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  • 1Centro de Ciencias Agropecuarias, Universidad Autonoma de Aguascalientes, Aguascalientes, Mexico
  • 2The Southwest Center, University of Arizona, Tucson, AZ, United States
  • 3Centro de Investigaciones Tropicales, Universidad Veracruzana, Xalapa, Mexico

We propose that comparisons of wild and domesticated Capsicum species can serve as a model system for elucidating how crop domestication influences biotic and abiotic interactions mediated by plant chemical defenses. Perhaps no set of secondary metabolites (SMs) used for plant defenses and human health have been better studied in the wild and in milpa agro-habitats than those found in Capsicum species. However, very few scientific studies on SM variation have been conducted in both the domesticated landraces of chile peppers and in their wild relatives in the Neotropics. In particular, capsaicinoids in Capsicum fruits and on their seeds differ in the specificity of their ecological effects from broad-spectrum toxins in other members of the Solanaceae. They do so in a manner that mediates specific ecological interactions with a variety of sympatric Neotropical vertebrates, invertebrates, nurse plants and microbes. Specifically, capsaicin is a secondary metabolite (SM) in the placental tissues of the chile fruit that mediates interactions with seed dispersers such as birds, and with seed predators, ranging from fungi to insects and rodents. As with other Solanaceae, a wide range of SMs in Capsicum spp. function to ecologically mediate the effects of a variety of biotic and abiotic stresses on wild chile peppers in certain tropical and subtropical habitats. However, species in the genus Capsicum are the only ones found within any solanaceous genus that utilize capsaicinoids as their primary means of chemical defense. We demonstrate how exploring in tandem the evolutionary ecology and the ethnobotany of human-chile interactions can generate and test novel hypotheses with regard to how the domestication process shifts plant chemical defense strategies in a variety of tropical crops. To do so, we draw upon recent advances regarding the chemical ecology of a number of wild Capsicum species found in the Neotropics. We articulate three hypotheses regarding the ways in which incipient domestication through “balancing selection” in wild Capsicum annuum populations may have led to the release of selective biotic and abiotic pressures. We then analyze which shifts under cultivation generated the emergence of Capsicum chemotypes, morphotypes and ecotypes not found in high frequencies in the wild. We hypothesize that this “competitive release” can lead to a diversification of the domesticate's investment in a greater diversity of SM potency across different cultural uses, cropping systems and ecogeographic regions. While most studies of plant domestication processes focus on morphological changes that confer greater utility or productivity in human-managed environments, we conclude that changes in the chemical ecology of a useful plant can be of paramount importance to their cultivators. The genus Capsicum can therefore provide an unprecedented opportunity to compare the roles of SMs in wild plants grown in natural Neotropical ecosystems with their domesticated relatives in the milpa agro-ecosystems of Mesoamerica. Even with the current depth of knowledge available for crop species in the genus Capsicum and Solanum, our understanding of how particular SMs affect the reproduction and survival of wild vs. domesticated solanaceous plants remains in its infancy.

Introduction

What changes occur in a Neotropical plant's chemical defenses when it is domesticated for crop production as a food, medicine, vermifuge or condiment, or for all four of these uses? There is remarkably little tested ecological theory regarding how domestication affects plant chemical defenses (Rindos, 1984Johns, 1990Casas et al., 2015). This may be because most phytogeographic, agroecological, and archaeobotanical studies of plant domestication have largely used morphological indicators to track the domestication process rather than identifying phytochemical indicators of changes in ecological interactions. As recently argued by Zeder (2017), ecologists need to identify tractable model systems that allows for an assessment of the core assumptions of the Extended Evolutionary Synthesis (EES).

The domestication of crop plants by human cultures provides one such case study opportunity. That is why we propose that the genus Capsicum can serve as important model system for discerning how changes in secondary metabolites (SMs) reveal shifts in plant chemical defenses that have occurred with domestication. In the case of domesticated chile peppers, these shifts influenced both (1) antagonistic interactions with predators and abiotic pressures, and (2) facilitated (including mutualistic) interactions among chiles, their avian dispersers, nurse plants and human cultures. The integration of ethnobotanical, paleoecological, archeological, linguistic, genetic and evolutionary perspectives on chile domestication that has been in process for the last two decades (Tewksbury and Nabhan, 2001Pickersgill, 2007Tewksbury et al., 2008bAguilar-Meléndez et al., 2009Haak et al., 2012Kraft et al., 2014Carrizo-García et al., 2016) has already contributed substantively to the possibilities of such an EES.

For these reasons, we have chosen to integrate ecological studies of wild Capsicum species in natural habitats of the Neotropics with ethnobotanical, agroecological and nutritional studies of domesticated Capsicum landraces in culturally-managed milpa habitats and indigenous diets of Mesoamerica. By doing so, we wish to further test hypotheses underpinning the theory that a major trend in crop evolution in the Neotropics has been a dramatic shift in the ecological functionality of plant chemical defenses (Johns, 1990). We propose that testing the following three hypotheses can help identify the most parsimonious fit with data and trends involving the evolutionary transition from wild Capsicum annuum var. grabriusculum to domesticated Capsicum annuum var. annuum:

(H1) a reduction and simplification of the potency of plant chemical defenses against seed predators, foliage herbivores and disease microbes with greater reliance on human intervention to protect the plants;

(H2) a diversification of the levels of potency and mixes of defense chemicals, given the wider range of habitats, cultural management and uses, and broader geography to which the crop chile plants are exposed;

(H3) an intensification of the potency of certain plant chemical defenses, given the need to protect the plants in agro-habitats where they occur at higher density and without as much beta diversity of neighboring plant species to slow the spread of predators, herbivores, competing weeds or diseases.

Crop plants in the Solanaceae (including Capsicum chile peppers) may be extremely useful models for looking at changes in potency, diversity or effectiveness of plant chemical defenses which occur with domestication. This is because their SMs and the ecological roles which these plant defenses play have been intensively investigated in the field and in the laboratory for well over two centuries (Johns, 1990Eich, 2008). Neverthless, it remains clear that we lack the detailed knowledge needed to determine how particular plant chemical defenses (e.g., specific capsaicinoids) function in repelling (or attracting) various sets of vertebrates, invertebrates and fungi which serve as seed predators, seed dispersers, fruit and foliage consumers or root parasites on various solanaceous crops. Even with the current depth of knowledge available for crop species in the genus Capsicum and Solanum, our understanding of how particular SMs affect the reproduction and survival of wild vs. domesticated solanaceous plants remains in its infancy.

Of the 97–102 genera represented by 2300–2460 distinct species documented in the Solanaceae (Hunziker, 2001Eich, 2008), SMs (such as the ornithine-derived alkaloids which function as the primary chemical defenses of most of these species) have so far been documented in more than 61 genera (Eich, 2008). Many of the SMs commonly found in the Solanaceae—such as tropane, nicotinoid, pyridine and terpenoid alkaloids—can be toxic or at least repellant to a broad variety of insects as well as to vertebrate herbivores; some also reduce fungal or bacterial infestations of seeds, fruit or foliage. We will focus the rest of this inquiry on the ecological and ethnobotanical consequences of these chemical defenses as found in seeds and fruits of solanaceous crops, with particular focus on chile peppers (Capsicum annuum).

These broad-spectrum alkaloids function as primary chemical defenses in a number of solanaceous crop plants, and in their wild relatives as well. We have therefore placed the domestication of Capsicum species in the context of other domestication studies for the following genera: Jaltomata (xaltomatl, sogorome); Lycium (goji berry); Nicotiana (tobacco); Solanum(potato, tomato, eggplant, garden huckleberry/chichiquelite); Physalis (tomatillo/ground cherry, cape gooseberry/uchuva) (e.g., Johns, 1990Pickersgill, 2007 among many others). While some of the same alkaloids characteristic of many species in the Solanaceace are present in extremely low concentrations in the foliage of Capsicum species, nearly all the species in this genus have taken up an altogether different strategy—Capsaicinoids, for defending their seeds and fruits from biotic stresses.

Departing from the norm in the Solanaceae—where species principally use broad-spectrum and highly toxic glyco-alkaloids for defense—most Capsicum species instead employ another, unique set of SMs that are not appreciably toxic to animals. In contrast to all other genera and species in the nightshade family, both wild and domesticated chile peppers produce several of the 22 known capsaicinoids, with capsaicin, dihydrocapsaicin and nordihydrocapsaicin being the most prevalent, widely-studied and economically important ones. However, it is likely that each distinct capsaicinoid functions in varying degrees to direct avian seed dispersal or to repel and reduce damage by insects, mammals, bacteria and fungi (esp. Fusarium) (Tewksbury and Nabhan, 2001Tewksbury et al., 2008bHaak et al., 2012). Unfortunately, to arrive at a comprehensive EES (Zeder, 2017), we will require more detailed knowledge on the specific ecological effects of 19 of those distinctive capsaicinoids on various faunal and fungal species found in Neotropical habitats.

The ability to produce capsaicinoids is a monophyletic synapomorphic carácter shared by most of the 35 + wild Capsicum species. The exceptions are few, and are found in the wild Andean clade (C. ciliatum = C. rhomboideum, C. scolnikianum, C. geminifolium, C. lanceolatum, and C. dimorphum), and the Longidentatum clade (C. longidentatum) (Eich, 2008Haak et al., 2012Carrizo-García et al., 2016).

Pungency in all other wild chile peppers has a simple genetic basis that is expressed only in glands within the placental fruit, where it serves to protect viable seeds from predation by granivorous mammals, or from microbial infestation. It also facilitates the directed dispersal of seeds by frugivorous birds such as thrashers, cardinals, and finches to safe sites for germination and recruitment under nurse plants, providing an unusually direct ecological link to changes in reproductive fitness that is often missing from studies of chemical ecology (Nabhan, 2004Tewksbury et al., 2008a). Pungency is polymorphic in several wild chile species (Carrizo-García et al., 2016), and such polymorphic populations have been identified along natural environmental gradients (Haak et al., 2012Carrizo-García et al., 2016). These polymorphisms provide unique opportunities to advance an extended evolutionary synthesis from field comparisons of wild and domesticated subspecies in the same crop species and economic genus (Hernández-Verdugo et al., 2001aHaak et al., 2012Chen et al., 2015).

These attributes make chile peppers excellent systems through which to investigate the evolution of adaptive constraints found under various levels of domestication.

Ironically, consumption of the very same capsaicinoids that function as chemical defenses for chile plants have long been used by Mesoamerican cultures as defenses against microbial and invertebrates challenging human health (Nabhan, 2004). Their many indigenous uses as food or medicine has likely benefited overall human health and reproductive fitness in Neotropical environments for well over six millennia (Perry and Flannery, 2007Kraft et al., 2014); these biomedically-significant ethnobotanical uses mediated by SMs (Mostafa-Kamal et al., 2015) possibly triggered the domestication and diversification of chile peppers.

Capsaicinoids are now the most widely used SMs in the world, even though their commercial production is dominated by landraces of just five species in the genus Capsicum. Now culturally-dispersed far beyond the Neotropics, each continent and its biomes favors different ecotypes of place-based landraces such as the tabasco pepper, ghost pepper, piri-piri, aji, habanero, jalapeño, and long green New Mexican chile. Today, more than a third of the world's human population daily consume food products derived from 2500+ landraces, standard varieties and modern hybrids of chile peppers (Tewksbury et al., 2008b). In fact, we predict that if one includes the number of human daily ingesting and topically-applying chile peppers as pharmaceuticals and folk medicinals then over half the world's population are currently consuming some form of chile peppers for nourishment, health and ultimately, reproductive fitness.

We will focus most of our analysis on discerning historic shifts in plant chemical defenses in the most widely-used Capsicum species – C. annuum L., domesticated in the dry subtropical habitats of Mesoamerica over 6,500 years ago (Kraft et al., 2014). We posit that these shifts in SM enhanced, or at least diversified, the mutualistic relationships among chile peppers and indigenous Mesoamerican cultures, as a result of relatively rapid selection and linguistically-traceable diffussion, that intensified around 6,500 years B.P. (Brown, 2010Kraft et al., 2014).

It appears that Homo sapiens is one of the few mammalian species which routinely overcome a deep-seated aversion to the consumption of pungent chile peppers (Rozin and Schiller, 1980Nabhan, 2004), perhaps because the evolutionary benefits of consuming chile fruits outweighed the costs when exposed to environmental challenges, commonly exhibited in certain Neotropical habitats.

Crop Domestication

Domestication is the outcome of both conscious and unconcious selection processes that lead to increased co-evolutionary adaptation of plants to cultivation and utilization by humans in managed environments (Gepts, 2010). Paleolithic cultures developed tools, food preparation and plant selection techniques for detoxifying certain plant foods rich in SMs (Johns and Kubo, 1988Johns, 1990). As such, the coevolutionary response of Mesoamerican cultures to chile peppers certainly included memes, but may also have included the selection of “non-taster” genes in humans for organoleptic tolerance of pungency and bitterness (Nabhan, 2004).

On the other hand, the suite of traits that marks the divergence from its wild ancestor(s) has been defined as the “domestication syndrome” (Harlan, 1992). A domestication syndrome may include selection for combinations of several different morphological and phytochemical traits, including seed retention (non-shattering), increased fruit and/or seed size, changes in branching and stature, changes in reproductive strategy, and, importantly, changes in SMs (Pickersgill, 2007Gepts, 2010Meyer et al., 2012).

Often, domestication selects against traits that formerly increased the plant's defensive or reproductive successes in natural environments (Meyer et al., 2012). However, this generalization may not completely fit for SMs such as capsaicinoids in C. annuum in the Neotropics, where a high diversity of landraces and wild populations express some degree of pungency as a natural defense against predators.

Cultural selection can therefore work in opposition to natural selection, and certain domesticated crops may exhibit reduced fitness, or, in some cases, an inability to survive outside of cultivation (Pickersgill, 2007Gepts, 2010). The very act of moving plants from natural habitats into culturally-managed habitats such as milpas alters the mix of selection pressures, leading to increased adaptation to cultivation, and to actual physical protection from pests and predators by cultural managers, potentially at the expense of traits conferring fitness in the natural environment (Meyer et al., 2012). In the very least, selection pressures for plant chemical defenses against predators might be relaxed if human intervention with the same predators (eg., rodents) is consistently offered to the crop variety over multiple generations.

Secondary Metabolites in Plants

Plant chemicals can be divided into two major categories: primary metabolites (PMs) and secondary metabolites (SMs). PMs are substances produced by all plant cells that are directly involved in growth, development, or reproduction (sugars, proteins, amino acids, and nucleic acids). PMs function in basic anabolic and catabolic processes required for respiration, nutrient assimilation, and growth/development (Kliebenstein, 2004Freeman and Beattie, 2008).

SMs may not be directly involved in growth or reproduction, but they are often involved with plant defense (Freeman and Beattie, 2008), particularly in the case of Capsicum species (Tewksbury et al., 2008b). SMs are considered the major mediators of ecological interactions of plants as a result of their large and diverse biological functions in nature. SMs are produced in response to certain biotic and/or abiotic stress signals or stimuli. They function in the defense against herbivores, microbes, viruses or competing plants, and also as signal compounds to attract pollinating or seed dispersing animals (Wink, 2003). Thus, SMs are very important for plant's survival and reproductive fitness. This complex multirole of SM has led plants to synthesize many different chemical compounds in nature during evolution (Kliebenstein, 2004).

According to their role in plant's defense, SMs have been classified on the basis of their host protection and fostering of beneficial biotic interactions. According to Freeman and Beattie (2008), SMs usually belong to one of three large chemical classes: terpenoids, phenolics, and alkaloids.

Terpenoids include a series of toxic and non-toxic phytochemicals produced in different plant organs that inhibit, repel, or attract other living organisms, such as predators (plant pathogens, herbivores invertebrates, vertebrates) and non-predators (dispersers, pollinators, pest-enemies).

Phenolics include a series of toxic and non-toxic compounds such as flavonoids, isoflavonoids, and phenolic monomers produced in different organs (roots, stems, leaves, flowers, fruits, and seeds). Phenolics and their derivatives have different functions in nature (UV-protectan, antifungal, antibiotic, insecticidal, and others).

Alkaloids are N-compounds produced and aggregated in different organs such as roots, leaves, fruits and seeds. Alkaloid-based SMs may function as bactericides, fungicides, insecticides and allelopathics. Alkaloids may have degrading and digestive effects on different tissues of predators and pathogens. Examples of this type of SM include cafeine, cocaine, morphine, nicotine, atrophine, plus capsaicine and other capsaicinoids. Other N-compounds important for plant chemical defense include cyanogenic glucosides, defensins, lectins, and hydrolitic enzymes.

Therefore, SMs in chile peppers and other solanaceous plants in Neotropical habitats have evolved as defense mechanisms against microorganisms (viruses, bacteria, fungi), herbivores (molluscs, hemipteran insects, vertebrates), and competing plants. They may also function to attraction of pollinators and seed dispersers by virtue of their fragrances and colors they express in the plants. Regardless of the efficacy of such benefits, SMs require a great deal of plant resources and energy to be produced. Consequently, they may be synthesized and translocated after a pathogen or pest has attacked the plant and triggered their activation. once activated, these chemical defensive compounds are usually very effective inhibitors of fungi, bacteria, nematodes, and hemipteran insect herbivores.

Chemical Ecology of Wild Capsicum in Neotropical Habitats

To address the changes in plant chemical defenses that have occurred with the domestication of Capsicum annuum, we must briefly establish the context through which wild chile peppers and other solanaceous plants deal with biotic and abiotic stresses prevalent in the Neotropics. In particular, we will focus on the biotic interactions as well as the biotic and abiotic stresses that wild chile plants may particularly respond to in dry subtropical thornscrub and tropical deciduous forest vegetation types, characteristic of the Sierra Madre Oriental and the Trans-Volcanic Belt in Mesoamerica. At least one EES-style integration has determined that these vegetation types are among the most likely Neotropical habitats where C. annuum domestication and diffusion may have occurred (Kraft et al., 2014). However, because there has been considerable change in the areas covered by these habitat types over the last 6500 years (Kraft et al., 2014), other proposed geographic areas such as the Yucatan peninsula remain viable enough as putative centers of chile pepper domestication that we do not wish to rule them out (Aguilar-Meléndez et al., 2009).

