Ecological understanding of root-infecting fungi using trait

advertisement
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. We thank Sarah Hortal, Anna
258
Simonin, Jen Walker, and anonymous reviewers for constructive comments.
259
260
References
261
262
263
264
265
266
267
268
269
270
271
272
273
274
275
276
277
278
279
280
281
282
283
284
285
286
287
288
289
290
291
292
293
294
295
296
297
298
299
300
301
1 van der Putten, W.H., et al. (2013) Plant-soil feedbacks: the past, the present and future
challenges. J. Ecol. 101, 265-276
2 Bever, J.D., et al. (2010) Rooting theories of plant community ecology in microbial
interactions. Trends Ecol. Evol. 25, 468-478
3 Tedersoo, L., et al. (2009) Ascomycetes associated with ectomycorrhizas: molecular diversity
and ecology with particular reference to the Helotiales. Environ. Microbiol. 11, 3166-3178
4 Schulz, B. and Boyle, C. (2005) The endophytic continuum. Mycol. Res. 109, 661-686
5 Sikes, B.A., et al. (2010) Deciphering the relative contributions of multiple functions within
plant-microbe symbioses. Ecology 91, 1591-1597
6 Parbery, D. (1996) Trophism and the ecology of fungi associated with plants. Biological
Reviews 71, 473-527
7 Jumpponen, A. and Trappe, J.M. (1998) Dark septate endophytes: a review of facultative
biotrophic root‐colonizing fungi. New Phytol. 140, 295-310
8 Smith, S.E. and Read, D.J. (2008) Mycorrhizal symbiosis. Academic Press
9 Glazebrook, J. (2005) Contrasting mechanisms of defense against biotrophic and
necrotrophic pathogens. Annu. Rev. Phytopathol. 43, 205-227
10 Rodriguez, R.J., et al. (2009) Fungal endophytes: diversity and functional roles. New Phytol.
182, 314-330
11 Porras-Alfaro, A. and Bayman, P. (2011) Hidden fungi, emergent properties: endophytes
and microbiomes. Annu. Rev. Phytopathol. 49, 291-315
12 He, T., et al. (2012) Fire-adapted traits of Pinus arose in the fiery Cretaceous. New Phytol.
194, 751-759
13 Paine, C.E.T., et al. (2011) Functional traits of individual trees reveal ecological constraints
on community assembly in tropical rain forests. Oikos 120, 720-727
14 Cornwell, W.K., et al. (2008) Plant species traits are the predominant control on litter
decomposition rates within biomes worldwide. Ecol. Lett. 11, 1065-1071
15 Raaijmakers, J.M., et al. (2009) The rhizosphere: a playground and battlefield for soilborne
pathogens and beneficial microorganisms. Plant Soil 321, 341-361
16 Garrett, S.D. (1970) Pathogenic root-infecting fungi.
17 Koide, R.T., et al. (2008) Ectomycorrhizal fungi and the biotrophy–saprotrophy continuum.
New Phytol. 178, 230-233
18 Cullings, K. and Courty, P.E. (2009) Saprotrophic capabilities as functional traits to study
functional diversity and resilience of ectomycorrhizal community. Oecologia 161, 661-664
