endophytic fungi in knotweed
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fungal analysis in japanese knot weed seedsTRANSCRIPT
f u n g a l b i o l o g y 1 1 6 ( 2 0 1 2 ) 7 8 5e7 9 1
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Endophytic fungi associated with Fallopia japonica(Polygonaceae) in Japan and their interactions with Pucciniapolygoni-amphibii var. tovariae, a candidate for classicalbiological control
Daisuke KUROSEa,*, Naruto FURUYAb, Kenichi TSUCHIYAb, Seiya TSUSHIMAa,Harry C. EVANSc
aNatural Resources Inventory Center, National Institute for Agro-Environmental Sciences, 3-1-3 Kannondai, Tsukuba, Ibaraki 305-8604,
JapanbLaboratory of Plant Pathology, Faculty of Agriculture, Kyushu University, 6-10-1 Hakozaki, Higashi-ku, Fukuoka 812-8581, JapancCABI Europe-UK, Bakeham Lane, Egham, Surrey, TW20 9TY, UK
a r t i c l e i n f o
Article history:
Received 22 August 2011
Received in revised form
16 April 2012
Accepted 18 April 2012
Available online 28 April 2012
Corresponding Editor:
Barbara Schulz
Keywords:
Endophyte diversity
ITS sequences
Japanese knotweed (Fallopia japonica)
Phomopsis
Puccinia polygoni-amphibii var. tovariae
Synergistic interaction
* Corresponding author. Tel.: þ81 29 838 8257E-mail addresses: [email protected],
cabi.org1878-6146/$ e see front matter ª 2012 The Bdoi:10.1016/j.funbio.2012.04.011
a b s t r a c t
Fallopia japonica (Polygonaceae), or Japanese knotweed, is now spreading globally, causing se-
rious problems in Europe and North America in both natural and urban habitats. There is an
urgent need for alternativemanagement solutions, and classical biological control, using co-
evolved natural enemies found in the native range, is currently being investigated. Here, we
isolated fungal endophytes from F. japonica in Japan, its natural habitat, to find endophytes
that might increase the virulence of a coevolved rust pathogen, Puccinia polygoni-amphibii var.
tovariae. A total of 1581 fungal endophytes were recovered from F. japonica and classified into
15 taxa. Five genera (Colletotrichum, Pestalotiopsis, Phoma, Phomopsis, and Alternaria) were
dominant as endophytes in F. japonica. A greenhouse study of the dominant endophy-
teepathogen interactions revealed three types of reactions: suppressive, synergistic, and
neutral. In particular, one Phomopsis isolate e closely related to Diaporthe medusaea, based
on ITS sequences e promoted the pathogenic aggressiveness of P. polygoni-amphibii var.
tovariae and, therefore, this interaction is potentially useful to increase the effectiveness
of the rust fungus as a biological control agent of F. japonica in its invasive range.
ª 2012 The British Mycological Society. Published by Elsevier Ltd. All rights reserved.
Introduction 19th Century (Synge 1956). This invasiveness has imposed
Fallopia japonica (Houtt.) Ronse Decr., or Japanese knotweed,
belongs to the family Polygonaceae and is a problematic inva-
sive weed in both North America and Europe, especially in the
UK, following its introduction into Europe from Japan in the
; fax: þ81 29 838 [email protected]
ritish Mycological Societ
a significant cost for urban development, as well as posing
a threat to biodiversity (Bailey & Conolly 2000). Control is dif-
ficult to achieve as the plant has an extensive rhizome system
that survives in spite of apparently successful above-ground
chemical control, necessitating the issue of official knotweed
c.jp, [email protected], [email protected], h.evans@
y. Published by Elsevier Ltd. All rights reserved.
786 D. Kurose et al.
management guidance documents in the UK (Welsh
Development Agency 1998; Environment Agency 2007). Thus,
there is an urgent need for sustainable control measures for
F. japonica in its invasive range. Classical biological control e
involving the introduction of coevolved natural enemies
from the plant’s centre of origine is being investigated as a po-
tential approach for management of this weed in the UK.
Surveys in the Japanese endemic range revealed a guild of
specialised natural enemies which can severely reduce the
vigour and change the population dynamics of F. japonica
(Kurose et al. 2006). In particular, two fungal agents, the rust
fungus, Puccinia polygoni-amphibii var. tovariae (Kurose et al.
2009b) and a leaf-spot fungus,Mycosphaerella polygoni-cuspidati
(Kurose et al. 2009a), caused severe damage to F. japonica in the
field. During attempts to isolate Mycosphaerella and other
necrotrophic fungal pathogens from the surface-sterilised,
infected leaves of F. japonica, pathogen colonies were fre-
quently overgrown by faster-growing fungal ‘contaminants’.
