December 2012 Number 1 - Utah Native Plant Society
December 2012 Number 1 - Utah Native Plant Society
December 2012 Number 1 - Utah Native Plant Society
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 />
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