Next Article 
Applied and Environmental Microbiology, December 1999, p. 5193-5197, Vol. 65, No. 12
0099-2240/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.
Fungi from Geothermal Soils in Yellowstone
National Park
Regina S.
Redman,1,2
Anastassia
Litvintseva,3
Kathy B.
Sheehan,3,4
Joan M.
Henson,3,4,* and
Rusty J.
Rodriguez1,2
Western Fisheries Research Center,
USGS/BRD,1 and Botany Department,
University of Washington,2 Seattle,
Washington 98115, and Microbiology
Department,3 and Thermal Biology
Institute,4 Montana State University,
Bozeman, Montana 59717
Received 18 March 1999/Accepted 7 September 1999
 |
ABSTRACT |
Geothermal soils near Amphitheater Springs in Yellowstone National
Park were characterized by high temperatures (up to 70°C), high heavy
metal content, low pH values (down to pH 2.7), sparse vegetation, and
limited organic carbon. From these soils we cultured 16 fungal species.
Two of these species were thermophilic, and six were thermotolerant. We
cultured only three of these species from nearby cool (0 to 22°C)
soils. Transect studies revealed that higher numbers of CFUs occurred
in and below the root zone of the perennial plant Dichanthelium
lanuginosum (hot springs panic grass). The dynamics of fungal
CFUs in geothermal soil and nearby nongeothermal soil were investigated
for 12 months by examining soil cores and in situ mesocosms. For all of
the fungal species studied, the temperature of the soil from which the
organisms were cultured corresponded with their optimum axenic growth temperature.
 |
INTRODUCTION |
Specific genetic and/or
physiological adaptations allow microorganisms to exist in many
environments that experience extremes of temperature, pH, chemical
content, and/or pressure (1, 10, 12, 25, 27, 33).
Thermophilic organisms may belong to any of the three domains of life,
but most thermophilic species that have been described are members of
the Archaea or Eubacteria (5, 20). Thermophilic members of
the Eukarya tolerate less heat than thermophilic members of the other
domains, and it is thought that the former organisms do not grow at
temperatures greater than 60°C (1, 10, 25, 27, 28). For
example, fungi are considered thermophilic if they grow at 50°C or
higher temperatures and do not grow at 20°C or lower temperatures
(10).
Fewer than 50 species of thermophilic fungi have been described
(reviewed in references 10 and
25). Many of these organisms were first isolated
from guayule undergoing retting (10), a process similar to
composting, during rubber production. However, in recent years
thermophilic fungi have been isolated from manure composts, industrial
coal mine soils, beach sands, nuclear reactor effluents, Dead Sea
valley soils, and desert soils of Saudi Arabia. Although two fungi from
natural geothermal soils have been mentioned previously (6,
29-31), there have been no in-depth characterizations of fungal
communities in geothermal soils. In fact, in a recent publication,
Yellowstone National Park soil scientists state that thermal soils are
typically sterile (34).
In general, there is an inverse relationship between biological
diversity and the amount of adaptation required to survive in a
specific habitat (33). Thus, we expected that geothermal soils in Yellowstone National Park would have less fungal diversity and
hence be more amenable to our overall goal of characterizing and
monitoring soil fungal communities and their responses to environmental
change. The objectives of this study were (i) to determine the
diversity of culturable thermotolerant and/or thermophilic fungal
species in Yellowstone National Park geothermal soils, (ii) to
determine the optimal in vitro growth conditions for these species, and
(iii) to characterize the temporal and spatial distribution of the
culturable thermophilic and thermotolerant fungal species.
 |
MATERIALS AND METHODS |
Site characterization.
Fungi were cultured from 27 different
soil samples collected at two geothermal sites (designated sites 1a and
1b) near Amphitheater Springs and at three nongeothermal sites near
Amphitheater Springs or Mammoth in Yellowstone National Park. We
selected Amphitheater Springs as a field site because its thermal,
acidic soil and sparse vegetation suggested that the biodiversity in
this ecosystem would be relatively less complex and, hence, more easily
characterized. Sites 1a and 1b were separated by 800 m of
nongeothermal soil and were 100 and 25 m in diameter,
respectively. These sites exhibited heterogeneity with regard to
temperature, pH, metal content, and the occurrence of the grass
Dichanthelium lanuginosum (28; data not shown).
