Mapping Nutritional Resources in the Blue Mountains of NE Oregon A crucial step in linking habitat to population responses Our Focus : Late Summer/Early Autumn WHY? General DDE – Animal Performance Relationships Percent of maximum 120 Poor Marginal Good Excellent <2.4 (53% DDM) 2.4-2.7 2.7-2.9 >2.9 (64% DDM) 100 80 60 40 20 0 Digestible energy of diets (kcal/gram of food) Calf growth Yearling growth Yearling preg Adult fat Adult preg Breeding times Winter survival General DDE – Animal Performance Relationships Percent of maximum 120 Poor Marginal Good Excellent <2.4 (53% DDM) 2.4-2.7 2.7-2.9 >2.9 (64% DDM) 100 80 60 40 20 0 Digestible energy of diets (kcal/gram of food) Calf growth Yearling growth Yearling preg Adult fat Adult preg Breeding times Winter survival Blue Mountains Nutrition Mapping Macroplots: n = 285 total n = 205 w/elk Developing Nutritional Resource Maps: The Methodology •Biomass Sampling (by species) •Over-story Measurements (canopy cover, tree density, basal area etc.) •Nutritional quality (DE, DP, tannins) of vegetation by forage class (annual grass/forb, deciduous shrub, perennial grass/fob, evergreen shrub, forest ferns) Developing Nutritional Resource Maps: The Methodology Tame, lactating females are used as a measuring device to quantify the nutritional quality of habitats relative to requirements of the animal. •Diet Quality (energy, protein) •Intake rates (g/min, g/day) •Nutrient intakes rates (DE/min etc) •Activity budgets •Selection indices Digestible Energy Content of Elk Diets, or DDE: Our Key Variable for Nutritional Resource Mapping DE plays a key, usually dominant role in virtually all life processes and it greatly affects how much food ruminants can eat each day…the “multiplier effect”. There is considerable precedence…National Research Council presents livestock nutritional requirements guidelines several ways, including DE content of food. Our objective is to build high resolution maps that show levels of DDE across landscapes, on a pixel by pixel basis. Integrating Plant Succession, Disturbance, and Elk Nutrition Habitat predictor variables Stand/site characteristics Animal response variables Stand age Understory vegetation characteristics Animal foraging outcomes Canopy cover Composition Bite mass BA, QMD, TPH, HT Biomass Season DP, DE Climate Palatability Soils Bite rate Performance outcomes Fat, Repro, Surv DDP, DDE Foraging time RANGELANDS •Ponderosa pine •Western juniper woodland •Mountain mahogany •Low sage •Rigid sage •Bluebunch wheatgrass •Sandberg bluegrass •Idaho fescue •WY big sage •Salt desert shrub •Bitterbrush •Threetip sage •Mtn big sage •Great Basin Pinyon-Juniper Woodland ... Source Type Rangelands Output Algorithms Date Current Months Precip Previous Months Precip = Rangelands DDE Potential Vegetation Type Continuous DDE DRY FORESTS •Rocky Mountain Aspen Forest and Woodland •Northern Rocky Mountain Dry-Mesic Montane Mixed Conifer Forest •Inter-Mountain Basins Aspen-Mixed Conifer Forest and Woodland •Northern Rocky Mountain Montane-Foothill Deciduous Shrubland •Inter-Mountain Basins Montane Riparian Systems •Middle Rocky Mountain Montane Douglas-fir Forest and Woodland Source Potential Vegetation Type Type Output Algorithms Rangelands Date Current Months Precip Previous Months Precip = Rangelands DDE Dry Forest Date Current Months Precip Previous Months Precip = Dry Forest DDE Continuous DDE WET FORESTS •Northern Rocky Mountain Mesic Montane Mixed Conifer Forest •Rocky Mountain Subalpine DryMesic Spruce-Fir Forest and Woodland •Rocky Mountain Subalpine Mesic-Wet Spruce-Fir Forest and Woodland •Rocky Mountain Montane Riparian Systems •Rocky Mountain Subalpine/Upper Montane Riparian Systems Source Potential Vegetation Type Type Output Algorithms Rangelands Date Current Months Precip Previous Months Precip = Rangelands DDE Dry Forest Date Current Months Precip Previous Months Precip = Dry Forest DDE Wet Forest Date Current Months Precip Previous Months Precip Canopy Cover = Wet Forest DDE Continuous DDE WET MEADOWS AGRICULTURE LANDS •No data with tame elk •Consultation with local ag agents •What crops are grown? •What crops would be irrigated? •Tables from NRC •Estimate means EVI > 3500 → Irrigated = 2.65 kcal/g EVI ≤ 3500 → Non-Irrigated = 2.40 kcal/g Source Potential Vegetation Type Type Output Algorithms Rangelands Date Current Months Precip Previous Months Precip = Rangelands DDE Dry Forest Date Current Months Precip Previous Months Precip = Dry Forest DDE Wet Forest Date Current Months Precip Previous Months Precip Canopy Cover = Wet Forest DDE Existing Vegetation Type Agriculture Wetland Inventory Wet Meadows = Potential & Existing Veg. Type Excluded Types = Irrigated Ag Enhanced Vegetation Index (Greenness) = DDE* Non-Irrigated Ag DDE* Wet Meadow DDE* No DDE * Constant value Continuous DDE 60 50 40 30 20 10 0 60 50 40 30 20 10 0 70 60 50 40 30 20 10 0 July 1 available nutrition vs September 1 July 1 available nutrition vs September 1 80 70 60 50 40 30 20 10 0 1-Jul 1-Sep Habitat Management Implications I. Ecological context a. Seasonal & soil depth/moisture greatly limit options for improving summer nutrition in dryer PNV types. b. Will get greatest summer nutritional payoff by operating in relatively wet/high elevation forest zones. Habitat Management Implications II. Habitat treatments a. Dense conifer overstories (>70%) eliminate good forage, and nutrient intake rates are very low. b. Reductions in overstory are needed, although uneven-aged management may be substantially superior to clearcutting. Habitat Management Implications I. II. Other habitats, other seasons a. Early spring may also be crucial for recovering elk in 3rd trimester. By early April, wet meadows and rangelands provide superior forage. Minimizing human impacts near these may be key. Cattle and wild herbivore effects.