Next Article in Journal
The Role of Methionine Restriction in Gastric Cancer: A Summary of Mechanisms and a Discussion on Tumor Heterogeneity
Next Article in Special Issue
Integrated Proteomics and Metabolomics of Safflower Petal Wilting and Seed Development
Previous Article in Journal
Inside the Biology of the β3-Adrenoceptor
Previous Article in Special Issue
Enzyme-Based Biostimulants Influence Physiological and Biochemical Responses of Lactuca sativa L.
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Proteomic and Metabolomic Analysis of the Quercus ilex–Phytophthora cinnamomi Pathosystem Reveals a Population-Specific Response, Independent of Co-Occurrence of Drought

by
Tamara Hernández-Lao
,
Marta Tienda-Parrilla
,
Mónica Labella-Ortega
,
Victor M. Guerrero-Sánchez
,
María-Dolores Rey
,
Jesús V. Jorrín-Novo
* and
María Ángeles Castillejo-Sánchez
*
Agroforestry and Plant Biochemistry, Proteomics and Systems Biology, Department of Biochemistry and Molecular Biology, University of Cordoba, UCO-CeiA3, 14014 Cordoba, Spain
*
Authors to whom correspondence should be addressed.
Biomolecules 2024, 14(2), 160; https://doi.org/10.3390/biom14020160
Submission received: 16 November 2023 / Revised: 18 January 2024 / Accepted: 25 January 2024 / Published: 29 January 2024

Abstract

:
Holm oak (Quercus ilex) is considered to be one of the major structural elements of Mediterranean forests and the agrosilvopastoral Spanish “dehesa”, making it an outstanding example of ecological and socioeconomic sustainability in forest ecosystems. The exotic Phytophthora cinnamomi is one of the most aggressive pathogens of woody species and, together with drought, is considered to be one of the main drivers of holm oak decline. The effect of and response to P. cinnamomi inoculation were studied in the offspring of mother trees from two Andalusian populations, Cordoba and Huelva. At the two locations, acorns collected from both symptomatic (damaged) and asymptomatic (apparently healthy) trees were sampled. Damage symptoms, mortality, and chlorophyll fluorescence were evaluated in seedlings inoculated under humid and drought conditions. The effect and response depended on the population and were more apparent in Huelva than in Cordoba. An integrated proteomic and metabolomic analysis revealed the involvement of different metabolic pathways in response to the pathogen in both populations, including amino acid metabolism pathways in Huelva, and terpenoid and flavonoid biosynthesis in Cordoba. However, no differential response was observed between seedlings inoculated under humid and drought conditions. A protective mechanism of the photosynthetic apparatus was activated in response to defective photosynthetic activity in inoculated plants, which seemed to be more efficient in the Cordoba population. In addition, enzymes and metabolites of the phenylpropanoid and flavonoid biosynthesis pathways may have conferred higher resistance in the Cordoba population. Some enzymes are proposed as markers of resilience, among which glyoxalase I, glutathione reductase, thioredoxin reductase, and cinnamyl alcohol dehydrogenase are candidates.

1. Introduction

Invasion by exotic pests and pathogens, together with global change drivers such as climate change, is causing forest decline worldwide, and this is increasing at an unprecedented rate [1,2]. The Mediterranean Basin is considered to be among the regions most susceptible to global change, and climate models predict a 2–5 °C increase in temperature and a 30% reduction in annual rainfall by the end of the 21st century in this region [3,4]. In addition, exotic pathogens, particularly those belonging to the genus Phytophthora, are causing devastating epidemics in this area. However, it is uncertain how the simultaneous and interactive effects of exotic pathogens and a drier climate will affect the regeneration dynamics of Mediterranean forests [5,6]. Most Phytophthora species are polyphagous with a range of host plants. Many Phytophthora species, such as Phytophthora infestans, P. cinnamomi, and P. ramorum, are destructive plant pathogens that cause severe crop losses and tree declines worldwide [2,5,6,7]. Phytophthora cinnamomi is one of the most aggressive pathogens of woody species [5,8]; it causes rot root and destroys the fine roots of the hosts, impeding nutrient and water uptake, with the consequent defoliation, loss of vigor, and even death of infected trees. However, the presence of multiple Pytophthora species (P. cinnamomi, P. quercina, and P. gonapodyides) in the same place can result in a faster decline of holm oak forests [9]. Phytophthora cinnamomi has been ranked in the top 10 oomycete plant pathogens based on scientific and economic importance [7]. This pathogen has been detected in 15 biodiversity hotspots, including the Mediterranean Basin [10].
Evergreen oaks such as holm oak (Quercus ilex) and cork oak (Quercus suber) are considered to be the major structural elements of Mediterranean forests and the agrosilvopastoral Spanish “dehesa” or Portuguese “montado”, making them outstanding examples of the ecological and socioeconomic sustainability of forest ecosystems [11,12]. Quercus ilex dominates the Mediterranean Basin, covering more than 6 million ha [13,14]. The heterozygosity and allelic richness of this species may explain its wide ecological reach and ecophysiological adaptability to extreme conditions [15,16,17]. However, the species is threatened by several factors associated with anthropogenic activity, such as the overexploitation and poor regeneration of livestock, and the combination of biotic and abiotic stresses, such as drought and high temperatures, together with the presence of invasive pathogens, causing so-called decline syndrome [18,19,20]. The soil-borne pathogen P. cinnamomi is considered to be one of the main drivers of holm oak decline [21,22,23,24]. It is predicted that global climate change will increase the incidence of P. cinnamomi in forest and crop species, promoting the extinction of endemic species in vulnerable areas [5,25]. The progressive loss of resilience revealed for holm oak might have to do with the timing of drought events, which, together with increased infestation by P. cinnamomi, will likely undermine the holm oak domain [26]. In declined areas, the presence of healthy (asymptomatic) trees close to diseased (symptomatic) ones has been observed [27,28]. Healthy trees can be considered escape individuals or elite genotypes based on the resiliency of their phenotype to adverse conditions. The contribution of genetic and epigenetic factors to intra- and inter-population Q. ilex phenotypic variability remains unknown, and to date, there have not been many molecular studies addressing this issue.
The main changes in plant status caused by P. cinnamomi infection have been related to physiological responses, such as stomatal closure, photosynthesis rate, and water imbalance [29,30,31]. As reported by Sghaier-Hammami et al. [29], the response of Q. ilex seedlings to P. cinnamomi resembles the drought stress response, with differences between provenances; a general decrease in proteins related to photosynthesis and an increase in starch biosynthesis were observed. A differential response to P. cinnamomi was observed between Q. suber and Q. variabilis upon using a combined proteomic and metabolomic approach [32]. The biggest changes in the leaf proteome included increased abundance of peroxidases, superoxide dismutases, and glutathione S-transferases in Q. variabilis, which probably contribute to decreased susceptibility to P. cinnamomi.
The effect of P. cinnamomi in combination with water deprivation on Q. ilex seedlings has also been studied at the phenotypic, physiological, biochemical, and molecular levels [30,33,34]. Previous studies demonstrated that drought increases susceptibility to P. cinnamomi in Q. ilex seedlings [9,30,33]. Ruiz-Gomez et al. [33] reported that the root mass fraction of Q. ilex seedlings was significantly reduced by P. cinnamomi infection, altering the growth pattern. However, the plants could not recover from the physiological effects of infection when the root rot coincided with water stress.
The combination of drought and P. cinnamomi was demonstrated to have a synergistic effect on Q. ilex seedlings from three contrasting Andalusian (Spanish) populations [34]. The authors reported that the easternmost population was the most susceptible to the combined stress, with a high proportion of stress-related proteins identified using a proteomic approach [34]. The proteins aldehyde dehydrogenase, glucose-6-phosphate isomerase, 50S ribosomal protein L5, and α-1,4-glucan-protein synthase were proposed as putative markers of resilience to the decline syndrome.
In order to elucidate the metabolic pathways involved in resistance against P. cinnamomi, the effect of inoculation, in well-watered and non-watered holm oak seedlings, was studied from morphophysiological and molecular (proteomics and metabolomics) perspectives. For this purpose, the offspring of mother trees, both symptomatic (with visual damage symptoms) and asymptomatic (without visual damage symptoms), from two Andalusian populations, Cordoba and Huelva, were surveyed. The results were compared to those obtained previously in similar Quercus studies. From the present work, a list of candidate genes is proposed as putative markers of resistance against P. cinnamomi to be used in breeding programs for resilience.

2. Materials and Methods

2.1. Plant Material

Quercus ilex mother trees from two populations, Huelva (Hu; Santa Olalla del Cala and Aroche) and Córdoba (Co; Hinojosa del Duque and El Viso), were surveyed (Table S1, Figure S1). In these two areas, the presence or absence of P. cinnamomi has been tested through soil baiting and morphological characterization [24]. Acorns from symptomatic (with visual damage symptoms) and asymptomatic (without visual damage symptoms) individuals were collected in autumn 2020, their surface was cleaned with 2.5% bleach solution, and floating acorns were discarded. Then, acorns were extensively washed again with tap water and blotted dry. To obtain a uniform germination rate, the pericarp was removed and the distal half of the cotyledon was cut out [35]. Germination was carried out in darkness at 25 °C in plastic trays (28 cm × 7 cm × 18 cm, about 60 acorns per tray) on a bed of perlite flooded with tap water and covered with a sheet of moistened filter paper. Seven days after imbibition, germinated seeds (with roots reaching 5–6 cm in length) were sown individually in plastic pots (3 L) using perlite as the substrate (Gramoflor GmbH & Co, Vechta, Germany). Sown seedlings were transferred to a climate-controlled greenhouse for growth under the following conditions: 25 ± 10 °C and 60 ± 10% air humidity, a 11/13 h photoperiod, 900 μmol (photons) m−2 s−1 light. All pots were watered with 200 mL tap water every 2 days and once a week with Hoagland solution [36] until plants reached 6 months old.

2.2. Experimental Design

Six-month-old seedlings were subjected to four treatments: (1) control (C; irrigation to field capacity, non-inoculated with P. cinnamomi), (2) drought (D; no irrigation, non-inoculated with P. cinnamomi), (3) inoculation (I; irrigation, inoculated with P. cinnamomi and irrigated), and (4) combined stress (D × I, inoculated with P. cinnamomi and non-irrigated) (Table S2).
Twelve seedlings with similar morphological characteristics in terms of height and number of leaves were selected per population (Hu and Co), adult tree (with and without damage), and treatment (C, D, I, and D × I) to perform the experiment. The P. cinnamomi strain (P90) was isolated from Q. ilex roots in Puebla de Guzmán (Huelva, Spain) and provided by Prof. Rafael M. Navarro Cerrillo [12,24,33,37]. The treatments were performed as described by Ruiz-Gómez et al. [33] and San-Eufrasio et al. [34]. Briefly, inoculation with P. cinnamomi was performed via root immersion for 10 min in carrot–agar (CA) liquid medium at a concentration of 43 chlamydospores/μL [33]. Roots of control seedlings were also immersed in sterile CA liquid without P. cinnamomi. After inoculation, seedlings were transplanted into pots with fresh perlite and flooded for 48 h. Then, excess water was removed before drought treatment. Drought was imposed by withholding water for 28 days [38]. The non-drought treatments included watering with 200 mL tap water every 2 days and once a week with Hoagland solution [36]. The presence of P. cinnamomi in the inoculated plants was confirmed on day 12 of the experiment by using root segments (<2 mm thick, ~1 cm long) placed in Petri dishes of selective medium (PARPBH), as described Ruiz-Gomez et al. [33] and San-Eufrasio et al. [34].

2.3. Morphological and Physiological Measurements

Leaf chlorosis, wilting, and senescence were visually observed throughout the experiment. Damage symptoms were quantified every three days according to an empirical scale described by San-Eufrasio et al. [38]: 0 = no leaves showing symptoms; 1 = one or two leaves showing slight drought symptoms (necrosis along edges and/or veins, changes in color of foliage (light green, yellow, or brown), and/or irregular spot changes); 2 = most leaves showing slight drought symptoms but one or two leaves still not showing symptoms; 3 = all leaves showing drought symptoms but they are not severe; 4 = all leaves showing severe drought symptoms (leaves with a totally dry yellow aspect); and 5 = whole seedling showing wilting and/or falling of leaves.
Quantum yield of photosystem II (Qy) was measured with a FluorPen FP100 portable leaf fluorimeter from Photon Systems Instruments (Drasiv, Czech Republic) every 3 days throughout the experiment. Three seedlings per treatment per population were selected to perform Qy measurements, always using the same three youngest fully expanded leaves of each plant, in the early morning when the leaves were adapted to nighttime darkness, according to San-Eufrasio et al. [38].
Seedlings with all leaves exhibiting severe symptoms (classified as 4–5 on the damage scale) and Qy values near 0 were considered to be dead.