Soil transects.
To determine if fungal CFUs were associated
with the presence of D. lanuginosum, we collected samples
along two 3-m linear transects with isolated D. lanuginosum
plants located several meters apart. Soil temperatures were measured
every 30 cm at depths of 5, 10, 15, and 20 cm before soil cores were collected.
Soil cores.
A 2.5-cm-diameter soil corer was sterilized with
95% ethanol, and 20-cm soil cores were collected. Each soil core was
divided into 5-cm portions, which were aseptically transferred to
plastic bags, mixed thoroughly, stored at 4°C, and processed within
hours. Soil was prepared by suspending 1.2 ml (~1 g) of soil in 20 ml of sterile water, vortexing the suspension for 30 s, and allowing the debris to settle. After aliquots for culturing were removed, the pH
values of the suspensions were determined (21).
Fungal isolation, growth, and identification.
To simulate
the low-nutrient-content conditions in geothermal soils, fungi were
isolated by plating soil suspensions on 0.1× potato dextrose agar
(PDA) (pH 5) (Difco Laboratories, Detroit, Mich.) and minimal medium
containing (per liter) 0.5 g of L-glutamic acid HCl,
0.5 g of citric acid · H2O, 0.5 g of malic
acid (disodium salt), 0.5 g of glucose, 0.1 g of yeast
extract, and 15 g of agar. The pH of the minimal medium was
adjusted to 4.0 with HCl. After autoclaving, 10 ml of a salts solution
(containing 50 g of K2HPO4 per liter,
10 g of NaCl per liter, 1 g of FeCl3 · 6H2O per liter, 10 g of CaCl2 · 2H2O per liter, and 25 g of MgCl2 per
liter) per liter was added to the minimal medium. All media contained
50 mg of streptomycin per liter and 50 mg of ampicillin per liter, which were added to cooled media after autoclaving to inhibit bacterial
growth. Soil suspensions were diluted to obtain 20 to 30 CFUs per
plate. Ten plates (subsamples) prepared from each soil sample were
incubated for 24 to 96 h at 40°C, and each morphologically unique fungal colony was subcultured on 0.1× PDA, corn meal agar (pH
5.0) (Difco), minimal medium, and 0.1× Sabouraud dextrose (Difco) agar
(pH 4.0). All of the fungal species observed grew on 0.1× PDA, which
was used for subsequent experiments. Fungal species were identified by
microscopic analysis by using taxonomic guides and standard procedures
(2, 4, 8-11, 13-18, 23-25, 32). Unidentified
Penicillium species were distinguished on the basis of
morphological variations and were designated Penicillium species 1 through Penicillium species 5. The absence of
species designations for some of the isolates (see Table 2) does not mean that the organisms are new species but rather reflects
difficulties in taxonomic identification. Isolates may be obtained from
us with the permission of the Yellowstone National Park Center for Resources.
Temperature and pH optima of fungi.
The temperature optima
of fungal isolates were determined by measuring colony diameters after
incubation of 0.1× PDA plates for 24 to 96 h at 20, 25, 30, 35, 40, 50, and 55°C. The species that grew at 50°C but not at 20°C
were considered thermophilic (10). The mesophilic species
were the species that grew at temperatures between 20 and 40°C and
could not tolerate 55°C (see below). The pH optima for fungal growth
were determined by measuring colony diameters after 0.1× PDA plates
adjusted to pH 3 to 7 were incubated for 24 to 96 h at 35 or
45°C. Growth rates were determined with the following equation:
g = d2
d1/24, where g is the growth rate and d1 and d2 are the colony diameters
measured over a 24-h period at 24 and 48 h after inoculation.
Thermotolerance of fungi.
