Tree Physiology 34, 915–918 doi:10.1093/treephys/tpu082 Commentary Physiological trade-offs in the complexity of pine tree defensive chemistry Luis Sampedro1 Misión Biológica de Galicia—Consejo Superior de Investigaciones Científicas, E36080 Pontevedra, Galicia, Spain (genecolpines.weebly.com); 1Corresponding author ([email protected]) Received July 27, 2014; accepted August 24, 2014; handling Editor Danielle Way Like all organisms on Earth, trees must finely tune the relative allocation of resources to their living functions (namely growth, maintenance, defence and reproduction), seeking to optimize the costs and benefits (Bazzaz et al. 1987). As resources are limited and those allocated to one trait cannot be allocated to another, conflicts in resource allocation may result in tradeoffs among different functions or traits (Agrawal et al. 2010). Such trade-offs might emerge as negative phenotypic correlations between pairs of traits with a shared source (reviewed by Saeki et al. 2014). Thus, patterns of phenotypic covariation (i.e., individual-based correlations) between traits help reveal possible conflicts in resource allocation and shared regulatory processes. One example in tree ecology and physiology is the relative allocation of resources to chemical defences (e.g., Keinanen et al. 1999, Koricheva et al. 2004, Donaldson et al. 2006, Agrawal 2011). Because of their life-history characteristics (such as being long-lived, large and forming extensive and stable populations) trees usually support a particularly diverse, extensive and temporally variable community of herbivores and pathogens. The selective pressure imposed by their antagonists has led to the evolution of effective resistance mechanisms, which include both constitutive and inducible defences (Zangerl and Bazzaz 1992). Constitutive defences, which are permanently expressed irrespective of the incidence of herbivores and pathogens, represent the first line of resistance. In contrast, induced resistance traits are activated, synthesized or mobilized in response to biotic challenges or cues of biotic damage. Plant resistance based on inducible defences, although energy saving, is a risky strategy as its benefits are based on the reliable identification of biotic cues (Karban 2011). Moreover, a plant could remain vulnerable for a period of time while induced defences are not activated or synthesized (e.g., Gómez et al. 2010). Therefore, plants need to combine a defensive system based on constitutive defences (which are omnipresent but have high associated costs) with induced defences (where the delay in activation is compensated for by the reduced cost associated with its production). The overlap of both strategies in space and time is assumed to be crucial for an efficient defence strategy (Cipollini and Heil 2010). Although there is an increasing body of theoretical predictions about this framework, little is known about the phenotypic integration of defensive investment in long-lived plants, whose life-history determinants (e.g., maintenance costs, delayed reproduction, multiple reproductive events and extent of life cycles) largely differ from those of herbaceous and annual plants examined to date. In this issue, Villari et al. (2014) present a case study of defence allocation patterns in pine trees. Constitutive and inducible defensive chemistry in pine trees is based on high concentrations of a variable array of carbon-based secondary compounds of a diverse chemical nature, namely terpenoids and phenolic compounds (Krokene et al. 2003, Keeling and Bolhmann 2006, Mumm and Hilker 2006). Villari et al. challenged individuals of a mature Scots pine alpine population growing under extreme environmental stress with bark plugs inoculated with two fungi associated with pine bark beetles (see Villari et al. 2012). Three weeks after inoculation, samples of bark and phloem tissues of induced and control trees were subjected to metabolite profiling of terpenoids and phenolics. The authors looked for phenotypic, individual-based correlations that provide information on possible resource-derived trade-offs between investment in secondary chemistry and © The Author 2014. Published by Oxford University Press. All rights reserved. For Permissions, please email: [email protected] 916 Sampedro growth rates, between different chemical compounds and between constitutive and inducible