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Applied and Environmental Microbiology, November 2000, p. 4725-4734, Vol. 66, No. 11
0099-2240/00/$04.00+0
Copyright © 2000, American Society for Microbiology. All rights reserved.
Detection and Identification of Decay Fungi in
Spruce Wood by Restriction Fragment Length Polymorphism Analysis of
Amplified Genes Encoding rRNA
Claudia A.
Jasalavich,
Andrea
Ostrofsky, and
Jody
Jellison*
Department of Biological Sciences, University
of Maine, Orono, Maine 04469-5735
Received 6 March 2000/Accepted 12 July 2000
 |
ABSTRACT |
We have developed a DNA-based assay to reliably detect brown rot
and white rot fungi in wood at different stages of decay. DNA, isolated
by a series of CTAB (cetyltrimethylammonium bromide) and organic
extractions, was amplified by the PCR using published universal primers
and basidiomycete-specific primers derived from ribosomal DNA
sequences. We surveyed 14 species of wood-decaying basidiomycetes
(brown-rot and white-rot fungi), as well as 25 species of
wood-inhabiting ascomycetes (pathogens, endophytes, and saprophytes).
DNA was isolated from pure cultures of these fungi and also from spruce
wood blocks colonized by individual isolates of wood decay
basidiomycetes or wood-inhabiting ascomycetes. The primer pair ITS1-F
(specific for higher fungi) and ITS4 (universal primer) amplified the
internal transcribed spacer region from both ascomycetes and
basidiomycetes from both pure culture and wood, as expected. The primer
pair ITS1-F (specific for higher fungi) and ITS4-B (specific for
basidiomycetes) was shown to reliably detect the presence of wood decay
basidiomycetes in both pure culture and wood; ascomycetes were not
detected by this primer pair. We detected the presence of decay fungi
in wood by PCR before measurable weight loss had occurred to the wood.
Basidiomycetes were identified to the species level by restriction
fragment length polymorphisms of the internal transcribed spacer region.
 |
INTRODUCTION |
Wood is an important renewable and
biodegradable natural resource with a multitude of uses. Wood is used
extensively as a structural material for buildings, wharves, telephone
poles, and furniture due to its high strength per unit weight, its
versatility, and its variety. Wood also serves as the industrial raw
material for the manufacture of paper and paper products, wood
composites, and other products made from cellulose, such as textiles
and cellophane. In many parts of the world wood is used as a fuel for
heating and cooking.
The primary biotic decomposers of wood are basidiomycete decay fungi,
which can attack and degrade both wood in the forest and wood in
service. In the forest ecosystem wood decay fungi play an important
role in carbon and nitrogen cycling and help to convert organic debris
into the humus layer of the soil. Some fungi attack living trees;
others invade downed timber and slash on the forest floor, lumber, and
wood in service. Wood decay basidiomycetes colonize and degrade wood
using enzymatic and nonenzymatic processes. Brown-rot fungi
preferentially attack and rapidly depolymerize the structural
carbohydrates (cellulose and hemicellulose) in the cell wall
leaving the modified lignin behind. White-rot fungi can
progressively utilize all major cell wall components, including both the carbohydrates and the lignin. As decay progresses the wood
becomes discolored and loses strength, weight, and density. Decay and
discoloration caused by fungi are major sources of loss in both timber
production and wood use, with losses of 15 to 25% marketable wood
volume in standing timber and of 10 to 15% in wood products during
storage and conversion. Each year ca. 10% of the timber cut in the
United States is used to replace wood in service that has decayed,
resulting in the expenditure of hundreds of millions of dollars for raw
materials, labor, and liability (22).
Brown rots rapidly and drastically reduce wood strength early in the
decay process, while white rots cause a slower progressive decrease in
wood strength. Brown-rot fungi can reduce wood strength by as much as
75% at less than 5% weight loss of the wood (22). For this
reason it is important to develop methods which can detect wood decay
very early, at the incipient stage prior to the occurrence of
significant strength loss. Techniques which have been used to detect
incipient decay include isolation and culturing of fungi, chemical
staining, nuclear magnetic resonance, and electrical resistance, as
well as serological methods, such as immunoblotting and enzyme-linked
immunosorbent assay (ELISA) (3). ELISA has been found to be
a sensitive method for detecting incipient decay (4, 11),
but the assay sensitivity can be inhibited by wood extractives
(12). Optimal methods for early detection of decay for wood
in service have not been developed.
The development of the DNA-based PCR (14) and taxon-specific
primers (2, 6, 7, 16, 17) is making it increasingly feasible
to detect and study fungi in their natural substrates. A DNA-based
method to detect the presence of wood decay fungi would potentially use
only small amounts of wood, thus allowing for nondestructive sampling.
The extreme sensitivity and potential specificity of the assay would
theoretically allow for the detection of fungal decay agents at an
incipient stage enabling remedial biocidal treatments to be applied
before significant strength loss had occurred. Detection of specific
decay agents is also a necessary prerequisite to allow evaluation of
fungal colonization and proliferation in preservative-treated woods
undergoing remediation. Specific and sensitive assay procedures would
aid in the monitoring and development of successful fungus-based
bioremediation technologies.
For our DNA-based detection method, we selected the internal
transcribed spacer (ITS) region (ITSI, the 5.8S ribosomal DNA [rDNA],
and ITSII) as the target sequence for amplification for three reasons.
