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Update on Ecological Genomics of Plant-Insect Interactions

Ecological Genomics of Plant-Insect Interactions: From Gene to Community^1,[C]

Laboratory of Entomology, Wageningen University, 6700 EH Wageningen, The Netherlands

A major challenge for current biology is to integrate research approaches that address different levels of biological organization, from subcellular mechanisms to functions in ecological communities. The study of plant-insect interactions provides interesting options for this. Ample information at the subcellular and the individual level is available on the one hand, while important insight in the (community) ecology of insect-plant interactions is available as well (Kessler and Baldwin, 2002; Bezemer and van Dam, 2005; Schoonhoven et al., 2005; Kessler and Halitschke, 2007; Snoeren et al., 2007). A major step forward will be to connect these research fields, and encouraging steps have been made during the past years.

Insects make up the most diverse and abundant group of plant consumers. A total of 45% of the approximately 1 million described insect species feed on plants (Schoonhoven et al., 2005). Given that the estimated number of insects species is several times higher (Stork, 2007), the number of herbivorous insect species is likely to be much higher too. Herbivorous insects may attack plants below ground as well as above ground, and not a single organ remains free of potential insect attack (Bezemer and van Dam, 2005; Schoonhoven et al., 2005). Plants have evolved a range of defenses to ward off this diversity of attackers, including constitutive and induced defenses (Walling, 2000; Kessler and Baldwin, 2002; Schoonhoven et al., 2005). Because an individual plant may potentially be under the attack of tens or hundreds of consumer species, it is impossible to have constitutive defenses against all these attackers. Furthermore, whether the potential enemies will indeed attack a certain individual is usually unpredictable. Moreover, constitutive defenses may also select for adaptation in herbivorous insects (Agrawal and Karban, 1999). Thus, inducible defenses may tune the defensive needs to the actual presence of attackers and in addition may transform plants into moving fortresses that have a modified phenotype and consequently retard adaptation in herbivores (Agrawal and Karban, 1999; Kahl et al., 2000). For instance, Nicotiana attenuata plants respond to mechanical damage with the induction of nicotine, a neurotoxin affecting most herbivores (Kahl et al., 2000). However, the plant has an attenuated nicotine induction in response to feeding damage by caterpillars of the specialist tobacco hornworm Manduca sexta, which can tolerate considerable levels of nicotine and furthermore can exploit it in its own defense against pathogens and parasitic wasps (Krischik et al., 1988). Instead, N. attenuata responds to Manduca feeding with the production of volatile terpenoids that can attract parasitic wasps that attack the caterpillars (Kahl et al., 2000).

Induced defenses comprise direct defenses, such as secondary metabolites and protease inhibitors that negatively affect herbivore growth and survival, as well as indirect defenses, such as herbivore-induced plant volatiles and herbivore-induced extrafloral nectar that enhance the effectiveness of natural enemies of herbivores, such as parasitoids or predators (Kessler and Baldwin, 2002; Heil et al., 2004; Kappers et al., 2005; D'Alessandro and Turlings, 2006; Mumm and Hilker, 2006). The induction of defenses is often specific for the attacker species (Kahl et al., 2000; Dicke et al., 2003; Arimura et al., 2005) and an individual plant can therefore express a range of different phenotypes where each phenotype has its own effects on the members of the community, such as herbivores, carnivores, and pollinators (Dicke et al., 2004; Kessler et al., 2004; Kessler and Halitschke, 2007; Bruinsma and Dicke, 2008). For instance, previous attack may influence the induction of subsequent defenses in specific ways and thereby affect herbivore and plant fitness (Kessler and Baldwin, 2004; Voelckel and Baldwin, 2004b). As a consequence, the investigation of induced defenses requires an approach that considers the total community as well as individual interactions among community members (Kessler and Baldwin, 2004; Kessler et al., 2004; Bruinsma and Dicke, 2008). Integrating this approach at different levels of biological organization is a major challenge that will link mechanisms in terms of transcriptional induction, metabolite induction, and ecological interactions (Mercke et al., 2004). After identifying genes that are involved in specific interactions, their ecological function should be investigated in in-depth studies addressing e.g. genotypes in which the gene of interest has been silenced (Paschold et al., 2007). In doing so, gene function is investigated at different levels of biological integration, and this provides novel insight into the ecological function of particular genes (Fig. 1).

View larger version (44K): [in this window] [in a new window] [as a PowerPoint slide]   Figure 1. Individual interactions such as those between Brassica plants and P. brassicae caterpillars result in effects at different levels of biological integration, from subcellular processes to community dynamics, and from the expression of genes involved in biosynthesis of induced plant volatiles to effects on attraction of parasitic wasps and changes in community dynamics. Pictures courtesy of Hans M. Smid, www.bugsinthepicture.com. [See online article for color version of this figure.]