2.4. Protein Extraction and GeLC-MSMS Analysis

Proteomic analysis was performed on leaf tissue from the offspring of asymptomatic mother trees. Leaves were sampled when chlorophyll fluorescence decreased to values in the 0–75% range with respect to the control, with a mean value of 35% (which occurred on day 12), in plants subjected to stress. Healthy leaves from three biological replicates per treatment and population were collected, washed with distilled water, dried with paper, and frozen in liquid nitrogen. Proteins were extracted from leaf tissue (300 mg) using the TCA/acetone-phenol protocol [39] and solubilized in a solution containing 7 M urea, 2 M thiourea, 4% (w/v) 3-[(3-cholamidopropyl)dimethylammonio]-1-propanesulfonate (CHAPS), 0.5% (w/v) Triton X-100, and 100 mM DTT. Protein extracts were then quantified via the Bradford method using bovine serum albumin (BSA) as the standard [40].
Extracted proteins (80 μg) were subjected to SDS-PAGE on 12% polyacrylamide gel (8.6 × 6.7 cm2) in a Mini-PROTEAN Cell (Bio-Rad, Hercules, CA, USA). The gel was run at 80 V and stopped when the bromophenol blue had advanced 0.5 cm into the resolving gel. The gel was stained with Coomassie brilliant blue R-250, and the resulting unique band was cut from the gel with a scalpel and transferred to individual 1.5 mL tubes for trypsin digestion and mass spectrometry analysis [41]. MS analysis was conducted at the Proteomics Facility for Research Support Central Service (SCAI) of the University of Cordoba (Spain) using a Thermo Scientific Orbitrap Fusion Tribrid mass spectrometer operated in positive ion mode. The specific settings used in the LC–MS/MS analysis are described elsewhere [42].

2.5. Protein Identification and Quantification

The raw data were processed using Proteome Discoverer v.2.3 software from Thermo Scientific. The SEQUEST engine was used to search MS2 spectra against the FASTA Quercus_database obtained from the translation of the Q. ilex transcriptome [43,44]. A maximum of two missed cleavages of trypsin was used in all searches. Precursor mass tolerance was set at 10 ppm, fragment ion mass tolerance at 0.1 Da, and charge state at +2 or greater. Peptides were filtered to 1% of the false discovery rate (FDR) and classified into proteins according to the law of parsimony.
The parameters for protein confidence identification were set to at least 2 matching peptides, a minimum score of 2, and sequence coverage mostly greater than 10%. Proteins were quantified in relative terms from the peak areas for precursor ions (average of the three strongest peptide ion signals) [45]. Raw data were deposited in the ProteomeXchange Consortium via PRIDE [46], under the identifier PXD046909. Protein values were normalized taking into account the relative protein abundance between samples using the sum of the peak area values for each sample (Table S3). Consistent values for at least three biological replicates of the same condition were considered for further statistical analysis. Then, proteins were categorized by function from their FASTA sequences using the online tool Mercator v.3.6 (MapMan; accessed on 10 July 2023) [47].

2.6. Metabolite Extraction and LC-MS Analysis

The metabolomic analysis was performed at the same sampling time as the proteomics analysis (day 12), with seedlings from asymptomatic Co and Hu mother trees subjected to P. cinnamomi inoculation without irrigation. Metabolites were extracted from freeze-dried leaf powder. Briefly, a buffer containing 1200 μL of cold ethanol/water (80:20) was added to 30 mg of leaf powder, and tissue disruption was driven by maceration with a pistil, followed by vortexing (10 s) and sonication (ultrasonic bath, 40 kHZ for 10 min). After centrifugation (16,000× g, 4 °C, 6 min), the supernatant was vacuum dried at 30 °C (Eppendorf 5301 Vacufuge Concentrator Plus, Eppendorf, Leicestershire, UK) and reconstituted in 0.5 mL of 50% methanol containing 0.1% of formic acid, centrifuged (20,000× g, 10 min), and filtered through 0.22 μm PTPE membranes (Thermo Fisher Scientific, Courtaboeuf, France). The filtrate was collected in 1.5 mL LC/MS certified sample vials.
All analyses were performed using a liquid chromatography system consisting of a binary UHPLC Dionex Ultimate 3000 RS connected to a Q Exactive Plus Hybrid Quadrupole–Orbitrap mass spectrometer (Thermo Fisher Scientific, Bremen, Germany), which was equipped with a heated-electrospray ionization probe (HESI-II). Chromatographic separations were performed using an Acquity UPLC BEH C18 column (2.1 × 100 mm, 1.7 µm) (Waters). The column was maintained at 40 °C and eluted under the following conditions: 5% B for 1 min, linear gradient from 5% to 100% in solvent B for 9 min, isocratic at 100% B for 2 min, return to initial conditions, 5% B for 3 min. A flow rate of 0.5 mL/min was used. Eluent A was 0.1% formic acid in water and eluent B was 0.1% formic acid in methanol. Injection volume was 5 µL.
MS detection was performed with the Q Exactive Orbitrap mass spectrometer operating in positive and negative polarities. HESI source parameters in positive mode were as follows: spray voltage of 3.5 kV; S-lens RF level of 50; capillary temperature of 320 °C; sheath and auxiliary gas flow of 60 and 25, respectively (arbitrary units); and probe heater temperature of 400 °C. For negative ion mode, all parameters remained the same, except that the spray voltage was set to −3.0 kV. Xcalibur v.4.3 software was used for instrument control and data acquisition. Full Scan MS mode was used at a resolution of 70,000 (full width half maximum (FWHM) at m/z 200) and data-dependent acquisition (DDA) MS2 mode was used at resolutions of 70,000 and 17,500 (FWHM at m/z 200) for Full Scan and Product Ion Scan, respectively, fragmenting the five most abundant precursor ions per MS scan (Top5). Full Scan MS and DDA-MS2 were used in positive and negative modes, and the mass range used for both experiments was 70–1050 m/z.

2.7. Metabolite Identification and Data Processing

Data were exported for analysis by Compound Discoverer v3.2 software (Thermo Fisher Scientific, Bremen, Germany), in which MS data treatment, alignment, peak selection, deconvolution, normalization, and annotation were carried out. Alignment was performed using a retention time with a maximum shift of 0.3 min and a mass tolerance of 3 ppm. Metabolites were quantified in relative terms considering the area of the corresponding chromatographic peaks of the MS1 precursor ion. Neutral masses obtained in positive and negative modes were evaluated to avoid duplicates (neutral mass in different modes and similar retention time) while retaining the most intense peaks. Metabolite values were normalized taking into account the relative abundance between samples, using the sum of the peak area for each sample. Values consistently present in at least three biological replicates of the same condition were considered for further statistical analysis. A table was generated that lists the abundance of metabolites in the samples (Table S4). Metabolite annotations were developed using DDA-MS2 similarity and the formula or exact mass searched in mzCloud and ChemSpider, respectively. Finally, annotations of the ions of interest were manually reviewed and classified into metabolic pathways (KEGG database; accessed November 2023) [48] and chemical families (ClassyFire; accessed on 15 November 2023) [49]. Raw data were deposited in the NIH Common Fund’s National Metabolomics Data Repository (NMDR) on the Metabolomics Workbench website (accessed on 12 December 2023) [50]. The data can be accessed directly via DataTrack ID: 4480.

2.8. Statistical Analysis

The area under the Qy curve was calculated [38] and data were analyzed using the Kruskal–Wallis test (nonparametric one-way analysis of variance). Means were separated using Dunn’s test with a probability level of 0.05. Statistical analyses were performed using STATISTIX 10.0 software (Analytical Software, Tallahassee, FL, USA).
Proteomics and metabolomics statistical analyses were performed using three biological replicates per treatment and population. Multivariate analysis (principal component analysis (PCA)) was performed for both proteomics and metabolomics using the FactoMineR package in R v4.2.1 [51]. The non-parametric Kruskal–Wallis test was applied to determine statistically variable proteins and metabolites between treatments using the stats package in R [52]. Proteins and metabolites showing significant differences (p ≤ 0.05) that were up-accumulated under the different stress conditions were used for downstream analysis. Venn diagrams were generated using ggvenn function from R package ggven [53] to visualize unique and common proteins and metabolites between populations with the same treatment and between treatments for each population.

2.9. Integrative Analysis of Proteomics and Metabolomics Data

Pathway enrichment analysis was carried out to investigate the pathways significantly activated under P. cinnamomi inoculation. For this, the significantly up-accumulated proteins and metabolites specific to and common between populations and treatments were manually mapped to their respective pathways using the Kyoto Encyclopedia of Genes and Genomes (KEGG) database (accessed on 14 November 2023) [48]. For this, the EC number for enzymes and KEGG ID for metabolites were used.
Multi-omics factor analysis (MOFA) is a computational method for discovering the principal sources of variation in multi-omics datasets. This analysis infers a set of hidden or latent factors that capture the biological and technical sources of variability [54]. Proteomic and metabolomic data were processed and integrated using the MOFA2 package (version 1.10.0) in R (version 4.3.1). To prepare for model training, two sets of the combined stress-regulatory layers were used: proteins and metabolites. Model training was carried out using the following options: maxiter = 1000, convergence_mode = slow.

3. Results and Discussion

The effects of and responses to P. cinnamomi were analyzed in offspring from holm oak mother trees in the Hu and Co populations (Table S1, Figure S1). They corresponded to declined and non-declined areas from the two locations, with the presence of the pathogen in the soil from the declined areas confirmed. In both locations, acorns were collected from trees that both showed and did not show damage symptoms (Figure S1). Damage symptoms included dark brown branches and around 40% defoliation. Symptomatic damaged trees also showed lower photosynthetic efficiency than asymptomatic ones (leaf fluorescence values of 0.8 and below 0.5 for damaged and non-damaged trees, respectively).
According to the experimental design, we evaluated and compared the response to P. cinnamomi in offspring based on the individual (genotype), provenance, coexistence (or not) with the pathogen, and health status (with or without damage symptoms). A similar experiment was conducted by Vivas et al. [55] using different provenances. They observed a higher probability of survival for seedlings from P. cinnamomi-infected trees than seedlings from non-infected trees, particularly seedlings with reduced growth. As P. cinnamomi and drought are the main causes of decline syndrome [33,34], as well as unpredictable consequences in climate change scenarios [1], the inoculation experiment was performed with well-watered and non-watered seedlings (corresponding to a soil matrix potential of 0 and −33 kPa at the end of the experiment for control watered and non-watered seedlings, respectively). During the 16-day experiment, damage symptoms, mortality, and the quantum yield of photosystem II (Qy) were evaluated. Proteomic and metabolomic analyses were performed with the offspring from the asymptomatic non-damaged mother trees of both populations on day 12, when leaf chlorophyll fluorescence decreased to an average of 35% of the initial value in plants subjected to the treatments relative to the control plants. The inoculation of plants under both water regimes resulted in successful infection of the root system in seedlings from both symptomatic and asymptomatic offspring, as revealed by visual and microscopic observation of P. cinnamomi mycelium in isolated root fragments sown in selective PARPBH medium (Figure S2) [56].

3.1. Seedling Damage Symptoms, Mortality, and Leaf Fluorescence

Leaf damage symptoms (chlorosis, necrosis, and wilting) and mortality depended on the individual and the treatment (Figure S3). All offspring from Hu mother trees, in all inoculated treatments, showed 100% mortality on day 16 (Figure 1). The mortality rate of offspring from asymptomatic Co trees was considerably lower than that of symptomatic trees. The rates for irrigated and non-irrigated inoculated treatments were 22% and 33% for the former, and 50% and 90% for the latter.
In general, mortality was higher for the Hu than the Co population, suggesting that the latter has higher resistance to P. cinnamomi. This difference was clearly observed when evaluating mortality at the midpoint of the experiment (Figure 1a,b), when the following comparative levels of resistance were found: Hu_symptomatic < Co_symptomatic < Hu_asymptomatic < Co_asymptomatic. This confirms the higher resistance of asymptomatic than symptomatic genotypes in both provenances. This finding differs from that reported by Vivas et al. [55]; in that study, resistance was higher in the offspring of infected than non-infected mother trees. In general, withholding water had a small effect at 12 days, when leaves were sampled for proteomic analysis (mortality rate lower than 30% for Hu population and around 40% for Co) (Figure 1a,b). In a previously published similar experiment, the drought effect was observed at later times [57]. This is because, at least for the two Hu individuals, the main effect observed was due to the inoculation. For the Co population, withholding water increased the rate of mortality of the offspring of symptomatic individuals, but not those of asymptomatic trees (Figure 1a). These data confirm the complexity of the plant–pathogen interaction and the resulting phenotype, determined by genetics (maternal inheritance), as can occur in the Co population; epigenetics [58,59]; or environmental factors (presence or lack of the pathogen in the soil, among other factors). As the density of the inoculum in the soil of the mother trees and the father of the offspring are unknown, corresponding to an allogamous species, it is only possible to speculate on resistance and its inheritance.
Leaf fluorescence is an estimating parameter for the quantum yield of photosystem II (Qy) and has been used as a parameter for the response to stress in plants [60,61,62]. Its value in the control plants was around 0.7 (Figure 1c,d). Inoculation caused a decrease in fluorescence values, and this effect was more apparent in Hu than Co. A significant decrease was observed due to the effect of withholding water and inoculating in the symptomatic Co offspring (Figure 1c), while there were no differences between symptomatic and asymptomatic Hu seedlings (Figure 1d). These data confirm the previous hypothesis of higher resistance to oomycetes in the Co population than the Hu population and between individuals within the Co population.