Because samples were taken from plants in their natural
range, and isolations were made only from the advancing
edges of fresh legions, we assumed that a proportion of these
may represent specialist or coevolved endophytic fungi rather
than generalist or opportunistic saprophytes.
Fungal endophytes occur within the living tissues of
plants (Petrini 1991; Clay 1993) without producing any appar-
ent symptoms, and their presence may confer certain advan-
tages to the host plant (Carroll 1991). Mutualistic endophytic
fungi offer a variety of potential benefits to their host plants:
growth enhancement; tolerance to abiotic factors, including
drought, heat, and heavy metals; resistance to pests and dis-
eases (Redman et al. 2001; Rudgers et al. 2004; Schulz & Boyle
2005). Evans (2008) reported that the endophytic mycobiota
of F. japonica is relatively depauperate in its weedy invasive
range in the UK, especially in urban situations; whilst
Huang et al. (2008) reported the common occurrence of
Fig 1 e Map of collection sites of Fallopia japonica for isol
fungal endophytes in Polygonum cuspidatum (syn. F. japonica)
in part of its native range in China. Our preliminary results
show that there is a rich and diverse endophytic mycobiota
associated with leaves of F. japonica in Japan (Daisuke Kurose,
unpublished) compared to the UK (Evans 2008).
From the viewpoint of the efficacy of classical biological
control, it is important to understand the interaction not
only between endophytes and hosts, but also between endo-
phytes and pathogens. Synergistic effects, following co-
inoculation with two pathogens or more, have been observed
during studies to enhance the impact of biological control
agents (Crawley et al. 1985; Morin et al. 1993a, b; Guske et al.
2004). However, interactions between fungal endophytes and
the pathogens have not been reported previously. If endo-
phytes have a potential role of promoting aggressiveness of
pathogens in their hosts, this interaction could possibly be
exploited for the biological control of weeds.
In this study, we investigated the fungal endophytes asso-
ciated with F. japonica in part of its native range in southern
Japan. Then, we monitored the interactions of dominant
endophytes with the rust pathogen, P. polygoni-amphibii var.
tovariae to find ones that synergistically interact with the
rust in F. japonica.
Materials and methods
Collection of samples
Samples were collected from Fallopia japonica, located at: Kusu
(33� 16. 6660N, 131� 09. 6210E; 350 m a.s.l.) in Oita Prefecture; Mt.
Hiko (33� 29. 1020N, 130� 53. 8170E; 488 m a.s.l.) in Fukuoka Pre-
fecture; and Unzen (32� 43. 8530N, 130� 16. 0600E; 693 m a.s.l.) in
Nagasaki Prefecture; all situated on Kyushu Island in Japan
(Fig 1) from where the European introductions originated
ation of fungal endophytes on Kyushu Island, Japan.
Endophyte-rust interactions in Japanese knotweed 787
(Bailey & Conolly 2000). Data from these three sites were used
for the analysis of the composition of fungal endophytes. Dur-
ing the study period, the annual rainfall at three sites was
1410, 2142, 2365 mm, and the median temperature was
14.1 �C, 15.3 �C, 12.7 �C, at Kusu, Mt. Hiko, and Unzen,
respectively.
Plants with more than five expanded leaves were sampled
at the beginning of this study, because preliminary experi-
ments using unopened leaves showed no fungal colonisation.
Fifty apparently healthy leaves were collected from ten indi-
vidual plants from each site in May, September, and Decem-
ber 2005. Samples were brought to the laboratory in paper
bags and stored in a refrigerator at 4 �C for no longer than
48 h prior to use.
Isolation of endophytes
Leaf pieces, approximately 0.5� 0.5 cm, were excised from ap-
parently healthy leaves of Fallopia japonica. The number of leaf
pieces depended on the size of the leaf. Surface sterilisation
was carried out by immersion in 70 % ethanol solution for
3e5 s and 1.5 % sodium hypochlorite solution for 10 min.
The leaf pieces were thoroughly rinsed three times in sterile
distilled water. After surface sterilisation, four leaf pieces
were placed on potato carrot agar (PCA; decoction of 20 g po-
tato and 20 g carrot, and 20 g agar l�1) in 9-cm diam Petri
dishes and incubated at 25 �C for 2 weeks. The absence of
strictly epiphytic bacteria, yeasts and zygomycetes from the
cultures indicated that the sterilisation protocol was effective
(Arnold et al. 2000). All fungal colonies growing from the leaf
pieces were subcultured onto PCA.
