23.10.2014 Views

December 2012 Number 1 - Utah Native Plant Society

December 2012 Number 1 - Utah Native Plant Society

December 2012 Number 1 - Utah Native Plant Society

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

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 />

115

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!