
Twenty-Fourth Annual Meeting and Symposium of the Desert Tortoise Council, March 5-8, 1999
Abstracts

Effects of Exotic Grasses via Wildfire on
Desert Tortoises and their Habitat
Matthew L. Brooks1, Todd C. Esque2, and Cecil R. Schwalbe3
1USGS-BRD, Western Ecological Research Center, Box Spring Field
Station, 41734 South Fork Dr., Three Rivers, CA 93271; 2USGS-BRD, Western Ecological Research Center, St. George
Field Station, 345 E. Riverside Dr., St. George, UT 84790; 3USGS-BRD, Arizona Cooperative
Park Studies Unit, 125 BioSciences East, University of Arizona,
Tucson, AZ 85721

One of the most significant effects of plant invasions worldwide
is the alteration of natural fire regimes. In most cases invasions
lead to increased frequency of fire, especially invasions of exotic
grasses. The effects of increased fire frequency can be dramatic
in regions where fires are historically rare. Estimates of historical
intervals between fires in the Mojave Desert range from 30 to
> 100 years. The invasion of exotic grasses has shortened this
interval to an average of 5 years in some areas, resulting in
significant changes in plant communities and in threats to the
desert tortoise (Gopherus agassizii).
Annual exotic grasses have been shown to cause type-conversion
of native desertscrub to exotic annual grasslands in the Great
Basin and Mojave deserts. Dead stems of the exotics red brome (Bromus madritensis subsp.
rubens), cheatgrass (Bromus tectorum)
and the Mediterranean grass (Schismus arabicus and S.
barbatus)
remain rooted and upright into the summer fire season and over
successive years, whereas those of most native forbs crumble soon
after they senesce. These exotic annual grasses often cover the
desert landscape resulting in continuous and persistent fine fuels
that facilitate the spread of fire in an otherwise fire-resistant
landscape. Frequency and cover of exotic annual grasses can increase
within 3 to 5 years after fires, thus increasing the continuity
and amount of fine fuels that promote additional fires. This grass/fire
cycle reduces fire return intervals and significantly threatens
desert tortoise populations and ecosystem integrity.
Perennial exotic grasses can also promote fires. One such species
is buffelgrass (Pennisetum ciliare) which was introduced as a
forage species to Sonora, Mexico. Thousands of hectare of Sonoran
Desert have been converted to buffelgrass stands for livestock.
In stands where buffelgrass is cultivated for livestock, fire
is sometimes used as a management tool to the keep stands vigorous.
Since this plant has naturalized, additional large expanses of
desert and thornscrub habitat have been converted to buffelgrass
that burn occasionally. This perennial grass has moved northward
from Mexico and into the Sonoran Desert of Arizona mostly along
roadways. In Arizona, several urban parks have been invaded by
buffelgrass and there has been habitat degradation due to fires
at these locations. Buffelgrass was only recently discovered in
Arizona wildlands and although fires that result from buffelgrass
stands appear to be imminent, to date they have not been recorded
in great numbers. The potential exists for buffelgrass to invade
other desert regions such as the Mojave and Colorado deserts,
and studies are planned to evaluate their potential geographic
range.
Fires affect desert tortoises directly by killing them with lethal
heat or low oxygen levels, and indirectly by altering their habitats.
Fires in general appear to be detrimental to the desert tortoise
and its habitats. Management of fire in the Mojave and Sonoran
deserts should focus on preventing invasions of new exotic grasses,
minimizing the dominance of exotic grasses already present, reducing
the number of human-caused fires, and suppression of fires when
they occur.
Brooks, M. L. 1998. Ecology of a biological invasion: alien annual
plants in the Mojave Desert. Dissertation, University of California,
Riverside. 186 pp.
Brooks, M. L. In press. Effects of Fire on the Desert Tortoise (Gopherus
agassizii). Proceedings of the International Conference
on Turtles and Tortoises - 1998.
Brooks, M. L. In review. Alien annual grasses and fire in the Mojave
Desert. Madrono.
Brown, D. E. and R. A. Minnich. 1986. Fire and creosote bush scrub
of the western Sonoran Desert, California. American Midland Naturalist
116:411-422.
DAntonio, C. M. and P. M. Vitousek. 1992. Biological Invasions
by exotic grasses, the grass/fire cycle, and global change. Annual
Review of Ecology and Systematics 3:63-87.
Esque, T. C., A. Brquez M., C. R. Schwalbe, T. R. Van Devender, M.
J. Nijhuis, and P. Swantek. In preparation. Effects of Fire on Desert Tortoises and
their Habitats. Chapter for a book on Sonoran Desert Tortoises.
Arizona-Sonora Desert Museum. Tucson, Arizona.
Esque, T. C., L. A. DeFalco, T. J. Hughes, B. E. Hatfield, and R.
B.
Duncan. In preparation. Observations on the effects of wildfire
on desert tortoise (Gopherus agassizii), small vertebrates, and
desert habitats. Southwestern Naturalist.
Esque, T. C., and C. R. Schwalbe. In preparation. Mediterranean
grasses and fire in the Sonoran Desert. Book on Invasions in the
Sonoran Desert. 1-2 May 1998. Arizona Sonora Desert Museum. Tucson,
Arizona.
Martin-R, M. H., J. R. Cox, and F. Ibarra-F. 1995. Climatic effects
on buffelgrass productivity in the Sonoran Desert. Journal of
Range Management 48:60-63.
OLeary, J. F. and R. A. Minnich. 1981. Postfire recovery of creosote
bush scrub vegetation in the Western Colorado Desert. Madrono 28:61-66.
Van Devender, T. R., R. S. Felger, and A. Brquez M. 1997. Exotic
plants in Sonora, Mexico. Pp. 10-15, In M. Kelly, E. Wagner, and
P. Warner (eds.), Proceedings of the California Exotic Pest Plant
Council Symposium Volume 3. Concord.
|