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38-1
I. Introduction
e peripheral root tissues form a morphologically, physically,
and chemically complex microcosm that provides a broad selec-
tion of dierent habitats for a myriad of microorganisms: bac-
teria, actinomycetes, protozoa, nematodes, microalgae, and
fungi. e boundary between roots and soil changes all the time
because roots constantly modify the nearby soil structure by
their mechanical and metabolic activity (Foster etal. 1983). e
rhizoplane, the epidermis, and the outer cortex are colonized
by microorganisms in a nonrandom manner. Heavy microbial
growth can occur on some individual cells, while neighboring
cells are almost devoid of microorganisms (Bowen and Rovira
1976). Patchiness of microbial root colonization probably reects
the uneven distribution of organic debris in the soil, which
serves as food base for the microorganisms. Many soil bacteria
and fungi are able to colonize inter- and or intracellularly the
epidermal and the outer cortical cells (OCO) of healthy roots.
Only a comparatively small number of organisms, for example,
mycorrhizal fungi, endophytes, and pathogens, possess, how-
ever, the ability to cross the inner boundary of the rhizosphere
and to colonize the inner of root tissues (Bazin etal. 1990).
An endophyte is literally dened as one plant living within
another organism. Applying the generally accepted ve-
kingdom system of Whittaker (1969), the term “endomycete”
would, thus, seem more appropriate for a fungus living inter-
nally in a plant. is term is, however, ambiguous because it
may lead to confusion with members of the Endomycetes, a
class introduced by von Arx (1967) to accommodate ascomyce-
tous yeasts and fungi with an yeast like growth phase. De Bary
(1866) coined the term “endophyte” to distinguish organisms
that invade and reside within host tissues or cells from “epi-
phytes,” those fungi living on the outer surfaces of plants.
Various plant/fungus symbioses constitute a continuum from
antagonism to mutualism, and the type of symbiosis may
change over time and space. Diseases caused by highly viru-
lent pathogens or well-developed ectomycorrhizae are imme-
diately obvious also to the nonspecialist, whereas the result
of a plant/fungus association in between these two extremes
may escape observation even by a specialist. e impossibil-
ity to unequivocally dene the behavior of an endophyte as
antagonistic or mutualistic becomes obvious by the ndings
of Freeman and Rodriguez (1993) who observed a fungal plant
pathogen to convert to a nonpathogenic, endophytic mutual-
ist by mutation at a single locus. us, a pragmatic denition
of endophytism should be applied, which includes all organ-
isms located within apparently healthy, functional root tissues
at the moment of sample collection. e currently available
methods to detect endophytes are destructive and, thus, the
addendum “at the moment of sample collection” was necessary
to account for the dynamic nature of plant–fungus interac-
tions. Only fungi will be considered in this chapter although
bacteria can live endophytically too (Chanway 1996; Schulz
et al. 2006). Endophytic bacteria have been shown to be of
vital importance in some symbioses, for example, actinorhi-
zal symbiosis between tree roots (Alnus spp.) and Frankia spp.,
symbiosis between sugarcane (Saccharum ocinarum L.) and
Acetobacter diazotrophicus, a nitrogen-xing bacterial endo-
phyte (Dong etal. 1994), or plant growth–promoting rhizo-
bacteria (Wei etal. 1994). e fungal partners in mycorrhizal
associations are clearly also endophytes because part or all
of their thallus is localized within the roots. Comprehensive
articles, reviews, and books have been provided for many of
38
Fungal Root Endophytes
I. Introduction ...........................................................................................................................38-1
II. Species and Hosts of Root Endophytes ..............................................................................38-2
Dark Septate Endophytes
III. Methods of Detection........................................................................................................... 38-4
IV. Root Endophytes of Herbaceous Plants .............................................................................38-5
Grass Endophytes • Orchid Endophytes • Other Herbaceous Plant Hosts
V. Root Endophytes of Woody Plant Species .......................................................................38-22
Root Endophytes of Woody Ericales • Root Endophytes of Pinales • Root Endophytes
in Other Woody Plant Species
VI. Conclusions and Outlook ...................................................................................................38-38
References .........................................................................................................................................38-38
Thomas N. Sieber
ETH (Swiss FederalInstitute
of Technology)
Christoph R. Grünig
Microsynth AG
© 2013 by Taylor & Francis Group, LLC
38-2 Root–Rhizosphere Interactions
the groups of classical mycorrhizal associations, namely,
ecto-(ECM), ectendo-(EEM), or arbuscular mycorrhizae (AM)
and the ericoid, arbutoid, orchid, or monotropoid mycorrhi-
zae (Harvais and Hadley 1967; Read 1983; Mikola 1988; Allen
etal. 1991; Egger etal. 1991; Allen and Allen 1992; Currah and
Zelmer 1992; Read 1992, 1996; Brundrett 2004; Smith and
Read 2008; Brundrett 2009). Emphasis in this chapter will
be laid on root–fungus associations that are not regarded as
mycorrhizae in the classical sense although literally they also
form “fungus–root” entities of tightly interwoven fungus-
plant tissues. Fungal root endophytes are ubiquitous and prob-
ably more abundant than classical mycorrhizae because they
are not conned to the root tips and can occur everywhere
in the root system. ey are regularly isolated during studies
about classical mycorrhizae but are then rather regarded as
nuisance than interesting research objects. Since fungal root
endophytes have been largely neglected, information about
their functions is rare. Aer all, the number of publications
about fungal root endophytes started to increase exponentially
since about a decade ago, and there is hope that this group of
organisms will eventually obtain the attention it deserves. In
addition to mycorrhizae, root-colonizing obligate biotrophs
with a prolonged latent phase such as certain smuts (Garcia-
Guzman etal. 1996) or rust fungi, that is, Tranzschelia fusca
(G. Winter) Dietel in the rhizomes of Anemone nemorosa L.,
will not be discussed in this chapter.
is chapter is based in part upon information in several
previous reviews (which it does not supersede): (Melin 1923;
Pearson and Read 1973; Garrett 1981; Foster etal. 1983; Read
1983; Wilcox 1983; Duddrige 1985; Foster 1986; Deacon 1987;
Bazin et al. 1990; Petrini 1991; Newell 1992; Cannon and
Hawksworth 1995; Bills 1996; Wilcox 1996; Jumpponen
andTrappe 1998a; Sieber 2002; Addy etal. 2005; Mandyamand
Jumpponen 2005; Sieber and Grünig 2006; Grünig etal. 2008b;
Peterson etal. 2008; Newsham etal. 2009). Our referencing
is not comprehensive, but we tried to include key references
that can provide access to more literature on fungal root endo-
phytes. In this chapter, we will concentrate on the taxonomy,
diversity, physiology, and ecology of root endophytes and con-
clude with some ideas about interesting avenues for future
research. Nomenclature of fungal names follows the system
applied in the Index Fungorum (http://www.indexfungorum.
org/Names/Names.asp). If both the teleomorph (sexual repro-
ductive stage) and the anamorph (asexual reproductive stage)
are produced, the name of the teleomorph will be used. Names
of the anamorph(s) can be retrieved from the list of synonyms
provided for teleomorphs with known anamorph(s) in the
Index Fungorum.
Morphology of the endophyte–root symbioses is very variable
and changes over time. It depends on both host and endophyte
species; developmental stage of the tree, type, and age of the
roots; edaphic and climatic conditions; and the microbial com-
munity in the rhizosphere. Sections IV.A1, IV.B1, IV.C1, V.A1,
V.B1, and V.C1 about the histology of the endophyte–root inter-
face will be included into this chapter of each host taxon.
II. Species and Hosts
ofRoot Endophytes
Endophytic fungi were detected in the roots of all examined
plant species. Grasses, orchids, and species of the Ericaceae and
Pinaceae are the best-studied plants (Figure 38.1). Diversity, fre-
quency, and population density of endophyte species depend
on the edaphic and climatic conditions, on the heterogeneity of
habitats and niches present within the host tissues, and on the
competing organisms. Dark septate endophytes (DSE) probably
occur in the roots of any plant species. ey are the most fre-
quent and most widespread root endophytes (Stoyke etal. 1992;
Ahlich and Sieber 1996; Jumpponen and Trappe 1998a; Grünig
etal. 2008b; Figure 38.1). Species of Cylindrocarpon, Fusarium,
Gibberella, Ilyonectria, and Neonectria and the Sebacinales are
frequent non-DSE. Fungi of the Sebacinales form mycorrhizae
with ECM plants and orchids (OM) and associations of uncertain
status with many other plant species (Warcup 1988; Weiss and
Oberwinkler 2001; Weiss etal. 2011). e genera Microdochium
and Cryptosporiopsis comprise both DSE and non-DSE species.
Microdochium nivale (Fr.) Samuels & I.C. Hallett (anamorph of
Monographella nivalis (Schanit) E. Müll.) and Microdochium
bolleyi (R. Sprague) de Hoog & Herm.-Nijh. are both endophytes
in grasses, but colonies of M. nivale are white changing to orange
where sporodochia form, whereas those of M. bolleyi are black.
A. Dark Septate Endophytes
DSE is a form taxon and serves primarily to dierentiate these
fungi from endophytes with septate, hyaline hyphae and from
fungi with sparsely septate, hyaline hyphae, which are character-
istic for AM fungi. However, the distinction based on the degree
of pigmentation is oen arbitrary because melanization varies
greatly in some species (Addy etal. 2005; Hambleton and Sigler
2005) especially that of mycelia in colonized roots (Yu etal. 2001;
Barrow 2003). We propose to dene DSE as those endophytic
fungi, which form either at least partly dark brown, dark gray, or
black colonies on 2% (w/v) malt extract agar (MEA) when incu-
bated at 20°C and/or distinctly melanized structures in roots.
Most DSE are ascomycetes, and consequently dematiaceous
ascomycetes that are able to colonize the interior of plant tissues
without inducing disease are potential DSE. However, the most
frequent root-colonizing DSE belong to the genera Microdochium
(anamorphic Monographella (Xylariales)), Periconia (anamor-
phic Pleosporales), Harpophora (anamorphic Gaeumannomyces),
Cadophora (anamorphic Helotiales), Cryptosporiopsis (anamor-
phic Pezicula (Helotiales)), Phialocephala, and Acephala (both
anamorphic Helotiales) (Figure 38.1). Some of the best-studied
DSE are Microdochium bolleyi, Periconia macrospinosa Lefebvre
& Aar.G. Johnson, Gaeumannomyces and Harpophora species,
Acephala applanata Grünig & T.N. Sieber, and Phialocephala
fortinii s.l. C.J.K. Wang& H.E. Wilcox. P. fortinii s.l. consists of
several morphologically indistinguishable but reproductively iso-
lated cryptic species (CSP) (Grünig 2004; Grünig etal. 2007) that
together with A. applanata form the P. fortinii s.l.–A. applanata
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38-3Fungal Root Endophytes
species complex (PAC) (Grünig etal. 2008b). PAC are among the
best-characterized DSE. ey are very widespread and abundant
in roots of woody plants, especially conifers and ericaceous plants,
all over the Northern Hemisphere (Tables 38.4 through 38.6).
Section II.A1 is therefore dedicated to them (see below).
Host specicity of DSE is the exception, but some species pre-
fer certain host taxa. Microdochium, Periconia, and Harpophora
species prefer grasses, whereas Cadophora, Cryptosporiopsis,
and PAC species preferentially occur on orchids and woody
plant species (Grünig etal. 2008b; Figure 38.1). PAC seem to be
conned to forest ecosystems because reports about their pres-
ence in arable soils or in roots of plants growing in these soils are
very rare (Ahlich-Schlegel 1997; Brenn etal. 2008).
1. Phialocephala fortinii s.l.–Acephalaapplanata
Species Complex
A. applanata is the only morphologically distinct PAC species,
because its colonies on MEA dier from those of Phialocephala
fortinii s.l. by the absence of aerial mycelium (Grünig and Sieber
2005). e structures of conidiophores are similar among spe-
cies and highly variable within species and, consequently, do not
allow to discriminate species (Grünig etal. 2008a). Dierentiation
of PAC species is only possible using molecular methods. Seven
of the Phialocephala fortinii s.l. species were formally described
based on population dierentiation and dierences at ve
sequence loci (Grünig etal. 2007, 2008a): Phialocephala fortinii
s.s., Phialocephala subalpina, Phialocephala letzii Grünig &
T. N. Sieber, Phialocephala uotilensis Grünig & T. N. Sieber,
Phialocephala turicensis Grünig & T. N. Sieber, Phialocephala
europaea Grünig & T.N. Sieber, and Phialocephala helvetica
Grünig & T.N. Sieber. Identication of members of PAC is pos-
sible using ITS sequencing (Grünig etal. 2008b). However, species
identication within PAC to the species level requires sequencing
of at least three of the sequence loci (Grünig etal. 2008a). Usually,
sequencing of the pPF-076, pPF-018, and beta-tubulin locus using
the primers listed in Grünig etal. (2007) is enough to identify
the species. Alternatively, identication can occur by multiplex-
polymerase-chain-reaction (PCR)-amplied microsatellite (MS)
loci using the primers developed by Queloz etal. (2008, 2010).
e geographical distribution of PAC species ranges from arc-
tic to subtropical regions throughout the Northern Hemisphere
(Piercey etal. 2004; Zhang etal. 2009; Queloz etal. 2011). e
wide geographic distribution of PAC contrasts with the results
obtained from baiting experiments, which provided no evidence
for aerial dispersal of PAC (Bachmann 2010). Nevertheless,
strains with identical inter-simple sequence repeats (ISSR) nger-
print and single-copy restriction fragment length polymorphism
(RFLP) haplotype were repeatedly found in forest stands situated
a few km apart, and migration rates measured between conti-
nents were low but still sucient to prevent speciation (Grünig
etal. 2004, 2011; Grünig and Sieber 2005; Queloz 2010). is is at
least surprising, since PAC do not or only rarely sporulate aer
prolonged incubation at low temperature, and germination of
conidia was never observed. Probably, anthropogenic gene and
genotype ow occurs by the movement of nursery plants colo-
nized by PAC locally and around the globe (Brenn etal. 2008).
Herbaceous plants
Others
Woody plants
Ericaceae
Poaceae
Others
DSE
PAC
Cadophora spp.
Pezicula spp.
Cryptosporiopsis spp.
Ilyonectria spp.
Neonectria spp.
Cylindrocarpon spp.
Microdochium spp.
Periconia
macrospinosa
Gibberella spp.
Fusarium spp.
Gaeumannomyces spp.
Harpophora spp.
Sebacinales
Pinaceae
non-DSE
Orchidaceae
FIGURE 38.1 Simplied schematic display of the main taxa of root endophytes and the major groups of their plant hosts. e black upper box
indicates occurrence of DSE, the blank lower box occurrence of non-DSE; species of taxa positioned in the black box are DSE, those in the blank
box non-DSE; the genera Microdochium and Pezicula (Cryptosporiopsis) comprise both DSE and non-DSE species.
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38-4 Root–Rhizosphere Interactions
Abundance distribution curves of PAC species in local com-
munities are hyperbolic with a few abundant species and many
“rare” species (Grünig et al. 2006), consistent with the com-
munity structures observed in many other biological systems
(McGill et al. 2007). In a recent study, 44 communities from
the Northern Hemisphere comprising more than 5000 PAC
strains were analyzed (Queloz et al. 2011). Species diversity
and community structure were neither correlated with the tree
community, geographical location, soil properties, manage-
ment practices, precipitation, nor temperature, supporting the
hypothesis of “everything is everywhere” (Baas-Becking 1934).
Indeed, it is known that host specicity of PAC species is low or
lacking because most species can be isolated from a broad range
of woody plant species (Grünig etal. 2008b). For example, the
most abundant PAC species, Phialocephala subalpina Grünig
& T.N. Sieber, was isolated from 16 plant species compared
to many fungal pathogens that oen have narrow host ranges
(Tables 38.4 through 38.6).
PAC species were shown to be a genetically highly variable on
a regional level (Harney etal. 1997; Grünig etal. 2001). Within
forest plots of 200 m
2
, PAC can form communities of up to 13
sympatrically occurring species (Grünig et al. 2004; Queloz
etal. 2010). More than 25 genets were present in an area of only
9 m
2
of forest soil, and this community remained stable for sev-
eral years (Queloz etal. 2005). More homogenous population
structures would be expected for these supposedly mitotic PAC
fungi. ere are at least two possibilities to explain this phe-
nomenon. Either the assumption of asexuality is wrong, and
PAC enjoy some hidden sex such as parasexuality, or it is a poly-
phyletic species complex, and what we see today is the result of
a convergent evolutionary process. From a molecular genetics
point of view, PAC meet the requirements for sex, because they
possess mating-type genes (Zaarano etal. 2010), and probably,
they are also functional because no gametic disequilibrium
can be found in PAC species based on single-copy RFLP data
(Grünig etal. 2007). Whereas mating-type genes of Acephala
applanata are organized in a homothallic fashion (MAT1-1 and
MAT1-2 in the same individual interrupted by a transposable
element), other PAC species are heterothallic possessing only
either the MAT1-1 or MAT1-2 idiomorph in their genomes
(Zaarano et al. 2010, 2011). Zaarano et al. (2010) showed
that in more than 80% of the populations of PAC species a 1:1
mating-type ratio and gametic equilibrium can be observed.
In addition, MAT genes were shown to evolve under strong
purifying selection. All three observations support the assump-
tion that cryptic sexual reproduction occurs in PAC species.
Moreover, the presence of sexual reproduction is also supported
by the nding of the teleomorphic state in Phaeomollisia piceae
T.N. Sieber & Grünig, a phylogenetically closely related species
(Grünig etal. 2009).
Another secret is whether PAC fungi are able to grow
through soil. PAC can readily be baited from forest soil using
Norway-spruce seedlings as bait (Ahlich et al. 1998; Trüssel
2011). However, it is not known if PAC actively grow through
soil toward host roots or are passively waiting as dormant
propagules, for example, microsclerotia in or on root debris,
until a susceptible root “grows past.” Trüssel (2011) tested myce-
lial growth through soil substrate in nonsterilized and gamma-
sterilized forest soil and peat–vermiculite. Norway-spruce
seedlings were used as bait separated from the PAC inoculated
substrate by a mesh screen that did not allow passage of roots.
Growth of mycelium occurred only in the sterilized substrates
and was slow with maximal distances of 2 cm covered in 3
months at 20°C, although the pH of 3.8 was optimal (Trüssel
2011). No growth occurred in nonsterilized forest soil probably
due to inhibition by other soil microorganisms. us, it remains
dubious if PAC can actively grow through soil or are transmitted
only by root contacts.
III. Methods of Detection
Isolation from plant tissues (1), histological examination (2),
assays of fungal-specic molecules, for example, ergosterol,
a sterol characteristic of fungal membranes (3), and culture-
independent DNA extraction and sequencing of specic loci
(4) are the four major groups of methods used to detect and
describe communities of endophytic fungi (Parsons 1981;
Savage and Sall 1981; El-Nashaar et al. 1986; Newell et al.
1988; Hampton etal. 1990; Newell 1992; Reissinger etal. 2001;
Sieber 2002; Schulz and Boyle 2005; Jumpponen and Jones
2009). Each of these methods has its advantages and disad-
vantages. Methods (1) and (4) but not (2) and (3) allow iden-
tication of the fungi. Only culturable fungi can be detected
with method (1), and the number and kind of species retrieved
depend on the strength of surface sterilization, the medium
used for incubation, and the sample size. With method (4),
it remains obscure whether the DNAs originated from liv-
ing or dead fungi, and consequently, the surface-sterilization
method used in combination with method (4) must not only
kill organisms on the plant surface but also remove their DNA.
Furthermore, method (4) strongly depends on the quality of
the databases used for sequence identication. Consequently,
only the application of several of these methods combined
allows obtaining a complete picture of the endophytic myco-
biota in a plant tissue.
Methods were developed to specically detect certain spe-
cies. Quantitative PCR was developed to detect and quantify
PAC in root tissues (Tellenbach etal. 2010). Quantication by
qPCR is, however, problematic because the amount of DNA is
measured and used to estimate biomass. Even if it is assumed
that each cell contains one nucleus, type and size of fungal cells
can vary considerably within and among isolates making esti-
mates inaccurate. For example, the method worked ne for PAC
strains that formed uniform, regular mycelia in the host but not
for those that produced lots of microsclerotia (Tellenbach etal.
2010). Although based on DNA, microsatellites provide an even
more sensitive detection and quantication method because
genets of the same species can be dierentiated and quantied
provided that genets possess dierent alleles at at least one locus
(Reininger etal. 2011b).
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38-5Fungal Root Endophytes
IV. Root Endophytes of
Herbaceous Plants
Agricultural plants are among the best-studied herbaceous
plants in regard to root endophytes. Nonagricultural herbaceous
plants have only rarely been examined, and the detection of non-
mycorrhizal root endophytes was mostly a by-product during
studies of OM or AM fungi.
A. Grass Endophytes
Members of the Clavicipitaceae are the best-known grass
endophytes. They have received a lot of attention in the past
due to their beneficial effects upon their hosts (Clay 1988;
Schardl 2010). Some function as biocontrol agents against
insects and other herbivores, others produce growth-pro-
moting metabolites. Most effects are based on various kinds
of alkaloids produced by these endophytes. Clavicipitaceous
grass endophytes are considered to colonize their hosts sys-
temically. However, roots are usually not colonized. Azevedo
and Welty (1995) inoculated axenically grown tall fescue
(Festuca arundinacea Schreb.) seedlings with Neotyphodium
coenophialum (Morgan-Jones & W. Gams) Glenn, C.W.
Bacon & Hanlin but could not observe direct penetration
of the fungus into intact root cortex cells. Consequently,
improved growth and biomass accumulation of roots as well
as altered root morphology of infected plants grown at low
nutrient availability (e.g., phosphorus) are mediated by the
endophyte activity in the aerial plant parts (Malinowski
etal. 1998; Malinowski and Belesky 1999). However, roots of
grasses are habitats for many non-clavicipitalean endophytes
(Table 38.1).
e most frequent genera of grass-root endophytes are
Fusarium, Gaeumannomyces, Gibberella, Harpophora,
Microdochium, Monographella, and Periconia (Figure 38.1).
For example, Riesen and Sieber (1985) and Sieber etal. (1988)
isolated more than 100 species from roots of winter wheat.
Fusarium culmorum (W.G. Sm.) Sacc., Fusarium oxysporum
Schltdl., Gibberella zeae (Schwein.) Petch, Microdochium bol-
leyi, Monographella nivalis, Periconia macrospinosa Lefebvre
& Aar.G. Johnson, and Phaeosphaeria nodorum (E. Müll.)
Hedjar., the causal agent of glume blotch, were the dominant
fungal species. M. bolleyi was also regularly recovered from the
roots of healthy eld-grown barley (Hordeum vulgare L.), oats
(Avena sativa L.), and pasture grass (Murray and Gadd 1981).