variation in defensive chemistry. Phenotypic correlation between growth rate, age and investment in defensive chemistry A major finding of Villari et al.’s study is that the tree-ring growth rate over the past 10 years was a good predictor of constitutive investment in terpenoids (for both total terpenoids and most of the individual terpenoids identified). However, tree-ring growth was not related to the concentration of total phenolics or individual phenolic compounds. In addition, induced variation of most individual and total terpenoids and phenolics was not related to tree-ring growth. In other words, Villari et al. (2014) found no evidence of allocation conflicts between primary and secondary metabolism, but rather, they uncovered a positive relationship between growth and defensive investment under those growth-limiting conditions, as predicted by the extended Growth–Differentiation Balance Hypothesis (GDBH) (Herms and Mattson 1992). From an evolutionary point of view, the theoretical background predicts that optimal relative investment in defences should be greater in slow-growing plant species or lineages adapted to stressful, growth-limiting environments due to greater construction costs (as posed by the Resource Availability Hypothesis by Coley et al. 1985, reviewed by Endara and Coley 2011). However, from a physiological point of view, the GDBH predicts that optimal investment in defences at the individual level is not a linear function of carbon assimilation and growth rates across the entire growth rate range of a species (Herms and Mattson 1992). Pine trees are a good model for studying these relationships, as they have differentiated secretory organs for production and storage of chemical defences. Terpenoids and phenolic compounds are secreted and stored in specialized tissues: the resin duct network of the xylem and cortex and the polyphenolic parenchyma cells in the phloem, respectively (Franceschi et al. 2005). Damage signalling triggers physiological processes and changes in the cambium, leading to swelling and/or differentiation of more or greater xylem resin ducts and polyphenolic parenchyma cells (Krokene et al. 2003, Hudgins and Franceschi 2004). These tissues remain functional and active for a time, serving as a footprint of previous induced responses or past damage. This is advantageous for retrospective studies linking growth rates and net (current + past) defensive investment. In this sense, the results of Villari et al. agree with recent papers suggesting that there is no evidence of phenotypic resource-based trade-offs between growth and resin-based defences in pine trees (Ferrenberg et al. 2014, RodríguezGarcía et al. 2014). On the other hand, studies characterizing the concentrations and profiles of both terpenoids and phenolics are scarce, making Tree Physiology Volume 34, 2014 this paper particularly welcome. While numerous studies have focused on terpenoids and phenolic compounds in conifers, most of these studies have been devoted to examining the chemical ecology of a single type of compound (e.g., single groups of terpenes, phenolics or alkaloids). The relative lack of more comprehensive studies may be due to the lack of facilities needed for the analysis of chemicals of different nature, as well as the expertise required for data analysis and interpretation of results. The complexity and diversity of defensive chemistry in trees is vast, and papers covering the entire array of chemicals (such as that from Villari et al.) are valuable for understanding the integration of tree defences and their environmental determinants. An important point for fully understanding resource-derived trade-offs is that the limiting source of carbon constraining the allocation must be clearly identified (recently reviewed by Saeki et al. 2014). In the case of pine defensive chemistry, the energy source for defensive chemistry is likely a combination of current assimilates and non-structural stored carbohydrates. Identifying the relative contribution of these two sources to pine defences may have important implications for plant physiology and ecology (Martinez-Vilalta 2014, Saffell et al. 2014). Although this topic has been studied at the cellular level (e.g., Affek and Yakir 2003, Schnitzler et al. 2004), more research is needed about the relative contribution of current carbon assimilation and stored carbohydrates to the