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Details - CALS Networking Lab - University of Arizona

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Chapter 3: Plant Inventory<br />

Brian F. Powell<br />

Previous and Ongoing Research<br />

Floras and Plant Collections<br />

We located specimens representing 883 species at<br />

the <strong>University</strong> <strong>of</strong> <strong>Arizona</strong> Herbarium (Appendix<br />

A). Many <strong>of</strong> these specimens were collected<br />

or reported in Bowers and McLaughlin (1987).<br />

Their treatise is the most comprehensive<br />

annotated flora for the Rincon Mountains, though<br />

species have been added to the list since its<br />

publication. Bowers and McLaughlin (1987)<br />

also provide an excellent overview <strong>of</strong> previous<br />

research and collecting from the range (as does<br />

Bowers [1984]), the plant communities present,<br />

species richness gradients, and a list <strong>of</strong> species<br />

extirpated from the range. The Bowers and<br />

McLaughlin list was compiled from work by<br />

Bowers (1984) above 4,500 feet elevation and by<br />

Carole Jenkins who collected from 1978 to 1982<br />

below 4,500 feet elevation. Jenkins never wrote<br />

up the results <strong>of</strong> her work. The list was updated<br />

in 1996 to include the addition <strong>of</strong> 34 species<br />

and the subtraction <strong>of</strong> four (due to incorrect<br />

identifications; Fishbein and Bowers 1996).<br />

There have been floras for four designated natural<br />

areas <strong>of</strong> the district: Wildhorse Canyon (Rondeau<br />

and Van Devender 1992), Chimenea Canyon<br />

(Fishbein et al. 1994a), Box Canyon (Fishbein<br />

et al. 1994b), and Madrona Canyon (Fishbein<br />

1995). Halvorson and Gebow (2000) compiled<br />

these works into a single volume. Halvorson and<br />

Guertin (2003) mapped locations <strong>of</strong> 27 species <strong>of</strong><br />

non-native plants.<br />

Monitoring, Research, and Single-species Studies<br />

Park personnel established long-term monitoring<br />

plots in low-elevation areas <strong>of</strong> both units<br />

(Saguaro NP 2005). They used the pointintercept<br />

method at 25 plots in the Rincon<br />

Mountain District and 20 plots in the Tucson<br />

Mountain District and surveyed these transects<br />

from 1998 to 2004 (Mark Holden, pers.<br />

comm.). Funicelli et al. (2001) resurveyed 25,<br />

15<br />

10 x 10 m vegetation plots (established 10 years<br />

prior to their surveys) and mapped each plant<br />

species. These plots were also used by Turner<br />

and Funicelli (2000) to resurvey the condition<br />

and population structure <strong>of</strong> the saguaro cactus.<br />

Swann et al. (2003a) used the same protocol as<br />

that used by Funicelli et al. (2001) to survey for<br />

plants on the east slope <strong>of</strong> the Rincon Mountains.<br />

Anderson (2001b) surveyed vegetation transects<br />

at random sites in the Rocking K and adjacent<br />

expansion areas.<br />

The saguaro cactus, the park’s namesake<br />

species, has been one <strong>of</strong> the most investigated<br />

non-agricultural plants in the world. McAuliffe<br />

(1993) provided an overview <strong>of</strong> saguaro research<br />

at the park as well as its political and scientific<br />

context. Schwalbe et al. (1999) surveyed<br />

vegetation in and adjacent to the area burned<br />

by the Mother’s Day fire <strong>of</strong> 1994. Baisan and<br />

Swetnam (1990) constructed a fire history (1657–<br />

1893) <strong>of</strong> the conifer forest in the vicinity <strong>of</strong> Mica<br />

Mountain. Though there is a GIS layer <strong>of</strong> 15<br />

dominant vegetation communities in the district,<br />

there is not a current, detailed vegetation map.<br />

In fact, the most current vegetation map was by<br />

Roseberry and Dole (1939).<br />

Current projects include a fire-effects<br />

monitoring program in the high elevation areas<br />

<strong>of</strong> the district (Saguaro NP, unpubl. data) and a<br />

program to map and remove non-native species<br />

(e.g., buffelgrass, fountaingrass, Saharan mustard,<br />

and Malta starthistle) from low-elevation areas <strong>of</strong><br />

both districts <strong>of</strong> the park.<br />

Methods<br />

We used three field methods to survey for<br />

vascular plants. General botanizing surveys<br />

involved opportunistically collecting what we<br />

thought might be new additions to the district’s<br />

flora or plants that we could not identify in the<br />

field. We also used modified-Whittaker plots<br />

and point-intercept transects to make quantitative<br />

comparisons among areas and provide data for<br />

long-term monitoring.

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