Stoyke and Currah (1991) isolated DSE from an unidenti-
fied grass species in an alpine habitat of the Rocky Mountains
in Alberta, Canada. Similarly, dark septate endophytic
hyphae were observed in grasses collected on various islands
of the Southern Atlantic Ocean and the Antarctic Peninsula
(Christie and Nicolson 1983), and Upson et al. (2009) iso-
lated 243 DSE strains from the roots of Deschampsia ant-
arctica E. Desv. and Colobanthus quitensis (Kunth) Bartl.
(Caryophyllaceae) collected from 17 sites across a 1470 km
transect through maritime and sub-Antarctica. Most DSE
belonged to the Helotiales. Leptodontidium orchidicola Sigler
& Currah, Pezoloma ericae (D.J. Read) Baral, and species
of Tapesia and Mollisia could be identified by ITS sequence
comparison. Li etal. (2005) detected considerable coloniza-
tion of roots of several grass species collected in Kunming,
China, by DSE.
Grass and cereal roots are often colonized by dark sep-
tate Gaeumannomyces species and relatives. Take-all, caused
by Gaeumannomyces graminis var. tritici J. Walker and
Gaeumannomyces graminis var. avenae (E.M. Turner) Dennis,
is the most important root disease of wheat and oat world-
wide (Freeman and Ward 2004), but many Gaeumannomyces
species are nonpathogenic (Deacon 1981; Sieber 1985; Deacon
1987; Skipp and Christensen 1989; Blaschke 1991; Crous etal.
1995; Gutteridge etal. 2007). Gaeumannomyces species pos-
sess Phialophora-like anamorphs, which have been accom-
modated in the genus Harpophora by Gams (2000). Whereas
it is accepted that Harpophora graminicola (Deacon) W. Gams
is the anamorph of Gaeumannomyces cylindrosporus Hornby,
Slope, Gutter. & Sivan. (Ward and Bateman 1999; Freeman and
Ward 2004), there is some debate about other Harpophora–
Gaeumannomyces connections, especially when it comes to
the anamorphs of the various varieties of G. graminis (Sacc.)
Arx & D.L. Olivier. A Harpophora species isolated by McKeen
(1952) from corn roots was described as Harpophora radicic-
ola (Cain) W. Gams by Cain (1952). Some workers interpreted
H. radicicola as the anamorphic state of G. graminis var.trit-
ici (Lemaire and Ponchet 1963; Simonsen 1971). However, this
was considered not tenable by Walker (1981). In fact, identity
of H. radicicola with Gaeumannomyces graminis var. maydis
J.M. Yao, Yong C. Wang & Y.G. Zhu, the maize take-all fungus
from China (Yao etal. 1992), was demonstrated using molec-
ular genetics methods (Ward and Bateman 1999). In addition,
the same authors found H. radicicola to be almost identical to
Harpophora zeicola (Deacon & D.B. Scott) W. Gams, which
was described as a weak parasite of drought or otherwise
stressed maize plants in South Africa and France (Deacon
and Scott 1983). G. graminis var. maydis was also observed
in the roots of three alpine grasses (Deschampsia caespitosa
(L.) P. Beauv., Festuca pumila Chaix, and Poa alpina L.) grow-
ing at timberline (1900 m asl.) in Bavaria (Blaschke 1991).
Colonization of roots of Deschampsia flxuosa (L.) Trin. by
an unidentified DSE increased with increasing temperature
under a global warming scenario but was not affected by ele-
vated CO
2
levels (Olsrud etal. 2010; Table 38.1).
1. Anatomy
Epidermal and cortical root cells of cereal and grass roots lled
with heavily melanized microsclerotia are characteristic for
colonization by M. bolleyi (Murray and Gadd 1981). In con-
trast, inter- and intracellular hyphae of this fungus are hyaline.
Colonization of the stelar tissues of healthy roots does usually not
occur. ese patterns of colonization correspond well with those
observed by Rasmann etal. (2009) for M. bolleyi in tomato roots
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38-6 Root–Rhizosphere Interactions
TABLE 38.1 Endophytes in Grasses (Family: Poaceae), Sedges (Family: Cyperaceae) and Bromeliads (Family: Bromeliaceae)
Endophyte Host
Type of
Experiment
b
Special
Eect
c
ReferencesGenus
a
Species
a
Fungus Order
a
DSE/Not DSE Species Plant Order
Woody/
Herbaceous
Acremonium sp. Hypocreales Not DSE Holcus lanatus Poales Grass Isol Sánchez Márquez etal. (2010)
Acremonium strictum Hypocreales Not DSE Ammophila arenaria Poales Grass In vitro exp a Hol etal. (2007)
Alternaria sp. Pleosporales DSE Bouteloua gracilis Poales Grass Isol Herrera etal. (2010)
Alternaria sp. Pleosporales DSE Holcus lanatus Poales Grass Isol Sánchez Márquez etal. (2010)
Aspergillus sp. Eurotiales Not DSE Stipa grandis Poales Grass Isol Su etal. (2010)
Bipolaris sp. Pleosporales DSE Bouteloua gracilis Poales Grass Isol Herrera etal. (2010)
Campanella sp. Agaricales DSE Bouteloua gracilis Poales Grass Isol Herrera etal. (2010)
Chaetomium funicola Sordariales Not DSE Hordeum vulgare Poales Grass In vitro exp b Vilich etal. (1998)
Chaetomium globosum Sordariales Not DSE Hordeum vulgare Poales Grass In vitro exp b Vilich etal. (1998)
Cladorrhinum foecundissimum Sordariales N.A. Elytrigia repens Poales Grass Isol & in
vitro exp
c Gasoni and Stegamn de
Gurnkel (2009)
Cladosporium cladosporiodes Capnodiales DSE Bothriochloa macra Poales Grass Isol White and Backhouse (2007)
Cladosporium cladosporiodes Capnodiales DSE Hyparrhenia hirta Poales Grass Isol White and Backhouse (2007)
Coniothyrium sp. Pleosporales Not DSE Triticum aestivum Poales Grass Isol Crous etal. (1995)
Cryptosporiopsis rhizophila Helotiales DSE Deschampsia exuosa Poales Grass In vitro exp d Zijlstra etal. (2005)
Curvularia inaequalis Pleosporales DSE Holcus lanatus Poales Grass Isol Sánchez Márquez etal. (2010)
Cylindrocarpon didymum Hypocreales Not DSE Triticum aestivum Poales Grass Isol Sieber (1985)
Dictyochaeta fertilis Chaetosphaeriales Not DSE Lolium perenne Poales Grass Isol Skipp and Christensen (1989)
Drechslera sp. Pleosporales DSE Holcus lanatus Poales Grass Isol Sánchez Márquez etal. (2010)
Embellisia chlamydospora Pleosporales DSE Carex stenophylla Poales Sedge Isol Graf, pers. comm. (2008)
Epicoccum sp. Pleosporales Not DSE Holcus lanatus Poales Grass Isol Sánchez Márquez etal. (2010)
Fusarium culmorum Hypocreales Not DSE Triticum aestivum Poales Grass Isol Sieber etal. (1988)
Fusarium oxysporum Hypocreales Not DSE Bothriochloa macra Poales Grass Isol White and Backhouse (2007)
Fusarium oxysporum Hypocreales Not DSE Holcus lanatus Poales Grass Isol Sánchez Márquez etal. (2010)
Fusarium oxysporum Hypocreales Not DSE Hyparrhenia hirta Poales Grass Isol White and Backhouse (2007)
Fusarium oxysporum Hypocreales Not DSE Lolium perenne Poales Grass Isol Skipp and Christensen (1989)
Fusarium oxysporum Hypocreales Not DSE Oryza sativa Poales Grass Isol Fisher and Petrini (1992)
Fusarium oxysporum Hypocreales Not DSE Stipa grandis Poales Grass Isol Su etal. (2010)
Fusarium redolens Hypocreales Not DSE Stipa grandis Poales Grass Isol Su etal. (2010)
Fusarium sp. Hypocreales DSE Bouteloua gracilis Poales Grass Isol Herrera etal. (2010), Khidir
etal. (2010)
Fusarium sp. Hypocreales DSE Sporobolus cryptandrus Poales Grass Isol Khidir etal. (2010)
Fusarium spp. Hypocreales Not DSE Stipa grandis Poales Grass Isol Su etal. (2010)
Gaeumannomyces cylindrosporus
d
Magnaporthaceae DSE Poa pratensis Poales Grass Isol Saleh and Leslie (2004)
Gaeumannomyces cylindrosporus
d
Magnaporthaceae DSE Various grass species Poales Grass Isol e Deacon (1981)
Gaeumannomyces cylindrosporus
d
Magnaporthaceae DSE Vulpia ciliata Poales Grass In vitro exp f Newsham (1999)
Gaeumannomyces graminis var.
graminis
Magnaporthaceae DSE Oryza sativa Poales Grass Isol Saleh and Leslie (2004)
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38-7Fungal Root Endophytes
Gaeumannomyces graminis var.
maydis
e
Magnapothaceae DSE Lolium perenne Poales Grass Isol Skipp and Christensen (1989)
Gaeumannomyces graminis var.
maydis
e
Magnaporthaceae DSE Zea mays Poales Grass Isol Cain (1952)
Gaeumannomyces graminis var.
maydis
e
Magnaporthaceae DSE Zea mays Poales Grass Isol Ward and Bateman (1999)
Gaeumannomyces sp. Magnaportaceae DSE Bouteloua gracilis Poales Grass Isol Herrera etal. (2010)
Gibberella avenacea Hypocreales Not DSE Triticum aestivum Poales Grass Isol Crous etal. (1995)
Gibberella zeae Hypocreales Not DSE Triticum aestivum Poales Grass Isol Sieber etal. (1988)
Harpophora oryzae Magnaporthaceae DSE Oryza sativa Poales Grass Isol Yuan etal. (2010)
Idriella lunata Helotiales Not DSE Stipa grandis Poales Grass Isol Su etal. (2010)
Ilyonectria radicicola Hypocreales Not DSE Triticum aestivum Poales Grass Isol Sieber (1985)
Leptodontidium sp. Helotiales Not DSE Holcus lanatus Poales Grass Isol Sánchez Márquez etal. (2010)
Meliniomyces variabilis
LtVB3
Leotiomycetes DSE Hordeum vulgare Poales Grass Isol Narisawa etal. (2004)
Microdochium bolleyi Xylariales DSE Elymus farctus Poales Grass Isol Sánchez Márquez etal. (2008)
Microdochium bolleyi Xylariales DSE Poa alpigena Poales Grass Isol Väre etal. (1992)
Microdochium bolleyi Xylariales DSE Triticum aestivum Poales Grass Isol Sieber etal. (1988)
Microdochium bolleyi Xylariales DSE Triticum aestivum Poales Grass In vitro &
eld exp
g Reinecke (1978)
Microdochium bolleyi Xylariales DSE Triticum aestivum Poales Grass Isol Riesen and Sieber (1985)
Microdochium bolleyi Xylariales DSE Triticum aestivum Poales Grass In vitro exp h Kirk and Deacon (1987)
Microdochium sp. Xylariales DSE Andropogon gerardii Poales Grass In vitro exp i Mandyam etal. (2010)
Microdochium sp. Xylariales DSE Bouteloua gracilis Poales Grass Isol Herrera etal. (2010)
Microdochium sp. Xylariales DSE Grasses Poales Grass Isol Mandyam etal. (2010)
Microdochium spp. Xylariales DSE Stipa grandis Poales Grass Isol Su etal. (2010)
Mollisia sp. Helotiales DSE Deschampsia antarctica Poales Grass Isol Upson etal. (2009)
Moniliophthora sp. Agaricales DSE Bouteloua gracilis Poales Grass Isol Herrera etal. (2010), Khidir
etal. (2010)
Moniliophthora sp. Agaricales DSE Sporobolus cryptandrus Poales Grass Isol Khidir etal. (2010)
Monodictys sp. Dothideomycetes DSE Carex stenophylla Poales Sedge Isol Graf, pers. comm. (2008)
Monographella nivalis Xylariales Not DSE Triticum aestivum Poales Grass Isol Sieber etal. (1988)
Monographella nivalis Xylariales Not DSE Triticum aestivum Poales Grass Isol Sieber etal. (1988)
Monosporascus sp. Xylariales Not DSE Stipa grandis Poales Grass Isol Su etal. (2010)
Neurospora sp. Sordariales Not DSE Stipa grandis Poales Grass Isol Su etal. (2010)
Paraphaeosphaeria sp. Pleosporales DSE Bouteloua gracilis Poales Grass Isol Herrera etal. (2010), Khidir
etal. (2010)
Paraphaeosphaeria sp. Pleosporales DSE Sporobolus cryptandrus Poales Grass Isol Khidir etal. (2010)
Paraphoma meti Pleosporales DSE Vulpia ciliata Poales Grass In vitro exp f Newsham (1994)
Penicillium sp. Eurotiales Not DSE Holcus lanatus Poales Grass Isol Sánchez Márquez etal. (2010)
Penicillium sp. Eurotiales Stipa grandis Poales Grass Isol Su etal. (2010)
Periconia macrospinosa Pleosporales DSE Andropogon gerardii Poales Grass In vitro exp j Mandyam etal. (2010)
(continued)
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38-8 Root–Rhizosphere Interactions
TABLE 38.1 (continued) Endophytes in Grasses (Family: Poaceae), Sedges (Family: Cyperaceae) and Bromeliads (Family: Bromeliaceae)
Endophyte Host
Type of
Experiment
b
Special
Eect
c
ReferencesGenus
a
Species
a
Fungus Order
a
DSE/Not DSE Species Plant Order
Woody/
Herbaceous
Periconia macrospinosa Pleosporales DSE Bothriochloa macra Poales Grass Isol White and Backhouse (2007)
Periconia macrospinosa Pleosporales DSE Holcus lanatus Poales Grass Isol Sánchez Márquez etal. (2010)
Periconia macrospinosa Pleosporales DSE Hyparrhenia hirta Poales Grass Isol White and Backhouse (2007)
Periconia macrospinosa Pleosporales DSE Stipa grandis Poales Grass Isol Su etal. (2010)
Periconia macrospinosa Pleosporales DSE Andropogon gerardii Poales Grass In vitro exp k Mandyam etal. (2010)
Periconia macrospinosa Pleosporales DSE Grasses Poales Grass Isol Mandyam etal. (2010)
Periconia macrospinosa Pleosporales DSE Holcus lanatus Poales Grass Isol Sánchez Márquez etal. (2010)
Periconia sp. Pleosporales DSE Bouteloua gracilis Poales Grass Isol Herrera etal. (2010)
Phaeocytostroma plurivorum Pezizomyc incert N.A. Stipa grandis Poales Grass Isol Su etal. (2010)
Phaeosphaeria nodorum Pleosporales Not DSE Triticum aestivum Poales Grass Isol Sieber etal. (1988)
Phaeosphaeria nodorum Pleosporales Not DSE Triticum aestivum Poales Grass Isol Sieber etal. (1988)
Phialocephala fortinii s.l. Helotiales DSE Deschampsia exuosa Poales Grass Isol Tejesvi and Ruotsalainen (2010)
Phialocephala fortinii s.l. Helotiales DSE Deschampsia exuosa Poales Grass In vitro exp l Zijlstra etal. (2005)
Phialocephala fortinii s.l. Helotiales DSE Poa alpigena Poales Grass Isol Väre etal. (1992)
Phialocephala fortinii s.l. Helotiales DSE Poa alpigena Poales Grass Isol Väre etal. (1992)
Phialocephala sp. 8 Helotiales DSE Carex aquatilis Poales Sedge Isol Grünig etal. (2009)
Phialophora sp. N.A. DSE Carex curvula Poales Sedge Isol Haselwandter and Read (1982)
Phialophora sp. N.A. DSE Carex rma Poales Sedge Isol f Haselwandter and Read (1982)
Phialophora sp. Helotiales N.A. Deschampsia exuosa Poales Grass Isol Tejesvi and Ruotsalainen (2010)
Phialophora sp. Helotiales N.A. Stipa grandis Poales Grass Isol Su etal. (2010)
Phialophora sp. 1 Helotiales DSE Triticum aestivum Poales Grass Isol Rooden, unpublished
Phialophora sp. 1 Helotiales DSE Triticum aestivum Poales Grass Isol Rooden, unpublished
Phoma sp. Pleosporales DSE Bouteloua gracilis Poales Grass Isol Herrera etal. (2010)
Phoma glomerata Pleosporales DSE Triticum aestivum Poales Grass Isol Crous etal. (1995)
Podospora sp. Sordariales Not DSE Holcus lanatus Poales Grass Isol Sánchez Márquez etal. (2010)
Polymyxa sp. Plasmodiophoraceae Not DSE Sorghum bicolor Poales Grass In vitro exp Galamay etal. (1992)
Pyrenochaeta sp. 1 Pleosporales DSE Holcus lanatus Poales Grass Isol Sánchez Márquez etal. (2010)
Rhizoctonia sp. Cantharellales DSE Carex curvula Poales Sedge Isol Haselwandter and Read (1982)
Rhizoctonia sp. Cantharellales DSE Carex rma Poales Sedge Isol f Haselwandter and Read (1982)
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38-9Fungal Root Endophytes
Rhizoctonia sp. Cantharellales DSE Carex lasiocarpa, C.
aquatilis
Poales Sedge Isol ormann etal. (1999)
Rhizoctonia spp. Cantharellales Not DSE Triticum aestivum Poales Grass Isol Sieber etal. (1988)
Tapesia sp. Helotiales DSE Deschampsia antarctica Poales Grass Isol Upson etal. (2009)
ielavia appendiculata Sordariales Not DSE Stipa grandis Poales Grass Isol Su etal. (2010)
Trematosphaeria clarkii Pleosporales DSE Oryza sativa Poales Grass Isol Fisher and Petrini (1992)
Trematosphaeria clarkii Pleosporales DSE Oryza sativa Poales Grass Isol Fisher and Petrini (1992)
Unidentied DSE DSE Arrhenatherum elatius Poales Grass Micros Deram etal. (2008)
Unidentied DSE DSE Bouteloua eriopoda Poales Grass In vitro exp Barrow etal. (2004)
Unidentied DSE DSE Bouteloua gracilis Poales Grass ITS Green etal. (2008)
Unidentied DSE DSE Bouteloua gracilis Poales Grass Micros Medina-Roldan etal. (2008)
Unidentied DSE DSE Cynodon dactylon Poales Grass Micros Li etal. (2005)
Unidentied DSE DSE Cyperus rotundus Poales Grass Micros Li etal. (2005)
Unidentied DSE DSE Deschampsia exuosa Poales Grass Open-top
chambers
in forest
m Olsrud etal. (2010)
Unidentied DSE DSE Deuterocohnia
longipetala
Poales Bromelia Micros Lugo etal. (2009)
Unidentied DSE DSE Digitaria cruciata Poales Grass Micros Li etal. (2005)
Unidentied DSE DSE Dyckia spp. Poales Bromelia Micros Lugo etal. (2009)
Unidentied DSE DSE Paspalum distichum Poales Grass Micros Li etal. (2005)
Unidentied DSE DSE Phragmites australis Poales Grass Micros Dolinar and Gaberscik (2010)
Unidentied DSE DSE Poa annua Poales Grass Micros Li etal. (2005)
Unidentied DSE DSE Tillandsia spp. Poales Bromelia Micros Lugo etal. (2009)
a
Genus, species and order (family) names according to index fungorum (http://www.indexfungorum.org/Names/Names.asp, December 20, 2011). If both the teleomorph (sexual reproductive stage) and
the anamorph (asexual reproductive stage) are produced, the name of the teleomorph is given. Names of anamorph(s) can be retrieved from the list of the teleomorph’s synonyms provided in the index. e
next lower taxon is given if the fungus Order is not known with certainty (“incertae sedis”).
b
Isol, isolation from surface-sterilized roots; in vitro exp, fungus used in in-vitro experiment(s); ITS, detection by DNA extraction, sequencing of the ITS regions and sequence comparison with sequence
databases; Micros, detection by microscopy.
c
Special eect details: (a) Plant growth stimulation; improved sand stabilizing role of host in coastal dunes; control of nematodes. (b) Growth stimulation of roots; control of Blumeria graminis. (c) Biocontrol
of damping-o, root and stem rot, caused by anatephorus cucumeris, in cotton. (d) Enhanced nitrogen uptake. (e) Control of Gaeumannomyces graminis. (f) Plant growth stimulation. (g) Control of
Phaeosphaeria nodorum, Fusarium and Gibberella species. (h) Control of Gaeumannomyces graminis var. tritici and Gaeumannomyces cylindrosporus. (i) Plant growth stimulation by one isolate. (j) Plant growth
stimulation by two of three isolates. (k) Plant growth stimulation by one of two isolates. (l) Increase of nitrogen uptake. (m) Increased colonization at higher temperatures, but not at elevated CO
2
.
d
Anamorph: Harpophora graminicola.
e
Anamorph: Harpophora radicicola.
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38-10 Root–Rhizosphere Interactions
(Figure38.2A). Microsclerotia like those formed by M. bolleyi
were also observed in roots of Poa alpina (cited as Poa alpi-
gena) in Spitsbergen (Väre etal. 1992).
Colonization by Harpophora spp. (anamorphic
Gaeumannomyces spp.) is usually recognized by dark septate
runner hyphae growing on the root surface. e surface myce-
lium of some species also possesses hyphopodia that can be
lobed or unlobed (Deacon 1981), a feature that is considered suit-
able to discriminate the varieties tritici, avenae, and maydis of
G. graminis, which possess simple hyphopodia from the variety
graminis that has lobed hyphopodia (Freeman and Ward 2004;
Figure38.2B). Depth of penetration into the root cortex and the
stele and, thus, virulence depend on the fungus and host species,
the environmental conditions, and the age and type of roots.
G. graminis var. maydis forms a net of stout brown runner
hyphae with lateral hyphopodia on the root surface (McKeen
1952). Infection of the cortical cells of primary, seminal, and
adventitious roots occurred by slender colorless microhy-
phae, but the roots appeared usually healthy. Sometimes indi-
vidual cells were completely lled with enlarged fungus cells
that later assumed thick, brown walls typical for microscle-
rotia (McKeen 1952). Skipp and Christensen (1989) observed
microsclerotia similar to those observed by McKeen (1952)
in cortical cells of roots of Lolium perenne L. from various
sites in New Zealand. Isolations from surface-sterilized root
segments conrmed presence of G. graminis var. maydis. G.
cylindrosporus is a nonpathogenic endophyte (Deacon 1987).
Mycelia of G. cylindrosporus and G. graminis develop similarly
on roots, but G. cylindrosporus does not penetrate the vascular
system. Whereas in young regions of the roots, the dark, lysis-
resistant runner hyphae of G. cylindrosporus are conned to
the root surface and the fungus penetrates only little into the
cortex, on older regions, the runner hyphae grow intercellu-
larly deep within the cortex (Deacon 1987).
Intracellular pycnidia of Phoma meti Brunaud were observed
in the root cortex of the annual grass Vulpia ciliata Dumort
(Newsham 1994). Intracellular sporulation may be ecologically
advantageous because conidia can spread rapidly right aer rup-
ture of the cell wall in sloughed-o cortical cells.
Galamay et al. (1992) observed blackberry-like sclero-
tia of an endophyte in the epidermal and hypodermal cells
of nodal and rst-order lateral roots of Sorghum bicolor (L.)