Morphological characterisation
The morphological identification of endophytic fungal iso-
lates to genus level was based on the macro-morphology
of the fungal culture as well as micro-morphology using
standard mycological manuals (e.g. Ellis 1971; Sutton
1980). To induce sporulation, each of the fungal isolates
was subcultured on potato dextrose agar (PDA; decoction
of 200 g potato, 15 g dextrose, 20 g agar l�1), PCA, and water
agar (WA; 20 g agar l�1), prior to placing an autoclaved leaf
piece of Fallopia japonica on each medium. After incubation
for 2 m at 25 �C, the isolates that failed to sporulate were
classified in the group Mycelia sterilia. Cultures of the rep-
resentative isolates in each taxon were stored under min-
eral oil or sterile distilled water (Smith 2002) at room
temperature.
Genotypic characterisation of dominant fungal endophytesand an unidentified Ascomycete
DNA isolation and PCR amplificationFive dominant taxa (Colletotrichum, Pestalotiopsis, Phoma, Pho-
mopsis, and Alternaria) and a member of an unidentified asco-
mycete genus were subjected to identification at the species
level using sequencing of the internal transcribed spacer
(ITS) region, including the 5.8S rDNA. Based on morphological
classification, different morphospecies in each taxon were
selected for molecular analysis. Mycelia grown on PCA at
20 �C were harvested after 1 m. Genomic DNA was extracted
with the DNeasy Plant Mini Kit (QIAGEN, Valencia, CA, USA)
according to the supplier’s protocols. ITS region including
the 5.8S rDNA was amplified as a single fragment using the
polymerase chain reaction (PCR) with Taq DNA polymerase
and with the primer pairs ITS1 (50-TCCGTAGGTGAACCTGCGG-30) and ITS4 (50-TCCTCCGCTTATTGATATGC-30)(White et al. 1990). Optimal conditions for PCR were deter-
mined with a 50-ml reaction volume containing 5.0 ml of 10�Taq buffer (100 mMTriseHCl, pH 9.0, 500 mMKCl and 20% Tri-
ton X-100), 1.25 U of Taq polymerase, 1.5 mM MgCl2, 200 mM
dNTPs, 1.0 ml of DNA template solution (10 ng) and 0.2 mM
each primer. Amplification of the desired fragment was per-
formed with a MyCycler Thermal Cycler (Bio-Rad, Hercules,
CA, USA) under the following conditions: 5 min initial dena-
turation at 96 �C, 36 cycles of denaturation for 45 s at 94 �C,annealing for 30 s at 50 �C, and extension for 1.5 min at
72 �C; the reaction was terminated after a final extension at
72 �C for 8 s.
DNA sequencingPCR products were purified using the QIAquick PCR purification
kit (QIAGEN, Valencia, CA, USA) following the manufacturer’s
protocol and prepared for sequencing using a BigDye Termina-
tor v3.1 Cycle Sequencing Ready Reaction Kit (Applied Biosys-
tems, Foster City, CA, USA) with the same primers used for
PCR amplification under the following conditions: 1 cycle of
96 �C for 1 min, 25 cycles of 96 �C for 10 s, 53 �C for 5 s, 60 �Cfor 4 min. Cycle sequencing reaction products were finally puri-
fied using a BigDye XTerminator Purification Kit (Applied Bio-
systems), and then sequenced using an ABI 3730xl DNA
Analyzer (Applied Biosystems). The DNA sequences obtained
in this study were deposited in the DDBJ/EMBL/GenBank data-
base systems under accession numbers AB640840-AB640842,
AB640844-AB640845, AB640847-AB640848, AB697732-AB697738,
and AB698854.
Inoculation and re-isolation of endophytes
Leaf inoculations were conducted in order to determine if the
isolated fungi could colonize healthy plants of Fallopia japonica
asymptomatically. Rhizomes collected from natural popula-
tions were grown in commercial proprietary compost, and
maintained in a greenhouse with supplementary lighting
and temperature of 20e25 �C. By using this methodology, the
shoots emerging from these rhizomes were confirmed free
of endophytes based on the fact that no microorganisms
were isolated from the leaves in pre-trials.
Freely-sporulating strains of five dominant taxa, Colletotri-
chum TH-SZ2d, Pestalotiopsis TH-SZ1c, PhomaHND-Bc, Phomop-
sis HS-SZ1j, and Alternaria W2374i, isolated during this study
and subsequently identified bymolecular phylogeny, were se-
lected for further inoculation experiments. Control plants
were inoculated with 0.05 % Tween-80 only. Plants of F. japon-
ica at the five-leaf stage were inoculated with spore suspen-
sions containing approximately 1.0� 106 spores ml�1 in
0.05 % Tween-80, using a fine brush to paint both adaxial
and abaxial sides of leaves. After treatment, all plants were
transferred to a dew chamber at 20 �C and 100 % relative
Table 1 e Isolation prevalence and number taxa of fungalendophytes isolated from Fallopia japonica at each site.
