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December 2012 Number 1 - Utah Native Plant Society

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<strong>Utah</strong> <strong>Native</strong> <strong>Plant</strong> <strong>Society</strong><br />

Table 1. Statistical Summary of the Flora<br />

of Cedar Breaks National Monument*<br />

Category<br />

Taxonomic Diversity<br />

Species &<br />

Varieties<br />

Full Species<br />

Only<br />

No. of Taxa<br />

Confirmed<br />

Present<br />

No. of Taxa<br />

Reported<br />

(not confirmed)<br />

Total<br />

347 7 354<br />

335 5 340<br />

Families 56 0 56<br />

Biogeographic Diversity<br />

Introduced 17 1 18<br />

<strong>Native</strong> 330 6 336<br />

Locally<br />

Endemic<br />

Regionally<br />

Endemic<br />

18 0 18<br />

20 0 20<br />

Disjunct 2 0 2<br />

Peripheral 0 0 0<br />

Sparse 6 0 6<br />

Widespread 284 6 290<br />

The number of taxa and plant families is based on Welsh and<br />

others (2008). Biogeographic diversity categories refer to the<br />

distribution of a species within <strong>Utah</strong> and the state’s contribution<br />

to its overall global range (Fertig 2009b). Introduced taxa<br />

are not native to <strong>Utah</strong> or North America but have become<br />

naturalized (breeding on their own without human assistance).<br />

Local Endemics have their entire global range restricted<br />

to an area of less than 16,500 square km (ca 6370 sq<br />

miles, or 1 degree of latitude x 2 degrees of longitude). Regional<br />

Endemics have global ranges of 16,500-250,000<br />

square km (an area about the size of Wyoming). Disjuncts are<br />

isolated from the contiguous portion of their range by a gap<br />

of more than 800 km (ca 500 miles). Peripherals are widespread<br />

globally but occur at the margin of their contiguous<br />

range in <strong>Utah</strong> and occupy less than 5% of the state’s area<br />

(usually only within a few miles of the state border). Sparse<br />

taxa occur widely across <strong>Utah</strong> or North America but their<br />

range within <strong>Utah</strong> is small and patchy, with populations restricted<br />

to specialized or uncommon habitats. Widespread<br />

taxa have global ranges exceeding 250,000 square km and<br />

occur over at least 10% of the state.<br />

* See Addendum for additional species documented since<br />

2009.<br />

Breaks National Monument are presently listed as sensitive<br />

by the US Forest Service or BLM and 14 were once<br />

candidates for listing as Threatened or Endangered under<br />

the US Endangered Species Act (Table 2).<br />

During 2007-2008 we targeted 16 of Cedar Breaks’<br />

rarest local endemics and CDC species of concern<br />

(Table 2) for survey. The number of target species increased<br />

to 18 with the discovery of extant populations of<br />

Madsen’s daisy and the first records of Welsh’s aster<br />

(Aster welshii) for the monument. We recorded at least<br />

one population of 16 of the target species at 546 different<br />

sampling points within Cedar Breaks National<br />

Monument or the Ashdown Gorge Wilderness Area.<br />

Since more than one target species was often present at<br />

each location, we actually documented 1181 different<br />

sample points for these species. For the clonal species<br />

Salix arizonica we delineated 16 discrete polygons in<br />

three main population clusters that cover a total area of<br />

just over one hectare (Fertig and Reynolds 2009).<br />

Ten of our target species occurred in over 10% of our<br />

samples. These species were found mostly on the red or<br />

white limey-sandstone layers of the Claron Formation<br />

along the rim and slopes of the Cedar Breaks Amphitheater.<br />

Cedar Breaks wild buckwheat (Eriogonum panguicense<br />

var. alpestre) was the most widespread and<br />

abundant of the rare species, being found in 36% of all<br />

samples and having a population estimated at 35,200-<br />

100,000 individuals (Fertig and Reynolds 2009). This<br />

plant also has the smallest geographic range of any<br />

taxon in our study, being known only from the Cedar<br />

Breaks area within the monument and the adjacent<br />

Dixie National Forest and Ashdown Gorge Wilderness.<br />

Only three other species were estimated to have populations<br />

of over 10,000 plants: Least lomatium (Lomatium<br />

minimum), Markagunt aster (Aster wasatchensis var.<br />

wasatchensis), and Least spring-parsley (Cymopterus<br />

minimus). The least abundant and most restricted species<br />

in the study area were Rosy cliff jamesia (known<br />

from only about 100 plants in two main areas; Madsen’s<br />

daisy (approximately 400 plants in three main areas),<br />

Reveal’s paintbrush (Castilleja parvula var. revealii<br />

with 500 plants in two main populations), Podunk<br />

groundsel (Senecio malmstenii with about 1500 individuals<br />

in five sites), and Welsh’s aster (with an estimated<br />

1700 plants scattered along Ashdown and Rattle<br />

creeks in the bottom of the amphitheater).<br />

We were unsuccessful in relocating just one of the 18<br />

target species, the Zion draba (Draba asprella var. zionensis).<br />

This species is known from a single herbarium<br />

specimen (Dickman s.n. CEBR) collected from “Cedar<br />

Breaks National Monument” in 1977. Unfortunately,<br />

nothing more precise is known about the original collection<br />

site. Zion draba occurs commonly in Zion National<br />

Park on Navajo Sandstone cliffs and canyons. Comparable<br />

Navajo Sandstone outcrops are not exposed at Cedar<br />

38

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