1 Ecological understanding of root-infecting fungi using trait-based 2 approaches 3 Carlos A. Aguilar-Trigueros1,2, Jeff R. Powell3, Ian C. Anderson3, Janis Antonovics4, 4 Matthias C. Rillig1,2 5 1 6 Germany 7 2 8 Germany 9 3 Freie Universität Berlin, Institut für Biologie, Plant Ecology, D-14195 Berlin, Berlin-Brandenburg Institute of Advanced Biodiversity Research, D-14195 Berlin, University of Western Sydney, Hawkesbury Institute for the Environment, Penrith 10 NSW 2751, Australia 11 4 12 Corresponding author: Rillig M.C. (rillig@zedat.fu-berlin.de) University of Virginia, Department of Biology, Charlottesville, VA 22904, USA 13 14 Word (main text): 2187 15 Abstract: 115 16 Additional elements: 1 Glossary box; 1 Text box (315 words); 1 Table; 1 Figure 17 1 18 Classification schemes have been popular to tame the diversity of root infecting 19 fungi. However, the usefulness of these schemes is limited to descriptive purposes. 20 We propose that a shift to a multidimensional trait-based approach to disentangle 21 the saprotrophic-symbiotic continuum will provide a better framework to 22 understand fungal evolutionary ecology. Trait information reflecting the 23 separation of root infecting fungi from free living soil relatives will help to 24 understand the evolutionary process of symbiosis; the role that species interactions 25 play in maintaining their large diversity in soil and in planta; and their 26 contributions at the ecosystem level. Methodological advances in several areas such 27 as microscopy, plant immunology and metatranscriptomics represent emerging 28 opportunities to populate trait data bases. 29 30 Limitations of categorical approaches to study plant–soil fungal interactions 31 Understanding the effects of plant–soil fungal interactions in natural communities 32 has become a major research area in plant science [1]. Interest in these interactions 33 stem from increasing awareness that soil biota play an important role in plant 34 performance, plant community assembly and ecosystem functioning [2]. 35 However the complexity of soil fungal communities challenges our ability to 36 understand the effects of such interactions on plant performance and on ecosystems 37 processes. Recent surveys show that roots interact with phylogenetically diverse 38 groups of fungi [3]. Moreover, the effects of particular plant-fungal combinations 39 depend on environmental conditions and on the host and fungal genotypes [4]. In 40 diverse communities and variable environments, net responses may be due to 41 complex indirect interactions among co-occurring fungi and plants [5]. 2 42 Given these complex associations, researchers regularly classify fungal taxa 43 into broad categories according to particular criteria. These criteria may be based on 44 nutritional mode (e.g., “biotroph”, “necrotroph” or “saprotroph” [6] (see Glossary)), 45 presence of hyphal melanization and formation of septa (e.g."dark septate 46 endophytes" [7]), or on a mix of taxonomic, morphological and physiological 47 characteristics (e.g. “arbuscular mycorrhizal”; “ectomycorrhizal” [8]). These 48 classificatory approaches have been important for distilling broad generalities from 49 the rich brew of fungal–plant interactions such as the recognition of contrasting 50 plant defense mechanisms against infecting fungi with different nutritional modes 51 [9]. 52 However, assignment of root infecting fungi into fixed categories is 53 problematic for species labeled as “endophytes”. For example, some of the criteria 54 used in delineating endophyte classes [10] are quantitative (number of potential 55 hosts; number of co-infections within a host or degree of tissue colonization) but 56 their delineation is imprecise (narrow vs. broad host range; low vs. high in planta 57 diversity; extensive vs. limited in planta colonization). Similarly, a suggestion that 58 “endophytic functional groups” should be based on their effects on host fitness 59 resulted in the rather unsatisfying conclusion that "some endophytes may be latent 60 pathogens, some may be derived from pathogens, and others may be latent 61 saprotrophs, but many are neither"[11]. Such classification schemes can provide a 62 useful initial framework to understand poorly studied plant–fungal interactions, but 63 the resulting generalizations often include the listing of so many exceptions to the 64 proposed scheme that the framework is not useful operationally. 