The ITS region is present at a very high copy number in the genome of
fungi, as part of the tandemly repeated nuclear rDNA; this, coupled
with PCR amplification, should produce a highly sensitive assay. The
DNA sequences of the ITSI and ITSII are highly variable; this feature
can be exploited to generate restriction fragment length polymorphism
(RFLP) patterns to identify wood decay fungi or to design
taxon-specific primers. The European Armillaria species
Armillaria cepistipes, A. gallica, A. borealis, A. ostoyae, and A. mellea are
clearly delimited by RFLPs of rDNA (18). RFLPs generated by
restriction digestion of the PCR-amplified ITS region have been used
successfully to study intraspecific variation in A. ostoyae
(17), to identify ectomycorrhizal fungi to the genera and/or
species level (5, 7, 8, 9, 10), and to identify
intersterility groups of Heterobasidion annosum (6). In designing an assay to detect fungi by PCR
amplification using total DNA isolated from infected plant material as
the template, it is important to be able to discriminate between DNAs
of fungal and plant origin. Primers which specifically amplify the ITS
region from only fungal DNA (7) and not plant DNA are
available. These fungus-specific primers were originally designed to
identify fungal symbionts directly from ectomycorrhizae and to identify
rusts, which are obligate parasites, in the host tissue (7).
More recently, these primers have been used to study the community structure of ectomycorrhizal fungi in a pine forest (8) and the genetic structure of a natural population of Suillus
pungens (2).
The objectives of our study were (i) to rigorously test the specificity
of the basidiomycete-specific primer (7) by surveying a
large number of wood decay basidiomycetes, as well as wood-inhabiting ascomycetes (pathogens, endophytes, and saprophytes); (ii) to optimize
the PCR assay conditions for specific detection of brown-rot and
white-rot fungi in wood; (iii) to identify the PCR-detected fungi to
species via RFLPs of the amplified internal transcribed spacer region;
and (iv) to develop a DNA-based method to detect incipient stages of
wood decay, thus allowing remedial treatments to be applied to wooden
structural members before substantial strength loss has occurred.
 |
MATERIALS AND METHODS |
Fungal culture.
The fungi used in this study and their
sources are given in Table 1. Cultures
were grown on plates of malt agar at room temperature for use in DNA
isolation or as inocula for soil block jars.
Soil block culture.
Modified ASTM soil block jars
(1) were set up as follows. A soil mix (1:1:1 by volume) was
prepared by mixing equal volumes of potting soil, sphagnum moss, and
vermiculite and then moistened with deionized distilled water. About 1 cup of the mix was placed in each pint-sized Mason jar, and water was
allowed to absorb overnight. The next day, 20 ml of water was added per
jar so that the soil mix was moist and a little free water was present.
Two pieces of birch tongue depressor were placed on the soil surface to
serve as feeder strips. Lids were inverted to prevent sealing and
screwed onto the jars with rings. Jars were autoclaved for 30 min. Two
days later the jars were again autoclaved for 30 min.
The feeder strips in each jar were inoculated with culture blocks (ca.
0.5 cm
3) of the appropriate fungal isolate, and one culture
block was
placed at each end of each feeder strip. In uninoculated
control
jars, blocks of sterile malt agar were used. Jars were
incubated
at room temperature to allow fungal colonization of feeder
strips.
Radial or longitudinal sections of spruce sapwood (1 by 1 by 0.25 in.
[1 in. = 25.4 mm]) cut from the same tree were oven
dried at 100°C
for 48 h, weighed, and then autoclaved for 30 min
enclosed in
glass petri dishes. After cooling, the wood blocks
were added
aseptically to the jars at one block per jar. Each
experiment used wood
blocks cut from only radial sections or from
only longitudinal
sections. Wood blocks cut from radial sections
were placed so that a
transverse face contacted the top of the
colonized feeder strips. Wood
blocks cut from longitudinal sections
were placed so that a
longitudinal face contacted the top of the
colonized feeder strip. Jars
were incubated at room temperature
to allow colonization of the spruce
blocks.
After the appropriate colonization time, the wood blocks were harvested
aseptically, observing precautions to prevent cross-contamination
of
the samples at all steps of processing. Mycelia on the surface
of the
block were removed by gently scraping them with a razor
blade, a new
blade being used for each block. The fresh weight
was recorded. The
block was cut in half vertically, i.e., perpendicular
to the face of
the block that had contacted the colonized feeder
strip. One-half was
placed in a small plastic sample bag, labeled,
and stored at

70°C
for DNA isolation. The fresh weight of the
other half block was
recorded, after which it was oven dried at
100°C for 48 h, and
its dry weight recorded to allow calculation
of the final dry weight of
the whole block at harvest based on
the following ratio: total fresh
weight/calculated total dry weight
= partial fresh weight/partial
dry weight. Wood decay was estimated
as the percent dry weight loss as
follows: percent weight loss
= [1

(final dry
weight/initial dry wt)] ×
100.
DNA isolation.
