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Endolithic photosynthetic communitieswithinancient and recenttravertine deposits inYellowstoneNational ParkTracy B. Norris & Richard W. Castenholz
Center for Ecology and Evolutionary Biology, University of Oregon, Eugene, OR, USA
Correspondence: Tracy B. Norris, Center for
Ecology and Evolutionary Biology, University
of Oregon, Eugene, OR 97403, USA.
Tel.:11 541 7298815; fax: 11 541 3462364;
e-mail: [email protected]
Received 12 October 2005; revised 10 February
2006; accepted 12 February 2006.
First published online 12 May 2006.
DOI:10.1111/j.1574-6941.2006.00134.x
Editor: Gary King
Keywords
endolithic; photo-microbial community;
cyanobacteria; travertine; Yellowstone National
Park.
Abstract
Molecular and culture based methods were used to survey endolithic, photosyn-
thetic communities from hot spring-formed travertine rocks of various ages,
ranging fromo10 to greater than 300 000 years. Much of this travertine contained
a 1–3-mm-thick greenish band composed mainly of cyanobacteria 1–5 mm below
the rock surface. The travertine rocks experienced desiccation in summer and
freezing in winter. A total of 83 environmental 16S rRNA gene sequences were
obtained from clone libraries and denaturing gradient gel electrophoresis. Small
subunit rRNA gene sequences and cell morphology were determined for 36
cyanobacterial culture isolates from these samples. Phylogenetic analysis showed
that the 16S rRNA gene sequences fell into 15 distinct clusters, including several
novel lineages of cyanobacteria.
Introduction
Extremophilic microorganisms are by definition those that
live at the outer limits of the physical parameters that define
the boundaries for life on Earth. One niche that encompasses
a number of extreme physical stresses is the endolithic
environment of rocks of hot and cold deserts. Here we are
using the term endolithic as defined by Friedmann et al.
(1967) as meaning ‘occupying a space within the rock tissue
without an apparent connection to the outer rock surface’, in
contrast to chasmolithic (living in fissures in rocks). The
term cryptoendolithic is used by some authors with the same
meaning as the more general term endolithic (e.g. Sun &
Friedmann, 1999; Hughes & Lawley, 2003). In such environ-
ments microorganisms must endure extremes of temperature
(often including freezing), desiccation, low nutrient supply,
and low photon flux. In most regions these communities are
composed primarily of photosynthetic microorganisms
(Friedmann, 1982; Bell, 1993; Gerrath et al., 1995; Sigler
et al., 2003). Cyanobacteria are commonly the principal
phototrophic members of endolithic communities. However,
these communities include heterotrophic bacteria and often
fungi, protolichens, and micro-algae. Studies of hot desert
and Antarctic endolithic communities have demonstrated
that, in general, endolithic communities are of low species
diversity (Friedmann, 1982; Bell, 1993; Nienow & Fried-
mann, 1993; Wessels & Budel, 1995), especially compared
with soil crusts that are subject to similar extremes but are
generally composed of more complex consortia of micro-
organisms (Garcia-Pichel et al., 2001; Redfield et al., 2002).
Many endolithic communities are characterized by a
1–4 mm thick greenish layer of phototrophs that commonly
occurs 1–5 mm below the upper surface of the rock they
inhabit (Fig. 1); however, the depth may vary considerably,
and in some cases the visible green layer may be spread over
more than 5 mm. The depth is presumably dependent on the
penetrance of light mainly (Matthes et al., 2001). Since
endolithic microorganisms inhabit the spaces between the
mineral particles and crystals they are usually found in
relatively porous and somewhat translucent rocks such as
limestone, sandstone, gypsum and dolomite. In addition to
these periodically dry environments, a thermal, active endo-
lithic community has been reported in extremely acidic, but
moist, siliceous sinter and dominated by unicellular red algae
of the order Cyanidiales (Gross et al., 1998; Walker et al., 2005).
Endolithic microorganisms, in general, probably favor
this environment as it allows them to escape competition by
occupying a niche that is uninhabitable for most other
microorganisms, although growth may be extremely slow
(Sun & Friedmann, 1999). Another possible advantage to
FEMS Microbiol Ecol 57 (2006) 470–483c� 2006 Federation of European Microbiological SocietiesPublished by Blackwell Publishing Ltd. All rights reserved
living in the rock interior is that it would provide an escape
from harsher conditions at the surface, such as high solar
irradiance (including UV radiation), rapid desiccation, and
abrasion by wind-borne elements. The endolithic environ-
ment may act as a refugium, where light, moisture and
nutrient availability form a fragile but sufficient balance for
life. The combination of these three factors surely dictates
the depth to which endolithic communities live within the
rocks.
Although much early work on endolithic communities
has stressed their prevalence in extremely hot and cold
deserts (Friedmann et al., 1967; Friedmann & Ocampo-
Friedmann, 1984), these types of communities are appar-
ently distributed globally and often in temperate climates as
well (e.g. Gerrath et al., 1995; Van Thielen & Garbary, 1999).
However, the ecology of these communities and their species
composition in temperate climates have rarely been studied.
Ancient and recent travertine deposited by hot springs in
the temperate climate of Yellowstone National Park, Wyom-
ing, USA, harbor an apparently unique endolithic commu-
nity. Travertine is a form of calcium carbonate (CaCO3)
deposited by calcareous springs or rivers, but with numer-
ous variations in porosity, crystal forms, and mineralogy
even within the Mammoth area of Yellowstone (see Fouke
et al., 2000). The July high temperature in this area averages
about 28 1C and often exceeds 34 1C but with nighttime lows
of �4–10 1C and a mean monthly precipitation of 2.0 cm.
The January mean low temperature is �15 1C, with ex-
tremes of �45 1C. Relative humidity values in summer may
commonly drop as low as 14%.
The goal of this work is to provide an initial survey of the
photosynthetic microorganisms that inhabit this extreme
environment. Much of the previous work on endolithic
communities has entailed only microscopy and relatively
little cultivation (Friedmann, 1982) or cultivation without
molecular evaluation, thus revealing mostly morphotypic
information. Only recently have molecular techniques been
applied to describe the community diversity of endolithic
communities (Sigler et al., 2003; Taton et al., 2003; de la
Torre et al., 2003; Walker et al., 2005). The present study uses
molecular methods as well as morphotypic characterization
of culture isolates to survey the taxonomic composition. We
believe studies of endolithic microbial communities are key
areas of investigation in furthering the exploration of past
life on Mars and, most certainly, exploration of early life on
the terrestrial Earth that may have occurred as early as
2.6� 109 years before the present (Watanabe et al., 2000).