synthesis of both constitutive and induced phenolics and terpenoids at the whole tree level (but see Goodsman et al. 2013). Advances in our understanding of this topic would help us to understand how environmental factors such as those leading to carbon starvation and altered carbon storage (e.g., water availability and winter temperature) will affect current and future defensive investment and capabilities in pine trees, subsequently impacting tree survival and performance in a changing climate. Phenotypic correlations between constitutive and inducible variation Villari et al. (2014) also explored the functional relationships between the constitutive concentration and inducible variation of pairs of compounds. Their analyses resulted in the classification of five response types, depending on the sign, shape (linear or quadratic) and slope of the response to their experimental treatments. Studying the pattern of phenotypic covariation between pairs of compounds is a valuable approach, as the functional linkage between resource-related traits is not necessarily linear, because gains in one trait could lead to multiplicative effects in the other. Thus, non-linear relationships are expected and must be explored to characterize the physiological trade-offs, as stressed by Saeki et al. (2014) in their recent review about concepts and methodology on this topic. As constitutive and induced resistance cannot be maximized at the same time, and lineages expressing high levels Physiological trade-offs in pine tree defensive chemistry 917 of constitutive resistance would obtain limited fitness benefits from expressing induced resistance, an evolutionary trade-off between both strategies is predicted (e.g., Kempel et al. 2011, but see Morris et al. 2006 for a critical review of methodological approaches). This type of negative genetic correlation between traits may impose evolutionary constraints on the simultaneous improvement of both strategies and thus influence evolutionary trajectories within populations, and as well as at the macroevolutionary level (Sgrò & Hoffmann 2004, but see Moreira et al. 2014). For this purpose, studies based on phenotypic correlations, although valuable, allow for only limited evolutionary inference compared with studies based on genotypic or family correlations, which provide information on heritable, genetic-based trade-offs (reviewed by Agrawal et al. 2010). In long-lived trees, this type of research has been mainly performed using young individuals (e.g., Sampedro et al. 2011, Carillo-Gavilán et al. 2012, Moreira et al. 2013), while the results from Villari et al. (2014) should encourage further research on this topic at the adult stage. Covariation between individual secondary compounds Villari et al. (2014) found no phenotypic correlations between the concentration of total phenolics and total terpenoids, and they detected no significant correlations between individual chemical compounds. Importantly, both results suggest that there are no conflicts or substrate competition in the alternative allocation to the phenylpropanoid and isoprenoid defensive pathways at the individual level. Such an absence of negative correlations between defensive chemicals at the individual level, or even a positive covariation, is not uncommon in plants (Koricheva et al. 2004). Due to the vast diversity in quality and concentration of pine chemical defences (i.e., Iason et al. 2011), and provided that defensive chemicals do not function in isolation, it seems that the next step is to take advantage of multivariate bioinformatic tools for the analysis of these types of large databases. Further efforts that combine the analytical approaches of evolutionary ecology, chemical ecology and tree physiology are required. The analysis of databases covering hundreds of compounds would greatly benefit from network analysis and whole plant metabolome approaches. A recent article by Harding et al. (2014) and some recent reviews on this topic (Kliebenstein 2014, Moore et al. 2014) illustrate these points, and they encourage new analytical approaches to understanding the complexity and common regulatory networks in constitutive and induced allocation of conifer defences. Advanced analysis of exhaustive chemical studies of adult trees in forest genetic trials with family or population structure would be crucial for understanding the multivariate