SYMBIOSIS (2005) 40, 87–96
©2005 Balaban, Philadelphia/Rehovot
ISSN 0334-5114
The inoculation with Oidiodendron maius and Phialocephala
fortinii alters phosphorus and nitrogen uptake, foliar C:N ratio
and root biomass distribution in Rhododendron cv. Azurro
Martin Vohník1,2*, Jana Albrechtová1,2, and Miroslav Vosátka1
1 Department of Mycorrhizal Symbioses, Institute of Botany, Academy of Sciences of the Czech Republic, Lesni 1,
252 43 Pruhonice, Czech Republic, Tel. +42-071015346, Fax. +42-0271015332, Email. vohnik@ibot.cas.cz;
2 Department of Plant Physiology, Faculty of Science, Charles University in Prague, Vinicna 5, 128 44 Prague,
Czech Republic
(Received August 9, 2005; Accepted October 22, 2005)
Abstract
A pioneering attempt to simultaneously introduce an ericoid mycorrhizal (ErM) fungus, Oidiodendron maius
Barron, and two strains of a dark septate endophyte (DSE) Phialocephala fortinii Wang & Wilcox (strain P. fortinii
F and P. fortinii H) into root systems of individual Rhododendron cv. Azurro plants was conducted in split root
systems. The inoculation had no effect on the total biomass of inoculated rhododendrons. However, plants
accumulated more root biomass into compartments inoculated with P. fortinii H than to those non-inoculated or
inoculated with P. fortinii F. Plants with the highest foliar P concentrations had been inoculated with O. maius, coinoculated with O. maius and P. fortinii H and inoculated with P. fortinii H. Inoculation with O. maius and coinoculation with O. maius and P. fortinii H also altered N uptake. Inoculation with O. maius and its co-inoculation
with both P. fortinii strains decreased the foliar C:N ratios. All fungi colonized host roots at low levels, P. fortinii F
being the most successful colonizer. Contrary to the other fungi, O. maius also colonized Rhododendron
microcuttings at low levels in vitro, and the colonization pattern was distinct from Hymenoscyphus ericae. Both P.
fortinii strains exhibited a typical DSE colonization pattern in vitro. Our study indicates that O. maius and P. fortinii
positively affect host plant nutrition and demonstrates interactions between separately developing ErM and DSE
fungi, which significantly affect plant physiology.
Keywords:
Ericoid mycorrhiza, dark septate endophytes, DSE-association, split root system, colonization
level, pseudomycorrhiza, co-inoculation
1. Introduction
Members of Ericaceae dominate vast areas in both
Northern and Southern hemisphere, which are often
characterized by "harsh edaphic conditions" (Cairney and
Meharg, 2003). These conditions include low pH, low
nutrient availability, high soil C:N ratio and high contents
of phenolic compounds and toxic elements (Smith and
Read, 1997). The roots of members of Ericaceae are
colonized by ErM fungi, which are regarded as important
mutualistic associates. ErM fungi positively influence
growth, survival and competitiveness of their host species
by enhancing nutrient uptake (Read, 1996; Read and PerezMoreno, 2003) and alleviating heavy metal toxicity (Perotto
et al., 2002).
The genus Oidiodendron contains a number of fungi,
* The author to whom correspondence should be sent.
which inhabit the roots of ericaceous species (Couture et
al., 1983; Dalpé, 1986; Xiao and Berch, 1995; Johansson,
2001), including rhododendrons (Douglas et al., 1989;
Currah et al., 1993a; Jansa and Vosátka, 2000; Usuki et al.,
2003). Among oidiodendrons, O. maius is frequently
detected in roots of ericaceous species (Perotto et al., 2002).
However, the ecophysiological role of oidiodendrons in the
rhizosphere of ericaceous species has not been studied
extensively: there is only little, if any, experimental work
on nutrient uptake by plants inoculated with Oidiodendron
species. This contrasts with their frequent occurrence and
isolations from ericoid mycorrhizal roots from natural sites.
Our general knowledge about the effects of oidiodendrons on
the physiology of ericaceous plants is limited to reports
about their heavy metal resistance (Martino et al., 2000) and
saprotrophic capabilities (Rice and Currah, 2001; Piercey et
al., 2002). The majority of the data regarding nutrient
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M. VOHNIK ET AL.
uptake in ErM is based on experiments with H. ericae
(Bajwa and Read, 1985; Bajwa et al., 1985; Kerley and
Read, 1995; Kerley and Read, 1997; Kerley and Read,
1998).
In addition to ErM fungi, root endophytes belonging to
the miscellaneous group of DSE fungi are reported to
colonize roots of ericaceous plants. The DSE comprise
ascomycetous fungi with a ubiquitous distribution and wide
range of host plants, yet their effects on host physiology are
ambiguous (Jumpponen and Trappe, 1998a). P. fortinii, the
most prominent DSE fungus, was found in roots of several
ericoid species (Stoyke et al., 1992; Currah et al., 1993b;
Ahlich and Sieber, 1996), including rhododendrons (for list
see Jumpponen and Trappe, 1998a). Similarly to
oidiodendrons, our knowledge about the ecophysiological
significance of DSE is scarce. Plant responses to DSE
generally vary from negative to positive (Jumpponen and
Trappe, 1998a; Jumpponen, 2001), and inoculation with
DSE often causes no apparent effect on biomass production
or nutrient uptake by host plants in pot cultures
(Jumpponen and Trappe, 1998b; Vohník et al., 2003).
Nevertheless, stressing their potential to improve plant
growth and nutrient uptake under certain conditions,
Jumpponen (2001) qualified their effect on host plants as
"mycorrhizal".
It can be expected that at natural sites with ericaceous
plant species, both ErM and DSE fungi occur together in
the soil and interact. The nature of these interactions is,
however, unknown. Direct observations have confirmed
multiple colonization in roots of ericaceous species. Urcelay
(2002) reported the simultaneous occurrence of ErM, DSE
and even arbuscular mycorrhiza in roots of Gaultheria
poeppiggi DC (Ericaceae). Also, molecular methods proved
the simultaneous presence of ErM (H. ericae-like and
oidiodendrons) and DSE (P. fortinii) fungi within the same
root system (Midgley et al., 2004).