Materials and methods
Field site and collections
Dry travertine rock samples were collected from six different
sites in or near the northwestern quadrant of Yellowstone
National Park. Replicate samples for molecular work and
culture isolation were collected in 2002. Samples for mole-
cular work were frozen at �20 1C upon returning to the lab
and dry samples to be used for culture isolations were stored
in plastic containers at ambient temperature in the dark.
Additional collections for cultures were made in 2003. All of
the sample sites are located in the Mammoth Upper Terraces
of Yellowstone National Park, except for the ‘Hoodoos’,
which comprise the travertine rockfall of Terrace Mountain
(above the Mammoth Upper Terraces), formed over 350 000
Fig. 1. Photograph of the Hoodoos area near
Mammoth Springs in Yellowstone National Park,
one of six sampling sites used in this study. The
rockfall in the foreground has come from Terrace
Mountain in the background, an ancient traver-
tine terrace formed over 300 000 yr BP. Inset:
close-up of travertine rock sample from the rock-
fall, demonstrating a subsurface green layer of
endolithic phototrophs, the appearance of which
is typical of the majority of endolithic bands
examined from various sites.
FEMS Microbiol Ecol 57 (2006) 470–483 c� 2006 Federation of European Microbiological SocietiesPublished by Blackwell Publishing Ltd. All rights reserved
471Endolithic photosynthetic microorganisms
years ago (Sturchio et al., 1994), and the ancient Gardiner
Lower Terraces, which are above the city of Gardiner,
Montana, and outside the boundaries of Yellowstone Na-
tional Park. The global positioning system (GPS) coordi-
nates for each collection site are as follows:
(1) Narrow Gauge Lower Terrace (NGL) 44158016600N
Lat., 110142062500W. Long.
(2) Narrow Gauge Upper Terrace (NGH) 44158018800N
Lat., 110142060900W. Long.
(3) Painted Pool Terrace (PAP) 44157090500N Lat., 1101
42080700W. Long.
(4) Narrow Gauge Ancient Terrace (NGA)
44158014800N Lat., 110142056500W. Long.
(5) Gardiner Lower Terrace (GLT) 45102008000N Lat.,
110141048500W. Long.
(6) Hoodoos (HDO) 44156065200N Lat., 110143004400W.
Long.
Abbreviations following site names were used for naming
the environmental clones and denaturing gradient gel
electrophoresis (DGGE) bands. The sampling locations
included travertine of various depositional ages.
DNA purification
DNA purification from travertine samples was done using a
modification of the method of More et al. (1994). The green
layer occurring 1–2 mm beneath the surface of travertine
samples was removed using a sterilized metal file and razor
blade, after abrasive removal of the upper few millimeters of
rock surface. Two aliquots of �1 g filings were collected for
each sample and transferred to 2 mL screw-cap microcen-
trifuge tubes. Next, 0.75 g of 0.1 mm diameter zirconia/silica
beads (BioSpec Products, Bartlesville, OK) were added to
each tube along with 600mL 120 mM sodium phosphate
(pH 8.0) and 400mL lysis buffer (10% sodium dodecyl
sulfate, 0.5 M Tris-HCl (pH 8.0) and 0.1 M NaCl). Cells
were lysed by shaking for 3 min at high speed on a Mini-
Beadbeater (BioSpec Products, Bartlesville, OK) and then
centrifuged for 3 min at 13 000 g. Supernatant (700mL) was
collected and DNA was precipitated on ice using 2 : 5 (v/v) of
7.5 M ammonium acetate and then centrifuged again. The
supernatant was collected and the DNA was isopropanol
precipitated. Finally, the pellet was washed with 70% ethanol
(�20 1C), air dried and resuspended in 100 mL of 10 mM
Tris (pH 8.0).
Clone library construction
PCR amplification from total community DNA was used for
clone library construction and DGGE. The cyanobacterial
specific primers CYA106F and CYA781R (Nubel et al., 1997)
were used to amplify 16S rRNA gene sequences, resulting in
a product of approximately 675 bp. Each PCR reaction
contained 1.5 mM MgCl2, 0.2 mM dNTPs, 0.5mM of each
primer, approximately 10 ng of template DNA, 0.1 mg mL�1
bovine serum albumin, 2.5 U Taq polymerase and 1�PCR
buffer (Promega, Madison, WI) in a total volume of 50mL.
The PCR amplification cycle was as follows: initial denatura-
tion for 5 min at 95 1C, then 30 cycles of 1 min of denatura-
tion at 94 1C, 1 min annealing at 60 1C, and 1 min extension
at 72 1C followed by a final extension of 7 min at 72 1C. PCR
amplicons were cloned into the PCR 2.1 cloning vector
using the TOPO TA cloning kit (Invitrogen, Carlsbad, CA).
Clone libraries of 60–100 clones were created for each site in
the study. For each library, 12–15 random clones were
selected for re-amplification of vector inserts and commer-
cial sequencing using the cyanobacteria-specific primers
CYA359F and CYA781R (Nubel et al., 1997). Sequenced
fragments had a length of approximately 380 bp. A GenBank
BLAST (basic local alignment search tool) search was
performed for each sequence to identify the nearest relatives.
The environmental clone sequences from this study were
submitted under the GenBank accession numbers
AY790390–AY790464.
DGGE
For DGGE analysis, cyanobacterial 16S rRNA gene se-
quences were amplified from total community DNA using
the cyanobacterial specific primers CYA359F and CYA781R.
DGGE analysis was performed using a D-Code system (Bio-
Rad, Hercules, CA) essentially as described by Muyzer et al.
(1993). Reamplified PCR products from bands were se-
quenced commercially and a BLAST search of the GenBank
database was done to identify species or strains of nearest
relatives. The sequences of DGGE bands from this study
were submitted to the GenBank database under the acces-
sion numbers AY790465–AY790472.
Culture methods
Rock samples that were used for molecular analysis were
also used for culture isolations of phototrophs. Fine parti-
culate samples of the green layer in the travertine samples
were removed with sterile file and blade as in the molecular
analyses. Most culture isolates were obtained by the dilution
to extinction method, although direct enrichments were also
used. A small portion of the filings (�0.5 g) was used to
initiate a dilution series in BG11 medium, or in some cases,
ND medium that lacked combined nitrogen (Castenholz,
1988). Cultures of filamentous morphotypes were isolated
from final dilution enrichments by transfer to agar plates.