Characteristic Kusu Mt. Hiko Unzen
No. of samples 513 513 513
No. of isolates recovered 469 571 541
Total taxa identified 14 11 11
Isolate prevalence (%)a 79.7 88.1 84.2
a Isolate prevalence (%) ¼ (total number of leaf pieces yielding
more than one isolate)/(total number of leaf pieces in that
trial) � 100.
788 D. Kurose et al.
humidity, without light, for 48 h. Subsequently, all inoculated
plants were maintained in the greenhouse together with the
control plants. Four weeks after inoculation, re-isolation
from all the inoculated leaves, and non-inoculated upper
leaves which grew after treatment, as well as the control
plants, was undertaken using the same procedure described
above in order to investigate colonisation of and systemic in-
fection by the selected strains. Three replicate plants, with
five leaves per plant, were used.
Endophytes/Puccinia interaction
The interaction of fungal endophyteswith the rust fungus, Pucci-
nia polygoni-amphibii var. tovariae, was examined in glasshouse
experiments to determine if they have a significant synergism
on the pathogenic activity of the rust in Fallopia japonica. The
five dominant endophytes selected previously, Colletotrichum
TH-SZ2d, Pestalotiopsis TH-SZ1c, Phoma HND-Bc, Phomopsis
HS-SZ1j, and Alternaria W2374i, were inoculated 1 week prior to
inoculation with P. polygoni-amphibii var. tovariae. The same
inoculationmethod of fungal endophyteswas used as described
previously. For Puccinia, urediniospores weremixedwith talcum
powder (spores: talc ¼ 1:10) (w/w) and then applied to both leaf
surfaces using a fine brush. In the control treatment, only
Tween-80 was applied 1 week before the rust fungus. An addi-
tional three replicates in each experiment were inoculated
with eachendophyte only, inorder to confirmendophyte coloni-
sation in case the Puccinia or the talcum powder impeded endo-
phyte re-isolation. Inoculated plants were placed in a dew
chamber at 20 �C, without light, for 48 h. Subsequently, all inoc-
ulated plants weremaintained in the greenhouse, together with
thecontrolplants inoculatedwith thePucciniaorendophyteonly.
Eachexperiment contained tenplants,withfive leavesper plant,
per treatment, and thisexperimentwas repeated four times.The
Puccinia infection was assessed in terms of the number of rust
pustules produced on the abaxial surface of each leaf per leaf
area (cm2) at every 3 days post-inoculation (dpi).
Statistical analysis
The percentage of isolate prevalence was counted as the ratio
of the number of leaf pieces infected with endophytes to the
total number (Petrini et al. 1982). Relative isolation frequency
was expressed as the proportion of the number of isolates
within one endophyte taxon to the total number. The result-
ing data from each experiment were performed by analysis
of variance (ANOVA) before using TukeyeKramer’s Honestly
Significant Difference (HSD) test to compare means. The sta-
tistical software package JMP� 7 for Windows (SAS Institute
Inc., Cary, NC, USA) was used for the analysis.
Results
Isolate prevalence
A total of 1539 leaf pieces were processed from three sites; 1581
fungal isolates were recovered. The overall isolate prevalence
(%) ateachsite isgiven inTable1. Inall cases, ahigh isolateprev-
alence (79.7e88.1 %) of fungal endophytes was shown.
Composition of endophytic assemblages
The 1581 fungal endophytes of fungal endophytes resulting
from the study were categorized into 15 taxa based on mor-
phological characteristics. These comprised ten genera of
Hyphomycetes, three genera of Ascomycetes, and an uniden-
tified Ascomycete genus, as well as the Mycelia sterilia group
(Fig 2). Out of these 14 genera plus Mycelia sterilia, Colletotri-
chum, Phomopsis, Pestalotiopsis, and Mycelia sterilia were sepa-
rated into two ormoremorphospecies, on the basis of conidial
size or colony characteristics. The unidentified Ascomycete is
considered to represent a new genus close to Pezicula (Derma-
teaceae, Helotiales), based on sequence data, which also pro-
duces a highly distinctive anamorph with arthrosporic
conidiogenesis, similar to that of Neozythia (Sutton 1980).
As shown in Fig 2, of all the taxa isolated from Fallopia ja-
ponica leaves, Colletotrichum spp. had the highest average in
relative isolation frequency. The second most frequent endo-
phytic taxa were Phoma sp., Phomopsis spp., Pestalotiopsis spp.,
and Alternaria sp. with mean relative isolation frequencies of
13.9 %, 12.7 %, 10.4 %, and 9.3 %, respectively (Fig 2).