To contribute to the understanding of physiological
processes in ericaceous host plants influenced by ericoid
mycorrhizal oidiodendrons and DSE fungi, we focused on
the effects of (co-)inoculation with O. maius and two strains
of P. fortinii on growth, nutrient uptake and root biomass
distribution in Rhododendron cv. Azurro. Two experiments
were conducted. The Fungal Compatibility Experiment,
carried out in split Petri dishes with tissue culture derived
cuttings, screened for compatibility of the fungal isolates
with rhododendrons. A parallel Fungal Efficacy Experiment
was conducted in split root systems to ensure spatial
isolation of two fungi, inoculated into an individual root
system, and was designed to screen the effects of inoculated
fungi on their host plants.
2. Materials and Methods
Fungal Compatibility Experiment
Tissue culture derived Rhododendron sp. cuttings with
newly emerging roots were introduced into split Petri dishes
(Figs. 1a–4a) with perforated central septa and root
compartments containing the medium (MMR throughout
the following text) after Dalpé (1986), which is modified
from Mitchell and Read (1981). Root compartments were
inoculated with pieces of agar overgrown by mycelium of
following fungal strains: Oidiodendron maius B,
Phialocephala fortinii F, Phialocephala fortinii H and a
strain of Hymenoscyphus ericae, included for the
comparison of the colonization pattern of this prominent
ericoid mycorrhizal fungus with O. maius B. The fungal
strains were pre-cultivated two months prior to the
experiment in the dark at room temperature on PDA media
(39 g.l–1, Difco). O. maius B was previously isolated from
Rhododendron sp., P. fortinii F from Vaccinium myrtillus
L. and P. fortinii H from Rhododendron sp. (Jansa and
Vosátka, 2000). These strains were identified both
morphologically and using phylogenetic analysis (Vohník
et al., 2003). H. ericae was the isolate from Leake and
Read (1989), originally isolated from Calluna vulgaris
Hull. One set of split dishes was left non-inoculated. After
the inoculation all dishes were sealed with ParafilmTM, and
the root compartments were wrapped with aluminum foil to
block light radiation. There were 5 cuttings in each
treatment, including a non-inoculated control.
After 3 months from the inoculation, the roots of the
cuttings were separated from the shoots, divided into halves
and stained either with trypan blue or chlorazol black,
respectively, according to the method described by Brundrett
et al. (1996). Roots were then observed at high
magnification (400–1,000×) with DIC, using Olympus
BX60 microscope. Pictures were taken with Olympus DP70
camera.
Fungal Efficacy Experiment
Rooted tissue culture derived cuttings of Rhododendron
cv. Azurro of equal total and root system size were planted
into split root systems composed of two Petri dishes. Prior
to the introduction of experimental plants, all dishes were
perforated at the side to allow insertion of roots (Fig. 5a).
Dishes were then filled with peat:perlite (2:1) substrate
amended with a slow release fertilizer (Osmocote, 5–6
months release time, 2 g.l–1) and autoclaved twice in
consecutive 24-hr periods at 121°C for 60 minutes.
Plants, 50 total, in the split root systems were cultivated
in a growth chamber (16/8h, 25/20°C day/night, 150 µmol
m–2s–1, 85±5% relative humidity) and regularly watered two
times per week with de-ionized water. After 50 days of
cultivation, the split root system of each plant was visually
checked to ensure that the roots were distributed equally
between both dishes. This procedure resulted in a selection
of 42 plants of similar size and equal root distribution,
which were then used for the experiment.
Mycelium of O. maius B, P. fortinii F and P. fortinii H
was pre-cultivated for two months on PDA media (39 g of
INOCULATION OF RHODODENDRON WITH O. MAIUS AND P. FORTINII
PDA powder, Difco, per 1 l of de-ionized water) at room
temperature in the dark. Plants in the split root systems
were inoculated i) separately with single fungal strains onto
one dish (then the other dish remained non-inoculated) –
treatments B = O. maius B, F = P. fortinii F and H = P.
fortinii H or ii) simultaneously with two different fungal
strains, each inoculated into one of the dishes – treatments
BF = O. maius B + P. fortinii F and BH = O. maius B + P.
fortinii H. At the beginning of the experiment, there were 7
plants in each treatment including a non-inoculated control.
The inoculation was performed by pipetting the inoculum
onto the substrate in the dishes. The inoculum was prepared
by homogenizing the mycelium of the respective fungus
(together with the agar growth medium from below the
colony) from 3 Petri dishes with 300 ml of autoclaved
water. In the case of both P. fortinii strains, which in two
months had overgrown the whole surface of medium in
dishes, the total content of the dishes (the mycelium + the
growth medium) was homogenized. For O. maius cultures,
which did not overgrow the whole surface, we excised only
the fungal colonies and the medium directly below them.
Five ml of the suspension were used per each inoculation
resulting in a total amount of 5 ml added per plant in
treatments B, F and H and 10 ml in treatments BF and BH.
Unequal inoculum volume as well as the presence of
residues of the growth medium in the inoculum did not
influence the analyzed parameters of inoculated plants (see
Results). Both dishes of control plants remained noninoculated. The control variant was set up to find whether
the root biomass distribution at the end of the experiment
would be equal between the two non-inoculated dishes of the
same plant, thus the shift in the root biomass was due to
the inoculation. After the inoculation, each dish was
wrapped with aluminum foil and placed into a plastic sack
to prevent cross-contamination between dishes (Fig. 5b).
The experimental plants were randomly placed in the growth
chamber and regularly watered two times per week with deionized water.
The roots were harvested 16 weeks after the inoculation.
One of the rhododendrons inoculated with O. maius B
developed extremely badly compared to the rest of plants and
was excluded from the measurements. The shoots were
separated from the roots, and the leaves were counted and
their area measured (LI-3100 Area Meter, LI-COR Inc.,
USA). The shoots were then dried in an oven at 80°C for 10
hours and weighed to obtain the weight of the dried shoot
biomass. The dried leaves were homogenized in a grinding
mill and analyzed for N, P, and C content (methods after
Ehrenberger and Gorbach, 1973). The concentration of P
was expressed in µg/g of the dried leaf biomass; the content
of N and C was given as percentage of the two substances
in the analyzed samples. C:N ratio was calculated using
percent carbon and nitrogen contents in the dried leaves.