65 66 We argue that a shift in focus from classification schemes to a multidimensional trait-based approach reflecting the biology of the fungi is necessary 3 67 for a better understanding of the ecology and evolution of root infecting fungi. These 68 approaches consider species as a conglomerate of unique combinations of multiple 69 traits, which could be depicted as species being points defined by multiple traits 70 represented as dimensions (Fig 1a). This view directly link particular ecological and 71 evolutionary questions with trait information. The proposed multidimensional trait- 72 based program presented here is focused on the traits that allocate “endophytic” or 73 “pathogenic” root fungi to a symbiotic lifestyle and separate them from free-living 74 saprotrophic relatives. We explain how trait information can be used to address three 75 essential questions: What are the mechanisms behind the evolution of root 76 endophytic or pathogenic lifestyles from free-living fungi and vice versa? What is 77 the importance of trait similarity in explaining the co-occurrence patterns of fungal 78 genotypes or species in planta and in the soil? And, which traits might be used to 79 understand the functional diversity of soil fungi? This is illustrated conceptually in 80 Figure 1. 81 82 A fungal-trait approach: understanding the saprotrophic-symbiotic continuum. 83 Trait-based approaches rely on measurements of phenotypic characters or traits to 84 guide inferences about particular ecological or evolutionary processes (Box 1). For 85 example, plant scientists have successfully used such approaches to understand how 86 fire has influenced the evolution within the Pinacea by combining trait information 87 with phylogenetic reconstructions [12]; measure the relative importance of abiotic 88 factors and biotic interactions in shaping community assembly of tropical trees by 89 measuring trait overdispersion in local communities [13]; or understanding how plant 4 90 diversity influences the variability of decomposition rates within climate regions by 91 combining decomposition data with leaf traits from databases [14]. 92 We explain how application of such trait-based approaches may be valuable at a 93 conceptual level in understanding the saprotrophic-symbiotic continuum in root 94 infecting fungi. This continuum is pertinent to this set of fungi as most root 95 endophytes constitute a gray area along the saprotrophic–symbiotic spectrum [10] 96 and facultative saprotrophy is a characteristic of most studied root pathogens [15]. 97 Indeed, this issue has been debated among plant pathologists ever since the seminal 98 work of Garrett [16]. More recently it has been a major focus of study among 99 researchers on ectomycorrhizal fungi [17, 18]. 100 Understanding the saprotrophic-symbiotic continuum is of particular 101 relevance to plant–fungal associations that have been labeled "endophytic" or "root 102 pathogenic". Despite being considered major components of natural communities 103 [10, 19], "endophytes" are not well defined in terms of their nutritional mode, there 104 is little empirical understanding of their life history strategies, which in turns makes 105 predicting their community and ecosystem impacts difficult. 106 Specifically we aim at explaining how characterizing this continuum using a 107 trait-based approach will make inroads on: first, explaining the evolutionary 108 trajectories of symbiotic fungi from soil-inhabiting relatives (and vice versa). 109 Second, understanding and predicting the functional role of fungi along this 110 continuum in nutrient and carbon dynamics within ecosystems. Third, providing a 111 mechanistic understanding of fungal community assembly and diversity maintenance 112 both in soil and in planta. In the following section, we lay out the basis for such an 5 113 approach, defining classes of traits relevant to this continuum, and suggest examples 114 of relevant and measureable traits. 115 116 Symbiotic and saprotrophic traits: a starting point 117 In Table 1 we provide some examples of traits that we consider to be critical in 118 assessing the ecology and evolution of “endophytic/pathogenic” root infecting fungi. 119 As will be evident from the brief discussion of the rationale for each of them, these 120 broad traits will themselves consist of many component traits that are operationally 121 measurable. We expand on some of these points below. 122 Symbiotic traits are often related to the ability of fungi to avoid or overcome 123 resistance responses driven by the plant immune system as host resistance is the main 124 filter preventing the use of the root niche [20]. Other traits may be related to the 125 metabolic interactions that occur in such symbioses; for example, systems for 126 translocation and bidirectional transport of nutrient and carbon resources [21]. 