Isolates in the five dominant genera, Colletotrichum, Phoma,
Phomopsis, Pestalotiopsis, and Alternaria, were identified to spe-
cies level based on ITS sequences. The Colletotrichum isolates
could be separated into Colletotrichum acutatum and Colletotri-
chum gloeosporioides; and Pestalotiopsis spp. comprised three
species, Pestalotiopsis microspora, Pestalotiopsis sydowiana, and
Pestalotiopsis vismiae. The Phomopsis isolates were grouped
into seven different species, Phomopsis eucommicola, Phomopsis
liquidambari, Phomopsis longicolla, Phomopsis loropetali, Phomop-
sis phoenicicola, Diaporthe medusaea, and Diaporthe phaseolorum.
Phoma and Alternariawere identified as Phoma macrostoma and
Alternaria alternata, respectively.
Re-isolation of endophytes
The five selected dominant endophytes, Colletotrichum TH-
SZ2d, Phoma HND-Bc, Phomopsis HS-SZ1j, Pestalotiopsis TH-SZ1c,
and Alternaria W2374i, which are closely related to Colletotri-
chum gloeosporioides, Phoma macrostoma, Diaporthe medusaea,
Pestalotiopsis vismiae, and Alternaria alternata, respectively,
were successfully re-isolated from the inoculated leaves 28
dpi, but not from the non-inoculated upper (youngest) leaves
(data not shown). No fungal endophyte was obtained from
the control plants. All the inoculated leaves remained
asymptomatic.
0
10
20
30
40
Mean
relative iso
latio
n f
req
uen
cy (%
)
Taxon
b
a
bb
b
cccd
cdcdcd
cdcd
cd d
Fig 2 e Mean relative isolation frequencies of different endophytic fungal taxa isolated from Fallopia japonica. Vertical bars
indicate standard errors (n [ 9). Columns with different letters are significantly different according to TukeyeKramer’s HSD
test (P < 0.05).
Endophyte-rust interactions in Japanese knotweed 789
Endophyte/Puccinia interaction
The results show three types of reactions in effectiveness on
rust disease development; ‘suppressive fungi’, ‘promoting
30
2)
Alternaria W2374i
20
25
f a
re
a (c
m2
Colletotrichum TH-SZ2d
Pestalotiopsis TH-SZ1c
Phoma HND-Bc
15
ed
in
ia / leaf
Phomopsis HS-SZ1j
Control (the rust only)
10
mb
er o
f u
re
0
5
Nu
m
0 3 6 9Days post-inocula
Fig 3 e The impact of endophyte inoculation on the performanc
Alternaria W2374i, Colletotrichum TH-SZ2d, Pestalotiopsis TH-SZ1
week before P. polygoni-amphibii var. tovariae. In control treatm
The Puccinia infection was assessed in terms of the number of ru
leaf area (cm2) at 3-d intervals post-inoculation. Photographs we
amphibii var. tovariae on Fallopia japonica. The photographs are
trichum TH-SZ2d, (C) Phoma HND-Bc. Vertical bars indicate stan
each of the dpi are not significantly different according to Tukeye
four times.
fungi’, and ‘non-effective or neutral fungi’ (Fig 3). Colonisation
by Alternaria W2374i and Phoma HND-Bc inhibited rust coloni-
sation; whilst that of Phomopsis HS-SZ1j significantly pro-
moted disease development 9, 12 and 15 dpi compared with
A
a aa
a a
ab ab
Bab
bb
b
bc
bc
C
cc
c
c
c c
bc
c
12 15tion
e of Puccinia polygoni-amphibii var. tovariae. Five endophytes,
c, Phoma HND-Bc, and Phomopsis HS-SZ1j, were inoculated 1
ent, only Tween-80 was applied 1 week before the Puccinia.
st pustules produced on the abaxial surface of each leaf per
re taken at 15 dpi of disease symptoms caused by P. polygoni-
of leaves inoculated with (A) Phomopsis HS-SZ1j, (B) Colleto-
dard errors (n [ 40). Values followed by the same letter for
Kramer’s HSD test (P < 0.05). This experiment was repeated
790 D. Kurose et al.
the control plants. No significant effects of Colletotrichum TH-
SZ2d, and Pestalotiopsis TH-SZ1c, were observed. Endophytes
were re-isolated from all the inoculated leaves, and none of
the fungal endophytes were obtained from the control leaves
treated with Tween-80 only.
In the plants pre-inoculated with the Phomopsis
straindalthough rust uredinia did not appear on the lower
leaf surface until 6 dpidafter 9 dpi the number of uredinia
per leaf area (cm2) was significantly increased as compared
with the plants inoculated with other endophytes, or with
Puccinia only.
