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Prunus trees in Germany—a hideout of unknown fungi?

Authors:
  • Senckenberg Museum of Natural History Görlitz, Germany

Abstract and Figures

Prunus belongs to the economically most important genera of fruit crops in Germany. Although wood pathogens possess the capability to damage the host substantially, the knowledge of the fungal pathogenic community and the mycobiome of Prunus wood in general is low. During a survey in important fruit production areas in Germany, branches with symptoms of fungal infection were sampled in Prunus avium, P. cerasus and P. domestica orchards, and 1018 fungal isolates were obtained primarily from the transition zone of symptomatic to non-symptomatic wood. By a combination of blastn searches and phylogenetic analyses based on ITS and LSU sequences with a strong focus on reliable reference data, a diversity of 172 fungal taxa belonging to Ascomycota, Basidiomycota and Mucoromycota were differentiated. The majority of the strains belonged to three classes of Ascomycota, namely Sordariomycetes, Leotiomycetes and Dothideomycetes. The dominant species were Aposphaeria corallinolutea (Dothideomycetes) and Pallidophorina paarla (Leotiomycetes) that were isolated more than a hundred times each, while all other taxa were isolated ≤ 30 times. Only part of them could be identified to species level. Because of the high plasticity of species boundaries, the identification certainty was divided into categories based on nucleotide differences to reference sequences. In total, 82 species were identified with high and 20 species with low (cf.) certainty. Moreover, about 70 species could not be assigned to a known species, which reveals Prunus wood to represent a habitat harbouring high numbers of potentially new species, even in a well-explored region like Germany.
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ORIGINAL ARTICLE
Prunus trees in Germanya hideout of unknown fungi?
Steffen Bien
1
&Ulrike Damm
1
Received: 9 March 2020 /Revised: 23 April 2020 / Accepted: 27 April 2020
#The Author(s) 2020
Abstract
Prunus belongs to the economically most important genera of fruit crops in Germany. Although wood pathogens possess the
capability to damage the host substantially, the knowledge of the fungal pathogenic community and the mycobiome of Prunus
wood in general is low. During a survey in important fruit production areas in Germany, branches with symptoms of fungal
infection were sampled in Prunus avium,P. cerasus and P. domestica orchards, and 1018 fungal isolates were obtained primarily
from the transition zone of symptomatic to non-symptomatic wood. By a combination of blastn searches and phylogenetic
analyses based on ITS and LSU sequences with a strong focus on reliable reference data, a diversity of 172 fungal taxa belonging
to Ascomycota,Basidiomycota and Mucoromycota were differentiated. The majority of the strains belonged to three classes of
Ascomycota, namely Sordariomycetes,Leotiomycetes and Dothideomycetes. The dominant species were Aposphaeria
corallinolutea (Dothideomycetes)andPallidophorina paarla (Leotiomycetes) that were isolated more than a hundred times
each, while all other taxa were isolated 30 times. Only part of them could be identified to species level. Because of the high
plasticity of species boundaries, the identification certainty was divided into categories based on nucleotide differences to
reference sequences. In total, 82 species were identified with high and 20 species with low (cf.) certainty. Moreover, about 70
species could not be assigned to a known species, which reveals Prunus wood to represent a habitat harbouring high numbers of
potentially new species, even in a well-explored region like Germany.
Keywords Cultivation .Fungal community .Stone fruit trees .Systematics .Wood inhabitants
Introduction
Fungal pathogens inhabiting the woody plant body can plug
vessels and necrotise tissue, which causes wilting, inhibition
of blossoming and dieback of branches and whole trees. The
resulting decrease in fruit or timber yield can ruin the produc-
tivity of orchards, vineyards and forests and can even require
replanting. Additionally, some of the pathogens can reduce
the quality of fruits, which causes further yield losses.
Moreover, trees in forests and orchards are usually grown in
monocultures and are therefore especially threatened by fun-
gal plant pathogens, both due to the increasing global plant
trade (Roy et al. 2014, Ghelardini et al. 2017) and effects of
climate change (Anderson et al. 2004, Gange et al. 2011, Luck
et al. 2011,Fisheretal.2012, Altizer et al. 2013). An example
for the threat an exotic pathogen can pose to native trees is
Hymenoscyphus fraxineus, the causal agent of ash dieback
that moved from eastern Asia to Europe, encountering ash tree
species being more susceptible (McMullan et al. 2018). Due
to extreme conditions like drought, trees become also more
susceptible to fungi that are already living as endophytes in-
side their wood, so-called weak parasites. They include spe-
cies of Botryosphaeriales that have frequently been isolated
from Prunus trees in South Africa (Damm et al. 2007a,b). In
Germany, one of these species, Diplodia pinea, has been re-
ported to cause serious damage to pine trees that suffered from
drought stress and had been attacked by bark beetles
(Heydeck and Dahms 2012, Petercord 2017). Furthermore,
trees can become more susceptible to pathogens or encounter
new potential pathogens if they are planted outside their typ-
ical growing region, for example by the northward expansion
Section Editor: Marc Stadler
Electronic supplementary material The online version of this article
(https://doi.org/10.1007/s11557-020-01586-4) contains supplementary
material, which is available to authorized users.
*Steffen Bien
steffenbien@hotmail.com
1
Senckenberg Museum of Natural History Görlitz, PF 300 154,
02806 Görlitz, Germany
https://doi.org/10.1007/s11557-020-01586-4
(2020) 19:667690
Mycological Progress
of European crop production due to global warming
(Maracchi et al. 2005,Santosetal.2017). In order to allow
an early detection and control of known and new threats for
the fruit industry, knowledge of the wood mycobiome of fruit
trees is crucial.
Fungal communities inside wood have frequently been
studied using culture-independent high-throughput sequenc-
ing (HTS) (e.g. Kubartová et al. 2012, Hoppe et al. 2016,
Purahong et al. 2018) and isolation techniques (e.g.
Kowalski 1983, Butin and Kowalski 1986, Lygis et al.
2005, Santamaría and Diez 2005, Simeto et al. 2005,Cloete
et al. 2011,Markakisetal.2017, Fischer et al. 2016).
However, many studies focused on endophytic fungi (e.g.
Barengo et al. 2000, Fröhlich et al. 2000, Gonthier et al.
2006) or were restricted to grapevine wood (e.g. Hofstetter
et al. 2012, Pancher et al. 2012, Bruez et al. 2014,2016).
Sweet cherry (Prunus avium), sour cherry (P. cerasus)and
plum (P. domestica) are the most important stone fruit crops
in German fruit industry (Garming et al. 2018). In 2018, more
than 350,000 t of sweet cherry, sour cherry and plum fruit
were produced on an area of around 12,000 ha (FAO 2020).
In spite of this economic importance, there are only a few
studies on the fungal diversity of aboveground woody parts
of Prunus trees (e.g. Bernadovičová and Ivanová 2011,
Haddadderafshi et al. 2011, Hortová and Novotný 2011,
Gramaje et al. 2012, Abdollahi Aghdam and Fotouhifar
2016,2017). Most of these studies are limited by a small
sample size, by a narrow sampling area or by relying solely
on morphological features for species identification.
The most extensive work so far has been conducted in a
survey on the fungal diversity of Prunus species in South
Africa (Damm et al. 2007a,b,2008a,b,c,2010,Moyoetal.
2018, Bien and Damm 2020). More than 40 taxa were report-
ed, predominantly within Botryosphaeriales (nine species)
and Phaeoacremonium (14 species). During this survey, 24
species of Botryosphaeria-ceae,Calosphaeriaceae,
Togniniaceae,Montagnulaceae,Coniochaetaceae,
Celotheliaceae,Tympanidaceae and Ploettnerulaceae were
recognised as new to science. However, these publications
aimed only on selected, very abundant or specifically interest-
ing taxa of wood-inhabiting fungi from Prunus wood in South
Africa; the complete diversity collected was not evaluated.
Moreover, no comprehensive study has been done on the
mycobiome of Prunus trees in Germany. In a study on several
tree species in the vicinity of a vineyard in Germany, only a
selection of eight fungal species (belonging to
Botryosphaeriaceae,Stereaceae,Tympanidaceae and
Valsaceae) isolated from wood of six Prunus species (includ-
ing P. cerasus and P. domestica) was reported (Gierl and
Fischer 2017).
With an extensive study such as the evaluation of a
mycobiome, time is the most limiting factor. For the selection
of an appropriate approach for identification, quantity and
quality have to be balanced against each other. Uncertainties
in identifications of fungi can arise due to deficiencies of both
morphological and molecular approaches. Morphological
identification of fungal cultures is hindered or impossible, if
strains do not develop identification-relevant features (fruiting
structures) or show phenotypic plasticity (Slepecky and
Starmer 2009), belong to a complex of cryptic species that
cannot be differentiated by morphological features (e.g.
Damm et al. 2012) or species had been described based on
one morph only, usually the sexual morph, that does not de-
velop in culture (e.g. Bien and Damm 2020). Even if morpho-
logical identification is possible, each genus requires a certain
amount of expertise (Hofstetter et al. 2019), as well as time to
obtain necessary literature and reference/type material. If
many taxa extending over the entire fungal kingdom need to
be identified in a reasonable time frame, an overall
morphology-based approach is not appropriate; identification
based on sequence data is the method of choice.
Fungal identification solely based on blastn searches
with ITS sequences is common practice (Hughes et al.
2009, Hofstetter et al. 2019); however, it has a lot of
shortcomings as well. Although the ITS region is consid-
ered as the universal barcode region for fungi and the
most commonly sequenced locus in mycology, it is not
suitable for species delimitation in each genus (Schoch
et al. 2012). Species identification in surveys using HTS
is even less certain, because the sequences generated are
very short, and the high number of sequences generated
puts even more time pressure on identification, allowing
only unquestioned/unvalued blastn searches. Moreover,
identification results cannot be verified by morphology
as no cultures are available. Therefore, species can often
only be identified up to genus level (LoBuglio and Pfister
2010, Johnston et al. 2014, Ekanayaka et al. 2017,Pärtel
et al. 2017, Purahong et al. 2018) or result in doubtful
identifications like those of Collophorina species that
are discussed in Bien et al. (2020).
The purpose of this study was to reveal the mycobiome
of Prunus trees in a temperate climate focusing on poten-
tial pathogens associated with wood necroses of P. avium,
P. cerasus and P. domestica in three important fruit pro-
duction areas in Germany. Some of the genera isolated
within this study, belonging to the Leotiomycetes and
Eurotiomycetes, have previously been analysed in depth
and several new taxa were revealed (Bien et al. 2020,
Bien and Damm 2020). The aim of this study was to give
an overview of the complete fungal diversity based on
LSU and ITS sequences, to highlight the possible depth
of identification based on these loci as part of a
mycobiome study and to detect potential new taxa. A
culture-dependent approach allowed verifying results by
morphology, if necessary, and facilitates further taxonom-
ic studies.
Mycol Progress (2020) 19:667690
668
Materials and methods
Sampling and fungal isolation
Branches with wood symptoms (e.g. canker, necroses,
wood streaking, gummosis) were collected from Prunus
domestica (61 branches), P. cerasus (64) and P. avium
(43) orchards in Saxony; from P. domestica (30) and
P. avium (60) orchards in Lower Saxony; and from
P. domestica (38) and P. avium (48) orchards in Baden-
Württemberg, Germany, in 2015 and 2016. Additionally,
a symptomatic wood sample from a P. cerasus tree locat-
ed in a private garden in Bavaria was included. From each
of these 345 branches, ten wood pieces (5 × 5 × 5 mm)
from the transition zone of symptomatic to non-
symptomatic wood tissue as well as each three pieces of
the same size from non-symptomatic wood of the same
branch were surface sterilised 30 s in 70% ethanol, 1 min
in 3.5% NaOCl and 30 s in 70% ethanol and washed for
1 min in sterilised water. Five pieces from symptomatic
tissue were placed on synthetic nutrient-poor agar (SNA,
Nirenberg 1976) medium, and the remaining five pieces
from symptomatic tissue as well as the three pieces from
non-symptomatic tissue on oatmeal agar (OA; Crous et al.
2019) medium both supplemented with 100 mg/L penicil-
lin, 50 mg/L streptomycin sulphate and 1 mg/L chloram-
phenicol. After incubation for several days at 25 °C, hy-
phal tips of developing fungi were transferred to SNA
medium with a sterilised pine needle. Single-spore or
single-hyphae isolates were obtained from the fungi for
further study.
The resulting strains are preserved in cryotubes contain-
ing sterile distilled water with 10% glycerol at 80 °C and
in sterile distilled water at + 4 °C in the culture collection of
the Senckenberg Museum of Natural History Görlitz,
Germany (GLMC). Specimens (dried cultures) were depos-
ited in the fungarium of the Senckenberg Museum of
Natural History Görlitz (GLM).
Phylogenetic analysis
Genomic DNA of the isolates was extracted using the meth-
od of Damm et al. (2008b). A partial sequence of the 28S
nrDNA (LSU) and the 5.8S nuclear ribosomal gene with the
two flanking internal transcribed spacers ITS-1 and ITS-2
(ITS) were amplified and sequenced using the primer pairs
LROR (Rehner and Samuels 1994) + LR5 (Vilgalys and
Hester 1990) and ITS-1F (Gardes and Bruns 1993)+ITS-
4(Whiteetal.1990), respectively.
ThePCRmixturecontained1μL of 1:10 DNA template,
2.5 μL 10X buffer (Peqlab, Erlangen, Germany), 1 μLof
each primer (10 mM), 2.5 μLMgCl
2
(25 mM), 0.1 μLTaq
polymerase (0.5 U, Peqlab, Erlangen, Germany) and 2.5 μL
of 2 mM dNTPs. Each reaction was made up to a final
volume of 20 μL with sterile water. DNA amplifications
were carried out in a Mastercycler® pro S (Eppendorf,
Hamburg, Germany). Conditions for the amplification of
LSU and ITS were set according to Paulin and Harrington
(2000) and Bien et al. (2020), respectively. The PCR prod-
ucts were visualised on a 1% agarose gel and sequenced by
the Senckenberg Biodiversity and Climate Research Centre
(BiK-F) laboratory (Frankfurt, Germany). The forward and
reverse sequences were assembled by using BioEdit
Sequence Alignment Editor (v. 7.2.5; Hall 1999).
All strains were grouped based on comparison of their
ITS sequences. One strain of each group with an identical
ITS sequence was selected for blastn searches and phylo-
genetic analysis. For generic determination of the isolates
and selection of reference strains, blastn searches were per-
formed on the NCBI GenBank (www.ncbi.nlm.nih.gov)
and EPPO-Q-Bank (qbank.eppo.int) databases. For each
genus, sequences of strains identified to species level,
preferably of ex-type strains and strains of the type species,
with at least 97% identity were included as reference strains
in the phylogenetic analyses. If no type strains were avail-
able, strains with a CBS (culture collection of the
Westerdijk Fungal Biodiversity Institute, Utrecht, the
Netherlands) number were favoured. Strains without spe-
cies determination were only used, if blastn searches did not
result in any close match with a strain identified to species
level.
For the phylogenetic analyses, the sequences
downloaded were added to the sequences generated in this
study and those of the appropriate outgroup sequences in
five LSU-ITS datasets depending on phylum and class.
Four datasets were assembled for species of the
Ascomycota classes Sordario-mycetes,Dothideomycetes,
Leotiomycetes and Eurotiomycetes, respectively. A fifth
dataset encompasses species of the classes
Agaricomycetes,Tremellomycetes and
Cystobasidiomycetes (Basidiomycota); Lecanoromycetes,
Pezizomycetes and Saccharomycetes (Ascomycota); as well
as the subdivision Mucoromycotina of the Mucoromycota.
The datasets of each locus were aligned automatically using
MAFFT v. 7.308 (Katoh et al. 2002, Katoh and Standley
2013), manually adjusted where necessary and subsequent-
ly concatenated using Geneious v. 10.2.2 (Kearse et al.
2012).
The phylogenetic analyses were conducted using
Bayesian inference (BI) and maximum likelihood (ML) as
described in Bien et al. (2020). The DNA sequences gener-
ated in this study were deposited in GenBank (Table 1)and
the alignments in TreeBASE (treebase.org/treebase-web/
home.html; TB2:S25316). The complete list of strains
included in the phylogenetic analyses is provided in the
supplementary material table (suppl. material tab.).
Mycol Progress (2020) 19:667690 669
Table 1 List of taxa isolated from Prunus wood in Germany with novelties and potential new reports, numbers of strains per wood tissue, host species
and sampling region, representative strains and GenBank numbers
Taxon Nov. Strains sy. n-
sy.
P.d. P.c. P.a. Sa LSa BW Ba Rep. strain GenBank no.