DNA was isolated from fresh mycelia taken
from the surface of plate cultures, from lyophilized mycelia, or from
infected wood by extraction with cetyltrimethylammonium bromide (CTAB)
in the presence of
-mercaptoethanol, followed by organic extractions and isopropanol precipitation of the DNA. Our method is based on those
of Taylor et al. (19) and Wilson (21). For fresh mycelia a 2× CTAB extraction buffer (2% [wt/vol] CTAB; 100 mM Tris
HCl, pH 8.0; 1.4 M NaCl; 20 mM EDTA; 0.2% [vol/vol]
-mercaptoethanol) was used, with the
-mercaptoethanol being added
just prior to use. For lyophilized mycelia or dry tissues such as wood
samples, a 1× CTAB extraction buffer (diluted 2× buffer) was used. It
is especially important to use the 1× CTAB extraction buffer for wood
samples; otherwise, the aqueous and organic phases invert due to
rehydration of the wood when the 2× CTAB extraction buffer is used.
Wood blocks were sampled by drilling through noninoculated wood
surfaces. Precautions were observed during drilling of the
wood blocks
to prevent cross-contamination of samples. Both the
work table and
gloves were swabbed with 70% ethanol to surface
sterilize them and to
collect any bits of sawdust before and after
drilling each sample. A
rechargeable cordless drill was used because
it has less surface area,
fewer crevices, and no cord to collect
dirt and sawdust, and a molded
housing which can be easily wiped
clean with 70% ethanol. Drill bits
were carefully cleaned with
laboratory detergent, rinsed, soaked in
95% ethanol, and flame
sterilized. A drill bit was inserted through a
cone of filter
paper (new for each sample), positioned so as to cover
the chuck
and prevent sawdust from entering it. We drilled through each
wood block, on a line perpendicular to the face of the block that
had
contacted the colonized feeder strip, with a 1/8-in. diameter
bit to
generate a fine sawdust from which DNA could be isolated
directly; no
further grinding of the sawdust was needed to achieve
good DNA
extraction. Once a prepared drill bit was used to drill
a wood sample,
it was not reused until it had been recleaned and
resterilized by the
procedure described above. Fresh or lyophilized
mycelia was simply
ground to a fine powder with liquid nitrogen
in a mortar and pestle for
use in DNA
extraction.
Ground or drilled material (100 to 200 µl) was transferred to a
sterile microfuge tube. Then, 600 µl of the appropriate CTAB
extraction buffer was added, and the sample was mixed to resuspend
the
powdered tissue in the buffer and incubated at 65°C for 2
h. The
sample was extracted with 1 volume of chloroform-isoamyl
alcohol (24:1,
vol/vol) and centrifuged at 10,000 ×
g for 10 min
at
room temperature. The aqueous phase was transferred to a new
tube, and
a 1/10 volume of 10% (wt/vol) CTAB in 0.7 M NaCl was
added. After
mixing, the sample was incubated at 65°C for 1 h.
Once again the
sample was extracted with chloroform-isoamyl alcohol
(24:1, vol/vol)
and centrifuged as described above. The aqueous
phase was transferred
to a new tube and extracted with 1 volume
of phenol-chloroform-isoamyl
alcohol (25:24:1, vol/vol/vol), followed
by centrifugation at
10,000 ×
g for 10 min at room temperature.
The aqueous
phase was transferred to a new tube, and the DNA was
precipitated by
the addition of 0.6 volume of ice-cold isopropanol.
After incubation at

20°C for 30 min, the DNA precipitate was
collected by
centrifugation at 12,000 ×
g for 15 min. The pellet
was washed twice with ice-cold 70% (vol/vol) ethanol and dried.
The
pellet was resuspended in DNA storage buffer (6 mM Tris HCl,
0.1 mM
EDTA; pH 7.5); 100 µl was used for DNA isolated from mycelia,
and 50 µl was used for DNA isolated from wood samples. Incubation
at 65°C
speeded up resuspension of the
DNA.
PCR amplification.
The ITS region was amplified by PCR from
DNA isolated from pure cultures of each of the fungi listed in Table 1
and from wood blocks colonized by individual isolates of wood decay
basidiomycetes or wood-inhabiting ascomycetes. Primers ITS1-F (CTT GGT
CAT TTA GAG GAA GTA A), which is specific for the higher fungi
(7), and ITS4 (TCC TCC GCT TAT TGA TAT GC), the universal
primer (20), were used together as a positive control for
amplification, since they would be expected to amplify the ITS region
from both ascomycetes and basidiomycetes. The primer pair ITS1-F and
ITS4-B (CAG GAG ACT TGT ACA CGG TCC AG), which is specific for
basidiomycetes (7), were used to specifically amplify the
ITS region from only basidiomycetes.
Amplifications were performed in 50-µl reactions of PCR buffer (10 mM
Tris HCl, pH 8.3; 50 mM KCl; 0.001% [wt/vol] gelatin
[Perkin-Elmer]), 200 µM concentrations of each deoxyribonucleotide
triphosphate, and 200 nM concentrations of each of the appropriate
primers, with nonacetylated bovine serum albumin (BSA; Sigma A-7906)
at
250 ng/µl, total DNA isolated from a pure fungal culture or
from a
wood decay sample, 0.056 µM TaqStart antibody (Clontech),
and 0.002 µM AmpliTaq DNA polymerase (Perkin-Elmer), i.e., 2 U
per 50-µl
reaction. The TaqStart antibody and AmpliTaq DNA polymerase
were mixed
together and preincubated prior to being added to the
rest of the
reaction components as per the manufacturer's instructions
(Clontech).
