The effect of ash on runoff and erosion after a severe forest wildfire, Montana, USA
Scott W. Woods A B and Victoria N. Balfour AA The University of Montana, Department of Ecosystem and Conservation Sciences, 32 Campus Drive, Missoula, MT 59812, USA.
B Corresponding author. Email: scott.woods@umontana.edu
International Journal of Wildland Fire 17(5) 535-548 https://doi.org/10.1071/WF07040
Submitted: 22 February 2007 Accepted: 22 July 2008 Published: 3 October 2008
Abstract
Ash formed by the combustion of vegetation and the litter and duff layers may affect runoff and erosion rates in the period immediately following wildfires, but only a handful of studies have specifically measured its effect. Approximately 1 month after the 2005 Tarkio Fire in western Montana, we applied simulated rainfall for 1 h at a mean intensity of 7.5 cm h–1 to six pairs of 0.5-m2 plots in an area burned at high severity and with a continuous 1-cm to 3.5-cm ash layer on the surface. The ash was retained in one plot per pair and removed from the other plot with a fine brush. The ash layer provided an additional 1.5 cm of water storage capacity and protected the underlying mineral soil from surface sealing, so that the time of ponding in the ash-covered plots was 12 ± 10 min longer, the final runoff rate was 2.1 ± 0.4 cm h–1 lower and the total infiltration was 2.0 ± 1.2 cm higher than in the plots without ash. The reduced runoff from the ash-covered plots in combination with reduced rainsplash detachment resulted in a 74% reduction in sediment yield relative to the plots without ash. Nine months after the fire, the ash was patchy and just a few millimetres thick, and a second set of simulations showed no significant differences in the time of ponding, final runoff rate, total infiltration or sediment yield between plots with and without ash. Ash may significantly reduce the runoff and erosion from severely burned areas in the period shortly after a fire. Consequently, the largest post-fire hydrogeomorphic hazard will occur after the ash layer has been removed by wind and water erosion, but before there has been substantial vegetative regrowth.
Additional keywords: infiltration, overland flow, sediment yield, soil erosion.
Acknowledgements
The present research was funded by a grant from the United States Department of Agriculture, Cooperative State Research Education and Extension Service, Watershed Processes Program (Award No. 2004–35102–15012). The USDA Forest Service, Ninemile Ranger District and Plum Creek Timber Co. facilitated access to the study site. Matt Wotherspoon, Jason Sappington, Carl Lanz, and Eric Sims assisted with field data collection. Two anonymous reviewers provided comments that improved the paper.
Agassi M , Bradford JM (1999) Methodologies for interrill soil erosion studies. Soil and Tillage Research 49, 277–287.
| Crossref | GoogleScholarGoogle Scholar |
Ben-Hur M, Shainberg I, Keren R , Gal M (1985) Effect of water quality and drying on soil crust properties. Soil Science Society of America Journal 49, 191–196.
Borselli L, Torri D, Poesen J , Salvador Sanchis P (2001) Effects of water quality on infiltration, runoff and interrill erosion processes during simulated rainfall. Earth Surface Processes and Landforms 26, 329–342.
| Crossref | GoogleScholarGoogle Scholar | CAS |
Cannon SH, Bigio ER , Mine E (2001) A process for fire-related debris flow initiation, Cerro Grande fire, New Mexico. Hydrological Processes 15, 3011–3023.
| Crossref | GoogleScholarGoogle Scholar |
DeBano LF (2000) The role of fire and soil heating on water repellence in wildland environments: a review. Journal of Hydrology 231, 195–206.
| Crossref |
Leighton-Boyce G, Doerr SH, Shakesby RA , Walsh RPD (2007) Quantifying the impact of soil water repellency on overland flow generation and erosion: a new approach using rainfall simulation and wetting agent on in situ soil. Hydrological Processes 21, 2337–2345.
| Crossref | GoogleScholarGoogle Scholar |
Mein RG , Larsen CL (1973) Modeling infiltration during a steady rain. Water Resources Research 9, 384–394.
| Crossref | GoogleScholarGoogle Scholar |
Onda Y, Dietrich WE , Booker F (2008) Evolution of overland flow after a severe forest fire, Point Reyes, California. Catena 72, 13–20.
| Crossref | GoogleScholarGoogle Scholar |
Prosser IP , Williams L (1998) The effects of wildfire on runoff and erosion in native Eucalyptus forest. Hydrological Processes 12, 251–265.
| Crossref | GoogleScholarGoogle Scholar |
Scott DF , van Wyk DB (1990) The effects of wildfire on soil wettability and hydrological behaviour of an afforested catchment. Journal of Hydrology 121, 239–256.
| Crossref |
Ulery AL, Graham RC , Amrhein C (1993) Wood-ash composition and soil pH following intense burning. Soil Science 156, 358–364.
| Crossref | GoogleScholarGoogle Scholar | CAS |
Valentin C , Bresson LM (1992) Morphology, genesis and classification of crusts in loamy and sandy soils. Geoderma 55, 225–245.
| Crossref | GoogleScholarGoogle Scholar |
Wondzell SM , King JG (2003) Post-fire erosional processes in the Pacific Northwest and Rocky Mountain regions. Forest Ecology and Management 178, 75–87.
| Crossref | GoogleScholarGoogle Scholar |
Woods SW, Birkas A , Ahl RS (2007) Spatial variability of soil hydrophobicity after wildfires in Montana and Colorado. Geomorphology 86, 465–479.
| Crossref | GoogleScholarGoogle Scholar |