Discussion
Our data show that Fallopia japonica has a rich and diverse en-
dophyticmycobiota in Japan. In the field, the unopened leaves
of F. japonicawere not colonized by endophytic fungi and older
leaves tended to have more endophytes than younger opened
leaves. This is in general agreement with investigations un-
dertaken with other host plants (e.g. Petrini 1991; Rodrigues
1994). Additionally, in the greenhouse, no endophytes were
isolated from the non-inoculated plants grown from the rhi-
zomes collected in the field, and none of the endophytes
that we inoculated colonised the test plants systemically.
These results suggest that the plants in the field are infected
by air-borne spores and are not systemically infected.
Five fungal genera, Colletotrichum, Pestalotiopsis, Phoma, Pho-
mopsis, and Alternaria, have been found as endophytes in nu-
merous other herbaceous host plants (e.g. Schulz et al. 1993;
Kumaresan & Suryanarayanan 2001; Photita et al. 2001, 2005;
Gange et al. 2007). In the present study, these were the domi-
nant endophyte representatives in F. japonica in Japan. Al-
though Phomopsis was also one of the dominant genera
isolated from this host in China, Colletotrichum, Pestalotiopsis,
Phoma, and Alternaria were not recorded (Huang et al. 2008).
The differences in Japan and China suggest that geography in-
fluences the distribution patterns of fungal endophytes, as
reported by Fisher et al. (1994).
An understanding of the fungal endophytes colonising the
target weed might be useful for understanding the success or
failure of classical biological control (Evans 2008). Endophytes
had already increased in September (data not shown) when
rust disease causedby Puccinia polygoni-amphibii var. tovariaebe-
gan to appear at the Kusu site. This pathogen caused severe
damage to F. japonica by December, and isolate prevalence of
endophytes was also high in December (data not shown).
Therefore, endophytic and pathogenic fungi may interact
with each other in plant tissues. In the present study, an inves-
tigation of the interaction between a rust fungus and the dom-
inant endophytic genera e such as Colletotrichum, Pestalotiopsis,
Phoma, Phomopsis, and Alternaria e was conducted. It has been
shown that endophytic fungi can induce resistance to patho-
gens (Arnold et al. 2003; Lee et al. 2009). Cheung & Barber
(1972) and Dingle & McGee (2003) reported that inoculation of
non-pathogenic fungal endophytes significantly reduced
stem/leaf rust disease in wheat, which is in agreement with
the results attained following inoculation with Alternaria and
Phoma in this study. However, in our study, we also found that
Phomopsis HS-SZ1j increased the number of uredinial pustules
of P. polygoni-amphibii var. tovariae. Thus, this Phomopsis strain
may be a synergist of the rust, thereby increasing its potential
as a biological control agent of F. japonica. To our knowledge,
this is the first report that an endophyte can act in synergy
withaplantpathogen, followingpre-inoculationwith theendo-
phyte ahead of the pathogen. The other four endophytes either
do not interact or have a different form of interaction.
Phomopsis spp. have been recorded as plant pathogens of
economically important crops, as well as inducers of latent in-
fection, and as asymptomatic endophytes in weeds and other
plant hosts (Cerkauskas et al. 1983; Kulik 1984; Okane et al.
1998; Bussaban et al. 2001; Kumaresan & Suryanarayanan
2001). Molecular analysis of the ITS region, including the 5.8S
rDNA sequences, indicates that PhomopsisHS-SZ1j is closely re-
lated toDiaporthe medusaeawhich is the teleomorph of Phomop-
sis rudis, previously recorded as a pathogen of Japanese pear in
Japan (Watanabe 1991). In the present study, no symptoms
were observed in F. japonica inoculated with the endophytic
Phomopsis strain. A fungus that occupies plant tissues asymp-
tomatically may also be a weak pathogen, or a virulent strain
detected during latency, or possibly a passive inhabitant of
a niche just waiting for an opportunity to propagate (Schulz
& Boyle 2005). Accordingly, this does not exclude the possibility
that PhomopsisHS-SZ1j may become pathogenic when the host
is stressed. Furthermore, the Phomopsis endophyte assemblage
associatedwith F. japonica in Japanwould appear to bemore di-
verse than that of other genera since seven distinct species
have been identified using morphology and molecular phylog-
eny. This result may imply that strains other than HS-SZ1j also
have the ability to increase the rust disease development.
In contrast,Alternaria and Phoma isolates inhibited rust col-
onisation; whilst Colletotrichum and Pestalotiopsis isolates were
non-effective or neutral on rust development. These results
offer evidence that there are three types of endophytic fungal
interactions, which could have an impact on plant pathogens;
‘suppressive fungi or bodyguards’, ‘promoting or synergistic
fungi’, and ‘non-effective or neutral fungi’, implying that un-
derstanding of the endophytic mycobiota and their potential
interactions is necessary when analysing the success or fail-
ure of classical biological control agents.