Filaments (trichomes) were allowed to migrate or grow out
from the source; then single trichomes (clones) on minute
agar blocks were removed with watchmaker’s forceps under
a dissecting microscope, and transferred to liquid medium
in sterile tubes (Castenholz, 1988). To obtain non-filamen-
tous types, the final enrichment was streak-plated and single
FEMS Microbiol Ecol 57 (2006) 470–483c� 2006 Federation of European Microbiological SocietiesPublished by Blackwell Publishing Ltd. All rights reserved
472 T.B. Norris & R.W. Castenholz
colonies were transferred to liquid medium. In most cases,
these cultures were replated for greater assurance of clon-
ality. In many cases, axenic cultures resulted, but the
presence of heterotrophic bacteria in some cultures still
allowed molecular cyanobacterial identification with the
use of the cyanobacteria-specific primers CYA359F and
CYA781R. Culture isolates of green algal strains were
sequenced using the 18S rRNA gene primers NS1 and NS2
(White et al., 1990), yielding a 555 bp product. The culture
isolate sequences from this study were submitted under the
GenBank accession numbers AY790836–AY790874.
Phylogenetic analysis
The 16S rRNA gene sequences were analyzed for phyloge-
netic affiliation using the BLAST (Altschul et al., 1997)
available on the NCBI website (http://www.ncbi.nlm.nih.-
gov/). The aligned SSU rRNA gene sequences of six known
cyanobacterial relatives were exported from the ARB pro-
gram (Ludwig et al., 2004) into CLUSTAL X (Thompson et al.,
1997) and used as a guide file for profile alignment of both
sequences from this study and additional cyanobacterial
sequences from GenBank. Alignments of partial 16S rRNA
gene sequences corresponded to Escherichia coli sequence
positions 412–807. The program PAUP 4.0b10 was used to
construct a distance tree by the neighbor joining method
(Swofford, 2001). The Kimura two-parameter algorithm was
used with pairwise deletion of gaps and missing data.
Bootstrap values from 1000 resamplings were calculated
and Chloroflexus aurantiacus DSM 637 was used as the
outgroup. The tree includes all of the environmental clones,
DGGE bands and culture sequences from this study as well
as some of the nearest relatives determined by BLAST.
Phylotypes that included more than one sequence, defined
by groups of sequences with greater than 97.5% sequence
identity (i.e. operational taxonomic units, OTUs), were
represented by a single sequence from that group for tree
construction. Parsimony was used as an alternate method of
tree construction to check for robustness of sequence
clusters.
Microscopy
Collections and cultures were examined using an American
Optical research microscope with phase contrast �40 and
�100 objectives. The photomicrography was with a Zeiss
Axioplan microscope, using a �100 plan-neofluor objective
with Nomarski DIC. Photo-images were made with a Nikon
Coolpix 990 digital camera. The taxonomic descriptions and
tentative genus names used in Bergey’s Manual of Systema-
tic Bacteriology (Boone & Castenholz, 2001) were used for
morphotypic identifications.
Results
Field collections
The greenish bands of about 1–2 mm thickness were usually
1–4 mm below the upper surface of the rocks and visible,
especially when the upper surfaces were light colored and
not covered with crustose lichens. Most of the samples were
quite similar to that shown in Fig. 1 (inset) but, in some
cases, vertical fracture lines occurred in the rocks that
apparently allowed light penetration and water to greater
depths (e.g. 5–10 mm). Such communities are termed
chasmolithic. If the rocks were extended as overhanging
ledges, the endolithic green layer was also apparent near the
lower surface. There was no visual evidence in this study of
microorganisms boring into the rocks. Although no quanti-
tative measurements were made, the youngest rocks were the
most porous and easily breakable, whereas the older rocks
were usually of significantly greater hardness. The collec-
tions were made mainly in mid summer. During a typical
warm summer day (25 to 430 1C) with 14–18% relative
humidity immediately above most of the sites, the water
content of the rocks was less than 3%, and even lower
(0.4%) in less porous rocks of the Hoodoos. In one sample
of relatively non-porous travertine, with a maximum noon-
time rock surface temperature of 435 1C, a temperature of
28 1C was reached at 5 mm depth by c. 14:00 hours and
minimum nighttime temperature of 10–12 1C by
04:00 hours AM (Jon Wraith, pers. comm.). Winter tem-
peratures are normally below 0 1C and often plunge to
�30 1C or lower. Only one of the sites was possibly influ-
enced by water from a neighboring active spring. Narrow
Gauge Lower Terrace (NGL) had experienced water flow 3–4
years prior to collecting, and this more porous and delicate
deposit retained 8–20% water, probably for several days.
Samples were collected from various compass faces of the
travertine deposits. Although not quantified, northerly or
more shaded exposures appeared to harbor an endolithic
green band more frequently and more prominently than in
other exposures.
Analysis of community diversity using DGGE
DGGE community profiles of cyanobacterial 16S rRNA gene
sequences for each site were generated (data not shown).
The profiles for each community were characterized by
a few (two to seven) distinct bands over a background of
many more poorly resolved, indistinct bands. By visual
inspection, it appears that the communities may share some
common phylotypes, as evidenced by the equidistant migra-
tion of bands from different profiles. Each profile also
contained some uniquely migrating bands as well. BLAST
search results for the sequences that were retrieved from
FEMS Microbiol Ecol 57 (2006) 470–483 c� 2006 Federation of European Microbiological SocietiesPublished by Blackwell Publishing Ltd. All rights reserved
473Endolithic photosynthetic microorganisms
DGGE bands are included in Table 1. In most cases the
nearest relative was an uncultured (and usually unidenti-
fied) cyanobacterium or occasionally a chloroplast of a
green alga or moss from another study.
Clone library analysis
A total of 75 cyanobacterial 16S rRNA gene sequences were
determined from the clone libraries, which included 12–15
clones from each site. The clones were divided into
phylotype groups (Table 1). We have defined members of a
phylotype group as sequences with greater than 97.5%
sequence identity to each other (Stackebrandt & Goebel,
1994), although this does not guarantee species or
genus identity. The combined sequence data for clones and
DGGE bands from all sites can be divided into 28 phylotype
‘groups’, of which 15 have two or more sequences.
An additional 13 phylotypes are each represented by a
single sequence. Within the phylotype groups there were
some sequences that were 100% identical (over �380 bp)
to GenBank database sequences. From the consoli-
dated clone library there were eight sequences that were
retrieved more than once, each of these appearing two or
three times. A BLAST search analysis revealed that 16 of
the 28 phylotype groups have a nearest relative in the
GenBank database with sequence identity of 97% or greater.
In almost all cases, the nearest relative was an un-
cultivated cyanobacterial sequence. The sources of these
nearest relatives were wide ranging environments that
included hot and cold deserts as well as other cryptoendo-
lithic sites.
The two largest phylotype groups dominating the clone
library were phylotypes C (12 clones) and E (13 clones11
DGGE band). These two phylotype groups were 98–99%
identical to uncultivated cyanobacterial clone sequences
originating from soil crusts of the Colorado Plateau (Red-
field et al., 2002; Yeager et al., 2004). Group C included
sequences from Gardiner Lower Terraces (GLT), Narrow
Gauge Upper Terrace and Painted Pool Terrace (PAP).