Mycelial plugs without spores from
cultures grown at 35°C were transferred to 0.1× PDA and incubated at
55°C for 7 days; then they were incubated at 35°C again. Colony
diameters were measured prior to the temperature shift and at 3, 4, and
5 days after the shift. The organisms that grew after the shift back to
35°C were considered thermotolerant organisms, and the organisms that
did not grow after the shift back to 35°C were considered mesophilic organisms.
In situ mesocosm construction and establishment.
Mesocosms
were constructed from polyvinyl chloride (PVC) pipe as follows. A 25-cm
length of 10-cm-diameter PVC pipe was cut in half along its length, and
two windows (4.5 by 20 cm) were cut out of each half of the pipe, as
shown in Fig. 1. The two halves of pipe
were placed together so that a tube was reformed, and the inner
circumference was lined with 1.5-mm-mesh nylon screen that was fixed
with nylon zip straps to the walls between the windows. Two T type
thermocouple probes were attached with nylon zip straps to the inside
walls on each half of the mesocosm at depths of 5 and 15 cm, and these
probes were monitored with a Campbell Scientific model CR10 data
logger. The top of the tube was secured with a nylon zip strap, and the
bottom of the tube was covered with nylon screen and secured with nylon
zip straps.

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FIG. 1.
In situ mesocosm design. The plant at the surface is
D. lanuginosum. The cross-hatching represents nylon mesh
over windows from which samples were obtained at depths of 5, 10, 15, and 20 cm. Thermocouple probes were placed at depths of 5 and 15 cm and
used to record temperatures every 2 h.
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Three mesocosms were constructed and placed in the geothermal soil at
site 1b approximately 1 m apart. A large soil core (10
by 25 cm)
containing one
D. lanuginosum plant was removed with
a
shovel and placed into each PVC tube. The mesocosms were placed
into
the original soil core sites and packed into position. Every
6 months
the data logger storage modules were downloaded and
replaced.
Community structure and dynamics.
The numbers of fungal CFUs
were determined four times between September 1996 and September 1997. We sampled a mesocosm by lifting it out of the ground and making a
small incision in each screened window in order to extract soil. Two
windows, representing replicates, at each depth (5, 10, 15, and 20 cm)
were sampled, and all subsequent samples were removed from the same
incisions in the windows. In addition, the surface soil near the plant
crown was sampled. The mesocosms were returned to their locations and packed into position. We also determined the numbers of fungal CFUs in
soil cores collected near the mesocosms (cores 36A through C) and in
adjacent cool-soil cores (cores 37A through C).
Soil sample suspensions were prepared as described above and plated
onto 0.1× PDA, which yielded 20 to 30 CFUs per plate;
10 plates
(subsamples) per sample were prepared. The minimum number
of CFUs
detected by this plating procedure was 40 CFUs/g of soil.
The plates
were incubated at 40°C for 48 to 96 h. The numbers
of CFUs of
each species obtained from two windows (replicates)
at each depth were
determined.
 |
RESULTS |
Relationship between fungal CFUs and D. lanuginosum.
We
monitored the number of fungal CFUs in soil cores along two linear
transects to determine if the number of fungal propagules increased in
the vicinity of the only plant present, D. lanuginosum. D. lanuginosum occurs in North America, the West Indies, and
northern South America, but at elevations such as those that occur in
Yellowstone National Park (>6,000 ft), it is restricted to
geothermally heated ground (26). The transects which we used
were at site 1a, where single plants were usually several meters apart.
The mean numbers of CFUs were 20 and 3.2 times higher in soil below
D. lanuginosum than in soil devoid of surface vegetation
along transect A (P = 0.008, as determined by
Student's t test) and transect B (P = 0.02,
as determined by Student's t test), respectively (Fig. 2 [only 5-cm data are shown]). There
also was an inverse relationship between the number of fungal CFUs and
soil depth; fewer CFUs were obtained from lower depths in all transect
cores. At depths of 15 to 20 cm, where D. lanuginosum roots
were no longer visible, the numbers of fungal CFUs did not differ from
the numbers of CFUs in cores that lacked D. lanuginosum
(data not shown).