19 Gilbert, G.S. (2002) Evolutionary ecology of plant diseases in natural ecosystems. Annu. Rev.
Phytopathol. 40, 13-43
20 Jones, J.D. and Dangl, J.L. (2006) The plant immune system. Nature 444, 323-329
21 Fellbaum, C.R., et al. (2012) Carbon availability triggers fungal nitrogen uptake and
transport in arbuscular mycorrhizal symbiosis. Proceedings of the National Academy of
Sciences 109, 2666-2671
22 Peterson, R.L., et al. (2008) Associations between microfungal endophytes and roots: do
structural features indicate function? Botany 86, 445-456
12
302
303
304
305
306
307
308
309
310
311
312
313
314
315
316
317
318
319
320
321
322
323
324
325
326
327
328
329
330
331
332
333
334
335
336
337
338
339
340
341
342
343
344
345
346
347
348
349
350
351
352
353
23 Baldrian, P., et al. (2011) Production of extracellular enzymes and degradation of
biopolymers by saprotrophic microfungi from the upper layers of forest soil. Plant Soil 338,
111-125
24 Duguay, K.J. and Klironomos, J.N. (2000) Direct and indirect effects of enhanced UV-B
radiation on the decomposing and competitive abilities of saprobic fungi. Applied Soil Ecology
14, 157-164
25 Rousk, J. and Bååth, E. (2011) Growth of saprotrophic fungi and bacteria in soil. FEMS
Microbiol. Ecol. 78, 17-30
26 Böllmann, J., et al. (2010) Defensive strategies of soil fungi to prevent grazing by Folsomia
candida (Collembola). Pedobiologia 53, 107-114
27 James, T.Y., et al. (2006) Reconstructing the early evolution of Fungi using a six-gene
phylogeny. Nature 443, 818-822
28 Veldre, V., et al. (2013) Evolution of nutritional modes of Ceratobasidiaceae (Cantharellales,
Basidiomycota) as revealed from publicly available ITS sequences. Fungal Ecology 6, 256-268
29 Andrews, J.H. and Harris, R.F. (2000) The ecology and biogeography of microorganisms on
plant surfaces. Annu. Rev. Phytopathol. 38, 145-180
30 Okubara, P.A. and Paulitz, T.C. (2005) Root defense responses to fungal pathogens: a
molecular perspective. In Root physiology: from gene to function, pp. 215-226, Springer
31 Chesson, P. (2000) Mechanisms of maintenance of species diversity. Annu. Rev. Ecol. Syst.,
343-366
32 Thrall, P.H., et al. (2007) Coevolution of symbiotic mutualists and parasites in a community
context. Trends Ecol. Evol. 22, 120-126
33 Parker, I.M. and Gilbert, G.S. (2007) When there is no escape: The effects of natural
enemies on native, invasive, and noninvasive plants. Ecology 88, 1210-1224
34 Tilman, D. (1997) The influence of functional diversity and composition on ecosystem
processes. Science 277, 1300-1302
35 Diaz, S., et al. (2007) Incorporating plant functional diversity effects in ecosystem service
assessments. Proceedings of the National Academy of Sciences of the United States of America
104, 20684-20689
36 van der Heijden, M.G.A. and Scheublin, T.R. (2007) Functional traits in mycorrhizal ecology:
their use for predicting the impact of arbuscular mycorrhizal fungal communities on plant
growth and ecosystem functioning. New Phytol. 174, 244-250
37 Koide, R.T., et al. (2014) Determining place and process: functional traits of ectomycorrhizal
fungi that affect both community structure and ecosystem function. New Phytol. 201, 433-439
38 Abarenkov, K., et al. (2010) The UNITE database for molecular identification of fungi –
recent updates and future perspectives. New Phytol. 186, 281-285
39 Pérez-Harguindeguy, N., et al. (2013) New handbook for standardised measurement of
plant functional traits worldwide. Aust. J. Bot. 61, 167
40 Jung, V., et al. (2010) Intraspecific variability and trait-based community assembly. J. Ecol.
98, 1134-1140
41 Cordlandwehr, V., et al. (2013) Do plant traits retrieved from a database accurately predict
on-site measurements? J. Ecol. 101, 662-670
42 Kattge, J., et al. (2011) TRY – a global database of plant traits. Global Change Biol. 17, 29052935
43 Neumann, E. and George, E. (2005) Extraction of extraradical arbuscular mycorrhizal
mycelium from compartments filled with soil and glass beads. Mycorrhiza 15, 533-537
