Evaluating short‐ and long‐term impacts of fuels treatments and simulated wildfire on an old‐forest species

Fuels-reduction treatments are commonly implemented in the western U.S. to reduce the risk of high-severity fire, but they may have negative short-term impacts on species associated with older forests. Therefore, we modeled the effects of a completed fuels-reduction project on fire behavior and California Spotted Owl (Strix occidentalis occidentalis) habitat and demography in the Sierra Nevada to assess the potential short- and long-term trade-offs. We combined field-collected vegetation data and LiDAR data to develop detailed maps of forest structure needed to parameterize our fire and forest-growth models. We simulated wildfires under extreme weather conditions (both with and without fuels treatments), then simulated forest growth 30 years into the future under four combinations of treatment and fire: treated with fire, untreated with fire, treated without fire, and untreated without fire. We compared spotted owl habitat and population parameters under the four scenarios using a habitat suitability index developed from canopy cover and large-tree measurements at nest sites and from previously derived statistical relationships between forest structure and fitness (k) and equilibrium occupancy at the territory scale. Treatments had a positive effect on owl nesting habitat and demographic rates up to 30 years after simulated fire, but they had a persistently negative effect throughout the 30-year period in the absence of fire. We conclude that fuels-reduction treatments in the Sierra Nevada may provide long-term benefits to spotted owls if fire occurs under extreme weather conditions, but can have long-term negative effects on owls if fire does not occur. However, we only simulated one fire under the treated and untreated scenarios and therefore had no measures of variation and uncertainty. In addition, the net benefits of fuels treatments on spotted owl habitat and demography depends on the future probability that fire will occur under similar weather and ignition conditions, and such probabilities remain difficult to quantify. Therefore, we recommend a landscape approach that restricts timber harvest within territory core areas of use (;125 ha in size) that contain critical owl nesting and roosting habitat and locates fuels treatments in the surrounding areas to reduce the potential for high-severity fire in territory core areas.

[1]  S. Stephens,et al.  Novel characterization of landscape-level variability in historical vegetation structure. , 2015, Ecological applications : a publication of the Ecological Society of America.

[2]  S. Stephens,et al.  Historical and current landscape‐scale ponderosa pine and mixed conifer forest structure in the Southern Sierra Nevada , 2015 .

[3]  Lee H. MacDonald,et al.  Post‐fire runoff and erosion from simulated rainfall on small plots, Colorado Front Range , 2001 .

[4]  J. Bailey,et al.  Comparative hazard assessment for protected species in a fire-prone landscape , 2012 .

[5]  Ross A. Gerrard,et al.  Realized population change for long‐term monitoring: California spotted owl case study , 2013 .

[6]  Scott L. Stephens,et al.  Relating fuel loads to overstorey structure and composition in a fire-excluded Sierra Nevada mixed conifer forest. , 2015 .

[7]  James K. Brown Handbook for inventorying downed woody material , 1974 .

[8]  M. Finney,et al.  Modeling wildfire risk to northern spotted owl (Strix occidentalis caurina) habitat in Central Oregon, USA , 2007 .

[9]  F. Davis,et al.  Regional variation in home-range-scale habitat models for fisher (Martes pennanti) in California. , 2007, Ecological applications : a publication of the Ecological Society of America.

[10]  Nicholas L. Crookston,et al.  An overview of the fire and fuels extension to the forest vegetation simulator , 2000 .

[11]  Maggi Kelly,et al.  A New Method for Segmenting Individual Trees from the Lidar Point Cloud , 2012 .

[12]  Charles W. McHugh,et al.  Simulation of long-term landscape-level fuel treatment effects on large wildfires , 2006 .

[13]  Klaus H. Barber,et al.  Stewardship and fireshed assessment: a process for designing a landscape fuel treatment strategy. , 2007 .

[14]  Janet L. Ohmann,et al.  Predictive mapping of forest composition and structure with direct gradient analysis and nearest- neighbor imputation in coastal Oregon, U.S.A. , 2002 .

[15]  S. Stephens,et al.  Stand-replacing patches within a ‘mixed severity’ fire regime: quantitative characterization using recent fires in a long-established natural fire area , 2010, Landscape Ecology.

[16]  C. Allen,et al.  The importance of rapid, disturbance-induced losses in carbon management and sequestration , 2002 .

[17]  D. H. Vuren,et al.  California Spotted Owl, Songbird, and Small Mammal Responses to Landscape Fuel Treatments , 2014 .

[18]  Wenkai Li,et al.  Delineating Individual Trees from Lidar Data: A Comparison of Vector- and Raster-based Segmentation Approaches , 2013, Remote. Sens..

[19]  Perry J. Williams,et al.  Home Range and Habitat Selection of Spotted Owls in the Central Sierra Nevada , 2011 .

[20]  Scott L. Stephens,et al.  Fuel treatment effects on modeled landscape- level fire behavior in the northern Sierra Nevada , 2010 .

[21]  M. Seamans,et al.  Effects of forest management on California Spotted Owls: implications for reducing wildfire risk in fire‐prone forests. , 2014, Ecological applications : a publication of the Ecological Society of America.

[22]  Kieran F. Suckling,et al.  A review of northern goshawk habitat selection in the home range and implications for forest management in the western United States , 2005 .

[23]  Brandon M. Collins,et al.  Constraints on Mechanized Treatment Significantly Limit Mechanical Fuels Reduction Extent in the Sierra Nevada , 2015 .

[24]  R. J. Gutiérrez,et al.  Evaluating the Efficacy of Protected Habitat Areas for the California Spotted Owl Using Long-Term Monitoring Data , 2012 .

[25]  W. Zielinski,et al.  Short-term effects of fuel treatments on fisher habitat in the Sierra Nevada, California , 2013 .