1
LSU ITS
Ascomycota
Dothideomycetes
Alternaria conjuncta G, a, c, d 3 3 1 1 1 1 2 GLMC 1338 MT156154 MT153704
Alternaria destruens G, P 24 24 8 7 9 13 7 4 GLMC 1234 MT156155 MT153705
Alternaria rosae G, P 1 1 1 1 GLMC 636 MT156156 MT153706
Angustimassarina cf. spp. 8 8 3 5 4 1 3 GLMC 891 MT156157 MT153707
Aposphaeria corallinolutea G, P 138 125 13 99 18 21 72 41 23 2 GLMC 1355 MT156159 MT153708
Aureobasidium pullulans d 15 15 11 2 2 10 1 4 GLMC 1460 MT156164 MT153709
Bipolaris cf. spp. 1 1 1 1 GLMC 248 MT156165 MT153710
Cladosporium cf. spp. 1 10 8 2 2 1 7 2 3 5 GLMC 1289 MT156192 MT153711
Cladosporium cf. spp. 2 2 1 1 2 2 GLMC 711 MT156193 MT153712
Coniothyrium ferrarisianum G, P 24 13 11 6 14 4 24 GLMC 380 MT156201 MT153713
Constantinomyces sp. 1 1 1 1 GLMC 1767 MT156202 MT153714
Devriesia pseudoamericana P 1 1 1 1 GLMC 819 MT156209 MT153715
Didymella macrostoma a, c, d 8 8 2 5 1 7 1 GLMC 1392 MT156215 MT153716
Diplodia mutila d 1 1 1 1 GLMC 1759 MT156216 MT153717
Diplodia seriata 1 1 1 1 GLMC 1527 MT156217 MT153718
Epicoccum cf. spp. 7 7 2 5 5 2 GLMC 369 MT156218 MT153719
Jeremyomyces cf. labinae 3 2 1 1 2 2 1 GLMC 327 MT156244 MT153720
Kalmusia cf. ebuli 4 4 3 1 4 GLMC 767 MT156245 MT153721
Kalmusia variispora G, P 4 4 4 1 3 GLMC 1347 MT156246 MT153722
Neocucurbitaria populi G, P 1 1 1 1 GLMC 348 MT156266 MT153723
Neoleptosphaeria rubefaciens G, P 1 1 1 1 GLMC 337 MT156269 MT153724
Nothophoma cf. quercina 18 17 1 7 11 11 1 6 GLMC 432 MT156271 MT153725
Paraphaeosphaeria neglecta P 2 2 1 1 GLMC 857 MT156275 MT153726
Parapyrenochaeta protearum G, P 2 1 1 1 1 1 1 GLMC 301 MT156276 MT153727
Phoma laundoniae G, a 1 1 1 1 GLMC 1459 MT156298 MT153728
Preussia persica G, P 2 2 2 1 1 GLMC 447 MT156301 MT153731
Preussia cf. spp. 1 1 1 1 GLMC 1754 MT156302 MT153732
Roussoella euonymi G, P 1 1 1 1 GLMC 1544 MT156304 MT153733
Lentitheciaceae sp. 1 1 1 1 GLMC 1563 MT156299 MT153729
Pleosporales sp. 1 1 1 1 GLMC 1316 MT156300 MT153730
Eurotiomycetes
Aspergillus chevalieri G, P 2 2 2 2 GLMC 899 MT156162 MT156109
Aspergillus glaucus G, d 1 1 1 1 GLMC 771 MT156163 MT156110
Capronia sp. 1 1 1 1 GLMC 1254 MT156189 MT156111
Exophiala sp. 3 1 2 3 3 GLMC 1670 MT156225 MT156112
Minutiella pruni-avium N 2 2 2 2 GLMC 1624 MN232925 MN232957
Minutiella sp. P 2 2 2 2 GLMC 1636 MN232927 MN232959
Penicillium angulare G, P 1 1 1 1 GLMC 1646 MT156277 MT156114
Penicillium brevicompactum G, P 6 6 6 3 3 GLMC 1661 MT156278 MT156115
Penicillium glabrum G, P 2 2 2 2 GLMC 1400 MT156279 MT156116
Penicillium cf. spp. 1 1 1 1 GLMC 1288 MT156280 MT156117
Rhinocladiella cf. quercus 3 3 2 1 2 1 GLMC 1752 MT156303 MT156118
Talaromyces sp. 2 2 2 2 GLMC 1678 MT156312 MT156119
Herpotrichiellaceae sp. 1 1 1 1 GLMC 914 MT156229 MT156113
Mycol Progress (2020) 19:667690
670
Table 1 (continued)
Taxon Nov. Strains sy. n-
sy.
P.d. P.c. P.a. Sa LSa BW Ba Rep. strain GenBank no.
1
LSU ITS
Lecanoromycetes
Lecanoromycetes sp. 2 2 1 1 1 1 GLMC 1733 MT156247 MT156137
Leotiomycetes
Arboricolonus simplex N 1 1 1 1 GLMC 459 MN232924 MN232935
Botrytis cinerea 4 1 3 4 3 1 GLMC 635 MT156168 MT156090
Cadophora luteo-olivacea P 12 12 12 1 8 3 GLMC 1264 MT156172 MN232938
Cadophora novi-eboraci P 8 8 8 7 1 GLMC 1472 MT156181 MN232947
Cadophora prunicola N 8 8 5 3 5 3 GLMC 1633 MT156183 MN232955
Cadophora ramosa N 1 1 1 1 GLMC 377 MT156187 MN232956
Collophorina africana d 21 20 1 21 7 14 GLMC 1736 MK314581 MK314542
Collophorina badensis N 10 10 10 10 GLMC 1684 MK314594 MK314546
Collophorina germanica N 2 2 2 1 1 GLMC 1445 MK314595 MK314550
Collophorina neorubra N 7 7 7 3 2 2 GLMC 929 MK314604 MK314533
Dermea cerasi A G 4 4 4 4 GLMC 1760 MT156207 MT156093
Dermea cerasi B G 1 1 1 1 GLMC 862 MT156206 MT156092
Dermea sp. 2 2 2 2 GLMC 867 MT156208 MT156094
Monilinia laxa G 4 4 4 2 2 GLMC 1290 MT156255 MT156091
Neofabraea vagabunda G, P 1 1 1 1 GLMC 718 MT156268 MT156100
Neofabraea sp. 8 8 5 3 7 1 GLMC 1284 MT156267 MT156099
Oidiodendron cf. griseum 8 7 1 6 2 8 GLMC 602 MT156272 MT156101
Oidiodendron sp. 1 1 1 1 1 GLMC 469 MT156102
Oidiodendron sp. 2 7 7 7 7 GLMC 485 MT156273 MT156103
Pallidophorina paarla a, c, d 112 110 2 17 12 83 33 64 15 GLMC 452 MK314608 MK314555
Pezicula cf. carpinea 4 4 3 1 4 GLMC 416 MT156283 MT156095
Pezicula eucrita P 2 2 2 2 GLMC 643 MT156284 MT156096
Pezicula sporulosa G, P 4 4 4 4 GLMC 1224 MT156286 MT156097
Pezicula sp. 14 14 14 5 9 GLMC 1726 MT156285 MT156098
Phialocephala piceae G, P 26 26 12 2 13 25 1 GLMC 331 MT156294 MT156105
Phialocephala sp. 1 1 1 1 1 GLMC 803 MT156295 MT156106
Phialocephala sp. 2 2 2 2 2 GLMC 385 MT156296 MT156107
Phialocephala sp. 3 6 6 5 1 6 GLMC 833 MT156297 MT156108
Proliferodiscus ingens N 1 1 1 1 GLMC 1751 MN232929 MN232961
Proliferodiscus sp. 7 7 6 1 3 3 1 GLMC 460 MN232930 MN232962
Leotiomycetes sp. 1 1 1 1 GLMC 792 MT156248 MT156104
Pezizomycetes
Trichophaeopsis bicuspis G, P 1 1 1 1 GLMC 1596 MT156319 MT156139
Saccharomycetes
Nakazawaea cf. holstii 1 1 1 1 GLMC 1309 MT156261 MT156138
Wickerhamomyces silvicola G, P 1 1 1 1 GLMC 1708 MT156324 MT156140
Sordariomycetes
Acremonium sp. 1 1 1 1 GLMC 1762 MT156152 MT153618
Akanthomyces muscarius G, P 5 5 5 5 GLMC 347 MT156153 MT153619
Anthostomella cf. pinea 2 1 1 1 1 2 GLMC 451 MT156158 MT153620
Arthrinium cf. arundinis 1 1 1 1 GLMC 230 MT156160 MT153621
Ascotricha chartarum G, P 1 1 1 GLMC 453 MT156161 MT153622
Biscogniauxia nummularia a, d 3 1 2 2 1 3 GLMC 829 MT156166 MT153623
Brunneomyces hominis G, P 1 1 1 1 GLMC 717 MT156169 MT153624
Mycol Progress (2020) 19:667690 671
Table 1 (continued)
Taxon Nov. Strains sy. n-
sy.
P.d. P.c. P.a. Sa LSa BW Ba Rep. strain GenBank no.
1
LSU ITS
Calosphaeria pulchella G, d 30 30 3 27 29 1 GLMC 1629 MT156188 MT153625
Chaetomium sp. 2 1 1 2 1 1 GLMC 946 MT156190 MT153626
Chaetosphaeria cf. spp. 1 1 1 1 GLMC 641 MT156191 MT153627
Clypeosphaeria sp. 1 1 1 1 GLMC 463 MT156194 MT153628
Colletotrichum godetiae c 8 8 8 8 GLMC 224 MT156195 MT153629
Coniochaeta cf. cipronana 1 1 1 1 GLMC 1710 MT156196 MT153633
Coniochaeta sp. 1 1 1 1 1 GLMC 355 MT156197 MT153630
Coniochaeta sp. 2 1 1 1 1 GLMC 723 MT156198 MT153632
Coniochaeta sp. 3 3 3 3 3 GLMC 487 MT156199 MT153631
Cordyceps farinosa P 2 2 2 2 GLMC 886 MT156151 MT153634
Diaporthe cf. eres 6 6 6 6 GLMC 532 MT156210 MT153637
Diaporthe cf. mahothocarpus 3 3 3 3 GLMC 260 MT156211 MT153635
Diaporthe rudis P 7 7 4 3 3 4 GLMC 1427 MT156212 MT153638
Diaporthe sp. 16 16 13 3 11 3 2 GLMC 309 MT156213 MT153636
Dichotomopilus cf. spp. 4 4 4 4 GLMC 425 MT156214 MT153639
Eutypa lata c 13 13 6 7 11 2 GLMC 427 MT156219 MT153640
Eutypa petraki var. hederae 1 1 1 1 GLMC 631 MT156220 MT153641
Eutypa petraki var. petrakii 6 6 6 2 4 GLMC 1645 MT156221 MT153642
Eutypa sp. 2 2 2 2 GLMC 1758 MT156222 MT153643
Eutypella cf. spp. 1 1 1 1 GLMC 625 MT156223 MT153644
Fusarium culmorum c 2 2 2 2 GLMC 218 MT156226 MT153645
Fusarium cf. spp. 1 10 10 4 6 6 1 3 GLMC 1465 MT156227 MT153647
Fusarium cf. spp. 2 7 7 3 4 4 3 GLMC 1293 MT156228 MT153646
Hypoxylon cf. fragiforme 5 4 1 3 2 2 1 2 GLMC 1653 MT156234 MT153653
Hypoxylon fuscum d 1 1 1 1 GLMC 1823 MT156235 MT153656
Hypoxylon howeanum a, d 5 3 2 3 2 4 1 GLMC 394 MT156236 MT153651
Hypoxylon sp. 1 15 12 3 7 8 1 2 12 GLMC 1456 MT156237 MT153652
Hypoxylon sp. 2 2 2 2 2 GLMC 1657 MT156238 MT153654
Hypoxylon sp. 3 1 1 1 1 GLMC 1725 MT156239 MT153655
Jackrogersella cf. cohaerens 7 6 1 3 1 3 3 4 GLMC 652 MT156240 MT153657
Jackrogersella sp. 1 1 1 1 GLMC 1516 MT156241 MT153658
Jattaea sp. 1 1 1 1 1 GLMC 503 MT156242 MT153659
Jattaea sp. 2 4 4 4 3 1 GLMC 853 MT156243 MT153660
Lepteutypa sp. 1 18 18 18 12 6 GLMC 1319 MT156249 MT153661
Lepteutypa sp. 2 5 5 4 1 1 4 GLMC 1557 MT156250 MT153662
Leucostoma cf. spp. 28 25 3 17 2 9 7 21 GLMC 1521 MT156251 MT153663
Lopadostoma dryophilum G, P 9 9 3 5 1 7 2 GLMC 1682 MT156254 MT153665
Lopadostoma cf. turgidum A 4 4 3 1 4 GLMC 757 MT156252 MT153664
Lopadostoma cf. turgidum B 1 1 1 1 GLMC 1768 MT156253 MT153666
Monocillium cf. tenue 10 10 8 2 10 GLMC 563 MT156256 MT153667
Nemania sp. 1 4 4 2 1 1 4 GLMC 413 MT156262 MT153668
Nemania sp. 2 1 1 1 1 GLMC 1515 MT156263 MT153669
Nemania sp. 3 4 3 1 3 1 4 GLMC 1799 MT156264 MT153670
Neocosmospora cf. perseae 1 1 1 1 GLMC 300 MT156265 MT153671
Neurospora sp. 6 5 1 1 4 1 5 1 GLMC 658 MT156270 MT153672
Ophiostoma sp. 4 4 3 1 4 GLMC 619 MT156274 MT153673
Phaeoacremonium hungaricum G, P 3 3 1 2 1 2 GLMC 1236 MT156288 MT153677
Mycol Progress (2020) 19:667690
672
Table 1 (continued)
Taxon Nov. Strains sy. n-
sy.
P.d. P.c. P.a. Sa LSa BW Ba Rep. strain GenBank no.
1
LSU ITS
Phaeoacremonium iranianum G, d 1 1 1 1 GLMC 490 MT156289 MT153674
Phaeoacremonium scolyti G 1 1 1 1 GLMC 570 MT156290 MT153676
Phaeoacremonium cf. viticola 9 9 2 7 9 GLMC 498 MT156287 MT153675
Phialemonium sp. 2 2 2 2 GLMC 576 MT156293 MT153678
Seimatosporium sp. 10 10 7 3 1 7 2 GLMC 1722 MT156305 MT153679
Simplicillium aogashimaense G, P 4 4 4 4 GLMC 349 MT156306 MT153681
Simplicillium minatense G, P 1 1 1 1 GLMC 520 MT156307 MT153680
Sporothrix variecibatus G, P 2 2 2 2 GLMC 353 MT156310 MT153683
Tolypocladium sp. 3 3 3 3 GLMC 1695 MT156313 MT153684
Trichoderma citrinoviride c 1 1 1 1 GLMC 235 MT156317 MT153685
Trichoderma cf. simmonisii 2 2 2 2 GLMC 350 MT156316 MT153686
Trichoderma cf. spp. 1 1 1 1 GLMC 512 MT156318 MT153687
Truncatella angustata P 3 3 1 2 2 1 GLMC 253 MT156320 MT153688
Xylaria longipes P 5 2 3 5 5 GLMC 1499 MT156328 MT153690
Valsaceae sp. 17 15 2 15 1 1 15 2 GLMC 412 MT156323 MT153689
Xylariaceae sp. 1 1 1 1 1 GLMC 1660 MT156325 MT153693
Xylariaceae sp. 2 1 1 1 1 GLMC 1594 MT156326 MT153692
Xylariaceae sp. 3 2 1 1 1 1 2 GLMC 848 MT156327 MT153691
Hypocreales sp. 1 2 1 1 2 2 GLMC 550 MT156231 MT153648
Hypocreales sp. 2 3 3 3 3 GLMC 686 MT156232 MT153650
Hypocreales sp. 3 2 1 1 2 2 GLMC 556 MT156233 MT153649
Sordariales sp. 1 1 1 1 GLMC 1232 MT156309 MT153682
Basidiomycota
Agaricomycetes
Bjerkandera cf. adusta 5 5 3 1 1 3 2 GLMC 431 MT156167 MT156120
Coniophora puteana G, d 1 1 1 1 GLMC 420 MT156200 MT156121
Coprinellus cf. spp. 1 1 1 1 GLMC 737 MT156203 MT156122
Coriolopsis gallica G, d 1 1 1 1 GLMC 1308 MT156204 MT156123
Exidia glandulosa c 1 1 1 1 GLMC 374 MT156224 MT156125
Heterobasidion annosum d 1 1 1 1 GLMC 1320 MT156230 MT156126
Mycoacia fuscoatra G, P 1 1 1 1 GLMC 1268 MT156260 MT156127
Peniophora cinerea a, c, d 13 13 1 11 1 12 1 GLMC 947 MT156281 MT156128
Peniophora quercina 2 2 2 2 GLMC 1640 MT156282 MT156129
Phellinus tuberculosus A d 4 4 4 3 1 GLMC 396 MT156291 MT156130
Phellinus tuberculosus B a, d 3 3 2 1 3 GLMC 1755 MT156292 MT156131
Sistotrema sp. 2 2 2 2 GLMC 1593 MT156308 MT156132
Stereum cf. spp. 3 3 3 3 GLMC 475 MT156311 MT156133
Trametes hirsuta 1 1 1 1 GLMC 467 MT156314 MT156134
Trametes versicolor 2 2 1 1 1 1 GLMC 1717 MT156315 MT156135
Cystobasidiomycetes
Cystobasidium pinicola G, P 3 3 2 1 3 GLMC 1603 MT156205 MT156124
Tremellomycetes
Udeniomyces sp. 1 1 1 1 GLMC 1365 MT156321 MT156136
Mucoromycota
Mucor circinelloides a 1 1 1 1 GLMC 1405 MT156257 MT156141
Mucor hiemalis P 1 1 1 1 GLMC 1395 MT156258 MT156142
Mucor sp. 1 1 1 1 GLMC 656 MT156259 MT156143
Mycol Progress (2020) 19:667690 673
Identification
The strains were identified to species, genus or higher level,
depending on the affinity to the available reference sequences.