Roots from both dishes of one experimental plant were
separated, washed under tap water, dried with filter paper and
weighed. This yielded the total weight of the fresh root
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biomass of the whole plant, and the total weights of the
fresh root biomass from each of the two dishes, belonging
to the same plant. About one half of the roots from each
dish were separated, weighed again and the ratio between the
weight of the separated part vs. the total weight of the fresh
root biomass from the same dish was calculated. The
separated part was dried in an oven for 4 hours at 80°C and
weighed again. Supposing that all parts of the root system
would change their weight during the drying the same way,
we re-calculated the total weight of the dried roots from one
dish using the weight of the dried separated part and the ratio
mentioned above. Obtained values were used for the
calculation of the total weight of the dried root biomass of
the whole plant and for the distribution of root biomass
within the single root system. The distribution of root
biomass within the single root system was found by
calculating the ratio between the weight of the dried root
biomasses in inoculated vs. non-inoculated dishes
(treatments B, F, and H) and between weights of the dried
root biomasses from the dishes inoculated with O. maius B
vs. inoculated with P. fortinii F or P. fortinii H (treatments
BF and BH).
Remaining roots not used for weighing were used to
assess mycorrhizal colonization. Roots were treated as in
Fungal Compatibility Experiment and observed at high
magnifications with DIC, using the equipment listed above.
The gridline intersection method (Brundrett et al., 1996)
proved unsuitable for evaluating colonization in the roots
because of low colonization levels. As an alternative to
percent colonization, we divided roots into two related
classes. The first class represented poor colonization
characterized by very scarce occurrence of both intra- and
extracellular hyphae, and the second class involved roots
colonized in the same way at higher level with occasional,
but still scarce presence of hyphal clumps on the root
surface.
Data were statistically analyzed for homogeneity of
variances using Levene's test and for normal distribution
using Chi-Square test. The data that did not have
homogenous variances or normal distribution were sqrt
(foliar P content) or log transformed (foliar N and C
content, the distribution of root biomass) to meet
assumptions of ANOVA. One-way ANOVA was used to
evaluate the effect of the inoculation on the weight of the
dried shoot, root and total biomass, on foliar nutrient
content, C:N ratio and root biomass distribution. Calculated
ratios of root biomass distribution were divided into two
groups: i) single fungus inoculation, the second dish noninoculated (treatments B, F and H) and ii) co-inoculation
with two fungi, one dish inoculated with O. maius B, the
other with one of P. fortinii strains (treatments BF and BH)
and the differences between treatments were calculated
within these groups. Significant differences between
treatments were evaluated using LSD test at p< 0.05.
StatisticaTM 5.1 software was used for the statistical
analysis.
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M. VOHNIK ET AL.
Figures 1–5. 1a: Inoculation of Rhododendron cuttings with O. maius B resulted in reduction of the root development;
1b: Intracellular structures (arrows) formed by O. maius B in Rhododendron root; 2a: Rhododendrons inoculated with H. ericae
developed branched root systems; 2b: Intracellular structures (arrows) formed by H. ericae in Rhododendron roots; 3a:
Rhododendrons inoculated with both strains of P. fortinii developed branched root systems; 3b: Intracellular microsclerotium
formed by P. fortinii H; 4a: Also non-inoculated rhododendrons had branched, well developed root systems; 4b: a non-colonized
root of a non-inoculated control plant; 5: A Rhododendron cv. Azurro rooted cutting in the split root system; 5a: before the
inoculation, 5b: after the inoculation. The fungal structures were stained with chorazol black (Fig. 1b) or trypan blue (Figs. 2b and
3b). Bars in the upper row correspond to 1 cm, in the lower row correspond to 10 µm.
INOCULATION OF RHODODENDRON WITH O. MAIUS AND P. FORTINII
3. Results
Fungal Compatibility Experiment
There were no apparent differences in the growth and
branching of the shoots among cuttings, and all grew well
without any signs of nutrient deficiency. Only the plants
inoculated with O. maius B seemed to exhibit less vigorous
shoot growth compared to the others, but this observation
was not statistically evaluated because of a low number of
replications per variant. Plants from all treatments except
those inoculated with O. maius B developed vigorous,
branched root system (Figs. 2a–4a). All fungal isolates
except O. maius B grew sufficiently on the media. In
contrast, plants inoculated with O. maius B had reduced,
dark pigmented and non-branched thick roots (Fig. 1a). O.
maius B colonies grew very slowly reaching maximum
diameter of 1.5 cm, compared to 5 cm for H. ericae and 7
cm for both P. fortinii colonies, at the end of the
experiment. O. maius B colonies also produced a lightly
brown pigment of unknown nature in the medium.
Screening of both trypan blue and chlorazol black stained
roots revealed a typical DSE-colonization pattern in
treatments inoculated with P. fortinii F and P. fortinii H:
abundant dark septate hyphae surrounded the roots growing
on its surface, penetrating rhizodermal cell walls and
occasionally forming primordia of hyaline microsclerotia
(Fig. 3b). H. ericae formed typical ericoid mycorrhizal
colonization pattern: its hyphae grew along the root surface
penetrating into rhizodermal cells and filling them with
dense hyphal coils (Fig. 2b). Trypan blue completely failed
to stain mycelium of O. maius B, and its intracellular
hyphae were stained only lightly with chlorazol black. The
colonization pattern of O. maius B was distinct from H.
ericae: its hyphae also formed intracellular coils, but these
had altered morphology and were looser compared to those
of H. ericae (Fig. 1b). The intracellular hyphae of O. maius
B never filled the cells to such extent as those of H. ericae.
Cells colonized with hyphae of O. maius B in the described
pattern, which resembled ErM, were very scarce, and overall
colonization was much less prominent and developed than
that of H. ericae.
Fungal Efficacy Experiment
The inoculation with either fungus had no significant
effect on the weight of the dried shoot, root or total
biomass, shoot:root ratio, leaf area or number of leaves of
experimental plants. However, the inoculation had a
significant effect on the distribution of root biomass within
the root system of plants inoculated with single fungal
strains (F=3.28, p=0.042). This was expressed by
statistically different ratio between the weights of the dried
root biomass found in inoculated vs. non-inoculated dishes.