[26]  R. G. Anthony,et al.  Relationship between wildfire, salvage logging, and occupancy of nesting territories by northern spotted owls† , 2013 .

[27]  James T. Peterson,et al.  Occupancy Estimation and Modeling Darryl I. MacKenzie James D. Nichols J. Andrew Royle Kenneth H. Pollock Larissa L. Bailey James E. Hines , 2006 .

[28]  M. Seamans,et al.  Modeling Nesting Habitat Selection of California Spotted Owls (Strix occidentalis occidentalis) in the Central Sierra Nevada Using Standard Forest Inventory Metrics , 2004 .

[29]  D. Odion,et al.  Is fire severity increasing in the Sierra Nevada, California, USA? , 2014 .

[30]  W. Zielinski,et al.  An assessment of fisher (Pekania pennanti) tolerance to forest management intensity on the landscape , 2013 .

[31]  David R. Anderson,et al.  CLIMATE, HABITAT QUALITY, AND FITNESS IN NORTHERN SPOTTED OWL POPULATIONS IN NORTHWESTERN CALIFORNIA , 2000 .

[32]  Jay D. Miller,et al.  Quantitative Evidence for Increasing Forest Fire Severity in the Sierra Nevada and Southern Cascade Mountains, California and Nevada, USA , 2009, Ecosystems.

[33]  Scott L. Goodrick,et al.  Future U.S. wildfire potential trends projected using a dynamically downscaled climate change scenario , 2013 .

[34]  R. J. Gutiérrez,et al.  California spotted owl habitat selection in the central Sierra Nevada , 1997 .

[35]  David Saah,et al.  Modeling hazardous fire potential within a completed fuel treatment network in the northern Sierra Nevada , 2013 .

[36]  M. Finney FARSITE : Fire Area Simulator : model development and evaluation , 1998 .

[37]  J. W. Wagtendonk,et al.  Effects of fire on spotted owl site occupancy in a late-successional forest , 2011 .

[38]  P. Kennedy,et al.  Meta‐analysis of avian and small‐mammal response to fire severity and fire surrogate treatments in U.S. fire‐prone forests , 2012, Ecological applications : a publication of the Ecological Society of America.

[39]  R. J. Gutiérrez,et al.  Habitat associations of California spotted owls in the central Sierra Nevada , 1992 .

[40]  Derek E. Lee,et al.  Habitat Use and Selection by California Spotted Owls in a Postfire Landscape , 2009 .

[41]  I. MacKenzie Occupancy estimation and modeling , 2013 .

[42]  David R. Anderson,et al.  SITE OCCUPANCY, APPARENT SURVIVAL, AND REPRODUCTION OF CALIFORNIA SPOTTED OWLS IN RELATION TO FOREST STAND CHARACTERISTICS , 2005 .

[43]  Jay D. Miller,et al.  Trends in Wildfire Severity: 1984 to 2010 in the Sierra Nevada, Modoc Plateau, and Southern Cascades, California, USA , 2012, Fire Ecology.

[44]  Yuan Zhang,et al.  Monitoring Trends and Burn Severity (MTBS): Monitoring wildfire activity for the past quarter century using landsat data , 2012 .

[45]  B. C. Ward,et al.  Using stochastic simulation to evaluate competing risks of wildfires and fuels management on an isolated forest carnivore , 2011, Landscape Ecology.

[46]  T. Swetnam,et al.  Warming and Earlier Spring Increase Western U.S. Forest Wildfire Activity , 2006, Science.

[47]  J. W. Wagtendonk,et al.  Effects of fire on small mammal communities in frequent-fire forests in California , 2015 .

[48]  Mark A. Finney,et al.  The challenge of quantitative risk analysis for wildland fire , 2005 .

[49]  J. Agee Fire Ecology of Pacific Northwest Forests , 1993 .

[50]  E. Knapp,et al.  Behaviour and effects of prescribed fire in masticated fuelbeds , 2011 .

[51]  T. Swetnam,et al.  Managing Forests and Fire in Changing Climates , 2013, Science.

[52]  R. L. Hutto,et al.  CHANGES IN BIRD ABUNDANCE AFTER WILDFIRE: IMPORTANCE OF FIRE SEVERITY AND TIME SINCE FIRE , 2005 .

[53]  Derek E. Lee,et al.  Influence of fire and salvage logging on site occupancy of spotted owls in the San Bernardino and San Jacinto Mountains of Southern California , 2013 .

[54]  Benjamin P. Bryant,et al.  Climate change and wildfire in California , 2008 .

[55]  R. J. Gutiérrez,et al.  Using integrated population models to improve conservation monitoring: California spotted owls as a case study , 2014 .

[56]  Scott L. Stephens,et al.  Simulating Fire and Forest Dynamics for a Landscape Fuel Treatment Project in the Sierra Nevada , 2011, Forest Science.

[57]  Danny C. Lee,et al.  Assessing risks to spotted owls from forest thinning in fire-adapted forests of the western United States , 2005 .

[58]  Scott L. Stephens,et al.  Fire regimes of mixed conifer forests in the north-central Sierra Nevada at multiple spatial scales , 2004 .

[59]  Alan Bahro Ager,et al.  Automating the Fireshed Assessment Process with ArcGIS , 2006 .

[60]  W. Zielinski,et al.  Evaluating Management Risks using Landscape Trajectory Analysis: A Case Study of California Fisher , 2011 .

[61]  L. E. Kruger,et al.  National workshop on recreation research and management, Portland, Oregon, USA, 8-10 February 2005. , 2007 .

[62]  W. Cohen,et al.  Lidar Remote Sensing for Ecosystem Studies , 2002 .

[63]  Derek E. Lee,et al.  Dynamics of Breeding-Season Site Occupancy of the California Spotted Owl in Burned Forests , 2012 .