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A networking resource devoted to biological soil crusts and the researchers who study them. We will provide a means for international scientists to communicate, share their research, share important news and announcements, ask questions and find collaborators. We will also provide a space for informal writing on research, opinion, and ideas (now seeking posters!).
Monday, September 30, 2013
Sunday, September 29, 2013
Friday, September 27, 2013
Thursday, September 26, 2013
Ancient soils reveal clues to early life on Earth
Ancient soils reveal clues to early life on Earth
New Nature paper out yesterday suggests using geochemistry that oxygen was in the atmosphere and cyanobacteria were in existence 3 billion years ago. No hard fossil evidence of the cyanobacteria exist...the line of thinking rests on the assumption that cyanos were the first oxygenic photosynthesizers. Anyways, cool paper.
New Nature paper out yesterday suggests using geochemistry that oxygen was in the atmosphere and cyanobacteria were in existence 3 billion years ago. No hard fossil evidence of the cyanobacteria exist...the line of thinking rests on the assumption that cyanos were the first oxygenic photosynthesizers. Anyways, cool paper.
Wednesday, September 25, 2013
BioOne Online Journals - A Field Guide to Biological Soil Crusts of Western U.S. Drylands
BioOne Online Journals - A Field Guide to Biological Soil Crusts of Western U.S. Drylands
Good to hear our field guide is standing the test of time and people are finding it useful after years of use. Thanks to Heather Root for the recent review.
Good to hear our field guide is standing the test of time and people are finding it useful after years of use. Thanks to Heather Root for the recent review.
Tuesday, September 24, 2013
Biocrust data repository
Preface: After a quick glance at the Maestre lab blog, I see they have added links to datasets deposited for public use on Dryad. Good idea. In fact I need to make some old data available myself, the only reason I haven't being that I'd have to sit down and document metadata (yuck!) and make sure the data was easy for someone else to use and I have so much other shit to do in every waking minute that it just hasn't been done. One day....be patient. In the meantime, thanks to Fernando & Co. for showing us how we should be operating.
It occurs to me that there ought to be a single place where someone could go an find links to datasets containing some form of biocrust data, and that this blog is the perfect launching pad. I'll have to think about a nice, more permanent way to do it, but in the meantime it occurs to me I can do it as a simple blog post that I will permalink on the top bar. It will be called Biocrust Data Repository just like this post (do you see it up there?), and I will periodically update it with your help. If you want a link to a dataset posted, leave a comment. You'll have to deposit the data somewhere such as Dryad or your own website, and I will link to the URL that you provide.
Dryad
This is the most widely used repository for data. Here's a search for the term "biological soil crust".
Figshare
This is a widely used repository for figures, presentations, and in some cases datasets. Here's a search for the term "biological soil crust".
Specific data resources (check back for updates)
Castillo-Monroy AP, Maestre FT, Delgado-Baquerizo M, Gallardo A (2010) Biological soil crusts modulate nitrogen availability in semi-arid ecosystems:insights from a Mediterranean grassland. Plant and Soil 333:21-34.
Escolar C, Martinez I, Bowker MA, Maestre FT (2012) Warming reduces the growth and diversity of biological soil crusts in a semi-arid environment:implications for ecosystem structure and functioning. Philosophical Transactions of the Royal Society B 367: 3087-3099.
Maestre FT, Puche MD (2009) Indices based on surface indicators predict soil functioning in Mediterranean semi-arid steppes. Applied Soil Ecology 41:342-350.
Weber B, Berkemeier T, Ruckteschler N, Caesar J, Heintz H, Ritter H, Brab H (2015) Development and calibration of a novel sensor to quantify the water content of surface soils and biological soil crusts. Methods in Ecology and Evolution http://dx.doi.org/10.1111/2041-210X.12459
To submit a link to an archived dataset, please leave a comment with the original paper citation (if applicable) and a link to where the data can be downloaded.
It occurs to me that there ought to be a single place where someone could go an find links to datasets containing some form of biocrust data, and that this blog is the perfect launching pad. I'll have to think about a nice, more permanent way to do it, but in the meantime it occurs to me I can do it as a simple blog post that I will permalink on the top bar. It will be called Biocrust Data Repository just like this post (do you see it up there?), and I will periodically update it with your help. If you want a link to a dataset posted, leave a comment. You'll have to deposit the data somewhere such as Dryad or your own website, and I will link to the URL that you provide.
Dryad
This is the most widely used repository for data. Here's a search for the term "biological soil crust".
