Postfire erosional processes in the Pacific Northwest and Rocky Mountain regions

The objective of this paper is to provide a general overview of the influence of wildland fires on the erosional processes common to the forested landscapes of the western United States. Wildfire can accelerate erosion rates because vegetation is an important factor controlling erosion. There can be great local and regional differences, however, in the relative importance of different erosional processes because of differences in prevailing climate, geology and topography; because of differences in the degree to which vegetation regulates erosional processes; and because of differences in the types of fire regimes that disrupt vegetative cover. Surface erosion, caused by overland flow, is a dominant response to wildfire in the Interior Northwest and Northern Rocky Mountains (Interior Region). A comparison of measured postfire infiltration rates and long-term records of precipitation intensity suggest that surface runoff from infiltration-excess overland flow should also occur in the Coastal and Cascade Mountains of the Pacific Northwest after fires, but this has not been documented in the literature. Debris slides and debris flows occur more frequently after wildfire in the Interior Region and in the Coastal and Cascade Mountains of the Pacific Northwest (Pacific Northwest Region). Debris flows can be initiated from either surface runoff or from soil-saturation-caused debris slides. In the Pacific Northwest Region, debris flows are typically initiated as debris slides, caused by soil saturation and loss of soil cohesion as roots decay following fire. In the Interior Region, both overland-flow-caused and debris-slide-caused debris flows occur after wildfire. Surface erosion, debris slides, and debris flows all occur during intense storms. Thus, their probability of occurrence depends upon the probability of intense storms occurring during a window of increased susceptibility to surface erosion and mass wasting following intense wildfire.

[1]  S. Berris,et al.  Comparative snow accumulation and melt during rainfall in forested and clear-cut plots in the Western Cascades of Oregon , 1987 .

[2]  P. Robichaud,et al.  The effects of log erosion barriers on post‐fire hydrologic response and sediment yield in small forested watersheds, southern California , 2001 .

[3]  W. C. Schmidt,et al.  Effects of fire on flora: a state of knowledge review , 1981 .

[4]  Lee H. MacDonald,et al.  Post‐fire runoff and erosion from simulated rainfall on small plots, Colorado Front Range , 2001 .

[5]  Effects of slash burning on surface soil erosion rates in the Oregon Coast Range , 1982 .

[6]  S. Cannon,et al.  A process for fire‐related debris flow initiation, Cerro Grande fire, New Mexico , 2001 .

[7]  S. Wells,et al.  Fire-Related Sedimentation Events on Alluvial Fans, Yellowstone National Park, U.S.A. , 1997 .

[8]  P. Robichaud,et al.  Water repellency by laboratory burning of four northern Rocky Mountain forest soils , 2000 .

[9]  D. Varnes SLOPE MOVEMENT TYPES AND PROCESSES , 1978 .

[10]  S. Trimble,et al.  U.S. Soil Erosion Rates--Myth and Reality , 2000, Science.

[11]  S. Wondzell The influence of forest health and protection treatments on erosion and stream sedimentation in forested watersheds of Eastern Oregon and Washington , 2001 .

[12]  Leonard F. DeBano,et al.  The role of fire and soil heating on water repellency in wildland environments: a review , 2000 .

[13]  William E. Dietrich,et al.  Construction of sediment budgets for drainage basins , 1982 .

[14]  佐藤 大七郎,et al.  Forest Ecology and Management , 1999 .

[15]  W. G. Wells The effects of fire on the generation of debris flows in southern California , 1987 .

[16]  Daniel R. Miller,et al.  Time, space, and episodicity of physical disturbance in streams , 2003 .

[17]  Frederick J. Swanson,et al.  Disturbance regimes of stream and riparian systems — a disturbance‐cascade perspective , 2000 .

[18]  M. Johansen,et al.  Post‐fire runoff and erosion from rainfall simulation: contrasting forests with shrublands and grasslands , 2001 .

[19]  D. Montgomery,et al.  Distribution of bedrock and alluvial channels in forested mountain drainage basins , 1996, Nature.