Group E included sequences from the same sites in addition
to Narrow Gauge Ancient Terrace (NGA). Another major
phylotype was group I (6 clones, 1 DGGE band, 1 culture
isolate), which was distantly related to a Plectonema sp. F3
strain (94% identity) and therefore may represent a novel
cyanobacterial lineage. Interestingly, group I is a cluster
composed entirely of sequences from Narrow Gauge Lower
Terrace (NGL).
In addition to cyanobacterial sequences, our clone library
recovered sequences of representatives of moss and green
algal lineages. Phylotype group G (4 clones, 1 DGGE band)
is 95% identical to the plastid sequence of the green alga
Koliella sempervirens. All of the sequences in this group were
recovered from the Hoodoos (HDO). Mosses (epilithic)
are also represented in the clone library by phylotype
group H (5 clones, 1 DGGE band), which shares 99%
identity to a plastid sequence of the moss Physcomitrella
patens. Sequences in this phylotype group originated from
both the Hoodoos (HDO) and the Gardiner Lower Terrace
(GLT).
Isolation of clonal cultures
In addition to molecular methods, culture isolation was
used to identify members of the phototrophic endolithic
communities. A straightforward approach of dilution to
extinction and direct enrichment in BG11 medium (or ND
medium) was used to isolate cyanobacterial strains from
each of the sites. The most apparent result of cultivation
is that the majority of isolates are filamentous cyanobacteria.
Subsequent to clonal isolation, the 16S rRNA gene sequence
was determined for 36 isolates of cyanobacteria and
three green algal isolates (Table 2). Of the 36 cyanobacterial
culture sequences, 27 are unique; the rest represent identical
isolates that were retrieved more than once. Duplicate
isolates are included in Table 2 to indicate the frequency
of retrieval. The Table also includes four culture isolates
from three additional endolithic sites in Yellowstone Na-
tional Park for which clone library analyses were not
performed.
In general, the cyanobacterial and green algal isolates have
high similarity to other cultivated strains. For the 27 unique
cyanobacterial isolates, 14 have nearest BLAST search rela-
tives of 97–100% identity to cultivated cyanobacterial
strains. The sequence of one isolate from Narrow Gauge
Lower Terrace (NGL) was 100% identical to the sequence of
Cyanobium gracile, a unicellular cyanobacterium with a
global distribution in freshwater lakes and brackish seas
(Crosbie et al., 2003). Of the other 13 strains with close
cultivated relatives, 10 are related to species of the genus
Leptolyngbya and three to Nostoc species. Only two of the
cultures, CCMEE 6048 and CCMEE 6034, had nearest
relatives that were environmental clones. Seven of the
unique culture sequences have 94% or less identity to
database sequences and may represent novel lineages. These
cultures encompassed the less common morphotypes culti-
vated in this study, including the genera Synechococcus,
Chroococcidiopsis, Gloeocapsa, and Schizothrix. In addition
to cyanobacteria, we also retrieved two green algal strains:
CCMEE 6027, with 99% identity to Bracteacoccus aerius,
and CCMEE 6038/6039, with 99% identity to Paradoxia
multiseta.
The majority of the culture sequences could not be
assigned to phylotype groups. The 16S rRNA gene sequences
from the culture isolates that could be assigned to phylotype
groups from environmental clones or DGGE bands are
included in Table 1 and are also listed in bold in Table 2.
FEMS Microbiol Ecol 57 (2006) 470–483c� 2006 Federation of European Microbiological SocietiesPublished by Blackwell Publishing Ltd. All rights reserved
474 T.B. Norris & R.W. Castenholz
Table 1. Summary of rRNA gene sequence data combined from clone libraries, DGGE and cultures
Phylotype
group� Sequenced clones, DGGE bands and culturesw Nearest GenBank relative % Identity
A (3) NGA2, NGA10, NGH2 Microcoleus steenstrupii clone 177-7A (AF355395),
Uncultured bacterium, quartz pebbles in the
Southern Mojave Desert (AF493857)
93
B (2) NGL2, NGL11 Cyanobacterium sp. MBIC10216 (AB058249) 98
C (12) GLT9, GLT1, GLT5, GLT7, GLT12, GLT15, NGH14,
GLT8, PAP4, GLT13, GLT6, PAP6
Uncultured soil crust cyanobacterium clone lichen23,
Colorado Plateau (AF428529)
98
D (2) PAP7, PAP3 Uncultured soil crust cyanobacterium clone lichen37,
Colorado Plateau (AF428542)
97
E (14) (PAP10, PAP12, PAP1band), GLT10, (NGH5, NGH6),
NGH11, PAP5, (PAP9, PAP11), NGA3, NGA11, PAP8,
PAP2
Uncultured bacterium clone CD14, Colorado Plateau
or Chihuahuan Desert (AY360997)
99
F (5) (NGH4, HDO4, HDO2band), HDO2, NGA6 Uncultured cyanobacterium DGGE gel band B15,
Swiss dolomite (AY153458)
99
G (5) HDO5, (HDO3, HDO11, HDO15), HDO1band Koliella sempervirens plastid (AF278747) [green alga] 95
H (6) (HDO8, HDO14, HDO3band), GLT11, GLT14, HDO7 Physcomitrella patens plastid (AP005672) [moss] 99
I (8) (NGL9, NGL10, NGL5band, CCMEE6011), NGL1,
NGL3, NGL4, NGL12
Plectonema sp. F3 (AF091110) 94
J (9) (NGL5, CCMEE6004, CCMEE6007), NGL13,
(CCMEE6024, CCMEE6021), (CCMEE6035,
CCMEE6036, CCMEE6037)
Leptolyngbya sp. CNP1-Z1-C2 (AY239601) 99
K (3) (NGL7, NGL8), NGL4band Uncultured cyanobacterium isolate DGGE band Lb,
petroleum polluted microbial mat (AF423349)
99
L (2) NGH1, NGH9 Uncultured cyanobacterium DGGE gel band B15,
Swiss dolomite (AY153458)
95
M (2) GLT4, NGA7 Uncultured soil crust cyanobacterium clone lichen36,
Colorado Plateau (AF428541)
94
N (2) NGH15, NGA9 Uncultured soil crust cyanobacterium clone lichen36,
Colorado Plateau (AF428541)
97
O (3) NGH7, NGA4, NGH10 Uncultured soil crust cyanobacterium clone lichen5,
Colorado Plateau (AF428511)
99
P NGL2band Nostoc sp. pcA (AJ437559) 99
Q NGL3band Uncultured Antarctic cyanobacterium Fr132
(AY151730)
99
R NGH3 Uncultured soil crust cyanobacterium clone lichen5,
Colorado Plateau (AF428511)
97
S NGH8 Uncultured bacterium clone CD14, Colorado Plateau
or Chihuahuan Desert (AY360997)
94
T NGH12 Uncultured bacterium clone 1790-2, Hawaiian
volcanic deposit (AY425770)
96
U PAP1 Uncultured soil crust cyanobacterium clone lichen36,
Colorado Plateau (AF428541)
97
V NGA1 Uncultured soil crust cyanobacterium clone lichen37,
Colorado Plateau (AF428542)
94
W NGA5 Uncultured soil crust cyanobacterium clone lichen21,
Colorado Plateau (AF428527)
96
X NGA8 Uncultured cyanobacterium isolate DGGE gel band
B3-14, Swiss dolomite (AY153452)
97
Y NGA12 Uncultured cyanobacterium DGGE gel band B15,
Swiss dolomite (AY153458)
97
Z HDO1 Uncultured soil crust cyanobacterium clone lichen21,
Colorado Plateau (AF428527)
94
AA HDO10 Koliella sempervirens plastid (AF278747) [green alga] 94
BB HDO12 Acaryochloris sp. Awaji-1 (AB112435) 93
�Number of sequences of each phylotype indicated in parentheses.wIdentical sequences are enclosed in parentheses.