In contrast, the pungency of wild chile pepper fruit repels small mammals that function as seed predators, but directs their dispersal to safe sites under nurse trees where germination, recruitment and establishment have higher probabilities (Tewksbury and Nabhan, 2001Carlo and Tewksbury, 2014). The seeds from these pungent wild chiles are also protected from “predation” by Fusarium fungi that might otherwise leave the infected seeds inviable (as evidence shows for C. chacoense). Thus, the directed dispersal adaptations of wild chile peppers afforded to them by the pungency of their specialized SMs–their capsaicinoids—have conferred to them a level of reproductive fitness that has incidentally allowed them to be present in abundance and accessible to human foragers in the Neotropics for millennia.

Changes in Secondary Metabolite Intensity With Chile Domestication

What are the traits that have been modified as a result of selection under cultivation that have made modern and fully domesticated varieties of chile peppers so poorly adapted to the natural Neotropical habitats? We propose that the morphological and/or phenotypic changes which occurred during cultural selection and domestication of C. annuum have been accompanied by (if not surpassed in importance by) corresponding changes in SMs that regulate ecological interactions of chile peppers with their surrounding abiotic and biotic environments. The complexity and specificity of SMs as chemical mediators of biotic interactions of both wild and domesticated C. annuum in the Neotropics are summarized in Figure 1.

FIGURE 1
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Figure 1. Ecological and cultural interactions shaping diversity of chile peppers (Capsicum annuum L.) across Mexico. (A) Graphic illustration of SMs as chemical mediators of ecological interactions with wild C. annuum in natural and semi-managed habitats. (Illustration designed by Frida Isabel Luna-Vallejo). (B) Map of Mexico showing indigenous territories, contrasted by colors. The symbols identify particular ecological zones where certain indigenous groups have persisted in modern times. All indigenous groups represented here have documented uses of chile peppers. (Map elaborated by Andres Lira Noriega and Araceli Aguilar-Melendez based on data from the authors, SINAREFI-SNICS-SAGARPA and SNIB/CONABIO 2016; the layer of indigenous territories was provided by Eckard Boege). (C) A representative sample of the wider array current morpho-typic diversity and levels of domestication of chile peppers across Mexico. (Photos by Ivan Montes de Oca Cacheux and Miguel Angel Sicilia Manzo/Image repository CONABIO).

Wild populations of chile pepper have coexisted and coevolved with many different organisms of tropical origin. Figure 1A focuses on two types of biotic interactions with wild Capsicum species: mutualistic and antagonistic. Every particular plant interaction is regulated by some SM produced and expressed in a particular organ, at a certain phenological stage, in response to specific biotic or abiotic signals. Chile pepper interactions have been strongly influenced by humans and cultural diversity in Mesoamerica over the last 10,000 years. The cultural diversity present in modern Mexico, and a sample of the wide morphological variation and levels of domestication that are currently found in Mexican chile peppers are shown in Figures 1B,C. The variation in Mexican chile peppers also applies to the chemical compounds, which may help explain the wide differences in fruit taste and flavor for different purposes and uses across Mexico.

Chen et al. (2015) indicated that among their various functions, SMs play particularly important roles in insect-plant interactions. Studies that have compared chemical defense traits in wild crop relatives and their cultivated counterparts are increasing in number, and their outcomes consistently show that domesticated plants provide a better food resource for herbivores than their more toxic wild progenitors. Several studies provide evidence of such changes in the chemical ecology and biotic interactions along a domestication gradient (Holt and Birch, 1984Benrey et al., 1998Rodriguez-Saona et al., 2011Dávila-Flores et al., 2013). These widely-observed trends seem to contextualize, if not explain, shifts in the chemical defenses of C. annuum during its domestication in certain but not all, Neotropical habitats of Mesoamerica.

To date, most studies of SMs in C. annuum in Mesoamerica have been focused on fruits of fully domesticated commercial varieties for consumption as fresh fruits (jalapeño, serrano, ancho and sweet pepper morphotypes). In addition, there are few ecological field studies of how capsaicinoids in wild Capsicum species of arid North America and tropical South America mediate relationships with native fauna, but they do not specify which capsaicinoid(s) drive those interactions (Tewksbury and Nabhan, 2001Tewksbury et al., 2008aCarlo and Tewksbury, 2014Haak et al., 2014). Most analyses have concentrated on capsaicinoids and few have included other SMs, such as phenolics and carotenoids. The literature available on SMs in chile peppers is focused on their presence in both, vegetative organs and in fruits and seeds (Do Rêgo et al., 2012Kim et al., 2014). The presence of SMs in different organs and genotypic backgrounds may help explain the existence of natural sources of genetic resistance in Capsicum to particular herbivorous pests and seed predators.

The identities of most SMs remains incomplete among wild C. annuum var. glabriusculum from the Neotropics. However, genetic resistance to Huasteco pepper virus has been documented for wild C. annuum from Nortwest Mexico (Hernández-Verdugo et al., 2001bRetes-Manjarrez, 2016). Of the known cases of genetic resistance among domesticated chile peppers are their tolerance to Phytophthora capsici and root knot nematodes, first documented in the Criollo de Morelos landrace—CM-334 (Pegard et al., 2005) also, leaf phenolic extracts from domesticated chile landraces have been used to control Alternaria altata in tomatoes.

Crop domestication can lead to a decrease in SMs associated with pest resistance, a trend corroborated by Meyer et al. (2012); they found a decline in levels of some SMs across 203 separate crop varieties, relative to levels in their wild progenitors, including C. annuum. However, other SMs, such as capsaicinoids, have dramatically increased within some natural and domesticated chile pepper landraces (e.g., Bhut Jolokia; Bosland and Baral, 2007), so that these changes are not unidirectional.

Given that “original” contexts for how wild Capsicum species function and survive in the Neotropics, Table S1 proposes a set of differences that may have been triggered by “balancing selection” during the domestication process. Balancing selection operated in ways that transformed some wild polymorphic populations into fully-domesticated but still heterogeneous C. annuum landraces. We place particular emphasis on levels of SMs and other adaptations that appear to confer reproductive fitness to Capsicum populations in Neotropical habitats.

Other Changes Occurring With Domestication of Chile Peppers

We do not wish to presume that shifts in SMs were the only changes which have occurred with the domestication of Capsicum species in Neotropical habitats. We wish to briefly mention several other traits of adaptive significance in Neotropical habitats.

Loss of Dispersal Mechanisms

Wild chile peppers are naturally dispersed by frugivorous birds to the understory of selected nurse plants (Tewksbury and Nabhan, 2001Carlo and Tewksbury, 2014), while domesticated chiles depend on human intervention for dispersal. Seed dispersal often involves lost of an abscission zone from some part of the plant. Fruits of wild chile peppers separate easily from the receptacle at maturity. Fruits of domesticated peppers remain firmly attached to the plant. Mature wild chile pepper fruits are consumed and effectively dispersed by a variety of frugivorous Neotropical birds. Domesticated peppers are either too large, or are not attractive to nor dispersed by most Neotropical birds. Different SMs may mediate seed dispersal in wild chiles, but carotenoids in the fruit pulp probably are likely the most important due to bird attraction by their red color. The pyrazine fragrances of chile peppers may also serve to attract certain birds.

Loss of Seed Dormancy

Most wild chile pepper seeds have staggered seed dormancy, which allows germination and recruitment when optimal conditions occur in a more variable and uncertain environment. Domesticated chiles do not exhibit any seed dormancy (Pickersgill, 2007). Therefore, domesticated chiles would likely have poor recruitment, survival and fitness if placed in most naturally wild environments. Seed dormancy in most wild Capsicum species is mediated by SMs such as ABA, a plant regulator that inhibits seed germination (Marrush et al., 1998Sariyildiz et al., 2005Nambara et al., 2010), and lignin, a structurally protective and hydrophobic compound of the seed coat (Randle and Honma, 1981Tewksbury et al., 2008bNambara et al., 2010).

Wild chile pepper seeds with thick lignified testas become increasingly impermeable to water on drying. This feature is disadvantageous for—if not absent from—most domesticated crop seeds, not only because these seeds germinate slowly, but also because they may require prolonged soaking to remove inhibitors from the seed coat (Randle and Honma, 1981Pickersgill, 2007Carlo and Tewksbury, 2014). Therefore, domesticated chile peppers generally have thinner testae than their wild progenitors.

Changes in Organ Size and Quantity

As part of the domestication syndrome, changes in secondary metabolite content may be correlated with other physical and chemical traits, such as nutrient content, size, or biomass (Chen et al., 2015). Compared to most domesticated landraces, wild Capsicum species exhibit smaller leaves, flowers, fruits and seeds, but a larger number of these organs per plant (Pickersgill, 2007). These characteristics—such small but numerous leaves and seeds—confer adaptability, stress reduction, survivability, and bet-hedging strategies to wild chile peppers for the production and dispersal of their seeds in Neotropical habitats (Tewksbury et al., 2008b).

Increased Morphological Variation

According to Chen et al. (2015), morphological changes arising from domestication can disrupt plant-herbivore-natural enemy interactions, however domesticated chile landraces now exhibit enormous inter-varietal and some intra-varietal heterogeneity in morphological traits.

This factor also is especially marked in the parts of the chile pepper plant used by Mesoamerican cultures. While domesticated chile peppers vary greatly in fruit size and shape, and to a lesser extent in color, wild C. annuum var. glabriusculum populations show little morphological variation in fruit size, shape, and color. In certain coastal Neotropical habitats, chile pepper fruits are selected for particular colors and shapes, said to be the best for seasoning turtle meat, while others, of different color and shape, are known as perfume peppers because they have a fragrant aroma as well as pungency. Pickersgill (2007) and Boster (1985) suggest that such traits result from cultural “selection for perceptual distinctiveness.”

In short, the different landraces of chile peppers grown and consumed across Mesoamerica display an astounding range of morphological variation in plant architecture and fruit shape, as well as in fruit color, pungency, and particular cultural uses (Bosland and Votava, 2000). All SMs in Capsicum species, including carotenoids, flavonoids, capsaicinoids, and ascorbic acid, are to some extent, linked with these morphological traits. Boster (1985) has deftly summarized the many references documenting the pronounced differences in morphology between wild and domesticated peppers.

Changes in Plant Habit Related to Resource Partitioning

Selection for increased harvest index (ratio of harvested to total biomass produced per plant) may result in reduced or suppressed lateral branching (Pickersgill, 2007). Reduced number of inflorescences per plant and producing more synchronous fruit ripening on an individual plant and within a stand, facilitating harvesting of the stand as a whole. Fewer nodes and shorter internodes, greater synchronization of maturation of vegetative branches and fruit ripening is also favored by a determinate habit.

The transition from the perennial indeterminate habit of wild chile peppers to the annualized compact habit of domesticated peppers has been triggered by selection for earliness, larger fruits, compact growth/reduced branching with reduced number of fruits per plant, and more synchronous fruit ripening. Loss of perennial plant habit may be the final/accumulated result of human selection for non-dormant seed, which probably modified fruit and seed morphologies, and SM potencies.

Changes in Reproduction

In Capsicum species, floral phenology and pollination, as well as fruit and seed development are influenced by different SMs. For example, carotenoid and flavonoid derivatives are secondary metabolites in the flower that attract pollinators. Similarly, fruit and seed dispersal are mediated by SMs which serve to attract seed dispersers. Simultaneously, fruit and seed protection is mediated by particular SMs (capsaicinoids and phenolics) that repel predators of fruits and seeds.

Wild C. annuum is an autogamous plant with protaginous flowers (exerted stigmas) and high rates of outcrossing by insect pollinators, and indeterminate growth in neotropical Mesoamerica. Flower initiation is late, but once initiated is persistent and very prolific, with overlapping stages of flower and fruit development over the season. Fully domesticated C. annuum land races can also be autogamous, but exhibit much lower rates of outcrossing, probably due to more synchrony in anther and stigma maturation. Most of the fully domesticated chile pepper land races exhibit determinate growth under cultivation, with more rapid onset of flower initiation, fruit development and ripening. For such reasons, fruit and seed production of fully domesticated chile landraces would be almost impossible under natural wild environments in the Neotropics.

Loss of Chemical or Physical Protection Against Biotic and Abiotic Stresses

Many other domesticated crops have partially or completely lost the SMs that protect their wild relatives against predators (herbivores, plant pests and pathogens), and abiotic stresses (drought, salinity, heat, frost, daming radiation, etc.). However, this trend does not necessarily hold true for most domesticated C. annuum land races. Capsaicinoids and other SMs are synthesized in the placental tissue of domesticated chile fruits after flowering as part of fruit development. In other words, in domesticated chiles, SMs may play a small role in chemical defense of plant tissues before fruit and seed development (Meyer et al., 2012Fernández-Marín et al., 2014).

Protection of wild chile pepper fruits in populations against predators is mostly conferred by capsaicinoids, although flavonoids and phenolics may also play protective roles against predators. However, protection against hervibory in wild chile plants (prior to their flowering) is also facilitated by the “prey refugia” offered by the dense thorny canopies of certain nurse plants. Where they lack nurse plant protection in Mesomerican milpas, domesticated chile peppers must rely on farmers themselves to evict (or to reduce the damage potentially wreaked by) mammalian predators and browsers (Pickersgill, 2007Gepts, 2010Padilha and Barbieri, 2016).

With regard to protection against abiotic stresses, wild chile pepper plants employ SMs such as flavonoids, phenolics and vitamin C for protection against drought, heat and daming radiation. In particular, carotenoid derivatives confer protection against plant cell oxidative reactions caused by lethal radiation, such as direct sunlight and UV light (Wahyuni et al., 2013).

Fully domesticated C. annuum landraces express widely varying concentrations of capsaicinoids compared to pungency levels in wild populations. Today, the mildest to most pungent domesticated chiles vary in the capsaicin and pungency content (~5,000–300,000 SHU); with most (but not all) wild populations being in the medium-to-high range (~100,000 SHU) of pungency (Eich, 2008). The hottest chile peppers belong to C. chinense and currently there are some cultivars of this species such as “Bhut Jolokia” and “Trinidad Scorpion” which have around 1.0 million SHU (Bosland and Baral, 2007), and “Carolina Reaper,” the hottest pepper in the world exceeding 1.5 million SHU (Padilha and Barbieri, 2016). Domesticated landraces of C. annuum may also have larger but more variable amounts of other SMs, including more antioxidant capacity (Wahyuni et al., 2011).

Agroecological Context of Milpa Cultivation as a Selective Pressure

Lack of both seed dormancy and a facultatively perennial plant habit probably enabled the shift from avian dispersal of fruits under nurse plant canopies in the wild to open cultivation of annual plants with non-dormant seeds in milpa agro-ecosystems. The loss of ecological interactions with birds and nurse plants due to intentional seed-saving and dispersal by humans must have generated incidental changes in SMs. Shifting the patterns of SMs through such selection could explain, in part, the emergence of new chemotypes, genotypes and morphotype landraces under cultivation in milpas within the Neotropics. The Mesoamerican milpa agroecosystem may have gradually replaced the nurse plants in agroforestry systems during the early domestication of C. annuum, but as it did, it likely accelerated unconscious selection away from wild chemotypes and morphotypes.

Synthesis of Coevolutionary Shifts Occurring With Domestication

We suggest that incipient cultivation and “re-balancing” selection of seed germinability in polymorphic founder populations of C. annuum var. glabrisculum in Mesoamerica around 6500 BP rapidly led to changes in gene frequencies associated with other adaptive traits. Curiously, this is roughly the time period when a new meme –a chile-processing technology and associated culinary techniques–first became evident in the prehistoric cultures of south-central Mexico. This technology was called mollicaxtli in Nahuatl (now molcajete today in Spanish, and consists of a round three-legged, grinding bowl and pestle for crushing dried spices, made out of fired clay or volcanic stone (Vela, 2009).

The molcajete's sudden emergence and wide diffusion suggests that domesticated chile pepper were not merely being eaten fresh, but surplus harvests were being dried and stored between growing seasons for use as a dried spice, condiment, medicine or vermifuge. Undoubtedly, these multiple uses of small, dried chile “pods” emerged long before the selection for larger fleshier fruits, which could be used as a vegetable that was stuffed with meats, fruits or other spices. Thus, a new technology (molcajetes) and its associated culinary uses, as well as seed saving and trade beyond their ancestral habitats may have accelerated selection for a wider range of Neotropical habitats and overall diversification of domesticated chile pepper landraces.

Most remarkably, chile pepper fruits of some cultivated landraces are many times hotter or milder than those of wild populations, suggesting that domestication has not only diversified, but shifted total pungency in both directions—to higher “heat levels” in some varieties (e.g., ghost peppers), and to lesser levels in nearly non-pungent varieties (e.g., bell peppers). There is limited evidence that the mixes of capsaicinoids found in cultivated chile varieties are also more variable than those in wild populations, but comparable sampling has been poor. Neverthless, we see evidence for both (H2)—a diversification of the levels of potency—and (H3)—an intensification of potency of selected SMs with chile pepper domestication.

In the case of milder (less pungent) chile peppers, we assume that farmers' protection of the plants compensates to some extent for lower levels of chemical defenses. Haak et al. (2012) have confirmed tradeoffs between expression of capsaicinoid pungency, and yield under water-stressed conditions. While capsaicinoids remain the most important plant chemical defenses in most domesticated chiles as they are in wild peppers, the roles of other secondary metabolites found in lower concentrations should not be dismissed.

Mesoamerican Human/Chile Pepper Coevolution in Relation to Benefits of Chemical Defenses

According to paleobiolinguistic reconstructions of the presumed origins and diffusion of domesticated chile peppers in Mesoamerica, the oldest reconstructed term for cultivated chiles is found in proto-Otomanguean from south-central Mexico, estimated to be in transcultural circulation by 6592 B.P. (Brown et al., 2013Kraft et al., 2014). This evidence is supported by archeological analyses that confirm the presence of domesticated chile fruit and spice-grinding molcajetes at sites along the Sierra Madre Oriental/Trans-Volcanic by 6000 years ago, especially in seasonally dry subtropical thornscrub (Kraft et al., 2014).