Samples were overlaid with mineral oil and amplified
in a MJ Research
Thermocycler Model PTC-100. PCR reactions consisted
of an initial
denaturation at 94°C for 1 min 25 s, 35 cycles of
amplification,
and a final extension at 72°C for 10 min; each
cycle of amplification
consisted of denaturation at 95°C for 35
s, annealing for
55 s (at 55°C for reactions with ITS1-F and ITS4
and at 60°C
for reactions with ITS1-F and ITS4-B), and extension
at 72°C for 1
min.
Weakly positive or negative amplifications were reconfirmed as positive
or negative by taking an aliquot of the PCR reaction
and reamplifying
it with the primer pair used in the original
reaction. Aliquots of the
PCR reaction using template DNA isolated
from wood and the primers
ITS1-F and ITS4-B were also reamplified
to ensure ample amplicon DNA
for multiple restriction digestions;
this allowed us to identify the
fungus present in the wood, even
when there were few to no physical
signs of
decay.
PCR products were separated by electrophoresis in 2% (wt/vol) agarose
gels in 1× TBE (89 mM Tris-borate, 89 mM boric acid,
2 mM EDTA) with
ethidium bromide (EtBr) at 100 ng/ml in the gel
and running buffer; DNA
bands were visualized by the fluorescence
of the intercalated EtBr
under UV light and
photographed.
Restriction digestion of PCR products.
PCR reaction products
were digested directly without further purification with restriction
endonucleases to obtain RFLPs; each sample was digested with
AluI, HaeIII, TaqI, or RsaI
in single-enzyme digests, as well as in a double digest with
TaqI and HaeIII. Per each 20-µl restriction
digest, 10 µl of unpurified, amplified PCR reaction was mixed with
the appropriate restriction reaction buffer and 10 U of the appropriate
enzyme and then incubated for 6 h at 37°C for the
AluI, HaeIII, or RsaI digests or at
65°C for the TaqI digests.
Restriction fragments were separated by electrophoresis in 2% (wt/vol)
and 2.5% (wt/vol) Sepharide Gel Matrix (Gibco-BRL)
in 1× TAE (40 mM
Tris acetate, 1 mM sodium EDTA) with EtBr at
100 ng/ml in the gel and
running buffer. DNA bands were visualized
by fluorescence under UV
light and
photographed.
 |
RESULTS |
DNA isolation from decayed wood.
CTAB extraction in the
presence of
-mercaptoethanol followed by organic extractions and
isopropanol precipitation of the DNA yielded DNA clean enough to
amplify by PCR regardless of whether the starting material was fungal
mycelia or decayed wood. The more decayed the wood, the more pigmented
was the DNA-containing aqueous phase. Subsequent extractions with
chloroform-isoamyl alcohol and phenol-chloroform-isoamyl alcohol
removed some of the pigmented by-products of wood decay, and more
remained behind in the aqueous isopropanol phase upon precipitation of
the DNA. However, substances inhibitory to PCR could carry through the purification procedure. For example, in preliminary experiments when
DNA was isolated from replicate sets of drilled samples from highly
decayed wood blocks (60% plus weight loss), the aqueous phase of
samples in which the initial CTAB extraction had lasted overnight were
much more strongly pigmented than those initially extracted for only
2 h, as in the standard protocol (see Materials and Methods); we
would expect more by-products of wood decay to be extracted in an
overnight versus a 2-h incubation. All of the 2-h CTAB-extracted DNA
preparations were amplified by PCR; however, several of the overnight
CTAB-extracted DNA preparations did not amplify, probably due to a
higher concentration of compounds inhibitory to PCR remaining after purification.
Optimization of PCR assay conditions for detection of
basidiomycetes.
The primers ITS1-F (higher fungus specific) and
ITS4 (universal primer) amplified only one band (500 to 1,300 bp,
depending on the fungal species) from DNA isolated from pure cultures
of both ascomycetes and basidiomycetes via an ordinary PCR protocol, i.e., no hot start was needed. However, when we amplified the ITS
region with the primers ITS1-F and ITS4-B (basidiomycete specific) from
total DNA isolated from pure cultures, we obtained a number of minor
amplification bands in both basidiomycetes and ascomycetes with the
published amplification protocol that used an annealing temperature of
55°C (7). Although the main product (850 to 1,460 bp,
depending on the fungal species) was not amplified from ascomycetes, a
small band amplified very strongly in certain species of ascomycetes,
e.g., a 210-bp band from Phialocephala fusca and a 330-bp
band from Ophiostoma ulmi, in addition to the other minor bands. We tested a series of incrementally higher annealing
temperatures and found that 60°C gave the cleanest results. The other
minor bands were no longer produced in amplifications from
basidiomycetes and ascomycetes, but the small strong band was still
amplified from P. fusca and O. ulmi; the addition
of a hot start to the PCR protocol eliminated this band. The primers
ITS1-F and ITS4-B amplify a product from only basidiomycetes when a hot
start and an annealing temperature of 60°C are used. Substitution of
the TaqStart antibody system for the traditional hot start method produced the same amplification results. The TaqStart antibody system
mimics a traditional hot start and yet is much simpler to use for
processing large numbers of samples at one time and with less risk of
introducing contaminating DNA.