DGGE, denaturing gradient gel electrophoresis.
FEMS Microbiol Ecol 57 (2006) 470–483 c� 2006 Federation of European Microbiological SocietiesPublished by Blackwell Publishing Ltd. All rights reserved
475Endolithic photosynthetic microorganisms
Table 2. Culture isolates retrieved from cryptoendolithic travertine communities
Culture isolate
CCMEE number Source Accession number Nearest GenBank relative%Identity Morphotype
6004, 6007� Narrow Gauge Lower Terrace(NGL)
AY790836, AY790837 Leptolyngbya sp. CNP1-Z1-C2(AY239601)
99 Leptolyngbya
6011 Narrow Gauge Lower Terrace(NGL)
AY790838 Plectonema sp. F3 (AF091110) 94 Leptolyngbya
6012 Narrow Gauge Lower Terrace(NGL)
AY790839 Cyanobium gracile PCC6307(AF001477)
100 Cyanobium
6105 Narrow Gauge Lower Terrace(NGL)
AY790854 Nostoc sp. strain NIVA-CYA 124(Z82776)
99 Nostoc
6109 Narrow Gauge Lower Terrace(NGL)
AY790856 Lyngbya aestuarii kopara-LY(AJ621838)
92 Synechococcus
6132 Narrow Gauge Lower Terrace(NGL)
AY790866 Oscillatoriales cyanobacteriumIL-9.1 (AF401743)
94 Leptolyngbya
6021, 6024 Narrow Gauge Upper Terrace(NGH)
AY790840, AY790841 Leptolyngbya PCC7104(AB039012)
97 Leptolyngbya
6026 Narrow Gauge Upper Terrace(NGH)
AY790842 LPP-group MBIC10597 (AB058267) 97 Leptolyngbya
6108, 6117 Narrow Gauge Upper Terrace(NGH)
AY790855, AY790871 Nostocales cyanobacteriumIL-15.1 (AF401744)
100 Nostoc
6122 Narrow Gauge Upper Terrace(NGH)
AY790863 Cyanothece sp. PCC 7424(AF132932)
93 Synechocystis
6133 Narrow Gauge Upper Terrace(NGH)
AY790867 Leptolyngbya sp. CNP1-Z1-C2(AY239601)
98 Leptolyngbya
6048 Painted Pool (PAP) AY790848 Uncultured bacterium clone CD14(AY360997), Colorado Plateau orChihuahuan Desert
95 Chroococcidiopsis
6104 Painted Pool (PAP) AY790853 Nostoc commune (AB094352) 99 Nostoc6111 Painted Pool (PAP) AY790858 Oscillatoriales cyanobacterium
IL-9.1 (AF401743)92 Leptolyngbya
6119 Painted Pool (PAP) AY790861 Leptolyngbya sp. SV1-MK-52(AY239604)
99 Leptolyngbya
6124 Painted Pool (PAP) AY790864 Leptolyngbya sp. SV1-MK-49(AY239605)
97 Leptolyngbya
6028 Narrow Gauge Ancient Terrace(NGA)
AY790843 Phormidium autumnale(AF218371)
97 Leptolyngbya
6034 Narrow Gauge Ancient Terrace(NGA)
AY790844 Uncultured bacterium Tui1-3 16S(AF353281), acid mine drainagesystem in New Zealand
97 Leptolyngbya
6027w Narrow Gauge Ancient Terrace(NGA)
AY790872 Bracteacoccus aerius (U63101)[green alga]
99 Bracteacoccus
6125 Narrow Gauge Ancient Terrace(NGA)
AY790865 Uncultured bacterium clone CD31(AY361002)
99 Leptolyngbya
6058 Gardiner Lower Terrace (GLT) AY790852 Gloeocapsa sp. PCC 73106(AF132784)
96 Gloeocapsa
6130, 6131/6120
Gardiner Lower Terrace (GLT)/ AY790868, AY790869, Leptolyngbya sp. SEV5-5-C6(AY239591)
92 Schizothrix
Painted Pool (PAP) AY7908626035, 6036,6037
Hoodoos (HDO) AY790845, AY790846,AY790847
Leptolyngbya PCC7104(AB039012)
98 Leptolyngbya
6038, 6039w Hoodoos (HDO) AY790873, AY790874 Paradoxia multiseta (AY422078)[green alga]
99 Chlorella
6110, 6126 Hoodoos (HDO) AY790857, AY790870 Nostocales cyanobacteriumIL-15.1 (AF401744)
96 Nostoc
6116 Hoodoos (HDO) AY790860 Oscillatoriales cyanobacteriumIL-9.1 (AF401743)
93 Leptolyngbya
6112, 6056 Rabbit Creek Terracez AY790851, AY790859 Phormidium autumnale(AF218371)
97 Leptolyngbya
6052 New Mound AY790849 Uncultured cyanobacteriumisolate DGGE gel band R2A(AY354465)
99 Leptolyngbya
6054 Reave’s Mound AY790850 Leptolyngbya sp. CNP1-B3-C9 16S(AY239600)
98 Leptolyngbya
�Sequences in bold belong to phylotype clusters that include clones and/or denaturing gradient gel electrophoresis bands.w18S rRNA gene sequences.zSilica sinter terrace.