Experimental plants developed significantly more root
biomass in the dishes inoculated with P. fortinii H than
91
non-inoculated dishes (p=0.03) and dishes inoculated with P.
fortinii F (p=0.01). A similar but non-significant (p=0.097)
trend was observed for dishes inoculated with O. maius B,
which appeared to favor root biomass distribution in
comparison with P. fortinii F. The distribution of root
biomass in the group of plants co-inoculated with O. maius
B and one of the P. fortinii strains was not influenced by
the inoculation (F=1.74, p=0.217).
The inoculation had significant effects on the foliar P
content (F=7.05; p=0.0001). In comparison with the noninoculated control, the separate inoculations with O. maius
B and P. fortinii H increased the P content in the leaves
1.34 (p=0.00007) and 1.22 times (p=0.005), respectively.
The co-inoculation with O. maius B and P. fortinii H
increased the P content in leaves 1.25 times (p=0.001)
compared to the control and 1.23 times (p=0.002) compared
to the co-inoculation with O. maius B and P. fortinii F. The
inoculation with O. maius B also increased the foliar P
content in comparison with P. fortinii F (1.25 times,
p=0.001) and with the co-inoculation with O. maius B and
P. fortinii F (1.31 times, p=0.0002). P. fortinii H also
increased the P content in comparison with P. fortinii F
(1.14 times, p=0.052). The inoculation also effected the N
foliar content, but this effect was only marginally
significant (F=1.99; p=0.053). At the given level of
significance, the inoculation with O. maius B increased the
N content 1.24 times (p=0.004) compared to the control,
1.15 times (p=0.041) compared to the inoculation with P.
fortinii F and 1.17 times (p=0.025) compared with P.
fortinii H. Co-inoculation with O. maius B and P. fortinii
H also increased the N content comparing to the control
(1.16 times, p=0.034). The inoculation had no effect on the
foliar C content but significantly influenced the foliar C:N
ratio (F=2.79, p=0.032). Inoculation with O. maius B
decreased the C:N ratio in comparison with the control
(p=0.002) and with P. fortinii H (p=0.036). Additonally, the
co-inoculation with either O. maius B and P. fortinii H or
with O. maius B and P. fortinii F decreased the C:N ratio
compared to the control (p=0.011 and p=0.032,
respectively).
Screening of the mycorrhizal colonization revealed very
low levels of intracellular colonization by fungal hyphae. If
present, O. maius B hyphae grew around the roots and were
attached to the root surface, only very rarely penetrating
rhizodermal cells to form sparse intracellular coils. Hyphae
of O. maius B failed to stain with trypan blue and were only
lightly stained with chlorazol black. P. fortinii H failed to
produce abundant DSE-colonization. Its hyphae grew
mostly on the root surface, and if they penetrated the root,
they grew along the central axis producing mostly lightly
stained (better with chlorazol black than in trypan blue)
hyaline hyphae. The hyphae of P. fortinii H scarcely formed
microsclerotia. Relatively higher colonization occurred in
the dishes inoculated with P. fortinii F, where dark septate
hyphae formed well-developed hyaline microsclerotia.
However, even in the dishes inoculated with P. fortinii F,
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M. VOHNIK ET AL.
the colonization was low, and we estimate it did not reach
more than 5% (counting both the presence of hyphae and
microsclerotia) of the total root length colonized. The
colonization level of O. maius B and P. fortinii H belonged
to the first class, with that of P. fortinii F within the
second class as described in Materials and Methods.
4. Discussion
Fungal Compatibility Experiment
The Fungal Compatibility Experiment showed that the
selected fungi were able to form both ErM and DSE in the
roots of Rhododendron micro-cuttings. O. maius B proved
to be the least efficient colonizer, exhibiting poor
intracellular colonization compared to the typical ErM
fungus H. ericae. The presence of O. maius B also reduced
the development of the root system of the inoculated plants
compared to the non-inoculated and the inoculated with H.
ericae or either of the two strains of P. fortinii. Similar
root growth depression by O. tenuissimum (Peck) Hughes
was observed by Dalpé (1986) in Vaccinium angustifolium
Ait., where O. tenuissimum failed to form ErM.
The root growth depression in mycorrhizal symbioses
can be attributed to the fact, that mycorrhizal plants, which
receive mineral nutrients from substrate through the
mycelium of symbiotic fungi, can invest less energy into
the formation of the root system. However, the situation
with O. maius B-inoculated plants, in which roots remained
mostly non-mycorrhizal, sharply contrasted with H. ericaeinoculated plants, which were readily ericoid mycorrhizal
and simultaneously produced more vigorous shoots and
especially roots. The mechanisms of the reduction of root,
and to some extent, also shoot development by O. maius B
thus remain unknown. Except for sucrose, the nutrients in
MMR are in mineral form and easily accessible to plants, as
revealed by the vigorous growth of the rhododendrons in the
control treatment. In contrast to H. ericae and both P.
fortinii strains, the presence of O. maius B apparently
altered the ability of rhododendrons to draw the nutrients
from MMR, likely by producing unknown inhibitory
compound(s), which reduced the development of the root
system, and thus reducing its absorptive area. Decreased
nutrient uptake then reduced shoot growth.
In contrast to H. ericae and both strains of P. fortinii,
the growth of O. maius B itself was reduced on MMR. It
was also reduced when compared to other cultivation media
we ordinary use for the cultivation of O. maius B (Potato
Dextrose Agar, Malt Extract Agar, Modified Melin
Norkrans medium, data not shown). Reduced growth of O.
maius on MMR, together with the production of a pigment
of unknown nature in the media was connected with reduced
growth of the roots and shoots of the inoculated plants – it
appears that O. maius B, apparently growing under sub-
optimal conditions, did not act as an ericoid mycorrhizal
symbiont.
Dulcos and Fortin (1983) found that the addition of a
small quantity of glucose (0.5 g/l) to the culture medium
enhanced ErM formation on V. angustifolium and
Vaccinium corymbosum L. seedlings with H. ericae
compared to the seedlings cultivated in the control medium
without glucose. A higher concentration of glucose (5 g/l)
decreased the colonization rate as well as the height of
inoculated Vaccinium seedlings compared to the control
medium. These results indicate that the level of the
colonization and the nature and effectiveness of the fungusroot association in in vitro experiments with ErM and DSE
fungi can be determined by the quality of the media, which
agrees with our results from O. maius B, although we
cannot provide any direct evidence about the effect of the
limited C-availability.