In order to achieve specific amplification of DNA isolated from decayed
wood, further adjustments to the PCR protocol were
needed. Addition of
nonacetylated BSA to PCR reactions, which
is known to relieve
inhibition of amplification by humic acids,
fulvic acids, and organic
components of soils and manure (
13),
allowed some
amplification to occur from samples containing inhibitory
wood decay
by-products; but this amplification was often nonspecific.
Additionally, a hot-start protocol, either the traditional method
or
the TaqStart antibody system, was required to obtain specific
amplification of DNA isolated from wood decay
samples.
We adopted as our standard PCR amplification conditions the inclusion
of nonacetylated BSA at 250 ng/µl and the use of a hot
start, the
TaqStart antibody system for all reactions regardless
of the tissue
source of template DNA or primers used. These conditions
are described
in detail in Materials and
Methods.
Fungal species survey.
We surveyed a total of 43 species (60 isolates) of fungi. These included 16 species of basidiomycetes, 14 of
which are wood decay fungi, both brown rot and white rot, and 27 species of ascomycetes, 25 of which are wood inhabiters (pathogens,
endophytes, and saprophytes). For the initial survey (Table 1), PCR
amplifications were performed using total DNA isolated from pure
cultures of the fungi as the DNA template. Primers ITS1-F and ITS4
amplified the ITS region from all of these fungi, both ascomycetes and
basidiomycetes, as expected. Primers ITS1-F and ITS4-B amplified the
ITS region from only the basidiomycetes (Fig.
1, Table 1).

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FIG. 1.
PCR amplification of nuclear rDNA from total DNA
isolated from pure cultures of basidiomycetes (A) and ascomycetes (B).
Electrophoresis in 2% (wt/vol) agarose in 1× TBE. The two outer lanes
contain molecular weight markers. Inner even-numbered lanes contain
samples amplified by the primer pair ITS1-F and ITS4-B, and the
odd-numbered lanes contain samples amplified by primers ITS1-F and
ITS4. (A) Lanes 2 to 9 contain brown-rot fungi, and lanes 10 to 17 contain white-rot fungi. Lanes 1 and 20, PCR markers (Promega); lanes 2 and 3, Coniophora puteana Fp-90099-Sp; lanes 4 and 5, Gloeophyllum trabeum Mad-617-R; lanes 6 and 7, Postia
placenta Mad-698-R; lanes 8 and 9, Serpula lacrimans
Harm-888-R; lanes 10 and 11, Lentinula edodes 117=1t(d);
lanes 12 and 13, Resinicium bicolor ATCC 64897; lanes 14 and
15, Scytinostroma galactinum ATCC 64896; lanes 16 and 17, Trametes versicolor Fp-101664-Sp; lanes 18 and 19, no
template DNA (i.e., negative controls). (B) Lanes 1 and 20, PCR markers
(Promega); lanes 2 and 3, Aureobasidium pullulans ATCC
34621; lanes 4 and 5, Hormonema dematiodes; lanes 6 and 7, Pestalotiopsis sp.; lanes 8 and 9, Leucostoma
kunzei; lanes 10 and 11, Scleroderris lagerbergii 1877;
lanes 12 and 13, Sirococcus conigenus; lanes 14 and 15, Sphaeropsis sapinea B468; lanes 16 and 17, Xenomeris
abietis; lanes 18 and 19, no template DNA (i.e., negative
controls).
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|
Detection of decay fungi in wood.
The next step was to see if
we could detect fungi in spruce wood by PCR amplification (Fig.
2, Table 2)
using total DNA isolated from colonized wood blocks as the DNA
template. We surveyed 30 species of fungi colonizing spruce wood. Two
replicate jars were set up and inoculated, as described in Materials
and Methods, for each of the wood-decaying basidiomycete species listed
in Table 1 (excluding Fomitopsis pinicola and
Trichaptum abietinum) and for each of the following
wood-inhabiting ascomycetes: Ceratocystis pilifera ATCC
60758, Ophiostoma ulmi ATCC 32439, Phialocephala fusca ATCC 62326, Phialophora mutabilis ATCC 42792, Trichoderma reesei ATCC 26921, Trichoderma viride
ATCC 32630, Aureobasidium pullulans, Hormonema
dematiodes, Pestalotiopsis sp., and Xenomeris abietis. Wood blocks cut from radial sections of spruce were added to the colonized feeder strips and harvested after 8 months of colonization.

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FIG. 2.
PCR amplification of nuclear rDNA from total DNA
isolated from wood blocks colonized by wood decay fungi or endophytes.
Electrophoresis in 2% (wt/vol) agarose in 1× TBE. The two outer lanes
contain molecular weight markers. Inner even-numbered lanes contain
samples amplified by the primer pair ITS1-F and ITS4-B, and the
odd-numbered lanes contain samples amplified by primers ITS1-F and
ITS4. Lanes 2 to 7, brown-rot basidiomycetes; lanes 8 to 13, white-rot
basidiomycetes; lanes 14 to 17, endophytic ascomycetes. Lanes 1 and 20, PCR markers (Promega); lanes 2 and 3, Postia placenta
Mad-698-R; lanes 4 and 5, Gloeophyllum trabeum Mad-617-R;
lanes 6 and 7, Leucogyrophana pinastri; lanes 8 and 9, Lentinula edodes 117=1t(d); lanes 10 and 11, Trametes
versicolor; lanes 12 and 13, Scytinostroma galactinum
ATCC 64896; lanes 14 and 15, Hormonema dematiodes; lanes 16 and 17, Pestalotiopsis sp.; lanes 18 and 19, no template DNA
(i.e., negative controls).