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FIG. 2.
Total fungal CFUs obtained at 5 cm along two thermal
soil transects with sparse vegetation. Core samples were collected
every 30 cm in May 1996 (transect A) and September 1996 (transect B)
and either had D. lanuginosum on the surface (+ plant) or
were devoid of vegetation ( plant). The error bars indicate standard
deviations (n 3; P = 0.008 for transect A and
P = 0.02 for transect B, as determined by Student's
t tests).
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Culturable fungi in geothermal soils.
We cultured 16 different
species of fungi from geothermal soils plated at 40°C (Table
1), although we observed other species when soil samples were plated at room temperature (data not shown). All
of the species that grew at 40°C were members of the Deuteromycetes, Ascomycetes, or Zygomycetes; no member of the Basidiomycetes was identified. The optimal temperature for laboratory growth for most of
these species was 35°C, and the optimal pH for most species was pH 5 when the organisms were grown on 0.1× PDA at the optimal temperature
(Table 1). Two organisms, Dactylaria constrictum var.
gallopava and Acremonium alabamense, grew at
55°C but not at 20°C and were classified as thermophiles
(10). Six other species (Absidia cylindrospora,
Aspergillus fumigatus, Aspergillus niger,
Penicillium species 1, Penicillium species 2, and
Penicillium species 3) had thermotolerant profiles because
they did not grow at 55°C but grew when they were incubated at 35°C
after exposure to 55°C for 1 week. The remaining species were
mesophilic since they did not grow at 35°C after exposure to 55°C
for 1 week.
When nongeothermal soil samples (e.g., cores 37A through C) were plated
at 40°C, only
A. fumigatus and two
Penicillium
species
were recovered. None of the other fungi listed in Table
1 were
isolated from four adjacent nongeothermal soils during this study
(cores 37A through C and data not
shown).
In situ soil mesocosms and characterization of geothermal
soils.
The soils at sites 1a and 1b are acid-altered rhyolite and
siliceous sinter geothermal soils (34), and they varied
significantly with respect to temperature, pH, organic carbon content,
and metal content both within and between cores (Table
2 and data not shown). The temperature
increased with depth in all of the geothermal soils (Table 2, mesocosms
31 through 33 and cores 36A through C and 74 other cores, including the
transect cores, from geothermal soils [data not shown]). In contrast,
the temperature in adjacent nongeothermal soil decreased with depth
(Table 2, cores 37A through C and three other nongeothermal soil cores
[data not shown]). There was no apparent relationship between
geothermal soil depth and pH. The temperatures of geothermal soil cores
near Amphitheater Springs varied substantially (Table 2, cores 4 through 35). In addition, cores could not be sampled more than once and
could not be used to assess changes in propagule frequency with time. To avoid these complications, we placed three in situ mesocosms (Fig.
1) at geothermal site 1b and collected samples from them during
September 1996 and February, May, and September 1997. We also took core
samples on the same collection dates between the mesocosms (cores 36A
through C) and from nearby nongeothermal soil (cores 37A through C) for
comparison. The geothermal soils never had snow cover and contained
more water in the winter than in the summer (data not shown).
As observed with all of the geothermal soils examined at sites 1a and
1b, the temperatures in the mesocosms increased with
depth (Table
2).
In addition, when temperatures were monitored
every hour over a 12-h
period, the data revealed that there were
daily temperature cycles at
depths of 5 and 15 cm in all three
mesocosms and that the temperatures
ranged from 0.5 to 60°C. A
nongeothermal soil, monitored over a 24-h
period in September
1996, did not exhibit this diurnal temperature
fluctuation; that
is, the temperature at depths of 10 to 20 cm was
stable at ~8°C
(data not shown). The lowest and highest
temperatures in the mesocosms
occurred in the winter and the summer,
respectively. During the
year, the temperature in a mesocosm varied up
to 46°C at each
depth. There was no apparent relationship between the
season and
the soil pH; core samples were almost always acidic, and the
pH
values were within the ranges listed in Table
2.