	SIGNAL TRANSDUCTION

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	GLOBAL TRANSCRIPTOME CHANGES IN RESPONSE TO HERBIVORY

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In response to insect herbivory, plants undergo an extensive rearrangement of gene transcription. Hundreds, up to several thousands, of genes can be up- or down-regulated. The number of studies addressing large-scale transcriptomic changes in response to insect herbivory is steadily increasing (e.g. Heidel and Baldwin, 2004; Reymond et al., 2004; Voelckel and Baldwin, 2004a; De Vos et al., 2005; Bodenhausen and Reymond, 2007; Broekgaarden et al., 2007; Kempema et al., 2007). This provides extensive new information about the first steps of plant responses to insect attack.

It appears that there can be considerable differences in the transcriptomic response of a plant to different attackers (Voelckel and Baldwin, 2004a; De Vos et al., 2005) as well as responses of different plant cultivars in response to the same herbivore (Broekgaarden et al., 2007). For instance, damage by cell content-feeding thrips (F. occidentalis) and chewing-biting caterpillars (P. rapae) results in similar numbers of differentially expressed genes (around 200). Yet, the gene sets differentially responding to these two herbivore species are quite different: of the JA-responsive genes, only 9% to 17% show similar responses to F. occidentalis and P. rapae (De Vos et al., 2005). Even in response to insects with a similar feeding mode, such as aphids (Myzus persicae) and whiteflies (B. tabaci), the transcriptomic changes can be quite different (Kempema et al., 2007). Plant genotypes can also differ in transcriptional responses to the same herbivore. Two white cabbage (Brassica oleracea var. capitata) cultivars differ considerably in the global gene expression patterns induced by P. rapae caterpillar attack (Broekgaarden et al., 2007). The two cultivars also differ in the level of direct defense against caterpillar (P. rapae) feeding. Several of the transcriptomic differences involve genes that may have an impact on P. rapae performance and may underlie the different mechanisms of direct defense present in the two cultivars. Linking studies at the level of transcriptomic changes with studies on metabolite production and expression of different levels of resistance will provide new insight into the mechanisms underlying variation in ecological interactions.

In Arabidopsis, mechanical damage induces a different transcript profile than P. rapae feeding (Reymond et al., 2000). Many wound-induced genes were induced either to a lesser extent or not at all by larval feeding, thus indicating that larval feeding strategies may minimize the induction of defense-related genes (Reymond et al., 2000). In contrast, similar expression patterns in response to feeding by both specialist P. rapae and generalist Spodoptera littoralis caterpillars have been found (Reymond et al., 2004). However, the transcript profiles were different in ET and SA mutants (Bodenhausen and Reymond, 2007). Native tobacco plants, N. attenuata, are able to distinguish between attack by two generalist (S. littoralis and Heliothis virescens) and a specialist (M. sexta) herbivore of the same feeding guild (Voelckel and Baldwin, 2004a). Despite the large overlap in transcriptional responses to all three lepidopteran larvae, these plants responded more similarly to attack from the two generalists than to attack from the specialist. The fatty acid-amino acid conjugate profiles of S. littoralis and H. virescens regurgitates are almost identical, but M. sexta regurgitate differs from the others and is dominated by fatty acid-Glu conjugates (Voelckel and Baldwin, 2004a). It is interesting to note that attack of Arabidopsis by the phloem-feeding aphid M. persicae and the silverleaf whitefly B. tabaci, which inflict relatively low levels of cell damage, results in the differential expression of many more genes than feeding by the chewing-biting caterpillar P. rapae, even when one should be careful in quantitatively comparing studies made in different laboratories (De Vos et al., 2005; Kempema et al., 2007).

Full transcriptomic analyses provide important insight into overall changes in gene expression, usually at a limited number of time points. Yet, quantitative real-time PCR can yield detailed dynamics of transcriptomic changes for a limited number of genes of particular interest (e.g. Zheng et al., 2007). Such analyses are of special interest to ecologists as they can provide information on the phenotypic plasticity in the expression of specific genes of interest that can be linked to the dynamics of interactions of the plant with members of the community.

	EFFECTS OF A FIRST ATTACK ON SUBSEQUENT BIOTIC INTERACTIONS

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In nature, plants are seldom attacked by a single herbivore species and most likely they are challenged by different herbivores and pathogens sequentially or simultaneously. After having been ignored for a long time, there is a renewed appreciation of the occurrence of plant-mediated competition between herbivorous insects and between insects and pathogens (Kaplan and Denno, 2007). However, investigations on the mechanisms underlying the effects of defenses induced by a first attack on other members of the community have so far been limited. Linking the ecological phenomena of community effects of plant infestation with mechanical information is now in reach with a possibility to understand ecological phenomena in the context of their mechanistic background.