structure of plant defences in long-lived plants, as well as the metabolic integration of costs and benefits of individual chemical species and their patterns of context dependency. In summary, Villari et al. (2014) provide new ideas and a valuable model for new approaches that should motivate scientists to put more effort into the fine-scale characterization of the diversity of secondary metabolites in response to biotic challenges. These approaches would benefit from advanced multivariate analyses and experimental designs using plant material with a known genetic background. This would help advance our knowledge of the phenotypic integration and physiological regulation of tree defensive chemistry, as well as the evolutionary ecology of defences in long-lived plants. This type of research has usually been performed on young individuals under controlled conditions, and it is clear that more effort is needed to examine adults under field conditions. Such research would be challenging, given the difficulties in establishing and maintaining mature field stands of known genetic backgrounds. Thus, we should encourage more intense interactions between forest tree breeders and tree physiologists, as future research in this field should utilize the long-term networks of progeny and provenance trials established by national and provincial forest services. Acknowledgments The author thank Rafael Zas and Xoaquin Moreira, Jose Climent, Luis Santos, Jordi Voltas and other colleagues in the FENOPIN group (http://www.genecolpines.weebly.com) for creative debating, questions and answers about defensive strategies in pine trees. The author also thanks the editor and two reviewers for their suggestions. Conflict of interest None declared. Funding Financial support was obtained from the Spanish National Research Grants (competitive grant AGL2012-40151 – FENOPIN) co-financed by EU-FEDER. References Affek HP, Yakir D (2003) Natural abundance carbon isotope composition of isoprene reflects incomplete coupling between isoprene synthesis and photosynthetic carbon flow. Plant Physiol 131:1727–1736. Agrawal AA (2011) New synthesis—trade-offs in chemical ecology. J Chem Ecol 37:230–231. Agrawal AA, Conner JK, Rasmann S (2010) Tradeoffs and negative correlations in evolutionary ecology. In: Bell MA, Eanes WF, Futuyma DJ, Levinton JS (eds) Evolution after Darwin: the first 150 years. Sinauer Associates, Sunderland, MA, pp 242–268. Bazzaz FA, Chiariello NR, Coley PD, Pitelka LF (1987) Allocating resources to reproduction and defence. BioScience 37:58–67. Tree Physiology Online at http://www.treephys.oxfordjournals.org 918 Sampedro Carrillo-Gavilán A, Moreira X, Zas R, Vila M, Sampedro L (2012) Early resistance of alien and native pines against two native generalist insect herbivores: no support for the natural enemy hypothesis. Funct Ecol 26:283–293. Cipollini D, Heil M (2010) Costs and benefits of induced resistance to herbivores and pathogens in plants. CAB Rev 5:1–25. Coley PD, Bryant JP, Chapin FS III (1985) Resource availability and plant anti-herbivore defense. Science 230:895–899. Donaldson JR, Kruger EL, Lindroth RL (2006) Competition- and resource-mediated tradeoffs between growth and defensive chemistry in trembling aspen (Populus tremuloides). New Phytol 169: 561–570. Endara MJ, Coley PD (2011) The resource availability hypothesis revisited: a meta-analysis. Funct Ecol 25:389–398. Ferrenberg S, Kane JM, Mitton JB (2014) Resin duct characteristics associated with tree resistance to bark beetles across lodgepole and limber pines. Oecologia 174:1283–1292. Franceschi V, Krokene P, Krekling T (2005) Anatomical and chemical defenses of conifer bark against bark beetles and other pests. New Phytol 167:353–376. Gómez S, van Dijk W, Stuefer JF (2010) Timing of induced resistance in a clonal plant network. Plant Biol 12:512–517. Goodsman DW, Lusebrink I, Landhäusser SM, Erbilgin N, Lieffers VJ (2013) Hierarchies in carbon availability, defense chemistry and susceptibility to fungal invasion along tree boles. New Phytol 197:586–594. Harding SA, Xue L-J, Du L, Nyamdari B, Lindroth RL, Sykes R, Davis MF, Tsai C-J (2014) Condensed tannin biosynthesis and polymerization synergistically condition carbon use, defense, sink strength and growth in Populus. Tree Physiol. doi:10.1093/treephys/tpt097. Herms DA, Mattson WJ (1992) The dilemma of plants: to grow or defend. Quart