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Gen. Tech. Rep. INT-GTR-344. Ogden, UT: U.S. Department of Agriculture, Forest Service, Intermountain Research Station. 65 p. | 1997

First Order Fire Effects Model: FOFEM 4.0, user's guide

Elizabeth D. Reinhardt; Robert E. Keane; James K. Brown

A First Order Fire Effects Model (FOFEM) was developed to predict the direct consequences of prescribed fire and wildfire. FOFEM computes duff and woody fuel consumption, smoke production, and fire-caused tree mortality for most forest and rangeland types in the United States. The model is available as a computer program for PC or Data General computer.Current information on FOFEM


Gen. Tech. Rep. PNW-GTR-628. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station. 30 p | 2005

Forest Structure and Fire Hazard in Dry Forests of the Western United States

David L. Peterson; Morris C. Johnson; James K. Agee; Theresa B. Jain; Donald McKenzie; Elizabeth D. Reinhardt

Peterson, David L.; Johnson, Morris C.; Agee, James K.; Jain, Theresa B.; McKenzie, Donald; Reinhardt, Elizabeth D. 2005. Forest structure and fire hazard in dry forests of the Western United States. Gen. Tech. Rep. PNW-GTR-628. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Research Station. 30 p. Fire, in conjunction with landforms and climate, shapes the structure and function of forests throughout the Western United States, where millions of acres of forest lands contain accumulations of flammable fuel that are much higher than historical conditions owing to various forms of fire exclusion. The Healthy Forests Restoration Act mandates that public land managers assertively address this situation through active management of fuel and vegetation. This document synthesizes the relevant scientific knowledge that can assist fuel-treatment projects on national forests and other public lands and contribute to National Environmental Policy Act (NEPA) analyses and other assessments. It is intended to support science-based decisionmaking for fuel management in dry forests of the Western United States at the scale of forest stands (about 1 to 200 acres). It highlights ecological principles that need to be considered when managing forest fuel and vegetation for specific conditions related to forest structure and fire hazard. It also provides quantitative and qualitative guidelines for planning and implementing fuel treatments through various silvicultural prescriptions and surfacefuel treatments. Effective fuel treatments in forest stands with high fuel accumulations will typically require thinning to increase canopy base height, reduce canopy bulk density, reduce canopy continuity, and require a substantial reduction in surface fuel through prescribed fire or mechanical treatment or both. Long-term maintenance of desired fuel loadings and consideration of broader landscape patterns may improve the effectiveness of fuel treatments.


Gen. Tech. Rep. RMRS-GTR-105. Ogden, UT: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station. 16 p. | 2003

Coarse woody debris: Managing benefits and fire hazard in the recovering forest

James K. Brown; Elizabeth D. Reinhardt; Kylie A. Kramer

Management of coarse woody debris following fire requires consideration of its positive and negative values. The ecological benefits of coarse woody debris and fire hazard considerations are summarized. This paper presents recommendations for desired ranges of coarse woody debris. Example simulations illustrate changes in debris over time and with varying management.


International Journal of Wildland Fire | 2007

Evaluation of a post-fire tree mortality model for western USA conifers

Sharon M. Hood; Charles W. McHugh; Kevin C. Ryan; Elizabeth D. Reinhardt; Sheri L. Smith

Accurately predicting fire-caused mortality is essential to developing prescribed fire burn plans and post-fire salvage marking guidelines. The mortality model included in the commonly used USA fire behaviour and effects models, the First Order Fire Effects Model (FOFEM), BehavePlus, and the Fire and Fuels Extension to the Forest Vegetation Simulator (FFE-FVS), has not been tested with independently collected post-fire tree mortality data. The model predicts mortality for a wide range of conifer species based on crown scorch and species-specific bark thickness. We evaluated the mortality model on 13 western USA conifers: subalpine fir, red fir, white fir, Douglas-fir, incense cedar, western larch, western hemlock, Engelmann spruce, whitebark pine, lodgepole pine, ponderosa pine, Jeffrey pine, and sugar pine. Predicted stand-level mortality was within ±20% of observed mortality for all species except incense cedar, western larch, red fir, and western hemlock. Individual tree mortality prediction was most accurate for subalpine fir, incense cedar, ponderosa pine, and Jeffrey pine. Evaluation of the model provides managers with an accuracy assessment for estimating the probability of mortality for the majority of western USA conifers when using the mortality model to make land management decisions.A


Research Paper FPL-RP-634. Madison, WI: U.S. Department of Agriculture, Forest Service, Forest Products Laboratory. 29 pages | 2006

Evaluation of silvicultural treatments and biomass use for reducing fire hazard in western states

Kenneth E. Skog; R. James Barbour; Karen L. Abt; Edward Bilek; Frank Burch; Roger D. Fight; Robert J. Hugget; Patrick D. Miles; Elizabeth D. Reinhardt; Wayne D. Shepperd