Nevertheless, several lines of research agree that the origin of the domesticated C. annuumlandraces may have also occurred elsewhere within the broader Mesoamerican region (Eshbaugh, 1970Hernández-Verdugo et al., 2001aPerry and Flannery, 2007Pickersgill, 2007Aguilar-Meléndez et al., 2009). In other words, the precise location or locations of domestication of C. annuum in Mesoamerica still remains unknown.

Based on linguistic analyses, Brown (2010) suggests that the earliest plant management in Mesoamerica was of grain, succulent and oil crops; they became cultivated as staples no later than 7000 years ago. The earliest cultivation of spices (including chiles) for seasoning these staples came centuries later.

In short, staples such as maize, maguey, nopal and avocado were probably cultivated to provide seasonal surpluses for storage and consumption at least a thousand years before the earliest detectable onset of chile pepper cultivation as a spice, anthelmentic medicine, vermifuge or condiment (but most likely not as a fresh green vegetable).

The pervasiveness of the use of chile peppers in treating illnesses in Mesoamerica and Aridoamerica (N Mexico and SW USA) is without peer, among any of the other crops domesticated in these regions. This fact alone suggests that the culinary uses of Capsicum were not the only catalysts to domestication. Table S2 shows several ancient medicinal uses derived from extensive studies of indigenous farming cultures in Mesoamerica. Collectively, this information suggests that a “Mesoamerican intellectual tradition” of indigenous medicinal-culinary knowledge (López Austin, 2001Good, 2005) may have guided the selection of SMs and other traits in chile pepper landraces. The very cultural persistence of chile plants (as well as maize, etc.) within milpas and dooryard gardens in this modern globalized world, is clear evidence that ancestral cultural traditions spanning 6000–7000 years, still have adaptive value today.

In addition, the milpa management traditions have been culturally maintained to keep alive what is culturally perceived as a sacred agroecosystem that maintains and regenerates everyday life, community values and collective identities among many Mesoamerican societies (Bonfil-Batalla, 2012Good, 2015). The medicinal, ceremonial and culinary uses of chile peppers by over 60 native cultures in Mesoamerica are embedded a small but inseparable and integral part of a broader cosmovision, one that persists up through this present moment (Alcorn, 1984Long-Solís, 1986López Austin, 2001de Avila, 2008). Any true EES that attempts to use chile pepper domestication as a model system must inevitably take these cultural memes into account.

There is no reason to assume that chiles were first gathered, then cultivated, for a single use, given that tobacco, cacao and other early crops also had multiple uses. However, as staple crops grew in yields and diets became more redundant, chile peppers may have played critically-important roles in protecting grains and legumes aggregated in storage facilities from post-harvest consumption by insect pests and fungi common in the Neotropics. Some of these same chemical defenses in chile peppers may have protected humans who were aggregated into increasingly dense habitations from intestinal parasites, and from body lice or fleas. Finally, the SMs in chile peppers may also have become increasingly necessary elements of the traditional diets and pharmacopeia as “nutraceuticals” that counteracted the greater redundancy in agricultural diets.

The pharmacological utility of SMs in chile peppers is not restricted to the control of fleas, lice and intestinal microbes. They have recently been demonstrated to be effective in reducing intestinal infections by aquatic helminthes of the same group as the intestinal worms that cause ill health and sluggishness among one third of the world's population, especially children in tropical climes (Mostafa-Kamal et al., 2015). This is a clear example of how plant chemical defenses have proven efficacy for “defending” human health against various biotic stresses among those who consume the same plant as a food, a medicine or both (Mostafa-Kamal et al., 2015).

In Table S2, we wish to underscore the myriad medicinal uses retrieved from historical documents that persist to this day in Mesoamerican intellectual traditions. Out of 47 ailments to which chile peppers were applied, 24 of these were recorded among Maya communities. In 2000, fieldwork in Yucatecan Mayan communities documented the persistence of medicinal uses of at least seven different types of chiles (Aguilar-Meléndez and Lira-Noriega, 2018), suggesting that the diversification of chile peppers may continue to generate direct benefits to human health.

Conclusions

In this paper three hypothesis were evaluated and discussed:

(H1) A reduction and simplification of the potency of plant chemical defenses against seed predators, foliage herbivores and disease microbes with greater reliance on human intervention to protect the plants. This assumes that fully domesticated modern and commercial varieties of peppers under intense monoculture are more susceptible to predators (insect pests and diseases), than their wild progenitors, because they produce less number and concentration of SM in fruits, seeds, and leaves.

(H2) A diversification of the levels of potency and mixes of defense chemicals, given the wider range of habitats and broader geography to which the crop plants are exposed. This assumes that different C. annuum landraces in different agroecosystems produce variable amounts and types of SM.

(H3) An intensification of the potency of certain plant chemical defenses, given the need to protect the plants in agro-habitats where they occur at higher density and without as much beta diversity of neighboring plant species to slow the spread of predators, herbivores, competing weeds or diseases. This assumes that some domesticated landraces and modern varieties produce larger concentrations of valued SMs (capsaicinoids and carotenoids) under intense monoculture, compared to their wild progenitors.

Of these three hypotheses, we see more evidence supporting both H2 and H3, with respect to the diversification and heightening of pungency through chile pepper domestication. H2– the diversification of levels in SMs under domestication– seems to fit with the mechanism of “balancing selection,” in the sense of maintaining polymorphisms in Mesoamerican chile pepper landraces. The H3 trend has mostly been in more recently advanced cultivars of chile peppers outside their area of Neotropical origins. The H1 trend toward a reduction in pungency and other SMs such as phenolics and carotenoids in fruits and other organs is most evident in the recently advanced “bell pepper” group of chile landraces and cultivars, which are also most popular outside of the Neotropics. There is no question that sweet bell pepper cultivars of C. annuummust rely on human protection to survive against different predators that may prey on roots, leaves, fruits, and seeds. While birds may damage bell peppers grown in temperate climates outside of the Neotropics, they are virtually ineffective in dispersing the fruit (or most seeds within the fruit) to safe sites for germination and recruitment.

We conclude that contrary to trends in other crops, domestication has not necessarily reduced potency or homogenized the levels of chemical defenses—or at least of capsaicinoids—in chile pepper fruits. It has diversified capsaicinoid potency levels among and across domesticated varieties, compared to those found in most wild chile peppers. However, scientists still lack sufficient evidence to conclude that such diversification has occurred in any other SMs involved in chile pepper plant defense.

The likely diversification of SM production and/or concentration in domesticated C. annuum is the result of differential human selection of different allelic combinations—including selection of many recessive genes, under different environments and managed ecosystems—that are only rarely expressed in truly wild populations (Haak et al., 2014).

Higher concentrations of pungent compounds such as capsaicin may confer better adaptation and fitness to chile pepper crops under novel environments. These highly pungent varieties are now finding new uses in pharmacological and culinary uses, but the majority of the world's human inhabitants continues to directly use wild or domesticated landraces of chile peppers medicinally and gastronomically as they have for centuries.

There is plausible evidence from diverse cultures in Mexico that the SMs expressed in C. annuumfruits have been efficacious in reducing human diseases as well as infestations of internal and external parasites. This may in part explain why so many of the distinctive medicinal uses of chiles persist in nearly every Mesoamerican and Aridoamerican culture today. The nutritional and medicinal benefits of chiles may initially appear diffuse or minor to evolutionary ecologists, but their collective benefits as perceived by their “co-evolved” Mesoamerican cultivators, curanderas, cooks and consumers are impressive.

The extraordinary potency and the current intensity of gastronomic and pharmacological uses of chile peppers (Bosland and Votava, 2000) suggest that chile peppers should no longer be relegated the status of a “minor crop” as standard economic botany references and global agricultural statistics have done in the past. By 2010, global production of domesticated Capsicum fruits had reached 1.8 million ha, with more than 29 million metric tons annually harvested (Wahyuni et al., 2013). Their production continues to expand, while their culinary as well as medicinal and pest-repellent uses continue to diversify.

We should acknowledge that the current efficacy and economic significance of chile peppers' secondary metabolities in our diets and pharmocopieas is not merely due to the historic inventiveness of and mutualistic interactions with our own kind. It has benefited from the selective pressures by fungi, hemipteran insects, nematodes and rodents, as well as the directed dispersal of chile seeds by numerous bird species in the Neotropics. As such, there remains much to be learned by further advancing analyses of chile domestication to serve as a model for extended evolutionary synthesis.

Author Contributions

JL-R: designed research and wrote the paper; GN: designed research and wrote the paper; AA-M: wrote the paper.

Funding

Funding for this publication comes in part from Programa de Fortalecimiento a la Calidad Educativa (PFCE) of the Universidad Autónoma de Aguascalientes, México.

Conflict of Interest Statement

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

The reviewer, DP, and handling Editor declared their shared affiliation.

Supplementary Material

The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fevo.2018.00048/full#supplementary-material

References

Aguilar-Meléndez, A., and Lira-Noriega, E. (2018). ”Dónde crecen los chiles en México?” in Los Chiles que le dan Sabor al Mundo. Contribuciones Multidisciplinarias, eds A. Aguilar-Meléndez, M. A. Vásquez Dávila, E. Katz, and M. R. Hernández Colorado (Xalapa: Universidad Veracruzana and IRD), 61–79.

Aguilar-Meléndez, A., Morrell, P. L., Roose, M. L., and Kim, S. C. (2009). Genetic diversity and structure in semiwild and domesticated chiles (Capsicum annuum; Solanaceae) from Mexico. Am. J. Bot. 96, 1190–1202. doi: 10.3732/ajb.0800155

PubMed Abstract | CrossRef Full Text | Google Scholar

Alcorn, J. B. (1984). Huastec Mayan Ethnobotany. Austin, TX: University of Texas Press.

Google Scholar

Benrey, B., Callejas, A., Rios, L., Oyama, K., and Denno, R. F. (1998). The effects of domestication of brassica and phaseolus on the interaction between phytophagous insects and parasitoids. Biol. Control 11, 130–140. doi: 10.1006/bcon.1997.0590

CrossRef Full Text | Google Scholar

Bonfil-Batalla, G. (2012). México Profundo. Mexico: Una civilización negada. De Bolsillo.

Bosland, P. W., and Baral, J. B. (2007). “Bhut Jolokia”—The world's hottest known chile pepper is a putative naturally occurring interspecific hybrid. HortScience 42, 222–224.

Google Scholar

Bosland, P. W., and Votava, E. J. (2000). Peppers: Vegetable and Spice Capsicums, Vol. 22. Wallingford, UK: CABI.

Boster, J. S. (1985). Selection for perceptual distinctiveness: evidence from aguaruna cultivars of Manihot esculenta. Econ. Bot. 39, 310–325. doi: 10.1007/BF02858802

CrossRef Full Text | Google Scholar

Brown, C. H. (2010). “Development of agriculture in prehistoric mesoamerica: the linguistic evidence,” in Pre-Columbian Foodways: Interdisciplinary Approaches to Food, Culture, and Markets in Ancient Mesoamerica, eds J. Staller and M. Carrasco (New York, NY: Springer), 71–107.

Google Scholar

Brown, C. H., Clement, C. R., Epps, P., Luedeling, E., and Wichmann, S. (2013). The paleobiolinguistics of domesticated chili pepper (Capsicum spp.). Ethnobiol. Lett. 4, 1–11. doi: 10.14237/ebl.4.2013.2

CrossRef Full Text

Carlo, T. A., and Tewksbury, J. J. (2014). Directness and tempo of avian seed dispersal increases emergence of wild chiltepins in desert grasslands. J. Ecol. 102, 248–255. doi: 10.1111/1365-2745.12180

CrossRef Full Text | Google Scholar

Carrizo-García, C., Barfuss, M. H. J., Sehr, E. M., Barboza, G. E., Samuel, R., Moscone, E. A., et al. (2016). Phylogenetic relationships, diversification and expansion of chili peppers (Capsicum, Solanaceae). Ann. Bot. 118, 35–51. doi: 10.1093/aob/mcw079

PubMed Abstract | CrossRef Full Text | Google Scholar

Casas, A., Parra, F., Rangel, S., Guillén, S., Blancas, J., and Figueredo, C. J. (2015). “Evolutionary ecology and ethnobiology,” in Evolutionary Ethnobiology, eds U. P. Albuquerque, P. Muniz de Madeiros, and A. Casas (Cham: Springer), 37–57.

Google Scholar

Chen, Y. H., Gols, R., and Benrey, B. (2015). Crop domestication and its impact on naturally selected trophic interactions. Annu. Rev. Entomol. 60, 35–58. doi: 10.1146/annurev-ento-010814-020601

PubMed Abstract | CrossRef Full Text | Google Scholar

Dávila-Flores, A. M., DeWitt, T. J., and Bernal, J. S. (2013). Facilitated by nature and agriculture: performance of a specialist herbivore improves with host-plant life history evolution, domestication, and breeding. Oecologia 173, 1425–1437. doi: 10.1007/s00442-013-2728-2

PubMed Abstract | CrossRef Full Text | Google Scholar

de Avila, B. A. (2008). “La diversidad lingüística y el conocimiento etnobiológico,” in Capital Natural de México. Vol. I: Conocimiento Actual de la Biodiversidad, ed J. Sarukhán (México, DF: CONABIO), 497–556.

Do Rêgo, E. R., Finger, F. L., and do Rêgo, M. M. (2012). “Consumption of pepper in Brazil and its implications on nutrition and health of humans and animals,” in Pepper: Nutrition, Consumption and Health, Vol. 1, eds M. A. Salazar and J. M. Ortega (New York, NY: Nova Science), 159–170.

Google Scholar

Eich, E. (2008). Solanaceae and Convolvulaceae: Secondary Metabolites: Biosynthesis, Chemotaxonomy, Biological and Economic Significance (A Handbook). Berlin, Heidelberg: Springer.

Google Scholar

Eshbaugh, W. H. (1970). A biosystematic and evolutionary study of Capsicum baccatum (Solanaceae). Brittonia 22, 31–43. doi: 10.2307/2805720

CrossRef Full Text | Google Scholar

Fernández-Marín, B., Milla, R., Martín-Robles, N., Arc, E., Kranner, I., Becerril, J. M., et al. (2014). Side-effects of domestication: cultivated legume seeds contain similar tocopherols and fatty acids but less carotenoids than their wild counterparts. BMC Plant Biol. 14:1599. doi: 10.1186/s12870-014-0385-1

CrossRef Full Text | Google Scholar

Freeman, B., and Beattie, G. (2008). An overview of plant defenses against pathogens and herbivores. Plant Health Instr. doi: 10.1094/PHI-I-2008-0226-01

CrossRef Full Text | Google Scholar

Gepts, P. (2010). Crop domestication as a long-term selection experiment. Plant Breed. Rev. 24, 1–44. doi: 10.1002/9780470650288.ch1

CrossRef Full Text | Google Scholar

Good, E. C. (2005). Ejes conceptuales entre los nahuas de Guerrero: expresión de un modelo fenomenológico mesoamericano. Estud. Cult. Náhuatl 36, 87–113.

Google Scholar

Good, E. C. (2015). “Las cosmovisiones, la historia y la tradición intelectual en Mesoamérica,” in Cosmovisión Mesoamericana. Reflexiones, polémicas y etnografías. Fideicomiso historia de las Americas. (México, DF: Serie Ensayos), 139–160.

Haak, D. C., Kostyun, J. L., and Moyle, L. C. (2014). “Merging ecology and genomics to dissect diversity in wild tomatoes and their relatives,” in Ecological Genomics: Ecology and the Evolution of Genes and Genomes, eds C. R. Landry and N. Aubin-Horth (Dordrecht: Springer), 273–298.

Google Scholar

Haak, D. C., McGinnis, L. A., Levey, D. J., and Tewksbury, J. J. (2012). Why are not all chilies hot? A trade-off limits pungency. Proc. R. Soc. B Biol. Sci. 279, 2012–2017. doi: 10.1098/rspb.2011.2091

CrossRef Full Text | Google Scholar

Harlan, J. R. (1992). Crops and Man. Madison, WI: American Society of Agronomy.

Google Scholar

Hernández-Verdugo, S., Guevara-González, R. G., Rivera-Bustamante, R. F., and Oyama, K. (2001b). Screening wild plants of Capsicum annuum for resistance to pepper huasteco virus (PHV): presence of viral DNA and differentiation among populations. Euphytica 122, 31–36. doi: 10.1023/A:1012624830340

CrossRef Full Text | Google Scholar

Hernández-Verdugo, S., Luna-Reyes, R., and Oyama, K. (2001a). Genetic structure and differentiation of wild and domesticated populations of Capsicum annuum (Solanaceae) from Mexico. Plant Syst. Evol. 226, 129–142. doi: 10.1007/s006060170061

CrossRef Full Text | Google Scholar

Holt, J., and Birch, N. (1984). Taxonomy, evolution and domestication of Vicia in relation to aphid resistance. Ann. Appl. Biol.105, 547–556. doi: 10.1111/j.1744-7348.1984.tb03081.x

CrossRef Full Text | Google Scholar

Hunziker, A. T. (2001). Genera Solanacearum: The Genera of Solanaceae Illustrated, Arranged According to a New System. Ruggell: A.R.G. Gantner.

Johns, T. (1990). With Bitter Herbs They Shall Eat it: Chemical Ecology and The origins of Human Diet and Medicine. Tucson: University of Arizona Press.

