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Hydrologic Response to Mechanical Shredding in a Juniper Woodland
Authors:Nathan L Cline  Bruce A Roundy  Fredrick B Pierson  Patrick Kormos  C Jason Williams
Institution:1. Graduate Research Assistant, Department of Plant and Wildlife Sciences, Brigham Young University, Provo, UT 84602, USA;2. Professor, Department of Plant and Wildlife Sciences, Brigham Young University, Provo, UT 84602, USA;3. Research Leader–Supervisory Research Hydrologist, US Department of Agriculture–Agricultural Research Service, Boise, ID 83712, USA;4. Hydrologic Technician, Northwest Watershed Research Center, US Department of Agriculture–Agricultural Research Service, Boise, ID 83712, USA;5. Hydrologist, Northwest Watershed Research Center, US Department of Agriculture–Agricultural Research Service, Boise, ID 83712, USA;1. Research Associate, Department of Plant and Wildlife Sciences, Brigham Young University, Provo, UT 84602, USA;2. Professor, Department of Plant and Wildlife Sciences, Brigham Young University, Provo, UT 84602, USA;3. Associate Professor, Department of Statistics, Brigham Young University, Provo, UT 84602, USA.;1. Rangeland Scientist, US Department of Agriculture, Agricultural Research Service (ARS), Burns, OR 97720, USA;2. Rangeland Ecologist, Oregon State University, Eastern Oregon ARS, La Grande, OR 97850;3. Professor Emeritus, Department of Animal and Rangeland Sciences, Oregon State University, Burns, OR 97720, USA
Abstract:We investigated soil compaction and hydrologic responses from mechanically shredding Utah juniper (Juniperus ostesperma Torr.] Little) to control fuels in a sagebrush/bunchgrass plant community (Artemisia nova A. Nelson, Artemisia tridentata Nutt. subsp. wyomingensis Beetle & Young/Pseudoroegneria spicata Pursh] A. Löve, Poa secunda J. Presl) on a gravelly loam soil with a 15% slope in the Onaqui Mountains of Utah. Rain simulations were applied on 0.5-m2 runoff plots at 64 mm · h?1 (dry run: soil initially dry) and 102 mm · h?1 (wet run: soil initially wet). Runoff and sediment were collected from runoff plots placed in five blocks, each containing four microsites (juniper mound, shrub mound, vegetation-free or bare interspace, and grass interspace) with undisturbed or tracked treatments for each microsite type and a residue-covered treatment for grass and bare interspace microsites. Soil penetration resistance was measured at the hill slope scale, and canopy and ground cover were measured at the hill slope and runoff plot scale. Although shredding trees at a density of 453 trees · ha?1 reduced perennial foliar cover by 20.5%, shredded tree residue covered 40% of the ground surface and reduced non–foliar-covered bare ground and rock by 17%. Tire tracks from the shredding operation covered 15% of the hill slope and increased penetration resistance. For the wet run, infiltration rates of grass interspaces were significantly decreased (39.8 vs. 66.1 mm · h?1) by tire tracks, but infiltration rates on juniper mounds and bare interspaces were unchanged. Bare interspace plots covered with residue had significantly higher infiltration rates (81.9 vs. 26.7 mm · h?1) and lower sediment yields (38.6 vs. 313 g · m?2) than those without residue. Because hydrologic responses to treatments are site- and scale-dependent, determination of shredding effects on other sites and at hill slope or larger scales will best guide management actions.
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