How plants handle multiple stresses: hormonal interactions underlying responses to abiotic stress and insect herbivory
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Adaptive plant responses to specific abiotic stresses or biotic agents are fine-tuned by a network of hormonal signaling cascades, including abscisic acid (ABA), ethylene, jasmonic acid (JA) and salicylic acid. Moreover, hormonal cross-talk modulates plant responses to abiotic stresses and defenses against insect herbivores when they occur simultaneously. How such interactions affect plant responses under multiple stresses, however, is less understood, even though this may frequently occur in natural environments. Here, we review our current knowledge on how hormonal signaling regulates abiotic stress responses and defenses against insects, and discuss the few recent studies that attempted to dissect hormonal interactions occurring under simultaneous abiotic stress and herbivory. Based on this we hypothesize that drought stress enhances insect resistance due to synergistic interactions between JA and ABA signaling. Responses to flooding or waterlogging involve ethylene signaling, which likely reduces plant resistance to chewing herbivores due to its negative cross-talk with JA. However, the outcome of interactions between biotic and abiotic stress signaling is often plant and/or insect species-dependent and cannot simply be predicted based on general knowledge on the involvement of signaling pathways in single stress responses. More experimental data on non-model plant and insect species are needed to reveal general patterns and better understand the molecular mechanisms allowing plants to optimize their responses in complex environments.
KeywordsDrought Flooding Herbivory Hormonal cross-talk Induced resistance Stress responses
ABA-responsive element binding factor
Apetala2/ethylene response factor
Constitutive triple response1
ERF-associated amphiphilic repression
EIN3-binding F-box protein
Jasmonate-ZIM domain corepressor
Novel interactor of JAZ
Type 2C protein phosphatase
Pyrabactin resistance1/PYR-like/regulatory component of ABA receptor
Skp, Cullin, F-box containing
Sucrose non-fermenting1-related protein kinase2 protein
Groucho/Tup1-type co-repressor TOPLESS
Vegetative storage protein
Plants have to constantly cope with a suite of biotic and abiotic stress factors. Their performance thus depends on the ability to quickly perceive changes in the environment and to express an adaptive response. Much effort has been made to understand the molecular mechanisms underlying plant adaptive responses because of their potential to improve agricultural production under adverse conditions.
Plant molecular responses to single abiotic stresses, such as drought, soil flooding, high or low temperatures, as well as to biotic interactions, such as insect herbivory and pathogen attacks, have been gradually elucidated. These responses are modulated by a complicated network of signaling pathways induced by a variety of small molecules, including Ca2+ signaling (Seybold et al. 2014), reactive oxygen and nitrogen species (Wang et al. 2013; Baxter et al. 2014) and phytohormones (Peleg and Blumwald 2011; Pieterse et al. 2012; De Vleesschauwer et al. 2014; Kazan 2015). Hormones and hormonal cross-talk play an important role in the molecular mechanisms that optimize plant responses to stresses which commonly occur simultaneously in the environment, such as abiotic stresses and herbivory. Over the years several reviews have discussed cross-talk between defense-related hormonal pathways in plants challenged by different herbivores, different pathogens or combinations thereof (e.g. Pieterse et al. 2002; Erb et al. 2008; De Vleesschauwer et al. 2014). Independently, ecophysiologists acquired substantial knowledge on the role of hormonal signaling pathways in responses to abiotic stresses, such as drought, flooding and shading (e.g. Peleg and Blumwald 2011; Voesenek and Bailey-Serres 2015). Since long, several ecological studies revealed that (induced) resistance to herbivores can be affected by simultaneously occurring abiotic stresses, such as drought (English-Loeb et al. 1997; Huberty and Denno 2004; Khan et al. 2010; Gutbrodt et al. 2011; Tariq et al. 2013). However, only recently there has been an increased interest to identify the molecular mechanisms underlying these interactive effects (Lu et al. 2015; Davila Olivas et al. 2016; Foyer et al. 2016; Nguyen et al. 2016). For this reason, this a good moment for merging the knowledge on hormonal signaling in abiotic and biotic induced responses with the aim to come to a unified conceptual framework of how the signaling pathways induced by different stresses may interact. Thereby, we focus on the interactions between herbivore induced responses and water related stresses, specifically drought and flooding. Both drought and soil flooding or waterlogging are common phenomena in natural and agricultural ecosystems, and the frequency of their occurrence is expected to increase due to climate change (IPCC 2013). Here, we first review the most recent knowledge on how hormonal pathways regulate plant responses to single stresses. Then we discuss how interactions between these pathways may modulate defense responses in plants under combined stress conditions, considering that hormonal cross-talk may serve to optimize plant performance in complex environments. Finally, we will specify which testable hypotheses follow from our current knowledge that may help to better understand the role of signaling interactions in plants under multiple stresses.