Johns, T., and Kubo, I. (1988). A survey of traditional methods employed for the detoxification of plant foods. J. Ethnobiol. 8, 81–129

Google Scholar

Kim, W.-R., Kim, E. O., Kang, K., Oidovsambuu, S., Jung, S. H., Kim, B. S., et al. (2014). Antioxidant activity of phenolics in leaves of three red pepper (Capsicum annuum) cultivars. J. Agric. Food Chem. 62, 850–859. doi: 10.1021/jf403006c

PubMed Abstract | CrossRef Full Text | Google Scholar

Kliebenstein, D. J. (2004). Secondary metabolites and plant/environment interactions: a view through Arabidopsis thalianatinged glasses. Plant Cell Environ. 27, 675–684. doi: 10.1111/j.1365-3040.2004.01180.x

CrossRef Full Text | Google Scholar

Kraft, K. H., Brown, C. H., Nabhan, G. P., Luedeling, E., Ruiz, J., de J. L., d'Eeckenbrugge, G. C., et al. (2014). Multiple lines of evidence for the origin of domesticated chili pepper, Capsicum annuum, in Mexico. Proc. Natl. Acad. SciU.S.A. 111, 6165–6170. doi: 10.1073/pnas.1308933111

CrossRef Full Text | Google Scholar

Long-Solís, J. (1986). Capsicum y Cultura: la Historia del Chilli. México: Fondo de Cultura Económica.

López Austin, A. (2001). “El núcleo duro, la cosmovisión y la tradición mesoamericana,”, in Cosmovisión, Ritual e Identidad de los Pueblos Indígenas de México, eds J. Broda and F. Báez-Jorge (México: CONACULTA y Fondo de Cultura Económica), 47–65.

Marrush, M., Yamaguchi, M., and Saltveit, M. E. (1998). Effect of potassium nutrition during bell pepper seed development on vivipary and endogenous levels of abscisic acid (ABA). J. Am. Soc. Horticult. Sci. 123, 925–930.

Google Scholar

Meyer, R. S., DuVal, A. E., and Jensen, H. R. (2012). Patterns and processes in crop domestication: an historical review and quantitative analysis of 203 global food crops. New Phytol. 196, 29–48. doi: 10.1111/j.1469-8137.2012.04253.x

PubMed Abstract | CrossRef Full Text | Google Scholar

Mostafa-Kamal, A., Chowdhury, K. A. A., Moazzam, M., Chy, H., Shill, L. K., Chowdhury, S., et al. (2015). Evaluation of anthelmintic activity of seeds of Sesamum indicum L. and fruits of Capsicum frutescens L. J. Pharmacogn. Phytochem. 3, 256–259.

Google Scholar

Nabhan, G. P. (2004). Why Some Like it Hot: Food, Genes, and Cultural Diversity. Washington, DC: Island Press.

Google Scholar

Nambara, E., Okamoto, M., Tatematsu, K., Yano, R., Seo, M., and Kamiya, Y. (2010). Abscisic acid and the control of seed dormancy and germination. Seed Sci. Res. 20, 55–67. doi: 10.1017/S0960258510000012

CrossRef Full Text | Google Scholar

Padilha, H. K. M., and Barbieri, R. L. (2016). Plant Breeding of Chili Peppers (Capsicum, Solanaceae)-A Review. Embrapa Clima Temperado-Artigo em periódico indexado (ALICE). Availabele online at: https://www.alice.cnptia.embrapa.br/bitstream/doc/1060246/1/RosaLiaartigo2016plantbreedingofchilipepperareview.pdf

Pegard, A., Brizzard, G., Fazari, A., Soucaze, O., Abad, P., and Djian-Caporalino, C. (2005). Histological characterization of resistance to different root-knot nematode species related to phenolics accumulation in Capsicum annuum. Phytopathology95, 158–165. doi: 10.1094/PHYTO-95-0158

CrossRef Full Text

Perry, L., and Flannery, K. V. (2007). Precolumbian use of chili peppers in the Valley of Oaxaca, Mexico. Proc. Natl. Acad. Sci. U.S.A. 104, 11905–11909. doi: 10.1073/pnas.0704936104

PubMed Abstract | CrossRef Full Text | Google Scholar

Pickersgill, B. (2007). Domestication of plants in the Americas: insights from Mendelian and molecular genetics. Ann. Bot.100, 925–940. doi: 10.1093/aob/mcm193

PubMed Abstract | CrossRef Full Text | Google Scholar

Randle, W. M., and Honma, S. (1981). Dormancy in peppers [Capsicum annuum]. Sci. Hortic. 14, 19–25. doi: 10.1016/0304-4238(81)90074-1

CrossRef Full Text | Google Scholar

Retes-Manjarrez, J. E. (2016). Detección de resistencia al virus huasteco vena amarilla del chile y su heredabilidad en genotipos silvestres de Capsicum annuum L. Interciencia 41, 541–547.

Google Scholar

Rindos, D. (1984). The Origins of Agriculture: An Evolutionary Perspective. San Diego, CA: Academic Press.

Google Scholar

Rodriguez-Saona, C., Vorsa, N., Singh, A. P., Johnson-Cicalese, J., Szendrei, Z., Mescher, M. C., et al. (2011). Tracing the history of plant traits under domestication in cranberries: potential consequences on anti-herbivore defences. J. Exp. Bot.. 62, 2633–2644. doi: 10.1093/jxb/erq466

PubMed Abstract | CrossRef Full Text | Google Scholar

Rozin, P., and Schiller, D. (1980). The nature and acquisition of a preference for chili pepper by humans. Motiv. Emot. 4, 77–101. doi: 10.1007/BF00995932

CrossRef Full Text | Google Scholar

Sariyildiz, Z., Demir, I., and Halloran, N. (2005). Germination at stress temperatures and ABA content of pepper (Capsicum annuum L.) seeds in relation to seed development. Eur. J. Horticult. Sci. 70, 67–70.

Google Scholar

Tewksbury, J. J., Levey, D. J., Huizinga, M., Haak, D. C., and Traveset, A. (2008a). Costs and benefits of capsaicin-mediated control of gut retention in dispersers of wild chilies. Ecology 89, 107–117. doi: 10.1890/07-0445.1

PubMed Abstract | CrossRef Full Text | Google Scholar

Tewksbury, J. J., and Nabhan, G. P. (2001). Seed dispersal: directed deterrence by capsaicin in chillies. Nature 412, 403-404. doi: 10.1038/35086653

CrossRef Full Text | Google Scholar

Tewksbury, J. J., Reagan, K. M., Machnicki, N. J., Carlo, T. A., Haak, D. C., Pe-aloza, A. L. C., et al. (2008b). Evolutionary ecology of pungency in wild chilies. Proc. Natl. Acad. Sci. U.S.A. 105, 11808–11811. doi: 10.1073/pnas.0802691105

PubMed Abstract | CrossRef Full Text | Google Scholar

Vela, E. (2009). Los Chiles de México. Mexico, DF: Catalogo visual. Editorial Raíces.

Wahyuni, Y., Ballester, A. R., Sudarmonowati, E., Bino, R. J., and Bovy, A. G. (2011). Metabolite biodiversity in pepper (Capsicum) fruits of thirty-two diverse accessions: variation in health-related compounds and implications for breeding. Phytochemistry 72, 1358–1370. doi: 10.1016/j.phytochem.2011.03.016

PubMed Abstract | CrossRef Full Text | Google Scholar

Wahyuni, Y., Ballester, A.-R., Sudarmonowati, E., Bino, R. J., and Bovy, A. G. (2013). Secondary metabolites of Capsicum species and their importance in the human diet. J. Nat. Prod. 76, 783–793. doi: 10.1021/np300898z

PubMed Abstract | CrossRef Full Text | Google Scholar

Wink, M. (2003). Evolution of secondary metabolites from an ecological and molecular phylogenetic perspective. Phytochemistry 64, 3–19. doi: 10.1016/S0031-9422(03)00300-5

PubMed Abstract | CrossRef Full Text | Google Scholar

Zeder, M. A. (2017). Domestication as a model system for the extended evolutionary synthesis., Interface Focus 7:20160133. doi: 10.1098/rsfs.2016.0133

CrossRef Full Text

Keywords: Capsicum annuum, plant domestication, secondary metabolites, plant chemical defenses, Neotropics, Mesoamerica

Citation: Luna-Ruiz JdJ, Nabhan GP and Aguilar-Meléndez A (2018) Shifts in Plant Chemical Defenses of Chile Pepper (Capsicum annuum L.) Due to Domestication in Mesoamerica. Front. Ecol. Evol. 6:48. doi: 10.3389/fevo.2018.00048

Received: 31 August 2017; Accepted: 05 April 2018;
Published: 24 April 2018.

Edited by:

Alejandro Casas, Instituto de Investigaciones en Ecosistemas y Sustentabilidad, Universidad Nacional Autónoma de México, Mexico

Reviewed by:

Daniel Pinero, Universidad Nacional Autónoma de México, Mexico
Rosa Lia Barbieri, Embrapa Clima Temperado, Brazil

Copyright © 2018 Luna-Ruiz, Nabhan and Aguilar-Meléndez. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.

*Correspondence: Jose de Jesus Luna-Ruiz, joselunaruiz11@yahoo.com.mx


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너무나 재미난 식물의 세계. 

지금까지 식물에 있는 가시의 종류가 초식동물에게서 자신을 방어하기 위한 무기로만 간주되었는데, 

곤충에게도 그러한 기능을 수행할 수 있다는 연구결과가 나왔다. 


가시를 제거한 잎과 가시가 달린 잎을 두고 애벌레에게 먹게 하자, 가시가 있는 잎을 더 늦게 먹는다는 사실이 밝혀졌다.




토종 배추나 토종 무의 잎에도 가시 같은 게 발달한 품종이 꽤 있는데 그런 이유였는가? 

또 벼의 까락도 그런 기능을 수행할 수 있을까? 


이거 너무너무 재미난 연구이다.





http://rsbl.royalsocietypublishing.org/content/13/5/20170176

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식물들도 알면 알수록 놀라울 뿐이다.
식물 자신에게 해충 등이 발생하면 그를 해결하기 위해 자체적인 노력도 기울이는 한편, 주변의 동료들에게도 자신들만의 수단으로 위험 상황을 알려 방어체계를 갖추도록 돕는다고 한다.

병해충이 발생하는 걸 막고자 간단하고 빠르며 편한 수단으로 농약만 찾을 일이 아닌 듯하다.

Overview of terpenoids in plant defence against herbivorous insects. Volatile terpenoids that belong to the HIPVs (herbivore-induced plant volatiles) and OIPVs (oviposition-induced plant volatiles) are released in response to herbivore attack and oviposition, respectively. Terpenoids induce defence responses in the systemic parts of the same plant. These volatiles attract insect carnivores that feed on the herbivores, thereby inducing indirect defence in plants, and prime neighbouring conspecific and heterospecific plants. The perception of terpenoids by neighbouring plants results in influx of calcium ions and membrane depolarization. Epigenetic regulation of this priming response is reported to evoke the priming memory for up to 5 d. Terpenoids also affect tritrophic interactions in soil.



Overview of arbuscular mycorrhiza (AM)-reinforced defence against herbivorous insects. Plants colonized by AM fungi are more tolerant by virtue of superior growth and nutrient uptake. Formation of AM may result in increased glandular trichome density, availability of substrates, induction of MEP (higher expression of DXS and DXR) and MVA (higher expression of HMGR) pathways, and induction of terpene synthases (TPSs). These factors in various combinations result in changes in the terpenoid profile in mycorrhizal (M) plants, inducing both direct and indirect defence responses against herbivore attack in the plant. Mycorrhizal colonization results in amplification of a wound signal, leading to priming of neighbouring plants. Common mycelial networks (CMNs) serve as signalling conduits between interconnected plants under herbivore attack. JA, jasmonic acid; SA, salicylic acid.





Background Plants, though sessile, employ various strategies to defend themselves against herbivorous insects and convey signals of an impending herbivore attack to other plant(s). Strategies include the production of volatiles that include terpenoids and the formation of symbiotic associations with fungi, such as arbuscular mycorrhiza (AM). This constitutes a two-pronged above-ground/below-ground attack–defence strategy against insect herbivores.

Scope Terpenoids represent an important constituent of herbivore-induced plant volatiles that deter herbivores and/or attract their predators. Terpenoids serve as airborne signals that can induce defence responses in systemic undamaged parts of the plant and also prime defence responses in neighbouring plants. Colonization of roots by AM fungi is known to influence secondary metabolism in plants; this includes alteration of the concentration and composition of terpenoids, which can boost both direct and indirect plant defence against herbivorous insects. Enhanced nutrient uptake facilitated by AM, changes in plant morphology and physiology and increased transcription levels of certain genes involved in the terpenoid biosynthesis pathway result in alterations in plant terpenoid profiles. The common mycorrhizal networks of external hyphae have added a dimension to the two-pronged plant defence strategy. These act as conduits to transfer defence signals and terpenoids.

Conclusion Improved understanding of the roles of terpenoids in plant and AM defences against herbivory and of interplant signalling in natural communities has significant implications for sustainable management of pests in agricultural ecosystems.



INTRODUCTION

Terpenoids represent the largest and structurally the most diverse group of volatiles released by plants. Biologically, a wide array of terpenoids can enable plants to interact with other organisms, such as insects, pathogens and neighbouring plants (Kant et al., 2004Mercke et al., 2004Kappers et al., 2005Cheng et al., 2007ab). Terpenoids are emitted either constitutively or induced in response to biotic (Dudareva et al., 20062013Unsicker et al., 2009Rasmann et al., 2012) and abiotic (Gouinguené and Turlings, 2002Loreto and Schnitzler, 2010) stresses.

Attack by insects induces plants to emit a blend of volatile organic compounds (VOCs). Terpenoids are important members of the class of herbivore-induced plant volatiles (HIPVs) (Gershenzon and Dudareva, 2007Mumm et al., 2008). Some terpenoids serve as repellents (Laothawornkitkul et al., 2008Unsicker et al., 2009Maffei, 2010), while others function in indirect plant defence by attracting arthropods that prey upon or parasitize herbivores (Kessler and Baldwin, 2001Rasmann et al., 2005Schnee et al., 2006). Additionally, terpenoids are produced in response to oviposition and are involved in the attraction of egg-parasitizing insects (Conti et al., 2008Büchel et al., 2011Tholl et al., 2011Hilker and Fatouros, 2015).

In addition to their roles in direct and indirect defences, plant terpenoids, along with other HIPVs, such as green leaf volatiles (GLVs), serve as airborne signals that can be perceived by undamaged systemic parts of the same plant (Frost et al., 2007Heil and Silva Bueno, 2007) and by neighbours (Karban et al., 2000). In response to perceived volatile signals, plants express defence genes and synthesize secondary metabolites (Shulaev et al., 1997Arimura et al., 2000bSugimoto et al., 2014) or prime their defences against pests (Engelberth et al., 2004Heil and Kost, 2006Ton et al., 2006). Although primed plants do not show any trait of resistance, they become prepared to respond more rapidly and more intensely when attacked (Conrath et al., 2006Heil and Ton, 2008).

The synthesis of terpenoids can be altered by numerous biotic and abiotic factors (Owen and Peñuelas, 2005Peñuelas and Munné-Bosch, 2005Brunetti et al., 2013). Among such influencing factors is the formation of arbuscular mycorrhiza (AM), defined as a symbiotic association of plant roots with soil fungi belonging to the phylum Glomeromycota. Arbuscular mycorrhizal fungi are heterokaryotic, obligate symbionts that confer on plants multifarious benefits, like improved access to nutrients and water and enhanced resistance to biotic and abiotic stresses (Finlay, 2008Smith and Read, 2008Miransari, 2010Ruiz-Lozano et al., 2012Evelin et al., 2013). In return for such colossal benefits, the fungus obtains carbon from the plants (Smith and Gianinazzi-Pearson, 1988Smith and Read, 2008). Arbuscular mycorrhiza interconnects plants by means of an extensive subterranean hyphal network. This network is specialized for nutrient (primarily phosphate) and water uptake (Miller et al., 1995). The bidirectional exchange of nutrients between the symbionts takes place at highly branched intracellular structures called arbuscules, which are formed in the inner cortex of the plant root by the mycobiont (Harrison, 2005Parniske, 2008). This interaction plays a crucial role in plant ecosystem functioning, as more than 80 % of the terrestrial plant species rely on AM fungi for their mineral nutrition (Smith and Read, 2008).

The formation of AM changes the physiology and ecology of the plant. Arbuscular mycorrhiza potentially strengthens both direct and indirect plant defence systems (Pozo and Azcón-Aguilar, 2007Jung et al., 2012Borowicz, 2013) by altering the secondary metabolism of the plant (Hohnjec et al., 2005Walker et al., 2012). Formation of AM has been demonstrated to change the concentration and composition of terpenoids (Copetta et al., 2006Khaosaad et al., 2006Kapoor et al., 2007Rapparini et al., 2008). This alters the plant’s attractiveness and also the insect’s behaviour (Schausberger et al., 2012Babikova et al., 2014aShrivastava et al., 2015). Cascading effects on higher trophic levels have also been reported (Gange et al., 2003), as have indirect effect on predators and parasitoids of herbivores (Gange et al., 2003Guerrieri et al., 2004Laird and Addicott, 2007). Consequently, increased knowledge of the mechanisms that influence production of terpenoids in AM plants will make important contributions to the biocontrol and integrated management of pests.

In this review, readers are first introduced to the terpenoids that contribute to HIPVs, and their synthesis in the plant cell. The review emphasizes the role of terpenoids in plant defence against herbivorous insects (Fig. 1) and discusses their probable role in airborne signalling within the plant and to nearby plants. It then focuses on the significance of terpenoids in AM-mediated reinforcement of direct and indirect defences against herbivory (Fig. 2), further discussing various mechanisms underlying changes in the concentration and composition of terpenoids in mycorrhizal plants. Finally, it outlines the prospects for bioengineered terpenoid-producing plants and AM symbiosis in the sustainable management of pests in agricultural systems.