3.2. Proteomic Analysis

Proteomic analysis was performed with the leaf tissue of seedlings from asymptomatic mother trees of both populations under the control (well watered and non-inoculated) and P. cinnamomi-inoculated (watered and non-watered) treatments. The leaves were sampled on day 12, when chlorophyll fluorescence on the leaves of the inoculated plants had decreased on average by 35% with respect to the control.
The average protein extraction yield from the leaves was 2.7 mg/g fresh weight, similar to that obtained from other holm oak provenances [63], with no significant differences between samples. For the shotgun analysis, 80 µg of protein from each sample was analyzed, allowing the identification of 3446 total protein species (2735 for Co and 3019 for Hu). The raw data were filtered for confident identification and quantification. Proteins with two or more peptides and a score higher than 2 that were consistently present in all three replicates in at least one condition were selected. This resulted in 2565 total proteins being confidently identified, 1590 in Co and 1444 in Hu individuals, with 1334 common to both (Table 1, Table S3). These data confirm the great variability commonly found in Q. ilex, with the protein profile depending on the genotype [64]. Two-dimensional PCA explained 40 and 43% of the total variability in Co and Hu, respectively (Figure 2a,b). PC1 (27.2%) correlated to some extent with the control, drought, and inoculation treatments in Co seedlings; on the contrary, it did not correlate with treatments in the Hu population.
The dataset of confident proteins was then subjected to the Kruskal–Wallis statistical test, which revealed 600 and 525 proteins for Co and Hu, respectively, with 350 common to both and significant differences between treatments (D, I, and D × I) compared to the control (Table 1). Variable proteins were classified into 14 main functional groups (Figure S4): carbohydrate, amino acid, lipid, secondary, and nucleotide metabolism; photosynthesis; stress; redox; transcription/translation; signaling; transport, folding, sorting, and degradation; development; and cellular processes. The variable up-accumulated proteins for Co and Hu, respectively, were 33 and 20 in response to drought, 49 and 61 in response to P. cinnamomi with watering, and 43 and 65 in response to P. cinnamomi without watering (Table 1, Figure S4a,b). Regarding down-accumulated proteins, the largest proportions were photosynthesis and folding, sorting, and degradation, specifically in the Hu population (Figure S4c,d).
Among the variable proteins, as shown in Table 2 and Figure 3, 182 were up-accumulated in response to stress compared to the control plants. The pattern of these proteins depended on the genotype and treatment. There were more treatment-specific proteins for Hu than Co (69 vs. 59) (Figure 3a,b, Table 2). Regarding common proteins between treatments, 31 were found for Co and 37 for Hu, and 14 were common to both (Figure 3c, Table 2). No common proteins that were represented more in the combined stress than the inoculated groups were found between the two populations. Among the 14 common proteins, the most represented group was carbohydrate metabolism, with 7 proteins: chloroplastic fructose-1,6-bisphosphatase, phosphoglycerate mutase, beta-xylosidase/alpha-L-arabinofuranosidase 2, beta-galactosidase, pyruvate dehydrogenase E1 component subunit alpha mitochondrial, and phosphoenolpyruvate carboxykinase (ATP) 1. Some studies have described the importance of sugars in plant defense against biotic and abiotic stresses [65]. Carbohydrates can also provide materials for the synthesis of defense compounds [66]. A balance between glycolysis and gluconeogenesis was reported in Q. ilex seedlings in response to P. cinnamomi [29]. Beta-xylosidase/alpha-L-arabinofuranosidase 2 and beta-galactosidase are cell wall proteins that play crucial roles in wall modification and the defense response against fungi, and function in the context of water deficit [67]. Two thaumatin-like proteins (TLPs), TLP1 and TLP1a, were also common to both populations (Table 2). TLPs are pathogenesis-related-5 (PR-5) proteins involved in the stress response. Studies of in vitro antifungal activity in Picea likiangensis against the pathogenic fungus Lophodermium piceae provided strong evidence for the significant role of these proteins in defense [68]. Among the stress proteins, ornithine aminotransferase (OAT), a protein involved in proline synthesis, was also found to be accumulated in both populations. The accumulation of proline is a well-documented mechanism that improves water stress tolerance in plants, as evidenced by numerous studies [69,70].
Regarding specific proteins, more up-accumulated enzymes were identified in the Hu population than the Co population (92 vs. 76). The most abundant functional groups of proteins accumulated in Hu were transcription/translation; folding, sorting, and degradation; and carbohydrate metabolism. Among the transcription/translation group, we found two chloroplast ribosomal proteins already described in previous studies as being related to drought tolerance or the response to combined P cinnamomi–drought stress in holm oak: the 50S ribosomal proteins L17 and L22. Many of the 50S ribosomal proteins have been shown to be positively regulated in response to abiotic stress to compensate for damage to photosynthetic proteins in response to drought [34,71]. The 60S ribosomal proteins L6, L13-1, L13a-2, and L21-1 and ubiquitin-60S ribosomal protein L40 have also been shown to accumulate in response to the pathogen. Transcriptomic and proteomic analyses showed an increase in 60S ribosomal protein in Q. ilex seedlings in response to drought [72] and to combined P. cinnamomi–drought stress [34].
Among the folding, sorting, and degradation group, chaperones were the most represented. Heat shock proteins (HSPs) are ubiquitous proteins initially characterized in terms of their response to heat shock, but are now recognized to be induced by a wide range of stressors, including exposure to cold, UV light, wounds, tissue remodeling, and biotic stresses [73]. HSPs have also been related to biotic and abiotic stress response in Q. ilex [34,74]. Other chaperones identified were DnaJ A6, DnaK, ClpB, Cpn60, and T-complex protein 1 subunit beta. ClpB has already been found to increase in Q. ilex under drought conditions [74]. DnaJ proteins alone or in association with HSP70, such as chaperone protein DnaK, are involved in protective mechanisms to rapidly and effectively repair PSII damaged by environmental stress [75].
Transport proteins, such as TOC75 and the translocon on the outer membrane of the chloroplast 64 protein, were also found to be accumulated in the Hu population in response to the pathogen. The system comprising a translocon at the outer chloroplast envelope (TOC) and a translocon at the inner chloroplast envelope (TIC) mediates the import of the vast majority of nuclear-encoded plastid proteins from the cytoplasm [76]. The regulation of TOC–TIC activities is essential in the dynamic remodeling of the organelle proteome, which is required to coordinate plastid biogenesis with developmental and physiological events. Importing photosynthetic proteins and balancing the stoichiometry of nuclear- and chloroplast-encoded subunits of the multisubunit photosynthetic apparatus are critical for the maintenance and repair of the photosynthetic apparatus under stress [77]. In addition, the V-type proton ATPase, a proton pump that contributes to cytosolic pH homeostasis and energizes transport processes across endomembranes of the secretory pathway, is crucial in the response to abiotic and biotic stresses [78]. Two subunits of this protein (A and C) were identified to be involved in the response to P. cinnamomi, with the latter significantly more represented in the combined stress groups (Table 2). This protein was previously identified to be involved in Q. ilex in response to P. cinnamomi [34]. In addition, the carotenoid cleavage dioxygenase has an essential role in the response to osmotic stress [79].
Another less represented group of proteins found to be accumulated in the Hu population were stress response proteins snakin-2 and temperature-induced lipocalin-1. Snakins are host defense peptides that can inhibit the growth of various bacteria and fungi at low concentrations [80]. Lipocalins are photoprotective proteins induced in response to various abiotic stresses, including dehydration, high light, and low temperature. These proteins contribute to protecting the thylakoid membrane against oxidative damage, thereby preventing the accumulation of fatty acid hydroperoxides and lipid peroxidation [81,82]. Lipocalin along with betaine aldehyde dehydrogenase and chlorophyll a-b binding chloroplastic protein were increased in Q. ilex under drought conditions [35,57].
Specific proteins up-accumulated in the Co population belonged to the main functional groups of carbohydrate metabolism; folding, sorting, and degradation; transcription; and redox (Figure S4a,m Table 2). Glyoxalase I and aconitate hydratase were accumulated in response to the combined stress. The glyoxalase (GLY) system, comprising GLYI and GLYII enzymes, has emerged as one of the primary detoxification pathways of methylglyoxal, a cytotoxic by-product of glycolysis, and is indispensable during abiotic and biotic stresses [83]. The role of glutathione (GSH) as an ROS scavenger regulating GLY enzymes and its physiological role in regulating various stress responses are well documented [84]. Aconitate hydratase, an enzyme of the glyoxylate bypass for the utilization of fatty acids as a carbon source, was identified in Castanea sativa in response to P. cinnamomi [85]. A delicate balance is required for proper functioning of this system, particularly during abiotic/biotic stress when the redox balance in cells is perturbed. In addition, several redox enzymes identified in this study, including glutathione reductase, thioredoxine reductase, NADPH-dependent thioredoxin reductase 3, monothiol glutaredoxin-S17, short-chain dehydrogenase/reductase SDR, and others, are also related to tolerance to drought [35,57] and resistance to P. ciannamomi [34] in Q. ilex.
The proteins of the transport porin/voltage-dependent anion-selective channel and GTP-binding nuclear protein Ran-3 were also accumulated in response to the pathogen, and the former was significantly accumulated under combined stress. Ion channels play an important role in turgor regulation in guard cells and become critical molecular targets of various signals, including osmotic stress [86,87]. Ras-related nuclear protein (RAN), a GTP-binding protein, functions in the nuclear–cytoplasmic transport of proteins and is involved in both the gibberellin and salicylic acid signaling pathways, promoting growth and disease resistance [88]. Mitochondrial Rho GTPase 1 belongs to the Rho family of proteins (ROPs), which are involved in plant immunity or susceptibility to disease [89]. The involvement of ROPs in plant–microbe interactions has been known for a long time. Activated immunogenic signals are transduced into characteristic immune reactions [89], as was demonstrated during the rice–Magnaporthe oryzae interaction [90,91]. Other proteins related to the defense response, such as protease stomatin/prohibitin-like protein, heat shock 70 kDa, carboxylesterase (CXE), and lipoxygenase (LOX), were also found to be accumulated in Co. Prohibitins and stomatins belong to a superfamily of proteins, together with a group of plant defense response genes named PID, referring to proliferation, ion, and death. Prohibitins are involved in proliferation and cell cycle control, and stomatins in ion channel regulation [92]. The role of CXE in response to pathogen attacks is well known [93], as was demonstrated in Arabidopsis transgenic plants, in which the overexpression of the AtCXE8 gene led to enhanced resistance to Botrytis cinerea [94]. Finally, the involvement of LOX in the defense response against biotic and abiotic environmental stresses has also been described [95].

3.3. Metabolomic Analysis

A total of 13,236 (negative and positive) ion features were resolved for both populations and treatments; 4069 of them were considered to be consistently present in at least one condition (Table S4), of which 1331 were annotated according to the metabolite databases (see Section 2.7). Two-dimensional PCA explained more than 50% of the total variability for the Co and Hu populations (Figure S5). PC1 discriminated between treatments, explaining 33.4% of the variability in Co and 36.4% in Hu. Qualitative and significant quantitative differences between treatments showed 508 and 611 up-accumulated metabolites for Co and Hu, respectively, and 633 and 542 down-accumulated metabolites. Focusing on significantly up-accumulated metabolites, the Venn diagram analysis showed 123 common to both populations (78 of them putatively annotated), 385 detected exclusively in Co (205 putatively annotated), and 488 in Hu (278 putatively annotated) (Figure 3d, Table S5).
A total of 97 metabolites (20 common to both populations, 31 specific to Co and 46 to Hu) were mapped to different pathways analyzed using the KEGG database (Table S5). The amino acid biosynthesis pathway was the best represented, including non-aromatic and aromatic amino acid metabolism, followed by carbohydrate metabolism, and phenolics and secondary metabolism. Lipid and energy metabolism, aminoacyl-tRNA biosynthesis pathways, and the metabolism of cofactors and vitamins are also highlighted in the metabolic pathway enrichment analysis (Table S5). Specific metabolites will be discussed in an integrated manner along with the enzymes of their metabolic pathways.

