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 />
Long-term Population Demographics and <strong>Plant</strong> Community Interactions<br />
of Penstemon harringtonii, an Endemic Species<br />
of Colorado’s Western Slope<br />
Thomas A. Grant III<br />
Program in Ecology, Colorado State University, Fort Collins, CO<br />
Michelle E. DePrenger-Levin,<br />
Denver Botanic Gardens Research and Conservation Dept, Denver, CO<br />
and Carol Dawson<br />
Bureau of Land Management Colorado State Office, Lakewood, CO<br />
Abstract. Penstemon harringtonii is an endemic species of Colorado’s western slope. Known from only six counties,<br />
Harrington’s penstemon is threatened primarily by habitat degradation and destruction in rural areas that are experiencing<br />
relatively rapid development and recreational pressure. Annual demographic monitoring since 1996 has<br />
not identified statistically significant changes in the overall number of rosettes, although significant inter-annual<br />
variation occurs at the two study sites. Additional research has focused upon the interactions of P. harringtonii with<br />
Artemisia tridentata (big sagebrush) and local plant species richness, and competition for soil moisture. Weak negative<br />
correlations between P. harringtonii and A. tridentata have been documented at both study sites, although the<br />
two sites have opposite trends in the correlation of P. harringtonii and species richness. Ordination techniques (nonmetric<br />
multi-dimensional scaling, NMS) are being explored as a means to find patterns that could increase our understanding<br />
of the rare species’ interactions with the dominant shrub (A. tridentata), local plant species diversity, and<br />
soil moisture. NMS found a positive correlation between species richness and the higher density P. harringtonii<br />
quadrats, although no strong relationships were identified between the rare species and soil moisture. Additional sites<br />
will be sampled in 2009 and 2010 to test hypotheses concerning the potential drivers of P. harringtonii density and<br />
provide guidance in the development of appropriate management and restoration methods.<br />
Long-term monitoring of Penstemon harringtonii<br />
Penland (Scrophulariaceae) was initiated in 1996 to determine<br />
population trends of this rare species. The penstemon<br />
is threatened by land development for homes<br />
and ski areas, oil and natural gas development, overgrazing,<br />
and off-road vehicle use (CoNPS 1997, Panjabi<br />
and Anderson 2006). Formerly a Category 2 candidate<br />
for listing under the Endangered Species Act (ESA), P.<br />
harringtonii is endemic to western Colorado (USDA<br />
NRCS 2009) and populations have been documented<br />
from six counties within the state (Eagle, Garfield,<br />
Grand, Pitkin, Routt, and Summit)(Panjabi and Anderson<br />
2006, Spackman et al. 1997). Currently, P. harringtonii<br />
is listed as a sensitive species by the U.S. Bureau<br />
of Land Management Colorado State Office and the<br />
USDA Forest Service Region 2. The species is ranked<br />
G3/S3 by The Nature Conservancy Natural Heritage<br />
ranking system (Spackman et al. 1997). Based upon the<br />
S3 ranking, the species is considered vulnerable to extirpation<br />
in the state and only 74 occurrences have been<br />
documented (Panjabi and Anderson 2006).<br />
The majority of populations occur in habitats dominated<br />
by Artemisia tridentata (big sagebrush), a hyd-<br />
raulic lifting species (Caldwell et al. 1998). The interaction<br />
between A. tridentata and growth of herbaceous<br />
plants such as P. harringtonii is unclear, although soil<br />
moisture and precipitation are acknowledged as limiting<br />
factors for primary production in semiarid sagebrush<br />
steppe ecosystems (Horton and Hart 1998).<br />
Initial goals of the project were to document population<br />
trends at two study sites, although this has been<br />
expanded into understanding the species’ relationship to<br />
A. tridentata density, soil moisture, and plant community<br />
composition with the ultimate goal of improving<br />
our management of the species and its habitat. We hypothesized<br />
that areas with lower densities of A. tridentata<br />
will have higher densities of P. harringtonii and<br />
greater species richness due to reduced competition for<br />
water. Although destruction or degradation of P. harringtonii’s<br />
habitat is the greatest threat, an understanding<br />
of the species’ interactions with big sagebrush and<br />
soil moisture may augment management of extant populations<br />
and restoration of degraded areas. Additionally,<br />
an understanding of the relationships between sagebrush,<br />
soil moisture and species richness may assist our<br />
ability to manage for diverse ecosystems.<br />
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