TERPENOIDS IN HIPVS

Terpenoids are one of the important constituents of volatiles that are released by plants in response to herbivore attack (Gershenzon and Dudareva, 2007Mumm et al., 2008). They are low molecular weight compounds derived from the basic five-carbon building blocks of isopentenyl diphosphate (IPP). The key players among the terpenoid volatiles that significantly contribute to HIPVs are monoterpenes (C10), sesquiterpenes (C15) and homoterpenes such as 4,8-dimethylnona-l,3,7-triene (DMNT) and 4,8,12-trimethyltrideca-1,3,7,11-tetraene (TMTT) (Leitner et al., 2005Arimura et al., 2008Mithöfer and Boland, 2012). Isoprene (2-methyl-1,3-butadiene), although not produced by many plants, has also been demonstrated to play an important role in defence against insect herbivory (Laothawornkitkul et al., 2008).

There are two pathways for the production of terpenoids: the cytoplasmic mevalonate (MVA) pathway and the plastidial 2-C-methyl-d-erythritol 4-phosphate (MEP) pathway (Aharoni et al., 2005Rodríguez-Concepcion, 2006Cheng et al., 2007a). Both pathways generate universal precursors for terpenoid synthesis from IPP and its isomer dimethylallyl diphosphate (DMAPP). While monoterpenes are synthesized via the MEP pathway, sesquiterpenes are produced by the MVA pathway. In contrast to the conventional allocation, which suggests the MVA and MEP pathways are strictly independent, there is emerging evidence that the two pathways cross-talk by allowing IPP to shuttle between different compartments (Piel et al., 1998Bick and Lange, 2003Bartram et al., 2006Rodríguez-Concepcion, 2006). However, it has been found that ∼80 % of the IPP derived from the MEP pathway contributes to sesquiterpene biosynthesis following herbivory (Bartram et al., 2006Arimura et al., 2008).

Condensation of C5 units gives rise to all-trans or all-cis prenyl diphosphate precursors that are converted by the terpene synthase (TPS) enzymes of different subfamilies into acyclic, mono-, bi- or tricyclic monoterpenes, sesquiterpenes or semivolatile diterpenes (Chen et al., 2011). Terpene synthases are generally multiproduct enzymes, and thus even a single TPS can significantly enhance the diversity of terpenoids (Gershenzon, 1994Tholl, 2006Arimura et al., 2008). The primary terpene skeletons may be further modified through secondary enzymatic reactions, such as dehydrogenations, hydroxylations, methylations and acylations (Dudareva et al., 2006).

Some terpenoids, such as β-ionone, are produced not directly from IPP, but instead from tetraterpenes such as carotenoids, by carotenoid cleavage dioxygenases (Dudareva et al., 2013). Homoterpenes such as DMNT and TMTT are synthesized by oxidative degradation of the sesquiterpene (3S)-(E)-nerolidol and the diterpene geranyl linalool by cytochrome P450 enzymes (Arimura et al., 2009Maffei, 2010).

TERPENOIDS IN DEFENCE AGAINST HERBIVORY

Direct interaction

Terpenoids can serve as repellents and reduce larval feeding and oviposition by herbivores (De Boer et al., 2004Laothawornkitkul et al., 2008Unsicker et al., 2009Maffei, 2010). For example, linalool (a monoterpenoid) and (E)-β-farnesene (a sesquiterpene) produced by plants repel herbivores and aphids, respectively (Aharoni et al., 2003Unsicker et al., 2009Maffei, 2010). Although the exact mechanisms by which terpenoids affect insect pests are not known, probable processes include the inhibition of ATP synthase, alkylation of nucleophiles and interference with moulting (Langenheim, 1994). Terpenoids such as α-pinene and β-pinene have been shown to disturb the nervous system in insects by inhibition of acetylcholinesterase (Yeom et al., 2012).

Indirect above-ground interactions

Terpenoids emitted as a result of herbivore attack have an important role in a plant’s indirect defences, attracting predators or parasites of herbivores and facilitating location of the attacked plants (Heil, 2008). For example, infestation of lima bean leaves by spider mites (Tetranychus urticae) triggers the de novoproduction of terpenoids such as (E)-β-ocimene, linalool, DMNT and TMTT (Dicke et al., 19901999De Boer et al., 2004Shimoda et al., 2005), which lure the predacious mites (Phytoseiulus persimilis) that prey on spider mites (Takabayashi and Dicke, 1996). The volatiles from spider mite-infested lima beans, treated with fosmidomycin (an inhibitor of the MEP pathway) were less attractive to the predatory mites than those from infested control plants, indicating the significance of terpenoids in indirect defence (Mumm et al., 2008).

The high chemical diversity within HIPV mixtures complicates identification of the compound(s) actually responsible for signalling herbivore enemies. However, it has been demonstrated by investigation of individual compounds that terpenoids such as the homoterpene TMTT can attract predatory mites (De Boer et al., 2004). Genetic engineering for enhanced expression of genes encoding enzymes for the formation of terpenoids has ascertained the role of individual compounds in tritrophic interactions. Transgenic Arabidopsis thaliana overexpressing strawberry nerolidol synthase, a TPS, attracted more predatory P. persimilis mites (Kappers et al., 2005). Similarly, overexpression of a corn TPS gene (TPS10) in Athalianaaugmented the attractiveness of these transgenic plants to the parasitic wasp Cotesia marginiventris (Schnee et al., 2006). Interestingly, changes in HIPV blends emitted at different times can impact the interactions among a plant, its herbivores and their parasitoids, and stimulate different preferences for herbivores and their parasitoids (Mathur et al., 2013Pashalidou et al., 2015). The generalist Spodoptera littoralis preferred undamaged Brassica juncea plants, whereas its parasitoid (C. marginiventris) preferred 48-h damaged plants (Mathur et al., 2013). In Brassica nigra, parasitoid wasps (Cotesiaglomerata) were attracted to plants infested with eggs just before and shortly after larval hatching of Pieris brassicae (Pashalidou et al., 2015). The authors have correlated this preference to temporal changes in the blend of HIPVs (terpenoids).

Response to oviposition

Plants may respond to herbivore egg deposition and activate defences before actual feeding injury is initiated, which might be a successful tactic to reduce impending herbivory (Hilker et al., 2002Mumm and Hilker, 2006Pashalidou et al., 2015). Analogous to HIPVs, plant volatiles induced specifically by insect oviposition are termed oviposition-induced plant volatiles (OIPVs) (Hilker and Fatouros, 2015). Terpenoids are important members of the class of OIPVs (Conti et al., 2008Tholl et al., 2011). The OIPV-specific terpenoids attract egg parasitoids (Wegener and Schulz, 2002Mumm and Hilker, 2005Büchel et al., 2011). Intriguingly, the attractiveness of egg-laden foliage to the egg parasitoid has been related to an increase in transcription levels of sesquiterpene synthase (Köpke et al., 2010Beyaert et al., 2012). Oviposition on Pinus sylvestris needles by the sawfly Diprion pini induced both local and systemic emission of terpenoid volatiles (Hilker et al., 2002Mumm and Hilker, 2006). This response was specific to oviposition, and could not be induced by artificial wounding (Hilker and Fatouros, 2015). However, volatile cues to attract egg parasitoids have not yet been identified.

Response to below-ground infestation

Below-ground VOC patterns are generally distinct from volatiles released from above-ground plant tissues (Peñuelas et al., 2014). Terpenes are the most prominent VOCs emitted from below-ground tissues (Rasmann et al., 2005Ali et al., 2011Palma et al., 2012Peñuelas et al., 2014), and among these sesquiterpenes are the compounds that show the greatest diffusion in the soil (Hiltpold and Turlings, 2008). Terpenoids have been shown to play a crucial role in the specificity of below-ground tritrophic interactions (Rasmann and Turlings, 2008). The most well-studied example is the induction of (E)-β-caryophyllene by maize roots infested by larvae of the leaf beetle Diabrotica virgifera virgifera, which attracted the entomopathogenic nematode Heterorhabditis megidis (Rasmann et al., 2005). on the other hand, (E)-β-caryophyllene also served as an attractant aiding D. virgifera larvae to identify a susceptible host (Robert et al., 2012). one possible explanation for the contradictory observations in the above studies is that as maize roots only emit (E)-β-caryophyllene (Hiltpold and Turlings, 2008), it can be presumed that the entomopathogenic nematode H. megidis has developed an adaptation to take cues from the (E)-β-caryophyllene emitted by maize roots for efficient prey-searching.

Multiple herbivore infestations

In nature, plants are generally infested by two or more herbivore species, either concurrently or serially. However, most of the studies in this area have been conducted on single-herbivore attack under controlled conditions. Infestation by two or more insect species causes complex variations in volatile profile, and cannot be predicted on the basis of observations on single herbivores. When two or more herbivores co-infest, the effects may be negative or additive, or one type of herbivore takes priority. For example, concurrent occurrence of herbivory above- as well as below-ground by S.littoralis and D. virgifera, respectively, negatively influenced tritrophic signalling due to decreased (E)-β-caryophyllene production by maize roots (Rasmann and Turlings, 2007). This may be explained by reduced availability of a C source required for the synthesis of the terpenoid precursors. on the other hand, HIPVs emitted by lima beans and pepper plants infested by two herbivore species attracted more predatory mites and predatory mirid bugs, respectively, compared with volatiles emitted by plants infested by either herbivore separately (Dicke et al., 2009). Furthermore, most studies are performed under highly controlled conditions, which impedes application of the results in natural environments. Thus, a major challenge is the development of experimental designs that consider the ecological reality of infestations.

AIRBORNE SIGNALLING TO NEIGHBOURING PLANTS AND SYSTEMIC PARTS OF THE SAME PLANT

The airborne volatile signals from herbivore-damaged plants (emitters) enable nearby conspecific and heterospecific undamaged plants (receivers) to foresee the impending arrival of herbivores and tailor their defence accordingly (Baldwin and Schultz, 1983Arimura et al., 2000aEngelberth et al., 2004Karban et al., 2006Heil and Silva Bueno, 2007Ramadan et al., 2011). Herbivore-induced plant volatiles serve as external signals for within-plant communication, and elicit a defence response in systemic parts of the affected plant (Karban et al., 2006Frost et al., 2007Heil and Silva Bueno, 2007Park et al., 2007Das et al., 2013). Damaged leaves immediately release VOCs and communicate more quickly with leaves located nearby that are not directly connected by vasculature (Heil and Ton, 2008). Plants may react to the signals connected with the presence of herbivores by upregulating defence genes (Arimura et al., 2000b), leading to increased production of defence-related metabolites such as phytohormones, proteinase inhibitors, terpenoids and/or extrafloral nectar (Tscharntke et al., 2001Engelberth et al., 2004Kost and Heil, 2006; Frost et al.2008aBlande et al., 2010). These changes are ultimately translated into reduced herbivory and improved fitness of receiver (Karban and Maron, 2002Kost and Heil, 2006Muroi et al., 2011). The responses include a combination of priming and induced defences, according to the allocation cost of different classes of defence, with plants priming more expensive responses and inducing less costly metabolites, such as extrafloral nectar or HIPVs, to attract natural enemies of the herbivore (Kost and Heil, 2006; Frost et al.2008b). Participation of volatiles in interplant below-ground interactions is not well elucidated (Schenkel et al., 2015Delory et al., 2016). Whether VOCs emitted by roots in the rhizosphere can diffuse into the phyllosphere and convey signals to prime above-ground parts of the same plant is also not effectively documented (Erb et al., 2008).

ROLE OF TERPENOIDS IN AIRBORNE SIGNALLING

An important step in understanding the mechanistic foundations of airborne priming is the elucidation of the actual messengers. Green-leaf volatiles and terpenoids are two important components of HIPVs. Green-leaf volatiles, which are aldehydes, alcohols and esters resulting from lipoxygenase cleavage of fatty acids, account for the distinctive odour of damaged leaves (Paré and Tumlinson, 1999). Although evidence for GLVs as priming signals has been observed in several plant species (Farag and Paré, 2002Ruther and Fürstenau, 2005Ruther and Kleier, 2005Kost and Heil, 2006Sugimoto et al., 2014), reports on terpenoids have been variable. The role of volatile terpenes in plant–plant interactions was initially reported in lima bean, where terpenoids such as β-ocimene, DMNT, TMTT and linalool, released upon feeding of T.urticae, induced the expression of defence genes encoding lipoxygenase (synthesis of jasmonic acid) and the pathogenesis-related protein PR-2 (β-1,3-glucanase) (Arimura et al., 2000b). In maize, however, terpenoids were not associated with priming defence responses in the receiver plants (Ruther and Fürstenau, 2005).

Early events in the perception of volatile signals comprise an alteration of the plasma membrane potential (Vm) and an increase in cytosolic calcium ([Ca2+]cyt) (Zebelo et al., 2012). It was observed that GLVs such as (E)-2-hexenal, (Z)-3-hexenal and (Z)-3-hexenyl acetate induced stronger Vm depolarization and a greater increase in cytosolic calcium flux compared with terpenoids such as α-pinene and β-caryophyllene. These terpenoids induced a significant Vm depolarization with respect to controls, but did not exert any significant effect on [Ca2+]cyt homeostasis (Zebelo et al., 2012). Moreover, Vm depolarization was found to increase with increasing GLV concentration. Green-leaf volatiles are immediately released after damage and their release ceases within a few minutes of damage (Arimura et al., 2009), while the release of monoterpenes typically starts 24 h after attack (Dudareva et al., 2006Pichersky et al., 2006). The emission of terpenoids is often systemic and extended (Paré and Tumlinson, 1999). These observations indicate that GLVs are better candidates than terpenoids for conveying airborne signals of herbivore attack. Further studies are required to identify the messengers (volatiles) involved in transmitting signals within and to nearby plants. The complementary approach of using plant mutants deficient in various components of HIPVs (GLVs or terpenoids) has enabled the role of individual compounds in plant–plant signalling to be deciphered (Baldwin et al., 2006). However, using this technique, Paschold et al. (2006) observed that neither GLVs nor terpenoids prime the expression of defence genes in Nicotiana attenuata. The role of various HIPVs as volatile priming signals has continued to be uncertain because in most studies healthy plants were treated with synthetic volatiles, a procedure that does not satisfactorily mimic the exact timing and concentrations of HIPV emissions in nature. Furthermore, genetic manipulation of plants for enhanced synthesis of HIPVs may result in several undesirable effects (Erb et al., 2015). As individual volatile compounds do not participate in plant–insect interactions in isolation, another key issue for exploration is the interactive effects of different VOCs in these interactions. Furthermore, techniques based on the limit of detection of terpenoids do not take into consideration the sensitivity of perception by biological systems (insects), and hence do not necessarily provide biologically useful information.

After herbivore departure, plants likely cease to release HIPVs that attract parasitoids (Puente et al., 2008). If emission were to continue, signals would deliver unreliable information to parasitoids, which would then be incapable of tracking their hosts. Receiver plants are not aware of how much later the herbivores will arrive, and therefore have no clues regarding how long the primed state should be maintained. However, very little is known about how receiver plants control the duration of the primed state, which is of importance in terms of the arrival time of herbivores. The molecular mechanisms involved in sustaining the primed state are also unresolved. Ali et al. (2013) demonstrated that the priming effect of HIPVs on resistance against herbivores is memorized and stored by plants through epigenetic regulation of DNA, with plants able to evoke this memory when attacked by herbivores. Treatment with HIPV was shown to result in demethylation of cytosine sites in the promoter region of a herbivore-responsive gene for Bowman–Birk-type trypsin inhibitor (TI). Further experiments are required to substantiate understanding of the epigenetic control of airborne signalling between plants.

ARBUSCULAR MYCORRHIZA AND HERBIVOROUS INSECT RESISTANCE

Arbuscular mycorrhizal fungi are reported to affect the performance of herbivores (Gange and West, 1994Vicari et al., 2002Pozo and Azcón-Aguilar, 2007Gehring and Bennett, 2009Borowicz, 2013). Arbuscular mycorrhiza symbioses adversely affect root-feeding insects, while their effects on leaf-feeding insects are variable (Pozo and Azcón-Aguilar, 2007Gehring and Bennett, 2009Borowicz, 2013). The extent of protection also changes with the feeding style of the attacking herbivore. Arbuscular mycorrhiza symbiosis seems to benefit phloem-sucking insects (aphids) (Gange et al., 1999Koricheva et al., 2009), while effects on chewing and leaf-mining insects are largely adverse (Gange and West, 1994Vicari et al., 2002Hoffmann et al., 2009); counter-examples, however, also exist (Babikova et al., 2014bShrivastava et al., 2015). This considerable variation can be ascribed to some extent to the species (plant, fungus and herbivore) involved in the tripartite interactions (Bennett and Bever, 2007Gange, 2007Leitner et al., 2010Pineda et al., 2010). Akin to the complexity of plant–herbivore–natural enemy tripartite interactions, AM also affects predators and parasitoids of herbivores (Gange et al., 2003Guerrieri et al., 2004Laird and Addicott, 2007).

Participating AM fungi may induce resistance to neighbouring plants, via hyphal networks functioning as plant–plant underground communication systems (Song et al., 2010Babikova et al., 2013). Common mycorrhizal network serve as conduits facilitating the transfer of defence signals and also terpenoids between neighbouring plants under herbivore attack (Song et al., 2014).

ROLE OF TERPENOIDS IN AM-REINFORCED RESISTANCE AGAINST HERBIVOROUS INSECTS

The significance of below-ground interactions between plant and AM fungi for assessing VOC emission rates and their consequent ecological role in the deployment of indirect defences by plants has been emphasized (Rapparini et al., 2008). The indirect effect of AM on herbivore defence has been correlated to changes in the blend of terpenoids that alter plant attractiveness and insect behaviour (Babikova et al., 2014a). In Phaseoluschallenged by spider mites, for example, AM symbiosis with Funneliformis mosseae increased the emission of β-ocimene and β-caryophyllene, resulting in increased attraction of predators of spider mites (Schausberger et al., 2012). Similarly, Shrivastava et al. (2015) observed a greater defence response against beet armyworm (Spodoptera exigua) in AM than in non-mycorrhizal plants, partly attributable to the difference in levels and blends of terpenoids. Arbuscular mycorrhiza formation led to enhanced levels of monoterpenes and sesquiterpenes, including monoterpenes such as myrcene, which were not detected in non-mycorrhizal plants. Myrcene is a semiochemical utilized by insects for communication, e.g. to deter thrips (Broughton and Harrison, 2012) or to attract aphidophagous hoverflies in a terrestrial orchid (Stökl et al., 2011).