Regulation of induced plant responses to insect herbivores
Due to herbivore-specific HAMPs (Acevedo et al. 2015; Xu et al. 2015), other signaling hormones in addition to JA are induced upon feeding to tailor the defenses against the attacker. The signal signature that is induced for a part is due to differences in herbivore feeding strategies. Piercing-sucking insects, such as aphids, have a ‘stealthy feeding strategy’ (De Vos et al. 2005) that avoids massive cell damage. On the other hand, the salivary sheet lining their mandibles contains specific enzymes that interact with the cells along the stylet path (Foyer et al. 2016). Aphid feeding thus induces a significantly different set of signaling pathways and transcripts than chewing herbivores, that cause more cell damage and possess different elicitors in their saliva (De Vos et al. 2005; Bidart-Bouzat and Kliebenstein 2011). On the other hand, herbivore-induced signal signatures can also be species-specific within herbivore feeding guilds. For example, feeding by caterpillars of Manduca sexta induces the accumulation of JA and ET, whereas Spodoptera exigua caterpillars induce JA and salicylic acid (SA) in Nicotiana attenuata (Diezel et al. 2009). In contrast, S. exigua induces JA and ET accumulation in maize (Zea mays) and Arabidopsis thaliana (Schmelz et al. 2003; Rehrig et al. 2014), whereas Pieris rapae triggers JA and ABA levels in the latter species (Vos et al. 2013b). Simultaneous SA and JA accumulation also occurs upon herbivory by the Colorado potato beetle (Leptinotarsa decemlineata) and the mealy bug (Phenacoccus solenopsis) on tomato plants (Solanum lycopersicum) (Chung et al. 2013; Zhang et al. 2015a). Although not all hormones were measured in each study, this strongly suggests that plant hormonal responses to herbivores depend on the specific plant–insect interaction. Cross-talk between JA and other phytohormones has been proposed to fine-tune plant defense responses to specific attackers (Pieterse et al. 2012; Erb et al. 2012).
ABA in defense regulation
A key question is where in the signaling cascades interactions between JA and ABA occur. The requirement of normal ABA biosynthesis for JA production (Adie et al. 2007), the COI-dependency of the ABA-induced MYC2 expression (Lorenzo et al. 2004) and the fact that methyljasmonate (MeJA) still induces LAP and PIN2 in ABA-deficient mutants (Carrera and Prat 1998), suggest that the interaction occurs upstream of JA signaling. Indeed, JA and ABA mutually enhance their biosynthesis (Adie et al. 2007; Fan et al. 2009; Brossa et al. 2011). Mechanistic details on such interaction, however, are still lacking. Interestingly, it has been shown that interactions may also occur more downstream. A mechanism similar to the suppression of JA-induced TFs by JAZ–NINJA–TPL was identified for the ABA-dependent TF ABI5 (ABA insensitive5) in Arabidopsis. ABI5 binding proteins (AFPs) are NINJA homologs and contain the EAR motif to interact with the corepressors TPL or TPRs for ABI5 inactivation (Pauwels et al. 2010). Although the tested AFPs do not interact with JAZ1, this similarity nevertheless suggests that the JA–ABA interaction may exist at this JAZ–NINJA connection, downstream of JA biosynthesis, dependent on the binding specificity of different JAZs to NINJA or ABPs. This is supported by the recent finding that ZmJAZ14, a JAZ protein in maize, is involved in both JA and ABA signaling (Zhou et al. 2015).