Overall, the endophyte assemblages isolated from F. japonica
in Japanwere diverse anddominated by five fungal genera:Colle-
totrichum, Pestalotiopsis, Phoma, Phomopsis, and Alternaria. In con-
trast, Evans (2008) reported that this plant in urban areas in the
UK lacks endophytes. More in-depth comparisons of the myco-
biota between Japan and theUKappear to bewarranted. In addi-
tion, the mechanisms underlying these competitive or
synergistic fungal interactions are not clear. Further study on
the interaction between these dominant endophytes and P. poly-
goni-amphibiivar. tovariae, couldenable thedevelopmentofanew
strategy of classical biological control using both coevolvedpath-
ogens and endophytes to increase disease impact.
Acknowledgements
This study was partly supported by a Grant-in-Aid (22380181,
227223) from the Japan Society for the Promotion of Science
for NF and DK.
Endophyte-rust interactions in Japanese knotweed 791
r e f e r e n c e s
Arnold AE, Maynard Z, Gilbert GS, Coley PD, Kursar TA, 2000. Aretropical fungal endophytes hyperdiverse? Ecology Letters 3:267e274.
Arnold AE, Mejia LC, Kyllo D, Rojas EI, Maynard Z, Robbins N,Herre EA, 2003. Fungal endophytes limit pathogen damage ina tropical tree. Proceedings of the National Academy of Sciences100: 15649e15654.
Bailey JP, Conolly AP, 2000. Prize-winners to pariahs e a history ofJapanese knotweed s.l. (Polygonaceae) in the British Isles.Watsonia 23: 93e110.
Bussaban B, Lumyong S, Lumyong P, McKenzie EHC, Hyde KD,2001. Endophytic fungi from Amomum siamense. CanadianJournal of Microbiology 47: 943e948.
Carroll GC, 1991. Fungal associates of woody plants as insectantagonists in leaves and stems. In: Barbosa P, Krischik VA,Jones CG (eds), Microbial Mediation of PlanteHerbivore Interac-tions. John Wiley & Sons, New York, pp. 253e271.
Cerkauskas RF, Dhingra OD, Sinclair JB, Asmus G, 1983.Amaranthus spinosus, Leonotis nepetaefolia, and Leonurussibiricus: new hosts of Phomopsis spp. in Brazil. Plant Disease 67:821e824.
Cheung DSM, Barber HN, 1972. Activation of resistance of wheat tostemrust.Transactions of the BritishMycological Society 58: 333e336.
Clay K, 1993. The ecology and evolution of endophytes. Agricul-ture, Ecosystems & Environment 44: 39e64.
Crawley DK, Walker HL, Riley JA, 1985. Interaction of Alternariamacrospora and Fusarium lateritium on Spurred Anoda. PlantDisease 69: 977e979.
Dingle J, McGee PA, 2003. Some endophytic fungi reduce thedensity of pustules of Puccinia recondita f. sp. tritici in wheat.Mycological Research 107: 310e316.
Ellis MB, 1971. Dematiaceous Hyphomycetes. CommonwealthMycological Institute, Kew.
Environment Agency, 2007. Managing Japanese Knotweed on Devel-opment Sites Available from: www.environment-agency.go-v.uk/static/documents/Leisure/japnkot_1_a_1463028.pdf (ac-cessed 28.06.2011)
Evans HC, 2008. The endophyte release hypothesis: implicationsfor classical biological control and plant invasions. In:Julien MH, Sforza R, Bon MC, Evans HC, Hatcher PE, Hinz HL,Rector BG (eds), Proceedings of the XII International Symposium onBiological Control of Weeds, La Grande Motte, France, 22e27 April2007. CABI Publishing, Wallingford, pp. 20e26.
Fisher PJ, Petrini O, Petrini LE, Sutton BC, 1994. Fungal endophytesfrom the leaves and twigs of Quercus ilex L. from England,Majorca and Switzerland. New Phytologist 127: 133e137.
Gange AC, Dey S, Currie AF, Sutton BC, 2007. Site- and species-specific differences in endophyte occurrence in two herba-ceous plants. Journal of Ecology 95: 614e622.
GuskeS,SchulzB,BoyleC, 2004.Biocontroloptions forCirsiumarvensewith indigenous fungal pathogens.Weed Research 44: 107e116.
Huang WY, Cai YZ, Hyde KD, Corke H, Sun M, 2008. Biodiversity ofendophytic fungi associated with 29 traditional Chinese me-dicinal plants. Fungal Diversity 33: 61e75.