FEMS Microbiol Ecol 57 (2006) 470–483c� 2006 Federation of European Microbiological SocietiesPublished by Blackwell Publishing Ltd. All rights reserved
476 T.B. Norris & R.W. Castenholz
Phylotype group J includes the most culture isolates, with
seven isolates retrieved from the Narrow Gauge Lower
Terrace, Hoodoos, and Narrow Gauge Upper Terrace. Phy-
lotype group J also includes two environmental clones from
the Narrow Gauge Lower Terrace; one with 100% identity to
isolates CCMEE 6004/6007. These sequences are 99% iden-
tical to Leptolyngbya sp. CNP1-Z1-C2, and microscope
observations confirm a Leptolyngbya morphotype for these
strains (Fig. 2). Phylotype I is the only other group with
overlap between environmental clones and cultures. Within
this group the culture CCMEE 6011 has 100% identity to
two environmental clone sequences and a DGGE band. This
phylotype group is a distant relative (94% identity) of the
filamentous cyanobacterium Plectonema sp. F3. There were
23 other culture isolate sequences that were unique and did
not fall into phylotype groups composed of multiple
sequences.
Morphotypic diversity
Figure 2 displays photomicrographs of selected culture
isolates that are included in Table 2 and in the phylogenetic
tree (Fig. 3). The nearest GenBank relative is indicated in
Table 2. The cyanobacteria shown in panels a, b, c, and f have
close morphological similarities to the genera to which they
are most closely related by sequence identity [i.e. Cyanobium
(CCMEE 6012), Nostoc (CCMEE 6104, CCMEE 6110) and
Gloeocapsa (CCMEE 6058)]. The filamentous cyanobacteria
shown in panels g, i, and j all resemble their closest
phylotypes with 97–99% identities, the artificial ‘form-
genus’ Leptolyngbya (Fig. 2). The Leptolyngbya-type in panel
h (CCMEE 6132), however, has only a 94% identity to a
loosely named member of the order Oscillatoriales (which
includes Leptolyngbya) (Table 2, Fig. 3). Panel e displays a
unicellular (or aggregated unicellular) type with some
10 µm
CCMEE 6012 CCMEE 6104 CCMEE 6110
CCMEE 6048
CCMEE 6122 CCMEE 6058
(a) (b) (c)
(d) (e) (f)
(g) (h) (i)
(j) (k)
CCMEE 6119 CCMEE 6132
CCMEE 6034
CCMEE 6109
CCMEE 6036
Fig. 2. Diversity of selected cyanobacterial
morphotypes in clonal culture isolated from
travertine samples. All photomicrographs are
shown at the same scale (bars = 10mm). Panel a
(CCMEE 6012 Cyanobium gracile); Panel b
(CCMEE 6104) and c (CCMEE 6110) Nostoc-
types); Panel d (CCMEE 6048 Chroococcidiop-
sis-like), Panel e (CCMEE 6122 Synechocystis-
like); Panel f (CCMEE 6058 Gloeocapsa-type);
Panels g, h, i, and j (CCMEE 6119, CCMEE 6132,
CCMEE 6034, and CCMEE 6036 Leptolyngbya-
types); Panel k (CCMEE 6109 Synechococcus-
type).
FEMS Microbiol Ecol 57 (2006) 470–483 c� 2006 Federation of European Microbiological SocietiesPublished by Blackwell Publishing Ltd. All rights reserved
477Endolithic photosynthetic microorganisms
NGH15NGA9PAP1
GLT4NGA7Phylotype C (12)Colorado Plateau soil crust clone lichen 23Phylotype D (2)Mojave desert clone18 (quartz pebbles)
Phylotype E (14)Colorado Plateau soil crust clone CD14
CCMEE6048HDO1
NGA1Colorado Plateau soil crust clone lichen 5
NGH7NGA4
NGH10NGH3
NGA5NGA8
Nostc commune UTEX 584CCMEE6104
NGL2bandNostoc sp. ATCC 53789Nostoc sp. PCC 9709CCMEE6105
CCMEE6108CCMEE6110
Nostoc sp. PCC7120Phylotype B (2)
Cyanobacterium sp. MBIC1021Phylotype A (3)NGH8
Microcoleus steenstrupii clone 177-7AMicrocoleus vaginatus PCC9802
Microcoleus sociatus MPI 96MS.KIDNGH12
Chroococcidiopsis sp. 029 (Negev)Chroococcidiopsis sp. 171 (Antarctica)
Chroococcidiopsis sp. SAG2026Chroococcidiopsis thermalis PCC 7203
NGH1NGH9
HDO12Phylotype F (5)
DGGE gel band B15 (Swiss Dolomite)NGA12
Phylotype G (5)HDO10
Koliella sempervirens plastidPhylotype H (6)
Colorado Plateau soil crust plastid moss35Physcomitrella patens plastid
Phylotype K (3)CCMEE6109
CCMEE6028CCMEE6125CCMEE6034
CCMEE6112Phormidium autumnale
CCMEE6052CCMEE6124
CCMEE6119CCMEE6120
CCMEE6132CCMEE6116CCMEE6111
NGL3bandAntarctic clone Fr132
CCMEE6054Synechocystis sp. PCC 6803
CCMEE6122CCMEE6058
Gloeocapsa sp. PCC73106CCMEE6026
Antarctic clone FBP290Phylotype I (8)
Plectonema sp. F3Phylotype J (9)CCMEE6133Leptolyngbya sp. PCC 7104
Leptolyngbya sp. CNP1-Z1-C2CCMEE6012
Cyanobium gracile PCC 6307Gloeobacter violaceus PCC 7421
Chloroflexus aurantiacus DSM 637
0.01 substitutions/site
I
II
III
IV
V
VI
VII
VIII
IX
X
XI
XII
XIII
XIV
X V
83
97
100
91
87
99
92
100
6692
100
10093
100
99
58
98
100
72
100
87
100
100
Fig. 3. Distance tree based on cyanobacterial 16S rRNA gene sequences from Yellowstone travertine samples. The tree includes 75 environmental
clone sequences (blue), 8 DGGE bands (blue with ‘‘band’’ suffix) and 24 culture isolate sequences (green). Lettered phylotypes (red) represent a
phylotype of sequences with 97.5% or greater sequence identity and correspond to information presented in Table 1 and may include cultures, clones
or DGGE bands or all three. Roman numerals identify sequence clusters discussed in the text. Bootstrap values from 1000 re-samplings are given for
some relevant nodes.
FEMS Microbiol Ecol 57 (2006) 470–483c� 2006 Federation of European Microbiological SocietiesPublished by Blackwell Publishing Ltd. All rights reserved
478 T.B. Norris & R.W. Castenholz
similarity to the morphotype Synechocystis but with only a
93% identity to the nearest relative, the unicellular genus
Cyanothece (Table 2). The cultures shown in panels d and k
are anomalous with respect to nearest relatives. Culture
CCMEE 6048 (panel d) resembles a Chroococcidiopsis mor-
phologically but does not have a close identity to the
previously sequenced members of this genus (Table 2,
Fig. 3). The unicellular rods shown in panel k resemble the
artificial ‘form-genus’ Synechococcus, but the closest relative
(92% identity) is a well-known marine, filamentous cyano-
bacterium (Table 2). However, identities below 97–98%
have little meaning even at the genus level, and reflect the
large gaps in the database at the present time.