ET in defense regulation
Like JA, ET signaling upon feeding by insect herbivores is common among plants. However, ET has very variable effects on defense regulation, acting more as a modulator of herbivore-induced responses than a direct elicitor (von Dahl and Baldwin 2007). Very few plant defenses are directly regulated by ET. One known case is the induction of defensive 1-cysteine protease (Mir1-CP) against both chewing Spodoptera frugiperda and phloem-feeding Rhopalosiphum maidis in maize. JA also induces Mir1-CP expression upon S. frugiperda feeding, which is dependent on ET signaling, since MeJA treatment had no effect on Mir1-CP induction in maize plants with blocked ET signaling (Ankala et al. 2009; Louis et al. 2015). In many cases, ET has been shown to modulate JA-mediated insect defenses, similar to the well-documented ET–JA synergism in regulating defensive genes induced upon infestation by necrotrophic pathogens, such as PDF1.2 and PR1, 4 and 5, via their co-regulation of the AP2/ERF TFs ERF1 and ORA59 (Lorenzo et al. 2003; Pré et al. 2008). For example, ET signaling contributes to the JA-mediated volatile emission upon S. exigua herbivory on maize or Bemisia tabaci infestation on Arabidopsis (Schmelz et al. 2003; Zhang et al. 2013). The wound-induced expression of tomato PIN2 requires both intact JA and ET pathways, but compromising ET signaling does not affect the M. sexta-increased PI transcript levels in N. attenuata (O’Donnell et al. 1996; Onkokesung et al. 2010a). The complex involvement of ET in modulating herbivore/JA-induced defense responses also shows in nicotine biosynthesis. Defective ET signaling in N. attenuata, in one case, resulted in reduced basal nicotine contents but enhanced inducibility of nicotine biosynthesis after M. sexta herbivory (von Dahl et al. 2007), but in other experiments, it did not affect basal levels and attenuated JA-induced nicotine response (Shoji et al. 2000; Winz and Baldwin 2001; Onkokesung et al. 2010a). Nevertheless, both maize and N. attenuata with compromised ET signaling are more susceptible to M. sexta and S. frugiperda, respectively, demonstrating the role of ET in fortifying plant defenses (Harfouche et al. 2006; Onkokesung et al. 2010a). On the other hand, ET signaling, via ERF1/ORA59 and their upstream TFs EIN3/EIL1 (Fig. 1c), also inhibits the JA/ABA-co-induced MYC2 and subsequently MYC2-mediated defense-related genes in Arabidopsis (Lorenzo et al. 2004; Zhu et al. 2011; Song et al. 2014a). Consequently, disruptions of ET perception and signaling in etr1, ein2-1 and ein3/eil1 mutants all increase Arabidopsis resistance to the generalist insects S. exigua and S. littoralis, whereas ET application results in plant susceptibility. ET signaling, however, does not influence the responses and resistance of Arabidopsis to the specialists Plutella xylostella and Pieris rapae (Stotz et al. 2000; Mewis et al. 2005; Bodenhausen and Reymond 2007; Song et al. 2014a).
Recent findings also shed light on the mechanism of how these hormonal cascades interact (Fig. 2). Several JA signaling repressor JAZs bind to and inactivate EIN3/EIL1 and recruit HDA6 (histone deacetylase6) to repress EIN3/EIL1-dependent transcription (Zhu et al. 2011). Upon herbivore-induced ET and JA accumulation, ET signaling stabilizes EIN3/EIL1 while JAZ removal by JA signaling disassociates HDA6-EIN3/EIL1 and activates EIN3/EIL1 to transcribe downstream ERF1/ORA59. Interestingly, the ABA-inducible MYCs also physically interact with EIN3/EIL1, which mutually inhibits their function. Moreover, MYC2 indirectly promotes proteasomal degradation of EIN3 by enhancing EBF1 expression (Song et al. 2014a; Zhang et al. 2014). This illustrates how the balance between ABA and ET signaling fine-tunes JA-mediated defenses induced by insect herbivory.