These identifications were assigned to a level of identification
certainty based on an evaluation of the respective clades in the
phylogenetic trees and nucleotide differences in the respective
ITS alignments. A species was assigned to identified with high
certainty, if the strain showed 4 nucleotide differences in the
ITS sequence to a named reference sequence. Letters at the
species name indicate a sequence variation within strains that
were identified as the same species. A low certainty was indi-
cated with cf., if the ITS sequence of a strain differed in 510
nucleotides from the closest named reference sequence. The
strain was assigned to a genus, but not to a species, if the ITS
sequence differed in > 10 nucleotides from the closest named
reference sequence or matched with more than one named ref-
erence sequence and marked with sp.or cf. spp., respective-
ly. If the strain belonged to a clade, for which no named refer-
ence sequence was available or with reference sequences be-
longing to more than one genus, the name of family, order or
class was applied. Identifications of part of the taxa to genus
level were verified based on microscopic examination of mor-
phological features formed on the used standard media.
Results
In total, 1018 fungal strains were isolated from Prunus wood,
which belonged to 172 species. The numbers of species isolated
per host species were as follows: 113 species from Prunus
domestica,70fromP. avium and 61 from P. cerasus
Table 1 (continued)
Taxon Nov. Strains sy. n-
sy.
P.d. P.c. P.a. Sa LSa BW Ba Rep. strain GenBank no.
1
LSU ITS
Umbelopsis isabellina G, P 5 3 2 5 5 GLMC 521 MT156322 MT156144
# branches sampled 129 64 151 168 90 86
Nov., novelties and potential first reports during this survey; sy., from symptomatic wood tissue; n-sy., from non-symptomatic wood tissue; P.d., from
Prunus domestica;P.c., from P. cerasus;P.a., from P. avium;Sa, from Saxony; LSa, from Lower Saxony; BW, from Baden-Württemberg; Ba, from
Bavaria; N, newly described in Bien et al. 2020 or in Bien and Damm 2020;G,P,a,c,d, potential first report from Germany, Prunus,P. avium,
P. cerasus or P. domestica,respectively;rep. strain, representative strain for the taxon
1
LSU, 28S nrDNA; ITS, internal transcribed spacers and intervening 5.8S nrDNA
Saxony
(n=168)
Baden-
Württemberg
(n=86)
Lower
Saxony
(n=90)
73
13
22
34
14
610
Prunus
avium
(n=151)
66
Prunus
domestica
(n=129)
31 20
17
16
14
8
Prunus
cerasus
(n=64)
ab
Fig. 1 Number of species isolated from Prunus wood in Germany aper host species and bper sampling region. n, number of sampled branches
Mycol Progress (2020) 19:667690
674
(Fig. 1a). While 66, 31 and 20 species, respectively, were ex-
clusively isolated from one of these hosts, 17 species occurred in
all of them. Regarding the main sampling regions, 122, 75 and
43 species were isolated from Prunus wood collected in Saxony,
Baden-Württemberg and Lower Saxony, respectively. While
73, 34 and 10 species, respectively, were exclusively isolated
from wood collected from one of these regions, 13 species oc-
curred in all of them (Fig. 1b). Five species were isolated from
all three Prunus species and in all collection areas, namely
Alternaria destruens,Aposphaeria corallinolutea,
Aureobasidium pullulans,Pallidophorina paarla and
Cladosporium cf. spp. 1 (Table 1). Aposphaeria corallinolutea
and Pa. were isolated 138 and 112 times, respectively, all other
taxa 30 times. Most of the taxa with 1530 strains were iso-
latedfromatleasttwohostspeciesandinatleasttwocollection
regions, except for Collophorina africana and Lepteutypa sp. 1
that were collected only from P. domestica,andConiothyrium
ferrarisianum that was collected only from Saxony.
The majority of the species (166 species) was isolated from
the transition zone between symptomatic and non-symptomatic
tissue, 138 species exclusively from this tissue, while 34 spe-
cies were isolated from asymptomatic tissue, six species (each
one isolate) exclusively from asymptomatic tissue.
Of the 172 species, 152 species belonged to the
Ascomycota (965 strains), 16 to the Basidiomycota (45 strains)
and four to the Mucoromycota (eight strains). Within the
Ascomycota, 75 species belonged to the Sordariomycetes
(356 strains), 30 to the Leotiomycetes (290 strains), 30 to the
Dothideomycetes (287 strains) and 13 to the Eurotiomycetes
(27 strains), representing 43.6%, 17.4%, 17.4% and 7.6%,
respectively, of the total diversity and 35%, 28.5%, 28.2%
and 2.7%, respectively, of the abundance of the complete
mycobiome of Prunus wood isolated in this study
(Fig. 2a, b). The sequences of the four most abundant classes
of Ascomycota were analysed in separate alignments, while
the remaining classes of the Ascomycota were analysed to-
gether with Basidiomycota and Mucoromycota.
Phylogenetic analyses
The combined sequence dataset 1 of the Sordariomycetes
consisted of 246 strains including the reference strains and
the outgroup Cadophora luteo-olivacea strain CBS 141.41
(Leotiomycetes) and comprised 1884 characters (gene bound-
aries: LSU: 1902, ITS: 9031884, including gaps). The final
ML optimisation likelihood of ML analysis was lnL = -
39,461.875859. In total, 356 isolates from Prunus wood
belonged to 75 taxa (Fig. 3). Thirty-one species (136 isolates)
were placed in the order Xylariales, of which 15 taxa were
determined to species, 13 to genus and three to family level.
Six species (77 isolates) were placed in the Diaporthales;the
generic determination of one of them was unclear. Three taxa
(35 isolates) were placed in the Calosphaeriales, four (14
isolates) in the genus Phaeoacremonium,Togniniales, and
two (six isolates) in the Ophiostomatales. Seventeen species
(57 isolates) were placed in the order Hypocreales; the generic
placement of three of them was unclear. Two taxa (nine iso-
lates) were placed in the order Glomerellales and determined
to species level. Four species (13 isolates) were placed in the
order Sordariales, one of which not determined to genus level.
One isolate was placed in the genus Chaetosphaeria,
Chaetosphaeriales. Four species (six isolates) were placed in
the genus Coniochaeta,Coniochaetales; one of them was
identified to species level. One species (two isolates) was
placed in a clade formed by strains of Phialemonium sp., sister
to the single-strain clade of the ex-type strain of Ph.
dimorphosporum (incertae sedis). With 30 strains,
BM
A
a
A
B
M
BM
A
b
Sordariomycetes
Leotiomycetes
Dothideomycetes
Eurotiomycetes
Saccharomycetes
Lecanoromycetes
Pezizomycetes
Agaricomycetes
Tremellomycetes
Cystobasidiomycete
s
Mucoromycota
Fig. 2 Percentage aof taxa per class and phylum and bof strains per class and phylum isolated from Prunus wood in Germany. A, Ascomycota;B,
Basidiomycota;M,Mucoromycota
Mycol Progress (2020) 19:667690 675
Calosphaeria pulchella (Calosphaeriales) was the most fre-
quently isolated species in the Sordariomycetes.
The combined sequence dataset 2 of the Dothideomycetes
consisted of 113 strains including the outgroup Penicillium
resticulosum strain CBS 609.94 (Eurotiomycetes) and com-
prised 1585 characters (gene boundaries: LSU: 1870, ITS:
8711585, including gaps). The final ML optimisation likeli-
hood of ML analysis was lnL =- 17,660.376634. In total, 287
isolates belonged to 30 taxa (Fig. 4). Twenty-three taxa (258
isolates) were placed in the Pleosporales, of which 17 were
determined to species, four to genus and each one to family
and order level. Four taxa (14 isolates) were placed in the
Capnodiales and determined to species or genus level. One
taxon (15 isolates) of the Dothideales was identified as
Aureobasidium pullulans. Each one isolate was identified as
Diplodia mutila and D. seriata (Botryosphaeriales). With 138
strains, Aposphaeria corallinolutea (Pleosporales) was the
most frequently isolated species in the Dothideomycetes.
The combined sequence dataset 3 of the Leotiomycetes
consisted of 84 strains including the outgroup Colletotrichum
godetiae strain CBS 133.44 (Sordariomycetes)andcomprised
1557 characters (gene boundaries: LSU: 1912, ITS: 913
1557, including gaps). The final ML optimisation likelihood of
ML analysis was lnL = - 11,950.782384. In total, 290 isolates
belonged to 30 taxa (Fig. 5). Twenty-four taxa (137 isolates)
were placed in the Helotiales, of which 15 were determined to
species and nine to genus level. Five taxa (152 isolates) were
placed in Phacidiales and determined to species level. One strain
remained in an uncertain taxonomic position on order level. With
112 strains, Pallidophorina paarla (Phacidiales)wasthemost
frequently isolated species in the Leotiomycetes.
The combined sequence dataset 4 of the Eurotiomycetes
consisted of 38 strains including the outgroup Diplodia
intermedia strain CBS 124462 (Dothideomycetes)andcom-
prised 1573 characters (gene boundaries: LSU: 1908, ITS:
9091573, including gaps). The final ML optimisation likeli-
hood of ML analysis was lnL =- 9837.561743. In total, 27 iso-
lates belonged to 13 taxa (Fig. 6). Seven taxa (15 isolates) were
placed within Eurotiales, of which five were determined to spe-
cies and two to genus level. Four taxa (eight isolates) were
placed in Chaetothyriales; one was determined to species, two
to genus and one to family level. Two taxa (four isolates) were
placed in Phaeomoniellales, of which one was determined to
species and one to genus level. All species of the Eurotiomycetes
were isolated with low frequencies (6strains).
The combined sequence dataset 5 of the remaining classes
of the Ascomycota,aswellasallBasidiomycota and
Mucoromycota consisted of 105 strains including the
outgroup Entomophthora sphaerosperma strain CBS 530.75
(Entomophthoromycotina,Zoopagomycota) and comprised
2058 characters (gene boundaries: LSU: 11115, ITS:
11162058, including gaps). The final ML optimisation like-
lihood of ML analysis was lnL =- 33,834.310764. Within the
16 taxa (45 strains) of Basidiomycota, 14 taxa (41 strains)
belonged to the in Agaricomycetes, of which 11 taxa were
identified to species and three to genus level (Fig. 7). One
isolate of the Tremellomycetes and one taxon (three isolates)
of the Cystobasidiomycetes were determined to genus and
species level, respectively. With 13 strains, Peniophora
cinerea was the most frequently isolated species in the
Basidiomycota. Species of the other phyla were isolated with
low frequencies (< 10 strains). One strain of the class
Pezizomycetes (Ascomycota) was determined as
Trichophaeopsis bicuspis. One taxon of the
Lecanoromycetes (two strains) could not be further deter-
mined. Two strains of the Saccharomycetes were determined
as Nakazawaea cf. holstii and Wickerhamomyces silvicola,
respectively. Within the 8 strains of Mucoromycota,five
strains were identified as Umbelopsis isabellina, two strains
as Mucor circinelloides and M. hiemalis, respectively, while
one further Mucor strain could not be assigned to a species.
Identification certainty
In total, 102 taxa were assigned to a particular species with
high (82 taxa) or low (20 taxa) certainty. A further 57 species
were determined to genus level. Thirteen species could not be
assigned to any genus and were identified to family (six),
order (five) or class (two), level, respectively. Almost all of
the 70 taxa that were not identified to species level belonged to
the Ascomycota, with the largest number of taxa belonging to
the Sordariomycetes (39), followed by Leotiomycetes (ten),
Dothideomycetes (nine) and Eurotiomycetes (five) (Fig. 8).
Only few undetermined species belonged to Basidiomycota,
Mucoromycota and to the remaining classes of Ascomycota.
Discussion
Fungal diversity of necrotic Prunus wood in Germany
In total, 172 fungal species were detected in the wood samples
of Prunus trees studied. The diversity detected in this study far
exceeds the number of taxa usually reported from isolation
studies of woody plants. In many cases, not more than 30 taxa
were reported (e.g. Barengo et al. 2000,Gonthieretal.2006,
Hortová and Novotný 2011,Markakisetal.2017). Only in
few studies up to or more than a hundred taxa were isolated
Fig. 3 Phylogeny of dataset 1 obtained by Bayesian inference analysis of
the combined LSU and ITS sequence alignment of Sordariomycetes.