Figshare
This is a widely used repository for figures, presentations, and in some cases datasets. Here's a search for the term "biological soil crust".
Specific data resources (check back for updates)
Castillo-Monroy AP, Maestre FT, Delgado-Baquerizo M, Gallardo A (2010) Biological soil crusts modulate nitrogen availability in semi-arid ecosystems:insights from a Mediterranean grassland. Plant and Soil 333:21-34.
Maestre FT, Puche MD (2009) Indices based on surface indicators predict soil functioning in Mediterranean semi-arid steppes. Applied Soil Ecology 41:342-350.
Weber B, Berkemeier T, Ruckteschler N, Caesar J, Heintz H, Ritter H, Brab H (2015) Development and calibration of a novel sensor to quantify the water content of surface soils and biological soil crusts. Methods in Ecology and Evolution http://dx.doi.org/10.1111/2041-210X.12459
To submit a link to an archived dataset, please leave a comment with the original paper citation (if applicable) and a link to where the data can be downloaded.
Monday, September 23, 2013
Kuntstformen der Natur (1904) - Ernst Haeckel
Sunday, September 22, 2013
Species of concern on the Colorado Plateau: Mosses & Lichens
Preface: nearly a decade ago I was asked to contribute to a book about species of concern in the Colorado Plateau ecoregion focusing on all taxa. I drafted up a section about mosses and lichens, focusing on gypsiferous species of biocrusts, which is a rare habitat. There are no federally listed mosses or lichens, not because they don't exist, but rather because the Endangered Species Act categorically excludes them.
I asked Roger Rosentreter (lichenologist), and Lloyd Stark (bryologist) for tips on other non-gypsiferous species I ought to mention.
Having heard nothing about the book in many years, I think I can assume the project is dead. In the meantime, I reckon its more useful here than on an old hard drive in an obsolete file format. I've supplemented it with links to images from the web, if they exist.
Regarding status, vulnerable means that it could conceivably be extirpated. For example rarity of habitat would render something vulnerable. At risk refers to a vulnerable species that is threatened by a stressor.
MOSSES AND LICHENS OF GYPSIFEROUS SOILS
I asked Roger Rosentreter (lichenologist), and Lloyd Stark (bryologist) for tips on other non-gypsiferous species I ought to mention.
Having heard nothing about the book in many years, I think I can assume the project is dead. In the meantime, I reckon its more useful here than on an old hard drive in an obsolete file format. I've supplemented it with links to images from the web, if they exist.
Regarding status, vulnerable means that it could conceivably be extirpated. For example rarity of habitat would render something vulnerable. At risk refers to a vulnerable species that is threatened by a stressor.
MOSSES AND LICHENS OF GYPSIFEROUS SOILS
NODULE CRACKED LICHEN
Status in region: At risk
Status elsewhere: At risk in the Americas
DESCRIPTION ~ Nodule cracked lichen was first
encountered in the Americas in the mid-1980's, and has been found to be locally
common species confined to the gypsiferous soils of the Colorado Plateau.
Although it is has a widespread distribution around the world, its preference
for a very rare habitat type in North America makes it a species of concern.
This lichen is composed of many scales of ~3-5 mm diameter with lobed margins.
Generally the appearance of the lichen is white due to a covering of oxalate
salts, but the thallus underneath is actually pale brown. It has black fruiting
bodies immersed in the thallus that lack any kind of rim around them. Colonies
are irregularly shaped and generally less than 5 cm in diameter.
Vulnerability Factors: Habitat specialist,
restricted range
NEVADA GYPSUM MOSS
Status in Region: At risk
Status in other regions: At risk
DESCRIPTION~ This rare moss was recently
described in 1995 as a result of morphologically well-developed collections
made during California bearpoppy studies. Nevada gypsum moss appears to be a
widely but sparsely distributed species of western North America,
almost exclusively on gypsiferous soils. It is distinguished by other mosses of
the same habitat by its lack of an awn (hair-like projection) on its leaf tips,
and its dark green to black leaves that tend to spiral around the stem near the
top. Its small stature (usually < 2mm tall) makes a handlens a must to
observe these features. Many desert mosses have skewed sex ratios, but to date
a male individual of this species has yet to be found making it one of the
champions.