Numbers of fungal CFUs in mesocosms and nearby soil cores.
In
general, the numbers of fungal CFUs in the three mesocosms and adjacent
core samples (cores 36A through C) were similar, and we isolated the
species listed in Table 1 from all mesocosms and adjacent cores. The
numbers of CFUs of all species changed with the season and increased in
the winter and spring, when soil moisture levels were greatest. The
numbers of culturable CFUs of four representative organisms, A. alabamense, D. constricta var. gallopava,
C. elegans, and Penicillium species 4, from one representative mesocosm (mesocosm 32) are shown in Fig.
3. Adjacent cores 36A through C and
mesocosms exhibited similar trends, and the standard deviations were
similar.

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FIG. 3.
Numbers of CFUs of representative species obtained from
one mesocosm (mesocosm 32) at depths of 5 to 20 cm from September 1996 to September 1997. Each point represents the average of two replicate
sample values, and the error bars indicate standard deviations (not
visible if the deviation was small). The temperature ranges in this
mesocosm at depths of 5 to 20 cm at different sampling times were as
follows: 31 to 63°C in September 1996, 7 to 24°C in February 1997, 21 to 50°C in May 1997, and 29 to 67°C in September 1997.
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In the winter, there were few CFUs (<40 CFUs/g of soil) of the
thermophile
A. alabamense in the cooler soil samples near
the
surface, or this organism was undetectable (Fig.
3 and Table
1).
Only 13% of the
A. alabamense CFUs were cultured from soils
with
temperatures below 20°C, whereas 48% were cultured from soils
with temperatures above 40°C. In contrast, the other thermophile,
D. constricta, was cultured from soils with a broader
temperature
range; 20% of the
D. constricta CFUs were
cultured from <20°C
soil, and 56% were cultured from 20 to 40°C
soil (Fig.
3 and Table
1). The mesophile
Penicillium species
4 was present only in cooler
soils (89% of the CFUs were obtained from
soils with temperatures
less than 20°C) and was not detectable in the
warmest soil samples
(Fig.
3 and Table
1). However, another
representative mesophile,
Cunninghamella elegans, was
cultured from soils with a broader
range of temperatures and was
present at all depths in the winter
and spring, but it was isolated
only from the cooler September
soil samples (Fig.
3 and Table
1). The
frequencies of all 16
species cultured from thermal soils were
consistent with the laboratory
growth temperature ranges and growth
optima of the organisms (Table
1 and data not
shown).
 |
DISCUSSION |
Physical analyses of soil cores revealed that significant
variations in soil temperature and pH occurred at geothermal soil sites
in Yellowstone National Park. Soil near Amphitheater Springs is acidic
because of sulfuric acid produced by the oxidation of sulfides, such as
hydrogen sulfide (H2S) and pyrite (FeS2), that are present at high concentrations in most geothermal areas of the park (3, 7). The relationships between temperature and soil depth also were due to geothermal activity.
Only two fungi isolated from geothermal soil grew at 55°C, but six
other species were thermotolerant. All of the isolates tolerated a wide
range of pH values and grew at pH 3 to 6. The highest numbers of fungal
CFUs occurred at soil depths of 5 cm, and more fungal CFUs were
isolated from soil cores containing roots of D. lanuginosum.
These findings suggested that the presence of plants is a primary
factor for fungal CFU production, at least at this geothermal site.
Very little is known about the nature of interactions between
root-associated fungi and plants adapted to geothermal environments.
Perhaps D. lanuginosum ameliorates the effects of this
extreme environment. This plant, like the plants of temperate soils,
may also provide fungal nutrients via root exudates, or alternatively,
the fungi may utilize the plants as a nutrient source by establishing
symbiotic or saprophytic associations (12).