Cadophora luteo-olivacea strain CBS 141.41 is used as outgroup. BI
posterior probability support values above 0.9 (bold) and ML bootstrap
support values above 70% are shown at the nodes. The strains isolated in
this study are emphasised in bold. Numbers in parentheses indicate the
number of isolated strains per taxon. Branches that are crossed by diag-
onal lines are shortened by 50%. T, ex-type strain; #, type species
Mycol Progress (2020) 19:667690
676
Xylariales
Diaporthales
Calosphaeriales
Xylariaceae sp. 1 GLMC 1660 (1)
Rosellinia sp. SO1_T24 L1A
Rosellinia sp. SO1_T34_L4A
Fungal sp. V-I7
Xylariaceae sp. 2 GLMC 1594 (1)
Fungal sp. V-E9
Rosellinia aquila MUCL 51703 #
Rosellinia australiensis CBS 142160 T
Rosellinia mearnsii MFLU 16-1382 T
Nemania diffusa GZ AT-F006
Nemania sp. 3 GLMC 1799 (4)
Nemania diffusa FR AT-113
Nemania serpens BHI-F650a #
Nemania sp. 1 GLMC 413 (4)
Nemania serpens CBS 679.86 #
Nemania sp. 2 GLMC 1515 (1)
Xylaria longipes GLMC 1499 (5)
Xylaria longipes CBS 347.37
Xylaria hypoxylon CBS 120.16 #
Xylaria hypoxylon CBS 126417 #
Anthostomella proteae CBS 110127 T
Clypeosphaeria sp. GLMC 463 (1)
Clypeosphaeria mamillana CBS 140735 T #
Sordariomycetes sp. 11262
Sordariomycetes sp. 11280
Xylariaceae sp. 3 GLMC 848 (2)
Anthostomella pinea CBS 128205 T
Anthostomella cf. pinea GLMC 451 (2)
Barrmaelia moravica CBS 142769 T
Barrmaelia rhamnicola CBS 142772 T #
Entosordaria perfidiosa CBS 142773 T #
Entosordaria quercina CBS 142774 T
Biscogniauxia marginata MFLUCC 12.0740
Biscogniauxia repanda ATCC 62606
Biscogniauxia nummularia GLMC 829 (3)
Biscogniauxia nummularia MUCL 51395 T #
Jackrogersella cf. cohaerens GLMC 652 (7)
Jackrogersella cohaerens CBS 119126
Jackrogersella minutella CBS 336.70
Jackrogersella multiformis CBS 119016 T #
Jackrogersella sp. GLMC 1516 (1)
Annulohypoxylon truncatum CBS 140778 T #
Hypoxylon fuscum CBS 113049 T
Hypoxylon fuscum GLMC 1823 (1)
Hypoxylon rubiginosum MUCL 52887 T
Pyrenomyxa morganii CBS 118186 T
Hypoxylon sp. 1 GLMC 1456 (15)
Hypoxylon perforatum CBS 115281
Hypoxylon sp. 2 GLMC 1657 (2)
Hypoxylon sp. 3 GLMC 1725 (1)
Hypoxylon fragiforme MUCL 51264 T #
Hypoxylon cf. fragiforme GLMC 1653 (5)
Hypoxylon howeanum MUCL 47599
Hypoxylon howeanum GLMC 394 (5)
Seimatosporium cornii MFLUCC 14-0467 T
Seimatosporium sp. GLMC 1722 (10)
Seimatosporium physocarpi CBS 139968 T
Seimatosporium pistaciae CBS 138865 T
Seimatosporium rosae CBS 139823 T
Truncatella angustata CBS 144025 T #
Truncatella angustata GLMC 253 (3)
Truncatella hartigii CBS 118148
Lepteutypa sp. 1 GLMC 1319 (18)
Lepteutypa sp. 2 GLMC 1557 (5)
Lepteutypa uniseptata HKUCC 6349
Lepteutypa fuckelii CBS 140409 T
Lepteutypa sambuci CBS 131707 T
Arthrinium arundinis CBS 114316
Arthrinium arundinis CBS 124788
Arthrinium cf. arundinis GLMC 230 (1)
Arthrinium malaysianum CBS 102053 T
Arthrinium thailandicum MFLUCC 15-0202 T
Eutypa lata CBS 208.87 T #
Eutypa lata GLMC 427 (13)
Eutypa petrakii var. hederae CBS 285.87 T
Eutypa petrakii var. hederae GLMC 631 (1)
Eutypa sp. GLMC 1758 (2)
Eutypa petrakii var. petrakii CBS 244.87
Eutypa petrakii var. petrakii GLMC 1645 (6)
Xylaria cubensis CBS 116.85
Eutypella virescens CBS 205.36 T
Eutypella cf. spp. GLMC 625 (1)
Eutypa tetragona CBS 284.87
Lopadostoma cf. turgidum A GLMC 757 (4)
Lopadostoma cf. turgidum B GLMC 1768 (1)
Lopadostoma turgidum CBS 133207 T #
Lopadostoma dryophilum GLMC 1682 (9)
Lopadostoma dryophilum CBS 133213 T
Lopadostoma lechatii CBS 133694 T
Ascotricha chartarum GLMC 453 (1)
Ascotricha chartarum CBS 104.25 #
Ascotricha lusitanica CBS 462.70 T
Ascotricha pusilla CBS 132.60
Diaporthe cotoneastri CBS 439.82 T
Diaporthe eres CBS 138594 T #
Diaporthe cf. eres GLMC 532 (6)
Diaporthe celeris CBS 143349 T
Diaporthe sp. GLMC 309 (16)
Diaporthe celastrina CBS 139.27
Diaporthe rudis CBS 113201 T
Diaporthe rudis GLMC 1427 (7)
Diaporthe mahothocarpus CGMCC 3.15181 T
Diaporthe cf. mahothocarpus GLMC 260 (3)
Leucostoma persoonii CBS 129.22
Leucostoma persoonii CBS 260.34
Leucostoma cf. spp. GLMC 1521 (28)
Leucostoma cinctum CBS 254.34
Valseutypella multicollis CBS 105.89 T
Valsaceae sp. GLMC 412 (17)
Valsa sordida CBS 197.50
Valsa ambiens CBS 423.52 #
Jattaea sp. 1 GLMC 503 (1)
Jattaea taediosa MR 3669 T
Jattaea discreta CBS 127681 T
Jattaea sp. 2 GLMC 853 (4)
Jattaea algeriensis STE-U 6201 #
Calosphaeria pulchella CBS 115999
Calosphaeria pulchella GLMC 1629 (30)
Calosphaeria africana CBS 120870 T
1/100
1/100
1/99
0.99/–
1/84
1/100
1/92
1/100
0.99/71
1/96
1/100
1/74
1/100
1/100
/75
1/95
1/100
1/100
0.99/78
1/100
1/100
1/92
1/100
1/100
1/100
1/100
1/100
1/100
0.99/87
1/100
1/100
1/100
1/100
1/100
0.99/86
1/100
1/100
0.91/–
1/97
1/95
0.95/81
1/100
0.98/100
1/100
1/100
1/100
1/91
1/97
0.99/72
1/75
0.97/94
1/100
1/100
1/97
1/86
1/97
1/91
1/100
1/96
1/100
1/100
0.94/–
1/74
0.98/98 1/100
1/100
1/100
1/100
1/100
1/100
1/90
0.99/84
1/99
1/99
1/100 1/100
1/100
1/100
1/100
1/99
0.95/95
1/100
1/100 1/100
1/100
0.98/–
1/100
1/100
Mycol Progress (2020) 19:667690 677
Ophiostomatales
Togniniales
Glomerellales
Hypocreales
incertae sedis
Trichoderma citrinoviride CBS 258.85 T
Phaeoacremonium cf. viticola GLMC 498 (9)
Phaeoacremonium viticola CBS 101738 T
Phaeoacremonium roseum DAOM 242365 T
Phaeoacremonium hungaricum CBS 123036 T
Phaeoacremonium hungaricum GLMC 1236 (3)
Phaeoacremonium iranianum CBS 101357 T
Phaeoacremonium iranianum GLMC 490 (1)
Phaeoacremonium angustius CBS 249.95 T
Phaeoacremonium scolyti GLMC 570 (1)
Phaeoacremonium scolyti CBS 113597 T
Phaeoacremonium parasiticum CBS 127262 #
Ophiostoma tasmaniense CBS 127212 T
Ophiostoma tsotsi CBS 122287 T
Ophiostoma sp. GLMC 619 (4)
Ophiostoma denticiliatum CBS 124498 T
Ophiostoma piliferum CBS 129.32 #
Ophiostoma piliferum CBS 138.33 #
Sporothrix variecibatus GLMC 353 (2)
Sporothrix variecibatus CMW23051 T
Sporothrix rossii CBS 116.78 T
Sporothrix schenckii CBS 359.36 T #
Cordyceps farinosa CBS 156.65
Cordyceps farinosa CBS 264.35
Cordyceps farinosa GLMC 886 (2)
Cordyceps militaris CBS 128.25 #
Cordyceps tenuipes CBS 226.60
Akanthomyces muscarius CBS 143.62 T
Akanthomyces muscarius GLMC 347 (5)
Akanthomyces attenuatus CBS 402.78
Akanthomyces aculeatus TS772 #
Simplicillium minatense GLMC 520 (1)
Simplicillium minatense JCM 18176 T
Simplicillium lanosoniveum CBS 123.42 T #
Simplicillium aogashimaense JCM 18167 T
Simplicillium aogashimaense GLMC 349 (4)
Hypocreales sp. 1 GLMC 550 (2)
Sarocladium implicatum MUT ITA 2365
Hypocreales sp. 2 GLMC 686 (3)
Hypocreales sp. ICMP 16980
Annulohypoxylon multiforme BHI-F464a
Hypocreales sp. 3 GLMC 556 (2)
Tolypocladium inflatum CBS 824.70 T #
Tolypocladium ovalisporum CBS 700.92 T
Tolypocladium sp. GLMC 1695 (3)
Tolypocladium album CBS 830.73
Tolypocladium album CBS 869.73 T
Fusarium reticulatum var. reticulatum CBS 190.31
Fusarium cf. spp. 1 GLMC 1465 (10)
Fusarium avenaceum CBS 128538
Fusarium sinensis CBS 122710 T
Fusarium cf. spp. 2 GLMC 1293 (7)
Fusarium culmorum CBS 128537
Fusarium culmorum GLMC 218 (2)
Neocosmospora perseae CBS 144142 T
Neocosmospora cf. perseae GLMC 300 (1)
Neocosmospora pseudensiformis CBS 125729 T
Trichoderma reesei CBS 383.78 T
Trichoderma citrinoviride GLMC 235 (1)
Trichoderma simmonsii CBS 130431 T
Trichoderma cf. simmonsii GLMC 350 (2)
Trichoderma neotropicale CBS 130633 T
Trichoderma atroviride CBS 142.95 T
Trichoderma scalesiae CBS 120069 T
Trichoderma cf. spp. GLMC 512 (1)
Trichoderma viride CBS 127113 #
Sarocladium oryzae CBS 399.73 #
Sarocladium zeae CBS 801.69 T
Sarocladium kiliense CBS 122.29 T
Sarocladium bacillisporum CBS 425.67 T
Sarocladium implicatum CBS 397.70A
Acremonium alternatum CBS 407.66 T #
Acremonium sp. GLMC 1762 (1)
Acremonium sclerotigenum CBS 124.42 T
Acremonium sordidulum CBS 385.73 T
Monocillium cf. tenue GLMC 563 (10)
Monocillium tenue CBS 432.66 T
Monocillium indicum CBS 313.61 T #
Brunneomyces hominis GLMC 717 (1)
Brunneomyces hominis CBS 139053 T
Brunneomyces europaeus CBS 652.96 T
Brunneomyces brunnescens CBS 559.73 T #
Colletotrichum godetiae GLMC 224 (8)
Colletotrichum godetiae CBS 133.44 T
Colletotrichum johnstonii CBS 128532 T
Colletotrichum pyricola CBS 128531 T
Chaetomium angustispirale CBS 137.58 T
Chaetomium coarctatum CBS 162.62 T
Chaetomium sp. GLMC 946 (2)
Chaetomium globosum CBS 160.62 T #
Dichotomopilus cf. spp. GLMC 425 (4)
Dichotomopilus funicola CBS 159.52 T
Dichotomopilus pseudofunicola CBS 142033 T
Dichotomopilus indicus CGMCC 3.14184 T #
Neurospora crassa CBS 367.70
Neurospora sitophila CBS 112.19 #
Neurospora sp. GLMC 658 (6)
Neurospora tetraspora CBS 178.33 T
Zopfiella tabulata CBS 230.78 #
Cercophora sp. CIM1_17
Sordariales sp. GLMC 1232 (1)
Uncultured Ascomycota dfmo0690_036
Zopfiella tardifaciens CBS 670.82 T
Clypeosphaeria perfidiosa CBS 407.68
Chaetosphaeria myriocarpa CBS 878.70
Chaetosphaeria pygmaea MR 1365
Chaetosphaeria cf. spp. GLMC 641 (1)
Chaetosphaeria myriocarpa CBS 141.53
Chaetosphaeria innumera MR 1175 #
Coniochaeta lignicola CBS 267.33 T
Coniochaeta luteoviridis CBS 206.38 T
Coniochaeta sp. 3 GLMC 487 (3)
Coniochaeta ligniaria CBS 424.65 #
Coniochaeta sp. 1 GLMC 355 (1)
Coniochaeta prunicola CBS 120875 T
Coniochaeta sp. 2 GLMC 723 (1)
Coniochaeta cipronana CBS 144016 T
Coniochaeta cf. cipronana GLMC 1710 (1)
Coniochaeta navarrae CBS 141016 T
Phialemonium atrogriseum CBS 604.67 T
Phialemonium obovatum CBS 279.76 T #
Phialemonium inflatum CBS 263.58
Phialemonium sp. GLMC 576 (2)
Phialemonium sp. 507-C
Phialemonium sp. Gall_27
Phialemonium dimorphosporum CBS 491.82 T
Cadophora luteo-olivacea CBS 141.41 T
0.3
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Chaetosphaeriales
Coniochaetales
Fig. 3 (continued)
Mycol Progress (2020) 19:667690
678
from wood (Lygis et al. 2005, Simeto et al. 2005, Hofstetter
et al. 2012). The high number of detected taxa in our study
presumably results from the high sample number of three
different target host species over a wider geographical area,
in contrast to most of the studies that display less diversity.
However, the isolated taxa only encompass those fungi pres-
ent at the time of sampling and accessible by isolation; a
multitude of fungi cannot be cultured in general or on standard
media (Allen et al. 2003,OBrien et al. 2005,Tsuietal.2011,
Muggia et al. 2017). Therefore, studies using culture-
independent high-throughput sequencing (HTS) techniques
usually report much higher species numbers from the fungal
diversity inside living or dead plant parts (up to 2000 opera-
tional taxonomic units, OTU) than studies using isolation
techniques (e.g. Kubartová et al. 2012, Hoppe et al. 2016,
Dissanayake et al. 2018, Jayawardena et al. 2018, Purahong
et al. 2018). As most of the taxa were isolated in this study
only once or few times, we would expect the number of taxa to
increase tremendously, if the number of wood samples would
be increased. The mycobiome of the woodof the three Prunus
species in Germany is far from being complete.
The two most abundant species, Aposphaeria
corallinolutea (Dothideomycetes,Pleosporales)and
Pallidophorina paarla (Leotiomycetes,Phacidiales), were
isolated >100 times each and from all three host species and
in all three collection areas. Aposphaeria corallinolutea was
revealed as the most dominant inhabitant of Prunus wood in
Germany in our study, while there are only five reports from
previous studies: from Fraxinus excelsior and Kerria japonica
in the Netherlands (de Gruyter et al. 2013), from decaying
wood in Thailand (Li et al. 2016), from dead branches of
Prunus padus in Russia (Tibpromma et al. 2017) and from
needles of Pseudotsuga menziesii in the USA (Daniels 2017).
The only ITS sequence of this species in GenBank originates
from the study in Thailand. Thus, A. corallinolutea is known
from several hosts, including Prunus, and from different coun-
tries, however, has not previously been reported from
Germany or from any of the Prunus species studied here.
The low number of reports could be explained by the lack of
studies on its main host plants/substrates that, based on this
study, includes necrotic wood of Prunus in Germany, but also
by the facts that A. corallinolutea was described only 2013 (de
Gruyter et al. 2013) and that the first and so far only ITS
sequence of a strain identified as this species was submitted
to GenBank only 2017 (Li et al. 2016). A blastn search with
the ITS sequence of strain GLMC 1355 revealed a 100%
match with an unidentified Ascomycota strain from leaves of
Fagus sylvatica in Germany (Unterseher and Schnittler 2009)
indicating the occurrence of this fungus on a further host as
well as in Germany. In contrast, the second most abundant
species, Pa. paarla, has previously frequently been reported
from a number of Prunus species in several countries includ-
ing Germany (Gierl and Fischer 2017,Bienetal.2020).
Part of the taxa isolated in this study probably represent
first reports for the genus Prunus, for specific Prunus species
or for Germany. We conducted a search of the 82 taxa iden-
tified to species level with high certainty on the USDA data-
base (Farr and Rossman 2019). For 41 of these taxa, no pre-
vious report from Germany and for 40 taxa, no previous report
from the host genus Prunus was listed (Table 1). Of further 25
taxa, there was no previous report from one or more of the
Prunus hosts, on which they were collected from in our study.
However, as some of the latest publications are missing, this
database is apparently not complete. Therefore, and due to the
unreliable identification results of many species, we consider
these reports as potential first reports. They need to be con-
firmed by in-depth studies of the respective species, which
was beyond the scope of this study.
The aim of this study was to reveal the mycobiome asso-
ciated with necroses of Prunus wood in Germany as complete
as possible in a reasonable time frame using a cultivation
approach. As the study was based on commercial orchards,
it was not possible to collect the exact amount of samples from
each host species with the same age, same cultivars etc. at the
same collection area. For some of the orchards, data like tree
age and cultivar were not even available. Therefore, a direct
comparison of the three collection areas and host species re-
garding strain or species numbers cannot be made as it is most
probably biased by other factors.
Comparison with other studies from Prunus
The results obtained in this study could only be compared to a
few other studies that used similar methods (culturing,
sequence-based identification). However, most of them were
conducted on different Prunus species and in different cli-
mates. The extensive survey of fungi in Prunus wood
(P. armeniaca,P. dulcis,P. persica,P. persica var.
nucipersica,P. salicina) in South Africa resulted in reports
of 47 species in several publications by Damm et al. (2007a,b,
2008a,b,c,2010), Moyo et al. (2018) and Bien and Damm
(2020) focusing on specific genera. Gramaje et al. (2012)iso-
lated nine fungal species from Prunus dulcis in Spain (Island
of Mallorca) including five species belonging to the
Botryosphaeriales as well as Collophorina hispanica,
Diaporthe amygdali,Eutypa lata and Phaeoacremonium
amygdalinum. The study of Inderbitzin et al. (2010) was re-
stricted to Botryosphaeriaceae from Prunus dulcis in CA,
USA, and that of Tian et al. (2018)toDiaporthe amygdali
and Botryosphaeria dothidea of P. persica in Yangshan,
China. The only study from Germany was that by Gierl and
Fischer (2017), who reported only eight fungal species from
symptomatic wood of six Prunus species, two of which were
also sampled by us, namely P. cerasus and P. domestica.