Phylogenetic analysis of molecular and culturesequences
A phylogenetic tree constructed by the neighbor-joining
method is shown, using the sequence data from the envir-
onmental clones, DGGE bands and culture isolates (Fig. 3).
Although the basal branching order of the tree is mostly
unsupported, the sequences from this study generally fell
into well-supported sequence clusters at the tips of these
branches and bootstrap values are given where relevant. The
sequences are distributed in 15 distinct sequence clusters or
cyanobacterial lineages. Phylogenetic trees were also con-
structed by Parsimony methods, and although the basal
branching order differed considerably, no differences were
observed in the major sequence clusters (data not shown).
Novel clusters
Clusters I and II are novel cyanobacterial lineages that
comprise the majority of the environmental clone se-
quences. Cluster I is the largest, with 45% of the environ-
mental clone sequences, including the two largest phylotype
groups. There is only one culture isolate sequence (CCMEE
6048) that belongs to this group. Morphologically this
culture resembles a Chroococcidiopsis, but it clearly does not
fall into a clade with other known Chroococcidiopsis isolates.
Cluster I includes environmental clone sequences from
every sample location except Narrow Gauge Lower Terrace
(NGL). An additional five environmental clone sequences
from this study belong to Cluster II. Clusters I and II are
comprised entirely of sequences from this study or GenBank
sequences of environmental clones from desert soil crusts;
they have no close relatives that are cultivated cyanobacterial
species. Cluster VII is another group without close culti-
vated relatives. This cluster is composed of eight environ-
mental clone sequences and one DGGE band. The major
phylotype group in this cluster is 99% identical to a DGGE
band retrieved from a cryptoendolithic environment of
dolomite in Switzerland. Clusters V and VI are small groups
of unique environmental clone sequences that are distantly
related to Microcoleus-like cyanobacteria.
Leptolyngbya clusters
There are four clusters of Leptolyngbya-like sequences, based
on morphology, sequence similarity or both. These four
clusters include a majority of the culture isolates from this
study. Cluster IX is composed entirely of culture isolate
sequences related to Leptolyngbya-like cultures and Phormi-
dium autumnale. Cluster X is a novel lineage that includes
one DGGE band and four culture isolates for which the
closest relative is an uncultivated Antarctic microbial mat
clone. Clusters XIII and XIV are two more distinct Lepto-
lyngbya-like clusters that each include a phylotype group
composed of sequences retrieved by both culture and
molecular methods. Cluster III is a well-supported clade of
heterocystous type sequences that include four culture
isolates of Nostoc-like morphology and one DGGE band.
Other sequences
A few of the 16S rRNA gene sequences do not fall into
distinct clusters. Members of Phylotype group K are closely
related (99% identity) to an environmental clone sequence
from a petroleum-polluted microbial mat, but have no close
cultivated relatives. Two culture isolates from this study,
CCMEE 6109 and CCMEE 6120, also lack close relatives and
represent completely novel culture isolates. Culture CCMEE
6109 is morphologically similar to Synechococcus (Fig. 2,
panel K), and culture CCMEE 6120 has a Schizothrix-like
morphology.
Discussion
Advantages of a multifaceted approach
This study has provided the first multifaceted (polyphasic)
survey of the photosynthetic, travertine-inhabiting endo-
liths in a temperate climate and laid the groundwork for
future environmental and physiological work on these
extreme phototrophs and their habitats. This study includes
whole community and culture molecular analyses, as well as
morphological information on culture isolates. Molecular
methods, such as the cloning of environmental DNA
sequences, are now generally regarded as providing a more
accurate description of microbial community diversity than
culture-based methods. But although molecular methods
are extremely useful tools for genetic inventories, they
provide limited information about the physiology or eco-
logy of community members and so a more ideal tactic is to
use a combination of approaches. The methods employed in
this study retrieved different but complementary informa-
tion about the variety of phototrophs in the travertine
FEMS Microbiol Ecol 57 (2006) 470–483 c� 2006 Federation of European Microbiological SocietiesPublished by Blackwell Publishing Ltd. All rights reserved
479Endolithic photosynthetic microorganisms
habitat. Molecular methods allowed us to propose that
unicellular cyanobacteria may be the most abundant
type of photosynthetic endoliths in this community, infor-
mation that will aid the development of methods used in
future culture isolation attempts. It is important to note that
there is no close similarity at the 16S rRNA gene level
between the photosynthetic microorganisms of these com-
munities and those that occur in active travertine-depositing
hot springs of the Mammoth area of Yellowstone National
Park (Fouke et al., 2003; Pentecost, 2003). None of the
sequences that we obtained from the cultures or travertine
came close to matching the sequences retrieved from the
active springs.
Comments on the methods used
DGGE was found to be of limited usefulness in this
particular study because, rather than being dominated by a
few sequence types, the DGGE profiles were composed of
many unresolved bands, making excision and sequencing
almost impossible. This is not an uncommon issue
and recent literature documents the limitations of DGGE
(Liu & Stahl, 2002). Therefore, we relied more on
environmental clone library construction for our molecular
survey. Almost all of the sequences retrieved in our environ-
mental clone library analysis were closely related to
other environmental clones from analogous environments,
rather than to cultivated strains. There are a few reasons
for the lack of database sequences of cultured strains of
cyanobacteria from environments where desiccation and
freezing tolerance are important for survival. Relatively few
habitats of this type have been surveyed outside of polar or
hot desert regions, and most of the recent studies have been
limited to molecular analyses of bulk DNA from environ-
mental samples [e.g. (Redfield et al., 2002; de la Torre et al.,
2003)]. Another reason is the apparent difficulty of cultiva-
tion of some types. In this study we were only able to isolate
a single culture belonging to sequence cluster I, which
contained 45% of the environmental cyanobacterial
sequences. Morphologically this isolate appears to be similar
to Chroococcidiopsis, but its phylogenetic placement is
clearly outside the clade of other Chroococcidiopsis strains
(Fig. 3, Panel d). Thus, morphological information alone
may be misleading, but the combination of genetic and
morphological data may be of great help in clarifying
taxonomic units.