127 Identification of relevant component traits for “root endophytic” associations 128 depends on understanding the molecular and physiological activities in fungal 129 colonization structures [22]. Saprotrophic traits are related to the enzymatic 130 machinery required to degrade the diversity of recalcitrant carbon sources [23], 131 production of antimicrobial compounds during competition with other fungi [24] and 132 with bacteria [25], and preventing or responding to fungivory by soil animals [26]. 133 The traits in this continuum may help us to understand the evolutionary 134 process behind the transitions from saprotrophism to symbiosis and vice versa [27]. 135 This could be achieved using comparative phylogenetic approaches quantifying the 136 variation in saprotrophic and symbiotic traits and identifying potential life history 6 137 trade-offs, instead of using categories such as endophyte, saprotroph or pathogen as 138 if they were characters [28]. It should also be possible to compare the evolutionary 139 processes underlying the colonization and exploitation of roots vs. leaves by fungal 140 endophytes or pathogens. The contrast between these two organs regarding their 141 structure and their local environments [29] may help explain differences in 142 colonization patterns between root and leaf “pathogens" or "endophytes” [4]. 143 Trait-based approaches could also be used to unravel compositional 144 differences in fungal communities inhabiting roots, the rhizosphere, and bulk soils. 145 As roots are living organs, fungal species with “symbiotic" traits should dominate in 146 the root compartment while species with “saprotrophic” ones should be more 147 abundant in the rhizosphere and bulk soil. Trait information, if mapped onto fungal 148 communities found in various soil compartments could be used to understand the 149 ecological basis and predictability of these assemblages. For instance, canonical 150 examples in agricultural research have led to the common view that root necrotrophic 151 pathogens, despite having saprotrophic abilities, are outcompeted by “strict” soil 152 saprotrophs [30]. Trait information could be used to test whether such putative trade- 153 offs apply to root “endophytes” or “pathogens” in natural systems. 154 Trait information also allows the formulation of novel hypotheses. For 155 example, does high trait diversity at the community level increase resistance to 156 invasion by other fungi? Successful invasion depends on the number of open niches 157 [31], and established fungal communities exhibiting high trait diversity may reduce 158 resources (space, nutrients, organic matter) or limit access to resources (by priming 159 host defenses or producing antibiotics). For fungi at the symbiotic end of the 160 spectrum, is growth in the soil environment limited by the diversity of resident 161 saprotrophic traits in the rhizosphere? Relationships between trait diversity and 7 162 invasion resistance may help predict the likelihood of disease outbreaks by highly 163 virulent root-infecting fungi in agricultural systems. 164 Assessing trait similarity provides a better means to assess the effect of 165 competition among co-infecting fungi in the evolution, maintenance and frequency 166 of mutualistic or pathogenic interactions [32]. Another application might be in 167 coupling trait information with the comparisons of root infecting fungal communities 168 among invasive plants in their native and introduced ranges: such information may 169 help explain the alleged reduction of pathogen attack of invasive plants in the 170 introduced ranges if infecting fungi do not possess the traits to effectively exploit the 171 new host [33]. 172 A trait based approach for the saprotrophic-symbiotic continuum may better 173 capture the importance of root infecting fungi in carbon and nutrient cycling at the 174 ecosystem level, in a manner completely analogous to the use of "functional trait 175 analysis" in plants [34, 35]. Little is currently known about the effects of fungal trait 176 diversity on ecosystem processes although the recent frameworks proposed for 177 mycorrhizal associations [36, 37] suggest that other root-inhabiting fungi may be 178 important contributors to ecosystem function. Trait-based approaches would allow 179 the recognition of factors that correlate with the main ecosystem processes, to 180 identify the taxa driving such effects, and lead to a better understanding of ecosystem 181 drivers. 