Botryosphaeriales are known as pathogens and endophytes
of various woody hosts (Slippers et al. 2007, Cloete et al.
Mycol Progress (2020) 19:667690 679
Pleosporales
Capnodiales
Dothideales
Botryosphaeriales
Epicoccum layuense CGMCC 3.18362 T
Epicoccum cf. spp. GLMC 369 (7)
Epicoccum nigrum CBS 173.73 T #
Epicoccum dendrobii CGMCC 3.18359 T
Nothophoma cf. quercina GLMC 432 (18)
Nothophoma quercina CBS 633.92
Nothophoma anigozanthi CBS 381.91 T
Nothophoma infossa CBS 123395 T #
Didymella macrostoma GLMC 1392 (8)
Didymella macrostoma CBS 839.84
Didymella ru micicola CBS 683.79 T
Didymella exigua CBS 183.55 T #
Didymella heteroderae CBS 630.97 T
Phoma laundoniae ICMP 10843
Phoma laundoniae GLMC 1459 (1)
Coniothyrium ferrarisianum GLMC 380 (24)
Coniothyrium ferrarisianum CBS 285.74
Sclerostagonospora cycadis CBS 123538 T
Sclerostagonospora ericae CBS 141318 T
Jeremyomyces labinae CBS 144617 T
Jeremyomyces cf. labinae GLMC 327 (3)
Alternaria conjuncta CBS 196.86 T
Alternaria conjuncta GLMC 1338 (3)
Alternaria arbusti CBS 596.93 T
Alternaria rosae CBS 121341 T
Alternaria rosae GLMC 636 (1)
Alternaria angustiovoidea CBS 195.86 T
Alternaria destruens ATCC 204363 T
Alternaria destruens GLMC 1234 (24)
Bipolaris drechsleri CBS 136207 T
Bipolaris cf. spp. GLMC 248 (1)
Bipolaris variabilis CBS 127716 T
Bipolaris maydis CBS 136.29 T #
Leptosphaeria sp. LQ122417
Leptosphaeria sp. LCC1-2
Pleosporales sp. GLMC 1316 (1)
Leptosphaeria cichorium MFLUCC 14-1063
Leptosphaeria doliolum MFLU 15-1875
Leptosphaeria slovacica CBS 389.80
Neoleptosphaeria rubefaciens GLMC 337 (1)
Neoleptosphaeria rubefaciens CBS 387.80
Neoleptosphaeria jonesii MFLUCC 16-1442 T
Coniothyrium glycines CBS 124455
Coniothyrium dolichi CBS 124140
Coniothyrium telephii CBS 188.71
Parapyrenochaeta protearum GLMC 301 (2)
Parapyrenochaeta protearum CBS 131315 T #
Parapyrenochaeta acaciae CBS 141291 T
Neocucurbitaria populi GLMC 348 (1)
Neocucurbitaria populi CBS 142393 T
Neocucurbitaria cava CBS 257.68 T
Neocucurbitaria unguis-hominis CBS 378.92 #
Kalmusia cf. ebuli GLMC 767 (4)
Kalmusia ebuli CBS 123120 T #
Paraconiothyrium fuscomaculans CBS 116.16 T
Kalmusia longispora CBS 582.83 T
Kalmusia variispora GLMC 1347 (4)
Kalmusia variispora CBS 121517 T
Paraphaeosphaeria neglecta GLMC 857 (2)
Paraphaeosphaeria neglecta CBS 124078 T
Paraphaeosphaeria michotii MFLUCC-13-0349 T #
Paraconiothyrium brasiliense CBS 100299 T
Paraconiothyrium archidendri CBS 168.77 T
Paraconiothyrium estuarinum CBS 109850 T #
Lentitheciaceae sp. GLMC 1563 (1)
Sclerostagonospora cycadis CBS 291.76
Murilentithecium clematidis MFLUCC 14-0562 T #
Murilentithecium rosae MFLUCC 15-0044 T
Preussia flanaganii CBS 112.73 T
Preussia funiculata CBS 659.74 #
Preussia cf. spp. GLMC 1754 (1)
Preussia persica CBS 117680 T
Preussia persica GLMC 447 (2)
Angustimassarina italica MFLUCC 15-0082 T
Angustimassarina lonicerae MFLUCC 15-0087 T
Angustimassarina populi MFLUCC 13-0034 T #
Angustimassarina cf. spp. GLMC 891 (8)
Aposphaeria corallinolutea CBS 131287 T
Aposphaeria corallinolutea GLMC 1355 (138)
Aposphaeria populina CBS 350.82
Roussoella euonymi GLMC 1544 (1)
Roussoella euonymi CBS 143426 T
Roussoella mukdahanensis MFLUCC 11-0201 T
Roussoella nitidula MFLUCC 11-0634 #
Constantinomyces sp. GLMC 1767 (1)
Constantinomyces patonensis CBS 117950 T
Constantinomyces oldenburgensis CBS 144642 T
Constantinomyces virgultus CBS 117930 T #
Devriesia shelburniensis (Devriesia s. str.) CBS 115876
Devriesia staurophora (Devriesia s. str.) CBS 375.81 #
Devriesia pseudoamericana GLMC 819 (1)
Devriesia pseudoamericana (Devriesia s. lat.) CBS 126270 T
Devriesia americana (Devriesia s. lat.) CBS 117726
Cladosporium acalyphae CBS 125982 T
Cladosporium needhamense CBS 143359 T
Cladosporium cf. spp. 1 GLMC 1289 (10)
Cladosporium xylophilum CBS 125997 T
Cladosporium herbarum CBS 121621 T #
Cladosporium macrocarpum CBS 121623 T
Cladosporium cf. spp. 2 GLMC 711 (2)
Cladosporium variabile CBS 121636 T
Aureobasidium pullulans GLMC 1460 (15)
Aureobasidium pullulans CBS 584.75 T #
Aureobasidium melanogenum CBS 105.22 T
Aureobasidium namibiae CBS 147.97 T
Diplodia mutila GLMC 1759 (1)
Diplodia mutila CBS 136014 T #
Diplodia neojuniperi CPC 22753 T
Diplodia seriata CBS 112555 T
Diplodia seriata GLMC 1527 (1)
Diplodia intermedia CBS 124462 T
Penicillium resticulosum CBS 609.94 T
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Mycol Progress (2020) 19:667690
680
2011). In previous studies, species of this order were reported
to be very abundant in wood of Prunus trees in South Africa,
the USA, Spain and China (Damm et al. 2007a,b, Inderbitzin
et al. 2010, Gramaje et al. 2012,Tianetal.2018). The dom-
inating species in the studies from South Africa and Spain
were D. seriata and Neofusicoccum parvum, respectively,
while only Botryosphaeria dothidea was reported in that from
China.Moreover, D. pinea, a pathogen of several Pinus spe-
cies in many countries (Farr and Rossman 2019), that also
cause serious damage to pine trees suffering from drought
stress and bark beetle attacks in Germany (Heydeck and
Dahms 2012,Petercord2017), had frequently been isolated
from P. persica in South Africa and tested positive for its
pathogenicity on this host (Damm et al. 2007a). Therefore,
host jumps from infected Pinus plantations to Prunus orchards
in close vicinity are possible. However, Botryosphaeriales
were surprisingly rare in this study. Only one strain each of
D. seriata and D. mutila was detected in wood of P. domestica
in the most southern sampling region in Germany; D. pinea
was not isolated at all. Brodde et al. (2019)documentedan
outbreak of Diplodia tip blight on Pinus sylvestris stands in
Sweden in 2016 caused by D. pinea and attributed it to the
increased summer temperatures. An influence of different cli-
matic conditions on distribution patterns of Botryosphaeriales
species has also been observed in the USA and Australia
(Taylor et al. 2005, Úrbez-Torres et al. 2006,Pittetal.
2010). However, a climatical or geographical explanation in
general can be ruled out, since species of this order have been
detected from fruit trees and grapevine in Central Europe be-
fore, even in different parts of Germany, including a report of
the same two species from P. armeniaca (Trapman et al. 2008,
Quaglia et al. 2014, Fischer et al. 2016, Gierl and Fischer
2017). Based on the results in this study, species of
Botryosphaeriaceae are currently not regarded as a threat for
German Prunus orchards.
With 14 species, Phaeoacremonium was the genus with the
highest diversity in the study on Prunus wood in South Africa
(Damm et al. 2008b), while only four Phaeoacremonium spe-
cies were isolated in Germany (this study). Three of them
were isolated in both studies, namely Pm. iranianum,Pm.
scolyti and Pm. viticola, provided the identification of the
latter, which was with low certainty (cf.), is correct.
Although the genera were found in Prunus wood in both
countries, completely different species of Coniochaeta
(Coniochaetales,Sordariomycetes), Calosphaeria,Jattaea
(Calosphaeriales,Sordariomycetes), Paraconiothyrium/
Paraphaeosphaeria (Pleosporales,Dothideomycetes)and
Phaeomoniellales (Eurotiomycetes) were collected in
Germany and in South Africa (Damm et al. 2008a,c,2010,
Bien and Damm 2020, this study). The latter order was much
more diverse and frequent in Prunus wood in South Africa; in
Germany, only two Minutiella species were collected. In con-
trast, Cadophora species were more frequently detected in
wood of different Prunus species in Germany, but only rarely
detected in South Africa; only Ca. prunicola was collected in
Prunus wood in both countries (Bien and Damm 2020).
Collophorina (syn. Collophora)andPallidophorina spe-
cies were isolated frequently in Prunus wood both in South
Africa and in Germany (Damm et al. 2010,Bienetal.2020,
this study). The dominating Collophorina species isolated
from several Prunus species in South Africa was C. rubra,a
species not reported from Germany, while the dominating one
in Germany was C. africana (syn. Collophora capensis). The
latter was originally found exclusively on wood of P. salicina
in South Africa, while in our study, it was exclusively present
on P. domestica. In the study by Damm et al. (2010), Pa.
paarla (syn. C. paarla,Collophora pallida) was mostly iso-
lated from P. salicina in South Africa, while this species was
one of the two dominating species in this survey occurring in
all Prunus species studied (Bien et al. 2020, this study). The
Collophorina species isolated from P. dulcis wood in Spain
(Gramaje et al. 2012), C. hispanica, was not found in our study.
Gierl and Fischer (2017) isolated Pa. paarla from symptomatic
wood of P. cerasus and P. persica,aswellasC. hispanica and
C. africana from P. armeniaca and P. dulcis, respectively.
Although five species of Diatrypaceae were collected in
the surveys in Germany and South Africa, Eutypa lata was the
only species found in both of them, in wood of P. cerasus and
P. domestica in Germany, as well as in P. armeniaca,
P. avium,P. dulcis and P. salicina in South Africa (Moyo
et al. 2018, this study). It was also found in wood of
P. dulcis in Mallorca (Gramaje et al. 2012). Furthermore,
Diaporthe species have been isolated in all three studies as
well. Based on preliminary studies, none of the species is
overlapping with those found in this study (Gramaje et al.
2012, U. Damm, unpubl. data). The remaining taxa cannot
be compared as no data were published from the survey in
South Africa.
Function of the fungal species inside wood
Only for part of the species/genera isolated in this study infor-
mation on lifestyle, like pathogenicity on Prunus species, is
available. In the survey on Prunus wood in South Africa,
preliminary pathogenicity tests on detached shoots revealed
the majority of tested species belonging to
Botryosphaeriaceae,Celotheliaceae,Coniochaetaceae,
Togniniaceae and Tympanidaceae to be potentially
Fig. 4 Phylogeny of dataset 2 obtained by Bayesian inferenceanalysis of
the combined LSU and ITS sequence alignment of Dothideomycetes.
Penicillium resticulosum strain CBS 609.94 is used as outgroup. BI
posterior probability support values above 0.9 (bold) and ML bootstrap
support values above 70% are shown at the nodes. The strains isolated in
this study are emphasised in bold. Numbers in parentheses indicate the
number of isolated strains per taxon. Branches that are crossed by diag-
onal lines are shortened by 50%. T, ex-type strain; #, type species
Mycol Progress (2020) 19:667690 681
pathogenic to P. persica var. nucipersica and/or P. salicina
(Damm et al. 2007a,2008b,2010). Species of all these fam-
ilies have been isolated in this study as well. However, apart
from the fact that these pathogenicity tests were preliminary
and not followed up by field tests, these results cannot be
transferred to this study, because most of the fungal species
isolated were different, and even the few species isolated in
both studies, for example Pa. paarla and C. africana,werenot
isolated from the same Prunus species. Therefore, the patho-
genicity of each fungal species isolated in this study would
need to be tested on its host species in Germany.
As we aimed at isolating pathogens causing necroses inside
Prunus wood, the majority of wood pieces we isolated from
were from the transition zone of symptomatic to non-
Helotiales
Phacidiales
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incertae sedis
Cadophora luteo-olivacea CBS 141.41 T
Cadophora luteo-olivacea GLMC 1264 (12)
Cadophora malorum CBS 165.42
Cadophora obscura CBS 269.33
Cadophora bubakii CBS 198.30
Cadophora novi-eboraci GLMC 1472 (8)
Cadophora novi-eboraci NYC14 T
Cadophora africana CBS 120890 T
Cadophora prunicola CBS 120891 T
Cadophora prunicola GLMC 1633 (8)
Cadophora fastigiata CBS 307.49 #
Cadophora melinii CBS 268.33
Cadophora ramosa GLMC 377 T (1)
Cadophora orientoamericana MYA-4972 T
Phialocephala piceae GLMC 331 (26)
Phialocephala piceae UAMH 10851 T
Phialocephala sp. 1 GLMC 803 (1)
Phialocephala compacta CBS 506.94
Phialocephala sp. 2 GLMC 385 (2)
Phialocephala catenospora DAOM C 250108 T
Phialocephala nodosa NB475 T
Phialocephala sp. 3 GLMC 833 (6)
Phialocephala dimorphospora CBS 300.62 T #
Proliferodiscus chiangraiensis MFLU 16-0588 T
Proliferodiscus sp. GLMC 460 (7)
Proliferodiscus inspersus var. magniascus KUS-F52660
Proliferodiscus ingens GLMC 1751 T (1)
Proliferodiscus tricolor CBS 122000
Pezicula eucrita GLMC 643 (2)
Pezicula eucrita CBS 662.96
Pezicula sporulosa GLMC 1224 (4)
Pezicula sporulosa CBS 224.96 T
Pezicula cf. carpinea GLMC 416 (4)
Pezicula carpinea CBS 283.39 #
Pezicula cinnamomea CBS 290.39
Pezicula sp. GLMC 1726 (14)
Pezicula sp. 3 CC-2015 CBS 268.78
Dermea cerasi A GLMC 1760 (4)
Dermea cerasi CBS 141.26 #
Dermea cerasi CBS 432.67 #
Dermea cerasi B GLMC 862 (1)
Dermea pruni CFCC 53007
Dermea sp. GLMC 867 (2)
Dermea persica MFLU 16-0259 T
Dermea pinicola CBS 142.46 T
Neofabraea sp. GLMC 1284 (8)
Neofabraea kienholzii CBS 126461 T
Neofabraea malicorticis AFTOL-ID 149 T #
Neofabraea malicorticis CBS 141.22 #
Neofabraea vagabunda GLMC 718 (1)
Neofabraea vagabunda CBS 261.32
Neofabraea vagabunda CBS 109875
Monilinia fructicola CBS 203.25 #
Monilinia fructicola CBS 329.35 #
Monilinia laxa GLMC 1290 (4)
Monilinia laxa AFTOL-ID 169
Monilinia laxa CBS 132.21
Botrytis cinerea GLMC 635 (4)
Botrytis cinerea CBS 261.71 T #
Botrytis fabae CBS 120.29 T
Botrytis porri CBS 190.26 T
Arboricolonus simplex GLMC 459 T # (1)
Oidiodendron cf. griseum GLMC 602 (8)
Oidiodendron griseum CBS 249.33
Oidiodendron sp. 1 GLMC 469 (1)
Oidiodendron griseum CBS 128807
Oidiodendron eucalypti CPC 32659 T
Oidiodendron tenuissimum CBS 238.31 T #
Oidiodendron maius CBS 126948
Oidiodendron sp. 2 GLMC 485 (7)
Collophorina africana GLMC 1736 (21)
Collophorina africana CBS 120872 T
Collophorina badensis GLMC 1684 T (10)
Collophorina germanica GLMC 1445 T (2)
Collophorina neorubra GLMC 929 T (7)
Collophorina rubra CBS 120873 T #
Pallidophorina paarla GLMC 452 (112)
Pallidophorina paarla CBS 120877 T #
Pseudeurotium bakeri CBS 878.71 T
Pseudeurotium zonatum CBS 329.36 T #
Pseudeurotium desertorum CBS 986.72 T
Leotiomycetes sp. GLMC 792 (1)
Pseudeurotium sp. 30404-E
Colletotrichum godetiae CBS 133.44 T
0.09
0.98/71
1/93
/77 1/88
1/91
1/100
Thelebolales
Fig. 5 Phylogeny of dataset 3 obtained by Bayesian inference analysis of
the combined LSU and ITS sequence alignment of Leotiomycetes.