Moench. e fungus was tentatively identied as Polymyxa
sp. (Plasmodiophoromycetes). Since tissues internal to the
(A) (B)
a
60 μm,
(C)
(E)
10
(F)
16
(D)
P1
P2
n
is
FIGURE 38.2 (A) Multicellular microsclerotia of Microdochium bolleyi lling single cortex cells in a tomato root. (From Rasmann, C. etal.,
Appl. Soil Ecol., 43, 22, 2009.) (B) Hyphopodia of Gaeumannomyces graminis var. graminis wild-type strain JH2033 formed on Mylar lms.
(From Money, N.P. etal., Fungal Genet. Biol., 24, 240, 1998.) Scale bar = 20 μm. (C) Intracellular spherical to pear-shaped chlamydospores of
Piriformospora indica in cortical cells of a barley root. (From Waller, F. etal., Proc. Natl. Acad. Sci. U S A, 102, 13386, 2005.) (D) Morphology and
fungal colonization (most probably Inocybe sp.) of coralloid rhizomes of the orchid Epipogium aphyllum. Magnication detail of infected cells with
view of elongated fungal pelotons cut transversally in P1 and longitudinally in P2 (n, orchid cell nucleus, is, inorescence shoots). (From Roy, M.
etal., Ann. Bot., 104, 595, 2009.) Scale bar = 50 μm. (E) Squash mount of mycorrhizal root of Calypso bulbosa stained with chlorazol black showing
sclerotium-like structures of a DSE in cortical cells. (From Currah, R.S. etal., Am. J. Bot., 75, 739, 1988.) Scale bar = 13 μm. (F) Epidermal micro-
sclerotium (*) of Phialocephala fortinii s.l. (CSP 12, strain UAMH 9525) in a root of Asparagus ocinalis. (From Yu, T. etal., Can. J. Microbiol., 47,
741, 2001.) Scale bar = 15 μm.
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38-11Fungal Root Endophytes
hypodermis were never colonized, it was assumed that the hypo-
dermis functions as a barrier to protect the inner tissues from
colonization by the fungus.
In substrate inoculated with Piriformospora indica Sav.
Verma, Aj. Varma, Rexer, G. Kost & P. Franken, the fungus
entered barley (H. vulgare L.) roots primarily via root hairs
and proceeded intracellularly into rhizodermal cells and later
on into the root cortex (Waller etal. 2005). It forms spherical
to pear-shaped chlamydospores in both root hairs and cortical
cells (Figure 38.2C). Hyphae were detected neither in the central
part of the roots beyond the endodermis nor in stems or leaves.
2. Endophyte–Pathogen Interactions,
Biological Control
Antagonism between Phaeosphaeria nodorum and M. bolleyi
was observed by Reinecke (1978) and Reinecke and Fokkema
(1981). M. bolleyi behaved also as an antagonist against Fusarium
species (Reinecke 1978; Sieber 1985) and was reported to
reduce damage to or colonization of cereal roots by G. graminis
var. tritici (Kirk and Deacon 1987). Similarly, G. cylindrosporus
controlled pathogens in Vulpia ciliata (Newsham 1999) and
gave signicant control of take-all by competition for senescing
root tissues (Deacon 1981). G. cylindrosporus is found in rela-
tively low amounts on cereal roots unless the cereal crop fol-
lows 1 or 2 years of grass (or cereal crop) (Deacon 1987). Crop
rotation, a very eective form of disease management with a
long tradition, seems to be disadvantageous for G. cylindrospo-
rus and, thus, for control of take-all. Several other endophytic
fungi possess antagonistic activity against G. graminis var.
tritici (Macia-Vicente etal. 2008): Acremonium blochii (Matr.)
W. Gams, Acremonium furcatum (Moreau & V. Moreau) ex
W. Gams, Aspergillus fumigatus Fresen., Cyclindrocarpon sp.,
Dactylaria sp., Gibberella intricans Wollenw. (teleomorph
of Fusarium equiseti (Corda) Sacc.), Ilyonectria radicicola
(Gerlach & L. Nilsson) Chaverri& C. Salgado (teleomorph of
Cylindrocarpon destructans (Zinsm.) Scholten), Phoma her-
barum Westend., P. leveillei Boerema & G.J. Bollen. A. blochii,
Aspergillus fumigatus, Dactylaria sp., G. intricans, and Phoma
herbarum reduced colonization of barley roots by this fungus.
Cladorrhinum foecundissimum Sacc. & Marchal, isolated from
the grass Elytrigia repens (L.) Desv. ex Nevski, controlled root
and stem rot caused by Rhizoctonia solani J.G. Kühn in cotton
(Gossypium hirsutum L.) (Gasoni and Stegman de Gurnkel
2009). Disease severity of powdery mildew (Blumeria graminis
(DC.) Speer f. sp. hordei Jacz.) on primary leaves of H. vulgare
was reduced when seeds had been treated with spore suspen-
sions of Chaetomium globosum Kunze ex Fr. and Chaetomium
funicola Cooke (Vilich etal. 1998). Endophytic Acremonium
strictum W. Gams in roots of the grass Ammophila arenaria
(L.) Link was nematicidal and reduced the adverse eects of
nematodes (Hol etal. 2007).
3. Endophyte–Plant Interactions
Root inoculations with a Microdochium species (DSE)
and Periconia macrospinosa Lefebvre & Aar.G. Johnson
(DSE) from grass roots collected in a mesic tallgrass prai-
rie increased the biomass of the grass Andropogon gerardii
Vitman (Mandyam etal. 2010). Nitrogen uptake of D. flex-
uosa was enhanced by the DSE Cryptosporiopsis rhizophila
Verkley & Zijlstra and Phialocephala fortinii s.l. (Zijlstra etal.
2005). Presence of the DSE Phoma fimeti in the roots of the
annual grass V. ciliata increased root and shoot biomass, root
lengths, and tiller numbers (Newsham 1994). Similarly, G. cyl-
indrosporus increased tiller number and biomass production
of V. ciliata (Newsham 1999). Metacordyceps chlamydosporia
(H.C. Evans) G.H. Sung, J.M. Sung, Hywel-Jones & Spatafora,
a clavicipitalean nematode parasite colonized barely roots
endophytically and promoted plant growth (Macia-Vicente
etal. 2008). Acremonium strictum was shown to increase root
biomass and the number of tillers in Ammophila arenaria
(Hol etal. 2007). Increased root fresh weight was observed
after seeds of barley (H. vulgare) were treated with spore sus-
pensions of C. globosum or C. funicola (Vilich etal. 1998).
Similarly, inoculations with Piriformospora indica enhanced
yield in barley (Waller etal. 2005).
B. Orchid Endophytes
Classical OM fungi of the Rhizoctonia-type are polyphyletic
and belong to several different orders of the Basidiomycotina
(Sebacinales, Ceratobasidiales, Tulasnellales) (Currah
and Zelmer 1992; Smith and Read 2008; Weiss etal. 2011).
Orchids, especially achlorophyllous, mycoheterotrophic ones,
often associate also with basidiomycetes that form ECM with
woody plants, for example, Inocybe, Hebeloma, Xerocomus,
Lactarius, or Thelephora species and, thus, probably indi-
rectly exploit the neighboring trees as carbon sources (Roy
etal. 2009; Table 38.2). In addition, many orchids host mem-
bers of the ascomycotina. Leptodontidium orchidicola Sigler
& Currah, Phialocephala fortinii s.l., Trichocladium opacum
(Corda) S. Hughes, and Trichosporiella multisporum Sigler
& Currah were frequently isolated from terrestrial orchids
(Currah etal. 1987, 1988, 1990; Currah and Sherburne 1992).
Tao etal. (2008) examined the endophytes of the terrestrial
orchid Bletilla ochracea Schltr. using denaturing gradi-
ent gel electrophoresis (DGGE) and random cloning analy-
sis and detected 10 operational taxonomic units (OTUs) of
endophytic fungi. Two Mycosphaerella species, an unknown
ascomycete species, and an Alternaria species dominated.
Oidiodendron spp. may be significant symbionts in orchids
because they are also known to form endomycorrhizae with
ericaceous plants (Currah and Zelmer 1992). Vujanovic
et al. (2000) described Phialocephala victorinii Vujan. &
St-Arn., an orchid endophyte with dark septate hyphae.
Epiphytic and lithophytic orchids in the tropics often yield
large numbers of isolates of fungi belonging to the Xylariales
(Bayman etal. 1997; Table 38.2). Members of the Xylariaceae
are also the most frequently isolated endophytes of leaves
of tropical palms (Rodrigues 1996). Epiphytic orchids may,
thus, harbor the same endophytes as the trees they grow on.
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38-12 Root–Rhizosphere Interactions
TABLE 38.2 Endophytes in Orchids (Family Orchidaceae)
Endophyte Host
Type of
Experiment
b
Special
Eect
c
ReferencesGenus
a
Species
a
Fungus Order
b
DSE/Not DSE Species Plant Order
Woody/
Herbaceous
Acremonium sp. Hypocreales Not DSE Dendrobium loddigesii Asparagales Orchid Isol Chen etal (2010b)
Alternaria sp. Pleosporales DSE Oncidium warmingii Asparagales Orchid Isol and in vitro
exp with crude
extracts
a Vaz etal. (2009)
Alternaria sp. Pleosporales DSE Bletilla ochracea Asparagales Orchid Mol Tao etal. (2008)
Armillaria mellea Agaricales Not DSE Gastrodia elata Asparagales Orchid Isol Xu and Guo (2000)
Aspergillus spp. Eurotiales Not DSE Lepanthes spp. Asparagales Orchid Isol Bayman etal. (1997)
Cadophora malorum Helotiales DSE Bletilla striata Asparagales Orchid Isol Chen etal. (2010a)
Cadophora sp. Helotiales Not DSE Gymnadenia conopsea Asparagales Orchid Isol Stark etal. (2009)
Cenococcum geophilum Dothideomycetes Not DSE Gymnadenia conopsea Asparagales Orchid Isol Stark etal. (2009)
Colletotrichum sp. Sordariomycetes Not DSE Dendrobium nobile Asparagales Orchid Isol Yuan etal. (2009)
Colletotrichum sp. Sordariomycetes Not DSE Lepanthes spp. Asparagales Orchid Isol Bayman etal. (1997)
Cryptococcus carnescens Tremellales Not DSE Gymnadenia conopsea Asparagales Orchid Isol Stark etal. (2009)
Cryptosporiopsis ericae Helotiales DSE Spiranthes sinensis Asparagales Orchid Isol Chen etal. (2010a)
Cylindrocarpon sp. Hypocreales Not DSE Cremastra appendiculata Asparagales Orchid Isol Zhang etal. (2006)
Cylindrocarpon sp. Hypocreales Not DSE Sophronitis fournieri Asparagales Orchid Isol Vaz etal. (2009)
Epicoccum nigrum Pleosporales DSE Maxillaria rigida Asparagales Orchid Isol and in vitro
exp with crude
extracts
b Vaz etal. (2009)
Exophiala sp. Chaetothyriales DSE Gymnadenia conopsea Asparagales Orchid Isol Stark etal. (2009)
Fusarium chlamydosporum Hypocreales Not DSE Dendrobium crumenatum Asparagales Orchid Isol Siddiquee etal. (2010)
Fusarium oxysporum Hypocreales Not DSE Gymnadenia conopsea Asparagales Orchid Isol Stark etal. (2009)
Fusarium sp. Hypocreales Not DSE Anacamptis pyramidalis Asparagales Orchid Isol Gezgin and Eltem (2009)
Fusarium sp. Hypocreales Not DSE Bulbophyllum involutum Asparagales Orchid Isol and in vitro
exp with crude
extracts
b Vaz etal. (2009)
Fusarium sp. Hypocreales Not DSE Dendrobium loddigesii Asparagales Orchid Isol Chen etal. (2010b)
Fusarium sp. Hypocreales Not DSE Isochilus linearis Asparagales Orchid Isol Vaz etal. (2009)
Fusarium sp. Hypocreales Not DSE Ophrys fusca Asparagales Orchid Isol Gezgin and Eltem (2009)
Fusarium sp. Hypocreales Not DSE Orchis sancta Asparagales Orchid Isol Gezgin and Eltem (2009)
Fusarium sp. Hypocreales Not DSE Serapias vomeracea
subsp. orientalis
Asparagales Orchid Isol Gezgin and Eltem (2009)
Geopyxis sp. Pezizales Not DSE Gymnadenia conopsea Asparagales Orchid Isol Stark etal. (2009)
Gibberella fujikuroi var.
fujikuroi
Hypocreales Not DSE Epidendrum secundum Asparagales Orchid Isol Vaz etal. (2009)
Guignardia mangifera Botryosphaeriales Not DSE Dendrobium nobile Asparagales Orchid Isol Yuan etal. (2009)
Gymnopus sp. Agaricales Not DSE Wullschlaegelia aphylla Asparagales Orchid Isol c Martos etal. (2009)
Hebeloma sp. Agaricales Not DSE Epipogium aphyllum Asparagales Orchid Isol Roy etal. (2009)
Hypocrea sp. Hypocreales not DSE Sophronitis longipes Asparagales Orchid Isol Vaz etal. (2009)
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38-13Fungal Root Endophytes
Hypoxylon sp Xylariales not DSE Dendrobium nobile Asparagales Orchid Isol Yuan etal. (2009)
Ilyonectria radicicola Hypocreales not DSE Gymnadenia conopsea Asparagales Orchid Isol Stark etal. (2009)
Inocybe sp. Agaricales not DSE Epipogium aphyllum Asparagales Orchid Isol Roy etal. (2009)
Lactarius pubescens Agaricales not DSE Gymnadenia conopsea Asparagales Orchid Isol Stark etal. (2009)
Lactarius sp. Agaricales not DSE Epipogium aphyllum Asparagales Orchid Isol Roy etal. (2009)
Lecanora sp. Lecanorales not DSE Gymnadenia conopsea Asparagales Orchid Isol Stark etal. (2009)
Leptodontidium orchidicola Helotiales DSE Orchids Asparagales Orchid Isol Currah etal. (1987, 1988, 1990)
Leptodontidium orchidicola Helotiales not DSE Gymnadenia conopsea Asparagales Orchid Isol Stark etal. (2009)
Leptodontidium sp. Helotiales DSE Cephalanthera longifolia Asparagales Orchid Isol Abadie etal. (2006)
Leptodontidium sp. Helotiales DSE Dendrobium nobile Asparagales Orchid Isol and in vitro exp d Hou and Guo (2009)
Morchella sp. Pezizales Not DSE Gymnadenia conopsea Asparagales Orchid Isol Stark etal. (2009)
Mycena alphitophora Agaricales Not DSE Gastrodia elata Asparagales Orchid Isol Xu and Guo (2000)
Mycena sp. Agaricales Not DSE Wullschlaegelia aphylla Asparagales Orchid Isol c Martos etal. (2009)
Mycosphaerella sp. N.A. Bletilla ochracea Asparagales Orchid Mol Tao etal. (2008)
Penicillium griseofulvum Ascomycota
incert
Not DSE Dendrobium nobile Asparagales Orchid Isol Yuan etal. (2009)
Penicillium spp. Eurotiales Not DSE Lepanthes spp. Asparagales Orchid Isol Bayman etal. (1997)
Pestalotia spp. Xylariales Not DSE Lepanthes spp. Asparagales Orchid Isol Bayman etal. (1997)
Peziza sp. Pezizales Not DSE Gymnadenia conopsea Asparagales Orchid Isol Stark etal. (2009)
Phialocephala fortinii s.l. Helotiales DSE Orchids Asparagales Orchid Isol Currah etal. (1987, 1988, 1990)
Phialocephala victorinii Helotiales DSE Orchids Asparagales Orchid Isol Vujanovic etal. (2000)
Phialocephala europaea Helotiales DSE Calypso bulbosa Asparagales Orchid Isol Currah etal. (1988)
Phialophora sp. Chaetothyriales Not DSE Gymnadenia conopsea Asparagales Orchid Isol Stark etal. (2009)
Phialophora sp. Helotiales Not DSE Cypripedium spp. Asparagales Orchid Isol Sheerson etal. (2005)
Resinicium sp. Aphyllophorales Not DSE Gastrodia similis Asparagales Orchid Isol c Martos etal. (2009)
Rhizoctonia spp. Cantharellales Not DSE Lepanthes spp. Asparagales Orchid Isol Bayman etal. (1997)
Rhodotorula mucilaginosa Sporidiobolales Not DSE Acianthera hamosa Asparagales Orchid Isol Vaz etal. (2009)
Russula brevipes Agaricales Not DSE Limodorum abortivum Asparagales Orchid Isol Girlanda etal. (2006)
Russula chloroides Agaricales Not DSE Limodorum abortivum Asparagales Orchid Isol Girlanda etal. (2006)
Russula delica Agaricales Not DSE Limodorum abortivum Asparagales Orchid Isol Girlanda etal. (2006)
Russula exalbicans Agaricales Not DSE Gymnadenia conopsea Asparagales Orchid Isol Stark etal. (2009)
Russula lepidicolor Agaricales Not DSE Dipodium hamiltonianum Asparagales Orchid Isol Dearnaley and Le Brocque
(2006)
Russula lilacea Agaricales Not DSE Dipodium hamiltonianum Asparagales Orchid Isol Dearnaley and Le Brocque
(2006)
Russula sp. Agaricales Not DSE Cypripedium parviorum Asparagales Orchid Isol Sheerson etal. (2005)
Serendipita vermifera Auriculariales Not DSE Orchids Asparagales Orchid Isol & in vitro exp d Weiss etal. (2011)
Terfezia sp. Pezizales Not DSE Gymnadenia conopsea Asparagales Orchid Isol Stark etal. (2009)
Tetracladium sp. Helotiales DSE Cephalanthera longifolia Asparagales Orchid Isol Abadie etal. (2006)
Tetracladium sp. Helotiales DSE Orchis militaris Asparagales Orchid Isol Vendramin etal. (2010)
elephora sp. elephorales Not DSE Epipogium aphyllum Asparagales Orchid Isol Roy etal. (2009)
Titaea maxilliforme Helotiales Not DSE Gymnadenia conopsea Asparagales Orchid Isol Stark etal. (2009)
(continued)
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38-14 Root–Rhizosphere Interactions
TABLE 38.2 (continued) Endophytes in Orchids (Family Orchidaceae)
Endophyte Host
Type of
Experiment
b
Special
Eect
c
ReferencesGenus
a
Species
a
Fungus Order
b
DSE/Not DSE Species Plant Order
Woody/
Herbaceous
Trichocladium opacum Sordariales DSE Orchids Asparagales Orchid Isol Currah etal. (1987, 1988, 1990)
Trichoderma asperellum Hypocreales Not DSE Epidendrum secundum Asparagales Orchid Isol Vaz etal. (2009)
Trichosporiella multisporum Helotiales Not DSE Orchids Asparagales Orchid Isol Currah etal. (1987, 1988, 1990)
Verpa conica Pezizales Not DSE Gymnadenia conopsea Asparagales Orchid Isol Stark etal. (2009)
Wilcoxina rehmii Pezizales Not DSE Gymnadenia conopsea Asparagales Orchid Isol Stark etal. (2009)
Wilcoxina sp. Pezizales DSE Cephalanthera longifolia Asparagales Orchid Isol Abadie etal. (2006)
Xerocomus sp. Agaricales Not DSE Epipogium aphyllum Asparagales Orchid Isol Roy etal. (2009)
Xylaria spp. Xylariales Not DSE Dendrobium nobile Asparagales Orchid Isol Yuan etal. (2009)
Xylaria spp. Xylariales Not DSE Lepanthes spp. Asparagales Orchid Isol Bayman etal. (1997)
Unidentied DSE DSE Maianthemum bifolium Asparagales Herb Isol Postma etal. (2007)
a
Genus, species and order (family) names according to index fungorum (http://www.indexfungorum.org/Names/Names.asp, December 20, 2011). If both the teleomorph (sexual reproductive stage) and
the anamorph (asexual reproductive stage) are produced, the name of the teleomorph is given. Names of anamorph(s) can be retrieved from the list of the teleomorph’s synonyms provided in the index. e
next lower taxon is given if the Fungus order is not known with certainty (“incertae sedis”).
b
Isol, isolation from surface-sterilized roots; in vitro exp, fungus used in in-vitro experiment(s); Mol, culture-free, molecular detection method.
c
Special eect details: (a) Antibacterial against Escherichia coli and Staphylococcus aureus. (b) Antimycotic against pathogenic yeasts Candida krusei and C. albicans. (c) Food chain link between dead leaves
and orchid. (d) Plant growth stimulation.
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38-15Fungal Root Endophytes
Confirmation of this assumption would evoke the question
of whether the infection occurs by hyphae growing directly
from one host to the other or by inoculi (spores, conidia) on
each host independently.
1. Anatomy
In contrast to the complex globular masses (hyphal coils) or
pelotons of branched and anastomosed hyphae formed by
classical orchid mycorrhizae within cortical cells (Roy et al.
2009; Figure 38.2D), L. orchidicola and Phialocephala forti-
nii were observed to form small sclerotia (Currah etal. 1988;
Figure38.2E).
2. Endophyte–Pathogen and Endophyte–Plant
Interactions
Crude extracts from Alternaria sp. (DSE) from the roots of
Oncidium warmingii Rchb. f. showed signicant antibac-
terial activity against Escherichia coli and Staphylococcus
aureus (Vaz et al. 2009). Similarly, Epicoccum nigrum Link
(DSE) from Maxillaria rigida Barb. Rodr. and an unidenti-
ed Fusarium species from Bulbophyllum involutum Borba,
Semir & F. Barros controlled the human pathogenic yeasts
Candida krusei (Castell.) Berkhout and Candida albicans (C.P.
Robin) Berkhout (Vaz etal. 2009). A Leptodontidium species
associated with a subtropical Dendrobium species stimu-
lated growth of Dendrobium nobile Lindl. seedlings in vitro
(Hou and Guo 2009).
C. Other Herbaceous Plant Hosts
A plethora of fungi were detected in asymptomatic, healthy
roots of many non-graminiculous, non-orchid herbaceous
plant species growing in arctic, alpine (Christie and Nicolson
1983; Stoyke and Currah 1991; Väre etal. 1992; Ruotsalainen
etal. 2004; Schmidt etal. 2008; Lv etal. 2010), aquatic (Kai
and Zhao 2006), arid (Lugo etal. 2009), or neotropical habi-
tats (Lehnert etal. 2009; Table 38.3). Terrestrial Bromeliaceae
were colonized by both AM fungi and DSE except Bromelia
urbaniana (Mez) L.B. Sm., which was not colonized by either
one of them. In contrast, epiphytic Bromeliaceae were colo-
nized only by DSE (Lugo etal. 2009). AM structures were
observed in seven and DSE in four of 32 hydrophyte species
from lakes and streams in Southwestern China (Kai and Zhao
2006). The frequency of hydrophytes hosting AM fungi and/
or DSE was higher in water bodies of the Upper Parana in
South America where AM was detected in nine species and
DSE in 16 of 24 species (De Marins etal. 2009). Fourteen spe-
cies of endophytes were isolated from the roots of Saussurea
involucrata Kar. & Kir. collected at >2600 m asl in the
Tianshan Mountains in China. Species of Cylindrocarpon,
Phoma, and Fusarium dominated the endophytic fungal
community (Lv etal. 2010). Fernandez etal. (2008) detected
DSE in the roots of Lycopodium paniculatum Desv. ex Poir.
and Equisetum bogotense Kunth in a Valdivian temperate
forest of Patagonia, Argentina. DSE were also detected in
Gentianaceae Gentianella magellanica Gaudich., Gentianella
parviflora (Griseb.) T.N. Ho, Gentianella multicaulis (Gillies
ex Griseb.) Fabris, and Gentiana prostrata Haenke indig-
enous in Argentina (Salvarredi et al. 2010). Trichoderma
asperellum Samuels, Lieckf. & Nirenberg, Gliocladium virens
J.H. Mill., Giddens & A.A. Foster, and Hypocrea lixii Pat.
were endophytic in and epiphytic on banana roots (Xia etal.