182 183 Trait measurement and storage of trait information in high quality databases 184 The full application of any trait-based approach depends on the accessibility of 185 databases that are well curated, well funded, and linked to genomic and phylogenetic 8 186 information. Phylogenetic databases have already been created for taxonomic 187 purposes (e.g. UNITE [38]; http://www.deemy.de for ectomycorrhizal fungi). Thus, 188 there is an excellent window of opportunity to integrate trait information generated 189 from morphological and physiological characterization of newly isolated fungi with 190 such platforms. Traits are measured on particular individuals, and meaningful 191 extrapolations to species (or higher ranks) also depend on having estimates of trait 192 variability among individuals and populations, as well as on the adequacy of the 193 species concept for fungi [36]. 194 Additionally, to be meaningful, trait information should be presented together 195 with data on the conditions and circumstances under which the traits were measured 196 (“metadata”). Trait information collected from culturable fungi under controlled 197 conditions is useful to quantify a particular trait (e.g. phytotoxin production). 198 Analogously, plant ecologists have populated trait-databases with measurements 199 from controlled experimental conditions with standardized methods [39]. This level 200 of control enables the use of meta-analytical tools to filter out the effect of variable 201 conditions to better address broad scale functional diversity-ecosystem functioning 202 questions [14]. 203 Coupling this approach with in situ trait measurements under natural 204 conditions (in mesocosms or the field) and with species abundance data will allow 205 estimates of the contribution of a species in the context of environmental variability. 206 Furthermore, in situ measurement of intraspecific trait variability could be used to 207 refine models of community assembly [40]. However, caution must be taken when 208 such trait information is intended to be used outside the particular system from which 209 the traits were measured. It has been shown that traits with high levels of plasticity 9 210 and measured from extreme habitats do not match well average values from 211 databases [41]. 212 In situ measurements are the only option to incorporate trait information for 213 non-culturable fungi and are analogous to measurements for long-lived plant species 214 (e.g., wood traits for tree species in the TRY database [42]). Hyphal length in soil or 215 nutrient concentration in the hyphae can be measured following extraction of hyphae 216 directly from the environment or from substrate-filled compartments [43, 44]. 217 Enzyme activity assays performed on ectomycorrhizal root tips [45] or fungal carbon 218 substrate usage by fungi [46] are usually measured on excised material, but they 219 may not accurately reflect process rates due to the effects of the manipulations. 220 Metatranscriptomic and other gene expression profiling approaches are promising 221 and have the potential to lead to major insights at the community level [47, 48] and 222 would be especially valuable if these could be targeted at fungal gene expression in 223 particular. More sophisticated approaches at the individual level using "omics" tools 224 (e.g., single cell genomics [49]; laser microdissection [50]) that can simultaneously 225 examine fungal characters and identify the species being examined, hold exciting 226 promise for future studies of soil fungal communities. 227 228 Concluding remarks 229 Rigorous comparative studies linked with phylogenetic information that is focused 230 on traits, rather than qualitative categories, are necessary to determine what 231 constitutes an adaptation to a particular life-style. In turn, traits can be used to make 232 predictions about the impact and causes of community structure, and traits that 233 strongly influence ecosystem function can be highlighted and measured for 10 234 predicting outcomes. In this paper, as illustrated in Figure 1, we advocate a more 235 objective trait-based approach to characterizing the processes involved in the 236 interactions of root and soil inhabiting fungi, and hence provide a way to assess their 237 importance at the evolutionary, community, and ecosystem levels. Others have 238 strongly supported the use of trait-based approaches to move forward research on 239 plant–fungal interactions [51, 52] and on microbial ecology [53]. In particular, there 240 has been a recent call to explicitly use conceptual frameworks from functional 241 ecology in ectomycorrhiza research, which promote integration of this important 242 fungal group into research on diversity-ecosystem functioning relations . 243 Although broad categories have their place in the initial development of a discipline, 244 they provide a rather abstract view of multi component processes at such a level of 245 simplicity that they may actually inhibit understanding. In studies of root-inhabiting 246 fungi, there has been a tendency to use qualitative categories to describe the 247 saprotrophic-symbiotic continuum, rather than search for generalizations that come 248 from more quantitative studies. Here we advocate a trait-based approach to 249 understand the evolutionary ecology of root-inhabiting fungi and illustrate how this 250 approach promises a clear way forward in this complex and technically difficult 251 field. 