Peanut (Arachis hypogaea) plants that are infected with the white mold fungus Sclerotium rolfsii are preferred by beet armyworm moths (Spodoptera exigua) for oviposition. However, beet armyworm moth larval feeding on fungus-infected plants results in enhanced risks of attack by parasitic wasps; volatiles emitted from plants infested with fungus plus caterpillars were more attractive than volatiles emitted from plants infested only with caterpillars (Cardoza et al., 2003). Arabidopsis plants infested by the caterpillar P. rapae are more resistant to several plant pathogens, including Turnip crinkle virus (De Vos et al., 2006). This was surprising because resistance to Turnip crinkle virus is dependent on SA, while P. rapae induces JA and ET but does not induce SA. It appeared that caterpillar-induced ET primed Arabidopsis for augmented expression of SA-dependent defenses (De Vos et al., 2006). Tomato plants damaged by aphids (Macrosiphum euphorbiae) were preferred for oviposition by beet armyworm moths, and the larvae consumed more on aphid-infested plants than on uninfested control plants (Rodriguez-Saona et al., 2005). Treatment of cultivated tomato plants with the phytohormone JA (as a mimic of herbivory) early in the season had long-lasting effects on community dynamics under field conditions (Thaler, 1999).

Multiple attacks may also affect indirect defenses. For instance, caterpillars of Plutella xylostella experience reduced parasitization by the parasitoid Cotesia plutellae on plants that are also infested by caterpillars of P. rapae as the parasitoids have a reduced attraction to plants infested by both caterpillar species compared to volatiles from plants only infested by their hosts P. xylostella. In this context, it is interesting to see that adult females of P. xylostella prefer to oviposit on plants already infested by P. rapae caterpillars (Shiojiri et al., 2002). N. attenuata plants that are infested by the mirid bug Tupiocoris notatus are better protected against M. sexta caterpillars because of modifications in direct and indirect defenses (Kessler and Baldwin, 2004) that have also been addressed at the transcriptomic and metabolite level (Voelckel and Baldwin, 2004b). Such an integrative approach to effects of infestation by a first attacker at different levels of biological integration will provide a major step forward to understanding multiple plant-attacker interactions.

	ARMS RACE BETWEEN PLANT DEFENSES AND INSECT ATTACKERS

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Plants and their attackers are involved in an intimate arms race (Schoonhoven et al., 2005). For instance, herbivores may inject salivary components in the plant to overcome plant defenses (Will et al., 2007), while plants may exploit salivary components of herbivores to induce defenses (Kessler and Baldwin, 2002). As mentioned above, plant defense responses are regulated by a network of signal transduction pathways. There is cross talk between the pathways; for instance, SA and JA pathways can negatively interact, while the JA and ET pathways often show positive interaction (Pieterse et al., 2002; Koornneef and Pieterse, 2008). From the plant's point of view, this network of signal transduction pathways may benefit its fine-tuning of defenses against the wide range of attackers it faces (e.g. Reymond and Farmer, 1998; De Vos et al., 2006). However, it may also provide attackers with means to interfere with the induction of defenses. For instance, B. tabaci down-regulate JA-mediated defense responses and induce SA defense responses that enhanced the whiteflies' performance and thus can be seen as a manipulation of the plant's defense responses (Zarate et al., 2007).

	PRIMING OF DEFENSES

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In addition to induction, plant defenses may also be primed (Frost et al., 2008); as a result, genes are up-regulated faster or stronger in response to attack than in nonprimed plants. Priming may be mediated by attack but also by exposure to volatiles. For instance, caterpillar attack can prime plants for induced resistance responses against a pathogen (De Vos et al., 2006), and induced defenses may also be primed by exposure of the plant's leaves to volatiles from attacked leaves from the same plant or a neighboring plant (e.g. Heil and Bueno, 2007; Ton et al., 2007). Priming is an ecologically interesting phenomenon, as it is likely to be less costly to the plant than induction of defenses (van Hulten et al., 2006). Moreover, priming seems to involve very limited gene expression and phytohormone induction, especially in tissues that have not been exposed to the priming agent (Verhagen et al., 2004). This may also limit the potential for manipulation of the plant's responses by attackers. Priming further adds to the plasticity of the plant's phenotype and thus to the dynamics of plant-insect interactions. This provides exciting new research options to ecologists to address community dynamics (e.g. Kessler et al., 2006).

	MOLECULAR ECOLOGY OF INSECT-PLANT INTERACTIONS

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The ultimate goal of ecology is to understand how the traits of an individual contribute to its fitness in terms of reproductive success. Until recently, this was investigated by comparing the performance of individuals or populations that differed in certain traits without (much) information on the underlying mechanisms and genes. Recent developments in molecular genetics have opened stimulating new avenues for ecologists through a molecular genetic approach. With the sequencing of plant genomes and the availability of well-characterized mutants and transgenics altered in traits that mediate interactions between plants and their biotic community members, ecologists can now address the ecological function of individual traits in very precise ways (Dicke et al., 2004; Kessler et al., 2004; Steppuhn et al., 2004).