Fungal Efficacy Experiment
In different habitats, different fungi usually inhabit plant
roots, as is the case with ericaceous species (Midgley et al.,
2004), even though the dominant role of H. ericae is
stressed. McLean and Lawrie (1996) stated, on the base of
the different colonization patterns, that more than one
fungus was involved in the screened ericoid mycorrhizae in
the roots of epacridaceous plants from different natural sites.
Each fungus may make different contribution to the
ecophysiology of its host plant depending on the large scale
of the environmental factors. This was also revealed in
Fungal Compatibility Experiment, where ErM fungi O.
maius B and H. ericae, grown on the same media, exhibited
different effects on host plants. In the Fungal Efficacy
Experiment, the direct comparison of the effects of O. maius
and both P. fortinii strains on the nutrient uptake by the
host plants showed a higher efficiency of O. maius than P.
fortinii. The results of our previous unpublished
experiments, performed under the conditions similar to
those presented here, repeatedly indicated that O. maius B
was more efficient in the terms of improved plant growth of
rhododendrons than H. ericae, which we had not expected.
Unfortunately, studies employing O. maius, and especially
both O. maius and H. ericae simultaneously are missing,
and the effect of both fungi is therefore difficult to compare.
Such studies would elucidate whether oidiodendrons could be
as efficient in facilitating nutrient uptake by host plants as
H. ericae and thus play the same or similar role in the
environments dominated by ericaceous species. Results of
our study indicate that oidiodendrons might have such
potential.
Phosphorus and especially nitrogen are primarily
transported to host plants by ericoid mycorrhizal fungi,
according to experiments using H. ericae as a mycorrhizal
partner of ericaceous plants (Smith and Read, 1997). Our
study shows positive effects of inoculation with O. maius,
in particular, on P uptake but also indicates a positive trend
INOCULATION OF RHODODENDRON WITH O. MAIUS AND P. FORTINII
93
Table 1. The effects of the inoculation on the total weight of the dried biomass, the weight of the dried shoot and root biomass,
foliar P content, percentual foliar N content and leaf C:N ratio. "B" corresponds to the treatment inoculated with Oidiodendron
maius B; "F" with Phialocephala fortinii F; "H" with Phialocephala fortinii H; "BF" corresponds with the treatment co-inoculated
with O. maius B and P. fortinii F; "BH" with the treatment co-inoculated with O. maius B and P. fortinii H. NS – non-significant
effect of the inoculation. The numbers in the table are means of the measured parameters and the 95% Confidence Intervals. The
different letters show significantly different groups at p<0.05.
Total weight
of the dried
biomass (g)
NS
Weight of the
dried shoot
biomass (g)
NS
Weight of the
dried root
biomass (g)
NS
P (µg/g)
p=0.00011
N (%)
p=0.053
C:N ratio
p=0.032
B (n=6)
1.24
(0.91–1.57)
1.13
(0.85–1.41)
0.11
(0.06–0.17)
1,288
(913–1,662)c
1.39
(1.19–1.57)c
34.6
(29.7–39.6)a
F (7)
1.51
(1.25–1.77)
1.36
(1.15–1.57)
0.15
(0.10–0.20)
818
(725–913)ab
1.21
(1.13–1.29)ab
39.4
(36.4–42.4)abc
H (7)
1.55
(1.28–1.81)
1.40
(1.17–1.63)
0.15
(0.10–0.19)
1,060
(849–1,272)bc
1.19
(1.06–1.32)ab
40.5
(36.0–44.9)bc
BF (7)
1.36
(1.13–1.58)
1.23
(0.85–1.41)
0.12
(0.09–0.16)
745
(609–882)a
1.26
(1.16–1.36)abc
37.8
(34.6–41.1)ab
BH (7)
1.29
(1.04–1.53)
1.15
(0.91–1.40)
0.13
(0.08–0.19)
1,138
(815–1,460)c
1.30
(1.16–1.44)bc
36.7
(32.8–40.4)ab
Control (7)
1.50
(1.15–1.84)
1.35
(1.06–1.64)
0.15
(0.09–0.20)
720
(552–888)a
1.12
(0.93–1.32)a
43.6
(36.8–50.3)c
Table 2. The effect of the inoculation on the distribution of root biomass between inoculated and non-inoculated dishes.
The treatment 0–0 represents control with both dishes non-inoculated, B–0 represents the treatment with one dish inoculated with
O. maius B and the other non-inoculated, F–0 is the treatment with one dish inoculated with P. fortinii F and the other noninoculated, H–0 is the treatment with one dish inoculated with P. fortinii H and the other non-inoculated. The treatment B–F had
one dish inoculated with O. maius B and the other with P. fortinii F; B–H had analogically the other dish inoculated with P. fortinii
H. WDR refers to the weight of the dried root biomass from a respective dish. Ratio expresses the ratio between the weight of the
dried root biomass from the inoculated vs. non-inoculated dish (treatments B–0, F–0 and H–0), two non-inoculated dishes
(treatment 0–0) or the dish inoculated with O. maius B vs. one of the P. fortinii strains (treatments B–F and B–H). The data were
divided into two groups (in the white cells: treatments B–0, F–0 and H–0; in the gray cells: treatments B–F and B–H) for the
statistical analysis (see Materials and Methods). The numbers in the table are means of the measured parameters ± SD (WDR) or the
95% Confidence Intervals (Ratio). The different letters show significantly different groups at p<0.05.
0–0
B–0
F–0
H–0
B–F
B–H
WDR (mg)
73.9±32a
71.8±33a
64.2±33a
49.9±23a
74.1±28a
75.7±25a
81.4±22a
65.4±32a
64.7±31a
58.7±23a
61.9±21a
73.0±45a
Ratio
1.04
(0.92–1.16)a
1.34
(0.81–1.86)ab
0.99
(0.77–1.22)a
1.61
(0.62–2.60)b
1.22
(0.67–1.77)a
0.99
(0.64–1.35)a
in N uptake by inoculated plants. To our knowledge, this is
the first report about such effects observed for ericaceous
plants inoculated with O. maius.