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Wood blocks with ascomycetes had a negligible weight loss, the majority
by less than 0.5%, and seemed unchanged in appearance.
The weight
losses of wood blocks with white-rot fungi were very
variable and
ranged from negligible to approximately 40%; there
was little to no
change in the color of the wood, but some of
the more decayed ones,
e.g., replicate blocks colonized by one
of the isolates of
Trametes versicolor had become stringy in texture.
Wood
blocks with brown-rot fungi had decayed the most and were
very brown in
color; all but one isolate had caused a weight loss
of 65 to 70%, the
exception being
Coniophora puteana isolate Fp-90099-Sp.
In
all of the wood block treatments, we had weight losses ranging
between
0 and 70%. Primers ITS1-F and ITS4 amplified DNA from
all of the
samples, including the uninoculated control blocks.
Primers ITS-1F and
ITS4-B amplified DNA from wood blocks that
had been inoculated with
only basidiomycetes, i.e., the brown-rot
isolates and white-rot
isolates; ITS1-F and ITS4-B did not amplify
DNA from uninoculated
control blocks nor from any of the wood
blocks inoculated with
wood-inhabiting ascomycetes. The unknown
contaminant fungus detected in
the uninoculated control blocks
is probably an ascomycete, since no
amplification occurs when
the basidiomycete-specific primer ITS4-B is
present in the PCR
reaction; we suspect it may be a mold known to
survive in wood
upon repeated autoclaving. We could reliably detect the
presence
of wood decay fungi by PCR with the primers ITS1-F and ITS4-B
in spruce blocks exhibiting a range of degradation
states.
Fungal identification.
In order to identify the basidiomycetes
detected by PCR, we generated RFLPs of the ITS region, the product
amplified by primers ITS1-F and ITS4-B, by restriction digestion with
RsaI, AluI, HaeIII, TaqI,
or TaqI-HaeIII. RsaI was not very
useful because it did not cut the amplicon from 10 out of the 14 species of wood-decaying basidiomycetes tested nor that from the
ectomycorrhizal Pisolithus tinctorius and the soil-borne
Rhizoctonia solani, which do not decay wood. The other
restriction endonucleases generated more fragments per digest, so that
each basidiomycete could be identified to the species level from the
combination of its RFLP profiles (Fig. 3,
Table 3). The majority of RFLP profiles
generated for any given enzyme were unique for each fungal species. The
two Gloeophyllum species, however, had identical
AluI RFLP profiles and identical HaeIII RFLP
profiles; G. trabeum and G. sepiarum could be
separated by their TaqI RFLP profiles and their
TaqI-HaeIII RFLP profiles. Different isolates of
a given fungal species usually had identical RFLP profiles for a
particular restriction endonuclease; this was true for each enzyme for
isolates of G. trabeum, Irpex lacteus,
Postia placenta, Resinicium bicolor, and
Serpula lacrimans. For other fungi, some enzymes would
generate RFLP profiles which separated isolates at the species level
and other enzymes would generate RFLP profiles which separated isolates
at the subspecies level. For example, isolates of Scytinostroma
galactinum had identical AluI RFLP profiles and
identical HaeIII RFLP profiles, but the isolates could be
distinguished from each other by their respective TaqI RFLP
profiles and TaqI HaeIII RFLP profiles.

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FIG. 3.
TaqI restriction digests of the PCR product
amplified by the primer pair ITS1-F and ITS4-B from DNA isolated from
pure cultures of basidiomycetes. Electrophoresis in 2% (wt/vol)
Sepharide Gel Matrix (Gibco-BRL) in 1× TAE. The two outer lanes
contain molecular weight markers. Each inner lane contains a different
fungal species; lanes 2 to 8 contain brown-rot fungi, and lanes 9 to 15 contain white-rot fungi. Lanes 1 and 18, PCR markers (Promega); lane 2, Coniophora puteana Fp-90099-Sp; lane 3, Fomitopsis
pinicola K8sp; lane 4, Gloeophyllum sepiarum 10-BS2-2;
lane 5, Gloeophyllum trabeum Mad-617-R; lane 6, Leucogyrophana pinastri; lane 7, Postia placenta
Mad-698-R; lane 8, Serpula lacrimans Harm-888-R; lane 9, Irpex lacteus KTS 003; lane 10, Lentinula edodes
117=1t(d); lane 11, Phanerochaete chrysosporium ATCC 24725;
lane 12, Resinicium bicolor ATCC 64897; lane 13, Scytinostroma galactinum ATCC 64896; lane 14, Trametes
versicolor Fp-101664-Sp; lane 15, Trichaptum abietinum
1247 MJL; lane 16, Pisolithus tinctorium ATCC 38054, an
ectomycorrhiza; lane 17, Rhizoctonia solani 1AP, a pathogen
of herbaceous plants.
|
|
The identities of basidiomycetes detected by PCR from colonized spruce
wood blocks were confirmed by comparing the RFLPs of
the product
amplified by primers ITS1-F and ITS4-B from DNA isolated
from wood
blocks to that from the respective pure culture of the
fungus. Figure
4 demonstrates that the
TaqI
RFLP profile for any
one wood block matches that of the
TaqI
digest of the amplicon
obtained from DNA from a pure culture of that
particular fungal
isolate; analogous results were also obtained with
AluI,
HaeIII,
and
TaqI-
HaeIII digestions.