SA antagonizes herbivore-induced defenses
SA signaling mediates defense responses to hemi(biotrophic) pathogens (Derksen et al. 2013). This is achieved via its receptor and regulator NPR1 (nonexpressor of PR genes1) and the action of two NPR1 homologs, NPR3 and NPR4, which are also SA receptors and mediate NPR1 degradation in SA-concentration-dependent manners (Kuai et al. 2015). In some cases, SA-induced defense responses are effective against sedentary sucking insects, such as aphids (Klingler et al. 2009; Zhang et al. 2015b). SA accumulation in host plants can be induced by HAMPs and can also be exploited by insects to suppress JA-mediated defenses (Thaler et al. 2012; Caarls et al. 2015). Glucose oxidase in S. exigua oral secretion induces an SA burst in N. attenuata, which suppresses JA and ET accumulation (Diezel et al. 2009). Moreover, several insects carry viruses or microbes that trigger SA accumulation. Tomato spotted wilt virus transmitted by thrips feeding increases SA concentrations in Arabidopsis, resulting in increased performance and preference of thrips for infected plants (Abe et al. 2012). Flagellin from Pseudomonas sp. present on the mouth parts of L. decemlineata can induce SA accumulation in tomato leaves upon feeding, thereby suppressing JA-dependent defenses, such as PIs and polyphenol oxidases, and herbivore-induced resistance (Chung and Felton 2011; Chung et al. 2013).
The SA antagonism of JA-dependent defenses occurs downstream of JA biosynthesis and independently of the COI1-JAZs pathway. It inhibits defenses mediated by both ABA and ET signaling (Fig. 2). Disruption of SA accumulation or NPR1 function thus increases resistance to several chewing and sucking insects (Stotz et al. 2002; Mewis et al. 2005; Zarate et al. 2007). Cytosolic NPR1 activity is also a mediator of the SA–JA antagonism, which, however, is bypassed if herbivores also induce ET accumulation (Spoel et al. 2003; Leon-Reyes et al. 2009; Van der Does et al. 2013). Moreover, SA leads to degradation of the JA/ET-responsive ORA59 and suppresses JA/ET-responsive GCC-box-containing genes, including ORA59, by recruiting the SA-induced GRX480 (Glutaredoxin480) to their promoters. This inhibits the positive transcription regulators class II TGAs thereby repressing JA/ET-induced responses (Zander et al. 2012, 2014; Van der Does et al. 2013). Less is known about how SA inhibits JA/ABA-responsive defenses. Potential points of convergence in this interaction are WRKY TFs. WRKY62 and WRKY70 regulate the SA–JA antagonism in defense responses and ABA-responsive defense genes (Li et al. 2004; Mao et al. 2007), whereas WRKY18, WRKY40 and WRKY60 are ABA-responsive and blocked by SA (Xu et al. 2006; Chen et al. 2010).
Growth hormones in defense regulation
In conclusion, interactions between hormonal signaling cascades help plants to fine-tune their defenses against a specific attacker. Conversely, insects may have the ability to interfere with these hormonal interactions to suppress defense responses to their benefit.