Colletotrichum godetiae strain CBS 133.44 is used as outgroup. BI
posterior probability support values above 0.9 (bold) and ML bootstrap
support values above 70% are shown at the nodes. The strains isolated in
this study are emphasised in bold. Numbers in parentheses indicate the
number of isolated strains per taxon. Branches that are crossed by diag-
onal lines are shortened by 50%. T, ex-type strain; #, type species
Mycol Progress (2020) 19:667690
682
symptomatic wood tissue. From most of the wood samples,
we isolated several fungi. Wood diseases are caused by a
complex of fungal pathogens, which is known from grapevine
trunk diseases like esca and Botryosphaeria dieback (Larignon
and Dubos 1997, Bertsch et al. 2013). Therefore, more than
one of the isolated fungi could be responsible for the symp-
toms on the respective branch. Moreover, transitions between
different lifestyles have been shown in a high number of fungi
(Promputtha et al. 2010, Álvarez-Loayza et al. 2011, Eaton
et al. 2011,OConnell et al. 2012, Kuo et al. 2014). As an
example, many of the wood-inhabiting fungi, including
Botryosphaeriaceae, are known as weak pathogens: they do
not cause symptoms and live inside their host endophytically
and become pathogenic, if the host plant is exposed to stress,
e.g. drought (Desprez-Loustau et al. 2006,Slippersand
Wingfield 2007). However, not only the presence of one or
more pathogens decides, if a disease develops, but also the
absence of other fungi or other organisms that prevent the
disease and keep the tree healthy. Thus, in a study of
Gennaro et al. (2003), the endophytic communities on declin-
ing oaks were less diverse than those on healthy trees, and
endophyte communities of needles of Norway spruce have
been proposed as indicators of tree health (Rajala et al.
2014). It is therefore hardly possible to draw conclusions
concerning the particular role of the individual species within
the temporal-spatial succession of fungal communities associ-
ated with wood necroses of Prunus trees in Germany.
We isolated fungi both from the transition zone of symp-
tomatic to non-symptomatic tissue and from non-symptomatic
tissue of the same branch providing that the sole isolation of a
certain species from one of the two zones would indicate a
certain life style, e.g. the sole isolation from non-symptomatic
tissue would indicate an endophytic life style. However, the
resulting data are not directly comparable, because the number
of wood pieces of the non-symptomatic tissue of a branch with
wood symptoms studied was lower than the number of wood
pieces from the transition zone of symptomatic to non-
symptomatic wood tissue. Moreover, in some branches, little
Eurotiales
Chaetothyriales
Phaeomoniellales
0.99/97
1/86
1/98
1/100
1/100
1/97
0.97/75
1/93
1/100
1/79
0.99/85
1/100
1/94
1/100
1/100
1/100
1/100
1/95
1/100
1/100
1/100
1/100
1/100
Penicillium expansum CBS 325.48 T
Penicillium resticulosum CBS 609.94 T
Penicillium cf. spp. GLMC 1288 (1)
Penicillium roqueforti CBS 221.30 T
Penicillium brevicompactum GLMC 1661 (6)
Penicillium brevicompactum CBS 257.29 T
Penicillium glabrum CBS 125543 T
Penicillium glabrum GLMC 1400 (2)
Penicillium angulare GLMC 1646 (1)
Penicillium angulare NRRL 28157 T
Penicillium dierckxii CBS 304.48
Aspergillus chevalieri GLMC 899 (2)
Aspergillus chevalieri CBS 522.65 T
Aspergillus chevalieri CBS 129311
Aspergillus glaucus GLMC 771 (1)
Aspergillus glaucus CBS 297.71 #
Aspergillus leucocarpus CBS 353.68 T
Talaromyces sp. GLMC 1678 (2)
Talaromyces dendriticus CBS 660.80 T
Talaromyces aculeatus CBS 289.48 T
Talaromyces islandicus CBS 394.50
Exophiala sp. GLMC 1670 (3)
Exophiala sideris CBS 127096
Exophiala capensis CBS 128771 T
Capronia kleinmondensis CBS 122671 T
Rhinocladiella atrovirens CBS 317.33 aut #
Herpotrichiellaceae sp. GLMC 914 (1)
Capronia sp. GLMC 1254 (1)
Capronia moravica CBS 603.96
Capronia fungicola CBS 614.96 T
Capronia mansonii CBS 101.67 T
Rhinocladiella quercus CPC 26621 T
Rhinocladiella cf. quercus GLMC 1752 (3)
Minutiella sp. GLMC 1636 (2)
Minutiella sp. CBS 145008
Minutiella pruni-avium GLMC 1624 T (2)
Minutiella tardicola CBS 121757 T
Diplodia intermedia CBS 124462 T
0.2
1/100
0.97/82
1/100
Fig. 6 Phylogeny of dataset 4 obtained by Bayesian inference analysis of
the combined LSU and ITS sequence alignment of Eurotiomycetes.
Diplodia intermedia strain CBS 124462 is used as outgroup. BI
posterior probability support values above 0.9 (bold) and ML bootstrap
support values above 70% are shown at the nodes. The strains isolated in
this study are emphasised in bold. Numbers in parentheses indicate the
number of isolated strains per taxon. Branches that are crossed by diag-
onal lines are shortened by 50%. T, ex-type strain; #, type species
Mycol Progress (2020) 19:667690 683
Polyporales
Russulales
Agaricales
Boletales
Hymenochaetales
Cantharellales
Auriculariales
Tremellomycetes
Cystobasidiomycetes
Pezizomycetes
Lecanoromycetes
Saccharomycetes
Mucoromycota Ascomycota
Agaricomycetes
Basidiomycota
Trametes versicolor GLMC 1717 (2)
Trametes versicolor CBS 296.33
Trametes suaveolens CBS 279.28 #
Trametes hirsuta GLMC 467 (1)
Trametes hirsuta CBS 282.73
Coriolopsis gallica GLMC 1308 (1)
Coriolopsis gallica CBS 429.34
Coriolopsis gallica CBS 428.34
Coriolopsis trogii RLG4286sp
Mycoacia nothofagi CBS 125847
Mycoacia fuscoatra CBS 125883 #
Mycoacia fuscoatra KHL13275 #
Mycoacia fuscoatra GLMC 1268 (1)
Mycoacia uda CBS 224.56
Geotrichopsis mycoparasitica CBS 687.93 T #
Bjerkandera adusta CBS 371.52 #
Bjerkandera cf. adusta GLMC 431 (5)
Bjerkandera fumosa CBS 152.79
Peniophora cinerea CBS 261.37
Peniophora cinerea GLMC 947 (13)
Peniophora pilatiana CBS 269.56
Peniophora quercina GLMC 1640 (2)
Peniophora quercina CBS 409.50 #
Peniophora simulans CBS 875.84
Heterobasidion annosum GLMC 1320 (1)
Heterobasidion annosum CBS 567.67 #
Heterobasidion annosum CBS 169.28 #
Heterobasidion araucariae CBS 743.94 T
Stereum armeniacum CBS 944.96
Stereum hirsutum CBS 930.70 #
Stereum cf. spp. GLMC 475 (3)
Stereum ostrea CBS 361.36
Coprinellus radians SZMC-NL-3986
Coprinellus xanthothrix SZMC-NL-3417
Coprinellus cf. spp. GLMC 737 (1)
Coprinellus curtus SZMC-NL-1490
Coprinellus heptemerus SZMC-NL-2144
Coprinellus deliquescens Wat27209 #
Coniophora puteana GLMC 420 (1)
Coniophora puteana CBS 148.32 #
Coniophora arida CBS 109.40
Coniophora merulioides CBS 152.35 aut
Phellinus tuberculosus A GLMC 396 (4)
Phellinus tuberculosus CBS 383.72
Phellinus tuberculosus B GLMC 1755 (3)
Phellinus igniarius CBS 380.72 #
Phellinus laevigatus CBS 256.30
Sistotrema eximum CBS 531.91
Sistotrema octosporum CBS 126038
Sistotrema hypogaeum CBS 393.63
Sistotrema brinkmannii CBS 402.54
Sistotrema sp. GLMC 1593 (2)
Exidia glandulosa GLMC 374 (1)
Exidia glandulosa CBS 126.24 #
Exidia nigricans MW 313
Exidia thuretiana CBS 215.63
Udeniomyces sp. GLMC 1365 (1)
Udeniomyces pyricola CBS 6754 T #
Udeniomyces pseudopyricola CBS 10076 T
Udeniomyces megalosporus CBS 7236 T
Cystobasidium pinicola CBS 9130 T
Cystobasidium pinicola GLMC 1603 (3)
Cystobasidium laryngis CBS 2221 T
Cystobasidium benthicum CBS 9124 T
Trichophaeopsis bicuspis GLMC 1596 (1)
Trichophaeopsis bicuspis NSW 8316 #
Trichophaeopsis tetraspora C F-47525
Trichophaeopsis sp. DHP-AR-19
Trichophaeopsis sp. DHP-CH-58
Melastiza contorta KH 01.06
Pseudaleuria quinaultiana p712L
Chaetothiersia vernalis BAP 492 T #
Melastiza cornubiensis KH 03.43
Orbicula parietina CBS 238.32
Lecanoromycetes sp. GLMC 1733 (2)
Uncultured Ascomycota agrFF142
Uncultured Ascomycota SMOTU80
Anthopsis catenata CBS 492.81 T
Anthopsis deltoidea CBS 263.77 T #
Cyanodermella oleoligni CBS 140345 T
Umbilicaria esculenta A6
Nakazawaea ernobii CBS 1737 T
Nakazawaea holstii CBS 4140 T #
Nakazawaea cf. holstii GLMC 1309 (1)
Nakazawaea populi CBS 7351 T
Nakazawaea pomicola CBS 4242 T
Wickerhamomyces silvicola CBS 1705 T
Wickerhamomyces silvicola GLMC 1708 (1)
Candida peoriensis CBS 8800 T
Wickerhamomyces rabaulensis CBS 6797 T
Wickerhamomyces canadensis CBS 5676 #
Umbelopsis isabellina CBS 560.63
Umbelopsis isabellina GLMC 521 (5)
Umbelopsis ovata CBS 499.82 T
Umbelopsis versiformis CBS 150.81 T #
Mucor bainieri CBS 293.63 T
Mucor circinelloides f. lusitanicus CBS 108.17 T
Ellisomyces anomalus CBS 243.57 T #
Mucor sp. GLMC 656 (1)
Mucor circinelloides GLMC 1405 (1)
Mucor circinelloides f. circinelloides CBS 195.68 T
Mucor hiemalis GLMC 1395 (1)
Mucor hiemalis f. hiemalis CBS 201.65
Mucor mucedo CBS 640.67 T #
Entomophthora sphaerosperma CBS 530.75
0.8
1/98
0.97/72
1/100
1/100
1/100
1/100
1/100
1/100
1/75
1/99
1/100
0.98/–
0.94/70
0.94/72
1/92
1/97
1/91
1/100
0.95/–
1/92
1/96
0.98/– 1/100
1/100
1/99
0.94/81
1/100
0.97/–
1/100
1/93
0.99/–
1/100
1/100
0.98/– 0.95/100
1/100
0.97/96
1/100
1/85
1/100
1/100
1/100
0.96/88
1/100
1/100
1/100
/99
1/100
1/100
1/97 1/100
1/100
1/97
/100
1/99
/86
1/99
1/100
1/96
1/96
1/99
1/100
1/100
1/97
0.90/79
0.96/82
1/100
1/100 1/100
1/92
1/95
1/100
1/100
0.99/92
1/98
0.92/74
1/74
1/76
1/98
1/99
1/100
1/100
0.94/–
Mycol Progress (2020) 19:667690
684
non-symptomatic tissue was available due to the large expan-
sion of the necroses and the symptomless tissueplaced on
OA for isolation was very closely located to the necrotic tis-
sue. Biggs et al. (1983) detected hyphae of Cytospora
chrysosperma up to 2 cm away from xylem tissue of
Populus with visible necroses caused by this fungus.
Therefore, isolation of a pathogenic fungus from nearby
symptomless tissue cannot be excluded and a similar fungal
diversity and abundance was expected. However, the number
of fungi isolated from non-symptomatic tissue was exception-
ally low compared to that from the transition zone of symp-
tomatic to non-symptomatic tissue. The fungi isolated solely
from symptomless tissue were isolated only once. And none
of the few species isolated more often from symptomless than
from symptomatic tissue was found more than five times in
total. This cannot be explained by the lower subsample num-
ber of non-symptomatic wood pieces. We attribute this to the
larger number of ecological niches of the wood pieces from
the transition zone resulting in a temporal-spatial succession
of fungal communities including endophytes, pathogens and
saprobionts.
Uncertainties in identifications
Of the 172 species isolated from Prunus wood in this study, 102
could be assigned to a particular species with different levels of
certainty. The ITS region of many species is highly variable,
which decreases the similarity values and results in unjustified
uncertainty (Nilsson et al. 2008, Simon and Weiß 2008, Hughes
et al. 2009). In contrast, ITS sequences of closely related species
can be identical or nearly so, which results in similarity values of
up to 100% and therefore unjustified certainty (e.g. Houbraken
et al. 2011,Dammetal.2019). This means, on the one hand,
some of the 70 taxa not assigned to a species could possibly be
identified to species level by including the whole variability of
the ITS sequences of the respective genus. On the other hand,
some of the 102 species that were assigned to a particular species
with high or low (cf.) certainty, even of those with identical ITS
sequences, could represent new species or species with no se-
quence data in GenBank. This demonstrates how imprecise an
identification based on solely ITS data is, even by availability of
full-length sequences, careful selecting the reference data and
inclusion of the nucleotide differences/identities.
The different inter- and intraspecific variability of ITS se-
quences is a dilemma of species identification in fungal diversity
studies dealing with big and diverse sampling datasets. It is sim-
ply not possible to study the variability of each taxon and con-
sider DNA variability of each species while defining a uniform
threshold for species differentiation. On the one hand, a rigorous
application of strict criteria for species delimitation ignores the
variability of different fungal taxa. On the other hand, if no clear
criteria are applied, species delimitation is to a certain degree
subjective and the different reasons for a specific decision hard
to compare.
0
10
20
30
40
50
60
70
80
Sordariomycetes
Dothideomycetes
Leotiomycetes
Eurotiomycetes
Saccharomycetes
Lecanoromycetes
Pezizomycetes
Agaricomycetes
Cystobasidiomycetes
Tremellomycetes
Mucoromycota
genus unknown6
species unknown5
species uncertain (cf. spp.)4
species uncertain (cf.)3
species identified2
species studied1
Number of species
Ascom
y
cota Basidiomycota
Fig. 8 Number of species in
different classes of Ascomycota,
Basidiomycota and
Mucoromycota detected inside
Prunus wood in Germany and
level of certainty of identification
based on ITS/LSU sequence
comparisons.
1
Species treated in
Bien et al. 2020 or Bien and
Damm 2020,
2
ITS 04 nucleotide
differences to a named reference
sequence,
3
ITS 510 nucleotide
differences to a named reference
sequence,
4
ITS 04 nucleotide
difference to reference sequences
of 2 different species,
5
ITS > 10
nucleotide differences to a named
reference sequence,
6
no reference
sequence in the same clade
Fig. 7 Phylogeny of dataset 5 obtained by Bayesian inferenceanalysis of
the combined LSU and ITS sequence alignment of miscellaneous
Ascomycota (Lecanoromycetes,Pezizomycetes,Saccharomycetes),
Basidiomycota and Mucoromycota.Entomophthora sphaerosperma
strain CBS 530.75 is used as outgroup. BI posterior probability support
values above 0.9 (bold) and ML bootstrap support values above 70% are
shown at the nodes. The strains isolated in this study are emphasised in
bold. Numbers in parentheses indicate the number of isolated strains per
taxon. Branches that are crossed by diagonal lines are shortened by 50%.
