Excerpt from FLOW Spring 2004 Issue


PHREATOPHYTE FACTS:

THE TRUTH ABOUT THE TREES


By Ben Lomeli


Fremont cottonwood (Populus Fremontii) and black willow (Salix nigra) are native Arizona phreatophytes (water table dependent plants).


These native riparian (riverine) trees are part of nature's healing process for entrenched (down-cut) rivers and streams, much like a protective scab that forms over a cut on your body.


The trees slow the flow, help build and hold soil in place, and provide a place for water storage, and its subsequent slow release back into the river system. Riparian vegetation helps regulate flows by making the system "spongy" again. Flood control and improved water quality in the watershed are natural benefits of riparian areas. The increased storage of water in riparian zones makes available much of the water required for riparian growth.


An earthquake, climatic changes, historic overgrazing, fuel wood removal, beaver eradication, and altered fire regimes all contributed to the San Pedro River's entrenchment between 1890 and 1908. Around the same time period, entrenchment changed many other southwestern rivers from surficial, sluggish cienega/marsh environments, to faster-flowing deeply incised rivers.


Following the entrenchment period, the San Pedro River floodplain widened between 1908 and 1955. Geomorphic studies show that widening has stabilized since 1955. Most southwestern alluvial streams experienced similar entrenchment and adjustment phases early this century.


As nature's response, rapid proliferation of cottonwood-willow riparian forests and increased river sinuosities immediately followed the entrenchment period.


Riparian vegetation increases roughness coefficients in channels and floodplains, slowing down flood flows, and causing deposition of soils and debris that build and stabilize banks. Gradually, through this healing process called aggradation, river beds and banks are stabilized, floodplains are built-up, and perennial river reaches are extended, resulting in a rise of base flow levels and water tables.


Riparian vegetation requires water during the growing season, but through aggradation, floodplain water storage capacity is increased all year long. Along with increased storage capacity, peak flows are attenuated through increased roughness coefficients from the standing vegetation, and downstream sediment and flooding damages diminish. Under these natural conditions, water tables rise, base flows are extended, and water quality is improved.


No long-term cost-effective gain in water yields (stream flows) resulted from any of several studies attempting to show that removal of riparian vegetation in southwestern streams (including the Gila, Salt, and Colorado Rivers) resulted in a salvage of water.


Good watershed ground cover is essential to infiltrate precipitation and to prevent excessive runoff and erosion. Grasses provide this necessary function but also require water for growth and maintenance. Watershed conditions shape the stream and floodplain. In a floodplain, grasses and shrubs also help the healing process, but during higher flows each year, the larger trees provide better protection and faster aggradation.


Each tributary contributes naturally regulated flows of water, sediment, and nutrients, and provides temperature buffering and biotic diversity. Riparian tribu

  taries act as wildlife corridors between mountains, uplands, and the river by providing habitat continuity for species migrations. Small pools and near-surface water along these washes make excellent habitats. The vegetation provides cover, food, and nesting and roosting areas. Riparian corridors also provide habitat for many insects and reptiles, which in turn serve as a base for a complete food chain.


Healthy tributary watersheds and riparian ecosystems help preserve the river's perennial nature by improving the form and timing of flows within the valley. As the river heals, trees that are no longer needed die off. Although cottonwoods and willows need groundwater within reach of their roots (only 10-15 feet), they are intolerant of prolonged inundation and will be forced to reestablish farther out on the floodplain. They actually have a very narrow window of opportunity in which to grow. That is why riparian corridors are so narrow.


All vegetated drainages play an important role in maintaining proper hydrologic function and a dynamic ecosystem equilibrium capable of supporting a healthy environment and a viable economy. In short, the trees hold the soil, and the soil holds the water.


Our challenge in the Upper Santa Cruz basin is not just one of balancing the water budget. Excessive pumping of groundwater between the mountain-front recharge zones and the river can cause loss of base flows in perennial stream reaches, and subsequent loss of riparian habitats. However, by working together, impacts can be mitigated with appropriate water management, groundwater recharge, and watershed improvement projects.


BIBLIOGRAPHY


Benson, L. and Darrow, R.A. 1945. "Trees and Shrubs of the Southwestern Deserts. University of Arizona Press, Tucson, Arizona.


Blaney, H.F. and Criddle, W.D. 1948. "Consumptive Use of Water Rates in the Upper Colorado River Basin. Soil Conservation Service, U.S. Department of Agriculture.


Brockman, F.C and Merrilees, R. 1968. "Trees of North America". Golden Press. New York, New York.


Bowser, C.W. 1952. "Water Conservation Through Elimination of Undesirable Phreatophyte Growth". In "Transactions", American Geophysical Union, Volume 33, Number 1.


Chaimson, J.F. 1985. "Riparian Vegetation Planting For Flood Control". Pages 120-123 in California Riparian Systems, University of California Press, Berkeley, California.


Cramer, S.F. 1952. "Activities of The South Pacific Division, Corps of Engineer, In Eradication and Control of Phreatophytes". In "Transactions", American Geophysical Union, volume 33, Number1.


First North American Riparian Conference. 1985. "Riparian Ecosystems and Their Management: Reconciling Conflicting Uses". U.S. Department of Agriculture, U.S. Forest Service. Proceedings GTR RM-120. Tucson, Arizona.


Floodplain Board Of Cochise County. 1987. "Floodplain Regulations For Cochise County, Arizona". Pages 1-2. Revised May 26, 1987. Bisbee, Arizona.


Gatewood, J.S., Robinson, W.T., et. al. 1950. "Use of Water by Bottom-Vegetation in Lower Safford Valley Arizona". United States Geological Survey Water-Supply Paper 1103.


Graf, W.L., 1980. "Introduction and Growth of Phreatophytes in the Channels of the Salt and Gila Rivers, Central Arizona". Department of Geography, Arizona State University.


Graf, W.L., Patten, D. T., Turner, B., April 1984. "Issues Concerning Phreatophyte Clearing, Revegetation, and Water Savings Along the Gila River, Arizona". U.S. Army Corps of Engineers.


Jackson, W., et. al. 1987. "Assessment Of Water Conditions And Management Opportunities In Support Of Riparian Values: BLM San Pedro River Properties, Arizona Project Completion Report". U.S. Department Of The Interior, U.S. Bureau Of Land Management.


Knopf, F.L, et. al. 1988. "Conservation Of Riparian Ecosystems In The United States". Reprinted from The Wilson Bulletin.


Koogler, J.C. 1952. "Phreatophyte control on Irrigation Projects in New Mexico" In "Transactions", American Geophysical Union, Volume 33, Number 1.


Laney, R.L. and Hjalmerson, H.W. 1977. "Effects of Phreatophyte Removal on Water