Hormonal regulation of plant responses to abiotic stresses
Due to its involvement in many developmental processes, such as shoot growth inhibition, stomatal movement, leaf senescence and primary root growth, ABA is considered as a master regulator of responses to abiotic stresses, such as drought, salt, heat and high light intensity (Fig. 3; Sharp et al. 2004; Daszkowska-Golec and Szarejko 2013; Liang et al. 2014). JA, SA and BRs also interact with ABA to promote stomatal closure, prevent water loss during osmotic stresses, and induce leaf senescence for resource remobilization (Hossain et al. 2011; Miura et al. 2012; Qi et al. 2015). Stomatal opening, on the other hand, is promoted by CKs and AUXs, while leaf senescence is inhibited by GAs, CKs and AUXs (Daszkowska-Golec and Szarejko 2013; Jibran et al. 2013). ET is also considered as a major inducer of leaf senescence (Kim et al. 2015), whereas ABA and ET show a clear antagonism in regulating stomatal movement (Tanaka et al. 2005) and shoot and root growth under drought (Fig. 3; Sharp and LeNoble 2002; Sharp et al. 2004; Yin et al. 2015). Similarly, ABA antagonizes ET in controlling flooding responses, such as shoot elongation, leaf hyponasty and adventitious root formation (Voesenek and Bailey-Serres 2015). The ET-mediated responses to flooding as well as shading, on the other hand, are synergistically regulated by GAs, BRs and AUXs (Cox et al. 2006; Gommers et al. 2013; van Veen et al. 2013; Pierik and Testerink 2014; Ayano et al. 2014). These insights demonstrate that plant responses to abiotic stresses and defense responses are controlled by the same interactive hormonal network.
Hormonal interactions regulate growth-defense tradeoffs
The simultaneous roles of hormones in plant development and defense led to the view that they interact to prioritize resources towards growth or defense. This is a relevant concept when considering abiotic-biotic stress interaction, as abiotic stress usually severely impairs plant growth. The probability to survive under adverse conditions may increase if limited resources are efficiently allocated to tolerate abiotic stresses or to defend valuable tissues against herbivores (Van Dam and Baldwin 2001; Skirycz and Inzé 2010; Atkinson and Urwin 2012; Vos et al. 2013a). There is substantial evidence that this happens in case of pathogen attack (Denancé et al. 2013; Huot et al. 2014); and the regulation of the growth-defense tradeoff when plants are under combined abiotic stress and insect herbivory may also follow this strategy. The best illustrated hormonal interaction to regulate growth-defense tradeoffs is between JA and GA. Similar to their interaction in regulating defenses, JA also antagonizes GA-dependent growth responses via JAZs-DELLAs. In the absence of JA, Arabidopsis JAZ9 binds the DELLA protein RGA, thereby preventing it from inhibiting the growth promoting TF PIF3 (phytochrome-interacting factor3). Upon herbivory, JA induces JAZ degradation and delays GA-mediated DELLA degradation, allowing DELLAs to inhibit GA-dependent plant growth responses (Yang et al. 2012). Furthermore, JA in concert with ET repress cell cycle processes and expansion of leaf cells by suppressing the cell expansion enhancers, AUXs. Conversely, AUXs were proposed as repressors of JA synthesis and JA/ET-dependent nicotine response. AUXs and JA, however, synergistically constrain N. attenuata regrowth after M. sexta herbivory (Shi et al. 2006; Onkokesung et al. 2010b; Noir et al. 2013; Machado et al. 2013). ABA and JA signaling also synergistically suppress plant growth and yield under drought stress (Kim et al. 2009; Harb et al. 2010). On the other hand, ABA signaling antagonizes nicotine biosynthesis in N. tabacum roots via PYL4, an ABA receptor that controls root metabolic responses to drought and drought resistance; whereas JA suppresses PYL4 expression in roots but enhances it in leaves (Fig. 2; Lackman et al. 2011; Pizzio et al. 2013; González-Guzmán et al. 2014). These examples show that the growth-defense balance is tightly regulated by a sophisticated network of hormonal cross-talk.
Furthermore, the growth-defense balance can also be controlled by master mediators that regulate multiple hormonal cascades. For example, the Arabidopsis CML42 (calmodulin-like protein42) suppresses both JA-dependent insect resistance and drought-responsive ABA accumulation; and the rice WRKY70 induces JA but represses GA biosynthesis and signaling (Vadassery et al. 2012; Li et al. 2015). However, the WRKY70-dependent prioritization of defenses over growth leads to resistance to the stem borer Chilo suppressalis but susceptibility to the brown planthopper Nilaparvata lugens, suggesting that defense prioritization is species-specific (Li et al. 2015).