2011), whereas Trichoderma brevicompactum G.F. Kraus,
C.P. Kubicek & W. Gams was isolated only from inside of the
roots. Genetic diversity of endophytic T. asperellum and G.
virens was lower than that of epiphytic ones, suggesting that
only selected genotypes are able to infect the roots. Väre etal.
(1992) studied the fungi associated with roots of 76 (72 herba-
ceous) plant species in Spitsbergen. Ectomycorrhizae and AM
fungi were absent from all herbaceous plant species, except
Pedicularis dasyantha Hadač that showed slight ectomycor-
rhizal colonization. In contrast, root endophytes were com-
monly isolated. As already mentioned earlier, Upson et al.
(2009) isolated 243 mostly helotialean DSE strains from the
roots of Deschampsia antarctica (grass) and Colobanthus
quitensis (Kunth) Bartl. (Caryophyllaceae) along a transect
across sub-Antarctica.
1. Anatomy
Rodríguez-Gálvez and Mendgen (1995) studied the ultrastructure
of the infection process by Fusarium oxysporum f. sp. vasinfectum,
causal agent of tracheomycosis of species of the Malvaceae, for
example, cotton. High-pressure freezing of infected cortical cells
revealed that F. oxysporum penetrates and grows within the host
cells without inducing damages such as plasmolysis, cell degenera-
tion, or host necrosis. It was suggested, therefore, that F. oxyspo-
rum f. sp. vasinfectum has an endophytic, biotrophic phase during
colonization of the root tips.
e most frequently observed fungal structures in the roots of
30 of 72 examined herbaceous plant species in Spitsbergen were
inter- and intracellularly growing melanized, septate mycelia
(DSE) (Väre etal. 1992). In addition, cortical cells of Polemonium
boreale Adams, a herbaceous Ericaceae, were lled with dark
microsclerotia that resembled those formed by M. bolleyi and
Phialocephala fortinii s.l. Similarly, Treu et al. (1996) detected
dark microsclerotia in root cells of various alpine plants collected
in Denali National Park, Alaska. A strain of P. fortinii s.l. CSP
12 (UAMH 9525) isolated from Vaccinium vitis-idaea L. formed
microsclerotia having a “puzzle-like” appearance in the roots
of Asparagus ocinalis L. similar to those observed in conifer
roots (Yu etal. 2001; Figure 38.2F). In the cortex of young roots
of Chinese cabbage, dark septate hyphae of Cladophialophora
(Heteroconium) chaetospira (Grove) Crous & Arzanlou were
abundant (Figure 38.3A), whereas the cortex of older roots was
lled with microsclerotia (Yonezawa et al. 2004). Similarly,
hyphae and chlamydospores of DSE were observed in primary
roots of Xenophyllum rosenii (R.E. Fr.) V.A. Funk (Asteraceae) col-
lected at 5389 m asl (Schmidt etal. 2008; Figure38.3B). Sclerotia
and hyphae growing very close to vascular bundles were also
observed in Equisetum pratense Ehrh. roots (Hodson etal. 2009).
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38-16 Root–Rhizosphere Interactions
TABLE 38.3 Endophytes in Other Herbaceous Plants
Endophyte Host
Type of
Experiment
b
Special
Eect
c
ReferencesGenus
a
Species
a
Fungus Order
a
DSE/Not DSE Species Plant Order
Woody/
Herbaceous
Acremonium alternatum Hypocreales Not DSE Brassica oleracea var.
gemmifera
Brassicales Herb In vitro exp a Raps and Vidal (1998),
Dugassa-Gobena etal.
(1998)
Acremonium strictum Hypocreales Not DSE Solanum lycopersicum Solanales Herb In vitro exp b Raps and Vidal (1996), Vidal
(1996)
Aureobasidium pullulans Dothideales Not DSE Pteridium aquilinum Pteridophyta Perennial fern Isol Petrini etal. (1992)
Cladophialophora chaetospira Chaetothyriales DSE Brassica campestris Brassicales Herb In vitro exp c Narisawa etal. (1998)
Cladosporium sp. Capnodiales DSE Saussurea involucrata Asterales Herb Isol Lv etal. (2010)
Cylindrocarpon sp. Hypocreales Not DSE Saussurea involucrata Asterales Herb Isol Lv etal. (2010)
Discocistella grevillei Helotiales Saussurea involucrata Asterales Herb Isol Lv etal. (2010)
Fusarium oxysporum Hypocreales Not DSE Brassica oleracea var.
capitata
Brassicales Herb In vitro exp Davis (1967), Matta (1989)
Fusarium oxysporum Hypocreales Not DSE Citrullus vulgaris Cucurbitales Herb In vitro exp d Davis (1967), Matta (1989)
Fusarium oxysporum Hypocreales Not DSE Dianthus caryophyllus Caryophyllales Herb In vitro exp d Davis (1967), Matta (1989)
Fusarium oxysporum Hypocreales Not DSE Linum usitatissimum Malpighiales Herb In vitro exp d Davis (1967), Matta (1989)
Fusarium oxysporum Hypocreales Not DSE Lycopersicon esculentum Solanales Herb In vitro exp d Davis (1967), Matta (1989)
Hypocrea lixii Hypocreales Not DSE Musa acuminata Zingiberales Herb Isol Xia etal. (2011)
Ilyonectria radicicola Hypocreales Not DSE Pteridium aquilinum Pteridophyta Perennial fern Isol Petrini etal. (1992)
Leptodontidium orchidicola Helotiales DSE Colobanthus quitensis Caryophyllales Herb Isol Upson etal. (2009)
Leptodontidium orchidicola Helotiales DSE Pedicularis bracteosa Lamiales Herb Isol Currah etal. (1987)
Leptodontidium orchidicola Helotiales DSE Saussurea involucrata Asterales Herb Isol Lv etal. (2010)
Leptosphaeria sp. Pleosporales DSE Saussurea involucrata Asterales Herb Isol Lv etal. (2010)
Meliniomyces variabilis LtVB3 Leotiomycetes DSE Brassica rapa Brassicales Herb In vitro exp e Ohtaka and Narisawa (2008)
Meliniomyces variabilis LtVB3 Leotiomycetes DSE Solanum lycopersicum Solanales Herb In vitro exp f Ohtaka and Narisawa (2008)
Microdochium bolleyi Xylariales DSE Lycopersicon esculentum Solanales Herb Isol and Micros g Rasmann etal. (2009)
Mortierella sp. Zygomycota Not DSE Pteridium aquilinum Pteridophyta Perennial fern Isol Petrini etal. (1992)
Mycocentrospora acerina Pleosporales DSE Saussurea involucrata Asterales Herb In vitro exp h Wu etal. (2010)
Mycocentrospora acerina Pleosporales DSE Saussurea involucrata Asterales Herb Isol Lv etal. (2010)
Phaeosphaeria avenaria Pleosporales DSE Saussurea involucrata Asterales Herb Isol Lv etal. (2010)
Phialophora cyclaminis Chaetothyriales DSE Cyclamen persicum Ericales Herb Isol Schol-Schwarz (1970)
Phoma chrysanthemicola Pleosporales DSE Chrysanthemum
morifolium
Asterales Herb Isol Aveskamp etal. (2009)
Phoma chrysanthemicola Pleosporales DSE Heteropappus
semiprostratus
Asterales Herb Isol de Graaf (unpublished)
Phoma chrysanthemicola Pleosporales DSE Saussurea involucrata Asterales Herb Isol Lv etal. (2010)
Phoma glomerata Pleosporales DSE Saussurea involucrata Asterales Herb Isol Lv etal. (2010)
Phoma sclerotioides Pleosporales DSE Saussurea involucrata Asterales Herb Isol Lv etal. (2010)
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38-17Fungal Root Endophytes
Piriformospora indica Sebacinales Not DSE Various spp. N.A. Various In vitro exp i Varma etal. (2001)
Tapesia sp. Helotiales DSE Colobanthus quitensis Caryophyllales Herb Isol Upson etal. (2009)
Trichoderma asperellum Hypocreales Not DSE Musa acuminata Zingiberales Herb Isol Xia etal. (2011)
Trichoderma virens Hypocreales Not DSE Musa acuminata Zingiberales Herb Isol Xia etal. (2011)
Trichoderma brevicompactum Hypocreales Not DSE Musa acuminata Zingiberales Herb Isol Xia etal. (2011)
Triscelophorus monosporus Pezizomycotina Not DSE Angiopteris evecta Pteridophyta Perennial fern Isol Raviraja etal. (1996)
Triscelophorus monosporus Pezizomycotina Not DSE Christela dentata Pteridophyta Small fern Isol Raviraja etal. (1996)
Unidentied DSE DSE Astragalus cf. arequipensis Fabales Herb Isol Schmidt etal. (2008)
Unidentied DSE DSE Bartsia pumila Lamiales Herb Isol Schmidt etal. (2008)
Unidentied DSE DSE Ceradenia spp. Polypodiales Herb Micros Lehnert etal. (2009)
Unidentied DSE DSE Cochlidium serrulatum Polypodiales Herb Micros Lehnert etal. (2009)
Unidentied DSE DSE Elaphoglossum spp. Polypodiales Herb Micros Lehnert etal. (2009)
Unidentied DSE DSE Equisetum bogotense Equisetales Herb Micros Fernandez etal. (2008)
Unidentied DSE DSE Galium odoratum Gentianales Herb Isol Postma etal. (2007)
Unidentied DSE DSE Gramitis paramicola Polypodiales Herb Micros Lehnert etal. (2009)
Unidentied DSE DSE Hydrilla verticillata Alismatales Herb Micros Kai and Zhao (2006)
Unidentied DSE DSE Hygrophila cf. costata Lamiales Herb Micros De Marins etal. (2009)
Unidentied DSE DSE Hymenophyllum spp. Polypodiales Herb Micros Lehnert etal. (2009)
Unidentied DSE DSE Lellingeria spp. Polypodiales Herb Micros Lehnert etal. (2009)
Unidentied DSE DSE Limnobium laevigatum Apiales Herb Micros De Marins etal. (2009)
Unidentied DSE DSE Lycopodium sp. Lycopodiales Herb Isol Schmidt etal. (2008)
Unidentied DSE DSE Lycopodium paniculatum Lycopodiales Herb Micros Fernandez etal. (2008)
Unidentied DSE DSE Melpomene spp. Polypodiales Herb Micros Lehnert etal. (2009)
Unidentied DSE DSE Mercurialis perennis Malpighiales Herb Isol Postma etal. (2006)
Unidentied DSE DSE Micropolypodium sp. Polypodiales Herb Micros Lehnert etal. (2009)
Unidentied DSE DSE Mnioides sp. Asterales Herb Isol Schmidt etal. (2008)
Unidentied DSE DSE Myriophyllum brasiliense Saxifragales Herb Micros De Marins etal. (2009)
Unidentied DSE DSE Oenanthe decumbens Apiales Herb Micros Kai and Zhao (2006)
Unidentied DSE DSE Pedicularis spp. Lamiales Herb Isol Li and Guan (2007)
Unidentied DSE DSE Perezia coerulescens Asterales Herb Isol Schmidt etal. (2008)
Unidentied DSE DSE Plantago asiatica Lamiales Herb Micros Li etal. (2005)
Unidentied DSE DSE Polygonum spp. Caryophyllales Herb Micros De Marins etal. (2009)
Unidentied DSE DSE Potamogeton tepperi Alismatales Herb Micros Kai and Zhao (2006)
Unidentied DSE DSE Rotala rotundifolia Myrtales Herb Micros Kai and Zhao (2006)
Unidentied DSE DSE Saxifraga aizoides Saxifragales Herb Isol j Ruotsalainen etal. (2004)
Unidentied DSE DSE Senecio sp. Asterales Herb Isol Schmidt etal. (2008)
Unidentied DSE DSE Sibbaldia procumbens Rosales Herb Isol j Ruotsalainen etal. (2004)
Unidentied DSE DSE Solidago virgaurea Asterales Herb Isol j Ruotsalainen etal. (2004)
Unidentied DSE DSE Stellaria nemorum Caryophyllales Herb Isol Postma etal. (2006)
Unidentied DSE DSE Stylidium productum Asterales Herb Isol Chambers etal. (2008)
Unidentied DSE DSE Terpsichore spp. Polypodiales Herb Micros Lehnert etal. (2009)
(continued)
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38-18 Root–Rhizosphere Interactions
TABLE 38.3 (continued) Endophytes in Other Herbaceous Plants
Endophyte Host
Type of
Experiment
b
Special
Eect
c
ReferencesGenus
a
Species
a
Fungus Order
a
DSE/Not DSE Species Plant Order
Woody/
Herbaceous
Unidentied DSE DSE Trichomanes spp. Polypodiales Herb Micros Lehnert etal. (2009)
Unidentied DSE DSE Trientalis europaea Ericales Herb Isol j Ruotsalainen etal. (2004)
Unidentied DSE DSE Trifolium repens Fabales Herb Micros Li etal. (2005)
Unidentied DSE DSE Viola biora Malpighiales Herb Isol j Ruotsalainen etal. (2004)
Unidentied DSE DSE Werneria orbignyana Asterales Herb Isol Schmidt etal. (2008)
Unidentied DSE DSE Werneria sp. Asterales Herb Isol Schmidt etal. (2008)
Unidentied DSE DSE Xenophyllum rosenii Asterales Herb Isol Schmidt etal. (2008)
a
Genus, species and order (family) names according to index fungorum (http://www.indexfungorum.org/Names/Names.asp, December 20, 2011). If both the teleomorph (sexual reproductive stage) and
the anamorph (asexual reproductive stage) are produced, the name of the teleomorph is given. Names of anamorph(s) can be retrieved from the list of the teleomorph’s synonyms provided in the index.
e next lower taxon is given if the Fungus order is not known with certainty (“incertae sedis”).
b
Isol, isolation from surface-sterilized roots; in vitro exp, fungus used in in-vitro experiment(s); Micros, detection by microscopy.
c
Special eect details: (a) Control of diamondback moth and cabbage aphid Brevicoryne brassicae. (b) Control of nematodes and greenhouse whitey larvae. (c) Control of clubroot (Plasmodiophora
brassicae). (d) Induction of resistance. (e) Control of Verticillium longisporum. (f) Control of Fusarium wilt. (g) Increased colonization by Microdochium bolleyi like fungi in organically grown tomatoes. (h)
Stimulation of plant root development. (i) Plant growth stimulation. (j) No correlation with altitude.
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38-19Fungal Root Endophytes
2. Endophyte–Pathogen, Endophyte–Nematode,
and Endophyte–Insect Interactions
More than 70 formae speciales of Fusarium oxysporum are
pathogenic on dierent hosts (Armstrong and Armstrong
1981). In general, each form causes symptoms only on one or
a few related plant species, whereas they occur as nonpatho-
genic endophytes in other plant species. Absence of adverse
eects of F. oxysporum isolates in infection experiments is in
line with this observation (Davis 1967; Gessler and Kuc 1982;
Rodríguez-Gálvez and Mendgen 1995). Nonpathogenic iso-
lates of F. oxysporum were shown to be able to penetrate and
colonize the tissues of carnation and tomato plants without
symptom expression (Postma and Rattink 1991; Hallmann and
Sikora 1994). Fusarium wilt disease is inhibited in plants inoc-
ulated with formae speciales of F. oxysporum to which they are
not susceptible prior to inoculation with forms to which they
are susceptible. is phenomenon is called “cross-protection”
or “induced resistance” (Davis 1967; Matta 1989). Inoculation
of individual tomato, ax, carnation, cabbage, and watermelon
seedlings with any one of nine formae speciales of F. oxyspo-
rum markedly reduced susceptibility to forms that they are
susceptible to (Davis 1967). Similarly, resistance of cucumber
(Cucumis sativus L.) against F. oxysporum f. sp. cucumeri-
num J.H. Owen was induced by inoculation of formae spe-
ciales that are not pathogenic on cucumber (Gessler and Kuc
1982). Cross-protection can be based on an indirect mecha-
nism mediated by the plant or on direct interactions between
inducer and challenger (Matta 1989). Chitin synthase–de-
cient mutants of the tomato root pathogen F. oxysporum f. sp.
lycopersici (Sacc.) W.C. Snyder & H.N. Hansen elicited plant
defense response and protected the plants against wild-type
infections (Pareja-Jaime et al. 2010). Fusarium solani colo-
nized tomato roots endophytically and protected them against
(C)
(D)
(A)
50 μm
(B)
ICO
OCO
EP
FIGURE 38.3 (A) Scanning electron micrographs of cross section of a Chinese cabbage root infected by Cladophialophora chaetospira. Abundant
fungal hyphae developing in EPs and within OCO (arrowheads, appressorium-like swollen structures; ICO, inner cortical cells; VC, vascular cyl-
inder). (From Yonezawa, M. etal., Mycoscience, 45, 367, 2004.) Scale bar = 5 μm. (B) Dark septate endophytic fungi in roots of Xenophyllum rosenii
at 5389 m. (From Schmidt, S.K. etal., Arct. Antarct. Alp. Res., 40, 576, 2008.) (C) Gaultheria poeppiggi EP of hair root lled with sclerotia of the
Phialocephala type. (From Urcelay, C., Mycorrhiza, 12, 89, 2002.) Scale bar = 10 μm. (D) Roots of Pinus strobus colonized by Phialocephala fortinii
s.l. (strain UAMH 10266). Longitudinal section of colonized root showing surface hyphae (arrowhead) and Hartig net (arrows) and intercellular
hyphae. (From Peterson, R.L. etal., Botany, 86, 445, 2008.) Scale bar = 50 μm.
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38-20 Root–Rhizosphere Interactions
the root pathogen F. oxysporum f. sp. radicis-lycopersici
Jarvis& Shoemaker (Kavroulakis etal. 2007). Vascular dis-
colorations were reduced compared to the controls when
wounded roots of tomato seedlings were treated with an
unidentied Acremonium species prior to inoculation with the
pathogen, F.oxysporum f.sp. lycopersici (Phillips etal. 1967).
Inoculations with nonpathogenic Fusarium forms can provide
protection not only against other forms of Fusarium but also
against other diseases. Metabolites of F. oxysporum can also
signicantly reduce growth of soilborne pathogens such as
Phytophthora cactorum (Lebert & Cohn) J. Schröt., Pythium
ultimum Trow, and anatephorus cucumeris (A.B. Frank)
Donk in vitro (Hallmann and Sikora 1996), and F. oxysporum
strain EF 119 was ecient against tomato late blight caused by
Phytophthora infestans (Mont.) de Bary and inhibited growth
of Pythium ultimum and Phytophthora capsici Leonian (Kim
et al. 2007). Inoculations of tomato plants with nonpatho-
genic F. oxysporum strains signicantly reduced coloniza-
tion by the plant parasitic root-knot nematode Meloidogyne
incognita Kofoid & White without adversely aecting plant
health (Hallmann and Sikora 1994; Dababat and Sikora 2007;
Dababat etal. 2008). Similarly, endophytic F. oxysporum can
control the burrowing nematode Radopholus similis Cobb,
which is one of the key pests of banana (Athman etal. 2006;
Mendoza and Sikora 2009; Paparu etal. 2009).
Biological control of diseases, nematode, or insect pests was
also reported for root endophytes other than Fusarium spp.
Root inoculations of tomato plants with the soilborne endo-
phyte Acremonium strictum signicantly reduced the fre-
quency of root-knots induced by the nematode Meloidogyne
hapla Chitwood (Raps and Vidal 1996). Altered plant growth
of endophyte-colonized roots and direct parasitism of A. stric-
tum on the nematode eggs were assumed to be responsible for
nematode control. Culture ltrates of endophytic fungi isolated
from roots of tomato and banana plants in Kenya and Uganda
caused a signicant reduction of the activity of several nema-
tode species (Schuster et al. 1995). Mortality of greenhouse
whiteies (Trialeurodes vaporariorum Westwood [Homoptera])
on tomato plants inoculated with the endophyte A. strictum
was only increased if the plants suered from drought stress.
Interestingly, the insects were preferentially feeding on plants
with inoculated roots (Vidal 1996). Similarly, the insect also
preferred French beans (Phaseolus vulgaris L.) inoculated with
A. strictum to uninoculated ones (Moll and Vidal 1995). In
0.5 mm
(E)
(F)
(G)
FIGURE 38.3 (continued) (E) Ectomycorrhiza formed by Acephala macrosclerotiorum on Pinus sylvestris. e mantle appears verrucous due to
characteristic, melanized wartlike sclerotia (arrowheads). (From Münzenberger, B. etal., Mycorrhiza, 19, 481, 2009.) (F) Cells of the phlobaphene
cork of a Norway-spruce (Picea abies) ne root lled with multicellular sclerotia composed of bubble-shaped, thick-walled, melanized cells of
Phialocephala fortinii s.l. Scale bar = 10 μm. (Courtesy of O. Holdenrieder). (G) Section of root of axenically grown Salix glauca inoculated with
P. fortinii s.l. (CSP13, strain UAMH 8148). Transverse section of a lateral root with a patchy fungal mantle (arrows) associated with the epidermal
layer and Hartig net initials (arrowheads). (From Fernando, A.A. and Currah, R.S., Can. J. Bot., 74, 1071, 1996.) Scale bar = 10 μm.
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38-21Fungal Root Endophytes
addition, females laid more eggs on inoculated than on unin-
oculated plants, and performance of the larvae on endophyte-
infected plants was slightly better. e observed changes of
the sugar and amino acid composition of the phloem sap were
assumed responsible for the behavior of the insects.
Root inoculations of Brussels sprouts (Brassica oleracea var.
gemmifera DC.) with the soilborne endophyte Acremonium
alternatum Link had a signicant eect on the performance of
diamondback moth (Plutella xylostella L.) (Dugassa-Gobena
et al. 1998; Raps and Vidal 1998). Larvae fed with leaves of
endophyte-inoculated plants experienced a higher mortality or
showed delayed growth, development, and pupation compared
to controls. e observed changes of the phytosterol composi-
tion of the host plants infected by endophytes were suspected to
confer control of the insect, because these changes altered the
suitability of certain phytosterols to be enzymatically dealkyl-
ated to cholesterol in insects. is subsequently interfered with
the molting processes of the larvae (Dugassa-Gobena etal. 1998;
Raps and Vidal 1998).