Kulik MM, 1984. Symptomless infection, persistence, and pro-duction of pycnidia in host and non-host plants by Phomopsisbatatae, Phomopsis phaseoli, and Phomopsis sojae, and the taxo-nomic implications. Mycologia 76: 274e291.
Kumaresan V, Suryanarayanan TS, 2001. Occurrence and distri-bution of endophytic fungi in a mangrove community. Myco-logical Research 105: 1388e1391.
Kurose D, Renals R, Shaw R, Furuya N, Takagi M, Evans H, 2006.Fallopia japonica, an increasingly intractable weed problem in
the UK: can fungal pathogens cut through this Gordian knot?Mycologist 20: 126e129.
Kurose D, Evans HC, Djeddour DH, Cannon PF, Furuya N,Tsuchiya K, 2009a. Systematics of Mycosphaerella species as-sociated with the invasive Fallopia japonica, including the po-tential biological control agent M. polygoni-cuspidati.Mycoscience 50: 179e189.
Kurose D, Furuya N, Matsumoto M, Djeddour DH, Evans HC,Tsuchiya K, 2009b. Evaluation of a Puccinia rust as a potentialbiological control agent of Fallopia japonica. Journal of the Facultyof Agriculture, Kyushu University 54: 59e64.
Lee K, Pan JJ, May G, 2009. Endophytic Fusarium verticillioides re-duces disease severity caused by Ustilago maydis on maize.FEMS Microbiology Letters 299: 31e37.
Morin L, Auld BA, Brown JF, 1993a. Interaction between Pucciniaxanthii and facultative parasitic fungi on Xanthium occidentale.Biological Control 3: 288e295.
Morin L, Auld BA, Brown JF, 1993b. Synergy between Pucciniaxanthii and Colletotrichum orbiculare on Xanthium occidentale.Biological Control 3: 296e310.
Okane I, Nakagiri A, Ito T, 1998. Endophytic fungi in leaves ofericaceous plants. Canadian Journal of Botany 76: 657e663.
Petrini O, 1991. Fungal endophytes of tree leaves. In: Andrews JH,Hirano SS (eds), Microbial Ecology of Leaves. Springer, New York,pp. 179e197.
Petrini O, Stone J, Carroll FE, 1982. Endophytic fungi in evergreenshrubs in western Oregon: a preliminary study. CanadianJournal of Botany 60: 789e796.
Photita W, Lumyong S, Lumyong P, Hyde KD, 2001. Endophyticfungi of wild banana (Musa acuminata) at Doi Suthep PuiNational Park, in Thailand. Mycological Research 105:1508e1513.
Photita W, Taylor PWJ, Ford R, Hyde KD, Lumyong S, 2005. Morpho-logical andmolecular characterization of Colletotrichum speciesfromherbaceous plants in Thailand. Fungal Diversity 18: 117e133.
Redman RS, Dunigan DD, Rodriguez RJ, 2001. Fungal symbiosisfrom mutualism to parasitism: who controls the outcome,host or invader? New Phytologist 151: 705e716.
Rodrigues KF, 1994. The foliar endophytes of the Amazonian palmEuterpe oleracea. Mycologia 86: 376e385.
Rudgers JA, Koslow JM, Clay K, 2004. Endophytic fungi alter rela-tionships between diversity and ecosystem properties. EcologyLetters 7: 42e51.
Schulz B, Boyle C, 2005. The endophytic continuum. MycologicalResearch 109: 661e686.
Schulz B, Wanke U, Draeger S, Aust H-J, 1993. Endophytes fromherbaceous plants and shrubs: effectiveness of surface steril-ization methods. Mycological Research 97: 1447e1450.
Smith D, 2002. Culturing, preservation and maintenance of fungi.In: Waller JM, Lenn�e JM, Waller SJ (eds), Plant Pathologist’sPocketbook, 3rd edn. CABI Publishing, Wallingford, pp. 384e409.
Sutton B, 1980. The Coelomycetes. Commonwealth MycologicalInstitute, Kew.
Synge PM, 1956. The Royal Horticultural Society Dictionary of Gar-dening. Royal Horticultural Society, Oxford.
Watanabe H, 1991. Epidemiological studies on the canker of Jap-anese pear caused by Diaporthe medusaea Nitschke. SpecialBulletin of the Tottori Horticultural Experiment Station 1: 75e86.
Welsh Development Agency, 1998. The Eradication of JapaneseKnotweed: model tender document. Welsh Development Agency,Cardiff.
White TJ, Bruns T, Lee SB, Taylor J, 1990. Amplification and directsequencing of fungal ribosomal RNA genes for phylogenetics.In: Gelfand M, Sninsky D, White T (eds), PCR Protocols: a guide tomethods and applications. Academic Press, San Diego,pp. 315e322.