The frequencies of the species which we identified corresponded with
soil temperatures and were consistent with the optimal laboratory
growth temperatures. More CFUs of all species were cultured from soils
with higher moisture contents in the winter and spring. However,
moisture alone was not sufficient for obtaining higher numbers of CFUs,
as the numbers of CFUs of all species increased only in moist soils
whose temperatures were within the optimal ranges. We cultured two true
thermophilic fungi from the geothermal soil samples, and these fungi
were never isolated from cooler soils. Although both A. alabamense and D. constricta were thermophilic, a
greater percentage of D. constricta CFUs than of A. alabamense CFUs was cultured from soils with moderate temperatures (20 to 40°C). This finding is consistent with the axenic growth temperature ranges of these organisms, as A. alabamense did
not grow axenically at 25°C, whereas D. constricta did
(Table 1). The mesophilic organism Penicillium species 4 was
most prevalent at temperatures below 20°C, whereas another mesophilic
species, C. elegans, was frequently cultured from soils with
temperatures between 20 and 40°C. Again, the laboratory growth
temperature optima of the organisms (Table 1) were correlated with the
frequencies at different soil temperatures. The numbers of CFUs of
other mesophilic and thermotolerant species were similarly consistent
with the axenic growth temperature ranges of the organisms.
Although none of the fungi listed in Table 1 is a new species, fungi in
Yellowstone National Park geothermal soils may have diverged from their
nongeothermal soil counterparts. The adaptive strategies of these fungi
may include the development of mycelia, spores, or sclerotia that
tolerate prolonged exposure to elevated temperatures and/or a wide
range of pH values. For example, one unidentified isolate in this study
was obtained from a decaying log (core 11) that was as hot as 107°C.
However, this fungus probably survived but did not grow at high
temperatures, since the upper limit for eukaryotic growth is thought to
be ~60°C. Although slides buried at our site revealed that there
was evidence of hyphal growth in geothermal soils, we did not identify
which species grew and which species merely survived at higher soil
temperatures. We cultured all of the species listed in Table 1 from
soils whose temperatures were outside the growth ranges of the
organisms, but additional experiments are needed to discern the
temperature tolerance and adaptive mechanism(s) of these fungi.
Many other fungal species could be present in the geothermal soils
examined, but they were not detected by traditional culturing methods
(19). For example, species present in very low numbers were
not detected because of the soil dilutions necessary to obtain countable CFUs. We also observed more total CFUs when suspensions were
diluted so that they yielded fewer CFUs per plate. This finding indicates that some species may inhibit the growth of other species in
more crowded culture conditions. Additional studies performed with
molecular-biology-based techniques (22), such as PCR
followed by denaturing gradient gel electrophoresis, should reveal
whether culturable fungal species are, indeed, the predominant fungal species in these soils and whether these soils harbor uncultured fungi
which can provide a more accurate assessment of the biodiversity of
this unique ecosystem.
 |
ACKNOWLEDGMENTS |
We thank R. Lindstrom and the National Park Service for providing
housing, information, and library facilities during this research and
Richard Stout for introducing us to geothermal soils and thermotolerant
plants in Yellowstone National Park. This project was made possible by
the permission, cooperation, and assistance of the National Park
Service and was carried out under the guidelines for research in
Yellowstone National Park.
This research was supported in part by a joint NSF-DOE-USDA grant
(R.J.R. was one of the principal investigators), by the U.S.
Geological Survey (R.J.R. was the principal investigator), and by
a U.S. Army Research Office grant (J.M.H. was the principal investigator).
 |
FOOTNOTES |
*
Corresponding author. Mailing address: Microbiology
Department, 109 Lewis Hall, Montana State University, P.O. Box 173520, Bozeman, MT 59717-3250. Phone: (406) 994-4690. Fax: (406) 994-4926. E-mail: jhenson{at}montana.edu.
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Applied and Environmental Microbiology, December 1999, p. 5193-5197, Vol. 65, No. 12
0099-2240/99/$04.00+0
Copyright © 1999, American Society for Microbiology. All rights reserved.
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