44 Camenzind, T. and Rillig, M.C. (2013) Extraradical arbuscular mycorrhizal fungal hyphae in
an organic tropical montane forest soil. Soil Biol. Biochem. 64, 96-102
45 Courty, P.-E., et al. (2006) Laccase and phosphatase activities of the dominant
ectomycorrhizal types in a lowland oak forest. Soil Biol. Biochem. 38, 1219-1222
46 Sobek, E. and Zak, J. (2003) The Soil FungiLog procedure: method and analytical approaches
toward understanding fungal functional diversity. Mycologia 95, 590-602
13
354
355
356
357
358
359
360
361
362
363
364
365
366
367
368
369
370
371
372
373
374
375
376
377
378
379
380
381
382
383
384
385
386
387
388
389
390
391
392
393
394
395
396
397
398
399
400
401
402
403
404
47 Bailly, J., et al. (2007) Soil eukaryotic functional diversity, a metatranscriptomic approach.
The ISME journal 1, 632-642
48 Xu, M., et al. (2013) Elevated CO2 influences microbial carbon and nitrogen cycling. BMC
Microbiol. 13, 124
49 Rinke, C., et al. (2013) Insights into the phylogeny and coding potential of microbial dark
matter. Nature 499, 431-437
50 Hacquard, S., et al. (2013) Laser microdissection and microarray analysis of Tuber
melanosporum ectomycorrhizas reveal functional heterogeneity between mantle and Hartig
net compartments. Environ. Microbiol. 15, 1853-1869
51 Parrent, J.L., et al. (2010) Moving from pattern to process in fungal symbioses: linking
functional traits, community ecology and phylogenetics. New Phytol. 185, 882-886
52 Chagnon, P.L., et al. (2013) A trait-based framework to understand life history of
mycorrhizal fungi. Trends Plant Sci. 18, 484-491
53 Powell, J.R., et al. (2013) A new tool of the trade: plant-trait based approaches in microbial
ecology. Plant Soil 365, 35-40
54 Chase, J.M. and Leibold, M.A. (2003) Ecological niches: linking classical and contemporary
approaches. University of Chicago Press
55 Powell, J.R., et al. (2009) Phylogenetic trait conservatism and the evolution of functional
trade-offs in arbuscular mycorrhizal fungi. Proceedings. Biological sciences / The Royal Society
276, 4237-4245
56 McGill, B.J., et al. (2006) Rebuilding community ecology from functional traits. Trends Ecol.
Evol. 21, 178-185
57 HilleRisLambers, J., et al. (2012) Rethinking Community Assembly through the Lens of
Coexistence Theory. Annual Review of Ecology, Evolution, and Systematics 43, 227-248
58 Hooper, D.U., et al. (2005) Effects of biodiversity on ecosystem functioning: a consensus of
current knowledge. Ecol. Monogr. 75, 3-35
59 Lavorel, S. and Garnier, E. (2002) Predicting changes in community composition and
ecosystem functioning from plant traits: revisiting the Holy Grail. Funct. Ecol. 16, 545-556
60 Mengiste, T. (2012) Plant immunity to necrotrophs. Annu. Rev. Phytopathol. 50, 267-294
61 Eastwood, D.C., et al. (2011) The plant cell wall–decomposing machinery underlies the
functional diversity of forest fungi. Science 333, 762-765
62 Woodward, S. and Boddy, L. (2008) Chapter 7 Interactions between saprotrophic fungi. In
British Mycological Society Symposia Series (Lynne Boddy, J.C.F. and Pieter van, W., eds), pp.
125-141, Academic Press
63 Ritchie, F., et al. (2013) Survival of Sclerotia ofRhizoctonia solaniAG3PT and Effect of SoilBorne Inoculum Density on Disease Development on Potato. J. Phytopathol. 161, 180-189
64 Bais, H.P., et al. (2006) The role of root exudates in rhizosphere interactions with plants and
other organisms. Annu. Rev. Plant Biol. 57, 233-266
65 Oldroyd, G.E. (2013) Speak, friend, and enter: signalling systems that promote beneficial
symbiotic associations in plants. Nat. Rev. Microbiol. 11, 252-263
66 Kemen, E. and Jones, J.D. (2012) Obligate biotroph parasitism: can we link genomes to
lifestyles? Trends Plant Sci. 17, 448-457
67 Lahrmann, U. and Zuccaro, A. (2012) Opprimo ergo sum—Evasion and Suppression in the
Root Endophytic Fungus Piriformospora indica. Mol. Plant-Microbe Interact. 25, 727-737
68 Hematy, K., et al. (2009) Host-pathogen warfare at the plant cell wall. Curr. Opin. Plant Biol.
12, 406-413
69 Pedras, M.S. and Ahiahonu, P.W. (2005) Metabolism and detoxification of phytoalexins and
analogs by phytopathogenic fungi. Phytochemistry 66, 391-411
70 Parrent, J.L., et al. (2009) Friend or foe? Evolutionary history of glycoside hydrolase family
32 genes encoding for sucrolytic activity in fungi and its implications for plant-fungal
symbioses. BMC Evol. Biol. 9, 148
14
405
406
407
71 Lehto, T. and Zwiazek, J. (2011) Ectomycorrhizas and water relations of trees: a review.
Mycorrhiza 21, 71-90
72 Agerer, R. (2001) Exploration types of ectomycorrhizae. Mycorrhiza 11, 107-114
408
409
410
Figure legend:
411
Figure 1. From categorization to trait analysis for root-infecting fungi. 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]
Download