The plants inoculated with O. maius B had higher foliar
N content when compared to both control and either of two
P. fortinii strains and also higher foliar P content when
compared to control and P. fortinii F. On the other hand, P.
fortinii H also increased foliar P content compared to the
control, which confirms its beneficial effect for the
inoculated plants and at the same time highlights the strain
specificity, since P. fortinii F failed to facilitate P uptake
by the inoculated plants. In regard to nutrient availability
for plants inoculated with DSE, Jumpponen et al. (1998)
reported enhanced phosphorus uptake by Pinus contorta
when inoculated with P. fortinii. Studies addressing similar
questions with ericaceous host plants are missing. In our
94
M. VOHNIK ET AL.
previous study (Vohník et al., 2003) we reported no effect
of two P. fortinii strains (one of them was P. fortinii F
from this study) on the growth of Rhododendron cv. BelleHeller in two different substrates, either sterilized or nonsterilized.
A few authors have reported the presence of both ErM
and DSE fungi in the root system of a single ericaceous
plant (Urcelay, 2002; Midgley et al., 2004). However, there
are no experimental data explaining the ecophysiological
significance of these observations. Our experiment is, to
our knowledge, the first attempt to artificially introduce
both kinds of fungi into the root systems of individual host
plants and to trace the effect of the introduction on the
physiology of the inoculated plants.
We show that in the terms of the nutrient uptake, the
interaction among O. maius and P. fortinii is highly strainspecific: co-inoculation with O. maius B and P. fortinii H
significantly increased foliar P and N content compared to
the control and increased foliar P content when compared to
co-inoculation with O. maius B and P. fortinii F. Coinoculation with O. maius B and P. fortinii F did not
influence P and N uptake. This indicates that P. fortinii F,
contrary to P. fortinii H, negated the positive effect of O.
maius B on P uptake by the host plants. It is difficult to
explain this observation, since both fungi were spatially
separated and the only communication among them could be
realized through the host plant shoot. The question whether
the strain specificity of the interaction is a result of the
origin of the fungal strains ("positively" interacting O.
maius B and P. fortinii H were isolated from the roots of
rhododendrons, "neutral" P. fortinii F from the roots of V.
myrtillus, see Materials and Methods) remains to be
answered in an experiment using V. myrtillus as a host
plant.
It should be emphasized that even if the co-inoculation
with O. maius B and P. fortinii H increased P uptake
compared to the control, co-inoculation with O. maius B
and P. fortinii strains was never more efficient in the terms
of nutrient uptake by host plant than the inoculation with
single O. maius B. We can draw two conclusions from these
observations. Firstly, under the experimental conditions,
plants will benefit most from the presence of the single O.
maius B without the need for other fungi in or around the
root system (here two strains of P. fortinii); secondly, even
the presence of fungi other than ErM in or around root
system (here P. fortinii H) will still increase P and N
uptake compared to the non-mycorrhizal control treatment,
without negatively influencing the measured physiological
parameters of host plants. Under different experimental
conditions, plants with a combination of O. maius B+P.
fortinii H in or around roots could have the advantage of the
presence of an extra DSE fungus, which might improve
access to soil nutrient sources other than peat, which was
used in our experiment. Based on these conclusions, we can
hypothesize that under our experimental conditions, O.
maius B is the superior associate with roots of
Rhododendron cv. Azurro compared to both P. fortinii
strains. It is interesting to compare this hypothesis with the
findings of Midgley et al. (2004) who reported that 75% of
327 fungal endophyte isolates from ericaceous Woollsia
pungens Cav. (Muell.) and Leucopogon parviflorus (Andr.)
Lindl. was represented by a single putative taxon with
affinities to Helotiales ericoid mycorrhizal ascomycetes,
which was spatially widespread in the root systems of both
plants. Therefore, it seems that single fungal strains are able
to dominate in root systems of ericaceous plants, depending
on the environmental conditions. It would be interesting to
simultaneously inoculate the root system of a single
ericaceous
host
plant
with
multiple
ericoid
mycorrhizal/DSE fungal strains. Shifting experimental
conditions could reveal the preferences of inoculated fungi
(or their host plants) in relation to the physiological
response of host plants.
Foliar C:N ratio is linked to soil C:N ratio and is an
important parameter characterizing substrate nutrient
availability (Cairney and Meharg, 2003). Our results show
that co-inoculation with O. maius B and both P. fortinii
strains decreased foliar C:N ratio, which would decrease C:N
ratio in the rhododendron litter. The significance of this
intricate effect remains unclear, since ericoid mycorrhizal
fungi are known to be able to draw nutrients directly from
complex organic substrates and thus have a competitive
advantage in the environments with high C:N ratios (Read
and Perez-Moreno, 2003). Decreased soil C:N ratios would
likely result in the substitution of ericaceous plants by
other species better adapted to this environmental condition
(Read et al., 2004).
Differences in root biomass distribution revealed the
tendency of the experimental plants to accumulate more root
biomass (reflected by the weight of the dried root biomass)
into dishes inoculated with P. fortinii H than to those noninoculated or inoculated with P. fortinii F. A similar trend,
however statistically non-significant, was observed for O.
maius B compared to non-inoculated dishes. Since there was
no influence of inoculation on the total weight of the dried
biomass of the whole root systems, we conclude that P.
fortinii H, and to a lesser extent O. maius B, altered the
distribution but did not stimulate extra production of roots
in the inoculated dishes. There is also a possibility that the
root distribution could have been influenced by the nutrients
supplied to the substrate through the inoculation procedure,
whereby the inoculum may have included some nutrients
from the fungal culture medium (see Materials and
Methods). If this was true, the inoculated dishes would have
been favored in terms of the distribution of the roots, which
was however not the case (compare the distribution of the
roots in the dishes inoculated with P. fortinii F and P.
fortinii H).