Hormonal regulation of defense responses under combined stresses
Despite our extensive knowledge on hormonal regulatory pathways and their interactions, predicting plant responses and phenotypes under combined biotic and abiotic stress remains difficult. Hormonal cascades may interact in non-additive manners and the results may enhance plant tolerance/resistance to one stress but not to another (Atkinson and Urwin 2012; Stam et al. 2014; Suzuki et al. 2014; Foyer et al. 2016). Also at the transcriptional level, stress combinations evoke responses that are unique or unpredictable from the responses to single stresses even if the points of convergence are known (Rasmussen et al. 2013; Atkinson et al. 2013). Abiotic stresses, such as drought, salt, heat or flooding, have been found to exert both positive and negative influences on resistance to pathogens and insect herbivores (DeLucia et al. 2012; Suzuki et al. 2014; Ramegowda and Senthil-Kumar 2015). For example, the strong JA-ABA synergism in many stress responses suggests that drought may promote plant resistance to herbivores. However, drought increases defense responses and render plants resistant to insect herbivores in some cases, but reduces defenses and resistance in others (English-Loeb et al. 1997; Huberty and Denno 2004; Khan et al. 2010; Gutbrodt et al. 2011; Tariq et al. 2013; Nguyen et al. 2016).
Recently, a few studies have tried to dissect hormonal interactions occurring under simultaneous abiotic stress and herbivory. In Brassica oleracea plants, drought and Mamestra brassicae herbivory interactively regulate the emission of volatile organic compounds (VOCs) as an indirect defense (Weldegergis et al. 2015). While drought alone induces SA accumulation and reduces the emissions of several VOCs, it also reduces herbivore-induced JA accumulation and consequently alters the herbivore-induced emissions of these VOCs. This resulted in M. brassicae moth preference to lay eggs on drought-stressed plants but no differences in larval performance compared to those on well-watered plants. Interestingly, ABA accumulation was observed upon herbivory but not in drought-stressed plants, possibly due to the intermittent drought stress regime with recovery periods, during which ABA catabolism may be induced (Wang 2002; Fleta-Soriano et al. 2015). In contrast, drought enhanced resistance of Solanum dulcamara plants to S. exigua larvae (Nguyen et al. 2016). Both dought and herbivory induced ABA and JA accumulation in S. dulcamara. Transcriptomic analyses showed drought further enhanced several herbivore-induced defense-related responses, such as terpenoid biosynthesis and PIs (Nguyen et al. 2016). Similarly, drought increased leaf ABA and JA concentrations, JA-dependent defense and Medicago truncatula plant resistance to the pea aphids Acyrthosiphon pisum (Gou et al. 2016). Therefore, the synergistic interaction between ABA and JA signaling is suggested to play an important role in regulating plant defense under drought. This is supported by the finding that ABA signaling is required for the full activation of VOC emission and JA-responsive direct defenses in N. attenuata (Dinh et al. 2013). Silencing of an ABA catabolism suppressor, NaHER1 (herbivore elicitor-regulated1), in N. attenuata resulted in reduced levels of these defense responses upon herbivory by M. sexta as well as plant resistance. Moreover, NaHER1-silenced plants are also drought-sensitive, suggesting that NaHER1 serves as a connection between responses to the two stresses.
On the other hand, there may be mechanisms underlying plant increased resistance to herbivores under drought that are independent of the ABA-JA signaling interaction. In maize, drought and root herbivory by Diabrotica virgifera synergistically enhance levels of ABA and ABA-dependent defense gene transcripts in the leaves and resistance to the leaf herbivore Spodoptera littoralis (Erb et al. 2011). However, leaf water loss, but not the induced ABA level itself, was strongly correlated to the resistance. Therefore, hydraulic changes induced by drought and root herbivory were suggested to play a role in inducing ABA/JA-independent signaling that increases resistance to above-ground herbivores.