Several analyses have shown that fire hazard is a concern for substantial areas of forestland, shrubland, grassland, and range in the western United States. In response, broadscale management strategies, such as the National Fire Plan, established actions to reduce the threat of undesirable fire. Available budgets are insufficient to pay for vegetative management on all acres where fire threat is considered unacceptable. The purpose of this report is to begin to identify locations in the west where fire hazard reduction treatments have a potential to “pay for themselves” at a scale and over a long enough time to make investment in additional forest product processing infrastructure a realistic option. The resulting revenues from these activities could presumably subsidize treatment for other locations. Accordingly, we concentrate on areas where wood removed during fire hazard reduction treatments has the potential to support a forest products infrastructure. Areas for treatment were selected by the criterion where either torching or crowning is likely during wildfires when wind speeds are below 25 mph. We considered thinning treatments designed to result in either evenaged or uneven-aged stand conditions. If there are ecological limitations on basal area that is allowed to be removed and there is a need to obtain a certain amount of merchantable wood volume to help cover costs, then uneven-aged treatments appear more likely to achieve one of our hazard reduction targets. Thinning to maintain an uneven-aged structure could be more controversial because it removes larger trees, although the revenue from such treatment covers harvest costs more frequently than does revenue from thinning to maintain an even-aged structure. The removal of large trees by uneven-aged thinning may be reduced by supplementary treatments to increase torching index rather than thinning to reach a high crowning index. Treatments analyzed would treat 7.2 to 18.0 million acres, including 0.8 to 1.2 million acres of wildland urban interface area, and would provide 169 to 640 million oven-dry tons of woody biomass (e.g., main stem, tops, and limbs). About 55% of biomass would be from sawlogs. Sixty to 70% of acres to be treated are in California, Idaho, and Montana. To prepare an example estimate of annual harvest amount for the 12 selected western states, we assume acres needing treatment are divided into two parts of equal area. For half the acres, an uneven-aged treatment would be applied if at least 300 ft3 of merchantable wood is removed; for the other half, an even-aged treatment would be applied if at least 300 ft3 of merchantable wood is removed. Under this scenario, treatment of 0.5 million acres/year would generate 14.6 million oven-dry tons of biomass per year or about 29% of the current level of roundwood removals for the selected states.


Archive | 1988

Eight-year tree growth following prescribed underburning in a western Montana Douglas-fir/western larch stand

Elizabeth D. Reinhardt; Kevin C. Ryan

Eight-year tree growth of western larch (Larix occidentalis) and Douglas-fir (Pseudotsuga menziesii) was measured following prescribed underburning on burned and control plots in western Montana. Western larch on bun.ed plots had reduced radial growth in the first year following fire but increased growth in the next 7 years. Douglas-fir had similar growth on burned and unburned plots. Growth was not reduced by low levels of crown scorch or cambial injury. Stand basal area growth was less on burned plots due to high fire-caused mortality.


Ecological Modelling | 1989

An advisory expert system for designing fire prescriptions

Elizabeth D. Reinhardt; Alden H. Wright; David H. Jackson

Abstract Prescribed fire is used to manipulate forest ecosystems to accomplish a variety of resource management objectives. To develop prescriptions that successfully achieve these objectives, managers use information from a variety of sources. These include results of scientific research and of their own experience. Much of the knowledge of expert practitioners has never been collected and made available to others. An expert system is being developed using rule-based inference and frame-based inheritance to integrate technical and heuristic information, and interpret it for application. Site data and the managers objectives for treating the site with prescribed fire are inputs to the expert system. The system develops a fire prescription: ranges of acceptable fire effects, a description of the desired fire treatment, and a range of conditions under which to burn to achieve the desired treatments and effects. The system documents its results.


In: Climate Change and United States Forests, Advances in Global Change Research 57 2014; pp. 151-182. | 2014

Chapter 7: Managing Carbon

Kenneth E. Skog; Duncan C. McKinley; Richard A. Birdsey; Sarah J. Hines; Christopher W. Woodall; Elizabeth D. Reinhardt; James M. Vose

Storing carbon (C) and offsetting carbon dioxide (CO2) emissions with the use of wood for energy, both of which slow emissions of CO2 into the atmosphere, present significant challenges for forest management (IPCC 2001).


Canadian Journal of Forest Research | 1988

Predicting postfire mortality of seven western conifers

Kevin C. Ryan; Elizabeth D. Reinhardt


Forest Science | 1988

Modeling long-term fire-caused mortality of Douglas fir

Kevin C. Ryan; David L. Peterson; Elizabeth D. Reinhardt

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Kevin C. Ryan

United States Forest Service

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David L. Peterson

United States Forest Service

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Kenneth E. Skog

United States Forest Service

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Robert E. Keane

United States Forest Service

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Richard A. Birdsey

United States Forest Service

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Donald McKenzie

United States Forest Service

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Duncan C. McKinley

United States Forest Service

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James K. Agee

University of Washington

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James M. Vose

United States Forest Service

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