYL4, (D) PsPYL8, (E) PsPYL9. The relative mRNA level in individual leaves was expressed relative to that in A leaves of control plants set to 1 after being normalized to the reference gene. A, the youngest unexpanded leaves; B1, the youngest fully expanded leaves; B2, fully expanded mature leaves; C, the oldest leaves. Results are the means (±SD) of three biological replicates. Different letters above the columns indicate significant differences between the means (p < 0.05).
Ijms 25 06582 g005
Figure 6. Changes in the transcript level of PsPYLs after 24 h of treatment with 50 µM ABA. (A) PsPYL1, (B) PsPYL2, (C) PsPYL4, (D) PsPYL8, (E) PsPYL9. The relative mRNA level in individual leaves was expressed in relation to that in A leaves of control plants, set to 1, after normalization to reference gene. A, the youngest unexpanded leaves; B1, the youngest fully expanded leaves; B2, fully expanded mature leaves; C, the oldest leaves. The results are the means (±SD) of three biological replicates. Different letters above the columns indicate significant differences between the means (p < 0.05).
Figure 6. Changes in the transcript level of PsPYLs after 24 h of treatment with 50 µM ABA. (A) PsPYL1, (B) PsPYL2, (C) PsPYL4, (D) PsPYL8, (E) PsPYL9. The relative mRNA level in individual leaves was expressed in relation to that in A leaves of control plants, set to 1, after normalization to reference gene. A, the youngest unexpanded leaves; B1, the youngest fully expanded leaves; B2, fully expanded mature leaves; C, the oldest leaves. The results are the means (±SD) of three biological replicates. Different letters above the columns indicate significant differences between the means (p < 0.05).
Ijms 25 06582 g006
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Zdunek-Zastocka, E.; Michniewska, B.; Pawlicka, A.; Grabowska, A. Cadmium Alters the Metabolism and Perception of Abscisic Acid in Pisum sativum Leaves in a Developmentally Specific Manner. Int. J. Mol. Sci. 2024, 25, 6582. https://doi.org/10.3390/ijms25126582

AMA Style

Zdunek-Zastocka E, Michniewska B, Pawlicka A, Grabowska A. Cadmium Alters the Metabolism and Perception of Abscisic Acid in Pisum sativum Leaves in a Developmentally Specific Manner. International Journal of Molecular Sciences. 2024; 25(12):6582. https://doi.org/10.3390/ijms25126582

Chicago/Turabian Style

Zdunek-Zastocka, Edyta, Beata Michniewska, Angelika Pawlicka, and Agnieszka Grabowska. 2024. "Cadmium Alters the Metabolism and Perception of Abscisic Acid in Pisum sativum Leaves in a Developmentally Specific Manner" International Journal of Molecular Sciences 25, no. 12: 6582. https://doi.org/10.3390/ijms25126582

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop