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Society for Ecological Restoration - Northwest Chapter Conference

California Spotted Owls and Fire and Fuels Management in the Sierra Nevada: An Example Application of Bayesian Modeling to Forest Planning

Presented Danny Lee, Pacific Southwest Research Station

See web version of PowerPoint presentation

Abstract
The recent USDA Forest Service decision to simultaneously amend the forest plans of 11 national forests in the Sierra Nevada is emblematic of current resource management conflicts on public lands. Much of the controversy surrounding the Sierra Nevada decision concerns the choice between conservation and maintenance of high-quality habitat for California spotted owls and the desire to manage forest structure and composition in order to reduce the incidence and extent of high intensity wildfires. California spotted owls preferentially select forest stands with high canopy closure, multistoried canopies, and higher-than-average amounts of snags and downed wood-features than can contribute to the intensity and spread of wildland fires. Using a combination of mechanical thinning and prescribed fire, fire risks can be reduced, but at a potential cost to the suitability of the stand as spotted owl habitat. The challenge is to find a treatment level that achieves an acceptable balance between fire risk reduction and maintenance of owl habitat. This tradeoff can be modeled using Bayesian decision analysis that incorporates a combination of empirical data, model forecasts, and professional judgment. At the heart of this analysis is an influence diagram and associated conditional probability matrices. The influence diagram has three types of nodes: decision nodes, chance nodes, and consequences. Arrows or arcs show the causal dependence among various nodes; the strength of the dependence is captured in the conditional probability relation. For the spotted owl example, decision nodes represent the how, where, and when of various treatments. Chance nodes depict features such as stand condition, wildland fire, and owl survival productivity for which there is uncertainty about their future state. A single consequence node integrates across possible outcomes to calculate an expected utility measure for a given decision. My presentation will focus on 3 steps in building and using influence diagrams: 1) building and parameterizing the influence diagram using various information sources, 2) a comparison of alternative treatments where the optimal decision depends heavily on current fire risk and stand conditions, and 3) using the influence diagram to assess the value of information that might be gained by experimental management.

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