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Biota of the Colorado Plateau

Biotic Communities

Alpine Tundra
Subalpine Conifer Forest
Quaking Aspen Forest
Mixed Conifer Forest
Ponderosa Pine Forest
Montane Chaparral/Scrub
Pinyon-Juniper Woodland
Mountain Grasslands
Semi-arid Grasslands
Mountain Wetlands
Riparian Areas
Paleocommunities
Elevational Range
Merriam's Life Zones

Changes in the Biota

Endangered Species
California Condor
Endangered Fish
Mammal populations
Megafaunal Extinction
Invasive/Exotic Species
Forest Composition
Species Range Expansion
Species Extirpations
Status and Trends of Plants
Succession
Riparian Degradation
Loss of Beaver
Wildfire History and Ecology
Ponderosa Fire Ecology
Tamarisk Invasion

Agents of Biotic Change

biotaBiotic Communities of the Colorado Plateau

Riparian Areas

Beaver Creek riparian habitat

Beaver Creek Canyon, east slope of La Sal Mountains, Utah. Photo © Ray Wheeler.

Riparian habitats, at the interface between wet and dry systems, are defined by the plants that inhabit them. Riparian plants depend on an intact hydrological regime where groundwater is maintained and natural surface flows occur. On the Colorado Plateau, many hydrological regimes are characterized by annual cycles of flooding and minimal flows, which determine sediment availability.

Several regionally significant rivers, including the San Juan, Escalante, Sevier, Little Colorado, Green, and Colorado, cut through the stark mesas and broad plains of the Colorado Plateau. Continuous corridors of riparian vegetation once covered hundreds of miles along desert and mountain rivers. Besides forested riparian communities, there were riparian shrublands, marshlands, and grasslands. These plant communities were found at elevations from high wet meadows and cienegas, to tree-banked streams, to slack water sloughs and marshes–the alpine, montane, and floodplains-plains riparian ecosystems.

Along many rivers and creeks on the Colorado Plateau at middle elevations, from about 5000 feet to nearly 8,000 feet, several broadleaf trees commonly form riparian gallery forests or woodlands. These communities are especially well-developed where environmental conditions permit a mix of some lower-elevation species with some higher-elevation species. Common native trees and shrubs, depending on location and elevation, include narrowleaf cottonwood (Populus angustifolia), box-elder (Acer negundo), bigtooth maple (Acer grandidentatum), Rocky Mountain maple (Acer glabrum), water birch (Betula occidentalis), aspen (Populus tremuloides), thin-leaf alder (Alnus tenuifolia), New Mexico locust (Robinia neomexicana), Scouler willow (Salix scouleriana), and arroyo willows (Salix lasiolepis).

At higher elevations a large proportion of the Colorado Plateau's streams pass through the upland montane forests of mixed-conifer and ponderosa pine communities. The riparian zones themselves are usually narrow, often following relatively steep stream channels in restricted valleys. White fir and blue spruce are the common conifers in and adjacent to these montane riparian ecosystems. The streams usually flood from snowmelt in the spring, and many riparian species depend on over-bank flooding for seed transport and burial in fresh, fertile alluvial sediments. Seed shedding and flooding tend to coincide.

Although the riparian habitats of these rivers and their tributaries represent less than 1 percent of the total acreage of public lands in the 11 western states, about 72% of all reptiles, 77% of all amphibian species, 80% of all mammals, and 90% of all bird species which occur regularly in the Colorado Plateau region routinely use riparian areas for food, water, cover or migration routes. About 30% of the region's bird species use wetlands and other aquatic areas to the exclusion of upland habitats. Wetland and riparian habitats also support a disproportionate number of species that are of concern because they migrate to neotropical areas, have small continental populations, or are declining.

Since settlement by Europeans, riparian forests of all types have suffered enormous declines due to destruction, conversion to other uses, or significant degradation in structure, function, or composition. Non-native saltcedar or tamarisk (Tamarix ramosissima) is now a dominant riparian shrubby tree in the Colorado River basin below 6,000 feet, spread rapidly throughout the system via wind-dispersed seeds. Overall, a 90% loss of presettlement riparian ecosystems has occurred in Arizona and New Mexico. For an essay on the causes and consequences of riparian loss and degradation, click here.


Resources:

Almand, J., and W. Krohn. 1979. The position of the Bureau of Land Management on the protection and management of riparian ecosystems. Pages 259­361 in R. Johnson and F. McCormick, technical coordinators. Strategies for protection and management of floodplain wetlands and other riparian ecosystems. Proceedings of the symposium, 11­13 December 1978. U.S. Forest Service General Technical Report WO-12, Washington, D.C.

Armour, C., Duff, D. and Elmore, W. 1991. The effects of livestock grazing on riparian and stream ecosystems. Fisheries 16: 7-11.

Brode, J. M. and Bury, R. B. 1984. The importance of riparian systems to amphibians and reptiles. Pp. 1035 In: Warner, R. E. and Hendrix, K. M., editors. California riparian systems: ecology, conservation, and productive management. University of California Press, Berkeley and Los Angeles.