Sixteen endophytic fungal isolates from roots of Chinese
cabbage (Brassica campestris L.) almost completely suppressed
clubroot, caused by the soilborne fungus Plasmodiophora bras-
sicae Woronin, in sterile soil (Narisawa etal. 1998). Two of these
isolates were also eective in nonsterile soil and could be identi-
ed as Cladophialophora chaetospira (DSE), a species commonly
found on rotting wood in Europe (Ellis 1976) and isolated from
roots of Picea abies (L.) Karst. (Crous etal. 2007). Similarly, DSE
isolate LtVB3 from barley roots was shown to colonize roots
of Chinese cabbage and tomato endophytically and suppress
Verticillium yellows of Chinese cabbage and Fusarium wilt of
tomato (Narisawa etal. 2004). LtVB3 could meanwhile be iden-
tied as Meliniomyces variabilis Hambl. & Sigler (Ohtaka and
Narisawa 2008). Several endophytes (Phaeosphaeria avenaria
(G.F. Weber) O.E. Erikss., Leptosphaeria sp., Phoma chrysanthe-
micola Hollós, Cladosporium sp., and Cylindrocarpon sp.) iso-
lated from the roots of the alpine plant Saussurea involucrata
(Kar. & Kir.) Sch. Bip. in the Tianshan Mountains in China pos-
sessed antimicrobial activity against human pathogenic fungi
and bacteria (Lv etal. 2010).
Piriformospora indica Sav. Verma, Aj. Varma, Rexer, G. Kost &
P. Franken (Sebacinales, Basidiomycota), a fungus isolated from
an AM spore collected from desert soil in India, is able to colo-
nize the roots of various plant species as an endophyte (Verma
et al. 1998; Figure 38.2C). Inoculation with the fungus and
application of fungal culture induced resistance of their hosts
against biotic and abiotic stress (Varma etal. 2001; Deshmukh
and Kogel 2007; Sering etal. 2007; Achatz etal. 2010). Due to
its ease of culture, this fungus serves as a model organism for
the study of benecial plant–microbe interactions and a new
tool for improving plant production systems. Colonization was
inter- and intracellular with coils and branches or round chla-
mydospore-like structures and no arbuscules. Neither shoot nor
stelar tissues were colonized. Recently, sebacinalean endophytes
were found to be universally present as symptomless endophytes
in many liverworts, bryophytes, pteridophytes, and herbaceous
angiosperms, for example, wheat, maize, and the model plant
Arabidopsis thaliana (Weiss etal. 2011).
3. Endophyte–Plant Interactions
Chinese cabbage seedlings from seed treated with the two
C. chaetospira strains isolated by Narisawa etal. (1998) appeared
healthy, and inoculation with one of the isolates promoted
plant growth. Similarly, Mycocentrospora acerina (R. Hartig)
Deighton, another DSE, promoted root development of
S. involucrata (Wu etal. 2010). Inoculation with Piriformospora
indica and application of fungal culture ltrate promoted plant
growth and seed yield (Varma etal. 2001; Deshmukh and Kogel
2007; Sering etal. 2007; Achatz etal. 2010).
Growth promotion and improved uptake of phosphorus were
observed also in cotton when the roots were colonized endo-
phytically by C. foecundissimum Sacc. & Marchal (Gasoni and
Stegman De Gurnkel 1997). Intercellular hyphae formed dense
layers on the distal (outer) side of the endodermis. e fungus
grew also intracellularly in root hairs.
4. Endophyte–Environment Interactions
Inoculation of DSE (Cadophora and Rhizoctonia species)
onto aseptically grown seedlings of the alpine sedges Carex
curvula All. and Carex firma Host. resulted in a significant
increase of dry matter production in C. firma but not in C.
curvula compared to uninoculated controls (Haselwandter
and Read 1982). The authors concluded that the function of
the relationship between Carex roots and their DSE may be
comparable to that found between plants and AM fungi. Like
AM, DSE provided improved phosphorus supply to the plant.
DSE may replace AM in stressed environments. This hypoth-
esis is supported by the findings of Currah and Van Dyk
(1986) who observed roots growing in alpine soils with little
organic matter to have DSE and those growing in habitats
with visibly more organic matter to have AM. Three alpine
species of the Fabaceae (Astragalus alpinus L., A. vexilliflexus
E. Sheld., Oxytropis jordalii A.E. Porsild), a family that is usu-
ally endomycorrhizal in other habitats, lacked AM but were
colonized by DSE (Currah and Van Dyk 1986), an observa-
tion similar to that made by Christie and Nicolson (1983)
for two grass species in the Antarctic region. Conversely,
O’Dell and Trappe (1992) detected AM in Astragalus cottonii
M.E. Jones, Lupinus latifolius Lindl. ex J. Agardh, L. lepidus
Douglas ex Lindl., and Oxytropis campestris (L.) DC. from
alpine habitats. The two Lupinus species and O. campestris
were also colonized by septate endophytes, whereas A. cot-
tonii was not. One of the DSE observed in the roots of L. lati-
folius was later on identified as Phialocephala fortinii (O’Dell
etal. 1993).
AM fungi were absent in Xenophyllum rosenii (R.E. Fr.)
V.A. Funk and Perezia coerulescens Wedd. (both Asteraceae),
but roots of both plant species were heavily colonized by DSE
fungi at 5391 m asl in the Peruvian Andes (Schmidt etal. 2008;
Figure 38.3B). At slightly lower elevations (5240–5250 m),
AM fungi were present while DSE fungi were rare except in
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38-22 Root–Rhizosphere Interactions
Bartsia pumila Benth. (Scrophulariaceae) and plants outside
of the Asteraceae. In Colorado at 4300 m asl, AM fungi were
rare, but all examined plants were colonized by DSE fungi
(Schmidt etal. 2008). Absence of AM fungi and presence of
dark septate hyphae were also observed for roots of various
herbaceous plant species collected in Arctic Canada (Bledsoe
etal. 1990). DSE occurred also in several alpine plants in the
Canadian Rocky Mountains (Stoyke and Currah 1991). In
contrast, Kohn and Stasovski (1990) found no DSE in roots
collected in arctic Canada, but AM was observed in one plant
species. Ruotsalainen etal. (2004) could not nd any consis-
tent correlation between the colonization of various Arctic–
alpine plants by AM or DSE and altitude in Northern Norway.
DSE might not only replace AM at high altitudes and latitudes
but also in acidic soils as suggested by Postma etal. (2007)
who found that colonization of herbaceous plants (Galium
odoratum (L.) Scop., Mercurialis perennis L., Stellaria nemo-
rum L.) by DSE increased with decreasing pH whereas colo-
nization by AM decreased. e same authors also detected a
positive correlation between leaf magnesium concentrations
and the presence of DSE in G. odoratum. DSE are probably the
most widespread root–fungus association in polar regions,
but their roles in plant nutrition and survival are still poorly
understood (Newsham etal. 2009). Li etal. (2005) detected
considerable colonization of roots of Trifolium repens L. and
Plantago asiatica L. by DSE. Colonization by DSE correlated
with relative humidity and sunlight hours but not with AM
colonization, temperature, rainfall, nitrogen, phosphorus
potassium, or organic matter content in the soil.
V. Root Endophytes of Woody
Plant Species
Many shrub and trees species belonging to various plant families
were examined for the presence of root endophytes (Tables 38.4
through 38.6). Members of the Cupressaceae (Lihnell 1939; Hennon
et al. 1990), Ericaceae (including Epacridaceae) (Oberholzer-
Tschütscher 1982; Widler and Müller 1984; Hutton etal. 1994;
Ahlich and Sieber 1996; Steinke etal. 1996; Hambleton and Currah
1997; Vodnik etal. 1997; Verkley etal. 2003; Ruotsalainen etal.
2004;Hambleton and Sigler 2005; Sigler etal. 2005; Grünig etal.
2009; Newsham etal. 2009; Bagyalakshmi etal. 2010; Kjoller etal.
2010; Tian etal. 2011), and Pinaceae (Bloomberg 1966; Parkinson
and Crouch 1969; Galaaen and Venn 1979; Kowalski 1982a,b;
Courtois and Ruschen 1987; Summerbell 1989; Courtois 1990b;
Danielson and Visser 1990; Kattner and Schönhar 1990; Fisher
etal. 1991a; Manka and Mroczkiewicz 1991; Heslin etal. 1992;
Holdenrieder and Sieber 1992; Kattner 1992a; Ahlich and Sieber
1996; Horton etal. 1998; Grönberg etal. 2006; Kaparakis and Sen
2006; Menkis etal. 2006; Brenn etal. 2008; Grünig etal. 2008b,
2009; Bachmann 2010; Kandalepas et al. 2010; Rivera-Orduna
etal. 2011; Wagg etal. 2011) are among the most intensively stud-
ied plant species. Some broadleaf tree and shrub species have been
examined as well (Currah and Van Dyk 1986; Domanski and
Kowalski 1987; Summerbell 1989; Sridhar and Bärlocher 1992;
Cother and Gilbert 1994; Fisher etal. 1995a, 1995b; Iqbal etal.
1995; Ahlich and Sieber 1996; Raviraja etal. 1996; Werner etal.
1997; Barrow etal. 2004; Beauchamp etal. 2005; Newsham etal.
2009; Bagyalakshmi etal. 2010; Kandalepas etal. 2010).
Since presence and function of fungal root endophytes have
most intensively been studied for members of the Ericales and
Pinales, Sections V.A and V.B will be dedicated to these two
groups of hosts.
A. Root Endophytes of Woody Ericales
Non-mycorrhizal endophytes are oen isolated from
ericaceous hosts in addition to the classical mycorrhi-
zal fungi Pezoloma (Hymenoscyphus) ericae (D.J. Read)
Baral (anamorph: Scytalidium vaccinii Dalpé, Litten
& Sigler) and Oidiodendron spp. Species of the genera
Acephala, Cryptosporiopsis, Cylindrocarpon, Meliniomyces,
Phialocephala, and Trichocladium are most oen observed
(Oberholzer-Tschütscher 1982; Widler and Müller 1984;
Väre etal. 1992; Hambleton and Currah 1997; Vodnik etal.
1997; Verkley etal. 2003; Hambleton and Sigler 2005; Sigler
et al. 2005; Grünig et al. 2006; Grünig et al. 2008b, 2009,
2011; Queloz et al. 2010; Table 38.4). Phialocephala forti-
nii s.l. were present in 17 of 19 ericaceous hosts from boreal
and alpine sites in Alberta, Canada (Hambleton and Currah
1997), in Gaultheria shallon Pursh from coastal British
Columbia, Canada, and in Calluna vulgaris (L.) Hull as well
as Vaccinium myrtillus L. from a subalpine site in Switzerland
(Ahlich and Sieber 1996; Grünig etal. 2006). A fungus iso-
lated by Vodnik etal. (1997) from the roots of Erica carnea
L. from Slovenia and deposited as Phialocephala fortinii at
UAMH as strain number 8433 could meanwhile be identi-
ed as Phialocephala subalpina Grünig & T.N. Sieber (Grünig
et al. 2008b). A hitherto unknown species of Phialocephala
was isolated from Vaccinium vitis-idaea, V. myrtillus and
V. uliginosum growing on permafrost soil in the Jura moun-
tains of Switzerland and described as Phialocephala glacialis
Grünig & T.N. Sieber (Grünig etal. 2009). Interestingly, the
same species was also detected in healthy needles of Norway-
spruce trees nearby. Allseven described species of P. fortinii
s.l. and A. applanata could be detected in roots of V. myrtillus
and other Vacciniumspecies in many countries in Europe and
some of them also in North America (Queloz 2010; Table 38.4).
Unidentied DSE were also isolated from Symplocos cochinchi-
nensis (Lour.) S. Moore and several other plant species from
shola vegetation in the Western Ghats region, southern India
(Bagyalakshmi etal. 2010).
Cryptosporiopsis species (anamorphic Pezicula species) are
regularly isolated from rhizomes and ne roots of ericaceous
plants. Cryptosporiopsis ericae Sigler from roots of Vaccinium
membranaceum Douglas ex Torr., V. ovalifolium Sm. and G.
shallon Pursh, and C. brunnea Sigler from G. shallon from
northwestern North America were described as new species
(Sigler etal. 2005), and a Cryptosporiopsis species was isolated
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38-23Fungal Root Endophytes
TABLE 38.4 Endophytes in Ericoid Plants (Family Ericaceae)
Endophyte Host
Type of
Experiment
b
Special Eect
c
ReferencesGenus
a
Species
a
Fungus Order
a
DSE/Not DSE Species Plant Order
Woody/
Herbaceous
Acephala applanata Helotiales DSE Vaccinium
myrtillus
Ericales Woody shrub Isol Queloz (2010)
Acephala sp. 1 Helotiales DSE Cassiope
mertensiana
Ericales Woody shrub Isol Grünig etal. (2009)
Acephala sp. 3 Helotiales DSE Vaccinium
myrtillus
Ericales Woody shrub Isol Grünig etal. (2009)
Acephala sp. 7 Helotiales DSE Calluna vulgaris Ericales Woody shrub Isol Pietrowski (unpublished)
Cryptocline dubia Helotiales Not DSE Arctostaphylos
uva-ursi
Ericales Woody shrub Isol Widler and Müller (1984)
Cryptosporiopsis sp. Helotiales DSE Arctostaphylos
uva-ursi
Ericales Woody shrub Isol Widler and Müller (1984)
Cryptosporiopsis sp. Helotiales DSE Erica carnea Ericales Woody shrub Isol Oberholzer-Tschütscher (1982)
Cryptosporiopsis brunnea Helotiales DSE Gaultheria shallon Ericales Woody shrub Isol Sigler etal. (2005)
Cryptosporiopsis ericae Helotiales Variable Vaccinium
membranaceum
Ericales Woody shrub Isol Sigler etal. (2005)
Cryptosporiopsis rhizophila Helotiales DSE Erica tetralix Ericales Woody shrub Isol Verkley etal. (2003)
Cylindrocarpon didymum Hypocreales Not DSE Arctostaphylos
uva-ursi
Ericales Woody shrub Isol Widler and Müller (1984)
Cylindrocarpon didymum Hypocreales Not DSE Erica carnea Ericales Woody shrub Isol Oberholzer-Tschütscher (1982)
Cystodendron dryophilum Helotiales Not DSE Arctostaphylos
uva-ursi
Ericales Woody shrub Isol Widler and Müller (1984)
Gliocladium solani f. nigrovirens Hypocreales Variable Arctostaphylos
uva-ursi
Ericales Woody shrub Isol Widler and Müller (1984)
Herpotrichia sp. Pleosporales DSE Vaccinium sp. Ericales Woody shrub Isol Müller (unpublished)
Ilyonectria radicicola Hypocreales Not DSE Erica carnea Ericales Woody shrub Isol Vodnik etal. (1997)
Marasmius scorodonius Agaricales Not DSE Arctostaphylos
uva-ursi
Ericales Woody shrub Isol Widler and Müller (1984)
Meliniomyces sp. 3 Leotiomycetes Variable Gaultheria shallon Ericales Woody shrub Isol Hambleton and Sigler (2005)
Meliniomyces sp. 3 Leotiomycetes Variable Vaccinium
myrtillus
Ericales Woody shrub Isol Hambleton and Sigler (2005)
Meliniomyces variabilis Leotiomycetes DSE Andromeda
polifolia
Ericales Woody shrub Isol Kjoller etal. (2010)
Meliniomyces variabilis Leotiomycetes DSE Empetrum
hermaphroditum
Ericales Woody shrub Isol Kjoller etal. (2010)
Meliniomyces variabilis Leotiomycetes DSE Rhododendron
albiorum
Ericales Woody shrub Isol Hambleton and Sigler (2005)
Meliniomyces variabilis Leotiomycetes DSE Vaccinium
uliginosum
Ericales Woody shrub Isol Kjoller etal. (2010)
Meliniomyces variabilis Leotiomycetes DSE Vaccinium
vitis-idaea
Ericales Woody shrub Isol Kjoller etal. (2010)
(continued)
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38-24 Root–Rhizosphere Interactions
TABLE 38.4 (continued) Endophytes in Ericoid Plants (Family Ericaceae)
Endophyte Host
Type of
Experiment
b
Special Eect
c
ReferencesGenus
a
Species
a
Fungus Order
a
DSE/Not DSE Species Plant Order
Woody/
Herbaceous
Microdochium bolleyi Xylariales DSE Polemonium
boreale
Ericales Herb Isol Väre etal. (1992)
Monodictys putredinis Dothideomycetes Not DSE Erica carnea Ericales Woody shrub Isol Oberholzer-Tschütscher (1982)
Oidiodendron griseum Dothideomycetes DSE Loiseleuria
procumbens
Ericales Woody shrub Isol Stoyke and Currah (1991),
Hambleton and Currah
(1997)
Oidiodendron griseum Dothideomycetes DSE Phyllodoce
glanduliora
Ericales Woody shrub Isol Stoyke and Currah (1991),
Hambleton and Currah
(1997)
Oidiodendron griseum Dothideomycetes DSE Vaccinium
myrtilloides
Ericales Woody shrub Isol Stoyke and Currah (1991),
Hambleton and Currah
(1997)
Oidiodendron griseum Dothideomycetes DSE Vaccinium
vitis-idaea
Ericales Woody shrub Isol Stoyke and Currah (1991),
Hambleton and Currah
(1997)
Oidiodendron maius Dothideomycetes DSE Various spp. Ericales Woody shrub Isol Hambleton and Currah (1997)
Pezoloma ericae Leotiomycetes DSE Calluna vulgaris Ericales Woody shrub Isol Read (1974)
Pezoloma ericae Leotiomycetes DSE Ledum
groenladicum
Ericales Woody shrub Isol Hambleton etal. (1999)
Phialocephala fortinii s.l. Helotiales DSE Polemonium
boreale
Ericales Herb Isol Väre etal. (1992)
Phialocephala fortinii s.l. Helotiales DSE Various spp. Ericales N.A. Isol Hambleton and Currah (1997)
Phialocephala europaea Helotiales DSE Vaccinium
myrtillus
Ericales Woody shrub Isol Queloz (2010)
Phialocephala europaea Helotiales DSE Vaccinium
uliginosum
Ericales Woody shrub Isol Queloz (2010)
Phialocephala europaea Helotiales DSE Vaccinium
vitis-idaea
Ericales Woody shrub Isol Queloz (2010)
Phialocephala fortinii s.s. Helotiales DSE Cassiope
mertensiana
Ericales Woody shrub Isol Queloz (2010)
Phialocephala fortinii s.s. Helotiales DSE Kalmia
microphylla
Ericales Woody shrub Isol Queloz (2010)
Phialocephala fortinii s.s. Helotiales DSE Luteka pectinata Ericales Woody shrub Isol Queloz (2010)
Phialocephala fortinii s.s. Helotiales DSE Vaccinium
myrtillus
Ericales Woody shrub Isol Grünig etal. (2008a)
Phialocephala fortinii s.s. Helotiales DSE Vaccinium
uliginosum
Ericales Woody shrub Isol Queloz (2010)
Phialocephala fortinii s.s. Helotiales DSE Vaccinium
vitis-idaea
Ericales Woody shrub Isol Queloz (2010)
Phialocephala glacialis Helotiales DSE Vaccinium
myrtillus
Ericales Woody shrub Isol Grünig etal. (2009)
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38-25Fungal Root Endophytes
Phialocephala helvetica Helotiales DSE Erica carnea Ericales Woody shrub Isol Queloz (2010)
Phialocephala helvetica Helotiales DSE Vaccinium
myrtillus
Ericales Woody shrub Isol Queloz (2010)
Phialocephala letzii Helotiales DSE Vaccinium
myrtillus
Ericales Woody shrub Isol Queloz (2010)
Phialocephala letzii Helotiales DSE Vaccinium
vitis-idaea
Ericales Woody shrub Isol Queloz (2010)
Phialocephala subalpina Helotiales DSE Arctostaphylos
uva-ursi
Ericales Woody shrub Isol Queloz (2010)
Phialocephala subalpina Helotiales DSE Empetrum
hermaphroditum
Ericales Woody shrub Isol Queloz (2010)
Phialocephala subalpina Helotiales DSE Erica carnea Ericales Woody shrub Isol Vodnik etal. (1997)
Phialocephala subalpina Helotiales DSE Vaccinium
myrtillus
Ericales Woody shrub Isol Grünig etal. (2008a)
Phialocephala subalpina Helotiales DSE Vaccinium
uliginosum
Ericales Woody shrub Isol Queloz (2010)
Phialocephala subalpina Helotiales DSE Vaccinium
vitis-idaea
Ericales Woody shrub Isol Queloz (2010)
Phialocephala turicensis Helotiales DSE Vaccinium
myrtillus
Ericales Woody shrub Isol Queloz (2010)
Phialocephala uotilensis Helotiales DSE Vaccinium
myrtillus
Ericales Woody shrub Isol Queloz (2010)
Phialophora bubakii Chaetothyriales Not DSE Erica carnea Ericales Woody shrub Isol Oberholzer-Tschütscher (1982)
Rhizoctonia sp. Cantharellales DSE Erica carnea Ericales Woody shrub Isol Vodnik etal. (1997)
Trichocladium opacum Sordariales DSE Arctostaphylos
uva-ursi
Ericales Woody shrub Isol Widler and Müller (1984)
Trichocladium opacum Sordariales Not DSE Erica carnea Ericales Woody shrub Isol Oberholzer-Tschütscher (1982)
Varicosporium sp. Helotiales DSE Arctostaphylos
uva-ursi
Ericales Woody shrub Isol Widler and Müller (1984)
Unidentied DSE DSE Empetrum
hermaphroditum
Ericales Woody shrub Isol a Ruotsalainen etal. (2010)
Unidentied DSE DSE Symplocos
cochinchinensis
Ericales Tree Isol Bagyalakshmi etal. (2010)
a
Genus, species and order (family) names according to index fungorum (http://www.indexfungorum.org/Names/Names.asp, December 20, 2011). If both the teleomorph (sexual reproductive stage) and
the anamorph (asexual reproductive stage) are produced, the name of the teleomorph is given. Names of anamorph(s) can be retrieved from the list of the teleomorph’s synonyms provided in the index.
e next lower taxon is given if the Fungus order is not known with certainty (“incertae sedis”).
b
Isol, isolation from surface-sterilized roots.
c
Special eect details: (a) Colonization frequency positively correlated with light intensity.
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38-26 Root–Rhizosphere Interactions
from C. vulgaris, Erica tetralix L., V. vitis-idaea, and V. myrtil-
lus in the Netherlands and described as C. rhizophila Verkley &
Zijlstra (Verkley etal. 2003).
Meliniomyces species seem to be widespread endophytes in
roots of Andromeda polifolia L., Empetrum hermaphroditum
Hagerup, Phyllodoce empetriformis (Sm.) D. Don, Rhododendron
albiorum Hook., V. membranaceum, V. uliginosum L., and
V. vitis-idaea in alpine heathlands and subarctic mires (Hambleton
and Sigler 2005; Kjoller etal. 2010).