Vulnerability Factors: Habitat specialist,
restricted range, possible low genetic diversity due to lack of sexual
reproduction
DESERT CRATER LICHEN
Status in region: Vulnerable {EDITORIAL NOTE: THIS SPECIES IS QUITE ABUNDANT, EVEN DOMINANT IN A RARE HABITAT TYPE}
Status elsewhere: Widespread and stable
DESCRIPTION ~ Desert crater lichen is found on
several continents but on the Colorado Plateau it is strongly
restricted to the rare gypsiferous soils where large white populations can be
visually impressive. This lichen forms rather large colonies often exceeding
5cm in diameter and is pure white. It tends to have a rugose, undulating
surface and has large (~ 2mm) black fruiting bodies which are bowl shaped and
sunken into the thallus surface like a crater. This species tends to have a
very clumped distribution, so if you find some you are likely to find a lot.
Vulnerability factors: habitat specialist,
restricted range
LARGELEAF GYPSUM LICHEN
Status in region: At risk
Status elsewhere: At risk globally
DESCRIPTION ~ Largeleaf gypsum lichen has been
confusing lichenologists since the 1920's, and was not discovered in the US
until 1990. Its unique fruiting body which grades into the vegetative thallus
afforded it a designation as a new genus solely representing a new family,
Gypsoplacaceae. It is a squamulose lichen with olive - tan squamules (scale-like
mini thalli) usually about 0.5 - 1 cm in diameter. The fruiting bodies, when
present, look like upraised brick red swellings on the squamules and may be
irregular to dome shaped. Although fairly large in the soil lichen world,
colonies are usually less than 5cm in diameter. This species is a rare one even within its specialized habitat which is also rare.
Vulnerability Factors: Low population density,
habitat specialist, restricted range.
GYPSUM-LOVING RIM LICHEN
Status in region: At risk
Status elsewhere: At risk globally
DESCRIPTION ~ This lichen was unknown to
science until collected in the San Rafael Swell in 1998, and has since been
observed at scattered locations around the Colorado Plateau. Gypsum-loving rim
lichen is chalky white to ashy gray and forms a tightly adhering crust on the
soil surface. Its thallus (vegetative portion) is divided into small partitions
called areoles. It bears black disk shaped fruiting bodies (1-2 mm dia.) with a
white margin that are flush with or sitting slightly atop the thallus. A
typical specimen is about 3 - 5 cm in diameter and irregularly shaped.
Vulnerability Factors: Habitat specialist,
restricted range.
Habitat: These species are strongly restricted
to arid and semi-arid sites with gypsiferous soils such as those derived from
gypsum-bearing portions of the Carmel
Formation, the Paradox Formation, and the Moenkopi Formation (most of
which occur at 5000 - 6500 ft). Such sites are found across southern Utah and
in southwestern Colorado. They occur as components of the conspicuously well
developed biological soil crusts generally found on these soils.
Threats and Concerns: On the Colorado Plateau,
these species are endemic to an inherently rare habitat type, and are uncommon
to rare within that habitat type even when undisturbed. Largeleaf gypsum lichen
is a rare species even within this special habitat type. Most of the gypsum
soils of the plateau are degraded to some extent by livestock activity and off
road vehicle use, and truly undisturbed examples may be lacking. As population
growth continues in the region, economical exploitation of the more pure gypsum
deposits may occur to satisfy demand for products such as drywall. Gypsum areas are particularly popular with users of dirt bikes and all-terrain vehicles.
Conservation: When planning road and trail
construction, gypsum areas should be avoided whenever possible. Enforcement of
off-road vehicle regulations should be prioritized in these areas. Plant cover
is poor on gypsum soils, therefore they offer relatively little forage value to
livestock. Grazing of these fragile habitats could and should be phased out
without creating major economic impacts. Because gypsiferous soils generally
occur in relatively small patches, a network of small fenced reserves could
potentially maintain the endemic biota.
Notes: Because several soil crust species and
some vascular plant species are rare gypsum endemics, and gypsum soils cover
very little area, it is practical and possible to conserve them all by
conserving the habitat in small reserves. We thank Dr. Larry St. Clair of BYU
for sharing his expertise on gypsiferous lichens, and Dr. Lloyd Stark of UNLV
for information pertaining to Didymodon nevadensis.
OTHER MOSSES AND LICHENS OF CONCERN
LITTLE FRINGE MOSS
Crossidium seriatum
Status in region: Unknown
Status elsewhere: At risk globally
DESCRIPTION ~ This little fringe moss is an
extremely rare western North American soil moss with a primarily hot desert
distribution. It has never been collected in the Colorado Plateau but likely
occurs in the more xeric portions, albeit very rarely. Although this species
cannot be separated from lookalikes in the field, perhaps its best identifying
characteristic is its extremely small size. A typical field specimen is
frequently less than 0.5 mm tall and although it does generally have a white
hairlike point on its leaf tips, it never appears as a white hairy cushion.