3.4. Integrated Proteome–Metabolome Analysis

An integrated analysis of proteins and metabolites up-accumulated in the Co and Hu populations in response to combined stress was performed. Pathway enrichment analysis revealed the most represented pathways in response to P. cinnamomi inoculation (Table S6): carbohydrate metabolism (mainly represented by pyruvate metabolism, the citrate cycle, glycolysis/gluconeogenesis, and glyoxylate and dicarboxylate metabolism) with 41 enzymes and 13 metabolites; amino acid metabolism (alanine, aspartate, and glutamate metabolism; arginine and proline metabolism; phenylalanine, tyrosine, and tryptophan biosynthesis; glycine, serine, and threonine metabolism; and glutathione metabolism, among others) with 22 enzymes and 26 metabolites; energy metabolism, with 15 enzymes and 5 metabolites; and secondary metabolism, with 10 enzymes and 15 metabolites (Figure S6). A heat map showing the differential patterns of the functional groups identified in response to P. cinnamomi, based on the abundance of enzymes, was constructed (Figure 4). Two main clusters were generated: one included pathways more represented in the Hu population in response to P. cinnamomi (mainly amino acid metabolism and isoquinoline alkaloid biosynthesis), and the other included pathways more represented in the Co population (glycolysis/gluconeogenesis, terpenoid backbone biosynthesis, flavonoid biosynthesis, some amino acid metabolism). Several pathways were highly represented in both populations (pyruvate metabolism, the TCA cycle, phenylpropanoid biosynthesis, and aminoacyl-tRNA biosynthesis, among others). MOFA inferred three latent factors (F1, F2, and F3) (Figure S7). Overall, proteomics explained more variability than metabolomics (Figure S7a,b). Significantly up-accumulated proteins and metabolites that presented high loadings (around the top 10% in absolute value) on the three factors are discussed and represented in Figure S7c.
Enzymes and metabolites of the aminoacyl-tRNA biosynthesis pathway, such as leucine–tRNA ligase, glycine–tRNA ligase, methionyl-tRNA synthetase, L-phenylalanine, L-arginine, L-glutamate, and L-valine, were mainly accumulated in the Hu population. Methionyl-tRNA synthetase was previously related to drought tolerance in holm oak [57]. The association of tRNA transcription and modification with plant cell growth and the response to pathogens has been described. In addition, mutations in proteins directly involved in tRNA synthesis and modification most frequently lead to pleiotropic effects on plant growth and immunity [96].
Enzymes and related metabolites of carbohydrate and amino acid metabolism were accumulated in the Hu population in response to the combined stress, including alpha 1,4-glucan phosphorylase, phosphoglycerate kinase, 6-phosphofructokinase, pyrophosphate-dependent, aconitase, glutamate synthase (ferredoxin), D-mannose, citrate, L-malate, and L-glutamate. Some of these proteins have been related to tolerance to drought stress in Q. ilex [57], Q. lobata, and Nitraria tangutorum [97,98], and heat stress in Populus tomentosa [99]. In the Co population, enzymes and metabolites of the glycolysis/gluconeogenesis pathways, including fructose-1,6-bisphosphatase, pyruvate kinase, phosphoglycerate mutase, alcohol dehydrogenase, pyruvate, malate, citrate, and lactate, among others, were also represented. This can be explained as a consequence of defective photosynthetic activity in inoculated plants, as was reported in Q. ilex in response to P. cinnamomi by Sghaier-Hammami et al. [29].
Other metabolic pathways also increased in response to the combined stress, such as the secondary metabolism pathways. The enzymes of the phenylpropanoid biosynthesis pathway, cinnamyl alcohol dehydrogenase (EC1.2.1.44), cinnamyl alcohol dehydrogenase 1 (EC1.1.1.195), and the metabolites coumarin and 4-coumaryl alcohol, were up-accumulated in the Co population. In addition, other enzymes and metabolites of flavonoid biosynthesis, including chalcone synthase, catechin, piceol, and silybin, were also increased in response to the pathogen (Table S6). The increase in the phenylpropanoid pathway can be interpreted as a mechanism of defense by strengthening the cell wall by incorporating lignin through the activity of cinnamyl alcohol dehydrogenases [100], as was proposed in Q. pubescens leaves in response to drought [101] and in Q. variabilis in response to P. cinnamomi [32]. Flavonoid biosynthesis has also been linked to tolerance to drought in Q. ilex [57,102] and the response to P. cinnamomi in C. sativa and Quercus spp. [32,85].
Overall, most of the proteins identified in response to the pathogen under watering conditions were also found in the presence of the pathogen under non-watering conditions. Therefore, a differential response was not observed between the two conditions of inoculation, as was previously observed in other holm oak populations [34]. There appears to be a protective effect of the photosynthetic apparatus and the osmotic regulation mechanism in both populations as a consequence of defective photosynthetic activity in inoculated plants. The activation of the glyoxalase system, together with a battery of ROS enzymes, may provide a more efficient detoxification mechanism for Co than Hu. This is consistent with the decreased leaf chlorophyll fluorescence observed on inoculated plants, which was more apparent in the Hu population.

4. Conclusions

Based on physiological and molecular analysis, the defense response to P. cinnamomi is dependent on the population, with the Co population found to be more resistant than the Hu population. No significant differences were observed between watered and non-watered inoculated plants, although the latter condition caused more severe symptoms. Proteomic and metabolomic analysis revealed differential involvement of metabolic pathways in both populations in response to P. cinnamomi. The accumulation of enzymes and metabolites of the glyoxalase system of detoxification, ROS proteins, and the phenylpropanoid and flavonoid biosynthesis pathways may provide higher resistance for the Co population through a more efficient system of protecting the photosynthetic apparatus and strengthening of the cell wall through the incorporation of lignin as a mechanism of defense. Some proteins related to pathogen defense were identified, especially in the Co population. However, overall, the observed response resembled that seen in response to drought. The increased levels of some specific enzymes and metabolites in the Co population may be key to providing greater resistance to the pathogen. This information highlights the variability in the response of holm oak to P. cinnamomi. Some candidate genes, among them beta-galactosidase, ornithine aminotransferase, glyoxalase I, glutathione reductase, thioredoxin reductase, and cinnamyl alcohol dehydrogenase, could be used for the selection of elite genotypes in breeding programs.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/biom14020160/s1. Table S1. Environmental features of the Quercus ilex populations. Altitude (meters above sea level -MASL), average temperature of the warmest months (Tmax) and the coldest months (Tmin), and average annual rainfall (P). Table S2. Summary of experimental design. Table S3. Raw data of proteins identified by shotgun (LC-MSMS) analysis. Table S4. Raw data of metabolites identified by LC-MSMS analysis. Table S5. Information regarding metabolites that showed over-accumulated response (Fold-Change >2) under stress conditions is included in this report. A distinction is made between those metabolites that were Up in both, Cordoba and Huelva populations, and those that were exclusive to each of the populations. Table S6. List of pathways activated in Q. ilex leaves in response to P. cinnamomi inoculation. Figure S1. Holm oak mother trees from two Andalusian populations, Cordoba and Huelva. Figure S2. Determination of Phytopthora cinnamomi presence by isolation from roots cuts of Quercus ilex seedlings inoculated with P. cinnamomi on PARPBH selective medium (a). Microscope view of P. cinnamomi mycelium with chlamydospores (scale bar 20 µm) (b). Figure S3. Visual evaluation and leaf damage symptoms of Cordoba (up) and Huelva (down) populations at day 12 of the experiment: control (C), P. cinnamomi inoculation under watered (I) and P. cinnamomi inoculation under non-watered (DxI) conditions. Figure S4. Functional groups of differential proteins up-accumulated (a,b) and down-accumulated (c,d) in seedlings from the asymptomatic Cordoba (a,c) and Huelva (b,d) mother trees under different treatments: control, drought, inoculation and combined stresses. Figure S5. Principal component analysis of consistent metabolites identified in Cordoba (a) and Huelva (b) populations under control and the combined P. cinnamomi inoculation and non-watered conditions. Figure S6. Kegg pathway classification of proteins and metabolites up-accumulated in response to P. cinnamomi. Figure S7. (a) Proportion of total variance explained (R2) by individual factors for each assay; (b) cumulative proportion of total variance explained; (c) Lolipop plots showing top loadings (top10% in absolute values) of discussed proteins and metabolites of latent factors 1 to 3.

Author Contributions

Conceptualization, J.V.J.-N. and M.Á.C.-S.; methodology, M.Á.C.-S., T.H.-L., M.T.-P., M.L.-O. and M.-D.R.; software, T.H.-L., M.L.-O., M.T.-P., V.M.G.-S. and M.Á.C.-S.; formal analysis, T.H.-L., M.T.-P., M.L.-O., M.-D.R. and M.Á.C.-S.; investigation, M.Á.C.-S., T.H.-L., M.T.-P., M.L.-O. and M.-D.R.; writing—original draft preparation, M.Á.C.-S. and T.H.-L.; writing—review and editing, M.Á.C.-S., J.V.J.-N., T.H.-L., M.T.-P., M.L.-O., V.M.G.-S. and M.-D.R.; supervision, M.Á.C.-S. and J.V.J.-N.; funding acquisition, J.V.J.-N. and M.Á.C.-S. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Spanish Ministry of Economy and Competitiveness within the framework of Projects PID2019-109038RB-I00 and PID2022-141599OB-I00, and PROYEXCEL_00881 grants from the Junta de Andalucía.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data are available in the repositories described in the manuscript and in the Supplemental Material.

Acknowledgments

M.Á.C.-S. is grateful for being awarded a Ramón y Cajal (RYC-2017-23706) contract by the Spanish Ministry of Science, Innovation and Universities. The author thankfully acknowledges F. J. Ruiz Gómez and R.M. Navarro Cerrillo for kindly providing us with the isolate of Phytophthora cinnamomi. The also thank the computer resources, technical expertise and assistance provided by the SCBI (Supercomputing and Bioinformatics) center of the University of Malaga (Spain).

Conflicts of Interest

The authors declare no conflicts of interest.