Dark-colored, sterile, and slow-growing mycelia were also
isolated in Australia from Epacridaceae, a family close to the
Ericaceae but distributed in the Southern Hemisphere (Hutton
et al. 1994). Pectic zymogram analysis revealed that none of
the Australian isolates matched fungi known to be infective
with Ericaceae in the Northern Boreal and Alpine Zone, for
example, Pezoloma ericae and Oidiodendron spp., even though
all isolates appeared morphologically similar and had simi-
lar growth rates. Two-thirds of the endophytes isolated from
Leucopogon parviorus (H. Andrews) Lindl., another represen-
tative of Epacridaceae, were sterile and had slow growth rates.
Some of them were dark and similar to P. ericae. Inspection of
roots under the light microscope revealed that there were at least
two dierent fungi that consistently formed ericoid mycorrhizal
structures at these sites, possibly P. ericae and Oidiodendron sp.
(Steinke etal. 1996).
1. Anatomy
Dark septate inter- and intracellular hyphae and microsclerotia
were observed in epidermal cells (EPs) of ericaceous “hair roots”
of Gaultheria poeppiggi DC. collected in the Cordoba mountains
of central Argentina (Urcelay 2002; Figure 38.3C). Similarly, DSE
were present in hair roots of Woollsia pungens (Cav.) F. Muell.
in New South Wales (Chambers etal. 2008). Phialocephala for-
tinii s.s. occurred as extensive wes of dark, septate hyphae on
the root surface and as intracortical sclerotia of compact, darkly
pigmented and irregularly lobed, thick-walled hyphae in axenic
seedlings of Menziesia ferruginea Sm. (Ericaceae) (Stoyke and
Currah 1991, 1993). Intracellular coils and colonization of the
vascular tissues were not observed. is association diers from
the ericoid mycorrhizal type, in which elaborate intracellular
hyphal branches are ensheathed by invaginations of the host
plasma membrane but represents a fungus–root association
that seems to be common in alpine plants. Similarly, the pattern
of root colonization of Rhododendron brachycarpum D.Don by
Phialocephala fortinii s.l. diered from that observed in ericoid
mycorrhizae (Currah etal. 1993). Phialocephala fortinii s.l. colo-
nized the EPs, in which it sometimes formed black sclerotia, but
was not able to colonize the thick-walled, phenol-rich exoder-
mal layer of hair roots. Intercellular colonization between epi-
dermis and exodermis layers was, however, common.
2. Endophyte–Plant Interactions
Presence of Phialocephala fortinii s.s. in axenic cultures of
M. ferruginea (Ericaceae) caused a 10-fold increase of seed-
ling mortality compared to mortality of control plants (Stoyke
and Currah 1993). Established plants and growth rates were,
however, not aected. Phialocephala fortinii-like DSE strains
were shown to dier in virulence against R. brachycarpum.
In resynthesis experiment, one strain had a signicant nega-
tive eect on dry weight accumulation of seedlings, but
plants looked healthy, whereas a second one had no eect
(Currah etal. 1993).
3. Endophyte–Environment Interactions
Phialocephala fortinii s.l. was only rarely detected in erica-
ceous roots from an acidic wetland but occurred quite fre-
quently in roots from an alpine site in Alberta (Hambleton
and Currah 1997). Phialocephala subalpina and a Rhizoctonia
sp. were shown to be sensitive to heavy metals and mainly
occurred in roots of E. carnea growing in non-polluted soil,
whereas Cladosporium herbarum (Pers.) Link and Ilyonectria
radicicola were the fungi most frequently isolated from
plant roots originating from lead contaminated soil (Vodnik
etal. 1997). Stress levels along three abiotic gradients (pol-
lution, elevation, distance from seashore) on Kola Peninsula
in Russia had no effect on root colonization of crowberry
(E. hermaphroditum) by DSE, but distance to mountain birch
(Betula pubescens ssp. czerepanovii (Orlova) Hämet-Ahti)
had an effect; colonization was higher outside the canopy
area (Ruotsalainen etal. 2010). Substitution of AM fungi at
higher altitude could not be observed for Trientalis europaea
L. and several other alpine plants collected along a gradient
from 0 to 1400 m at Mt. Paras, North Norway (Ruotsalainen
etal. 2004).
B. Root Endophytes of Pinales
Endophyte species diversity strongly depends on the degree of
surface sterilization and the sample size; the weaker the ster-
ilization and the more samples, the more species are detected.
For example, Holdenrieder and Sieber (1992) could detect 120
taxa in >500 serially washed Norway-spruce root segments.
However, if surface sterilization is applied, diversity of fun-
gal communities steeply decreases. Moreover, the diversity of
endophyte communities in roots is also much lower than that
of endophyte communities in aboveground plant parts (Sieber
1988, 1989, 2007; Sridhar and Bärlocher 1992; Kowalski 1993;
Sieber-Canavesi and Sieber 1993; Ahlich and Sieber 1996;
Menkis 2004; Rivera-Orduna etal. 2011). Only ve species of
endophytes (Alternaria sp., Cochliobolus sp., Penicillium sp.,
Phoma medicaginis, and a species of the Xylariaceae) could
be isolated from roots of Taxus globosa Schltdl. in Mexico,
whereas bark contained at least 17 dierent species (Rivera-
Orduna etal. 2011). More than 90% of the isolates collected
from root tips of Picea abies and Pinus sylvestris L. belonged
to the genus Phialocephala (Menkis 2004; Table 38.5). Non-
mycorrhizal ne roots of healthy Abies alba Mill., Picea abies,
and Pinus sylvestris in Europe are heavily colonized by endo-
phytic fungi. Depending on the site, between 88% and 100%
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38-27Fungal Root Endophytes
TABLE 38.5 Endophytes in Conifers
Endophyte Host
Type of
Experiment
b
Special Eect
c
ReferencesGenus
a
Species
a
Fungus Order
a
DSE/Not DSE Species Plant Order
Woody/
Herbaceous
Acephala applanata Helotiales DSE Abies alba Pinales Tree Isol Queloz (2010)
Acephala applanata Helotiales DSE Picea abies Pinales Tree Isol Grünig and Sieber (2005)
Acephala applanata Helotiales DSE Pinus mugo Pinales Tree Isol Queloz (2010)
Acephala applanata Helotiales DSE Pinus sylvestris Pinales Tree Isol Queloz (2010)
Acephala macrosclerotiorum Helotiales DSE Picea abies Pinales Tree Isol Menkis etal. (2004)
Acephala macrosclerotiorum Helotiales DSE Pinus sylvestris Pinales Tree Isol Münzenberger etal. (2009)
Acephala sp. 2 Helotiales DSE Pinus sylvestris Pinales Tree Isol Grünig etal. (2009)
Acephala sp. 4 Helotiales DSE Pinus banksiana Pinales Tree Isol Grünig etal. (2009)
Alternaria sp. Pleosporales DSE Taxus globosa Pinales Tree Isol Rivera-Orduna etal. (2011)
Anguillospora liformis Pleosporales Not DSE Picea glauca Pinales Tree Isol Sridhar and Bärlocher (1992)
Aspergillus versicolor Eurotiales Not DSE Picea abies Pinales Tree Isol Courtois (1990a,b)
Cadophora nlandica Helotiales DSE Picea abies Pinales Tree Isol Menkis (unpublished)
Cadophora nlandica Helotiales DSE Pinus resinosa Pinales Tree in vitro exp a Alberton etal. (2010)
Cadophora nlandica Helotiales DSE Pinus sylvestris Pinales Tree Isol Wang and Wilcox (1985)
Cadophora malorum Helotiales DSE Picea abies Pinales Tree Isol Sieber (unpublished)
Cadophora sp. 1 Helotiales DSE Picea abies Pinales Tree Isol Queloz (2010)
Cadophora sp. 2 Helotiales DSE Abies alba Pinales Tree Isol Ahlich and Sieber (1996)
Cadophora sp. 2 Helotiales DSE Pinus sylvestris Pinales Tree Isol Bachmann (2010)
Chloridium paucisporum Chaetosphaeriales DSE Pinus resinosa Pinales Tree In vitro exp a Alberton etal. (2010)
Cladophialophora chaetospira Chaetothyriales DSE Picea abies Pinales Tree Isol Crous etal. (2007)
Cochliobolus sp. Pleosporales DSE Taxus globosa Pinales Tree Isol Rivera-Orduna etal. (2011)
Coniothyrium sp. Pleosporales Not DSE Pinus sylvestris Pinales Tree Isol Görke (1998)
Cryptosporiopsis abietina Helotiales Not DSE Picea abies Pinales Tree Isol Kattner and Schönhar (1990)
Cryptosporiopsis radicicola Helotiales DSE Abies alba Pinales Tree Isol Ahlich and Sieber (1996)
Cryptosporiopsis radicicola Helotiales DSE Pinus sylvestris Pinales Tree Isol Ahlich and Sieber (1996)
Cryptosporiopsis sp. Helotiales DSE Chamaecyparis
nootkatensis
Pinales Tree Isol Hennon etal. (1990)
Cryptosporiopsis cf melanigena Helotiales DSE Picea abies Pinales Tree Isol Queloz (2010)
Cryptosporiopsis ericae Helotiales Variable Picea abies Pinales Tree Isol Sigler etal. (2005)
Cylindrocarpon aquaticum Hypocreales Not DSE Picea glauca Pinales Tree Isol Sridhar and Bärlocher (1992)
Cylindrocarpon didymum Hypocreales Not DSE Chamaecyparis
nootkatensis
Pinales Tree Isol Hennon etal. (1990)
Cylindrocarpon didymum Hypocreales Not DSE Pinus sylvestris Pinales Tree Isol Ahlich and Sieber (1996)
Cylindrocarpon obtusisporum Hypocreales Variable Picea abies Pinales Tree Isol Queloz (2010)
Didymella bryoniae Pleosporales DSE Picea abies Pinales Tree Isol Queloz (2010)
Didymosphaeria sp. Pleosporales DSE Picea abies Pinales Tree Isol Brenn etal. (2008)
Gelatinosporium sp. Helotiales Not DSE Chamaecyparis
nootkatensis
Pinales Tree Isol Hennon etal. (1990)
(continued)
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38-28 Root–Rhizosphere Interactions
TABLE 38.5 (continued) Endophytes in Conifers
Endophyte Host
Type of
Experiment
b
Special Eect
c
ReferencesGenus
a
Species
a
Fungus Order
a
DSE/Not DSE Species Plant Order
Woody/
Herbaceous
Herpotrichia sp. Pleosporales DSE Picea abies Pinales Tree Isol Grünig (unpublished)
Humicolopsis cephalosporioides Pezizomycotina DSE Picea abies Pinales Tree Isol Courtois (1990a,b)
Ilyonectria radicicola Hypocreales Not DSE Picea abies Pinales Tree Isol Görke (1998)
Ilyonectria radicicola Hypocreales Variable Pinus sylvestris Pinales Tree Isol Bachmann (2010)
Leptosphaeria sp. 1 Pleosporales DSE Pinus sylvestris Pinales Tree Isol Bachmann (2010)
Macrophomina phaseolina Botryosphaeriales DSE Pinus sylvestris Pinales Tree Isol Bachmann (2010)
Meliniomyces sp. 2 Leotiomycetes Variable Pinus sylvestris Pinales Tree Isol Hambleton and Sigler (2005)
Meliniomyces sp. 4 Leotiomycetes Variable Pinus sylvestris Pinales Tree Isol Hambleton and Sigler (2005)
Meliniomyces variabilis Leotiomycetes DSE Pinus resinosa Pinales Tree In vitro exp a Alberton etal. (2010)
Meliniomyces variabilis Leotiomycetes DSE Tsuga heterophylla Pinales Tree Isol Hambleton and Sigler (2005)
Meliniomyces vraolstadiae Leotiomycetes DSE Pinus resinosa Pinales Tree In vitro exp a Alberton etal. (2010)
Paecilomyces sp. Eurotiales Not DSE Pinus radiata Pinales Tree Isol Sieber and Langenegger
(unpublished)
Penicillium nigricans Eurotiales DSE Picea abies Pinales Tree Isol Courtois (1990a,b)
Phialocephala europaea Helotiales DSE Abies alba Pinales Tree Isol Queloz (2010)
Phialocephala europaea Helotiales DSE Larix kaempferi Pinales Tree Isol Queloz (2010)
Phialocephala europaea Helotiales DSE Picea abies Pinales Tree Isol Grünig etal. (2008a)
Phialocephala europaea Helotiales DSE Picea glauca Pinales Tree Isol Queloz (2010)
Phialocephala europaea Helotiales DSE Pinus sylvestris Pinales Tree Isol Queloz (2010)
Phialocephala fortinii s.l. Helotiales DSE Abies alba Pinales Tree Isol Ahlich and Sieber (1996)
Phialocephala fortinii s.l. Helotiales DSE Picea abies Pinales Tree Isol Ahlich and Sieber (1996)
Phialocephala fortinii s.l. Helotiales DSE Pinus resinosa Pinales Tree In vitro exp a Alberton etal. (2010)
Phialocephala fortinii s.l. Helotiales DSE Larix decidua Pinales Tree Isol Grünig etal. (2008a)
Phialocephala fortinii s.s. Helotiales DSE Pinus sylvestris Pinales Tree Isol Ahlich and Sieber (1996)
Phialocephala fortinii s.s. Helotiales DSE Abies alba Pinales Tree Isol Queloz (2010)
Phialocephala fortinii s.s. Helotiales DSE Larix decidua Pinales Tree Isol Queloz (2010)
Phialocephala fortinii s.s. Helotiales DSE Picea abies Pinales Tree Isol Grünig etal. (2008a)
Phialocephala fortinii s.s. Helotiales DSE Picea glauca Pinales Tree Isol Queloz (2010)
Phialocephala fortinii s.s. Helotiales DSE Picea mariana Pinales Tree Isol Queloz (2010)
Phialocephala fortinii s.s. Helotiales DSE Pinus cembra Pinales Tree Isol Queloz (2010)
Phialocephala fortinii s.s. Helotiales DSE Pinus mugo Pinales Tree Isol Queloz (2010)
Phialocephala fortinii s.s. Helotiales DSE Pinus sylvestris Pinales Tree Isol Grünig etal. (2008a)
Phialocephala helvetica Helotiales DSE Juniperus sp. Pinales Tree Isol Queloz (2010)
Phialocephala helvetica Helotiales DSE Picea abies Pinales Tree Isol Grünig etal. (2008a)
Phialocephala helvetica Helotiales DSE Pinus leucodermis Pinales Tree Isol Queloz (2010)
Phialocephala helvetica Helotiales DSE Pinus sylvestris Pinales Tree Isol Queloz (2010)
Phialocephala letzii Helotiales DSE Abies alba Pinales Tree Isol Queloz (2010)
Phialocephala letzii Helotiales DSE Picea abies Pinales Tree Isol Grünig etal. (2008a)
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38-29Fungal Root Endophytes
Phialocephala sphaeroides Helotiales DSE Picea abies Pinales Tree Isol Grünig etal. (2009)
Phialocephala subalpina Helotiales DSE Abies alba Pinales Tree Isol Queloz (2010)
Phialocephala subalpina Helotiales DSE Abies spectabilis Pinales Tree Isol Queloz (2010)
Phialocephala subalpina Helotiales DSE Picea abies Pinales Tree Isol Grünig etal. (2008a)
Phialocephala subalpina Helotiales DSE Picea glauca Pinales Tree Isol Queloz (2010)
Phialocephala subalpina Helotiales DSE Pinus mugo Pinales Tree Isol Queloz (2010)
Phialocephala subalpina Helotiales DSE Pinus strobus Pinales Tree Isol Queloz (2010)
Phialocephala subalpina Helotiales DSE Pinus sylvestris Pinales Tree Isol Grünig etal. (2008a)
Phialocephala subalpina Helotiales DSE Tsuga dumosa Pinales Tree Isol Queloz (2010)
Phialocephala turicensis Helotiales DSE Abies alba Pinales Tree Isol Queloz (2010)
Phialocephala turicensis Helotiales DSE Picea abies Pinales Tree Isol Queloz (2010)
Phialocephala turicensis Helotiales DSE Taxus baccata Pinales Tree Isol Queloz (2010)
Phialocephala uotilensis Helotiales DSE Abies alba Pinales Tree Isol Queloz (2010)
Phialocephala uotilensis Helotiales DSE Picea abies Pinales Tree Isol Grünig etal. (2008a)
Phialophora melinii Helotiales Not DSE Chamaecyparis
nootkatensis
Pinales Tree Isol Hennon etal. (1990)
Phoma sp. 1 Pleosporales DSE Pinus sylvestris Pinales Tree Isol Bachmann (2010)
Phoma exigua Pleosporales DSE Picea abies Pinales Tree Isol Queloz (2010)
Phoma medicaginis Pleosporales DSE Taxus globosa Pinales Tree Isol Rivera-Orduna etal. (2011)
Phoma radicina Pleosporales DSE Pinus sylvestris Pinales Tree Isol Bachmann (2010)
Phomopsis sp. Diaporthales Not DSE Pinus radiata Pinales Tree Isol Sieber and Langenegger
(unpublished)
Rhizoctonia sp. Cantharellales Not DSE Pinus sylvestris Pinales Tree in vitro exp b Grönberg etal. (2006)
Sphaeropsis sapinea Pezizomycotina DSE Pinus radiata Pinales Tree Isol Sieber and Langenegger
(unpublished)
Sporidesmium sp. Pleosporales Not DSE Chamaecyparis
nootkatensis
Pinales Tree Isol Hennon etal. (1990)
Sydowia polyspora Dothideales DSE Pinus sylvestris Pinales Tree Isol Görke (1998)
Trichoderma hamatum Hypocreales Not DSE Picea abies Pinales Tree Isol Kattner and Schönhar (1990)
Trichoderma polysporum Hypocreales Not DSE Picea abies Pinales Tree Isol Kattner and Schönhar (1990)
Trichoderma viride Hypocreales Not DSE Picea abies Pinales Tree Isol Kattner and Schönhar (1990)
a
Genus, species and order (family) names according to index fungorum (http://www.indexfungorum.org/Names/Names.asp, December 20, 2011). If both the teleomorph (sexual reproductive stage) and
the anamorph (asexual reproductive stage) are produced, the name of the teleomorph is given. Names of anamorph(s) can be retrieved from the list of the teleomorph’s synonyms provided in the index.
e next lower taxon is given if the Fungus order is not known with certainty (“incertae sedis”).
b
Isol, isolation from surface-sterilized roots; in vitro exp, fungus used in in-vitro experiment(s).
c
Special eect details: (a) Plant growth stimulation at elevated CO
2
. (b) Stimulation of early root development.
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38-30 Root–Rhizosphere Interactions
of the trees examined in Finland, Germany, and Switzerland
had roots colonized by endophytes, and DSE were most abun-
dant (Ahlich and Sieber 1996; Görke 1998). ey were present
in between 53% and 90% of the trees, and the majority of the
isolates belonged to PAC. Up to 70% of the ne roots of a single
root system of Norway spruce (Picea abies) can be colonized by
DSE (Holdenrieder and Sieber 1992). Taxodium distichum (L.)
Rich. seems to be an exception regarding dominance of DSE,
because DSE were very rare in roots of this tree species and
occurred in only 0.33% of the root samples (Kandalepas etal.
2010). Whereas DSE, especially PAC, dominate the endophyte
communities, species of Cryptosporiopsis and Cylindrocarpon
occur sometimes also quite frequently in conifer roots
(Courtois 1990a; Kattner and Schönhar 1990; Holdenrieder
and Sieber 1992; Ahlich and Sieber 1996; Table38.5). A special
community was observed in submersed roots of Picea glauca
(Moench) Voss (Sridhar and Bärlocher 1992). e commu-
nity was dominated by aquatic hyphomycetes, for example,
Anguillospora liformis Greath. and Heliscus lugdunensis Sacc.
& erry (Table 38.5).
Non-mycorrhizal endophytes are oen associated with ecto-
mycorrhizae of conifers. DSE, Umbelopsis isabellina (Oudem.)
W. Gams, Penicillium spinulosum om, and Penicillium mon-
tanense M. Chr. & Backus were most frequently associated with
ectomycorrhizae of Picea mariana (Mill.) Britton, Sterns &
Poggenb. (Summerbell 1989). Oidiodendron sp. considered non-
mycorrhizal on conifers, and DSE were most frequently isolated
from ectomycorrhizae of Sitka spruce (Picea sitchensis (Bong.)
Carrière) in Irish forest mixed stands (Schild etal. 1988; Heslin
etal. 1992). Oidiodendron sp. and DSE appeared to be antag-
onistic. DSE were only abundant when Oidiodendron sp. was
rare and vice versa. Douglas-r seedlings preinoculated with
the ectomycorrhizal fungus Rhizopogon vinicolor A.H. Sm. and
outplanted on eastern Vancouver Island were to some extend
colonized by DSE aer one growing season (Berch and Roth
1993). DSE were shown to survive forest res as resident inocu-
lum and to colonize Pinus muricata D. Don seedlings right aer
germination (Horton etal. 1998). Eighteen percent of the seed-
lings sampled until 5 months aer germination were colonized
by AM fungi, ectomycorrhizal fungi, and DSE simultaneously.
Except for members of the Epacridaceae, root endophytes of
woody plant species have not been examined intensively in the
Southern Hemisphere. is is especially true for conifers. Root
samples of Pinus radiata D. Don collected at four sites in Western
Australia revealed Sphaeropsis sapinea (Fr.) Dyko & B. Sutton,
a fungus usually conned to pine needles in the Northern
Hemisphere, to be the main colonizer at two of the four sites
(Sieber and Langenegger, unpublished). A Paecilomyces sp. and
a Phomopsis sp. dominated at each one of the other two sites.
DSE are prevalent in roots of conifer seedlings in nurser-
ies and naturally regenerating seedlings in the forest. Primary
roots of 1-year-old nursery-grown Douglas-r (Pseudotsuga
menziesii (Mirb.) Franco) seedlings were most frequently
colonized by DSE, Fusarium spp., and Cylindrocarpon spp.
(Bloomberg 1966). Similarly, DSE were among the earliest and
most abundant root colonizers of nursery-grown seedlings of
Pinus banksiana Lamb., Pinus contorta Douglas ex Loudon, and
Picea glauca (Moench) Voss (Danielson and Visser 1990). e
frequency of root segments of nursery seedlings of Picea abies
and Pinus sylvestris L. colonized by endophytic fungi in general
varied between 0.5% and 10% and that by PAC between 0% and
4%, that is, colonization density was signicantly lower than
expected from densities observed in spruce forests (Brenn etal.
2008). Interestingly, PAC could only be detected in plants from
nurseries situated directly in forests or very close to forests but
not in plants from nurseries on agricultural plots, because PAC
are very rare in arable soils (Ahlich-Schlegel 1997). Endophytic
fungi were isolated from 1- to 5-year-old seedlings of Pinus
nigra var. laricio Maire sampled in an area of natural tree regen-
eration (Parkinson and Crouch 1969). DSE were most frequently
isolated from roots of 5-year-old seedlings and Penicillium spp.
dominated in roots of younger plants. e frequency of coloni-
zation by DSE varied between 30% and 100% among plant indi-
viduals. DSE did not show any preference for specic parts in
the root system. Penicillium spp. were, however, most frequently
isolated from the upper tap and upper lateral roots, whereas
Ilyonectria radicicola showed a preference for the lower vertical
roots.