T, ex-type strain; #, type species
Mycol Progress (2020) 19:667690 685
Moreover, blastn searches often not only result in uncertain
but more importantly in wrong identifications due to the se-
quence data in NCBI GenBank, of which many are incom-
plete, include artefacts, are mixed up or derived from wrongly
identified samples and therefore not suitable as reference data
(Vilgalys 2003, Nilsson et al. 2006, Bidartondo 2008, Hyde
et al. 2010,Koetal.2011). Therefore, only sequences of ex-
type strains can be reliable references. However, even se-
quences of ex-type strains can be unreliable, if they are based
on sequences withlow quality or mixed up with other species,
as revealed for example in Colletotrichum hymenocallidicola
(Damm et al. 2019). Nonetheless, the main drawback of iden-
tification based on sequence data (in GenBank) is the limited
part of the overall known fungal diversity with available se-
quence data, especially those from type material. It is possible
that the number of species that were not identified to species
level and regarded as new species is lower. That means, some
of these 70 potentially new species as well as some of those
with uncertainty identified species could represent species that
had previously been described based on morphology, howev-
er, lacking sequence data in GenBank.
Species identified with high certainty
In total, 82 taxa (630 strains) were identified to species level
with certainty. All species belonging to the genera
Arboricolonus,Cadophora,Collophorina,Pallidophorina
and Proliferodiscus in the Leotiomycetes and Minutiella in
the Eurotiomycetes have previously been studied in detail
morphologically as well as by multi-locus phylogenetic anal-
yses (Bien et al. 2020,BienandDamm2020). Therefore, their
identifications are reliable. Three and two species of
Cadophora and Collophorina, respectively, and one species
each of Proliferodiscus and Minutiella, as well as the genus
Arboricolonus have been described in these two previous
studies based on strains isolated from Prunus wood in
Germany collected within our survey.
Strain GLMC 380 belonging to the Dothideomycetes
shows that also strains assigned to a species with certainty
can actually be of uncertain systematic position. The sequence
of this strain (representing further 23 strains) was identical
with that of a strain referred to as Coniothyrium ferrarisianum
(CBS 285.74). Both strains form a clade sister to a clade
formed by two ex-type strains of Sclerostagonospora.Other
strains of Coniothyrium,Co. dolichi,Co. glycines and Co.
telephi, formed a distant clade also within the Pleosporales.
There is no DNA sequence of the type species Co. palmarum
available; the genus Coniothyrium is currently regarded as
polyphyletic (Verkley et al. 2004,2014). Therefore, the sys-
tematic placement of the genus Coniothyrium as well as of the
individual species, including Co. ferrarisianum, still needs to
be clarified.
Species identified with low certainty
In total, 20 taxa (98 strains) were assigned to a species with
low certainty, because the ITS sequences differed in 510
nucleotides from the closest named reference sequences.
These are taxa that need to be studied in depth; species bound-
aries need to be evaluated, etc. It is possible that part of these
taxa represent new species. Even the affiliation of some of the
taxa to genus level still needs to be clarified, for example
Anthostomella cf. pinea strain GLMC 451 (see below).
Taxa identified to genus level
In total, 57 taxa (255 strains) were assigned to a genus, but not
to a species. Of these, 16 taxa (86 strains) matched with more
than one named reference sequence (cf. spp.); these fungi are
unlikely to represent new species and can probably be identi-
fied to species level based on secondary barcodes. It is also
possible that one of the species in the respective clade repre-
sents a synonym that has previously not been revealed yet.
The ITS sequences of the other 41 taxa (169 strains) dif-
fered in > 10 nucleotides from the closest named reference
sequence. Most of these taxa represent new species, unless
the species was described only based on morphology and no
ITS sequence is available.
Species not identified to genus level
Thirteen species could not be identified to genus level (35
strains), because they did not match with named reference se-
quences in blastn searches and were placed isolated within the
phylogenies (e.g. Leotiomycetes sp. GLMC 792,
Lecanoromycetes sp. GLMC 1733) or because the respective
genus is polyphyletic and sequences of the type species are either
not available or belong to a different clade within the phylogeny.
The 13 taxa were therefore identified to family (six taxa), order
(five taxa) or class (two taxa) level only; most of them belong to
the Sordariomycetes.
Although some of the closest matches in blastn searches with
the ITS sequences of strains GLMC 1660 (Xylariaceae sp. 1) and
GLMC 1594 (Xylariaceae sp. 2) were strains previously identi-
fied as Rosellinia sp., we doubt these taxa belong to this genus,
because sequences of ex-type strains of two species and of a
strain of the type species, R. aquila (Wendt et al. 2018), belong
to different clades. Affiliation of the strains isolated in this study
to the genus Rosellinia cannot be clarified with the data at hand.
Strain GLMC 848 (Xylariaceae sp. 3) is placed together
with two strains from Juniperus deppeana in the USA referred
to as Sordariomycetes sp. (Hoffman and Arnold 2010). The
clade formed by these strains is sister to a clade formed by
strain GLMC 451 (Anthostomella cf. pinea, this study) and the
ex-type strain of Anthostomella pinea (CBS 128205).
However, the genus Anthostomella is polyphyletic
Mycol Progress (2020) 19:667690
686
(Daranagama et al. 2015), which is confirmed here as the ex-type
strain of another species, An. proteae (CBS 110127), belongs to
a different clade. None of these clades was confirmed to repre-
sent the genus Anthostomella, because there is no sequence of
the type species of the genus, An. limitata, available. Therefore,
the affinity of both strains, GLMC 848 and GLMC 451, to
Anthostomella is unclear.
Strain GLMC 1232 (Sordariales sp.) groups with a
strain referred to as Cercophora sp. (CIM1_17,
Mapperson and Dearnaley, unpubl. data), an uncultured
Ascomycota (dfmo0690_036) from soil in the USA
(OBrien et al. 2005) and the ex-type strain of Zopfiella
tardifaciens (CBS 670.82). A strain of the type species of
Zopfiella,Z. tabulata (CBS 230.78), is placed in a single-
strain clade sister to this group. The intergeneric relation-
ships of Lasiosphaeriaceae genera including Zopfiella
and Cercophora were described as inconclusive due to
the uncertainty about the phylogenetic value of different
morphological characters (Cai et al. 2005).
Strain GLMC 1316 (Pleosporales sp.) clustered with two
strains referred to as Leptosphaeria sp. (LCC1-2, Li et al.
unpubl.; LQ122417, Qiong et al., unpubl. data) that are distant
from a clade formed by strains of three further Leptosphaeria
species, none of which are ex-type strains. The affiliation of the
isolated strain to this genus is therefore doubtful.
The ITS sequence of strain GLMC 1563 (Lentitheciaceae
sp.) is identical with that of a strain previously identified as
Sclerostagonospora cycadis (CBS 291.76). Both strains form
a clade sister to a clade formed by two ex-type strains of
Murilentithecium species, including the type species of the
genus. As the ex-type strain of S. cycadis (CBS 123538) be-
longs to a different clade within the Pleosporales, sister to the
ex-type strain of S. ericae, strain CBS 291.76 must have been
wrongly identified. Both strains are likely to be a
Murilentithecium species, which needs to be confirmed.
Strain GLMC 792 (Leotiomycetes sp.), belonging to the
Leotiomycetes, grouped with strain 30404-E that had been iso-
lated from wood in Greenland and identified as Pseudeurotium
sp. (Pedersen et al., unpubl. data). However, the placement in
this genus is doubtful, because this clade is distant from the
Pseudeurotium clade formed by three ex-type strains including
the type species of the genus.
This study highlights that a common substrate like wood of
fruit trees in Germany actually represents an underexplored hab-
itat and houses a widely unknown mycobiome with widely un-
known host spectrum/specificity, distribution, conservation sta-
tus, life cycle and function and probably large potentials for
applications. We expect most of the taxa not assigned to a spe-
cies and part of the species identified with more or less certainty
to represent new species or even new genera. In order to clarify
their identity, these species should be treated in depth in further
follow-up studies by a polyphasic approach consisting of multi-
locus sequence analyses and sound morphological examinations.
Availability of data and material The DNA sequences generated in this
study were deposited in GenBank (Table 1, suppl. material tab.). The
datasets generated and analysed during the current study are available
from the TreeBASE website, http://purl.org/phylo/treebase/phylows/
study/TB2: S25316.
Authorscontributions Both authors have contributed equally. Both au-
thors read and approved the final manuscript.
Funding information Open Access funding provided by Projekt DEAL.
This study contributes to the German Barcode of Life project, funded by
the Federal Ministry of Education and Research of Germany (www.
bolgermany.de).
Compliance with ethical standards
Conflict of interest The authors declare that they have no conflicts of
interest.
Ethics approval Not applicable
Consent to participate Not applicable
Consent for publication Not applicable
Open Access This article is licensed under a Creative Commons
Attribution 4.0 International License, which permits use, sharing,
adaptation, distribution and reproduction in any medium or format, as
long as you give appropriate credit to the original author(s) and the
source, provide a link to the Creative Commons licence, and indicate if
changes were made. The images or other third party material in this article
are included in the article's Creative Commons licence, unless indicated
otherwise in a credit line to the material. If material is not included in the
article's Creative Commons licence and your intended use is not
permitted by statutory regulation or exceeds the permitted use, you will
need to obtain permission directly from the copyright holder. To view a
copy of this licence, visit http://creativecommons.org/licenses/by/4.0/.
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... nlm.nih.gov, Altschul et al. 1997) database and genus or species determination of the sequenced isolates was conducted using the method of Bien and Damm (2020). Identifications were based primarily on an evaluation of nucleotide differences in the respective ITS alignments to selected reference sequences. ...
... It can be assumed that as the sample size and number of sample plots increases, more taxa, particularly those with lower frequency, should be detected in young stands (Bien and Damm 2020). This assumption is further supported by the results of this study, which included the detection of additional five fungal taxa (Sordaria sp., X. longipes, Trichoderma sp., Jackrogersella cohaerens, Fusarium sp.) through the process of re-isolations during the pathogenicity testing. ...
... Chethana et al. 2021). In order to provide clear information about the level of certainty on the reported identifications, taxon designation based on the procedure of Bien and Damm (2020) was utilized. In twelve cases, identification was limited to genus level due to ITS concordance with more than one species and a lack of clear discriminating morphological features in the culture. ...
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The causative agent of sooty bark disease, Cryptostroma corticale , has, for some years, caused increased damage to maples ( Acer spp.) in Germany and throughout Europe. It has been stated that this pathogen can occur latently in Acer . In this study, the composition of endophytic fungi of woody stem tissues of sycamore ( Acer pseudoplatanus ) saplings were analysed in order to investigate whether C. corticale is present in young, visually healthy maple trees from natural regeneration. The most abundant taxa of the 30 isolated endophytes were Diaporthe cf. rudis and Petrakia irregularis . An association of five fungal species ( Biscogniauxia mediterranea , Coniochaeta velutina , Gibellulopsis catenata , Neocucurbitaria quercina , Tangerinosporium thalitricola ) with A. pseudoplatanus was reported for the first time. Cryptostroma corticale was not present in the juvenile sycamore stems. Furthermore, its pathogenicity was studied in comparison to other pathogens associated with A. pseudoplatanus , namely Diplodia mutila , Dothiorella sp., Nectria cinnabarina , Neonectria coccinea , Neonectria punicea and Stegonsporium pyriforme . The longest necroses were induced by C. corticale followed by N. coccinea . In a trial with a C. corticale spore suspension sprayed directly on stem bark, the fungus could be re-isolated from woody tissue, however necroses were evoked only when the bark was wounded prior to infection. The results from the experiments presented here function as additional evidence for the ability of C. corticale to establish endophytically within the host and, in particular, for the ability of the fungus to establish a successful infection/entrance through intact bark.
... Diaporthales are known to be the causal agent of branch dieback and trunk disease of Prunus s.l., often reported as endophytes, saprobes or phytopathogens. This includes the genus Diaporthe Bien & Damm, 2020;Nekrasov et al., 2022] and Cytospora Ehrenb. [Fan et al., 2020]. ...
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... Observations, especially in Great Britain, have suggested that the substrate affinity of wood decay fungi can change with time and is related to climate (Renvall 1995;Gange et al., 2011;Boddy et al., 2014;Bien and Damm 2020), but this phenomenon has not yet been linked to the degree of host specificity. Early criticism highlighted the need for systematic study (Heilmann-Clausen and Laessøe 2012); when more rigorous analyses were implemented, the results of wood decay host shifts remained, as did the more ecologically relevant questions regarding the causes, outside of climate, for host shifts (Gange et al., 2012). ...
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A field investigation of olive trees in Istria, Croatia, revealed branch dieback and cracked bark. Samples of diseased branches were collected from eight different locations and analysed. Additionally, meteorological data from two locations were analysed to determine if there was a connection between climatic changes and the appearance of pathogens in the region. Pathogenicity tests were conducted on olive seedlings. This study provides a description of Biscogniauxia and Sordaria species' morphology and elucidates their phylogeny based on the internal transcribed spacer (ITS), beta-tubulin (TUB2) and translation elongation factor 1-alpha (TEF1-α) regions. This research represents the first documented occurrence of Biscogniauxia mediterranea causing charcoal disease in olive trees in Croatia. Additionally, it is the first report of Biscogniauxia nummularia (Bull.) Kuntze and Sordaria fimicola causing diseases in olive trees anywhere in the world. Furthermore, this study marks one of the initial forays into molecular investigations of these species isolated from olive trees. Considering the potential threat posed by the inherent aggressiveness of Biscogniauxia species, further research is deemed necessary to curb the development of charcoal disease.
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Fungal trunk diseases (FTDs) have been a significant threat to the global stone fruit industry. FTDs are caused by a consortium of wood-decaying fungi. These fungi colonize woody tissues, causing cankers, dieback, and other decline-related symptoms in host plants. In this study, a detailed screening of the fungal microbiota associated with the decline of stone fruit trees in the Czech Republic was performed. The wood fragments of plum and apricot trees showing symptoms of FTDs were subjected to fungal isolation. The partial internal transcribed spacer (ITS) region, partial beta-tubulin (tub2) and translation elongation factor 1-α (tef) genes were amplified from genomic DNA extracted from fungal cultures. All isolates were classified, and the taxonomic placement of pathogenic strains was illustrated in phylogenetic trees. The most abundant pathogenic genus was Dactylonectria (31 %), followed by Biscogniauxia (13 %), Thelonectria (10 %), Eutypa (9 %), Dothiorella (7 %), Diplodia (6 %), and Diaporthe (6 %). The most frequent endophytic genus was Aposphaeria (17 %). The pathogenicity of six fungal spp. (Cadophora daguensis, Collophorina africana, Cytospora sorbicola, Dothiorella sarmentorum, Eutypa lata, and Eutypa petrakii var. petrakii to four Prunus spp. was evaluated and the Koch’s postulates were fulfilled. All tested isolates caused lesions on at least one Prunus sp. The most aggressive species was E. lata, which caused the largest lesions on all four tested Prunus spp., followed by E. petrakii var. petrakii, and D. sarmentorum. Japanese plum (Prunus salicina) and almond (P. amygdalus) were the most susceptible hosts while apricot (P. armeniaca) was the least susceptible host in the pathogenicity trial.
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Prunus serotina is an important invasive plant species in Poland. It was introduced to European forests, even in places currently protected by law, such as national parks. One major factor contributing to the spread of this species is the lack of infecting pathogens and incomplete knowledge about the relationship between the plant and microorganisms. This study aimed to identify fungal communities collected from freshly cut stumps of live and dead black cherry tree specimens growing in a protected forest. The main working hypotheses were as follows: (i) fungal communities inhabiting the wood of dead and living trees will differ in diversity and the number of taxa; and (ii) saprotrophic fungi will dominate in the wood of dead tree stumps. This study applied Illumina sequencing based on the amplification of the fungal ribosomal ITSI region. The average number of sequences (OTU) obtained from the analysis of dead tree wood was 101,758, while that of living trees was 94,150. These sequences belonged to 312 taxa, among which 254 were isolated from the wood of dead trees and 171 from that of living trees. Among the saprotrophs on dead trees, the following species were identified: Stereum rugosum, Ganoderma adspersum, G. applanatum, Peniophora cinerea, and Ascocoryne cylichnium. On the other hand, in the wood of living trees, Cytospora leucostoma and Botrytis cinerea were the most abundant saprotrophic species. The fungal communities inhabiting the wood of dead and living trees differed in the diversity and abundance of taxa, thus confirming our hypothesis. The results of our research conducted in a protected area indicate that black cherry wood can be naturally colonized by many pathogen species that can further limit its expansion.