Both O. maius B and P. fortinii H failed to form
extensive intracellular root colonization in the Fungal
Efficacy Experiment. Intracellular structures, such as ericoid
mycorrhizal coils and loops and DSE intraradical hyaline
INOCULATION OF RHODODENDRON WITH O. MAIUS AND P. FORTINII
hyphae, supposed to be the nutrient exchange sites (Smith
and Read, 1997; Barrow, 2003), were missing in significant
amounts. Similar to our observation, Piercey et al. (2002)
reported a lack of ErM structures in Rhododendron
groenlandicum inoculated with two strains of O. maius and
attributed this observation to the saprobic abilities of O.
maius strains. The authors stated that oidiodendrons were
more efficient as free-living saprobes than in association
with roots. In contrast, Usuki et al. (2003) reported that O.
maius formed ErM with Rhododendron obtusum var.
kaempferi. At low levels of mycorrhizal colonization, it is
difficult to attribute the effects of the inoculation directly to
the inoculated mycorrhizal fungi. However, it is accepted
that in the case of ectomycorrhizal symbioses, even low
colonization levels can produce significant effects on host
plant performance (Smith and Read, 1997). Unfortunately,
similar studies with ericoid mycorrhiza or DSE associations
are missing.
The screening of the stained roots revealed that the fungi
inoculated into the dishes in the Fungal Efficacy
Experiment were alive during our experiment. The
inoculated fungi were apparently able to survive without
carbon flow from the plants and thus, behave
saprotrophically. The increased nutrient content of host
plant tissues observed with fungal inoculation, despite a
lack of vigorous mycorrhizal structures, indicates the ability
of the inoculated fungi to enhance nutrient uptake in their
host plants. Combining the observations of increased
nutrient uptake, altered root biomass distribution and low
colonization rates, we deduce that O. maius B and P. fortinii
H increased nutrient availability in the rhizosphere of the
host plants rather than directly transported nutrients into the
plant tissues. As a result, the inoculated plants tended to
produce more root biomass in the compartments with
higher nutrient availability, thus increasing the area for
nutrient absorption. Our deduction emphasizes the
saprotrophic capabilities of both O. maius B and P. fortinii
H strains and highlights the significance of such features for
plants in general, because they enable the fungi from the
mycorrhizal/saprotropic boundary to support the nutrient
uptake of plants without considerable intracellular
colonization. Under some circumstances, strains of O.
maius and P. fortinii certainly can form intracellular
structures of the ErM and DSE patterns. Our study indicates
that the absence of such structures in the roots does not
imply the absence of effects of these fungi on the
physiology of the host plants.
For example, we observed proliferating, vigorously
growing non-mycorrhizal roots of rhododendrons in organic
material (old homogenized tree bark) colonized by mycelium
connected with fruitbodies of saprotrophic Agrocybe
(unpublished data). The root system outside of the organic
material was much less developed, even when containing
intracellular structures resembling ErM. The need to study
the fungal community not only in, but also around, the
roots of ericaceous plants is evident.
95
To summarize, the results of our experiments revealed i)
positive effect of O. maius on P, and to some extent also on
N uptake, connected with lowered foliar C:N ratio; ii)
strain-specific influence of P. fortinii on P and N uptake and
the potential of P. fortinii to improve this uptake in
inoculated plants; iii) highly strain-specific interaction of O.
maius with P. fortinii, driving the effect of both fungi on N
a P uptake when inoculated simultaneously; iv) the ability
of P. fortinii H to influence the biomass distribution in the
root system of its host plant, likely by releasing nutrients
into the rhizosphere and v) the ability of O. maius B and P.
fortinii H to influence nutrient uptake at very low
colonization rates, likely by increasing nutrient availability
in the rhizosphere.
Acknowledgements
The study was financed by the Grant Agency of Charles
University (project GAUK 211/2004/B-BIO/PrF), and the
COST E38.003 project 1P05OC081. M. Vohník was
financially supported by the Grant Agency of the Czech
Republic (project GACR no. 206/03/H137). Authors thank
to Jan Holub (Biolab Ltd., Olomouc, CZ) for the plant
material, Marie Albrechtová (Institute of Botany,
Pruhonice, CZ) for the analyses of the nutrients, Tomás
Frantík (Institute of Botany, Pruhonice, CZ) for the support
with the statistical analyses, Kirsten Lloyd (University of
New Hampshire, USA) for spell-check and comments on
the manuscript and Elena Martino (University of Torino,
Italy) for providing the culture of H. ericae. We appreciate
valuable comments of two anonymous reviewers, which
helped to improve the manuscript and stimulated the
Discussion chapter.
REFERENCES
Ahlich, K. and Sieber, T.N. 1996. The profusion of dark septate
endophytic fungi in non-ectomycorrhizal fine roots of forest
trees and shrubs. New Phytologist 132: 259–270.
Bajwa, R. and Read, D.J. 1985. The biology of mycorrhiza i n
the Ericaceae: IX. Peptides as nitrogen sources for
mycorrhizal and non-mycorrhizal plants. New Phytologist
101: 459–467.
Bajwa, R., Abuarghub, S., and Read, D.J. 1985. The biology of
mycorrhiza in the Ericaceae. X. The utilization of proteins
and the production of proteolytic enzymes by mycorrhizal
plants. New Phytologist 101: 469–486.
Barrow, J.R. 2003. Atypical morphology of dark septate fungal
root endophytes of Bouteloua in arid southwestern USA
rangelands. Mycorrhiza 13: 239–247.
Brundrett, M., Bougher, N., Dell, B., Grove, T., and Malajczuk,
N. 1996. Working with mycorrhizas in forestry and
agriculture. ACIAR Monograph 32, Canberra, 374 pp.
Cairney, J.W.G. and Meharg, A.A. 2003. Ericoid mycorrhiza: a
partnership that expoits harsh edaphic conditions.
European Journal of Soil Science 54: 735–740.
96
M. VOHNIK ET AL.
Couture, M., Fortin, J.A., and Dalpé, Y. 1983. Oidiodendron
griseum Robak: An endophyte of ericoid mycorrhiza i n
Vaccinium spp. New Phytologist 95: 375–380.
Currah, R.S., Tsuneda, A., and Murakami, S. 1993a.
Conidiogenesis in Oidiodendron periconioides and
ultrastructure of ericoid mycorrhizas formed with
Rhododendron brachycarpum. Canadian Journal of Botany
71: 1481–1485.
Currah, R.S., Tsuneda, A., and Murakami, S. 1993b.
Morphology and ecology of Phialocephala fortinii in roots
of Rhododendron brachycarpum. Canadian Journal o f
Botany 71: 1639–1644.
Dalpé, Y. 1986. Axenic synthesis of ericoid mycorrhiza i n
Vaccinium angustifolium Ait. by Oidiodendron species.
New Phytologist 103: 391–396.