1. Anatomy
Structural features of the endophyte–root symbioses of conifers
are best studied for symbioses with PAC fungi. In contrast to
mycorrhizal fungi, PAC are not conned to the root tips but can
occur everywhere in the root system from root tips to the bark
of coarse roots at the stem base. First- and second-order laterals
of primary roots of Pinus contorta colonized by Phialocephala
fortinii s.l. were characterized by surface patches of sclerotia and
loose wes of hyphae growing along the root surface and hyphae
as well as sclerotia growing inter- and intracellularly in the
outer cortex (O’Dell etal. 1993). Occasionally, patches of inter-
cellular labyrinthine fungal tissue, similar to Hartig net tissue,
were formed on the surface of primary pine roots, and proxi-
mal portions of lateral roots frequently had a sporadic mantle.
Similarly, roots of Pinus strobus L. showed varying amounts of
surface hyphae, Hartig net structures, and intracellular hyphae
(Peterson etal. 2008; Figure 38.3D). Acephala macrosclerotio-
rum Münzenberger & Bubner, a recently described close relative
of PAC, formed thin mantles and a distinct Hartig net on Pinus
sylvestris and Picea abies (Münzenberger etal. 2009). A. mac-
rosclerotiorum forms characteristic, melanized wartlike scle-
rotia giving the mantle a verrucous appearance (Figure 38.3E).
DSE formed good mantles and Hartig nets on some of the best
nursery stocks of pines and white spruce (Danielson and Visser
1990). It persisted on the stock for as long as the seedlings were
in the nursery, but once outplanted, it was replaced by mycor-
rhizal fungi, especially elephora terrestris Ehrh. and E-strain
fungi. Hartig net structures could not be observed in resynthe-
sis experiments between Picea abies and various PAC strains,
and microsclerotia production was strongly strain dependent
(Tellenbach etal. 2010).
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38-31Fungal Root Endophytes
Colonization of ne roots (diameter <5 mm) of Norway
spruce and Scots pine by DSE was examined in eld samples
from Finland and Switzerland (Sieber, unpublished). Density
of surface mycelia and intracortical fungal structures are much
lower in eld samples than in roots from in vitro synthesis
experiments, and thus, the endophytes are more dicult to
locate. DSE were observed to colonize primary roots down to
the innermost cortical cells. Colonization of the endodermis
or the expanded pericycle did not occur. DSE most frequently
occurred as intra- and intercellular hyphae and small intracellu-
lar microsclerotia composed of cells with thin, melanized walls.
e rhytidome of older conifer roots is frequently colonized by
dark, septate hyphae down to the youngest layer of phellem cells.
Intensely colonized roots can be recognized already in the eld
by the black appearance of the rhytidome; sometimes, it is nec-
essary to remove the loose bark scales to see the more proxi-
mal phellem tissues (Grünig etal. 2008b). e black appearance
of the rhytidome is due to cells of the phlobaphene cork lled
with multicellular sclerotia composed of bubble-shaped, thick-
walled, melanized cells (Holdenrieder, personal communica-
tion, 1997; Figure 38.3F). ese sclerotia might serve as inoculi
and food bases from where mycelia can grow to colonize new
substrates. Holdenrieder (1989) presented excellent SEM pic-
tures of hyphal aggregations of DSE lling entire phellem cells of
Norway-spruce roots. Endophytic colonization of cells proximal
to the phellem has, so far, not conclusively been demonstrated
but is certainly possible considering the frequent colonization of
the xylem in forest trees by DSE (including PAC) (Görke 1998).
Intracellular colonization of Norway-spruce seedlings inocu-
lated with DSE and Cryptosporiopsis cf. abietina Petr., possibly
conspecic with C. radiciola Kowalski & Kehr, was observed in
root cortex cells (Haug etal. 1988). Whereas the infection by
DSE was conned to the cortex, C. cf. abietina colonized also
the vascular tissue and caused decline of the seedlings. e older
seedlings (5-month-old compared to 3-week-old) resisted for a
longer period of time. Interestingly, addition of malt caused DSE
to become pathogenic and to colonize the vascular tissues.
2. Endophyte–Pathogen Interactions,
Biological Control
Some endophytes were demonstrated to confer biological
control against other microorganisms. Duda and Sierota (1987)
successfully used Trichoderma viride Pers., which was found
highly pathogenic on Norway-spruce seedlings (Forbrig 1989)
to control damping-o of Pinus sylvestris seedlings caused by
Fusarium oxysporum or Rhizoctonia solani. DSE were shown to
protect roots of Picea abies, Pinus sylvestris, and Quercus robur L.
against other organisms, for example, F. oxysporum and R. solani
(Manka 1960; Manka and Przezbòrski 1978, 1987). DSE had only
an adverse eect onto the trees when these had been planted on
an unsuitable site or aer an Armillaria attack. Some isolates of
Phialocephala subalpina increased survival of Norway-spruce
seedlings inoculated with either one of the two root pathogens
Phytophthora plurivora T. Jung & T.I. Burgess (syn. P. citri-
cola Sawada) or Elongisporangium undulatum (H.E. Petersen)
Uzuhasi, Tojo & Kakish. (syn. Pythium undulatum H.E. Petersen)
(Tellenbach and Sieber 2012). Phialocephala subalpina seems to
confer an indirect benet to its host and might therefore be tol-
erated in natural spruce populations, despite negative eects on
plant performance.
Biological control seems to be eective not only among fungal
species but also among genotypes (strains) of the same species.
Pathogenicity is oen strain dependent (Tellenbach etal. 2011)
(see text in the following paragraph). Nonpathogenic PAC strains
signicantly reduced density of colonization of Norway-spruce
(Picea abies) roots by pathogenic PAC strains, attenuating adverse
eects on plant growth (Reininger etal. 2011a, 2012). is high-
lights the importance of high genotypic diversity of PAC fungi
colonizing the same root system.
3. Endophyte–Plant Interactions
DSE had very marked pathogenic properties toward Pinus syl-
vestris under pure culture conditions. However, DSE could
achieve dominance on root surfaces of healthy elongating roots
of pines growing under natural conditions, when its pathogenic
eects appear to be reduced (Robertson 1954). De la Bastide and
Kendrick (1990) treated white-pine seedlings (Pinus strobus)
with benomyl to reduce the pathogenic eect of DSE. Adverse
eects caused by DSE occurred also in experiments of Richard
etal. (1971) with Picea mariana, Wilhelm etal. (1969) with Pinus
pinea L. seedlings, Wilcox and Wang (1987) with Pinus resinosa
Aiton, Picea rubens Sarg., and Betula alleghaniensis Britton, and
Melin (1923) with Pinus sylvestris and Picea abies.
General health status as expressed by needle color, pres-
ence or absence of needle-tip chlorosis, mortality rate, and dry
weight of Norway-spruce seedlings used to bait DSE from for-
est soils was not correlated with the colonization of the roots
by DSE (mainly PAC) (Ahlich etal. 1998). Hennon etal. (1990)
frequently isolated DSE, Cryptosporiopsis sp., Gelatinosporium
sp., Sporidesmium sp., Cylindrocarpon didymum (Harting)
Wollenw., and Cadophora melinii Nannf. from healthy
and declining cedar roots during their studies on declin-
ing Chamaecyparis nootkatensis (D. Don) Spach in Southeast
Alaska. DSE were most frequently isolated. Healthy and
declining trees were equally frequently colonized. Except for
C. didymum, none of the fungi proved to be pathogenic in infec-
tion experiments with cedar seedlings. None of the seedlings
died. Similarly, DSE were isolated from diseased and healthy
seedlings of Norway spruce equally frequently and were not
pathogenic in infection experiments (Galaaen and Venn 1979).
is contrasts with Pythium sylvaticum W.A. Campb. & F.F.
Hendrix that was isolated almost only from diseased seedlings
and was highly virulent when inoculated onto axenically grown
seedlings. e endophytic mycobiota in roots of European silver
r (A. alba) seedlings was examined at a site with natural regen-
eration and another site where r did not regenerate (Kowalski
1982a). Ilyonectria radicicola (teleomorph of C. destructans)
was the most frequently isolated pathogenic fungus, especially
in young, 1-year-old seedlings. In natural regenerations, DSE
were very common and I. radicicola occurred only sporadically.
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38-32 Root–Rhizosphere Interactions
Likewise, I. radicicola was demonstrated to be pathogenic on
r and pine seedlings in vitro (Dahm etal. 1987). Virulence
was aected by pH, temperature, light intensity, and also by
associated bacteria and actinomycetes. In contrast, Bloomberg
(1966) isolated DSE and Cylindrocarpon spp. more frequently
from healthy Douglas-r seedlings. e frequency of Fusarium
spp. did, however, not depend on the health status of the plants.
DSE, Trichoderma viride, and I. radicicola were pathogenic
when inoculated onto 2 to 3-week-old axenically grown seed-
lings of Picea abies (Forbrig 1987, 1989). T. viride and I. radici-
cola killed the seedlings rapidly. DSE were suspected to infect
only weakened trees. e interactions with Norway spruce of
more than 30 isolates of four dierent PAC species and from
three geographical regions were strongly isolate dependent
and ranged from neutral to highly virulent, but no strain had
a stimulating eect on plant growth (Tellenbach etal. 2011).
Variation in virulence was much higher within than among
PAC species, but only isolates of Phialocephala subalpina, one
of the most frequent PAC species, were highly virulent. Disease
caused by Phialocephala subalpina genotypes from the native
range of Norway spruce was more severe than that induced by
genotypes from outside the range. Virulence was not correlated
with the phylogenetic relatedness of the isolates but was posi-
tively correlated with the extent of fungal colonization as mea-
sured by quantitative real-time PCR. e results obtained by
Tellenbach etal. (2011) contrast with those reported by Peterson
et al. (2008) who observed the production of lateral roots of
Pinus strobus seedlings inoculated with Phialocephala fortinii
s.l. being greater than that of uninoculated controls.
Chloridium paucisporum C.J.K. Wang & H.E. Wilcox from
3-year-old nursery seedlings of Pinus resinosa was found to stim-
ulate Pinus resinosa seedlings growth (Wilcox and Ganmore-
Neumann 1974). e plant–fungus association was found to
be EEM but dierent from that of E-strain fungi. Jumpponen
and Trappe (1998b) showed that the culture system under which
an association is studied may also aect the host–fungus inter-
action. e eects of various glucose concentrations on Pinus
contorta seedlings inoculated with Phialocephala fortinii s.l.
were studied in an axenic and an open pot system. Inoculation
resulted in substantial increase of biomass in the axenic system,
and host biomass increased with increasing glucose concentra-
tion. Glucose alone did not signicantly aect host biomass. In
the open pot cultures, inoculation did not aect biomass. e
observed growth stimulation in the closed culture system was
probably due to CO
2
fertilization as a consequence of fungal
respiration (Jumpponen and Trappe 1998b). Growth stimula-
tion and inhibition were observed also in cell-free extracts of
endophytes. Culture ltrates of T. viride reduced and ltrates of
DSE stimulated elongation of excised roots of Pinus sylvestris,
whereas I. radicicola reduced formation of lateral roots (Turner
1962). Binucleate Rhizoctonia endophytes promoted formation
of adventitious roots of Scots pine (Pinus sylvestris L.) hypo-
cotyl cuttings (Kaparakis and Sen 2006). Similarly, Rhizoctonia
stimulated early seedling growth in a nitrogen-limited soil
(Grönberg etal. 2006).
4. Endophyte–Environment Interactions
Knowledge about the inuence of environmental factors on
frequency and colonization of root endophytes is sparse.
Although some factors were identied in the past, more eorts
are needed to get a more complete picture of the key factors
and how they interact with each other and with the endo-
phyte–plant system. e proton [H
+
] concentration (pH) in
the soil and the type of biogeoclimatic zone were identied as
factors aecting root endophyte communities. Statistically
signicant correlations existed between soil pH and the fre-
quency of colonization by Cryptosporiopsis radicicola Kowalski
& C. Bartnik, Cylindrocarpon didymum, and DSE (Ahlich and
Sieber 1996). e correlations with C. radicicola and C. didy-
mum were positive, and the correlation with DSE was negative.
Some Cylindrocarpon species are well known to prefer alkaline
conditions (Matturi and Stenton 1964; Domsch et al. 1980;
Schönhar 1987). DSE were, however, considered not to be inu-
enced by soil pH according to Melin (1924). Although DSE were
absent in the soil samples of only 2 of 72 sites, DSE occurred
less frequently in soils with a high pH value (Ahlich etal. 1998).
Maximum isolation was from soils with pH values ranging from
3.5 to 4.5. Similarly, Manka (1960) gives pH 4 as the optimum
for growth of DSE. Danielson and Visser (1989) considered a pH
value of 3.1 the minimum for growth of DSE contrasting with
the results of Ahlich etal. (1998) who detected DSE in almost
90% of the root segments of the Norway-spruce seedlings used
to bait endophytes from a forest soil with pH 3.0. A relationship
between altitude and pH value was reported by Holdenrieder
and Sieber (1992) who found the most prominent dierence in
fungal associations in Norway-spruce roots to exist between
roots colonized mainly by I. radicicola from alkaline soils at low
altitude and roots dominated by DSE from acidic soil (peat bog),
as well as from alkaline soil at high altitude.
In Switzerland, Phialocephala fortinii s.l. proofed to occur
preferentially on high altitudes (Ahlich and Sieber 1996).
Trichoderma viride occurred preferentially in roots from
extremely acidic soils, T. hamatum (Bonord.) Bainier from
moderately acidic, and T. polysporum (Link) Rifai from weakly
acidic soils (Kattner and Schönhar 1990). Cryptosporiopsis abi-
etina (perhaps conspecic with C. radicicola) and I. radicicola
preferred a neutral environment. Liming reduced T. viride and
a Penicillium sp., whereas the frequency of DSE, Penicillium
spinulosum om, T. polysporum, and some Mortierella spp.
increased (Kattner 1992b). Inoculations with root endophytes
may enhance survival rates of seedlings planted at polluted sites.
LoBuglio and Wilcox (1988) inoculated Pinus resinosa seedlings
with Cadophora nlandica (C.J.K. Wang & H.E. Wilcox) T.C.
Harr. & McNew and planted them onto iron tailings in an old
iron mine. C. nlandica inoculated seedlings had a higher sur-
vival rate than uninoculated controls. In addition, mortality of
seedlings treated with C. nlandica was lower than that of seed-
lings treated with ectomycorrhizal fungi.
Data about the inuence of phosphorus (P) and nitro-
gen (N) availability on colonization by endophytes and plant
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38-33Fungal Root Endophytes
performance are sparse. Pinus contorta seedlings inoculated
with Phialocephala fortinii s.l. showed enhanced P uptake and
increased growth (Jumpponen etal. 1998). In addition, N uptake
was increased when Phialocephala fortinii s.l. inoculation was
combined with addition of N. N fertilization of a 20-year-old
stand of western hemlock (Tsuga heterophylla (Raf.) Sarg.)
with urea did not change the total number of ne roots and
the number of basidiomycetous mycorrhizae (Kernaghan etal.
1995). However, Cenococcum geophilum mycorrhizae decreased
slightly, whereas those lacking mantels such as EEM and DSE
increased.
Pinus sylvestris seedlings inoculated with DSE (Phialocephala
fortinii s.l., Cadophora nlandica, Chloridium paucisporum,
Pezoloma ericae, Meliniomyces variabilis, and M. vraolstadiae
Hambl. & Sigler) accumulated on average 17% more biomass
than control seedlings under elevated CO
2
combined with N
limitation, indicating that DSE fungi increase plant nutrient
use eciency and are, thus, more benecial to the plant under
elevated CO
2
(Alberton etal. 2010).
5. Extracellular Enzymes and Fungicide Resistance
e production of biocidal metabolites, plant growth hormones,
exoenzymes, and siderophores or the resistance against noxious
substances can be advantageous when competing with other
soil microorganisms for space, nutrients, and/or infection sites
(Currah and Tsuneda 1993; Ahlich-Schlegel 1997; Caldwell etal.
2000; Bartholdy et al. 2001; Schulz etal. 2002; Grünig et al.
2008b). C. nlandica and several PAC isolates utilized cellulose,
laminarin, starch, and xylan as sole carbon source and pro-
teins and nucleic acids as sole nitrogen and phosphorus sources
(Caldwell et al. 2000). However, lignolytic activity was not
observed. T. viride, Mortierella nana Linnem., and DSE exhib-
ited higher pectolytic than cellulolytic activity, and the activity
was strain dependent (Dahm 1987). Trichoderma isolates were
the most active, DSE the least. Presence of cellulolytic activ-
ity of DSE was demonstrated by Gams (1963), Levisohn (1954),
and Melin (1923). e opposite observation by Schelling (1952)
may be due to the fact that she used neither trace elements nor
growth factors in her experiments. Ahlich-Schlegel (1997) tested
more than 200 DSE isolates for fungicide resistance and the
presence of extracellular enzymes and was able to demonstrate
that enzyme activity is strain dependent. One-third of all strains
produced proteases. Some Acephala applanata strains were able
to produce amylases, but other PAC species were not. Laccase
activity, an oxidase used to degrade lignin, was observed in all
A. applanata strains but was present only in half of the other
PAC strains. Most strains produced phenoloxidases, but activity
was much higher in A. applanata isolates. Similar observations
were made by Grünig etal. (2008b) who found A. applanata to
be a good producer of amylases, laccases, and proteases in con-
trast to other PAC species. Benomyl at a concentration of ≥10
mg L
−1
inhibited all strains, whereas thiabendazole did so only
at a concentration of ≥100 mg L
−1
(Ahlich-Schlegel 1997). At
10 mg L
−1
thiabendazole, all A. applanata isolates were inhib-
ited; the reaction of the other DSE was variable. Cycloheximide
at ≥100 mg L
−1
inhibited A. applanata, Phialocephala letzii,
Phialocephala helvetica, and Phialocephala subalpina the most
and Phialocephala uotilensis and Phialocephala turicensis the
least (Ahlich-Schlegel 1997; Grünig etal. 2008a,b). Toxins were
responsible for pathogenicity of I. radicicola but the high pec-
tinase and cellulase production of this fungus were assumed to
enhance virulence (Lyr and Kluge 1968).
Bartholdy etal. (2001) studied the siderophore proles of ve
PAC strains. Siderophores controlling the uptake of iron ions by
fungi play a crucial role in the infection process in some plant–
fungus systems (Johnson 2008). e siderophore proles of two
Phialocephala fortinii s.s. strains were highly similar. ey pro-
duced almost exclusively ferricrocin. In contrast, a strain each of
Phialocephala subalpina and Phialocephala europaea possessed
unique siderophore proles and produced ferrirubin in addition
to ferricrocin, but the amount of ferricrocin produced was signi-
cantly lower in Phialocephala subalpina and signicantly higher in
Phialocephala europaea than in Phialocephala fortinii s.s. A strain
of CSP9 isolated from Larix decidua Mill. in Germany produced
the plant growth hormone IAA (Schulz etal. 2002). e vacuolar
system in hyphae of PAC strain UAMH_9608 (Phialocephala
fortinii s.s.) was investigated, and the presence of polyphosphate
in the vacuoles was conrmed (Saito etal. 2006). An endophytic
strain of Phialocephala scopiformis T. Kowalski & Kehr, a species
with high anities to the PAC, was recently reported to produce
rugulosin—a toxic metabolite against some herbivores of Picea
glauca needles (Miller etal. 2008; Sumarah etal. 2008). Whether
PAC members also produce secondary metabolites toxic to some
herbivores feeding on roots remains to be tested.
6. Stress Tolerance and Oligotrophic Growth of DSE
DSE are resistant against repeated thawing–freezing and against
permanent drought and are able to grow under oligotrophic
conditions. MEA discs and cellophane pieces colonized by PAC
isolates were frozen at −20°C and thawn and refrozen daily
(Ahlich-Schlegel 1997). Most isolates survived for at least 10 days.
Phialocephala fortinii s.l. survived on average longer than A. appla-
nata. One Phialocephala fortinii s.l. isolate survived for more than
50 days. Drought resistance was tested by putting cellophane sheets
colonized by PAC isolates in a desiccator. All isolates survived for
at least 8 months. PAC isolates were grown on nitrogen-free water
agar and subcultured four times every 21 days. Mycelium was very
sparse in all isolates, but growth was not reduced even aer the
fourth subculture. Colony diameters ranged from 29 to 43 mm
for Acephala applanata and 43–63 for Phialocephala fortinii s.l.
Growth under oligotrophic conditions was studied in plastic Petri
dishes that may have released some nitrogen into the medium.
us, the experiment should be repeated using glass Petri dishes.
C. Root Endophytes in Other
Woody Plant Species
Members of the Betulaceae, Fagaceae, and Salicaceae are the
best studied for the presence of root endophytes (Table 38.6).