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In recent decades the vitality and physical stability of European ash trees in Germany have been reduced by European ash dieback, especially when associated with stem collar necroses and rots. This study was carried out to investigate the composition of the fungal communities associated with stem collar necroses. Filamentous fungi were isolated from 58 ash trees out of nine forest stands in northern, eastern, and central Germany. Obtained isolates were identified to a genus or species level by means of morphological and molecular analyses. In total 162 morphotypes including endophytic, saprotrophic, and pathogenic fungi were isolated. For 33 species found no prior reports from Fraxinus excelsior were recognised, including Cryptostroma corticale and Diplodia sapinea . None of the identified species were found at all studied sites, though Diplodia fraxini was the most common fungus with regard to frequency within all isolates , occurring at seven sample sites. This species is followed by Hymenoscyphus fraxineus , Armillaria spp., Neonectria punicea , Diaporthe cf. eres , Fusarium cf. lateritium , and Paracucurbitaria sp. in order of frequency within all isolates. The aforementioned species are characterised and analysed in respect to their occurrence in stem collar necroses and at sample sites. The influence of site conditions on the fungal composition was described for five intensively sampled sites with a minimum of five studied trees (Schwansee, Rhüden, Berggießhübel, Satrup, and Schlangen). The sampling site of Schlangen was further subdivided into four subplots with different positions in the terrain. In the remaining four extensive sample sites, either one or two trees, respectively, were sampled and analysed (Oranienbaumer Heide, Woltershausen, Wolfenbüttel, and Neuhege). Over all sample sites, fungal communities of symptomatic stem tissue are similar concerning the most frequent fungi, but vary greatly according to singularly isolated fungi.
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In recent decades the vitality and physical stability of European ash trees in Germany have been reduced by European ash dieback, especially when associated with stem collar necroses and rots. This study was carried out to investigate the composition of the fungal communities associated with stem collar necroses. Filamentous fungi were isolated from 58 ash trees out of nine forest stands in northern, eastern, and central Germany. Obtained isolates were identified to a genus or species level by means of morphological and molecular analyses. In total 162 morphotypes including endophytic, saprotrophic and pathogenic fungi were isolated. For 33 species found no prior reports from Fraxinus excelsior were recognised, including Cryptostroma corticale and Diplodia sapinea . None of the identified species were found at all studied sites, though Diplodia fraxini was the most common fungi with regard to frequency within all isolates, occurring at seven sample sites. This species is followed by Hymenoscyphus fraxineus , Armillaria spp., Neonectria punicea , Diaporthe cf. eres , Fusarium cf. lateritium , and Paracucurbitaria sp. in order of frequency within all isolates. The aforementioned species are characterised and analysed in respect to their occurrence in stem collar necroses and at sample sites. The influence of site conditions on the fungal composition was described for five intensively sampled sites with a minimum of five studied trees (Schwansee, Rhüden, Berggießhübel, Satrup, and Schlangen). The sampling site of Schlangen was further subdivided into four subplots with different positions in the terrain. In the remaining four extensive sample sites either one or two trees, respectively, were sampled and analysed (Oranienbaumer Heide, Woltershausen, Wolfenbüttel, and Neuhege). Over all sample sites fungal communities of symptomatic stem tissue are similar concerning the most frequent fungi, but vary greatly according to singularly isolated fungi.
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During a survey on fungi associated with wood necroses of Prunus trees in Germany, strains belonging to the Leotiomycetes and Eurotiomycetes were detected by preliminary analyses of ITS sequences. Multi-locus phylogenetic analyses (LSU, ITS, TUB, EF-1α, depending on genus) of 31 of the 45 strains from Prunus and reference strains revealed several new taxa, including Arboricolonus gen. nov., a new genus in the Helotiales (Leotiomycetes) with a collophorina-like asexual morph. Seven Cadophora species (Heloti-ales, Leotiomycetes) were treated. The 29 strains from Prunus belonged to five species, of which C. luteo-olivacea and C. novi-eboraci were dominating; C. africana sp. nov., C. prunicola sp. nov. and C. ramosa sp. nov. were revealed as new species. The genus Cadophora was reported from Prunus for the first time. Phialophora bubakii was combined in Cadophora and differentiated from C. obscura, which was resurrected. Asexual morphs of two Proliferodiscus species (Helotiales, Leotiomycetes) were described, including one new species, Pr. ingens sp. nov. Two Minutiella species (Phaeomoniellales, Eurotiomycetes) were detected, including the new species M. pruni-avium sp. nov. Prunus avium and P. domestica are reported as host plants of Minutiella.
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Strains with a yeast-like appearance were frequently collected in two surveys on the biodiversity of fungi in Germany, either associated with necroses in wood of Prunus trees in orchards in Saxony, Lower Saxony and Baden-Württemberg or captured in spore traps mounted on grapevine shoots in a vineyard in Rhineland-Palatinate. The morphology of the strains was reminiscent of the genus Collophorina : all strains produced aseptate conidia on integrated conidiogenous cells directly on hyphae, on discrete phialides, adelophialides and by microcyclic conidiation, while in some strains additionally endoconidia or conidia in conidiomata were observed. Blastn searches with the ITS region placed the strains in the Leotiomycetes close to Collophorina spp. Analyses based on morphological and multi-locus sequence data (LSU, ITS, EF-1α , GAPDH ) revealed that the 152 isolates from wood of Prunus spp. belong to five species including C. paarla , C. africana and three new species. A further ten isolates from spore traps belonged to seven new species, of which one was isolated from Prunus wood as well. However, a comparison with both LSU and ITS sequence data of these collophorina-like species with reference sequences from further Leotiomycetes revealed the genus Collophorina to be polyphyletic and the strains to pertain to several genera within the Phacidiales . Collophorina paarla and C. euphorbiae are transferred to the newly erected genera Pallidophorina and Ramoconidiophora , respectively. The new genera Capturomyces , Variabilispora and Vexillomyces are erected to accommodate five new species isolated from spore traps. In total nine species were recognised as new to science and described as Collophorina badensis , C. germanica , C. neorubra , Capturomyces funiculosus , Ca. luteus , Tympanis inflata , Variabilispora flava , Vexillomyces palatinus and V. verruculosus .
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Using the basic GenBank local alignment search tool program (BLAST) to identify fungi collected in a recently protected beech forest at Montricher (Switzerland), the number of ITS sequences associated to the wrong taxon name appears to be around 30%, even higher than previously estimated. Such results rely on the in-depth re-examination of BLAST results for the most interesting species that were collected, viz. first records for Switzerland, rare or patrimonial species and problematic species (when BLAST top scores were equally high for different species), all belonging to Agaricomycotina. This paper dissects for the first time a number of sequence-based identifications, thereby showing in every detail-particularly to the user community of taxonomic information-why sequence-based identification in the context of a fungal inventory can easily go wrong. Our first conclusion is that in-depth examination of BLAST results is too time consuming to be considered as a routine approach for future inventories: we spent two months on verification of approx. 20 identifications. Apart from the fact that poor taxon coverage in public depositories remains the principal impediment for successful species identification, it can be deplored that even very recent fungal sequence deposits in GenBank involve an uncomfortably high number of misidentifications or errors with associated metadata. While checking the original publications associated with top score sequences for the few examples that were here reexamined , a positive consequence is that we uncovered over 80 type sequences that were not annotated as types in GenBank. Advantages and pitfalls of sequence-based identification are discussed, particularly in the light of undertaking fungal inventories. Recommendations are made to avoid or reduce some of the major problems with sequence-based identification. Nevertheless, the prospects for a more reliable sequence-based identification of fungi remain quite dim, unless authors are ready to check and update the metadata associated with previously deposited sequences in their publications.
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In Deutschland wurde im Jahr 2017 auf rund 76.000 ha in rund 11.000 Betrieben Obst angebaut. Der Obstbau ist gegliedert in den Anbau von Baumobst (49.934 ha), Strauchbeeren (6.838 ha) und Erdbeeren (18.649 ha). Der Bericht gibt einen umfassenden Überblick über die Entwicklung der Anbauflächen und Betriebsstrukturen in den Bundesländern im Zeitraum von 2005/06 bis 2016/17 sowie eine detaillierte Charakterisierung des Obstanbaus in den Bundesländern nach angebauten Obstkulturen in den Landkreisen. Darüber hinaus wird der nationale und internationale Handel mit Frischobst in diesem Working Paper beschrieben. Die Baumobstanbauflächen sind im betrachteten Zeitraum zunächst leicht zurückgegangen, um dann laut Baumobsterhebung 2017 wieder anzusteigen. Vor allem die Anbauflächen von Sauerkirschen haben deutlich abgenommen, während die Süßkirschenfläche nach einem Rückgang bis 2012 wieder leicht angestiegen ist. Die Anbauflächen von Birnen sowie Pflaumen und Zwetschen haben zwischen 2007 und 2012 abgenommen und sind seitdem auf fast gleichem Niveau stabil geblieben. Mit etwa 68 % der Baumobstfläche stehen die Äpfel an erster Stelle. Dabei ist die Apfelanbaufläche in den letzten 10 Jahren in etwa konstant geblieben. Der Strauchbeerenanbau ist im gleichen Zeitraum um rund 44 % angestiegen. Dies ist vor allem auf den Anstieg des Heidel-beeranbaus zurückzuführen, aber auch die Gesamtgröße der Anbaufläche von Sanddorn, Aroniabeeren, Stachelbeeren, Brombeeren und Holunder ist gestiegen. Die Größe der Anbaufläche von Himbeeren im Freiland ist zwar zurückgegangen, allerdings gab es starke Zuwächse im Anbau unter Glas. Etwa ein Viertel der Strauchbeerenfläche entfällt auf Betriebe mit vollständigem oder teilweisem ökologischen Anbau. Die Fläche für den Erdbeeranbau hat sich im Betrachtungszeitraum von 17.500 ha in 2006 zunächst auf rund 16.000 ha in 2009 reduziert, um dann bis 2013 auf einen Wert von rund 19.400 ha zu wachsen. Seitdem ist die Erdbeeranbaufläche besonders im Freiland rückläufig, während der geschützte Anbau stetig ansteigt. Die Betriebsstrukturen zeigen eine typische Verteilung der Betriebsgrößen zwischen den Bundesländern. In Süddeutschland sind die Obstbaubetriebe im Durchschnitt deutlich kleiner als in Nord- und Ostdeutschland. Die größten durchschnittlichen Anbauflächen je Betrieb sind in Thüringen, Sachsen und Brandenburg zu finden. Allerdings hat sich die durchschnittliche Anbaufläche von Baumobst je Betrieb in den neuen Bundesländern zwischen 2012 und 2017 verringert. Bezogen auf die Obstarten ist die durchschnittliche Anbaufläche je Betrieb für Erdbeeren mit 7,9 ha (Daten für 2016) am größten, gefolgt von den Strauchbeeren mit 6,8 ha (Daten für 2017) und dem Baumobst mit 7 ha (Daten für 2017). Dabei ist die Variation zwischen den Bundesländern enorm. Im Baumobstanbau liegt Sachsen mit durchschnittlich 58 ha je Betrieb vorn, im Strauchbeerenanbau Mecklenburg-Vorpommern mit rund 18 ha und bei den Erdbeeren Schleswig-Holstein mit rund 13 ha durchschnittlicher Anbaufläche je Betrieb. Die Verteilung der Anbauflächen nach Größenklassen zeigt, dass bei allen Obstkulturen ein großer Anteil der Anbaufläche in Betrieben mit über 10 ha liegt. Die Entwicklung der Betriebsstrukturen im Betrachtungszeitraum verdeutlicht, dass sich der Strukturwandel im Obstbau fortsetzt: Die Anzahl der Betriebe sinkt vor allem in den niedrigen Größenklassen, während die durchschnittliche Anbaufläche je Betrieb stetig ansteigt. Die Analyse der regionalen Verteilung des Obstbaus zeigt deutliche und jeweils typische Anbauschwerpunkte. Beispielhaft zu nennen sind die Bodenseeregion (v. a. der Bodenseekreis) und das Alte Land (v. a. der Landkreis Stade) mit dem Apfelanbau sowie die Rheinebene Baden-Württembergs (v. a. der Ortenaukreis) mit einem Schwerpunkt im Anbau von Süßkirschen, Pflaumen und Zwetschen. Im niedersächsischen Vechta werden mehr Erdbeeren angebaut als in jedem anderen Landkreis Deutschlands, wohingegen ganz in der Nähe, in den Landkreisen Diepholz und Nienburg, Deutschlands größtes Heidelbeeranbaugebiet liegt. Auf Großhandelsebene standen im Jahr 2014 aus deutscher Erzeugung knapp 1,5 Mio. t Frischobst zur Verfügung. Davon wurden rund 43 % über Erzeugerorganisationen vermarktet, während 17 % von meist größeren Erzeugern selbst an den Lebensmitteleinzelhandel vermarktet wurden. Etwa ein Viertel ging in die Verarbeitung. Ergänzt wird die deutsche Erzeugung auf Großhandelsebene durch Importe, die im Jahr 2014 etwa 6,3 Mio. t erreichten. Knapp zwei Drittel davon waren Südfrüchte. Demgegenüber sind die Exporte mit rund 0,7 Mio. t nur von geringer Bedeutung. Bei den Einkaufsstätten der Verbraucher für Frischobst nimmt der Lebensmitteleinzelhandel mit 83 % der Menge eine herausragende Bedeutung ein. Auch wenn der Einkauf auf Wochenmärkten und Hofläden an Bedeutung gewonnen hat, werden hier insgesamt nur 6,4 % der Frischobstmenge an die Verbraucher abgesetzt. Der Export von Obst aus Deutschland zeigt insgesamt keinen eindeutigen Trend auf. Die Apfelexportmengen schwanken stark im Betrachtungszeitraum von 2007 bis 2016, bedingt unter anderem durch die jährlichen Erntemengen, die Bedingungen auf den europäischen Märkten und auch durch den russischen Importstopp. Bei Birnen und Quitten scheinen sich die Ausfuhren leicht rückläufig zu entwickeln, während die Exporte von Heidelbeeren zwar auf einem insgesamt niedrigen Niveau liegen, aber deutlich angestiegen sind. Bei den Importen sind verschiedene Entwicklungen zu beobachten: Während die Einfuhren traditioneller Obstarten inklusive der Südfrüchte wie Bananen, Orangen, Ananas und Tafeltrauben annähernd gleich geblieben oder leicht zurück-gegangen sind, sind die Importe von Wasser- und Zuckermelonen, exotischen Früchten wie Mangos und Avocados sowie von Beerenfrüchten, insbesondere Heidelbeeren und Himbeeren, deutlich angestiegen. Eine gemeinsame Betrachtung der Veränderungen in der Obsterzeugung und im internationalen Handel zeigt eine allgemeine Entwicklungsrichtung des Obstsektors hin zu einer Diversifizierung. Der Anbau bzw. Import von Obstarten, die traditionell in großen Mengen nachgefragt werden (z. B. Äpfel, Birnen, Pflaumen und Zwetschen, Bananen und Orangen), stagniert oder ist sogar rückläufig. Parallel dazu steigt die Nachfrage nach verschiedenen Beerenfrüchten, insbesondere Heidelbeeren und Himbeeren, sowie nach exotischen Südfrüchten. Auf der Angebotsseite führen die Ausweitung des geschützten Anbaus von Erdbeeren und Himbeeren sowie eine zunehmende Überdachung von Süßkirschen zu einer höheren Qualität und einer Ausweitung der zeitlichen Verfügbarkeit dieser stark saisonalen Früchte. Den gleichen Effekt haben eine verbesserte Lager- und Transporttechnik sowie Innovationen im Bereich Verpackung für eine Verlängerung der Haltbarkeit. Dies betrifft sowohl die deutsche Erzeugung als auch die europäischen und außereuropäischen Wettbewerber, so dass die Verfügbarkeit an Obst in Deutschland insgesamt besser und vielfältiger geworden ist. JEL Codes: Q15, Q 17 Schlüsselwörter: Baumobstanbau, Strauchbeerenanbau, Erdbeeren, Strukturwandel, Obstan-baustatistik, Warenstromanalyse Frischobst, Importe und Exporte Obst
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Douglas-fir provides social, economic, and ecological benefits in the Pacific Northwest (PNW). In addition to timber, forests support abundant plant and animal biodiversity and provide socioeconomic viability for many rural communities. Products derived from Douglas-fir account for approximately 17% of the U.S. lumber output with an estimated value of $1.9 billion dollars. Employment related to wood production accounts for approximately 61,000 jobs in Oregon. Timberland also supports water resources, recreation, and wildlife habitat. Minor defoliation has previously been linked to Swiss Needle Cast, associated with the fungus Phaeocryptopus gaeumannii, however, unprecedented large-scale defoliation began in the 1990s and has increased since, leading to decreased growth and yield. Areas affected areas by SNC exceed 500,000 acres in Oregon. Defoliation symptoms are inconsistent with predicted effects of P. gaeumannii, and targeted chemical control has had mixed results. While the microbiome community of conifer needles is poorly described to date, we hypothesize the full interstitial microbiome complex is involved in disease response in conifers.
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