EFFECTS OF ARBUSCULAR MYCORRHIZA on TERPENOIDS

Arbuscular mycorrhiza symbiosis can affect a number of volatile organic compounds, including terpenes. Arbuscular mycorrhiza fungal colonization has been shown to enhance the production of triterpenoids (Akiyama and Hayashi, 2002), apocarotenoids (Klingner et al., 1995Fester et al., 2002Strack and Fester, 2006Akiyama, 2007Walter and Strack, 2011) and abscisic acid (Meixner et al., 2005) in roots of various plants. Systemic effects of AM on the quantity and quality of terpenoids in above-ground parts of plants have also been mooted (Kapoor et al., 2002abCopetta et al., 2006Khaosaad et al., 2006Kapoor et al., 2007Zubek et al., 2010Weisany et al., 2015Rydlová et al., 2016). These studies have so far been largely confined to the effects of AM on individual components of terpenoids or a suite of terpenoids (essential oil composition) that have pharmaceutical value. Arbuscular mycorrhiza may enhance the biosynthesis of an individual terpenoid either by increase in isoprene precursors through the induction of biosynthesis pathways and/or by induction of terpene synthase enzymes (Shrivastava et al., 2015). Increases in the level of substrates by enhanced P uptake and increased photosynthetic efficiency have been described (Wright et al., 1998abKapoor et al., 2002abRasouli-Sadaghiani et al., 2010). The role of P is perceptible in the synthesis of terpenoids both via the MVA pathway, which requires acetyl-CoA, ATP and NADPH, and via the MEP pathway, requiring glyceraldehyde phosphate and pyruvate, of which P is a constituent. Photosynthesis provides ATP and carbon substrate (glyceraldehyde-3-phosphate or pyruvate) for isoprene synthesis. Increased foliar biomass in AM plants results in greater photosynthetic capacity and thus increased production of total photosynthates required for terpenoid biosynthesis (Niinemets et al., 2002Cao et al., 2008Hofmeyer et al., 2010). However, P nutrition alone fails to explain terpenoid accumulation in AM fungus-colonized plants (Copetta et al., 2006Khaosaad et al., 2006Rydlová et al., 2016). This is not unanticipated, assuming that the biosynthesis of isoprene precursors is regulated by complex mechanisms, some of them independent of P nutrition (Kirby and Keasling, 2009Vranova et al., 2012Kumari et al., 2013).

The enzyme 1-deoxy-d-xylulose 5-phosphate synthase (DXS) catalyses the rate-limiting step of the MEP pathway. Walter et al. (2000) first demonstrated fungal-induced upregulation of DXS and DXR (1-deoxy-D-xylulose 5-phosphate reductoisomerase) transcript levels in AM-colonized roots of various cereals. This was followed by a series of reports on the upregulation of DXS transcripts in mycorrhizal roots of various plants (Hans et al., 2004Strack and Fester, 2006Floß et al., 2008). Transcription of genes encoding DXS and DXR enzymes is upregulated by AM symbiosis and correlated with quantitative terpenoid concentration in leaves (Mandal et al., 2015a). This increase in transcription and terpenoid content has been ascribed to an increased concentration of the phytohormone jasmonic acid (Mandal et al., 2015aNair et al., 2015) and/or improved mineral nutrient availability (Mandal et al., 2015a), and may therefore be influenced by both nutritional and non-nutritional mechanisms (Mandal et al., 2013). Results obtained so far suggest that the AM fungal-mediated increase in concentrations of terpenoids is due to enhanced production of IPP/DMAPP derived from the MEP pathway (Mandal et al., 2015a). There were have been no reports of AM-mediated changes in the MVA pathway in the literature until recently, when Venkateshwaran et al. (2015) reported that mevalonic acid is crucial for the transduction of symbiotic signals produced by AM fungi to induce symbiotic gene expression in plants.

Arbuscular mycorrhiza influences the concentration of specific terpenoids and their derivatives in plants by upregulating the transcription of downstream genes of the dedicated biosynthesis pathway (Mandal et al., 2015ab). Induction of TPS family genes TPS31TPS32 and TPS33 in mycorrhizal tomato (Zouari et al., 2014) further suggests a probable mechanism underlying the change in terpenoid profile observed in AM plants.

Glandular trichomes are one of the most common secretory structures that produce and accumulate terpenoids in plants (Karban and Baldwin, 1997Van Schie et al., 2007Kang et al., 2010Schilmiller et al., 2010). A direct relation between augmented concentration of terpenoids and glandular trichome density has been observed in a number of plants (Ringer et al., 2005Bartram et al., 2006Behnam et al., 2006Muñoz-Bertomeu et al., 2006). Correspondingly, an increase in trichome density upon colonization by AM fungi has often been proposed to augment concentration of terpenoids (Copetta et al., 2006Kapoor et al., 2007Morone-Fortunato and Avato, 2008). It was demonstrated in Artemisia annua that AM enhances glandular trichomes by inducing the transcription of TTG1 (transparent testa glabra 1), a transcription factor that acts at the top of the regulatory hierarchy of trichome development (Mandal et al., 2015a). However, continued studies are required to elucidate the mechanisms of enhanced production of glandular trichomes and further ascertain the role of phytohormones in AM plants.

CONCLUSIONS AND FUTURE PROSPECTS

The volatile nature of terpenoids confers the ability to act as efficient signalling molecules. Potential deployment in pest management practices in agriculture depends upon the efficient control of emission (augmenting or repressing) in plants (Vickers et al., 2014). Genetic manipulation of plants for terpenoid emission is a promising method to alter tritrophic interactions. In recent years, transgenic plants producing terpenoids have been used to repel herbivores (Aharoni et al., 2003), deter oviposition (McCallum et al., 2011) and attract predators (Bouwmeester et al., 2003Kappers et al., 2005Beale et al., 2006) and parasitoids (Schnee et al., 2006). The physiological cost of terpenoid production has been assumed to be minor, given their low molecular weight and the relatively low concentrations emitted (Dicke and Sabelis, 1990Halitschke et al., 2000). on the other hand, a number of studies have demonstrated that constitutive transgenic production of terpenes can result in negative physiological effects on the plant (Aharoni et al., 2003Robert et al., 2013). These effects may be manifested as stunted growth, reduced reproductive yield and also enhanced conspicuousness and attractiveness of plants to pests (Robert et al., 2013). Furthermore, constitutive emission of HIPVs by transgenic plants would render these emissions unreliable as cues for natural enemies that might waste hunting time in prey-free environments (Gish et al., 2015). Therefore, synchronized engineering strategies that consider herbivore-induced emissions are required to circumvent these cost effects. Further studies are required to evaluate the physiological and ecological costs of terpenoid manipulation in the field to determine the future of this approach for environmental pest management strategies (Robert et al., 2013).

Engineering of tritrophic interactions to successfully protect crop species requires consideration of a number of aspects (Bouwmeester et al., 2003Degenhardt et al., 2003). For example, identification of an appropriate carnivore species for effective control of herbivore populations is required – one that is naturally present in the cultivation area and attracted by manipulating a known terpenoid (Vickers et al., 2014). Engineered emissions, however, should not attract other herbivores. The overall benefit of manipulated terpenoid emissions can be significantly enhanced by making the release inducible, by inserting a herbivore-inducible tissue-specific promoter with the terpene synthase gene (Degenhardt et al., 2009). Such controlled release would prevent the attraction of herbivores by healthy plants and would lead to recruitment of natural enemies only when the plant is attacked by herbivores (Robert et al., 2013). The lack of understanding of mechanisms by which plants recognize and respond to olfactory cues restricts the prospects for the utilization of terpenoids in crop plants. The highly simplified community structure of large-scale agricultural plantings is another challenge for the effective application of HIPVs, as natural enemy attraction may be ineffective in controlling pests in the core regions of large agricultural fields (Gish et al., 2015).

Alteration of the terpenoid profile in AM plants appears to be one of the important mechanisms for augmented defence against herbivorous insects. Different AM fungal species have variable effects on terpenoid blends (Kapoor et al., 2002bSailo and Bagyaraj, 2005Arpana et al., 2008), and consequently likely differentially influence plant–herbivore and higher trophic level interactions. In this context, comparative studies using different AM fungal species are warranted, to enable differentiation of universal from species-specific responses, and also to identify those AM fungal species efficient in defence against specific herbivores. As the efficiency of AM symbiosis may be limited by nutrient availability in agricultural fields, comprehensive studies are also required to evaluate the relevance of AM symbiosis to herbivore defence under different nutrient regimes.

ACKNOWLEDGEMENTS

We are grateful to Professor R. Geeta, Professor Rajesh Tandon and Professor Sudheshna Mazumdar-Leighton for critically reviewing the manuscript and for their valuable comments. We thank the Research Council of the University of Delhi, Delhi, India, for financial assistance.

LITERATURE CITED

Aharoni
 
A
Giri
 
AP
Deuerlein
 
S
, et al.  . 
2003
Terpenoid metabolism in wild-type and transgenic Arabidopsis plants
The Plant Cell
  
15
2866
2884
.
Aharoni
 
A
Jongsma
 
MA
Bouwmeester
 
HJ.
 
2005
Volatile science? Metabolic engineering of terpenoids in plants
Trends in Plant Science
  
10
594
602
.
Akiyama
 
K.
 
2007
Chemical identification and functional analysis of apocarotenoids involved in the development of arbuscular mycorrhizal symbiosis
Bioscience, Biotechnology, and Biochemistry
  
71
1405
1414
.
Akiyama
 
K
Hayashi
 
H.
 
2002
Arbuscular mycorrhizal fungus promoted accumulation of two new triterpenoids in cucumber roots
Bioscience, Biotechnology, and Biochemistry
  
66
762
769
.
Ali
 
JG
Alborn
 
HT
Campos-Herrera
 
R
, et al.  . 
2011
Subterranean, herbivore induced plant volatile increases biological control activity of multiple beneficial nematode species in distinct habitats
PLoS one
  
7
1
6
.
Ali
 
M
Sugimoto
 
K
Ramadan
 
A
Arimura
 
G.
 
2013
Memory of plant communications for priming anti-herbivore responses
Scientific Reports
  
3
1872
.
Arimura
 
G
Ozawa
 
R
Shimoda
 
T
Nishioka
 
T
Boland
 
W
Takabayashi
 
J.
 
2000a
Herbivory-induced volatiles elicit defence genes in lima bean leaves
Nature
  
406
512
515
.
Arimura
 
G
Tashiro
 
K
Kuhara
 
S
Nishioka
 
T
Ozawa
 
R
Takabayashi
 
J
2000b
Gene responses in bean leaves induced by herbivory and by herbivore-induced volatiles
Biochemical and Biophysical Research Communications
  
277
305
310
.
Arimura
 
G
Garms
 
S
MaVei
 
M
, et al.  . 
2008
Herbivore-induced terpenoid emission in Medicago truncatula: concerted action of jasmonate, ethylene and calcium signalling
Planta
  
227
453
464
.
Arimura
 
G
Matsui
 
K
Takabayashi
 
J.
 
2009
Chemical and molecular ecology of herbivore-induced plant volatiles: proximate factors and their ultimate functions
Plant Cell Physiology
  
50
911
923
.
Arpana
 
J
Bagyaraj
 
DJ
Prakasa Rao
 
EVS
Parameswaran
 
TN
Abdul Rahiman
 
BA.
 
2008
Symbiotic response of patchouli [Pogostemon cablin (Blanco) Benth.] to different arbuscular mycorrhizal fungi
Advances in Environmental Biology
  
2
20
24
.
Babikova
 
Z
Gilbert
 
L
Bruce
 
TJA
, et al.  . 
2013
Underground signals carried through common mycelial networks warn neighbouring plants of aphid attack
Ecology Letters
  
16
835
843
.
Babikova
 
Z
Gilbert
 
L
Randall
 
KC
Bruce
 
TJA
Pickett
 
JA
Johnson
 
D.
 
2014a
Increasing phosphorus supply is not the mechanism by which arbuscular mycorrhiza increase attractiveness of bean (Vicia faba) to aphids
Journal of Experimental Botany
  
65
5231
5241
.
Babikova
 
Z
Gilbert
 
L
Bruce
 
TJA
Dewhirst
 
S
Pickett
 
JA
Johnson
 
D.
 
2014b
Arbuscular mycorrhizal fungi and aphids interact by changing host plant quality and volatile emission
Functional Ecology
  
28
375
385
.
Baldwin
 
IT
Schultz
 
JC.
 
1983
Rapid changes in tree leaf chemistry induced by damage: evidence for communication between plants
Science
  
221
277
279
.
Baldwin
 
IT
Halitschke
 
R
Paschold
 
A
von Dahl
 
CC
Preston
 
CA.
 
2006
Volatile signaling in plant-plant interactions: “talking trees” in the genomics era
Science
  
311
812
815
.
Bartram
 
S
Jux
 
A
Gleixner
 
G
Boland
 
W.
 
2006
Dynamic pathway allocation in early terpenoid biosynthesis of stress-induced lima bean leaves
Phytochemistry
  
67
1661
1672
.
Beale
 
MH
Birkett
 
MA
Bruce
 
TJ
, et al.  . 
2006
Aphid alarm pheromone produced by transgenic plants affects aphid and parasitoid behavior
Proceedings of the National Academy of Sciences of the USA
  
103
10509
10513
.
Behnam
 
S
Farzaneh
 
M
Ahmadzadeh
 
M
Tehrani
 
AS.
 
2006
Composition and antifungal activity of essential oils of Mentha piperita and Lavendula angustifolia on post-harvest phytopathogens
Communications in Agriculture and Applied Biological Sciences
  
71
1321
1326
.
Bennett
 
AE
Bever
 
JD.
 
2007
Mycorrhizal species differentially alter plant growth and response to herbivory
Ecology
  
88
210
218
.
Beyaert
 
I
Köpke
 
D
Stiller
 
J
Hammerbacher
 
A
, et al.  . 
2012
Can insect egg deposition ‘warn’ a plant of future feeding damage by herbivorous larvae?
 
Proceedings of the Royal Society, B
  
279
101
108
.
Bick
 
JA
Lange
 
BM.
 
2003
Metabolic cross talk between cytosolic and plastidial pathways of isoprenoid biosynthesis: unidirectional transport of intermediates across the chloroplast envelope membrane
Archives of Biochemistry and Biophysics
  
415
146
154
.
Blande
 
JD
Holopainen
 
JK
Li
 
T.
 
2010
Air pollution impedes plant-to-plant communication by volatiles
Ecology Letters
  
13
1172
1181
.
De Boer
 
JG
Posthumus
 
MA
Dicke
 
M.
 
2004
Identification of volatiles that are used in discrimination between plants infested with prey or non-prey herbivores by a predatory mite
Journal of Chemical Ecology
  
30
2215
2230
.
Borowicz
 
VA.
 
2013
The impact of arbuscular mycorrhizal fungi on plant growth following herbivory: a search for pattern
Acta Oecologica
  
52
1
9
.
Bouwmeester
 
HJ
Kappers
 
IF
Verstappen
 
FW
, et al.  . 
2003
. Exploring multi-trophic plant–herbivore interactions for new crop protection methods. In: 
Pickett
 
J
, ed. 
Proceedings of the BCPC International Congress: Crop Science and Technology
 . 
Alton
British Crop Protection Council
1123
1134
.
Broughton
 
S
Harrison
 
J.
 
2012
Evaluation of monitoring methods for thrips and the effect of trap colour and semiochemicals on sticky trap capture of thrips (Thysanoptera) and beneficial insects (Syrphidae, Hemerobiidae) in deciduous fruit trees in Western Australia
Crop Protection
  
42
156
163
.
Brunetti
 
C
George
 
RM
Tattini
 
M
Field
 
K
Davely
 
MP.
 
2013
Metabolics in plant environmental physiology
Journal of Experimental Botany
  
64
4011
4020
.
Büchel
 
KK
Malskies
 
S
Mayer
 
M
, et al.  . 
2011
How plants give early herbivore alert: volatile terpenoids emitted from elm attract egg parasitoids to plants laden with eggs of the elm leaf beetle
Basic and Applied Ecology
  
12
403
412
.
Cao
 
B
Dang
 
QL
 
X
Zhang
 
S.
 
2008
Effects of [CO2] and nitrogen on morphological and biomass traits of white birch (Betula papyrifera) seedlings
Forest Ecology Management
  
254
217
224
.
Chen
 
F
Tholl
 
D
Bohlmann
 
J
Pichersky
 
E.
 
2011
The family of terpene synthases in plants: a mid-size family of genes for specialized metabolism that is highly diversified throughout the kingdom
The Plant Journal
  
66
212
229
.
Cheng
 
AX
Lou
 
YG
Mao
 
YB
Lu
 
S
Wang
 
LJ
Chen
 
XY.
 
2007a
Plant terpenoids: biosynthesis and ecological functions
Journal of Integrative Plant Biology
  
49
179
186
.
Cheng
 
AX
Xiang
 
CY
Li
 
JX
, et al.  . 
2007b
The rice (E)-β-caryophyllene synthase (OsTPS3) accounts for the major inducible volatile sesquiterpenes
Phytochemistry
  
68
1632
1641
.
Conrath
 
U
Beckers
 
GJM
Flors
 
V
, et al.  . 
2006
Priming: getting ready for battle
Molecular Plant-Microbe Interactions
  
19
1062
1071
.
Conti
 
E
Zadra
 
C
Salerno
 
G
, et al.  . 
2008
Changes in the volatile profile of Brassica oleracea due to feeding and oviposition by Murgantia histrionica (Heteroptera: Pentatomidae)
European Journal of Entomology
  
105
839
847
.
Copetta
 
A
Lingua
 
G
Berta
 
G.
 