252 253 Acknowledgements 254 We thank the Alumni Network Program of Freie Universität Berlin for funding. CA 255 was also supported by the German Academic Exchange Service (DAAD), ICA by a 256 fellowship from the German Federal Ministry of Education and Research, and JA by 11 257 an Alexander von Humboldt Research Award. 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Schematic 412 representation of a trait-based approach to understanding the ecology and evolution of 413 root infecting fungi. Instead of placing species into fixed categories such as pathogen 414 endophyte or saprotroph trait-based multivariate approaches represent species as 415 particular combinations of traits in various dimensions. Such information can be 416 coupled with: (A) phylogenic data () to understand evolutionary change; (B) their effect 417 on species performance under different ecological factors () to understand mechanisms 418 of community assembly and species co-existence and; (C) with their ecosystem function 419 to explore their role on ecosystem processes. Note: The graphic in (B) represent the 420 lower resource boundaries above which species 1 and 2 can still grow (zero net growth 421 isoclines as in [54]). In this figure, the position of lines depends on the traits the species 422 posses to exploit two resources: carbon from the host or from decaying matter. 423 424 Glossary box 425 Biotroph: nutritional mode in which a fungal symbiont relies exclusively on living host 426 cells as a source of nutrients. 427 Functional trait: Species traits directly linked with a particular ecosystem process. 428 Different species sharing similar functional traits are pooled into functional groups. 15 429 Life history trait: Traits reflecting allocation of resources of an individual into different 430 fitness components. 431 Necrotroph: nutritional mode in which a fungal symbiont causes host cell death in 432 order to acquire nutrients. 433 Saprotroph: nutritional mode in which a free-living fungus obtains nutrients from 434 decaying organic matter, without inducing the death of the tissue. 435 Symbiosis: a physiological or structurally intimate interaction between phylogenetically 436 unrelated organisms, without implying a specific effect on either organisms’ fitness. 437 Trait: any morphological, physiological, or phenological character of an organism. 438 439 Box 1. Rationales for trait-based approaches 440 The rationale for collecting data for particular traits may differ. Traits may be chosen 441 because they are likely to contribute to answer particular questions: a "top-down" 442 approach. Alternatively, traits may be chosen because they can be integrated with the 443 ever-increasing body of genomic and gene expression data allowing linkage of 444 particular genes with tangible phenotypes, or traits, of ecological importance. This 445 would be a "bottom-up" approach. Additionally, there is tremendous value in 446 including traits simply because they are "easy to measure": databases are as valuable 447 in generating hypotheses as they are in testing them, and unusual and unpredicted 448 trait associations are a stimulus for deeper investigation. 449 Traits can be used to test hypotheses of evolutionary processes in conjunction 450 with independently derived, usually sequence-based, phylogenetic information. Thus, 16 451 they provide objective ways to identify and test potential evolutionary trade-offs in 452 life history traits and relate them to environmental conditions using phylogenetic 453 comparative methods. For example, this approach has been used to evaluate 454 allocation of carbon by arbuscular mycorrhiza fungal species to hyphal structures in 455 roots and soil where percentage of root colonization and length of extra-radical 456 mycelia were used as traits [55]. 457 Trait-based approaches can also be used to understand community assembly. 458 First, they allow the identification of potentially important physiological and 459 ecological mechanisms by correlating traits with species performance along 460 environmental gradients [56]. Second, trait similarity among species can be used to 461 infer niche similarity and determine its effects on species sorting [57]. For example, 462 the existence of trait trade-offs in important ecological factors or niche axes is 463 fundamental for a mechanistic understanding of species co-existence [54]. 