Brown, D. E., Lowe, C. H. and Hausler, J. F. 1977. Southwestern riparian communities: Their biotic importance and management in Arizona. Pp. 201-211 In: Johnson, R. R. and Jones, D. A., editors. Importance, preservation, and management of riparian habitat. General Technical Report RM-43. USDA Forest Service, Rocky Mountain Forest and Range Experiment Station, Fort Collins, CO.

Brown, D. E., Carmony, N. B. and Turner, R. M. 1981. Drainage map of Arizona showing perennial streams and some important wetlands. Arizona Game and Fish Department, Phoenix, AZ.

Brown, B. T. and Trossett, M. W. 1989. Nesting-habitat relationships of riparian birds along the Colorado River in Grand Canyon, Arizona. Southwestern Naturalist 34: 260-270.

Brown, B. T. 1989. Breeding ecology of riparian birds along the Colorado River in Grand Canyon, Arizona. Technical Report No. 25. Cooperative National Park Resources Studies Unit/University of Arizona, Tucson, AZ.

Cooper, D. J., Merritt, D. M., Anderson, D. C. and Chimner, R. A. 1999. Factors controlling the establishment of Fremont cottonwood seedlings on the Upper Green River, USA. Regulated Rivers: Research and Management 15: 419-440.

DeBano, L. F. and Schmidt, L. J. 1989. Improving Southwestern riparian areas through watershed management. Report RM-182. USDA Forest Service, Rocky Mountain Forest and Range Experiment Station, Fort Collins, CO, 33 pp.

Farley, G. H., Ellis, L. M., Stuart, J. N. and N. J. Scott, J. 1994. Avian species richness in different-aged stands of riparian forest along the middle Rio Grande, New Mexico. Conservation Biology 8: 1098-1108.

Hewitt, M. J., III. 1990. Synoptic inventory of riparian ecosystems: The utility of Landsat Thematic Mapper data. Forest Ecology and Management 33/34: 605.

Irvine, J. R. and West, N. E. 1979. Riparian tree species distribution and succession along the lower Escalante River, Utah. Southwestern Naturalist 24: 331-346.

Johnson, R. R. 1991. Historic changes in vegetation along the Colorado River in the Grand Canyon. Pp. 178-206 In: Marzolf, G. R., editor. Colorado River ecology and dam management. National Academy Press, Washington, D.C.

Kay, C. E. 1994. The impact of native ungulates and beaver on riparian communities in the Intermountain West. Natural Resources and Environmental Issues 1: 23-44.

Knopf, F. L. 1989. Riparian wildlife habitats: more, worth less, and under invasion. Pp. 20-22 In: Mutz, K., Cooper, D., Scott, M. and Miller, L., editors. Restoration, creation, and management of wetland and riparian ecosystems in the American West. Society of Wetland Scientists, Rocky Mountain Chapter, Boulder, CO.

Lowe, C. H. 1964. Arizona's natural environment: landscapes and habitats. University of Arizona Press, Tucson, 136 pp.

Molles, M. C., Jr. and Dahm, C. N. 1990. A perspective on El Niño and La Niña: global implications for stream ecology. Journal of the North American Benthological Society 9: 68-76.

National Park Service. 1982. The Nationwide Rivers Inventory. National Park Service, Washington, D.C.

Reichenbacher, F. W. 1984. Ecology and evolution of southwestern riparian plant communities. Desert Plants 6: 15-22.

Rieger, J. 1992. Western riparian and wetland ecosystems. Restoration & Management Notes 10: 52-55.

Suttkus, R. D. 1976. Survey of fishes, mammals and herptofauna of the Colorado River and adjacent riparian areas of the Grand Canyon National Park. Final Technical Report No. 5. Colorado River Research Program, Grand Canyon, AZ.

Szaro, R. C. 1989. Riparian forest and scrubland community types of Arizona and New Mexico. Desert Plants 9: 69-138.

Szaro, R. C. 1991. Wildlife communities of southwestern riparian ecosystems. In: Rodiek, J. E. and Bolen, E. G., editors. Wildlife and Habitats in Managed Landscapes. Island Press, Washington, D.C.

Szaro, R. C. and Rinne, J. N. 1988. Ecosystem approach to management of Southwestern riparian communities. Trans. N. Am. Wildl. Nat. Resour. Conf. 53: 502-511.

Tremble, M. 1993. The Little Colorado River. Pp. 283-289 In: Tellman, B., Cortner, H. J., Wallace, M. G., DeBano, L. F. and Hamre, R. H., editors. Riparian management: common threads and shared interests. USDA Forest Service, Rocky Mountain Forest and Range Experiment Station, Fort Collins, CO.

Valencia, R. A., Wennerlund, J. A., Winstead, R. A., Woods, S., Riley, L., Swanson, E. and Olson, S. 1993. Arizona riparian inventory and mapping project. Arizona Game and Fish Department, Phoenix, AZ.

van der Leeden, F., Troise, F. L. and Todd, D. K. 1990. The water encyclopedia. Second edition. Lewis Publishers, Inc., Chelsea, MI, 808 pp.