References

  1. Allen, C.D.; Breshears, D.D.; McDowell, N.G. On Underestimation of Global Vulnerability to Tree Mortality and Forest Die-off from Hotter Drought in the Anthropocene. Ecosphere 2015, 6, 1–55. [Google Scholar] [CrossRef]
  2. Hansen, E.M. Phytophthora Species Emerging as Pathogens of Forest Trees. Curr. For. Rep. 2015, 1, 16–24. [Google Scholar] [CrossRef]
  3. Intergovernmental Panel on Climate Change (IPCC). Climate Change 2013: The Physical Science Basis. In Contribution of Working Group I to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change; Intergovernmental Panel on Climate Change, Ed.; Cambridge University Press: Cambridge, UK, 2013; Volume 1535, ISBN 9781107057999. [Google Scholar]
  4. Doblas-Miranda, E.; Alonso, R.; Arnan, X.; Bermejo, V.; Brotons, L.; de las Heras, J.; Estiarte, M.; Hódar, J.A.; Llorens, P.; Lloret, F.; et al. A Review of the Combination among Global Change Factors in Forests, Shrublands and Pastures of the Mediterranean Region: Beyond Drought Effects. Glob. Planet. Change 2017, 148, 42–54. [Google Scholar] [CrossRef]
  5. Burgess, T.I.; Scott, J.K.; Mcdougall, K.L.; Stukely, M.J.C.; Crane, C.; Dunstan, W.A.; Brigg, F.; Andjic, V.; White, D.; Rudman, T.; et al. Current and Projected Global Distribution of Phytophthora cinnamomi, One of the World’s Worst Plant Pathogens. Glob. Change Biol. 2017, 23, 1661–1674. [Google Scholar] [CrossRef]
  6. Homet, P.; Matías, L.; Godoy, O.; Gómez-Aparicio, L. Evidence for Antagonistic Effects of Climate Change and Exotic Pathogens on Regeneration of Mediterranean Forests. J. Ecol. 2023, 112, 174–188. [Google Scholar] [CrossRef]
  7. Kamoun, S.; Furzer, O.; Jones, J.D.G.; Judelson, H.S.; Ali, G.S.; Dalio, R.J.D.; Roy, S.G.; Schena, L.; Zambounis, A.; Panabières, F.; et al. The Top 10 Oomycete Pathogens in Molecular Plant Pathology. Mol. Plant Pathol. 2015, 16, 413–434. [Google Scholar] [CrossRef] [PubMed]
  8. Jung, T.; Pérez-Sierra, A.; Durán, A.; Jung, M.H.; Balci, Y.; Scanu, B. Canker and Decline Diseases Caused by Soil- and Airborne Phytophthora Species in Forests and Woodlands. Persoonia 2018, 40, 182–220. [Google Scholar] [CrossRef] [PubMed]
  9. Corcobado, T.; Miranda-Torres, J.J.; Martín-García, J.; Jung, T.; Solla, A. Early Survival of Quercus ilex Subspecies from Different Populations after Infections and Co-infections by Multiple Phytophthora Species. Plant Pathol. 2017, 66, 792–804. [Google Scholar] [CrossRef]
  10. Bezuidenhout, C.M.; Denman, S.; Kirk, S.A.; Botha, W.J.; Mostert, L.; McLeod, A. Phytophthora taxa associated with cultivated Agathosma, with emphasis on the P. citricola complex and P. capensis sp. nov. Persoonia 2010, 25, 32–49. [Google Scholar] [CrossRef]
  11. Marañón, T.; Ibáñez, B.; Anaya-Romero, M.; Muñoz-Rojas, M.; Pérez-Ramos, I.M. Oak trees and woodlands providing ecosystem services in Southern Spain. In Trees beyond the Wood. An Exploration of Concepts of Woods, Forests and Trees; Rotherham, I.D., Handley, C., Agnoletti, M., Samojlik, T., Eds.; Wildtrack Publishing: Sheffield, UK, 2012; pp. 369–378. [Google Scholar]
  12. Ruiz-Gómez, F.J.; Pérez-de-Luque, A.; Navarro-Cerrillo, R.M. The Involvement of Phytophthora Root Rot and Drought Stress in Holm Oak Decline: From Ecophysiology to Microbiome Influence. Curr. For. Rep. 2019, 5, 251–266. [Google Scholar] [CrossRef]
  13. Ducrey, M. Quelle Sylviculture et Quel Avenir Pour Les Taillis de Chêne Vert (Quercus ilex L.) de La Région Méditerranéenne Française. Rev. For. Francaise 1992, 44, 12–34. [Google Scholar] [CrossRef]
  14. De Rigo, D.; Caudullo, G. Quercus ilex in Europe: Distribution, Habitat, Usage and Threats. In European Atlas of Forest Tree Species; Publications Office of the European Union: Luxembourg, 2016; pp. 152–153. [Google Scholar]
  15. Ortego, J.; Bonal, R.; Munoz, A. Genetic Consequences of Habitat Fragmentation in Long-Lived Tree Species: The Case of the Mediterranean Holm Oak (Quercus ilex, L.). J. Hered. 2010, 101, 717–726. [Google Scholar] [CrossRef] [PubMed]
  16. Guzmán, B.; Rodríguez López, C.M.; Forrest, A.; Cano, E.; Vargas, P. Protected Areas of Spain Preserve the Neutral Genetic Diversity of Quercus ilex L. Irrespective of Glacial Refugia. Tree Genet. Genomes 2015, 11, 124. [Google Scholar] [CrossRef]
  17. Fernández i Marti, A.; Romero-Rodríguez, C.; Navarro-Cerrillo, R.; Abril, N.; Jorrín-Novo, J.; Dodd, R. Population Genetic Diversity of Quercus ilex Subsp. ballota (Desf.) Samp. Reveals Divergence in Recent and Evolutionary Migration Rates in the Spanish Dehesas. Forests 2018, 9, 337. [Google Scholar] [CrossRef]
  18. Brasier, C.M. Oak Tree Mortality in Iberia. Nature 1992, 360, 539. [Google Scholar] [CrossRef]
  19. Corral-Ribera, M.; Fidalgo, C.H.; Peco, B.V. Environmental Variables in the Distribution of La Seca Disease in the Holm Oak (Quercus ilex Subsp. ballota). In Espacio Tiempo y Forma. Serie VI, Geografía; Universidad Nacional de Educación a Distancia: Madrid, Spain, 2018; p. 107. [Google Scholar] [CrossRef]
  20. Surová, D.; Ravera, F.; Guiomar, N.; Martínez Sastre, R.; Pinto-Correia, T. Contributions of Iberian Silvo-Pastoral Landscapes to the Well-Being of Contemporary Society. Rangel. Ecol. Manag. 2018, 71, 560–570. [Google Scholar] [CrossRef]
  21. Corcobado, T.; Cubera, E.; Moreno, G.; Solla, A. Quercus ilex Forests Are Influenced by Annual Variations in Water Table, Soil Water Deficit and Fine Root Loss Caused by Phytophthora cinnamomi. Agric. For. Meteorol. 2013, 169, 92–99. [Google Scholar] [CrossRef]
  22. Corcobado, T.; Moreno, G.; Azul, A.M.; Solla, A. Seasonal Variations of Ectomycorrhizal Communities in Declining Quercus ilex Forests: Interactions with Topography, Tree Health Status and Phytophthora cinnamomi Infections. Forestry 2015, 88, 257–266. [Google Scholar] [CrossRef]
  23. Fernández-Habas, J.; Fernández-Rebollo, P.; Casado, M.R.; García Moreno, A.M.; Abellanas, B. Spatio-Temporal Analysis of Oak Decline Process in Open Woodlands: A Case Study in SW Spain. J. Environ. Manag. 2019, 248, 109308. [Google Scholar] [CrossRef]
  24. Sánchez-Cuesta, R.; Ruiz-Gómez, F.J.; Duque-Lazo, J.; González-Moreno, P.; Navarro-Cerrillo, R.M. The Environmental Drivers Influencing Spatio-Temporal Dynamics of Oak Defoliation and Mortality in Dehesas of Southern Spain. For. Ecol. Manag. 2021, 485, 118946. [Google Scholar] [CrossRef]
  25. Malcolm, J.R.; Liu, C.; Neilson, R.P.; Hansen, L.; Hannah, L. Global Warming and Extinctions of Endemic Species from Biodiversity Hotspots. Conserv. Biol. 2006, 20, 538–548. [Google Scholar] [CrossRef]
  26. Alderotti, F.; Verdiani, E. God Save the Queen! How and Why the Dominant Evergreen Species of the Mediterranean Basin Is Declining? AoB Plants 2023, 15, plad051. [Google Scholar] [CrossRef]
  27. Duque-Lazo, J.; Van-Gils, H.; Groen, T.A.; Navarro-Cerrillo, R.M. Transferability of Species Distribution Models: The Case of Phytophthora cinnamomi in Southwest Spain and Southwest Australia. Ecoll. Modell. 2016, 320, 62–70. [Google Scholar] [CrossRef]
  28. Duque-Lazo, J.; Navarro-Cerrillo, R.M.; Ruíz-Gómez, F.J. Assessment of the Future Stability of Cork Oak (Quercus suber L.) Afforestation under Climate Change Scenarios in Southwest Spain. For. Ecol. Manag. 2018, 409, 444–456. [Google Scholar] [CrossRef]
  29. Sghaier-Hammami, B.; Valero-Galvàn, J.; Romero-Rodríguez, M.C.; Navarro-Cerrillo, R.M.; Abdelly, C.; Jorrín-Novo, J. Physiological and Proteomics Analyses of Holm Oak (Quercus ilex Subsp. Ballota [Desf.] Samp.) Responses to Phytophthora cinnamomi. Plant Physiol. Biochem. 2013, 71, 191–202. [Google Scholar] [CrossRef] [PubMed]
  30. Corcobado, T.; Cubera, E.; Juárez, E.; Moreno, G.; Solla, A. Drought Events Determine Performance of Quercus ilex Seedlings and Increase Their Susceptibility to Phytophthora cinnamomi. Agric. For. Meteorol. 2014, 192–193, 1–8. [Google Scholar] [CrossRef]
  31. Hardham, A.R.; Blackman, L.M. Phytophthora cinnamomi . Mol. Plant Pathol. 2018, 19, 260–285. [Google Scholar] [CrossRef] [PubMed]
  32. Saiz-Fernández, I.; Đorđević, B.; Kerchev, P.; Černý, M.; Jung, T.; Berka, M.; Fu, C.-H.; Horta Jung, M.; Brzobohatý, B. Differences in the Proteomic and Metabolomic Response of Quercus suber and Quercus variabilis During the Early Stages of Phytophthora cinnamomi Infection. Front. Microbiol. 2022, 13, 894533. [Google Scholar] [CrossRef] [PubMed]
  33. Ruiz Gómez, F.; Pérez-de-Luque, A.; Sánchez-Cuesta, R.; Quero, J.; Navarro Cerrillo, R. Differences in the Response to Acute Drought and Phytophthora cinnamomi Rands Infection in Quercus ilex L. Seedlings. Forests 2018, 9, 634. [Google Scholar] [CrossRef]
  34. San-Eufrasio, B.; Castillejo, M.Á.; Labella-Ortega, M.; Ruiz-Gómez, F.J.; Navarro-Cerrillo, R.M.; Tienda-Parrilla, M.; Jorrín-Novo, J.V.; Rey, M.-D. Effect and Response of Quercus Ilex Subsp. Ballota [Desf.] Samp. Seedlings from Three Contrasting Andalusian Populations to Individual and Combined Phytophthora cinnamomi and Drought Stresses. Front. Plant Sci. 2021, 12, 722802. [Google Scholar] [CrossRef] [PubMed]
  35. Simova-Stoilova, L.P.; Romero-Rodríguez, M.C.; Sánchez-Lucas, R.; Navarro-Cerrillo, R.M.; Medina-Aunon, J.A.; Jorrín-Novo, J.V. 2-DE Proteomics Analysis of Drought Treated Seedlings of Quercus ilex Supports a Root Active Strategy for Metabolic Adaptation in Response to Water Shortage. Front. Plant Sci. 2015, 6, 627. [Google Scholar] [CrossRef]
  36. Hoagland, D.R.; Arnon, D.I. The Water-Culture Method for Growing Plants without Soil. Circ.—Calif. Agric. Exp. Stn. 1950, 347, 32. [Google Scholar]
  37. Ruiz Gómez, F.J.; Navarro-Cerrillo, R.M.; Pérez-de-Luque, A.; Oβwald, W.; Vannini, A.; Morales-Rodríguez, C. Assessment of Functional and Structural Changes of Soil Fungal and Oomycete Communities in Holm Oak Declined Dehesas through Metabarcoding Analysis. Sci. Rep. 2019, 9, 5315. [Google Scholar] [CrossRef] [PubMed]
  38. San-Eufrasio, B.; Sánchez-Lucas, R.; López-Hidalgo, C.; Guerrero-Sánchez, V.M.; Castillejo, M.Á.; Maldonado-Alconada, A.M.; Jorrín-Novo, J.V.; Rey, M.-D. Responses and Differences in Tolerance to Water Shortage under Climatic Dryness Conditions in Seedlings from Quercus Spp. and Andalusian Q. ilex Populations. Forests 2020, 11, 707. [Google Scholar] [CrossRef]
  39. Wang, W.; Vignani, R.; Scali, M.; Cresti, M. A Universal and Rapid Protocol for Protein Extraction from Recalcitrant Plant Tissues for Proteomic Analysis. Electrophoresis 2006, 27, 2782–2786. [Google Scholar] [CrossRef] [PubMed]
  40. 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]
  41. Castillejo, M.Á.; Bani, M.; Rubiales, D. Understanding Pea Resistance Mechanisms in Response to Fusarium oxysporum through Proteomic Analysis. Phytochemistry 2015, 115, 44–58. [Google Scholar] [CrossRef]
  42. Castillejo, M.Á.; Fondevilla-Aparicio, S.; Fuentes-Almagro, C.; Rubiales, D. Quantitative Analysis of Target Peptides Related to Resistance Against Ascochyta Blight (Peyronellaea pinodes) in Pea. Proteome Res. 2020, 19, 1000–1012. [Google Scholar] [CrossRef]
  43. Guerrero-Sanchez, V.M.; Maldonado-Alconada, A.M.; Amil-Ruiz, F.; Jorrin-Novo, J.V. Holm Oak (Quercus ilex) Transcriptome. De Novo Sequencing and Assembly Analysis. Front. Mol. Biosci. 2017, 4, 70. [Google Scholar] [CrossRef]
  44. Guerrero-Sanchez, V.M.; Maldonado-Alconada, A.M.; Amil-Ruiz, F.; Verardi, A.; Jorrín-Novo, J.V.; Rey, M.-D. Ion Torrent and Lllumina, Two Complementary RNA-Seq Platforms for Constructing the Holm Oak (Quercus ilex) Transcriptome. PLoS ONE 2019, 14, e0210356. [Google Scholar] [CrossRef]
  45. Al Shweiki, M.R.; Mönchgesang, S.; Majovsky, P.; Thieme, D.; Trutschel, D.; Hoehenwarter, W. Assessment of Label-Free Quantification in Discovery Proteomics and Impact of Technological Factors and Natural Variability of Protein Abundance. J. Proteome Res. 2017, 16, 1410–1424. [Google Scholar] [CrossRef]
  46. Perez-Riverol, Y.; Csordas, A.; Bai, J.; Bernal-Llinares, M.; Hewapathirana, S.; Kundu, D.J.; Inuganti, A.; Griss, J.; Mayer, G.; Eisenacher, M.; et al. The PRIDE Database and Related Tools and Resources in 2019: Improving Support for Quantification Data. Nucleic Acids Res. 2019, 47, D442–D450. [Google Scholar] [CrossRef] [PubMed]
  47. Lohse, M.; Nagel, A.; Herter, T.; May, P.; Schroda, M.; Zrenner, R.; Tohge, T.; Fernie, A.R.; Stitt, M.; Usadel, B. Mercator: A Fast and Simple Web Server for Genome Scale Functional Annotation of Plant Sequence Data. Plant Cell Environ. 2014, 37, 1250–1258. [Google Scholar] [CrossRef]
  48. KEGG: Kyoto Encyclopedia of Genes and Genomes Database. Available online: https://www.genome.jp/kegg/ (accessed on 15 November 2023).
  49. Djoumbou Feunang, Y.; Eisner, R.; Knox, C.; Chepelev, L.; Hastings, J.; Owen, G.; Fahy, E.; Steinbeck, C.; Subramanian, S.; Bolton, E.; et al. ClassyFire: Automated Chemical Classification with a Comprehensive, Computable Taxonomy. J. Cheminform. 2016, 8, 61. [Google Scholar] [CrossRef]
  50. MetabolomicsWorkbench. Available online: https://www.metabolomicsworkbench.org (accessed on 12 December 2023).
  51. Lê, S.; Josse, J.; Husson, F. FactoMineR: An R Package for Multivariate Analysis. J. Stat. Softw. 2008, 25, 1–18. [Google Scholar] [CrossRef]