Douglas, G.C., Heslin, M.C., and Reid, C. 1989. Isolation of
Oidiodendron maius from Rhododendron and ultrastructural
characterization of synthesized mycorrhizas. Canadian
Journal of Botany 67: 2206–2212.
Duclos, J.L. and Fortin, J.A. 1983. Effect of glucose and active
charcoal on in vitro synthesis of ericoid mycorrhiza with
Vaccinium ssp. New Phytologist 94: 95–102.
Ehrenberger, F. and Gorbach, S. 1973. Methoden der
organischen Elementar- und Spurenanalyse. Verlag Chemie,
Weinheim.
Jansa, J. and Vosátka, M. 2000. In vitro and post vitro
inoculation of micropropagated rhododendrons with ericoid
mycorrhizal fungi. Applied Soil Ecology 15: 125–136.
Johansson, M. 2001. Fungal associations of Danish Calluna
vulgaris roots with special reference to ericoid mycorrhiza.
Plant and Soil 231: 225–232.
Jumpponen, A. and Trappe, J.M. 1998a. Dark septate
endophytes: a review of facultative biotrophic rootcolonizing fungi. New Phytologist 140: 295–310.
Jumpponen, A. and Trappe, J.M. 1998b. Performance of Pinus
concorta inoculated with two strains of root endophytic
fungus, Phialocephala fortinii: effects of synthesis system
and glucose concentration. Canadian Journal of Botany 7 6 :
1205–1213.
Jumpponen, A., Mattson, K.G., and Trappe, J.M. 1998.
Mycorrhizal functioning of Phialocephala fortinii with
Pinus contorta on glacier forefront soil: interactions with
soil nitrogen and organic matter. Mycorrhiza 7: 261–265.
Jumpponen, A. 2001. Dark septate endophytes – are they
mycorrhizal? Mycorrhiza 11: 207–211.
Kerley, S.J. and Read, D.J. 1995. The biology of mycorrhiza i n
the Ericaceae. XVIII. Chitin degradation by Hymenoscyphus
ericae and transfer of chitin-nitrogen to the host plant. New
Phytologist 131: 369–375.
Kerley, S.J. and Read, D.J. 1997. The biology of mycorrhiza i n
the Ericaceae. XIX. Fungal mycelium as a nitrogen source for
the ericoid mycorrhizal fungus Hymenoscyphus ericae and its
host plant. New Phytologist 136: 691–701.
Kerley, S.J. and Read, D.J. 1998. The biology of mycorrhiza i n
the Ericaceae. XX. Plant and mycorrhizal necromass as
nitrogenous substrates for ericoid mycorrhizal fungus
Hymenoscyphus ericae and its host. New Phytologist 1 3 9 :
353–360.
Leake, J.R. and Read, D.J. 1989. The biology of mycorrhiza in
the Ericaceae: XIII. Some characteristics of the extracellular
proteinase activity of the ericoid endophyte Hymenoscyphus
ericae. New Phytologist 112: 69–76.
Martino, E., Turnau, K., Girlanda, M., Bonfante, P., and
Perotto, S. 2000. Ericoid mycorrhizal fungi from heavy
metal polluted soils: their identification and growth in the
presence of zinc ions. Mycological Research 1 0 4 :
338–344.
McLean, C.B. and Lawrie, A.C. 1996. Patterns of root
colonization in epacridaceous plants collected from different
sites. Annals of Botany 77: 405–411.
Midgley, D.J., Chambers, S.M., and Cairney, W.G. 2004.
Distribution of ericoid mycorrhizal endophytes and rootassociated fungi in neighbouring Ericaceae plants in the
field. Plant and Soil 259: 137–151.
Mitchell, D.T. and Read, D.J. 1981. Utilization of inorganic
and organic phosphates by the mycorrhizal endophytes of
Vaccinium macrocarpon and Rhododendron ponticum.
Transactions of the British Mycological Society 7 6 :
255–260.
Perotto, S., Girlanda, M., and Martino, E. 2002. Ericoid
mycorrhizal fungi: some new perspectives on old
acquaintances. Plant and Soil 244: 41–53.
Piercey, M.M., Thormann, M.N., and Currah, R.S. 2002.
Saprobic characteristics of three fungal taxa from ericalean
roots and their association with the roots of Rhododendron
groenlandicum and Picea mariana in culture. Mycorrhiza
12: 175–180.
Read, D.J. 1996. The structure and function of the ericoid
mycorrhizal root. Annals of Botany 77: 365–374.
Read, D.J. and Perez-Moreno, J. 2003. Mycorrhizas and
nutrient cycling in ecosystems – a journey towards
relevance? New Phytologist 157: 475–492
Read, D.J., Leake, J.R., and Perez-Moreno, J. 2004.
Mycorrhizal fungi as drivers of ecosystem processes i n
heathland and boreal forest biomes. Canadian Journal o f
Botany 82: 1243–1263.
Rice, A.V. and Currah, R.S. 2001. Physiological and
morphological variation in Oidiodendron maius. Mycotaxon
79: 383–396.
Smith, S.E. and Read, D.J. 1997. Mycorrhizal Symbiosis.
Second Edition. Academic Press, London. 605 pp.
Stoyke, G., Egger, K.N., and Currah, R.S. 1992.
Characterization of sterile endophytic fungi from the
mycorrhizae of subalpine plants. Canadian Journal o f
Botany 70: 2009–2016.
Urcelay, C. 2002. Co-occurrence of three fungal root
symbionts in Gaultheria poeppiggi DC in Central
Argentina. Mycorrhiza 12: 89–92.
Usuki, F., Junichi, A.P., and Kakishima, M. 2003. Diversity of
ericoid mycorrhizal fungi isolated from hair roots of
Rhododendron obtusum var. kaempferi in a Japanese red
pine forest. Mycoscience 44: 97–102.
Vohník, M., Lukancic, S., Bahor, E., Regvar, M., Vosátka, M.,
and Vodnik, D. 2003. Inoculation of Rhododendron cv.
Belle-Heller with two strains of Phialocephala fortinii i n
two different substrates. Folia Geobotanica 38: 191–200.
Xiao, G. and Berch, S.M. 1995. The ability of known ericoid
mycorrhizal fungi to form mycorrhizae with Gaultheria
shallon. Mycologia 87: 467–470.