December 2012 Number 1 - Utah Native Plant Society
December 2012 Number 1 - Utah Native Plant Society
December 2012 Number 1 - Utah Native Plant Society
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Calochortiana <strong>December</strong> <strong>2012</strong> <strong>Number</strong> 1<br />
were chosen to include a range of environmental variability,<br />
growth form, and plant communities. Herbarium<br />
records of known occurrences were used to identify initial<br />
sample sites. We established multiple field sites to<br />
determine the geographic coordinates, environmental<br />
attributes (slope, aspect, soils, parent material) and<br />
vegetation data (associated species) in order to develop<br />
two predictive models for each species: a field key and a<br />
probability-of-occurrence or predictor map. The field<br />
key was developed from environmental attributes and<br />
associated species data collected at the sites and used<br />
only field data. Predictive maps were developed with a<br />
geographic information system (GIS) containing slope,<br />
elevation, aspect, soils, and geologic data – then randomly<br />
tested. Classification-tree (CT) software was<br />
used to generate dichotomous field keys and the maps of<br />
occurrence probabilities. Predictions from both models<br />
were randomly field-validated during the second phase<br />
of the study, and final models were developed through<br />
an iterative process. Data collected during the field validation<br />
were then incorporated into subsequent predictive<br />
models. The models identified potential habitat by<br />
combining elevation, slope, aspect, rock type, and geologic<br />
process into habitat models for each species. The<br />
cross-validated models were >96% accurate and generally<br />
predicted presence with accuracy >60%.<br />
Ute Ladies’-Tresses in the Diamond Fork Watershed:<br />
An Update<br />
Bridget M. Atkin and Steve R. Ripple, BIO-WEST,<br />
Logan, <strong>Utah</strong><br />
Abstract: Ute ladies’-tresses (Spiranthes diluvialis)<br />
(ULT) was listed as threatened in 1992. The largest<br />
known population is in the watershed of Diamond Fork<br />
Creek and its tributary, Sixth Water Creek. Between<br />
1916 and 2004, these streams were used as canals, and<br />
they conveyed irrigation water diverted from Strawberry<br />
Reservoir to the Wasatch Front. Increased peak flows<br />
altered the stream channel and aquatic ecosystem, creating<br />
unique conditions that allowed the rare orchid to<br />
thrive. In 2004 a system of pipes was installed to divert<br />
water directly into the Spanish Fork River, thereby reducing<br />
the flows in Diamond Fork and Sixth Water<br />
Creeks. Studies of ULT populations have been conducted<br />
since 1992 under the direction of <strong>Utah</strong> Reclamation<br />
Mitigation and Conservation Commission. Results<br />
show that ULT colonies are still maintaining large<br />
numbers. However, monitoring of ULT has been difficult.<br />
The unique life-cycle characteristics of ULT, along<br />
with its dynamic habitat, create many challenges.<br />
Highly variable yearly ULT counts are very difficult to<br />
interpret or correlate with environmental parameters. In<br />
2005 other studies were initiated and more associated<br />
plant species data are now being systematically collected<br />
to track changes that may indicate whether the<br />
decreased flows are impacting ULT habitat. During<br />
2007 ULT numbers showed at least two flushes, in early<br />
August with tiny individual plants. Conversely, in 2008<br />
ULT numbers were highest in mid-September and<br />
plants were large. These observations have wide reaching<br />
implications pertinent to many species, indicating<br />
that unless a population is observed carefully, data could<br />
easily be misinterpreted.<br />
Arizona Cliffrose (Purshia subintegra), An Arizona<br />
Endemic<br />
Debra Crisp, Coconino National Forest, Flagstaff, AZ,<br />
and Barbara G. Phillips, Zone Botanist, Coconino, Kaibab<br />
and Prescott National Forests<br />
Abstract: The Arizona cliffrose is a long-lived shrub,<br />
endemic to white Tertiary (Miocene and Pliocene)<br />
limestone lakebed deposits that are high in lithium, nitrates,<br />
and magnesium and is an Endangered species. It<br />
occurs in four disjunct populations spread across an area<br />
of approximately 200 miles in central Arizona. Threats<br />
to Arizona cliffrose include livestock grazing, mineral<br />
exploration, road and utility corridor development, offhighway<br />
vehicle use, urban development and drought.<br />
In this poster we summarize the results of some longterm<br />
monitoring transects initiated in 1987. These transects<br />
are in the Cottonwood population, which is<br />
thought to be the healthiest and contains the most diverse<br />
age structure of the four known populations. Data<br />
on these transects were collected three times, in 1987,<br />
1996 and in 2008.<br />
Demography and Pollination Biology of Graham's<br />
Penstemon (Penstemon grahamii), a Uinta Basin Endemic;<br />
5-year results.<br />
Rita [Dodge] Reisor and Wendy Yates, Red Butte Garden<br />
and Arboretum, University of <strong>Utah</strong>, Salt Lake City,<br />
<strong>Utah</strong><br />
Abstract: Penstemon grahamii is a Uinta Basin endemic<br />
which grows on oil-shale outcrops of the Green<br />
River Formation. Long-term monitoring plots were established<br />
for P. grahamii to collect basic life history<br />
data, study pollination biology, and survey critical habitat.<br />
Research was conducted over 5 years (2004 to 2008)<br />
during May – June, at the Blue Knoll/Seep Ridge and<br />
Buck Canyon population sites located on BLM land.<br />
Data gathered includes rosette diameter, number of inflorescences,<br />
inflorescence height, flowers per inflorescence,<br />
number of fruiting individuals, and herbivory.<br />
The breeding systems study used the following treat-<br />
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