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|
FIG. 4.
TaqI restriction digests of the PCR product
amplified by the primer pair ITS1-F and ITS4-B from DNA isolated from
wood decay basidiomycetes. Electrophoresis in 2% (wt/vol) Sepharide
Gel Matrix (Gibco-BRL) in 1× TAE. The two outer lanes contain
molecular weight markers. Each group of three inner lanes represents
the TaqI digests for one fungal isolate amplified from DNA
isolated from each of two different wood blocks and a pure culture from
left to right, respectively. (A) Lanes 1 and 20, PCR markers (Promega);
lanes 2 to 4, Gloeophyllum trabeum; lanes 5 to 7, Gloeophyllum trabeum, Mad-617-R; lanes 8 to 10, Postia
placenta; lanes 11 to 13, Postia placenta Mad-698-R;
lanes 14 to 16, Trametes versicolor; lanes 17 to 19, Trametes versicolor Fp-101664-Sp. (B) Lanes 1 and 20, PCR
markers (Promega); lanes 2 to 4, Resinicium bicolor; lanes 5 to 7, Resinicium bicolor ATCC 44175; lanes 8 to 10, Resinicium bicolor ATCC 64897; lanes 11 to 13, Scytinostroma galactinum; lanes 14 to 16, Scytinostroma galactinum ATCC 64896; lanes 17 to 19, Scytinostroma galactinum ATCC 44178.
|
|
Time course studies.
In order to determine how early we could
detect wood decay fungi in wood, we ran two time course studies with
the brown-rot fungi Postia placenta isolate Mad-698-R and
Gloeophyllum trabeum isolate Mad-617-R. Soil block jars were
set up and inoculated as described in Materials and Methods. For each
time course experiment, three replicate jars were inoculated for each
combination of time and fungal isolate, as well as for a time-zero
uninoculated control and an 8-month-incubated uninoculated control. The
first time course used wood blocks cut from radial sections of spruce
sapwood, and the second time course used wood blocks cut from
longitudinal sections. Wood blocks were harvested after 1, 2, 4, and 8 weeks and after 4 and 8 months of colonization.
Wood decay progressed more rapidly in wood blocks cut from radial
versus longitudinal sections of spruce sapwood, as evidenced
by the
change in percent weight loss of the wood over time (Table
4). A few samples from the first time
course and several from
the second time course amplified weakly or not
at all with primers
ITS1-F and ITS4-B; the positive or negative nature
of each was
confirmed by reamplification of an aliquot of the original
PCR
reaction.
Gloeophyllum trabeum and
P. placenta, both brown-rot
basidiomycetes, could be detected in wood
by PCR amplification
using primers ITS1-F (higher fungus specific) and
ITS4-B (basidiomycete
specific) after 1 week of colonization, the
shortest colonization
period used in the study.
G. trabeum
was detected in all replicates
of all samples from all colonization
times in both cuts of wood
and could be detected at a 0.3% mean weight
loss of the wood.
P. placenta was detected in all of the
samples from all of the
wood blocks cut from radial sections but not in
all of those cut
from longitudinal sections. After 1 week of
colonization (0.5%
mean weight loss),
P. placenta could be
detected in only one of
three of the wood blocks cut from longitudinal
sections, but by
2 week (3.0% mean weight loss), it could be detected
in three
of three blocks; detection was also variable at later time
points.
 |
DISCUSSION |
Although our procedure for DNA isolation and purification
may be longer than desired to routinely screen large numbers of wood
samples, we thought it best to begin the process of assay development
with a method highly likely to yield DNA amplifiable by PCR, since many
by-products of wood decay, if present at too high a concentration in
the reaction, would inhibit amplification of the DNA template. When
setting up PCR reactions with wood samples that have very low DNA
concentrations, diluting out the inhibitors could also mean diluting
out the DNA past the threshhold of detection. So it is better to start
with a DNA preparation from which one has removed as much of the
inhibitory materials as possible. With the minipreparation procedure
described in the Materials and Methods, one person can drill and
isolate DNA from 24 wood samples in one work day, observing all the
necessary precautions both during drilling of the wood and DNA
isolation to prevent any cross-contamination of samples.
Avoiding cross-contamination of samples is critical. Early on, we found
that preparation of the wood for DNA isolation is the step at which
cross-contamination can most easily occur due to the inherent
properties of sawdust. For example, a Wiley mill is not a good choice
for grinding samples for PCR work. It is very difficult to clean out
all of the crevices in which sawdust can be caught and, even after
disassembly, careful brushing out of remaining debris, reassembly, and
running through several volumes of clean fungus-free wood, and
recleaning all the surfaces and crevices with a cotton swab, there is
still carryover from one wood decay sample to the next; furthermore,
this whole process takes an unacceptably long time. A drill is a much
better choice. A rechargeable cordless drill has fewer crevices and
surfaces to collect dirt and debris and can be more easily cleaned than a Wiley mill. Drill bits are easy to clean and flame sterilize and are
relatively inexpensive, so one can have many of them ready to use. One
can prepare wood samples for DNA isolation very rapidly with a drill
and at far less risk of sample cross-contamination via sawdust. It is
also important to wear gloves and to keep the work area clean, i.e., it
is advisable to swab both your gloves and work surface with 70%
ethanol to collect any bits of sawdust between drilling each sample. By
observing these precautions, as described in detail in Materials and
Methods, we have not detected any cross-contamination in samples
prepared by drilling and so have adopted this procedure for routine use.
