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December 2012 Number 1 - Utah Native Plant Society

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Calochortiana <strong>December</strong> <strong>2012</strong> <strong>Number</strong> 1<br />

Molecular Genetic Diversity and Differentiation in Clay Phacelia<br />

(Phacelia argillacea Atwood: Hydrophyllaceae)<br />

Steven Harrison<br />

Brigham Young University, Provo, UT<br />

Susan E. Meyer,<br />

US Forest Service Rocky Mountain Research Station, Shrub Sciences Laboratory, Provo UT<br />

and Mikel Stevens,<br />

Brigham Young University, Provo, UT<br />

Abstract. Clay phacelia (Phacelia argillacea Atwood) was listed as federally endangered in 1978. It is known from<br />

only two populations in Spanish Fork Canyon, <strong>Utah</strong>. Samples were taken in each of three years from each of these<br />

two populations. We used AFLP markers to assess the genetic relatedness between the two populations and degree of<br />

differentiation between P. argillacea and three of its congeners. Six AFLP primer combinations resulted in 535 reliable<br />

marker loci of which 124 were polymorphic. Phacelia argillacea is genetically distinct from both its close and<br />

distant congeners. The two P. argillacea populations were not strongly differentiated, suggesting that gene flow between<br />

these populations probably occurred historically. In contrast, cohorts establishing in different years within a<br />

population were often genetically differentiated. Sampling in a single year would seriously underestimate genetic<br />

diversity in this species.<br />

Phacelia argillacea Atwood (clay phacelia) is a narrow<br />

endemic presently known from two locations approximately<br />

8 kilometers apart in the Spanish Fork Canyon,<br />

<strong>Utah</strong> County, <strong>Utah</strong> (Figure 1). The genus Phacelia<br />

is the largest in the Hydrophyllaceae. Phacelia argillacea<br />

is a member of the Crenulatae group of section Phacelia,<br />

subgenus Phacelia and is thought to be most<br />

closely allied to P. glandulosa Nutt., a species of wide<br />

distribution in extreme eastern <strong>Utah</strong>, western Colorado,<br />

Wyoming, eastern Idaho, and Montana (Atwood 1975).<br />

Another apparently closely allied species is the recently<br />

described P. argylensis Atwood (Welsh et al. 2003),<br />

known only from the type location in Argyle Canyon,<br />

Carbon County, <strong>Utah</strong> (Figure 1). The Crenulatae group<br />

(which consists of approximately 35 species) differs<br />

from other species of Phacelia in producing four-seeded<br />

capsules, faveolate seeds with a central ridge on the<br />

ventral side, and have a chromosome number of n=11<br />

(Atwood 1975).<br />

Recent taxonomic work in the genus Phacelia has<br />

confirmed the placement of P. glandulosa within the<br />

Crenulatae but has not included either P. argillacea or<br />

P. argylensis (Garrison 2007, Gilbert et al. 2005). Our<br />

goal was to examine molecular genetic diversity within<br />

and among the two known populations of P. argillacea<br />

as a necessary step in designing strategies for introducing<br />

new populations of this species on public land. We<br />

also wanted to make a preliminary assessment of the<br />

degree of differentiation between P. argillacea and its<br />

close congeners P. glandulosa and P. argylensis. We<br />

included the more distant congener P. crenulata Torr.<br />

ex S. Wats. as an out group in the analysis.<br />

Phacelia argillacea is an annual or biennial and has<br />

years when few or no actively growing plants are present.<br />

Its seeds germinate from spring to late summer or<br />

early fall and produce a rosette of leaves which grows<br />

during the winter months and bolts in the spring to produce<br />

a flowering shoot (Armstrong 1992, Meyer personal<br />

observation). The species is an edaphic endemic<br />

that is confined to steep hillsides of the Green River<br />

shale formation. Because of its restricted habitat and<br />

small and widely fluctuating population size, P. argillacea<br />

was declared an endangered species in 1978 (US<br />

Fish and Wildlife Service 1978, 1989).<br />

In 1990, The Nature Conservancy purchased the<br />

Tucker site, which at the time was the only known extant<br />

population for P. argillacea, and fenced it to prevent<br />

damage from grazing and trampling by deer and<br />

sheep and from disturbance caused by highway and railroad<br />

construction (Armstrong 1992). The plant was<br />

later rediscovered at the Railroad site, further down the<br />

canyon (Figure 1, inset). This population is on private<br />

land and is not fenced or managed for conservation.<br />

Known impacts to the Railroad site are highway widening<br />

coupled with the construction of a retaining wall,<br />

subsequent erosion, and trailing and grazing of domestic<br />

and native ungulates. P. argillacea may also be threatened<br />

by invasive weeds and drought.<br />

127

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