Culture isolates from this study also complemented
information retrieved by molecular methods. Using stan-
dard cyanobacterial culturing techniques (Castenholz,
1988), we isolated over 100 strains of cyanobacteria. Of the
36 isolates that have been sequenced, 27 are unique strains of
cyanobacteria, four of which belong to phylotype groups
defined by our clone library sequences. Although there was
some overlap between cultures and environmental se-
quences, many of the cultures fall into separate sequence
clusters apart from the environmental sequences. A majority
of these cultures are filamentous cyanobacteria, which are
typically easier to isolate, and, therefore, more frequently
obtained than unicellular types. Culture isolates CCMEE
6004, 6007, 6133, 6119, 6125 and 6054 had 98–99% 16S
rRNA gene identity to cyanobacterial strains or sequences
originating from North American desert environments, and
the 16S rRNA gene sequence of culture CCMEE 6052 is 99%
identical to a DGGE band sequence originating from a hot
spring source elsewhere in Yellowstone National Park (Black
Sand Pool). Two of the Leptolyngbya sequence clusters, X
and XIII, include relatives that are environmental clone
sequences from Antarctica. Many of the culture sequences
from this study are most closely related (but not identical)
to sequences obtained from other extreme environments,
including deserts. Little is known about dissemination of
cyanobacteria, particularly from one continent to another.
However, a convincing case of endemism has been demon-
strated in thermophilic cyanobacteria from disjunct transo-
ceanic hot springs (Papke et al., 2003). The method of
dispersal of the endolithic microorganisms of our study is
unknown, but it is possible that exfoliation of rock surfaces
that exposes the microbial layer with subsequent dissemina-
tion by wind or insects may result in inoculation of other
surfaces (e.g. Friedmann & Weed, 1987; Sun & Friedmann,
1999), but a gradual lateral spread within the rock may also
occur (Van Thielen & Garbary, 1999).
Problems using 16S rRNA gene sequencesimilarities for species identification
It is also important to note that, although 16S rRNA gene
sequences may show close relationships (i.e. the sharing of a
common ancestor), similarities do not discriminate taxa at
the species level and extended periods of evolution may still
separate cyanobacteria that have 98–100% identities of 16S
rRNA gene sequences. In the present study, an excellent
example is that of culture CCMEE 6012 for which a BLAST
search indicates 100% 16S rRNA gene identity with a
few sequenced strains in the database that have been
identified as Cyanobium gracile (Table 2). The fact that the
other strains were isolated from lakes (Germany, Hungary)
and the Baltic Sea would indicate that the genomes of
these strains must differ greatly, at least in the genes related
to the obvious ecological and physiological disparities.
Two strains of the marine pico-cyanobacterium, Prochloro-
coccus marinus have 16S rRNA gene sequence identities of
over 97% but the complete genomes of both show enor-
mous differences, some of which equate with the different
light regime preferences for these two strains (Rocap et al.,
2003).
FEMS Microbiol Ecol 57 (2006) 470–483c� 2006 Federation of European Microbiological SocietiesPublished by Blackwell Publishing Ltd. All rights reserved
480 T.B. Norris & R.W. Castenholz
Comparisons with other endolithic microbialcommunities
Endolithic communities in hot deserts tend to be dominated
by unicellular cyanobacteria (Whitton & Potts, 2000). How-
ever, cold deserts of Antarctica have endolithic habitats
dominated in some cases by eukaryotes (e.g. green algae
and protolichens) and in others by cyanobacteria, many of
which are unicellular (Van Thielen & Garbary, 1999; de la
Torre et al., 2003). de la Torre et al. (2003) found that an
environmental clone library derived from one of these
Antarctic cryptoendolithic communities (one of the
McMurdo Dry Valleys) was, in fact, dominated by a single
cyanobacterial phylotype. Cultivation of a cyanobacterial
strain with 100% 16S rRNA gene identity to this phylotype
revealed that it had a coccoid morphology. The limited
information that exists at present would suggest that tempe-
rate endolithic habitats tend to have a greater diversity of
taxa than those of hot and cold deserts. Surveys of endolithic
communities in dolomitic rocks of Switzerland (Sigler et al.,
2003) and limestones of the Niagara Escarpment (Gerrath
et al., 1995, 2000) in Canada recovered a wide range of
cyanobacterial genera, including both filamentous and uni-
cellular types. In both of these studies the green algae
Chlorella and Stichococcus made a major contribution to
the community structure, and yellow-green algae also oc-
curred in the Niagara limestones. Endolithic communities
have also been found in moist acidic geothermal environ-
ments (Gross et al., 1998; Walker et al., 2005), in which case,
the only phototrophs of the community were members of
the acidophilic red algal order Cyanidiales. In contrast, the
travertine cryptoendolithic community of Yellowstone was
dominated by cyanobacteria, and few green algae were
retrieved in cultures or clone libraries. Although our clone
library pool was small, it was evident that a similar distribu-
tion of phylotypes was retrieved from all of the sampling
sites except Narrow Gauge Lower Terrace (NGL), which did
not share any phylotypes with other sites. This area is the
most recently formed travertine (3–4 years) and is also
much softer, and more porous than in the other locations,
properties that may allow longer retention of moisture and
therefore may be inhabited by less desiccation-tolerant
strains. In the travertine system overall, a broad range of
cyanobacterial genera are present. This suggests that adapta-
tions to desiccation and freezing tolerance are not limited to
a few cyanobacterial genera, but rather arose convergently
or, alternatively, early in the cyanobacterial radiation.
Future prospects
A future goal of this research is to describe in some detail the
physical and chemical properties of selected ancient traver-
tines of Yellowstone National Park, measurements of rock
porosity, water retention, nutrient composition, and light
attenuation. In addition, the physiology of desiccation- and
freezing-tolerance of cultured community members repre-
sents an ultimate objective. However, the tolerances of many
culture isolates of this study to desiccation stress at low
relative humidity (equivalent to summer values in Yellow-
stone National Park), to high temperature, to freezing, and
to various salinities have already been assayed in a prelimin-
ary study. Results indicate enhanced tolerances of travertine
isolates to these stresses compared to tolerance levels in most
cyanobacteria from aquatic or moister habitats (Norris and
Castenholz, unpublished data). The importance of continu-
ing to study endolithic environments and their microbial
communities is underscored by their relevance as analogues
for life on early terrestrial Earth and for possible past or
present life on Mars.
Acknowledgements
This work was performed while T.B.N. held a National
Research Council Research Associateship Award at the
University of Oregon in affiliation with NASA-Ames Re-
search Center. Special thanks go to undergraduate Pamela
N. Johnston who contributed greatly to the culture isolation
work and to undergraduate Julie Fox who assayed tolerances
to desiccation and other stresses. This work was supported
by a research grant from the Thermal Biology Institute at
Montana State University to T.B.N. and by a NASA/ARC
Cooperative grant NCC 2-5524 to R.W.C. We would like to
thank the Yellowstone Center for Resources, Yellowstone
National Park, for permission to collect within the park
(Permit No. 0185). R.W.C. is a member of the NASA
Astrobiology institute.
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483Endolithic photosynthetic microorganisms