2006
Effects of three AM fungi on growth, distribution of glandular hairs, and essential oil production in Ocimum basilicum L. Var. Genovese
Mycorrhiza
  
16
485
494
.
Das
 
A
Lee
 
SH
Hyun
 
TK
Kim
 
SW
Kim
 
JY.
 
2013
Plant volatiles as method of communication
Plant Biotechnology Reports
  
7
9
26
.
Degenhardt
 
J
Gershenzon
 
J
Baldwin
 
IT
Kessler
 
A.
 
2003
Attracting friends to feast on foes: engineering terpene emission to make crop plants more attractive to herbivore enemies
Current Opinion in Biotechnology
  
14
169
176
.
Degenhardt
 
J
Hiltpold
 
I
Köllner
 
TG
, et al.  . 
2009
Restoring a maize root signal that attracts insect-killing nematodes to control a major pest
Proceedings of the National Academy of Sciences of the USA
  
106
13213
13218
.
Delory
 
BM
Delaplace
 
P
Fauconnier
 
ML
du Jardin
 
P.
 
2016
Root-emitted volatile organic compounds: can they mediate belowground plant-plant interactions?
 
Plant and Soil
  
402
1
26
, in press. doi:10.1007/s11104-016-2823-3.
Dicke
 
M
Sabelis
 
MW.
 
1990
. Does it pay plants to advertize for bodyguards? Towards a cost-benefit analysis of induced synomone production. In: 
Lambers
 
H
Cambridge
 
ML
Konings
 
H
Pons
 
TL
, eds. 
Causes and consequences of variation in growth rate and productivity of higher plants
 . 
The Hague
SPB Academic Publishing
341
358
.
Dicke
 
M
Vanbeek
 
TA
Posthumus
 
MA
, et al.  . 
1990
Isolation and identification of volatile kairomone that affects acarine predator-prey interactions – involvement of host plant in its production
Journal of Chemical Ecology
  
16
381
396
.
Dicke
 
M
Gols
 
R
Ludeking
 
D
Posthumus
 
MA.
 
1999
Jasmonic acid and herbivory differentially induce carnivore-attracting plant volatiles in lima bean plants
Journal of Chemical Ecology
  
25
1907
1922
.
Dicke
 
M
van Loon
 
JJA
Soler
 
R.
 
2009
Chemical complexity of volatiles from plants induced by multiple attack
Nature
  
5
317
324
.
Dudareva
 
N
Negre
 
F
Nagegowda
 
DA
Orlova
 
I.
 
2006
Plant volatiles: recent advances and future perspectives
Critical Reviews in Plant Sciences
  
25
417
440
.
Dudareva
 
N
Klempien
 
A
Muhlemann
 
K
Kaplan
 
I.
 
2013
Biosynthesis, function and metabolic engineering of plant volatile organic compounds
New Phytologist
  
198
16
32
.
Engelberth
 
J
Alborn
 
HT
Schmelz
 
EA
Tumlinson
 
JH.
 
2004
Airborne signals prime plants against insect herbivore attack
Proceedings of the National Academy of Sciences of the USA
  
10
1781
1785
.
Erb
 
M
Ton
 
J
Degenhardt
 
J
Turlings
 
TC.
 
2008
Interactions between arthropod-induced aboveground and belowground defenses in plants
Plant Physiology
  
146
867
874
.
Erb
 
M
Veyrat
 
N
Robert
 
CAM
, et al.  . 
2015
Indole is an essential herbivore-induced volatile priming signal in maize
Nature Communications
  
6
6273
.
Evelin
 
H
Giri
 
B
Kapoor
 
R.
 
2013
Ultrastructural evidence for AMF mediated salt stress mitigation in Trigonella foenum-graecum
Mycorrhiza
  
23
71
86
.
Farag
 
MA
Paré
 
PW.
 
2002
C-6-green leaf volatiles trigger local and systemic VOC emissions in tomato
Phytochemistry
  
61
545
554
.
Fester
 
T
Schmidt
 
D
Lohse
 
S
, et al.  . 
2002
Stimulation of carotenoid metabolism in arbuscular mycorrhizal roots
Planta
  
216
148
154
.
Finlay
 
RD.
 
2008
Ecological aspects of mycorrhizal symbiosis: with special emphasis on the functional diversity of interactions involving the extraradical mycelium
Journal of Experimental Botany
  
59
1115
1126
.
Floβ
 
DS
Hause
 
B
Lange
 
PR
Küster
 
H
Strack
 
D
Walter
 
MH.
 
2008
Knock-down of the MEP pathway isogene 1-deoxy-d-xylulose 5-phosphate synthase 2 inhibits formation of arbuscular mycorrhiza-induced apocarotenoids, and abolishes normal expression of mycorrhiza-specific plant marker genes
The Plant Journal
  
56
86
100
.
Frost
 
CJ
Appel
 
HM
Carlson
 
JE
De Moraes
 
CM
Mescher
 
MC
Schultz
 
JC.
 
2007
Within-plant signalling by volatiles overcomes vascular constraints on systemic signalling and primes responses against herbivores
Ecology Letters
  
10
490
498
.
Frost
 
CJ
Mescher
 
MC
Dervinis
 
C
Davis
 
JM
Carlson
 
JE
De Moraes
 
CM.
 
2008a
Priming defense genes and metabolites in hybrid poplar by the green leaf volatile cis‐3‐hexenylacetate
New Phytologist
  
180
722
734
.
Frost
 
CJ
Mescher
 
MC
Carlson
 
JE
De Moraes
 
CM.
 
2008b
Plant defense priming against herbivores: getting ready for a different battle
Plant Physiology
  
146
818
824
.
Gange
 
AC.
 
2007
. Insect-mycorrhizal interactions: patterns, processes and consequences. In: 
Oghushi
 
T
Craig
 
TP
Price
 
PW
, eds. 
Ecological communities: plant mediation in indirect interactions
 . 
Cambridge
Cambridge University Press
124
144
.
Gange
 
AC
West
 
HM.
 
1994
Interactions between arbuscular mycorrhizal fungi and foliar-feeding insects in Plantago lanceolata L
New Phytologist
  
128
79
87
.
Gange
 
AC
Bower
 
E
Brown
 
VK.
 
1999
Positive effects of an arbuscular mycorrhizal fungus on aphid life history traits
Oecologia
  
120
123
131
.
Gange
 
AC
Brown
 
VK
Aplin
 
MA.
 
2003
Multitrophic links between arbuscular mycorrhizal fungi and insect parasitoids
Ecology Letters
  
6
1051
1055
.
Gehring
 
C
Bennett
 
A.
 
2009
Mycorrhizal fungal–plant–insect interactions: the importance of a community approach
Environmental Entomology
  
38
93
102
.
Gershenzon
 
J.
 
1994
Metabolic costs of terpenoid accumulation in higher plants
Journal of Chemical Ecology
  
20
1281
1328
.
Gershenzon
 
J
Dudareva
 
N.
 
2007
The function of terpene natural products in the natural world
Nature Chemical Biology
  
3
408
414
.
Gish
 
M
De Moraes
 
CM
Mescher
 
MC.
 
2015
Herbivore-induced plant volatiles in natural and agricultural ecosystems: open questions and future prospects
Current Opinion in Insect Science
  
9
1
6
.
Gouinguené
 
SP
Turlings
 
TCJ.
 
2002
The effects of abiotic factors on induced volatile emissions in corn plants
Plant Physiology
  
129
1296
1307
.
Guerrieri
 
E
Lingua
 
G
Digilio
 
MC
Massa
 
N
Berta
 
G.
 
2004
Do interactions between plant roots and the rhizosphere affect parasitoid behaviour?
 
Ecological Entomology
  
29
753
756
.
Halitschke
 
R
Keßler
 
A
Kahl
 
J
Lorenz
 
A
Baldwin
 
IT.
 
2000
Ecophysiological comparison of direct and indirect defenses in Nicotiana attenuata
Oecologia
  
124
408
417
.
Hans
 
J
Hause
 
B
Strack
 
D
Walter
 
MH.
 
2004
Cloning, characterization, and immunolocalization of a mycorrhiza-inducible 1-deoxy-d-xylulose 5-phosphate reductoisomerase in arbuscule-containing cells of maize
Plant Physiology
  
134
614
624
.
Harrison
 
MJ.
 
2005
Signaling in the arbuscular mycorrhizal symbiosis
Annual Review of Microbiology
  
59
19
42
.
Heil
 
M.
 
2008
Indirect defence via tritrophic interactions
New Phytologist
  
178
41
61
.
Heil
 
M
Kost
 
C.
 
2006
Priming of indirect defences
Ecology Letters
  
9
813
817
.
Heil
 
M
Silva Bueno
 
JC.
 
2007
Within-plant signaling by volatiles leads to induction and priming of an indirect plant defense in nature
Proceedings of the National Academy of Sciences of the USA
  
104
5467
5472
.
Heil
 
M
Ton
 
J.
 
2008
Long-distance signalling in plant defence
Trends in Plant Science
  
13
264
272
.
Hilker
 
M
Fatouros
 
NE.
 
2015
Plant responses to insect egg deposition
Annual Review of Entomology
  
60
493
515
.
Hilker
 
M
Kobs
 
C
Varama
 
M
Schrank
 
K.
 
2002
Insect egg deposition induces Pinus sylvestris to attract egg parasitoids
Journal of Experimental Biology
  
205
455
461
.
Hiltpold
 
I
Turlings
 
TCJ.
 
2008
Belowground chemical signaling in maize: when simplicity rhymes with efficiency
Journal of Chemical Ecology
  
34
628
635
.
Hoffmann
 
D
Vierheilig
 
H
Riegler
 
P
Schausberger
 
P.
 
2009
Arbuscular mycorrhizal symbiosis increases host plant acceptance and population growth rates of the two-spotted spider mite Tetranychus urticae
Oecologia
  
158
663
 
671
.
Hofmeyer
 
PV
Seymour
 
RS
Kenefic
 
LS.
 
2010
Production ecology of Thuja occidentalis
Canadian Journal of Forest Research
  
40
1155
1164
.
Hohnjec
 
N
Vieweg
 
MF
Pühler
 
A
Becker
 
A
Küster
 
H.
 
2005
Overlaps in the transcriptional profiles of Medicago truncatularoots inoculated with two different glomus fungi provide insights into the genetic program activated during arbuscular mycorrhiza
Plant Physiology
  
137
1283
1301
.
Jung
 
SC
Martinez-Medina
 
A
Lopez-Raez
 
JA
Pozo
 
MJ.
 
2012
Mycorrhiza-induced resistance and priming of plant defenses
Journal of Chemical Ecology
  
38
651
664
.
Kang
 
JH
Shi
 
F
Jones
 
AD
Marks
 
MD
Howe
 
GA.
 
2010
Distortion of trichome morphology by the hairless mutation of tomato affects leaf surface chemistry
Journal of Experimental Botany
  
61
1053
1064
.
Kant
 
MR
Ament
 
K
Sabelis
 
MW
Haring
 
MA
Schuurink
 
RC.
 
2004
Differential timing of spider mite-induced direct and indirect defenses in tomato plants
Plant Physiology
  
135
483
495
.
Kappers
 
IF
Aharoni
 
A
Van Herpen
 
TWJM
Luckerhoff
 
LLP
Dicke
 
M
Bouwmeester
 
HJ.
 
2005
Genetic engineering of terpenoid metabolism attracts, bodyguards to Arabidopsis
Science
  
309
2070
2072
.
Kapoor
 
R
Giri
 
B
Mukerji
 
KG.
 
2002a
Glomus macrocarpum: a potential bioinoculant to improve essential oil quality and concentration in dill (Anethum graveolens L.) and carum (Trachyspermum ammi (Linn.) Sprague)
World Journal of Microbiology and Biotechnology
  
18
459
463
.
Kapoor
 
R
Giri
 
B
Mukerji
 
KG.
 
2002b
Mycorrhization of coriander (Coriandrum sativum L.) to enhance the concentration and quality of essential oil
Journal of the Science Food and Agriculture
  
88
1
4
.
Kapoor
 
R
Chaudhary
 
V
Bhatnagar
 
AK.
 
2007
Effects of arbuscular mycorrhiza and phosphorus application on artemisinin concentration in Artemisia annua L
Mycorrhiza
  
17
581
587
.
Karban
 
R
Baldwin
 
IT.
 
1997
Induced responses to herbivory
 . 
Chicago
University of Chicago Press
.
Karban
 
R
Maron
 
J.
 
2002
The fitness consequences of interspecific eavesdropping between plants
Ecology
  
83
1209
1213
.
Karban
 
R
Baldwin
 
IT
Baxter
 
KJ
Laue
 
G
Felton
 
GW.
 
2000
Communication between plants: induced resistance in wild tobacco plants following clipping of neighboring sagebrush
Oecologia
  
125
66
71
.
Karban
 
R
Shiojiri
 
K
Huntzinger
 
M
McCall
 
AC.
 
2006
Damage-induced resistance in sagebrush: volatiles are key to intra- and interplant communication
Ecology
  
87
922
930
.
Kessler
 
A
Baldwin
 
IT.
 
2001
Defensive function of herbivore induced plant volatile emissions in nature
Science
  
291
2141
2144
.
Khaosaad
 
T
Vierheilig
 
H
Nell
 
M
Zitterl-Eglseer
 
K
Novak
 
J.
 
2006
Arbuscular mycorrhiza alter the concentration of essential oils in oregano (Origanum sp., Lamiaceae)
Mycorrhiza
  
6
443
446
.
Kirby
 
J
Keasling
 
JD.
 
2009
Biosynthesis of plant isoprenoids: perspectives for microbial engineering
Annual Review of Plant Biology
  
60
335
355
.
Klingner
 
A
Bothe
 
H
Wray
 
V
Marner
 
FJ.
 
1995
Identification of a yellow pigment formed in maize roots upon mycorrhizal colonization
Phytochemistry
  
38
53
55
.
Köpke
 
D
Beyaert
 
I
Gershenzon
 
J
Hilker
 
M
Schmidt
 
A.
 
2010
Species-specific responses of pine sesquiterpene synthases to sawfly oviposition
Phytochemistry
  
71
909
917
.
Koricheva
 
J
Gange
 
AC
Jones
 
T.
 
2009
Effects of mycorrhizal fungi on insect herbivores: a meta-analysis
Ecology
  
90
2088
2097
.
Kost
 
C
Heil
 
M.
 
2006
Herbivore-induced plant volatiles induce an indirect defence in neighbouring plants
Journal of Ecology
  
94
619
628
.
Kumari
 
S
Priya
 
P
Misra
 
G
Yadav
 
G.
 
2013
Structural and biochemical perspectives in plant isoprenoid biosynthesis
Phytochemistry Reviews
  
12
255
291
.
Langenheim
 
JH.
 
1994
Higher plant terpenoids: a phytocentric overview of their ecological roles
Journal of Chemical Ecology
  
20
1223
1280
.
Laird
 
RA
Addicott
 
JF.
 
2007
Arbuscular mycorrhizal fungi reduce the construction of extrafloral nectaries in Vicia faba
Oecologia
  
152
541
551
.
Laothawornkitkul
 
J
Paul
 
ND
Vickers
 
CE
, et al.  . 
2008
Isoprene emissions influence herbivore-feeding decisions
Plant, Cell & Environment
  
31
1410
1415
.
Leitner
 
M
Boland
 
W
Mithöfer
 
A.
 
2005
Direct and indirect defences induced by piercing-sucking and chewing herbivores in Medicago truncatula
New Phytologist
  
167
597
606
.
Leitner
 
M
Kaiser
 
R
Hause
 
B
Boland
 
W
Mithöfer
 
A.
 
2010
Does mycorrhization influence herbivore-induced volatile emission in Medicago truncatula?
 
Mycorrhiza
  
20
89
101
.
Loreto
 
F
Schnitzler
 
JP.
 
2010
Abiotic stresses and induced BVOCs
Trends in Plant Science
  
15
154
166
.
Maffei
 
ME.
 
2010
Sites of synthesis, biochemistry and functional role of plant volatiles
South African Journal of Botany
  
76
612
631
.
Mandal
 
S
Evelin
 
H
Giri
 
B
Singh
 
VP
Kapoor
 
R.
 
2013
Arbuscular mycorrhiza enhances the production of stevioside and rebaudioside-A in Stevia rebaudiana via nutritional and non-nutritional mechanisms
Applied Soil Ecology
  
72
187
194
.
Mandal
 
S
Upadhyay
 
S
Wajid
 
S
, et al.  . 
2015a
Arbuscular mycorrhiza increase artemisinin accumulation in Artemisia annuaby higher expression of key biosynthesis genes via enhanced jasmonic acid levels
Mycorrhiza
  
25
345
357
.
Mandal
 
S
Upadhyay
 
S
Singh
 
VP
Kapoor
 
R.
 
2015b
Enhanced production of steviol glycosides in mycorrhizal plants: a concerted effect of arbuscular mycorrhizal symbiosis on transcription of biosynthetic genes
Plant Physiology and Biochemistry
  
89
:
100
106
.
Mathur
 
V
Tytgat
 
TOG
Hordijk
 
CA
, et al.  . 
2013
An ecogenomic analysis of herbivore-induced plant volatiles in Brassica juncea
Molecular Ecology
  
22
6179
6196
.
McCallum
 
EJ
Cunningham
 
JP
Lücker
 
J
Zalucki
 
MP
De Voss
 
JJ
Botella
 
JR.
 
2011
Increased plant volatile production affects oviposition, but not larval development, in the moth Helicoverpa armigera
Journal of Experimental Biology
  
214
3672
3677
.
Meixner
 
C
Ludwig-Muller
 
J
Miersch
 
O
Gresshoff
 
P
Staehelin
 
C
Vierheilig
 
H.
 
2005
Lack of mycorrhizal autoregulation and phytohormonal changes in the super nodulating soybean mutants nts1007
Planta
  
222
709
715
.
Mercke
 
P
Kappers
 
IF
Francel
 
WAV
Oscar
 
V
Marcel
 
D
Harro
 
JB.
 