Interestingly, there is much less knowledge on the effect of soil flooding on herbivore resistance, possibly because most model plants are crops and drought is more commonly recognized as a problem in production systems around the world than flooding or waterlogging. Only recently Lu et al. (2015) studied the hormonal interaction between flooding and root herbivory in rice. The study showed, however, that hormonal responses to root herbivory or artificial wounding was not altered by flooding. In S. dulcamara, soil flooding increased ABA, but not JA, levels in the leaves and suppressed many transcriptional responses involved in primary and secondary metabolism, including defense-related responses. These changes, however, did not affect the plant resistance to S. exigua larvae (Nguyen et al. 2016).
These insights, though not always as expected beforehand, are invaluable to understand how plants fine-tune their responses to specific combinations of stress conditions. Based on what we know about the interactions between hormones and a few experimental studies, we suggest that drought in general may enhance resistance because of the synergistic effect of ABA and JA signaling. Drought and herbivory both significantly reduce plant performance but when a drought period is followed by herbivory, the negative effect is more than additive (Davila Olivas et al. 2016). Thus it may be functional for a drought-stressed plant to reduce additional damage by increasing herbivore defenses. It should be stressed that the resulting effect on the herbivore may differ, depending on its level of host plant specialization or feeding strategy (Foyer et al. 2016). On the other hand, flooding or waterlogging elicits the production of ET. The interaction of ET with herbivore-induced responses is not as uniform as that found for ABA. Hence it can be expected that flooding has a neutral or negative effect on plant resistance. It is likely that plants surrounded by water (temporarily) do not receive as many herbivores as a plant on dry land. Therefore, it is conceivable that flooded plants may increase their performance more if they invest in overcoming the negative effects of hypoxia, for example by producing aerenchymous adventitious roots (Dawood et al. 2016).
Simultaneously occurring stresses may compromise plant hormonal homeostasis. If this leads to a misregulation of stress responses, it may result in lower plant survival or yield reduction. Therefore, a better understanding of these hormonal interactions is essential to attain resilient and ‘multitasking’ crop plants that can perform well in adverse and variable environments. However, hormonal interactions under combined stresses cannot be simply inferred from experiments applying single stresses. Thus, more studies on plants responses to multiple and simultaneous stresses, especially abiotic stresses and insect herbivory, are needed to gain insights on how hormones truly interact under such—more natural—conditions. Furthermore, downstream changes induced by multiple stresses should be investigated by untargeted high-throughput approaches, such as transcriptomics, proteomics or metabolomics to obtain a broad and precise view of the regulatory and phenotypic consequences of hormonal interactions. Finally, plant performance or resistance should be assessed to validate the ecological effects of these molecular interactions. Given the common co-occurrence of abiotic and biotic stresses, the response to stress combination is likely to be under strong natural selection. Thus, we argue that the seemingly low level of conservation in the effect of abiotic stress on herbivore defenses, depending on plant and insect species, does not represent random output of the signaling network. Rather, it may be the consequence of divergent choices in prioritization and thus resource allocation that only appear upon combined stress application. Recognition of general patterns then requires availability of a larger set of data. Preferably, experiments should be carried out using plant species thriving in both wet and dry habitats as well as with a diverse natural herbivore community. This will allow us to ‘learn from nature’ whether plants can be selected to handle multiple stresses at the same time while maintaining a high performance.
This project is funded by a grant (844.10.001) in the ALW-Ecogenomics program from the Netherlands Organisation for Scientific Research (NWO). NMvD gratefully acknowledges the support of the German Centre for Integrative Biodiversity Research (iDiv) Halle-Jena-Leipzig funded by the German Research Foundation (FZT 118).
Duy Nguyen took the lead in writing this review, with active contributions of Nicole M. van Dam, Ivo Rieu, and Celestina Mariani during the writing process.
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