  52. R Core Team. A Language and Environment for Statistical Computing; R Foundation for Statistical Computing: Vienna, Austria, 2022; Available online: https://www.R-project.org/ (accessed on 10 October 2023).
  53. Yan, L. Ggvenn: Draw Venn Diagram by “Ggplot2”. R Package, Version 19; R Project: Vienna, Austria, 2021.
  54. Argelaguet, R.; Velten, B.; Arnol, D.; Dietrich, S.; Zenz, T.; Marioni, J.C.; Buettner, F.; Huber, W.; Stegle, O. Multi-Omics Factor Analysis—A Framework for Unsupervised Integration of Multi-omics Data Sets. Mol. Syst. Biol. 2018, 14, e8124. [Google Scholar] [CrossRef] [PubMed]
  55. Vivas, M.; Hernández, J.; Corcobado, T.; Cubera, E.; Solla, A. Transgenerational Induction of Resistance to Phytophthora cinnamomi in Holm Oak. Forests 2021, 12, 100. [Google Scholar] [CrossRef]
  56. Jeffers, S.N. Comparison of Two Media Selective for Phytophthora and Pythium Species. Plant Dis. 1986, 70, 1038. [Google Scholar] [CrossRef]
  57. San-Eufrasio, B.; Bigatton, E.D.; Guerrero-Sánchez, V.M.; Chaturvedi, P.; Jorrín-Novo, J.V.; Rey, M.-D.; Castillejo, M.Á. Proteomics Data Analysis for the Identification of Proteins and Derived Proteotypic Peptides of Potential Use as Putative Drought Tolerance Markers for Quercus ilex. Int. J. Mol. Sci. 2021, 22, 3191. [Google Scholar] [CrossRef] [PubMed]
  58. Amaral, J.; Ribeyre, Z.; Vigneaud, J.; Sow, M.D.; Fichot, R.; Messier, C.; Pinto, G.; Nolet, P.; Maury, S. Advances and Promises of Epigenetics for Forest Trees. Forests 2020, 11, 976. [Google Scholar] [CrossRef]
  59. Hofmeister, B.T.; Denkena, J.; Colomé-Tatché, M.; Shahryary, Y.; Hazarika, R.; Grimwood, J.; Mamidi, S.; Jenkins, J.; Grabowski, P.P.; Sreedasyam, A.; et al. A Genome Assembly and the Somatic Genetic and Epigenetic Mutation Rate in a Wild Long-Lived Perennial Populus trichocarpa. Genome Biol. 2020, 21, 259. [Google Scholar] [CrossRef]
  60. Bolhàr-Nordenkampf, H.R.; Öquist, G. Chlorophyll Fluorescence as a Tool in Photosynthesis Research. In Photosynthesis and Production in a Changing Environment; Springer: Dordrecht, The Netherlands, 1993; pp. 193–206. [Google Scholar]
  61. Peguero-Pina, J.J.; Sancho-Knapik, D.; Morales, F.; Flexas, J.; Gil-Pelegrín, E. Differential Photosynthetic Performance and Photoprotection Mechanisms of Three Mediterranean Evergreen Oaks under Severe Drought Stress. Funct. Plant Biol. 2009, 36, 453. [Google Scholar] [CrossRef] [PubMed]
  62. Sancho-Knapik, D.; Mendoza-Herrer, Ó.; Gil-Pelegrín, E.; Peguero-Pina, J. Chl Fluorescence Parameters and Leaf Reflectance Indices Allow Monitoring Changes in the Physiological Status of Quercus ilex L. under Progressive Water Deficit. Forests 2018, 9, 400. [Google Scholar] [CrossRef]
  63. Valero-Galván, J.; González-Fernández, R.; Navarro-Cerrillo, R.M.; Gil-Pelegrín, E.; Jorrín-Novo, J.V. Physiological and Proteomic Analyses of Drought Stress Response in Holm Oak Provenances. J. Proteome Res. 2013, 12, 5110–5123. [Google Scholar] [CrossRef]
  64. Castillejo, M.A.; Pascual, J.; Jorrín-Novo, J.V.; Balbuena, T.S. Proteomics Research in Forest Trees: A 2012–2022 Update. Front. Plant Sci. 2023, 14, 1130665. [Google Scholar] [CrossRef]
  65. Jeandet, P.; Formela-Luboińska, M.; Labudda, M.; Morkunas, I. The Role of Sugars in Plant Responses to Stress and Their Regulatory Function during Development. Int. J. Mol. Sci. 2022, 23, 5161. [Google Scholar] [CrossRef]
  66. Hartmann, H.; Trumbore, S. Understanding the Roles of Nonstructural Carbohydrates in Forest Trees—From What We Can Measure to What We Want to Know. New Phytol. 2016, 211, 386–403. [Google Scholar] [CrossRef]
  67. Niu, L.; Liu, L.; Wang, W. Digging for Stress-Responsive Cell Wall Proteins for Developing Stress-Resistant Maize. Front. Plant Sci. 2020, 11, 576385. [Google Scholar] [CrossRef]
  68. Liu, Y.; Liu, L.; Asiegbu, F.O.; Yang, C.; Han, S.; Yang, S.; Zeng, Q.; Liu, Y. Molecular Identification and Antifungal Properties of Four Thaumatin-like Proteins in Spruce (Picea likiangensis). Forests 2021, 12, 1268. [Google Scholar] [CrossRef]
  69. Roosens, N.H.; Bitar, F.A.; Loenders, K.; Angenon, G.; Jacobs, M. Overexpression of Ornithine-δ-Aminotransferase Increases Proline Biosynthesis and Confers Osmotolerance in Transgenic Plants. Mol. Breed. 2002, 9, 73–80. [Google Scholar] [CrossRef]
  70. Anwar, A.; She, M.; Wang, K.; Riaz, B.; Ye, X. Biological Roles of Ornithine Aminotransferase (OAT) in Plant Stress Tolerance: Present Progress and Future Perspectives. Int. J. Mol. Sci. 2018, 19, 3681. [Google Scholar] [CrossRef] [PubMed]
  71. Zhu, D.; Luo, F.; Zou, R.; Liu, J.; Yan, Y. Integrated Physiological and Chloroplast Proteome Analysis of Wheat Seedling Leaves under Salt and Osmotic Stresses. J. Proteom. 2021, 234, 104097. [Google Scholar] [CrossRef]
  72. Guerrero-Sánchez, V.M.; López-Hidalgo, C.; Rey, M.-D.; Castillejo, M.Á.; Jorrín-Novo, J.V.; Escandón, M. Multiomic Data Integration in the Analysis of Drought-Responsive Mechanisms in Quercus ilex Seedlings. Plants 2022, 11, 3067. [Google Scholar] [CrossRef] [PubMed]
  73. Park, C.-J.; Seo, Y.-S. Heat Shock Proteins: A Review of the Molecular Chaperones for Plant Immunity. Plant Pathol. J. 2015, 31, 323–333. [Google Scholar] [CrossRef] [PubMed]
  74. Guerrero-Sánchez, V.M.; Castillejo, M.Á.; López-Hidalgo, C.; Alconada, A.M.M.; Jorrín-Novo, J.V.; Rey, M.-D. Changes in the Transcript and Protein Profiles of Quercus ilex Seedlings in Response to Drought Stress. J. Proteom. 2021, 243, 104263. [Google Scholar] [CrossRef]
  75. Kong, F.; Deng, Y.; Zhou, B.; Wang, G.; Wang, Y.; Meng, Q. A Chloroplast-Targeted DnaJ Protein Contributes to Maintenance of Photosystem II under Chilling Stress. J. Exp. Bot. 2014, 65, 143–158. [Google Scholar] [CrossRef]
  76. Richardson, L.G.L.; Singhal, R.; Schnell, D.J. The Integration of Chloroplast Protein Targeting with Plant Developmental and Stress Responses. BMC Biol. 2017, 15, 118. [Google Scholar] [CrossRef]
  77. Richardson, L.G.L.; Schnell, D.J. Origins, Function, and Regulation of the TOC–TIC General Protein Import Machinery of Plastids. J Exp. Bot. 2020, 71, 1226–1238. [Google Scholar] [CrossRef]
  78. Seidel, T. The Plant V-ATPase. Front. Plant Sci. 2022, 13, 931777. [Google Scholar] [CrossRef]
  79. Wei, H.; Movahedi, A.; Liu, G.; Li, Y.; Liu, S.; Yu, C.; Chen, Y.; Zhong, F.; Zhang, J. Comprehensive Analysis of Carotenoid Cleavage Dioxygenases Gene Family and Its Expression in Response to Abiotic Stress in Poplar. Int. J. Mol. Sci. 2022, 23, 1418. [Google Scholar] [CrossRef]
  80. Shang, C.; Ye, T.; Zhou, Q.; Chen, P.; Li, X.; Li, W.; Chen, S.; Hu, Z.; Zhang, W. Genome-Wide Identification and Bioinformatics Analyses of Host Defense Peptides Snakin/GASA in Mangrove Plants. Genes 2023, 14, 923. [Google Scholar] [CrossRef]
  81. Malnoë, A.; Schultink, A.; Shahrasbi, S.; Rumeau, D.; Havaux, M.; Niyogi, K.K. The Plastid Lipocalin LCNP Is Required for Sustained Photoprotective Energy Dissipation in Arabidopsis. Plant Cell 2018, 30, 196–208. [Google Scholar] [CrossRef] [PubMed]
  82. Henri, P.; Rumeau, D. Ectopic Expression of Human Apolipoprotein D in Arabidopsis Plants Lacking Chloroplastic Lipocalin Partially Rescues Sensitivity to Drought and Oxidative Stress. Plant Physiol. Biochem. 2021, 158, 265–274. [Google Scholar] [CrossRef]
  83. Garai, S.; Bhowal, B.; Kaur, C.; Singla-Pareek, S.L.; Sopory, S.K. What Signals the Glyoxalase Pathway in Plants? Physiol. Mol. Biol. Plants 2021, 27, 2407–2420. [Google Scholar] [CrossRef] [PubMed]
  84. Hasanuzzaman, M.; Nahar, K.; Anee, T.I.; Fujita, M. Glutathione in Plants: Biosynthesis and Physiological Role in Environmental Stress Tolerance. Physiol. Mol. Biol. Plants 2017, 23, 249–268. [Google Scholar] [CrossRef]
  85. Saiz-Fernández, I.; Milenković, I.; Berka, M.; Černý, M.; Tomšovský, M.; Brzobohatý, B.; Kerchev, P. Integrated Proteomic and Metabolomic Profiling of Phytophthora cinnamomi Attack on Sweet Chestnut (Castanea sativa) Reveals Distinct Molecular Reprogramming Proximal to the Infection Site and Away from It. Int. J. Mol. Sci. 2020, 21, 8525. [Google Scholar] [CrossRef] [PubMed]
  86. MacRobbie, E.A.C. Signalling in Guard Cells and Regulation of Ion Channel Activity. J. Exp. Bot. 1997, 48, 515–528. [Google Scholar] [CrossRef] [PubMed]
  87. Luan, S. Signalling Drought in Guard Cells. Plant Cell Environ. 2002, 25, 229–237. [Google Scholar] [CrossRef]
  88. Xu, P.; Ma, W.; Liu, J.; Hu, J.; Cai, W. Overexpression of a Small GTP-binding Protein Ran1 in Arabidopsis Leads to Promoted Elongation Growth and Enhanced Disease Resistance against P. Syringae DC3000. Plant J. 2021, 108, 977–991. [Google Scholar] [CrossRef]
  89. Engelhardt, S.; Trutzenberg, A.; Hückelhoven, R. Regulation and Functions of ROP GTPases in Plant–Microbe Interactions. Cells 2020, 9, 2016. [Google Scholar] [CrossRef] [PubMed]
  90. Ono, E. Essential Role of the Small GTPase Rac in Disease Resistance of Rice. Proc. Natl. Acad. Sci. USA 2001, 98, 759–764. [Google Scholar] [CrossRef]
  91. Kawano, Y.; Kaneko-Kawano, T.; Shimamoto, K. Rho Family GTPase-Dependent Immunity in Plants and Animals. Front. Plant Sci. 2014, 5, 522. [Google Scholar] [CrossRef]
  92. Nadimpalli, R.; Yalpani, N.; Johal, G.S.; Simmons, C.R. Prohibitins, Stomatins, and Plant Disease Response Genes Compose a Protein Superfamily That Controls Cell Proliferation, Ion Channel Regulation, and Death. J. Biol. Chem. 2000, 275, 29579–29586. [Google Scholar] [CrossRef] [PubMed]
  93. Gershater, M.C.; Edwards, R. Regulating Biological Activity in Plants with Carboxylesterases. Plant Sci. J. 2007, 173, 579–588. [Google Scholar] [CrossRef]
  94. Leinweber, F.-J. Possible Physiological Roles of Carboxylic Ester Hydrolases. Drug Metab. Rev. 1987, 18, 379–439. [Google Scholar] [CrossRef] [PubMed]
  95. Viswanath, K.K.; Varakumar, P.; Pamuru, R.R.; Basha, S.J.; Mehta, S.; Rao, A.D. Plant Lipoxygenases and Their Role in Plant Physiology. J. Plant Biol. 2020, 63, 83–95. [Google Scholar] [CrossRef]
  96. Soprano, A.S.; Smetana, J.H.C.; Benedetti, C.E. Regulation of tRNA Biogenesis in Plants and Its Link to Plant Growth and Response to Pathogens. Biochim. Biophys. Acta Gene Regul. 2018, 1861, 344–353. [Google Scholar] [CrossRef] [PubMed]
  97. Liu, C.; Duan, N.; Chen, X.; Li, H.; Zhao, X.; Duo, P.; Wang, J.; Li, Q. Metabolic Pathways Involved in the Drought Stress Response of Nitraria tangutorum as Revealed by Transcriptome Analysis. Forests 2022, 13, 509. [Google Scholar] [CrossRef]
  98. Gugger, P.F.; Peñaloza-Ramírez, J.M.; Wright, J.W.; Sork, V.L. Whole-Transcriptome Response to Water Stress in a California Endemic Oak, Quercus lobata. Tree Physiol. 2016, 37, 632–644. [Google Scholar] [CrossRef]
  99. Ren, S.; Ma, K.; Lu, Z.; Chen, G.; Cui, J.; Tong, P.; Wang, L.; Teng, N.; Jin, B. Transcriptomic and Metabolomic Analysis of the Heat-Stress Response of Populus tomentosa Carr. Forests 2019, 10, 383. [Google Scholar] [CrossRef]
  100. Tronchet, M.; Balagué, C.; Kroj, T.; Jouanin, L.; Roby, D. Cinnamyl Alcohol Dehydrogenases-C and D, Key Enzymes in Lignin Biosynthesis, Play an Essential Role in Disease Resistance in Arabidopsis. Mol. Plant Pathol. 2010, 11, 83–92. [Google Scholar] [CrossRef] [PubMed]
  101. Madritsch, S.; Wischnitzki, E.; Kotrade, P.; Ashoub, A.; Burg, A.; Fluch, S.; Brüggemann, W.; Sehr, E.M. Elucidating Drought Stress Tolerance in European Oaks Through Cross-Species Transcriptomics. G3 2019, 9, 3181–3199. [Google Scholar] [CrossRef] [PubMed]
  102. Tienda-Parrilla, M.; López-Hidalgo, C.; Guerrero-Sanchez, V.M.; Infantes-González, Á.; Valderrama-Fernández, R.; Castillejo, M.-Á.; Jorrín-Novo, J.V.; Rey, M.-D. Untargeted MS-Based Metabolomics Analysis of the Responses to Drought Stress in Quercus ilex L. Leaf Seedlings and the Identification of Putative Compounds Related to Tolerance. Forests 2022, 13, 551. [Google Scholar] [CrossRef]
Figure 1. (a,b) Percentage of seedling mortality and (c,d) measurements of quantum yield of photosystem II (Qy) in dark-adapted leaves from Cordoba (a,c) and Huelva (b,d) populations during drought (D), P. cinnamomi inoculation (I), and combined (D × I) stress with respect to control (C) seedlings from asymptomatic (A) and symptomatic (S) Q. ilex mother trees. Values represent mean ± SE of three biological replicates. Different letters, calculated from the area under the Qy curve, denote significant differences among treatments (p < 0.05).
Figure 1. (a,b) Percentage of seedling mortality and (c,d) measurements of quantum yield of photosystem II (Qy) in dark-adapted leaves from Cordoba (a,c) and Huelva (b,d) populations during drought (D), P. cinnamomi inoculation (I), and combined (D × I) stress with respect to control (C) seedlings from asymptomatic (A) and symptomatic (S) Q. ilex mother trees. Values represent mean ± SE of three biological replicates. Different letters, calculated from the area under the Qy curve, denote significant differences among treatments (p < 0.05).
Biomolecules 14 00160 g001
Figure 2. Principal component analysis of proteins consistently identified in seedlings from asymptomatic (a) Cordoba and (b) Huelva mother trees under different treatments: control, drought, inoculation, and combined stress.