We have developed a DNA-based method to reliably detect brown-rot and
white-rot fungi in spruce wood using the published (7) primers ITS1-F (higher fungus specific) and ITS4-B (basidiomycete specific) to amplify the ITS region. We have optimized the reaction conditions for PCR with these primers for template DNA isolated from
both pure culture and spruce wood and can detect brown-rot and
white-rot fungi from incipient through advanced stages of wood decay.
Some late-stage brown-rot samples appeared to have weaker amplification
signals than less-decayed samples (data not shown). This could be due
to carryover of by-products of wood decay inhibitory to PCR,
degradation of DNA in the late stages of wood decay, or a combination
of the two. Currently, our assay is only qualitative; more work needs
to be done to make it quantitative. The ability to detect decay fungi
in other species of wood, preservative-treated wood, and wood
composites should also be examined. The differing chemical compositions
of both the undecayed and decayed forms of these substrates could
introduce new kinds of PCR-inhibitory compounds that may or may not be
eliminated or neutralized by our current methodology.
While the primer pair ITS1-F and ITS4-B will detect only
basidiomycetes, it will detect any basidiomycete present. For example, if the wood sample were taken from a root, there might be mycorrhizae present that would also be detected. Identity of the basidiomycete present can be achieved by restriction digestion of the PCR product. We
could distinguish wood decay basidiomycetes at the species level by
comparing the RFLP profiles obtained by TaqI digestion of
the ITS region amplified by ITS1-F and ITS4-B or by comparing the
combination of different RFLP profiles generated from this amplicon by
a number of different restriction endonucleases. Gardes et al.
(8) identified 20 taxa of ectomycorrhizal fungi to the species or species group level from the RFLP profiles of the ITS region
amplified by these primers using DNA from mycorrhizae and basidiocarps.
Using this method to identify all of their samples, these researchers
were able to create a snapshot of the community structure of these
ectomycorrhizal fungi both above and below ground in natural stands of
Pinus muricata.
Although PCR amplification followed by digestion with restriction
endonucleases worked fine for samples containing only one fungus, field
samples could pose a greater challenge and contain more than one
species of wood decay basidiomycete. As the number of different wood
decay basidiomycetes contained in a wood sample increases, it would
become correspondingly more difficult to identify them all to the
species level based on RFLPs. For a more specific and one-step assay
for a particular basidiomycete species, it would be better to develop a
species-specific PCR primer based on a suitably informative area of the
DNA sequence of the ITS region of that species. This concept could be
extended to develop an assay in which a number of different species
could be identified concurrently in one PCR reaction. Recently, Schmidt
and Moreth (16) developed species-specific primers based on
the DNA sequence of ITSII for the indoor rot fungi Serpula
lacrimans and Serpula himantioides. We are currently
designing species-specific primers for other brown-rot fungi.
We are also looking at DNA sequences of enzymes thought to be involved
in wood decay to see if it is possible to design primers that would
specifically detect only wood decay basidiomycetes and not other
basidiomycetes. It would be useful to be able to detect several wood
decay species concurrently in samples where other non-wood-decaying
species are likely to occur, e.g., tree roots and forest soils.
However, for the purposes of detecting wood decay fungi in branches,
tree trunks, harvested timber, or wood in service, where the
probability of nondecay basidiomycetes colonizing the internal wood is
very low, the assay we developed using the published primers ITS1-F and
ITS4-B is potentially very useful. The very lack of specificity which
limits the direct identification of the fungus to species can be an
advantage in developing a broad-based assay. Previous workers have used
PCR amplification in conjunction with RFLP analysis to identify wood
decay fungi (15, 23), but their work has focused on
identification of the fungi in culture or fungal material present on
the wood versus the direct identification of early stages of decay
within the wood. By focusing our efforts on the development of an assay
that can sample directly from wood, we hope to eventually eliminate the
need to culture the decay fungi as a first step, so that detection
would not be limited by the ability to culture them from a specific
wood sample. Although our current PCR method is broad based for
basidiomycetes, if used in combination with species-specific primers,
one could detect a particular wood decay species of interest and also
be alerted to the presence of other basidiomycetes, i.e., other
potential decay fungi, in the wood sample.
 |
ACKNOWLEDGMENTS |
This work was supported by grant number 95-34158-1347 from the
USDA and by the Maine Agricultural and Forest Experiment Station.
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Department of
Biological Sciences, University of Maine, Orono, ME 04469-5735. Phone: (207) 581-2995. Fax: (207) 581-2969. E-mail:
jellison{at}maine.maine.edu.
This work is contribution no. 2407 from the Maine Agricultural and
Forest Experiment Station, Orono, Maine.
 |
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