Such tools are most abundantly available for molecular model species such as Arabidopsis and are used to investigate mechanisms of induced defense through a molecular genetic approach (for review, see Van Poecke, 2007). However, Arabidopsis is not the ideal plant for investigating the ecology of insect-plant interactions due to its early-season phenology. Other crucifers are more suitable to investigate the effects of genes on community ecology. There is extensive information on the ecology of brassicaceous plants (e.g. Louda and Rodman, 1996; Agrawal, 2000; Shiojiri et al., 2002; Harvey et al., 2003; van Dam et al., 2004; Gols et al., 2005). The ecology of B. oleracea is not only investigated for agricultural varieties (e.g. Shiojiri et al., 2002) but also for feral and native populations (Moyes et al., 2000; Bukovinszky et al., 2008). This provides interesting options for an ecogenomic approach to community ecology of Brassica-insect interactions. Arabidopsis can be an interesting tool for advancing molecular ecological information on other brassicaceous plant species (e.g. Broekgaarden et al., 2007). Arabidopsis may even aid the understanding of gene functioning in non-brassicaceous plants; for instance, by transferring terpene synthase genes from non-brassicaceous plants to Arabidopsis, the ecological effects of the volatile terpenoid products of the terpene synthase in terms of attraction of carnivorous arthropods can be investigated (Kappers et al., 2005; Schnee et al., 2006).

Moreover, solanaceous plant species such as N. attenuata and Solanum nigrum are being rapidly developed for molecular ecological studies of community dynamics (Kessler et al., 2004; Schmidt et al., 2004). This is done by gaining extensive knowledge on the molecular genetic basis of plant responses to environmental stress and developing tools to alter the expression of specific genes. For instance, blocking the jasmonate cascade by silencing the LIPOXYGENASE3 gene in this species has important consequences for the insect community associated with N. attenuata in its native environment; some herbivores that were never before encountered on this plant were now able to colonize the plant (Kessler et al., 2004). Moreover, silencing the CORONATINE INSENSITIVE1 gene results in changes in a range of defense-related characteristics and changes in interactions with the natural community (Paschold et al., 2007). Such experiments where plants altered in the expression of a single gene are exposed to their natural community provide important new information that can be supplemented with data on experiments in the laboratory that address the effects of the altered gene expression on individual plant-insect interactions (e.g. Li et al., 2002; Paschold et al., 2007).

	FUTURE PERSPECTIVES

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The rapid development of novel tools to address the ecological function of genes is likely to revolutionize ecology by allowing integration from molecular genetics and community ecology. To date, large numbers of well-characterized mutants and transgenic lines have been available only for model species like Arabidopsis. However, through mutant screens or with the development of RNA interference, and virus-induced gene silencing, generating specific lines in which individual genes have been knocked out is going to provide ecologists working on ecological model plants with important new tools (e.g. Paschold et al., 2007) to investigate the effects of individual genes on individual plant-insect interactions or on community dynamics. So far, these techniques allow for investigating the effects of two extremes, i.e. the presence or absence of a functional expression of the gene of interest. However, ecologists are especially interested in quantitative variation, and, thus, the development of tools to address the effect of quantitative genetic variation should be a next step. One way of proceeding on that route can be to exploit natural variation, and the molecular genetic information on the genes of interest will be very helpful in finding genotypes that differ quantitatively in the functional expression of genes of interest.

At present, ecologists with an interest in molecular ecology have almost exclusively addressed the ecological function of plant genes. However, given the long history of the interest in the reciprocal aspects of plant-insect interactions (Ehrlich and Raven, 1964; Schoonhoven et al., 2005), there is a need to enter the field of molecular ecology from the insect side. Given that several insect genomes are being sequenced, including herbivores and their natural enemies, we may soon see tools being developed to address functional ecological questions at the insect side of plant-insect interactions.

Received October 23, 2007; accepted December 28, 2007; published March 6, 2008.

	FOOTNOTES

 
¹ This work was supported by the Netherlands Organization for Scientific Research, NWO (VICI grant no. 865.03.002 to M.D.).

The author responsible for distribution of materials integral to the findings presented in this article in accordance with the policy described in the Instructions for Authors (www.plantphysiol.org) is: Marcel Dicke (marcel.dicke{at}wur.nl).

^[C] Some figures in this article are displayed in color online but in black and white in the print edition.

www.plantphysiol.org/cgi/doi/10.1104/pp.107.111542

^* Corresponding author; e-mail marcel.dicke{at}wur.nl.

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