464 At the ecosystem level, species sharing traits that influence particular 465 ecosystem properties or species’ responses to environmental conditions can be 466 pooled into particular functional groups [58]. For example, Tilman [34] showed that 467 functional trait diversity is a better predictor of community productivity than 468 taxonomic diversity. This functional ecology perspective has focused on determining 469 which traits allow species to face environmental changes –response traits- as well as 470 which traits determine how species influence the environment –effect traits; and 471 establishing the link between these set of traits to make better trait-based models of 472 community assembly and ecosystem functioning [59]. Recently there has been a call 473 to use this conceptual framework for ectomycorrhizal fungi [37]. 474 17 475 18 476 Table 1. Examples of traits that are potentially important for characterizing fungi that fall along the symbiotic and saprotrophic continuum. Fungal traits Description and rationale Refs Production of cell-wall degrading enzymes They broaden the spectrum of carbon sources for saprotrophic growth, but at the same time they trigger host defenses as a result of disruption of cell walls in living cells. The ability to decompose lignin (e.g. by white rot saprotrophs) expands availability of carbon substrates in woody systems. This trait seems rare in ectomycorrhizal fungi. Key traits to cope with interference competition by fungi and bacteria are the production of antibiotics as well as the enzymes that degrade them. Soil fungi may produce toxic metabolites, melanin or crystalline cell inclusions to avoid fungivory by soil animals. Resting structures permit survival under adverse conditions: a lack of appropriate hosts or inadequate carbon sources. Whether this is more or less likely in endophytic fungi is not known, and may depend on root or plant longevity. Root symbiotic fungi have both vertical and horizontal transmission, but how these transmission modes differ from corresponding dispersal modes of more saprotrophic fungi is not understood. Root exudates (either inducible or constitutive) constrain growth patterns of fungal species and are a component of host resistance. Whether and how they are degraded, is likely to be important in colonization. Many symbiotic fungi have specialized structures for initial penetration of host tissue. These structures also produce physical, enzymatic and chemical signals that enable the early infection process. Extensive intercellular growth (apolastic growth) may reflect the ability of fungi to avoid the disruption of host cell walls, and so avoid the activation of resistance responses such as by reactive oxygen species, phenols, pathogenesis-related proteins, and phytoalexins. Some symbionts have structures that include the invagination of plant membranes (e.g. haustoria and arbuscules), but such invaginations may also occur in fungi with saprotrophic abilities (e.g. Piriformospora indica). Cell wall thickening is one of the first general responses against pathogen invasion. The ability to avoid or prevent such responses during hyphal penetration may be essential for a symbiotic lifestyle. Some fungi depend on the production of phytotoxins and the ability to degrade plant derived antimicrobial compounds for successful entry. Symbiotic fungi can obtain sugars from the host by either secreting fungal invertases or by being reliant on plant invertases. Fungal invertases are seemingly absent in ectomycorrhizal symbionts. In some fungi, establishment of symbiosis requires effective exchange of resources with the host plant. Gene expression is regulated in fungi based on their location in the host cells, the compounds being transported, and the direction of transport. While such processes are well established in mycorrhizal associations, there is little evidence whether other root symbionts exhibit similar mechanisms of resource exchange. Root fungal symbionts often maintain dual growth in the root and the soil. Allocation of biomass to the extra-radical mycelium and the spatial distribution of hyphae in soil affect the transfer of nutrients. Several morphological “foraging types” have been identified in ectomycorrhizae and are likely in other root symbionts. [60] Lignolytic ability Antibiotic production Palatability Resting structures Dispersal/Transmission mode Degradation of antimicrobial root exudates Penetration structures Ratio of inter- to intracellular colonization Perifungal membrane Induction of host cell wall reinforcements Phytotoxin production and detoxification enzymes Fungal invertases Transporter traits and their expression Extra-radical mycelia and "foraging" pattern. 477 19 [61] [62] [26] [63] [10] [64] [65] [9] [66, 67] [68] [60, 69] [70] [21, 50] [55, 71, 72]