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Details - CALS Networking Lab - University of Arizona

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species was encountered along the entire length<br />

<strong>of</strong> the transect divided by effort (in most cases a<br />

maximum <strong>of</strong> 300 intercepts per height category)<br />

and multiplied by 100. We calculated percent<br />

composition <strong>of</strong> each species in each height<br />

category as the number <strong>of</strong> times a species was<br />

encountered divided by the number <strong>of</strong> times all<br />

other species were encountered. If there was at<br />

least a single species encountered along a transect<br />

(in each height category), the total percent<br />

composition equaled 100 percent.<br />

Community Types<br />

We sought to identify plant communities within<br />

the district and to compare characteristics among<br />

them. We did not use the original stratification<br />

<strong>of</strong> random transects for this analysis because we<br />

were more interested in classifying communities<br />

than drawing inference to a larger area. To group<br />

transects, we used Ward’s hierarchical cluster<br />

analysis using data from point-intercept transects.<br />

Cluster analysis is a multivariate technique that<br />

groups like entities (in our case transects) that<br />

share similar values. We used the total number<br />

<strong>of</strong> point intercepts by the most common plant<br />

species in all four height categories for this<br />

analysis. A detailed summary <strong>of</strong> point-intercept<br />

data will be available along with other archived<br />

materials (see Chapter 1).<br />

Results<br />

We collected 741 specimens representing 523<br />

species from the Rincon Mountain District<br />

<strong>of</strong> Saguaro National Park (Appendix A). We<br />

found 39 species that had not previously been<br />

documented in the district, almost one-half <strong>of</strong><br />

them (n = 19) during the course <strong>of</strong> surveying<br />

at point-intercept and/or modified-Whittaker<br />

plots. The list <strong>of</strong> new species that we found<br />

included five non-native species, most notably<br />

African sumac (Rhus lancea). Native species <strong>of</strong><br />

note that we added to the flora included cleftleaf<br />

wildheliotrope (Phacelia crenulata), <strong>Arizona</strong><br />

dewberry (Rubus arizonensis), and American<br />

black nightshade (Solanum americanum).<br />

Based on a thorough review <strong>of</strong> past<br />

studies, floras, and collections located at the<br />

19<br />

<strong>University</strong> <strong>of</strong> <strong>Arizona</strong>, there have been a total <strong>of</strong><br />

1,170 specific and intraspecific taxa documented<br />

at the district, <strong>of</strong> which 78 (6.7%) are non native.<br />

Excluding eight species in the UA collection that<br />

Bowers and McLaughlin (1987) cite as likely<br />

extirpated from the district, there have been<br />

1,120 species (1,162 including intraspecific taxa)<br />

documented since the early 1980s (Appendix<br />

A). Of these species, six were thought to be<br />

extirpated by Bowers and McLaughlin (1987) but<br />

were found by other studies: purple scalystem<br />

(Elytraria imbicata), Lemmon’s hawkweed<br />

(Hieracium lemmonii), alderleaf mountain<br />

mahogany (Cercocarpus montanus), Baltic rush<br />

(Juncus balticus), poverty rush (J. tenius), and<br />

common barley (Hordeum vulgare) (Appendix<br />

A).<br />

Community Types<br />

Based on our interpretation <strong>of</strong> the cluster analysis<br />

using data from point-intercept transects, there<br />

are four communities (i.e., clusters) represented:<br />

• Sonoran Desertscrub. Five lowelevation<br />

transects (112, 115, 130, 138,<br />

and 139) and one middle elevation<br />

transect (121). Mixed cacti and<br />

paloverde (Parkinsonia spp.), with some<br />

velvet mesquite (Prosopis velutina),<br />

especially in the dry washes.<br />

• Oak Savannah. Four middle-elevation<br />

transects (101, 106, 189, and 111). Open<br />

areas dominated by perennial grasses<br />

with scattered trees, mostly oaks.<br />

• Pine-oak Woodland. Two middle<br />

(125 and 120) and three high (107,<br />

155, and 128) elevation transects.<br />

Most transects had dense stands <strong>of</strong><br />

manzanita (Arctostaphylos spp.) and<br />

oaks, interspersed with some pine trees,<br />

mostly pinon and ponderosa pine (Pinus<br />

ponderosa).<br />

• Conifer Forest. Two high elevation<br />

random transects (113 and 191). Tall<br />

forests <strong>of</strong> ponderosa pine, Douglas fir<br />

(Pseudotsuga menziesii), and some<br />

oaks, especially Gambel oak (Quercus<br />

gambelii).

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