Species of Cryptosporiopsis, Cylindrocarpon, Meliniomyces, and
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38-34 Root–Rhizosphere Interactions
TABLE 38.6 Endophytes in Other Woody Plants
Endophyte Host
Type of
Experiment
b
Special
Eect
c
ReferencesGenus
a
Species
a
Fungus Order
a
DSE/Not DSE Species Plant Order
Woody/
Herbaceous
Acephala applanata Helotiales DSE Betula pubescens Fagales Tree Isol Queloz (2010)
Acephala sp. 2 Helotiales DSE Sorbus aucuparia Rosales Tree Isol Grünig etal. (2009)
Alternaria alternata Pleosporales DSE Atriplex vesicaria Caryophyllales Woody shrub Isol Cother and Gilbert (1994)
Alternaria chlamydospora Pleosporales DSE Atriplex vesicaria Caryophyllales Woody shrub Isol Cother and Gilbert (1994)
Anguillospora liformis Pleosporales Not DSE Acer spicatum Sapindales Tree Isol Sridhar and Bärlocher (1992)
Anguillospora liformis Pleosporales Not DSE Betula papyrifera Fagales Tree Isol Sridhar and Bärlocher (1992)
Anguillospora longissima Pleosporales Not DSE Salix babylonica Malpighiales Tree Isol Iqbal etal. (1995)
Articulospora proliferata Helotiales Not DSE Mangifera indica Sapindales Tree Isol Iqbal etal. (1995)
Articulospora proliferata Helotiales Not DSE Salix babylonica Malpighiales Tree Isol Iqbal etal. (1995)
Ascochyta sp. Pleosporales DSE Atriplex vesicaria Caryophyllales Woody shrub Isol Cother and Gilbert (1994)
Cadophora fastigiata Helotiales DSE Quercus robur Fagales Tree Isol Halmschlager and Kowalski (2004)
Cadophora sp. Helotiales DSE Quercus petraea Fagales Tree Isol Halmschlager and Kowalski (2004)
Cadophora sp. 3 Helotiales DSE Myricaria prostrata Caryophyllales Woody shrub Isol Graf, pers. comm. (2008)
Chaetomium cochliodes Sordariales Not DSE Aphelandra tetragona Lamiales Woody shrub Isol Werner etal. (1997)
Cladosporium tenuissimum Capnodiales DSE Alnus glutinosa Fagales Tree Isol Fisher etal. (1991b)
Clavariopsis aquatica Pleosporales Not DSE Salix babylonica Malpighiales Tree Isol Iqbal etal. (1995)
Coniothyrium sp. Pleosporales DSE Atriplex vesicaria Caryophyllales Woody shrub Isol Cother and Gilbert (1994)
Cryptosporiopsis radicicola Helotiales DSE Fagus sylvatica Fagales Tree Isol Ahlich and Sieber (1996)
Cryptosporiopsis radicicola Helotiales DSE Quercus petraea Fagales Tree Isol Halmschlager and Kowalski (2004)
Cryptosporiopsis melanigena Helotiales DSE Quercus petraea Fagales Tree Isol Kowalski etal. (1998)
Cryptosporiopsis radicicola Helotiales DSE Quercus robur Fagales Tree Isol Kowalski and Bartnik (1995)
Cylindrocarpon didymum Hypocreales Not DSE Fagus sylvatica Fagales Tree Isol Ahlich and Sieber (1996)
Cylindrocarpon magnusianum Hypocreales Not DSE Fagus sylvatica Fagales Tree Isol Görke (1998)
Cystodendron sp. Helotiales Variable Quercus petraea Fagales Tree Isol Halmschlager and Kowalski (2004)
Embellisia chlamydospora Pleosporales DSE Myricaria prostrata Caryophyllales Woody shrub Isol Graf, pers. comm. (2008)
Flagellospora curvula Hypocreales Not DSE Mangifera indica Sapindales Tree Isol Iqbal etal. (1995)
Flagellospora curvula Hypocreales Not DSE Populus hybrida Malpighiales Tree Isol Iqbal etal. (1995)
Flagellospora curvula Hypocreales Not DSE Salix babylonica Malpighiales Tree Isol Iqbal etal. (1995)
Flagellospora fusaroides Hypocreales Not DSE Mangifera indica Sapindales Tree Isol Iqbal etal. (1995)
Flagellospora fusaroides Hypocreales Not DSE Salix babylonica Malpighiales Tree Isol Iqbal etal. (1995)
Gibberella intricans Hypocreales Not DSE Atriplex vesicaria Caryophyllales Woody shrub Isol Werner etal. (1997)
Fusarium oxysporum Hypocreales Not DSE Atriplex vesicaria Caryophyllales Woody shrub Isol Cother and Gilbert (1994)
Fusarium sp. Hypocreales Not DSE Mangifera indica Sapindales Tree Isol Iqbal etal. (1995)
Fusarium sp. Hypocreales Not DSE Populus hybrida Malpighiales Tree Isol Iqbal etal. (1995)
Fusarium sp. Hypocreales Not DSE Salix babylonica Malpighiales Tree Isol Iqbal etal. (1995)
Gibberella baccata Hypocreales Not DSE Atriplex vesicaria Caryophyllales Woody shrub Isol Cother and Gilbert (1994)
Gibberella nygamai Hypocreales Not DSE Atriplex vesicaria Caryophyllales Woody shrub Isol Cother and Gilbert (1994)
Haematonectria haematococca Hypocreales Not DSE Aphelandra tetragona Lamiales Woody shrub Isol Werner etal. (1997)
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38-35Fungal Root Endophytes
Ilyonectria radicicola Hypocreales Not DSE Alnus glutinosa Fagales Tree Isol Fisher etal. (1991b)
Ilyonectria radicicola Hypocreales Not DSE Aphelandra tetragona Lamiales Woody shrub Isol Werner etal. (1997)
Ilyonectria radicicola Hypocreales Not DSE Betula pendula Fagales Tree Isol Görke (1998)
Ilyonectria radicicola Hypocreales Not DSE Fagus sylvatica Fagales Tree Isol Görke (1998)
Ilyonectria radicicola Hypocreales Not DSE Gynoxys oleifolia Asterales Tree Isol Fisher etal. (1995b)
Ilyonectria radicicola Hypocreales Variable Quercus robur Fagales Tree Isol Halmschlager and Kowalski (2004)
Ilyonectria radicicola Hypocreales Variable Tilia petiolaris Malvales Tree Isol Schroers etal. (2008)
Nectria lugdunensis Hypocreales Not DSE Acer spicatum Sapindales Tree Isol Sridhar and Bärlocher (1992)
Nectria lugdunensis Hypocreales DSE Alnus glutinosa Fagales Tree Isol Fisher etal. (1991b)
Leptodontidium sp. Helotiales DSE Eucalyptus regnans Myrtales Tree Isol Tedersoo etal. (2009)
Leptodontidium sp. Helotiales DSE Nothofagus
cunninghamii
Fagales Tree Isol Tedersoo etal. (2009)
Leptodontidium sp. Helotiales DSE Pomaderris apetala Rosales Tree Isol Tedersoo etal. (2009)
Libertella spp. Xylariales Not DSE Atriplex vesicaria Caryophyllales Woody shrub Isol Cother and Gilbert (1994)
Lunulospora curvula Pezizomycotina Not DSE Populus hybrida Malpighiales Tree Isol Iqbal etal. (1995)
Lunulospora curvula Pezizomycotina Not DSE Salix babylonica Malpighiales Tree Isol Iqbal etal. (1995)
Meliniomyces bicolor Leotiomycetes DSE Nothofagus procera Fagales Tree Isol Hambleton and Sigler (2005)
Meliniomyces bicolor Leotiomycetes DSE Quercus robur Fagales Tree Isol Hambleton and Sigler (2005)
Meliniomyces sp. 1 Leotiomycetes Variable Betula pubescens Fagales Tree Isol Hambleton and Sigler (2005)
Meliniomyces vraolstadiae Leotiomycetes Variable Betula pubescens Fagales Tree Isol Hambleton and Sigler (2005)
Meliniomyces vraolstadiae Leotiomycetes Variable Betula pubescens Fagales Tree Isol Hambleton and Sigler (2005)
Monodictys arctica Dothideomycetes DSE Saxifraga oppositifolia Saxifragales Woody shrub Isol Day etal. (2006)
Oidiodendron sp. Dothideomycetes DSE Eucalyptus regnans Myrtales Tree Isol Tedersoo etal. (2009)
Oidiodendron sp. Dothideomycetes DSE Nothofagus
cunninghamii
Fagales Tree Isol Tedersoo etal. (2009)
Oidiodendron sp. Dothideomycetes DSE Pomaderris apetala Rosales Tree Isol Tedersoo etal. (2009)
Penicillium pinetorum Eurotiales Not DSE Aphelandra tetragona Lamiales Woody shrub Isol Werner etal. (1997)
Penicillium restrictum Eurotiales Not DSE Betula pendula Fagales Tree Isol Görke (1998)
Penicillium restrictum Eurotiales Not DSE Fagus sylvatica Fagales Tree Isol Görke (1998)
Phialocephala europaea Helotiales DSE Fagus sylvatica Fagales Tree Isol Queloz (2010)
Phialocephala europaea Helotiales DSE Salix sp. Malpighiales Tree Isol Queloz (2010)
Phialocephala europaea Helotiales DSE Sorbus aucuparia Rosales Woody shrub Isol Queloz (2010)
Phialocephala fortinii s.l. Helotiales DSE Betula pendula Fagales Tree Isol Görke (1998)
Phialocephala fortinii s.l. Helotiales DSE Fagus sylvatica Fagales Tree Isol Ahlich and Sieber (1996)
Phialocephala fortinii s.s. Helotiales DSE Betula pendula Fagales Tree Isol Queloz (2010)
Phialocephala fortinii s.s. Helotiales DSE Betula pubescens Fagales Tree Isol Queloz (2010)
Phialocephala fortinii s.s. Helotiales DSE Sorbus aucuparia Rosales Woody shrub Isol Queloz (2010)
Phialocephala helvetica Helotiales DSE Fagus sylvatica Fagales Tree Isol Queloz (2010)
Phialocephala letzii Helotiales DSE Fagus sylvatica Fagales Tree Isol Queloz (2010)
Phialocephala letzii Helotiales DSE Helianthemum sp. Malvales Woody shrub Isol Queloz (2010)
Phialocephala letzii Helotiales DSE Sorbus aucuparia Rosales Woody shrub Isol Queloz (2010)
(continued)
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38-36 Root–Rhizosphere Interactions
TABLE 38.6 (continued) Endophytes in Other Woody Plants
Endophyte Host
Type of
Experiment
b
Special
Eect
c
ReferencesGenus
a
Species
a
Fungus Order
a
DSE/Not DSE Species Plant Order
Woody/
Herbaceous
Phialocephala sp. 9 Helotiales DSE Myricaria prostrata Caryophyllales Woody shrub Isol Graf, pers. comm. (2008)
Phialocephala sphaeroides Helotiales DSE Aralia nudicaulis Apiales Woody shrub Isol Wilson etal. (2004)
Phialocephala subalpina Helotiales DSE Betula pendula Fagales Tree Isol Queloz (2010)
Phialocephala subalpina Helotiales DSE Betula tortuosa Fagales Tree Isol Queloz (2010)
Phialocephala subalpina Helotiales DSE Sorbus aucuparia Rosales Woody shrub Isol Queloz (2010)
Phialocephala turicensis Helotiales DSE Fagus sylvatica Fagales Tree Isol Queloz (2010)
Phoma prunicola Pleosporales DSE Atriplex vesicaria Caryophyllales Woody shrub Isol Cother and Gilbert (1994)
Phoma variospora Pleosporales DSE Atriplex vesicaria Caryophyllales Woody shrub Isol Cother and Gilbert (1994)
Phomopsis alnea Diaporthales Not DSE Alnus glutinosa Fagales Tree Isol Fisher etal. (1991b)
Phomopsis spp. Diaporthales DSE Atriplex vesicaria Caryophyllales Woody shrub Isol Cother and Gilbert (1994)
Pleospora herbarum Pleosporales DSE Atriplex vesicaria Caryophyllales Woody shrub Isol Cother and Gilbert (1994)
Pleospora obrusa Pleosporales DSE Atriplex vesicaria Caryophyllales Woody shrub Isol Cother and Gilbert (1994)
Pleospora phaeocomoides Pleosporales DSE Atriplex vesicaria Caryophyllales Woody shrub Isol Cother and Gilbert (1994)
Pyrenochaeta sp. 1 Pleosporales DSE Caragana versicolor Fabales Woody shrub Isol Graf, pers. comm. (2008)
Serendipita vermifera Auriculariales Not DSE Tilia sp. Malvales Tree In vitro exp a Oberwinkler (1964)
Sesquicillium candelabrum Hypocreales Not DSE Betula pendula Fagales Tree Isol Görke (1998)
Sesquicillium candelabrum Hypocreales Not DSE Fagus sylvatica Fagales Tree Isol Görke (1998)
Sporormiella intermedia Pleosporales DSE Atriplex vesicaria Caryophyllales Woody shrub Isol Cother and Gilbert (1994)
Tetracladium marchalianum Helotiales Not DSE Mangifera indica Sapindales Tree Isol Iqbal etal. (1995)
Tetracladium marchalianum Helotiales Not DSE Populus hybrida Malpighiales Tree Isol Iqbal etal. (1995)
Tetracladium marchalianum Helotiales Not DSE Salix babylonica Malpighiales Tree Isol Iqbal etal. (1995)
Trichoderma viride Hypocreales Not DSE Aphelandra tetragona Lamiales Woody shrub Isol Werner etal. (1997)
Triscelophorus konajensis Pezizomycotina Not DSE Coea arabica Gentianales Woody shrub Isol Raviraja etal. (1996)
Triscelophorus monosporus Pezizomycotina Not DSE Coea arabica Gentianales woody shrub Isol Raviraja etal. (1996)
Unidentied DSE DSE Atriplex canescens Caryophyllales Woody shrub In vitro exp Barrow etal. (2004)
Unidentied DSE DSE Daphniphyllum
neilgherrense
Saxifragales Tree Isol Bagyalakshmi etal. (2010)
Unidentied DSE DSE Elaeocarpus munronii Oxalidales Tree Isol Bagyalakshmi etal. (2010)
Unidentied DSE DSE Euodia roxburghiana Sapindales Tree Isol Bagyalakshmi etal. (2010)
Unidentied DSE DSE Syzygium arnottianum Myrtales Tree Isol Bagyalakshmi etal. (2010)
Unidentied DSE DSE Syzygium montanum Myrtales Tree Isol Bagyalakshmi etal. (2010)
Unidentied DSE DSE Tamarix ramosissima Caryophyllales Woody shrub Isol Beauchamp etal. (2005)
a
Genus, species and order (family) names according to index fungorum (http://www.indexfungorum.org/Names/Names.asp, December 20, 2011). If both the teleomorph (sexual reproductive stage) and
the anamorph (asexual reproductive stage) are produced, the name of the teleomorph is given. Names of anamorph(s) can be retrieved from the list of the teleomorph’s synonyms provided in the index. e
next lower taxon is given if the Fungus order is not known with certainty (“incertae sedis”).
b
Isol, isolation from surface-sterilized roots; in vitro exp, fungus used in in-vitro experiment(s).
c
Special eect details: (a) Plant growth stimulation.
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38-37Fungal Root Endophytes
Phialocephala were most frequently isolated. Cryptosporiopsis
radicicola, a species oen isolated from roots of Quercus robur
(Kowalski and Bartnik 1995; Halmschlager and Kowalski
2004), was the dominant endophyte in roots of European beech
(Fagus sylvatica) in Switzerland (Ahlich and Sieber 1996), and
Cryptosporiopsis melanigena T. Kowalski & Halmschl. was
oen isolated from roots of Q. robur and Q. petraea (Kowalski
etal. 1998). According to Kowalski (1983), the wood and bark
endophyte Pezicula cinnamomea (DC.) Sacc., with its ana-
morph Cryptosporiopsis grisea (Pers.) Petr., can also spread
into the roots of dying trees. e main colonizer of Dryas
octopetala L. roots sampled at Spitsbergen was a Cryptosporiopsis
species (Fisher etal. 1995a). DSE (including Phialocephala forti-
nii s.l.) were demonstrated to be the most frequent endophytes
in apparently healthy xylem of roots of Betula pendula and F.
sylvatica in Germany (Görke 1998; Table 38.6). Similarly, DSE
were observed in 42% and 40% of the root samples from Iva
frutescens L. and Triadica sebifera (L.) Small, respectively, col-
lected in the southeastern marshes of Louisiana (Kandalepas
etal. 2010). DSE also dominated the endophyte community in
woody shrubs collected in Kailash-Manasarovar Region on the
Tibetan plateau at 4700 m (F. Graf, personal communication,
July 2008; Table 38.6). Desertication by wind and water erosion
is a serious threat in this region, and the mycelium of mycor-
rhizal and other endophytic fungi could have a stabilizing eect
(Burri etal. 2009).
However, DSE do not always dominate the non-mycorrhizal
endophyte community in roots of woody plants. DSE were absent
or rare in roots of Gynoxis oleifolia Muchler (Compositae) col-
lected in Ecuador at 3300 m asl. I. radicicola, Epicoccum nigrum
Link, Trichoderma harzianum Rifai, and Truncatella angustata
(Pers.) S. Hughes were the endophytic fungi most frequently
observed (Fisher etal. 1995b).
Very special endophyte communities are found on roots con-
stantly submersed in water (Sengupta etal. 1988; Fisher etal.
1991b; Sridhar and Bärlocher 1992; Iqbal etal. 1995; Raviraja
et al. 1996). Submersed roots are oen colonized by aquatic
hyphomycetes in addition to “terrestrial” fungi (Table 38.6). e
eects of aquatic hyphomycetes on their host are probably small.
Submersed roots may, however, constitute refuge and perma-
nent sources of inoculum for the aquatic hyphomycetes to per-
sist in streams (Raviraja etal. 1996). Two septate, dematiaceous
endophytes, a coelomycete and a Rhizoctonia-like fungus, were
frequently isolated from roots of some mangroves and saline-
resistant plants growing in the seabound delta region of West
Bengal (Sengupta etal. 1988). ey grew inter- and intracellu-
larly either alone or simultaneously with AM and formed sclero-
tia in culture. Absence of AM in some halophytes indicates that
endophytes may replace AM in extreme habitats, similar to what
has been observed for arctic and alpine herbaceous plants.
Some woody plant species were examined also on the Southern
Hemisphere. Roots of Nothofagus cunninghamii (Hook.) Oerst.,
Eucalyptus regnans F. Muell., and Pomaderris apetala Labill.
from Tasmania were colonized by species of Leptodontidium
and Oidiodendron (Tedersoo etal. 2009). ese helotialean fungi
are phylogenetically closely related to root endophytes and eri-
coid mycorrhizal fungi of the Northern Hemisphere, suggest-
ing strong ecological and evolutionary links. Seventy-one fungal
endophytes could be isolated from bladder saltbush (Atriplex
vesicaria Heward ex Benth.) in Southern Australia (Cother and
Gilbert 1994). Fusarium spp., Alternaria chlamydospora Mouch.,
Libertella spp., Phoma variospora Shreem., and Sporormiella
intermedia (Auersw.) S.I. Ahmed & Cain ex Kobayasi were iso-
lated as root endophytes for the rst time in Australia. Species of
known pathogenic genera (Ascochyta, Coniothyrium, Phomopsis,
Pleospora) occurred also quite frequently.
1. Anatomy
Phialocephala fortinii CSP 13 (CSP 13 according to Grünig etal.
(2008b)) formed a Hartig net and a thin, patchy mantle in axenic
culture with Salix glauca L. seedlings (Fernando and Currah
1996; Figure 38.3G). An interesting fungus–root association was
described by Sequerra etal. (1995). Penicillium nodositatum Valla
was observed to penetrate and colonize cortical cells of roots of
Alnus incana (L.) Moench and to induce myconodules similar to
those formed by actinorhizal bacteria (Frankia spp.). Host defense
was minimal, and the host plasma membrane, invaginated around
the endophyte, kept its integrity as it does in symbiotic associations.
Penicillium nodositatum was, thus, considered as a neutral micro-
symbiont similar to a compatible but ineective Frankia strain.
2. Endophyte–Pathogen Interactions
Trichoderma spp. and Gliocladium spp. were shown to control
Phytophthora cactorum root and crown rot of apple (Smith etal.
1990). Some isolates signicantly reduced root rot and increased
plant weight. DSE were shown to protect roots of Picea abies,
Pinus sylvestris, and Q. robur against other organisms, for
example, F. oxysporum and R. solani (Manka 1960; Manka and
Przezbòrski 1978, 1987).
3. Endophyte–Plant Interactions
Leptodontidium orchidicola caused a marked increase in host root
length but also invaded the stele, causing extensive cellular lysis in
axenic culture with Salix glauca seedlings (Fernando and Currah
1996). In pot monocultures with various subalpine plant spe-
cies, the eects of L. orchidicola strains on host dry weight were
strain and host specic (Fernando and Currah 1996). e eects
of Phialocephala fortinii CSP 13 were also host specic. In pot
combination cultures (Dryas octopetala, Picea abies, Potentilla
fruticosa L., and S. glauca in the same pot), the Phialocephala
fortinii s.l.–Potentilla fruticosa symbiosis resulted in a signicant
increase in shoot weight in contrast to the results of the same sym-
biosis in monoculture resynthesis. DSE isolated from mangroves
stimulated growth of Cajanus cajan (L.) Millsp. in the absence of
easily available phosphorus (Sengupta etal. 1988).
4. Endophyte–Environment Interactions
Caldwell etal. (2000) studied the utilization of major forms of
carbon, nitrogen, and phosphorus commonly present in plant
litter and detritus for two dark septate, root endophyte isolates
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38-38 Root–Rhizosphere Interactions
from alpine Salix species. Both isolates utilized cellulose, lam-
inarin, starch, and xylan as sole carbon source and proteins
and ribonucleic acids as sole nitrogen and phosphorus sources.
However, lignolytic activity could not be detected.
VI. Conclusions and Outlook
e presence of non-mycorrhizal fungal endophytes in plant
roots is a worldwide phenomenon. ere is probably no plant
species without root endophytes. Species diversity of endophyte
communities in roots is low compared to the one in aerial tis-
sues. However, the within-species genotypic diversity of root
endophytes can be high. Fungi with melanized, septate hyphae
are prevalent in many of the communities. ese fungi usually
do not sporulate readily in culture and are, therefore, assigned to
the form taxon DSE. DSE are a very diverse group of fungi. ey
can be separated into two subgroups. e rst includes DSE,
which occur mainly on herbaceous plants such as species of
the Harpophora–Gaeumannomyces complex, Microdochium or
Periconia. e second subgroup is formed by PAC, which occur
preferentially in woody plant roots. PAC are rare or absent in
plant roots from arable soils or pastures. Antagonism with spe-
cies of the Harpophora–Gaeumannomyces complex and/or other
microorganisms could be the reason. Harpophora species were
shown to confer induced resistance (cross-protection) against
closely related species or varieties in agricultural plants, espe-
cially cereals. Similarly, PAC were shown to protect forest trees
in a similar way, for example, against oomycetous root patho-
gens. e system of induced resistance is expected to be even
more balanced in undisturbed forest ecosystems than in agri-
cultural systems because the microbial community in the rhi-
zosphere and in the roots was allowed to equilibrate for decades
if not centuries. e study of these systems is hampered by the
high genotypic variability of the organisms involved.
With the availability of many dierent molecular genetics
markers, it is now possible to identify and characterize species
and genets of PAC allowing experimentation with clearly dened
strains. Several strains are available from international culture
collections. e high variability of DSE and PAC also explains,
at least in part, the contradictory results obtained in endophyte–
plant interaction experiments. Whereas there are several exam-
ples of non-PAC DSE with benecial eects on plant growth, the
majority of PAC revealed no eect or only slightly positive eects.
More recent in vitro multi-strain experiments with dened PAC
strains indicate that PAC function along a continuum from neu-
tral to pathogenic. Plant growth promotion has not been observed.
However, though PAC are costly, they seem to provide control
of more serious pathogens and perhaps also herbivores. Future
experiments should be shied more toward natural conditions.
e genome of strain UAMH11012 of Phialocephala subalpina
was sequenced, and gene models are currently manually validated
and annotated. First estimates based on 10 Mbp manually vali-
dated gene models show that the Phialocephala subalpina genome
will include roughly 20,000 gene models. Special emphasis is given
to annotation of gene clusters related to secondary metabolites.
e availability of the annotated genome of Phialocephala subal-
pina will allow performing transcriptomic analysis of host–PAC
interactions and comparative genomic studies with ectomycor-
rhizal and pathogenic fungi in the near future. In addition, the
completely sequenced and annotated mitochondrial genome of
Phialocephala subalpina is already available (Duò et al. 2012).
Several mitochondrial loci proved to be suitable for species diag-
nosis in PAC and can be used for community studies.
We do not know the functions root endophytes had in the
past nor which functions they will have in the future. We only
know that nature is a dynamic system. What we see today is one
picture in the evening-lling lm entitled “Evolution,” but it is
fascinating to speculate about the next step.
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