Figure 2. Principal component analysis of proteins consistently identified in seedlings from asymptomatic (a) Cordoba and (b) Huelva mother trees under different treatments: control, drought, inoculation, and combined stress.
Biomolecules 14 00160 g002
Figure 3. Variable proteins significantly up-accumulated in seedlings from asymptomatic (a) Cordoba and (b) Huelva mother trees under different treatments: control (C), drought (D), inoculation (I), and combined stress (D × I). (c) Comparative analysis of both populations in response to different stresses. (d) Variable metabolites significantly up-accumulated under combined stress.
Figure 3. Variable proteins significantly up-accumulated in seedlings from asymptomatic (a) Cordoba and (b) Huelva mother trees under different treatments: control (C), drought (D), inoculation (I), and combined stress (D × I). (c) Comparative analysis of both populations in response to different stresses. (d) Variable metabolites significantly up-accumulated under combined stress.
Biomolecules 14 00160 g003
Figure 4. Heat map showing differential patterns of functional groups of protein in response to P. cinnamomi with (I) and without (D × I) watering, and in control (C) group. Co (Cordoba) and Hu (Huelva) populations.
Figure 4. Heat map showing differential patterns of functional groups of protein in response to P. cinnamomi with (I) and without (D × I) watering, and in control (C) group. Co (Cordoba) and Hu (Huelva) populations.
Biomolecules 14 00160 g004
Table 1. Summary of features of shotgun proteomic/metabolomic analysis.
Table 1. Summary of features of shotgun proteomic/metabolomic analysis.
FeatureCordobaHuelvaCommon to Both
Raw data2735/10,9833019/10,0512540/7798
≥2 peptides226124512261
Score ≥ 2226024482203
Consistent proteins159014441334
Statistical significance (p ≤ 0.05)600/1298525/1309350/503
Up-accumulated:
D/C33202
I/C49616
DxI/C43/38565/4885/123
DxI/I17290
Table 2. Significantly up-accumulated proteins classified by functional group in response to drought (D), P. cinnamomi inoculation (I), and combined stress (D × I) compared to control seedlings from asymptomatic Cordoba (Co) and Huelva (Hu) mother trees. Asterisks indicate up-accumulated proteins in D × I compared to I.
Table 2. Significantly up-accumulated proteins classified by functional group in response to drought (D), P. cinnamomi inoculation (I), and combined stress (D × I) compared to control seedlings from asymptomatic Cordoba (Co) and Huelva (Hu) mother trees. Asterisks indicate up-accumulated proteins in D × I compared to I.
Molecular FunctionProtein IDProtein DescriptionUp-AccumulatedPopulation
Carbohydrate
metabolism
qilexprot_70617Fructose-1,6-bisphosphatase, chloroplasticD × I/D × I, ICo/Hu
qilexprot_74362Beta-xylosidase/alpha-L-arabinofuranosidase 2D√I/ICo/Hu
qilexprot_27855D-tagatose-1,6-bisphosphate aldolase subunit gatYD × I, I/D × I, ICo/Hu
qilexprot_67493Phosphoglycerate mutase (2,3-diphosphoglycerate-independent)D × I, I/ICo/Hu
qilexprot_46285Phosphoenolpyruvate carboxykinase (ATP) 1D × I, I, D/D × I, ICo/Hu
qilexprot_11680Pyruvate dehydrogenase E1 component subunit alpha, mitochondrialI/D × ICo/Hu
qilexprot_45099Beta-galactosidaseI/D × I, ICo/Hu
qilexprot_65736Phosphoglycerate kinaseDCo
qilexprot_54727Malate dehydrogenaseDCo
qilexprot_57046Malate dehydrogenaseD × ICo
qilexprot_32059Glucose-6-phosphate 1-dehydrogenase, cytoplasmic isoform 2DCo
qilexprot_19946Pyruvate dehydrogenase E1 component subunit beta, mitochondrialDCo
qilexprot_10831FGGY carbohydrate kinase domain-containing proteinDCo
qilexprot_58277Aconitate hydrataseD × ICo
qilexprot_73875Malic enzymeD × I, DCo
qilexprot_20787Uridine 5’-diphosphate-sulfoquinovose synthaseD × I, ICo
qilexprot_43884Glyoxalase ID × I, ICo
qilexprot_52600Pyruvate kinaseD × I, ICo
qilexprot_12453Fructose-1,6-bisphosphataseD × I, ICo
qilexprot_32875Alcohol dehydrogenase 1D × I, ICo
qilexprot_48598Pyruvate decarboxylase 1D × I, I, DCo
qilexprot_38653Succinate dehydrogenase (ubiquinone) flavoprotein subunit, mitochondrialICo
qilexprot_18792Triosephosphate isomerase, cytosolicICo
qilexprot_38624ATP-dependent 6-phosphofructokinaseICo
qilexprot_19665RibokinaseICo
qilexprot_61660Sorbitol dehydrogenaseICo
qilexprot_49147Succinyl–CoA ligase (ADP-forming) subunit alphaI, DCo
qilexprot_48238Granule-bound starch synthase 1, chloroplastic/amyloplasticDHu
qilexprot_27919Alpha 1,4-glucan phosphorylaseD × IHu
qilexprot_55364Glyceraldehyde-3-phosphate dehydrogenaseD × IHu
qilexprot_75569Glyceraldehyde-3-phosphate dehydrogenaseD × IHu
qilexprot_4907Probable galactinol-sucrose galactosyltransferase 2D × I, IHu
qilexprot_491746-Phosphogluconate dehydrogenase, decarboxylatingD × I, I, DHu
qilexprot_16282AconitaseIHu
qilexprot_178Acetyltransferase component of pyruvate dehydrogenase complexIHu
qilexprot_50083Phosphoglycerate kinaseD × IHu
qilexprot_46354Succinyl–CoA ligase (ADP-forming) subunit alphaD × IHu
qilexprot_70366-phosphofructokinase, pyrophosphate-dependentIHu
Amino acid metabolismqilexprot_49163Aspartate aminotransferase 3, chloroplasticD/DCo/Hu
qilexprot_19886Phosphoserine aminotransferase 1, chloroplasticD/D × I, ICo/Hu
qilexprot_7937Glutamine synthetaseD × ICo
qilexprot_968Ferredoxin-dependent glutamate synthaseD × I, ICo
qilexprot_73896Carbamoyl-phosphate synthase large chain, chloroplasticD × I, ICo
qilexprot_49389Arginase 1, mitochondrialDHu
qilexprot_74641D-3-phosphoglycerate dehydrogenase 1, chloroplasticD × IHu
qilexprot_41437Glutamate synthase (ferredoxin)D × I, IHu
qilexprot_45599Glutamate synthase (ferredoxin)D × I, IHu
qilexprot_26928Glutamate synthase (ferredoxin)D × I, IHu
qilexprot_7419Serine hydroxymethyltransferaseIHu
qilexprot_55598Alpha isopropylmalate synthaseIHu
Lipid metabolismqilexprot_55785Epoxide hydrolase 3DCo
qilexprot_56587NADH-cytochrome b5 reductase-like proteinDCo
qilexprot_36359Acyl-CoA oxidase 1DCo
qilexprot_19906Acyl-CoA dehydrogenaseDCo
qilexprot_58843Acyl-coenzyme A oxidaseDCo
qilexprot_29429Acetyl-CoA acetyltransferaseD × ICo
qilexprot_66905CXE carboxylesteraseICo
qilexprot_40937CXE1 Carboxylesterase 1ICo
qilexprot_72077Lipoxygenase *D × ICo *
qilexprot_6090912-Oxophytodienoate reductase 1DHu
qilexprot_77659Phospholipase D alpha 1D × IHu
qilexprot_616803-Hydroxybutyryl-CoA dehydrataseIHu
qilexprot_10167Acetate/butyrate–CoA ligase AAE7, peroxisomalI, DHu
Nucleotide metabolismqilexprot_35697Phosphoribosylaminoimidazolecarboxamide formyltransferaseD × I, ICo
qilexprot_38489Dihydropyrimidine dehydrogenase (NADP(+)), chloroplasticD × IHu
qilexprot_29525Adenylosuccinate synthetase, chloroplasticD × I, IHu
Cellular processesqilexprot_59288MPBQ/MSBQ methyltransferaseD × ICo
qilexprot_72324Putative membrane protease, stomatin/prohibitin-like proteinD × I, DCo
qilexprot_26311Aluminum-induced protein with YGL and LRDR motifsICo
qilexprot_32288Dynamin-related protein 3AD × IHu
qilexprot_19558Dynamin-related protein 3AD × I, IHu
qilexprot_31321Carotenoid cleavage dioxygenase 1D × IHu
qilexprot_9244Turgor-responsive-like proteinD × I, IHu
qilexprot_16156Tublin binding cofactor CIHu
Developmentqilexprot_67941Apoptosis inhibitor 5-like protein API5IHu
qilexprot_56133ATPase family AAA domain-containing protein 3IHu
qilexprot_68348Sieve element occlusion protein 1IHu
Photosynthesisqilexprot_6646Chlorophyll a-b binding protein, chloroplasticDCo
qilexprot_16571Chlorophyll a-b binding protein, chloroplasticDHu
qilexprot_77212Cytochrome b559 subunit alphaDHu
Energy metabolismqilexprot_2302Ferredoxin-NADP reductaseIHu
Folding, sorting and degradationqilexprot_41199Small heat shock protein, chloroplasticI/D × I, ICo/Hu
qilexprot_73457Non-heme dioxygenase N-terminal domain-containing proteinDCo
qilexprot_24541Non-heme dioxygenase N-terminal domain-containing proteinD × I, DCo
qilexprot_10667Glycine cleavage system H protein, mitochondrialD × ICo
qilexprot_22106Xaa-Pro aminopeptidase 2D × ICo
qilexprot_76191Heat shock 70 kDa proteinD × I, ICo
qilexprot_68090Putative heat shock protein 70ICo
qilexprot_42055Proteasome subunit beta type-1ICo
qilexprot_4991Heat shock protein 40DHu
qilexprot_11703Chaperone protein DnaJ A6, chloroplasticD × IHu
qilexprot_1754222.0 kDa class IV heat shock proteinD × IHu
qilexprot_67032Proteasome subunit beta type 4D × IHu
qilexprot_36038Small heat shock proteinD × IHu
qilexprot_55307Small heat shock protein, chloroplasticD × I, IHu
qilexprot_29045Protein Cpn60 *D × IHu/Co *
qilexprot_38494Presequence protease 1, chloroplastic/mitochondrialD × I, IHu
qilexprot_31991Oligopeptidase A (partial)D × I, IHu
qilexprot_50467ClpBD × I, IHu
qilexprot_46770TCPBD × I, IHu
qilexprot_46485Chaperone protein DnaKD × I, IHu
qilexprot_55829T-complex protein 1 subunit betaD × I, I, DHu
qilexprot_68821Prolyl tripeptidyl peptidaseIHu
Redoxqilexprot_41994OxidoreductaseDCo
qilexprot_47035NADH-ubiquinone reductase 75 kDa subunitD × ICo
qilexprot_8286Monothiol glutaredoxin-S17D × ICo
qilexprot_22755Thioredoxin reductaseD × I, ICo
qilexprot_13916Glutathione reductase, chloroplasticD × I, ICo
qilexprot_4433NADPH-dependent thioredoxin reductase 3D × I, ICo
qilexprot_27576Short-chain dehydrogenase/reductase SDRICo
qilexprot_67856Sulfite reductase 1 (ferredoxin), chloroplasticICo
qilexprot_53092Thioredoxin reductase 1ICo
qilexprot_38487Glutathione reductaseICo
qilexprot_21080Putative uncharacterized protein PDID × IHu
qilexprot_21353Mitochondrial peroxiredoxin IIFD × IHu
qilexprot_67058Aldo/keto reductaseD × IHu
qilexprot_6108Peroxiredoxin-2BD × IHu
qilexprot_4209Polyphenol oxidaseD × I, DHu
qilexprot_45306NADPH HC toxin reductaseD × I, DHu
Secondary metabolismqilexprot_7930Cinnamoyl alcohol dehydrogenaseDCo
qilexprot_62609Clavaminate synthase-like proteinDCo
qilexprot_67426Cinnamyl alcohol dehydrogenase 1D × I, ICo
qilexprot_29542Chalcone synthaseICo
qilexprot_16776Protein STRICTOSIDINE SYNTHASE-LIKE 3DHu
qilexprot_29588Betaine aldehyde dehydrogenaseIHu
qilexprot_6949Glutamate decarboxylaseIHu
Stressqilexprot_16524Ornithine aminotransferaseD/D × I, DCo/Hu
qilexprot_66333Thaumatin-like protein 1aD × I, D/D × I, ICo/Hu
qilexprot_52513Thaumatin-like protein 1D × I, D/D × I, ICo/Hu
qilexprot_62485Snakin-2D × IHu
qilexprot_4320Temperature-induced lipocalin-1D × IHu
qilexprot_75875Cysteine desulfurase 1, chloroplasticIHu
qilexprot_77543Succinate-semialdehyde dehydrogenaseIHu
Transcription/Translationqilexprot_49279Plastid lipid-associated protein 3, chloroplasticI/D × I, ICo/Hu
qilexprot_32535Plastid transcriptionally active 16D × I, ICo
qilexprot_33379Plastid transcriptionally active 16D × I, ICo
qilexprot_40661Histone H2AD × I, ICo
qilexprot_59253Histone H2AI, DHu
qilexprot_31771EF-TuD × I, ICo
qilexprot_48469DNA-directed RNA polymerase subunit alphaD × I, I, DCo
qilexprot_70773Alanine–tRNA ligaseICo
qilexprot_6743650S ribosomal protein L1, chloroplasticICo
qilexprot_61172Ubiquitin-conjugating enzyme E2 variant 1DDHu
qilexprot_35357Developmentally regulated G-protein 3D × IHu
qilexprot_4713550S ribosomal protein L17, chloroplasticD × IHu
qilexprot_28988Elongation factor 2D × IHu
qilexprot_4846830S ribosomal protein S8, chloroplasticD × IHu
qilexprot_22027Histone H4D × IHu
qilexprot_71551Ubiquitin-60S ribosomal protein L40D × IHu
qilexprot_1667550S ribosomal protein L22, chloroplasticD × I, DHu
qilexprot_74256Leucine–tRNA ligase, cytoplasmic *D × I, IHu *
qilexprot_42234Glycine–tRNA ligase, chloroplastic/mitochondrial 2D × I, IHu
qilexprot_4929760S ribosomal protein L13-1IHu
qilexprot_19368Polyadenylate-binding protein RBP45IHu
qilexprot_5013760S ribosomal protein L13a-2IHu
qilexprot_3896860S ribosomal protein L21-1IHu
qilexprot_5611860S ribosomal protein L6IHu
qilexprot_46161Methionyl-tRNA synthetaseD × I, IHu
Signalingqilexprot_22041Mitochondrial Rho GTPase 1D × ICo
qilexprot_41913NADH:ubiquinone oxidoreductase complex I intermediate-associated protein 30D × I, ICo
Transportqilexprot_13099Porin/voltage-dependent anion-selective channel protein *D × I, I, DCo */Hu *
qilexprot_22308GTP-binding nuclear protein Ran-3ICo
qilexprot_20347Hexapeptide transferase family proteinICo
qilexprot_25532FerritinD × IHu
qilexprot_9762Nuclear pore complex protein NUP98AD × I, IHu
qilexprot_48381Clathrin heavy chain 2D × I, I, DHu
qilexprot_19028Polyadenylate-binding protein 8 *IHu/Co *
qilexprot_23804Protein TOC75, chloroplasticIHu
qilexprot_16395/
qilexprot_4497
V-type proton ATPase catalytic subunit A/V-type proton ATPase subunit C *IHu *
qilexprot_64280Translocon at outer membrane of chloroplasts 64IHu
qilexprot_74226PABPIHu
Miscellaneousqilexprot_29442Aldehyde dehydrogenase *DCo *
qilexprot_42491Citrate synthaseDCo
qilexprot_71234UDP-sulfoquinovose synthaseD × ICo
qilexprot_14071At2g30880/F7F1.9 *I, DHu *
Not assignedqilexprot_79169Putative uncharacterized protein Sb03g011745DCo
qilexprot_20701Putative reversibly glycosylatable polypeptideDCo
qilexprot_48145Putative uncharacterized protein At5g13030D × ICo
qilexprot_36527Fruit protein pKIWI502I, DCo
qilexprot_45328NAD(P)-binding Rossmann-fold proteinDHu
qilexprot_34141NAD(P)-binding Rossmann-fold proteinD × IHu
qilexprot_72624Spermatogenesis-associated protein 20D × I, IHu
qilexprot_63727Pdx1 *D × IHu *
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