[20]  J. D. Helvey EFFECTS OF A NORTH CENTRAL WASHINGTON WILDFIRE ON RUNOFF AND SEDIMENT PRODUCTION , 1980 .

[21]  J. Li,et al.  MUDFLOW DISASTERS IN MOUNTAINOUS AREAS , 1991 .

[22]  J. Moody,et al.  Comparison of soil infiltration rates in burned and unburned mountainous watersheds , 2001 .

[23]  J. D. Helvey Watershed Behavior after Forest Fire in Washington , 1973 .

[24]  Hydrologic and Erosional Responses of a Granitic Watershed to Helicopter Logging and Broadcast Burning , 1995 .

[25]  J. Moody,et al.  Initial hydrologic and geomorphic response following a wildfire in the Colorado Front Range , 2001 .

[26]  J. G. King,et al.  Mountain erosion over 10 yr, 10 k.y., and 10 m.y. time scales , 2001 .

[27]  J. J. Geraghty,et al.  Water Atlas of the United States , 1973 .

[28]  S. Wood,et al.  Fire, storms, and erosional events in the Idaho batholith , 2001 .

[29]  R. Schuster,et al.  Relative Effects on a Low-Volume Road System of Landslides Resulting from Episodic Storms in Northern Idaho , 1999 .

[30]  Peter R. Robichaud,et al.  Fire effects on infiltration rates after prescribed fire in Northern Rocky Mountain forests, USA , 2000 .

[31]  William A. Reiners,et al.  Net Erosion on a Sagebrush Steppe Landscape as Determined by Cesium‐137 Distribution , 1991 .

[32]  D. Neary,et al.  Fire's effects on ecosystems , 1998 .

[33]  David Brandes,et al.  Runoff from a semiarid Ponderosa pine hillslope in New Mexico , 1997 .

[34]  R. D. Harr,et al.  Some characteristics and consequences of snowmelt during rainfall in western Oregon , 1981 .

[35]  Robert L. Beschta,et al.  Logging, infiltration capacity, and surface erodibility in Western Oregon. , 1980 .

[36]  R. L. Hunt,et al.  Influences of forest and rangeland management on salmonid fishes and their habitats , 1992 .

[37]  Henry A. Froehlich,et al.  Infiltration, water repellency, and soil moisture content after broadcast burning a forest site in southwest Oregon , 1989 .

[38]  J. Moody,et al.  Post‐fire, rainfall intensity–peak discharge relations for three mountainous watersheds in the western USA , 2001 .

[39]  S. Wells,et al.  Fire and alluvial chronology in Yellowstone National Park: Climatic and intrinsic controls on Holocene geomorphic processes , 1995 .

[40]  J. G. Elliott,et al.  Developing a post‐fire flood chronology and recurrence probability from alluvial stratigraphy in the Buffalo Creek watershed, Colorado, USA , 2001 .

[41]  D. J. Vanes Slope movement types and processes, in Landslides Analysis and control , 1978 .

[42]  W. Megahan,et al.  NATURAL EROSION RATES AND THEIR PREDICTION IN THE IDAHO BATHOLITH 1 , 1997 .

[43]  R. Beschta,et al.  Seasonal variation of infiltration capacities of soils in western Oregon. , 1981 .

[44]  J. Stednick,et al.  Strength and persistence of fire‐induced soil hydrophobicity under ponderosa and lodgepole pine, Colorado Front Range , 2001 .

[45]  C. T. Dyrness,et al.  Impact of clear-cutting and road construction on soil erosion by landslides in the western Cascade Range, Oregon , 1975 .

[46]  Frederick J. Swanson,et al.  Floods, channel change, and the hyporheic zone , 1999 .

[47]  James R. Sedell,et al.  A Disturbance-Based Ecosystem Approach to Maintaining and Restoring Freshwater Habitats of Evolutionarily Significant Units of Anadromous Salmonids in the Pacific Northwest , 1995 .

[48]  R. Gresswell Fire and Aquatic Ecosystems in Forested Biomes of North America , 1999 .