With the naked eye, individuals look like little black dots.
Vulnerability Factors: Low population density,
restricted range
Habitat: This moss occurs on sandy or
gypsiferous soils of aridlands. Dr. Lloyd Stark suggests that this species is
primarily centered around the gypsiferous soils near Lake Mead, thus its most
likely habitat on the Colorado Plateau includes the more xeric gypsiferous
substrates at the margins of the Colorado Plateau ecoregion such as those near St. George, Utah. Other possible localities include exposures of the Paradox formation in
Cataract Canyon and adjacent side canyons.
Threats and concerns: Soil disturbances of
various sorts are the most likely stressors: foot traffic, livestock grazing,
and off road vehicles.
Conservation: Initially, the best strategy is
simply to determine that the species does indeed occur on the Colorado Plateau
so that the habitat characteristics can be better defined and stressors better
identified. As a preemptive strategy, gypsiferous habit reserves should be
developed as described previously. Fortunately, the most likely localities for
this species happen to be in protected areas (Canyonlands National Park, and
Glen Canyon National Recreation Area), but they could potentially be impacted
by river users.
Entosthodon planoconvexus
Status in region: Vulnerable
Status elsewhere: Globally vulnerable
DESCRIPTION ~ This exceedingly rare moss is
known on the Colorado Plateau from only one location in Canyonlands (deposited by the author at the National Park Service Southeast Utah Group's herbarium in Moab, Utah), and is
known from only four other collections worldwide. Entosthodon planoconvexus
is a short moss with rather large yellowish green leaves that are spreading
when moist and shriveled when dry. Its sporophyte, when present, consists of an
upside-down pear-shaped capsule borne on a reddish stalk.
Vulnerability factors: Low population density
Habitat: Because of its rarity, the habitat of
this species is poorly defined although it tends to occur on dry soil at the
base of rocks. The Canyonlands specimen grew in a dry sandy soil layer over
rock and adjacent to a rock outcrop. It is an occasional associate of
liverworts of the genus Targionia.
Threats and Concerns: The main concerns with Entosthodon
planoconvexus are its naturally highly isolated small populations. Because
it tends to grow in at least partially protected habitats, the population is
likely stable, however stochastic events or disturbance could easily drive this
species locally extinct. Livestock and recreation impacts are the most likely
anthropogenic stressors of this species.
Conservation: It is difficult to recommend conservation
strategies for this species without knowing what potential stressors are.
Perhaps the best strategy is simply to determine where the species occurs so
that the habitat characteristics can be better defined and stressors
identified. Currently, bryophytes are not generally included in inventory and
monitoring projects.
Notes: Dr. Lloyd Stark of UNLV provided
helpful information on this species.
MINNESOTA ROCK LICORICE
Lichinella minnesotensis
Status in Region: Unknown
Status elsewhere: Possibly vulnerable in western North
America
DESCRIPTION~ This rock licorice lichen is apparently
a North American endemic with a primarily eastern distribution. There are some
rather disjunct collections from the midwest and west including a single
collection from near Kanab, Utah. This black lichen is composed of clumps of
ascending convoluted lobes. It is jelly like and semi-transparent when wet.
Colonies are generally only about 1 cm in diameter.
Vulnerability Factors: Isolated populations
Habitat: Minnesota rock licorice is found in
shallow fissures or crevices on rock outcrops. The sole Colorado Plateau
collection was from a limestone substrate of the Timpoweap member of the
Moenkopi formation in Grand Staircase-Escalante National Monument. It is difficult to characterize the habitat
characteristics of this species on the Colorado Plateau because only one
collection has been made.
Threats and Concerns: It is unknown whether
this species is threatened by anthropogenic forces, buts its rarity in the
region suggest it is vulnerable. Fortunately, its habitat type affords
considerable protection.
Conservation: It is difficult to recommend
conservation strategies for this species without knowing what potential
stressors are. Perhaps the best strategy is simply to determine where the
species occurs so that the habitat characteristics can be better defined and
stressors identified if they exist. Currently, lichens are not generally
included in inventory and monitoring projects.
Notes: Dr. Roger Rosentreter of the BLM
provided information on his Kanab-area collection of this species.
HAIRY MOUTH MOSS
Trichostonum sweetii
Status in region: Vulnerable
Status elsewhere: Globally vulnerable
DESCRIPTION ~ Hairy mouth moss is known from
only three collections on the Colorado Plateau (one a dubious identification)
and only a handful more from western North America where it is endemic. This is
a fairly large moss for arid regions (up to 2cm tall) and is an inhabitant of
shady crevices. It has large, narrow, bright green leaves (2-3 mm long) which
are spreading and widest just below the apex.