2004
Combined transcript and metabolite analysis reveals genes involved in spider mite induced volatile formation in cucumber plants
Plant Physiology
  
135
2012
2024
.
Miller
 
MH
McGonigle
 
TP
Addy
 
HD.
 
1995
Functional ecology of vesicular arbuscular mycorrhizas as influenced by phosphate fertilization and tillage in an agricultural ecosystem
Critical Reviews in Biotechnology
  
15
241
255
.
Miransari
 
M.
 
2010
Contribution of arbuscular mycorrhizal symbiosis to plant growth under different types of soil stress
Plant Biology
  
12
563
569
.
Mithöfer
 
A
Boland
 
W.
 
2012
Plant defense against herbivores: chemical aspects
Annual Review of Plant Biology
  
63
431
450
.
Morone-Fortunato
 
I
Avato
 
P.
 
2008
Plant development and synthesis of essential oils in micropropagated and mycorrhiza inoculated plants of Origanum vulgare L. ssp. hirtum (Link) Ietswaart
Plant Cell Tissue and Organ Culture
  
93
139
.
Mumm
 
R
Hilker
 
M.
 
2005
The significance of background odour for an egg parasitoid to detect plants with host eggs
Chemical Senses
  
30
337
343
.
Mumm
 
R
Hilker
 
M.
 
2006
Direct and indirect chemical defence of pine against folivorous insects
Trends in Plant Science
  
11
351
358
.
Mumm
 
R
Posthumus
 
MA
Dicke
 
M.
 
2008
Significance of terpenoids in induced indirect plant defence against herbivorous arthropods
Plant, Cell & Environment
  
31
575
585
.
Muñoz-Bertomeu
 
J
Arrillaga
 
I
Ros
 
R
Segura
 
J.
 
2006
Up-regulation of 1-deoxy-d-xylulose-5-phosphate synthase enhances production of essential oils in transgenic spike lavender
Plant Physiology
  
142
890
900
.
Muroi
 
A
Ramadan
 
A
Nishihara
 
M.
 
2011
The composite effect of transgenic plant volatiles for acquired immunity to herbivory caused by inter-plant communications
PLoS one
  
6
e24594
.
Nair
 
A
Kolet
 
SP
Thulasiram
 
HV
Bhargava
 
S.
 
2015
Systemic jasmonic acid modulation in mycorrhizal tomato plants and its role in induced resistance against Alternaria alternata
Plant Biology
  
17
625
631
.
Niinemets
 
Ü
Seufert
 
G
Steinbrecher
 
R
Tenhunen
 
JD.
 
2002
A model coupling foliar monoterpene emissions to leaf photosynthetic characteristics in Mediterranean Quercus species
New Phytologist
  
153
257
275
.
Owen
 
S
Peñuelas
 
J.
 
2005
Opportunistic emissions of volatile isoprenoids
Trends in Plant Science
  
10
420
426
.
Palma
 
R
Mutis
 
A
Manosalva
 
L
, et al.  . 
2012
Behavioral and electrophysiological responses of Hylastinus obscurus to volatiles released from the roots of Trifolium pratense L
Journal of Soil Science and Plant Nutrition
  
12
183
193
.
Paré
 
PW
Tumlinson
 
JH.
 
1999
Plant volatiles as a defense against insect herbivores
Plant Physiology
  
121
325
332
.
Park
 
SW
Kaimoyo
 
E
Kumar
 
D
Mosher
 
S
Klessig
 
DF.
 
2007
Methyl salicylate is a critical mobile signal for plant systemic acquired resistance
Science
  
318
113
116
.
Parniske
 
M.
 
2008
Arbuscular mycorrhiza: the mother of plant root endosymbioses
Nature Reviews. Microbiology
  
6
763
775
.
Paschold
 
A
Halitschke
 
R
Baldwin
 
IT.
 
2006
Using ‘mute’ plants to translate volatile signals
The Plant Journal
  
45
275
291
.
Pashalidou
 
FG
Gols
 
R
Berkhout
 
BW
, et al.  . 
2015
To be in time: egg deposition enhances plant-mediated detection of young caterpillars by parasitoids
Oecologia
  
177
477
486
.
Peñuelas
 
J
Munné-Bosch
 
S.
 
2005
Isoprenoids: an evolutionary pool for photoprotection
Trends in Plant Science
  
10
166
169
.
Peñuelas
 
J
Asensio
 
D
Tholl
 
D
, et al.  . 
2014
Biogenic volatile emissions from the soil
Plant, Cell & Environment
  
37
1866
1891
.
Pichersky
 
E
Noel
 
JP
Dudareva
 
N.
 
2006
Biosynthesis of plant volatiles: nature's diversity and ingenuity
Science
  
311
808
811
.
Piel
 
J
Donath
 
J
Bandemer
 
K
Boland
 
W.
 
1998
Mevalonate-independent biosynthesis of terpenoid volatiles in plants: induced and constitutive emission of volatiles
Angewandte Chemie, International Edition
  
37
2478
2481
.
Pineda
 
A
Zheng
 
SJ
van Loon
 
JJA
Pieterse
 
CMJ
Dicke
 
M.
 
2010
Helping plants to deal with insects: the role of beneficial soil-borne microbes
Trends in Plant Science
  
15
507
514
.
Pozo
 
MJ
Azcón-Aguilar
 
C.
 
2007
Unraveling mycorrhiza-induced resistance
Current Opinion in Plant Biology
  
10
393
398
.
Puente
 
ME
Kennedy
 
GG
Gould
 
F.
 
2008
The impact of herbivore-induced plant volatiles on parasitoid foraging success: a general deterministic model
Journal of Chemical Ecology
  
34
945
958
.
Ramadan
 
A
Muroi
 
A
Arimura
 
G.
 
2011
Herbivore-induced maize volatiles serve as priming cues for resistance against post-attack by the specialist armyworm Mythimna separata
Journal of Plant Interactions
  
6
155
158
.
Rapparini
 
F
Llusia
 
J
Peñuelas
 
J.
 
2008
Effect of arbuscular mycorrhizal (AM) colonization on terpene emission and content of Artemisia annua L
Plant Biology
  
10
108
122
.
Rasmann
 
S
Turlings
 
TC.
 
2007
Simultaneous feeding by aboveground and belowground herbivores attenuates plant-mediated attraction of their respective natural enemies
Ecology Letters
  
10
926
936
.
Rasmann
 
S
Turlings
 
TC.
 
2008
First insights into specificity of below ground tritrophic interactions
Oikos
  
117
362
369
.
Rasmann
 
S
Köllner
 
TG
Degenhardt
 
J
, et al.  . 
2005
Recruitment of entomopathogenic nematodes by insect-damaged maize roots
Nature
  
434
732
737
.
Rasmann
 
S
Hiltpold
 
I
Ali
 
J.
 
2012
. The role of root-produced volatile secondary metabolites in mediating soil interactions. In: 
Montanaro
 
G
Bartolomeo
 
D
, eds. 
Advances in selected plant physiology aspects
 . 
Rijeka
InTech
269
290
.
Rasouli-Sadaghiani
 
MH
Hassani
 
A
Barin
 
M
Danesh
 
YR
Sefidkon
 
F.
 
2010
Effects of arbuscular mycorrhizal (AM) fungi on growth, essential oil production and nutrients uptake in basil
Journal of Medicinal Plants Research
  
4
2222
2228
.
Ringer
 
KL
Davis
 
EM
Croteau
 
R.
 
2005
Monoterpene metabolism. Cloning, expression, and characterization of (−)-isopiperitenol/(−)-carveol dehydrogenase of peppermint and spearmint
Plant Physiology
  
137
863
872
.
Robert
 
CAM
Veyrat
 
N
Glauser
 
G
, et al.  . 
2012
A specialist root herbivore exploits defensive metabolites to locate nutritious tissues
Ecology Letters
  
15
55
64
.
Robert
 
CAM
Erb
 
M
Hiltpoldt
 
I
, et al.  . 
2013
Genetically engineered maize plants reveal distinct costs and benefits of constitutive volatile emissions in the field
Plant Biotechnology Journal
  
11
628
639
.
Rodríguez-Concepcion
 
M.
 
2006
Early steps in isoprenoid biosynthesis: multilevel regulation of the supply of common precursors in plant cells
Phytochemistry Reviews
  
5
1
15
.
Ruiz-Lozano
 
JM
Porcel
 
R
Azcón
 
C
Aroca
 
R.
 
2012
Regulation by arbuscular mycorrhizae of the integrated physiological response to salinity in plants: new challenges in physiological and molecular studies
Journal of Experimental Botany
  
63
4033
4044
.
Ruther
 
J
Fürstenau
 
B.
 
2005
Emission of herbivore-induced volatiles in absence of a herbivore – response of Zea mays to green leaf volatiles and terpenoids
Zeitschrift für Naturforschung C
  
60
743
756
.
Ruther
 
J
Kleier
 
S.
 
2005
Plant-plant signaling: ethylene synergizes volatile emission in Zea mays induced by exposure to (Z)-3-hexen-1-ol
Journal of Chemical Ecology
  
31
2217
2222
.
Rydlová
 
J
Jelínková
 
M
Karel Dušek
 
K
Dušková
 
E
Miroslav Vosátka
 
M
Püschel
 
D.
 
2016
Arbuscular mycorrhiza differentially affects synthesis of essential oils in coriander and dill
Mycorrhiza
  
26
:
123
131
.
Sailo
 
GL
Bagyaraj
 
DJ.
 
2005
Influence of different AM fungi on the growth, nutrition and forskolin content of Coleus forskohlii
Mycological Research
  
109
795
798
.
Schausberger
 
P
Peneder
 
S
Jürschik
 
S
Hoffmann
 
D.
 
2012
Mycorrhiza changes plant volatiles to attract spider mite enemies
Functional Ecology
  
26
441
449
.
Schenkel
 
D
Lemfack
 
MC
Piechulla
 
B
Splivallo
 
R.
 
2015
A meta-analysis approach for assessing the diversity and specificity of belowground root and microbial volatiles
Frontiers in Plant Science
  
6
1
11
.
Schilmiller
 
A
Shi
 
F
Kim
 
J
, et al.  . 
2010
Mass spectrometry screening reveals widespread diversity in trichome specialized metabolites of tomato chromosomal substitution lines
The Plant Journal
  
62
391
403
.
Schnee
 
C
Kollner
 
TG
Held
 
M
Turlings
 
TC
Gershenzon
 
J
Degenhardt
 
J.
 
2006
The products of a single maize sesquiterpene synthase form a volatile defense signal that attracts natural enemies of maize herbivores
Proceedings of the National Academy of Sciences of the USA
  
103
1129
1134
.
Shimoda
 
T
Ozawa
 
R
Sano
 
K
Yano
 
E
Takabayashi
 
J.
 
2005
The involvement of volatile infochemicals from spider mites and from food-plants in prey location of the generalist predatory mite Neoseiulus californicus
Journal of Chemical Ecology
  
31
2019
2032
.
Shrivastava
 
G
Ownley
 
BH
Augé
 
RM
, et al.  . 
2015
Colonization by arbuscular mycorrhizal and endophytic fungi enhanced terpene production in tomato plants and their defense against a herbivorous insect
Symbiosis
  
65
65
74
.
Shulaev
 
V
Silverman
 
P
Raskin
 
I.
 
1997
Airborne signalling by methyl salicylate in plant pathogen resistance
Nature
  
385
718
721
.
Smith
 
SE
Gianinazzi-Pearson
 
V.
 
1988
Physiological interactions between symbionts in vesicular-arbuscular mycorrhizal plants
Annual Review of Plant Physiology and Plant Molecular Biology
  
39
221
244
.
Smith
 
SE
Read
 
DJ.
 
2008
Mycorrhizal symbiosis
 , 
4th edn.
 
London
Academic Press
.
Song
 
YY
Zeng
 
SR
Xu
 
JF.
 
2010
Interplant communication of tomato plants through underground common mycorrhizal networks
PLoS one
  
5
e13324
.
Song
 
YY
Ye
 
M
Li
 
CY
, et al.  . 
2014
Hijacking common mycorrhizal networks for herbivore-induced defence signal transfer between tomato plants
Science Reports
  
4
3915
.
Stökl
 
J
Brodmann
 
J
Dafni
 
A
Ayasse
 
M
Hansson
 
BS.
 
2011
Smells like aphids: orchid flowers mimic aphid alarm pheromones to attract hoverflies for pollination
Proceedings of the Royal Society, B
  
278
1216
1222
.
Strack
 
D
Fester
 
T.
 
2006
Isoprenoid metabolism and plastid reorganization in arbuscular mycorrhizal roots
New Phytologist
  
172
22
34
.
Sugimoto
 
K
Matsui
 
K
Iijima
 
Y
, et al.  . 
2014
Intake and transformation to a glycoside of (Z)-3-hexenol from infested neighbors reveals a mode of plant odor reception and defense
Proceedings of the National Academy of Sciences of the USA
  
111
7144
7149
.
Takabayashi
 
J
Dicke
 
M.
 
1996
Plant-carnivore mutualism through herbivore-induced carnivore attractants
Trends in Plant Science
  
1
109
113
.
Tholl
 
D.
 
2006
Terpene synthases and the regulation, diversity and biological roles of terpene metabolism
Current Opinion in Plant Biology
  
9
297
304
.
Tholl
 
D
Sohrabi
 
R
Huh
 
JH
Lee
 
S.
 
2011
The biochemistry of homoterpenes – common constituents of floral and herbivore-induced plant volatile bouquets
Phytochemistry
  
72
1635
1646
.
Ton
 
J
D'Alessandro
 
M
Jourdie
 
V
 et al.   
2006
Priming by airborne signals boosts direct and indirect resistance in maize
The Plant Journal
  
49
16
26
.
Tscharntke
 
T
Thiessen
 
S
Dolch
 
R
Boland
 
W.
 
2001
Herbivory, induced resistance and interplant signal transfer in Alnus glutinosa
Biochemical Systematics and Ecology
  
29
1025
1047
.
Unsicker
 
SB
Kunert
 
G
Gershenzon
 
J.
 
2009
Protective perfumes: the role of vegetative volatiles in plant defense against herbivores
Current Opinion in Plant Biology
  
12
479
485
.
Van Schie
 
CCN
Haring
 
MA
Schuurink
 
RC.
 
2007
Tomato linalool synthase is induced in trichomes by jasmonic acid
Plant Molecular Biology
  
64
251
263
.
Venkateshwaran
 
M. D
Chabaud
 
M
, et al.  . 
2015
A role for the mevalonate pathway in early plant symbiotic signaling
Proceedings of the National Academy of Sciences of the USA
  
112
9781
9786
.
Vicari
 
M
Hatcher
 
PE
Ayres
 
PG.
 
2002
Combined effect of foliar and mycorrhizal endophytes on an insect herbivore
Ecology
  
83
2452
2464
.
Vickers
 
CE
Bongers
 
M
Liu
 
Q
Delatte
 
T
Bouwmeester
 
H.
 
2014
Metabolic engineering of volatile isoprenoids in plants and microbes
Plant Cell and Environment
  
37
1753
1775
.
Vranova
 
E
Coman
 
D
Gruissem
 
W.
 
2012
Structure and dynamics of the isoprenoid pathway network
Molecular Plant
  
5
318
333
.
Walker
 
V
Couillerot
 
O
Von Felten
 
A
, et al.  . 
2012
Variation of secondary metabolite levels in maize seedling roots induced by inoculation with AzospirillumPseudomonas and Glomus consortium under field conditions
Plant Soil
  
356
151
163
.
Walter
 
MH
Strack
 
D.
 
2011
Carotenoids and their cleavage products: biosynthesis and functions
Natural Product Reports
  
28
663
692
.
Walter
 
MH
Fester
 
T
Strack
 
D.
 
2000
Arbuscular mycorrhizal fungi induce the non-mevalonate methylerythritol phosphate pathway of isoprenoid biosynthesis correlated with accumulation of the ‘yellow pigment’ and other apocarotenoids
The Plant Journal
  
21
571
578
.
Wegener
 
R
Schulz
 
S.
 
2002
Identification and synthesis of homoterpenoids emitted from elm leaves after elicitation by beetle eggs
Tetrahedron
  
58
315
319
.
Weisany
 
W
Raei
 
Y
Pertot
 
I.
 
2015
Changes in the essential oil yield and composition of dill (Anethum graveolens L.) as response to arbuscular mycorrhiza colonization and cropping system
Industrial Crops and Products
  
77
295
306
.
Wright
 
DP
Scholes
 
JD
Read
 
DJ.
 
1998a
Effects of VA mycorrhizal colonization on photosynthesis and biomass production of Trifolium repens L
Plant, Cell & Environment
  
21
209
216
.
Wright
 
DP
Read
 
DJ
Scholes
 
JD.
 
1998b
Mycorrhizal sink strength influences whole plant carbon balance of Trifolium repensL
Plant, Cell & Environment
  
21
881
891
.
Yeom
 
HJ
Kang
 
JS
Kim
 
GH
Park
 
IK.
 
2012
Insecticidal and acetylcholine esterase inhibition activity of Apiaceae plant essential oils and their constituents against adults of German cockroach (Blattella germanica)
Journal of Agricultural and Food Chemistry
  
60
7194
7203
.
Zebelo
 
SA
Matsui
 
K
Ozawac
 
R
Maffei
 
ME.
 
2012
Plasma membrane potential depolarization and cytosolic calcium flux are early events involved in tomato (Solanum lycopersicon) plant-to-plant communication
Plant Science
  
196
93
100
.
Zouari
 
I
Salvioli
 
A
Chialva
 
M
, et al.  . 
2014
From root to fruit: RNA-Seq analysis shows that arbuscular mycorrhizal symbiosis may affect tomato fruit metabolism
BMC Genomics
  
15
221
.
Zubek
 
S
Stojakowska
 
A
Anielska
 
T
Turnau
 
K.
 
2010
Arbuscular mycorrhizal fungi alter thymol derivative contents of Inula ensifolia L
Mycorrhiza
  
20
497
504
.


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