Rev Biol 67:283–335. Hudgins JW, Franceschi VR (2004) Methyl jasmonate-induced ethylene production is responsible for conifer phloem defense responses and reprogramming of stem cambial zone for traumatic resin duct formation. Plant Physiol 135:2134–2149. Iason GR, O'Reilly-Wapstra J, Brewer MJ, Summers RW, Moore BD (2011) Do multiple herbivores maintain chemical diversity of Scots pine monoterpenes. Philos Trans Royal Soc Lond B Bio Sci 366:1337–1345. Karban R (2011) The ecology and evolution of induced resistance against herbivores. Funct Ecol 25:339–347. Keeling CI, Bohlmann J (2006) Genes, enzymes and chemicals of terpenoid diversity in the constitutive and induced defence of conifers against insects and pathogens. New Phytol 170:657–675. Keinanen M, Julkunen-Tiitto R, Mutikainen P, Walls M, Ovaska J, Vapaavuori E (1999) Trade-offs in phenolic metabolism of silver birch: effects of fertilization, defoliation and genotype. Ecology 80:1970–1986. Kempel A, Schadler M, Chrobock T, Fischer M, van Kleunen M (2011) Tradeoffs associated with constitutive and induced plant resistance against herbivory. Proc Natl Acad Sci USA 108:5685–5689. Kliebenstein (2014) Orchestration of plant defense systems. Trends Plant Sci 19:250–255. Tree Physiology Volume 34, 2014 Koricheva J, Nykanen H, Gianoli E (2004) Meta-analysis of trade-offs among plant antiherbivore defenses: are plants jacks-of-all-trades, masters of all? Am Nat 163:64–75. Krokene P, Solheim H, Krekling T, Christiansen E (2003) Inducible anatomical defense responses in Norway spruce stems and their possible role in induced disease resistance. Tree Physiol 23:191–197. Martínez-Vilalta J (2014) Carbon storage in trees: pathogens have their say. Tree Physiol 34:215–217. Moore BD, Andrew RL, Külheim C, Foley WJ (2014) Explaining intraspecific diversity in plant secondary metabolites in an ecological context. New Phytol 201:733–750. Moreira X, Zas R, Sampedro L (2013) Additive genetic variation in resistance traits of an exotic pine species: little evidence for constraints on evolution of resistance against native herbivores. Heredity 110:449–456. Moreira X, Mooney KA, Rasmann S, Petry WK, Carrillo-Gavilán A, Zas R, Sampedro L (2014) Trade-offs between constitutive and induced defences drive geographical and climatic clines in pine chemical defences. Ecol Lett 17:537–546. Morris WF, Traw MB, Bergelson J (2006) On testing for a tradeoff between constitutive and induced resistance. Oikos 112:102–110. Mumm R, Hilker M (2006) Direct and indirect chemical defence of pine against folivorous insects. Trends Plant Sci 11:351–358. Rodríguez-García A, López R, Martín JA, Pinillos F, Gil L (2014) Resin yield in Pinus pinaster is related to tree dendrometry, stand density and tapping-induced systemic changes in xylem anatomy. For Ecol Manag 313:47–54. Saeki Y, Tuda M, Crowley PH (2014) Allocation tradeoffs and life histories: a conceptual and graphical framework. Oikos 123:786–793. Saffell BJ, Meinzer FC, Woodruff DR, Shaw DC, Voelker SL, Lachenbruch B, Falk K (2014) Seasonal carbohydrate dynamics and growth in Douglas-fir trees experiencing chronic, fungal-mediated reduction in functional leaf area. Tree Physiol 34:218–228. Sampedro L, Moreira X, Zas R (2011) Costs of constitutive and jasmonate-induced pine tree chemical defences emerge only under low nutrient availability. J Ecol 99:818–827. Schnitzler J-P, Graus M, Kreuzwieser J, Heizmann U, Rennenberg H, Wisthaler A, Hansel A (2004) Contribution of different carbon sources to isoprene biosynthesis in poplar leaves. Plant Physiol 135:152–160. Sgrò CM, Hoffmann AA (2004) Genetic correlations, tradeoffs and environmental variation. Heredity 93:241–248. Villari C, Battisti A, Chakraborty S, Michelozzi M, Bonello P, Faccoli M (2012) Nutritional and pathogenic fungi associated with the pine engraver beetle trigger comparable defenses in Scots pine. Tree Physiol 32:867–879. Villari C, Faccoli M, Battisti A, Bonello P, Marini L (2014) Testing phenotypic trade-offs in the chemical defence strategy of Scots pine under growth-limiting field conditions. Tree Physiol 34:919–930. Zangerl AR, Bazzaz FA (1992) Theory and pattern in plant defense allocation. In: Fritz R, Simms E (eds) Plant resistance to herbivores and pathogens, ecology, evolution and genetics. University of Chicago Press, Chicago, IL, pp 363–391.
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