Hernández-Lao, T.; Tienda-Parrilla, M.; Labella-Ortega, M.; Guerrero-Sánchez, V.M.; Rey, M.-D.; Jorrín-Novo, J.V.; Castillejo-Sánchez, M.Á. Proteomic and Metabolomic Analysis of the Quercus ilex–Phytophthora cinnamomi Pathosystem Reveals a Population-Specific Response, Independent of Co-Occurrence of Drought. Biomolecules 2024, 14, 160. https://doi.org/10.3390/biom14020160

AMA Style

Hernández-Lao T, Tienda-Parrilla M, Labella-Ortega M, Guerrero-Sánchez VM, Rey M-D, Jorrín-Novo JV, Castillejo-Sánchez MÁ. Proteomic and Metabolomic Analysis of the Quercus ilex–Phytophthora cinnamomi Pathosystem Reveals a Population-Specific Response, Independent of Co-Occurrence of Drought. Biomolecules. 2024; 14(2):160. https://doi.org/10.3390/biom14020160

Chicago/Turabian Style

Hernández-Lao, Tamara, Marta Tienda-Parrilla, Mónica Labella-Ortega, Victor M. Guerrero-Sánchez, María-Dolores Rey, Jesús V. Jorrín-Novo, and María Ángeles Castillejo-Sánchez. 2024. "Proteomic and Metabolomic Analysis of the Quercus ilex–Phytophthora cinnamomi Pathosystem Reveals a Population-Specific Response, Independent of Co-Occurrence of Drought" Biomolecules 14, no. 2: 160. https://doi.org/10.3390/biom14020160

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