They may occur as small tufts or scattered individuals mixed with other
species.
Friday, September 20, 2013
Biocrusts of Northern Arizona NAtional Monuments Post 4: Wupatki
This is the latest in a series, see here for a lichen key, here for a moss key, and here for a description of Walnut Canyon biocrusts.
Wupatki-Wupatki
was the largest national monument examined. We found that in the case of
potential biocrust abundance low to medium values were observed within the monument. All of our outputs suggest
that the areas where biocrusts attain the greatest importance are the limestone
flats above the Doney cliffs, including Antelope Prairie. This conclusion is
deceptive because it does not take into account eolian reworked cinders.
Surfaces covered by cinders are not available habitat for BSCs. We had no
available spatial data on the extent of cinder deposits, therefore we generated
a map of cinder cover based upon interpolation of our surface data (Figure 1). Amos et al.
(1981) provide data on thicker cinder deposits, but do not address the thin
eolian deposition of cinders that strongly influences western Wupatki. Because
mapping cinder cover was outside the scope of our project, this data should be
considered a rough approximation only. The cinder map reveals that a large
proportion of Wupatki that otherwise could support BSCs
likely does not because a large proportion of the available surface is covered
with cinders (Figure 2a). There may however be less cinder deposition on the
northern portions of the Doney Cliffs where our models predict high potential
for BSC abundance, function and biodiversity.
Figure 1. Surface cinder cover in Wupatki National Monument, estimated by interpolation from non-systematic ground-based samples. |
Overall,
BSC cover is sparse in Wupatki, apparently due to several factors. The cinder
deposits of the western portions virtually prohibit biocrust development because
there is simply no soil at the surface, i.e. no available habitat. To the east,
the Wupatki basin has less cinder deposition but is quite arid and hot, and is
lacking in sandy soils which tend to support higher biocrust cover on the Colorado
Plateau. This area consists mainly of highly eroded exposures of moenkopi
shale, and alluvial terraces of various ages. Minor biocrust development was detected on some alluvial
terraces, but was not clearly related to terrace age. Occasionally northern exposures
(especially shrub mounds within such sites) supported some crust cover (Figure 2). It is possible, especially in the Wupatki
Basin, that the landscape is not at its potential due to the legacy of
disturbance both from livestock and the widespread prehistoric agriculture that
occurred there. Calcareous sandy soils and non-bentonitic shale-derived soils
in low disturbance conditions generally support greater biocrust cover than that observed in the Wupatki Basin.
Thursday, September 19, 2013
Sunday, September 15, 2013
Grand Canyon Trust announces 2012 John Wesley Powell Award recipients
A great honor for Jayne to be one of the first two scientists to receive this award
Grand Canyon Trust announces 2012 John Wesley Powell Award recipients
Grand Canyon Trust announces 2012 John Wesley Powell Award recipients
Saturday, September 14, 2013
Thursday, September 12, 2013
Biocrusts of Northern Arizona National Monuments Post 3: Walnut Canyon
This is my third post on the theme of biocrusts in the National Monuments of Northern Arizona. Find a lichen key here, and a moss key here. Walnut Canyon, Wupatki, Sunset Crater, Montezuma Castle (& Well), and Tuzigoot were sampled.
Walnut Canyon- Of the National Monuments sampled above the Mogollon rim, Walnut Canyon is where BSCs are most consistently important.
We
sampled intermediate precipitation portions of the Walnut Canyon
rim that had been fenced since at least 1974. We also used surrogate sites with
Kaibab limestone parent materials in range exclosures near Flagstaff,
and on the south rim of the Grand Canyon to
capture more variance in climate parameters. In general, we found that the
entire canyon rim likely has potential for BSC cover . Even in sites
known to have burned relatively recently, we were able to find some BSC
development.
We made the simplifying assumption that the canyon bottom
was unavailable to BSCs due to flooding, and that the canyon walls were too
steep to afford more than minimal available habitat. North facing slopes
supporting Douglas fir stands were examined and found to contain very little
BSC habitat. We did observe the mosses S.
ruralis and Brachythecium sp.,
growing along with the lichen Cladonia
fimbriata primarily growing in rock crevices and on organic matter. Because
of the steep rocky terrain, very low available BSC habitat, and the low spatial
extent of these habitats, we chose not to formally survey them.
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