Soil water repellency is commonly found in piñón {Piniis spp.)-juniper (Juniperus spp.) (P-J) woodlands and may limit site recovery after a fire. Understanding the extent of this problem and the impact it has on vegetation recovery will help guide land managers in conducting their restoration efforts. In this study, we (i) examined the spatial distribution and severity of post-fire soil water repellency in a burned P-J woodland, (ii) related ecohydrologic properties to prc-fire tree canopy cover and post-fire vegetation establishment, and (iii) demonstrated a geographic information system (GlS)-based approach to extrapolate observed patterns to the lite boundary scale. During a 2-)i period, several soil and vegetative measurements were performed along radial line transects extending from the trunk of burned Utah juniper [Jumperus osteosperma (Torr.)Little] trees to twice the canopy radius. Results indicate that water tepellency patterns are highly correlated with pre-fire tree canopy cover. Critical water repellency extended from the base of the tree to just beyond rhe canopy edge, while subcritical water repellency extended half a canopy radius past the edge of the critical water repellency zone. At sites where critical water repellency was present, infiltration rates, soil moisture, and vegetation cover and density were significantly less than non-water-repellent sites. These variables were also reduced in soils with subcritical water repellency (albeit to a lesser extent). Results were exported into a GIS-based model and used in conjunction with remotely sensed imagery to estimate the spatial distribution of soil watet repellency at the landscape scale.Abbreviations: CR, canopy radius; GIS, geographic information system; P-J, piñon-juniptr; RFE, radial feature extraction; SWC, soil water content; WDPT, water drop penetration time.
S ince European settlement of the western United States, piñón {Pinus spp.)and juniper (Juniperus spp.) species have expanded their range to more than 40 million ha (Romme et al., 2009), encroaching on historical grassland and sagebrush {Artemisia tridentata Nutt.) communities (Miller et al., 2008). Proposed primary-causal factors iticlude high-intensity grazing, fire suppression, increased atmospheric CO2 concentrations, and climate change (Johnson et al., 1993;West, 1999; Miller and Tausch, 2001;Romme et al., 2009). This ecosystem shift has impacted soil resources, plant community structure and composition, forage quality and quantity, water and nutrient cycles, wildlife habitat, and biodiversity (Miller et al., 2008). As P-J woodlands mature, increased fuel loads and canopy cover can lead to large-scale, high-intensity crown fires (Miller et al., 2000(Miller et al., , 2008 Miller and Tausch, 2001 ). After a fire, the ability of a site to recover depends on the extent that physical and biological processes controlling ecosystem function have been altered, both pre-and post-fire (Miller and Tausch, 2001;Briske et al., 2006; Petersen and Stringham, 2008). Ecological resilience may ...