A new research paper published this month in the Proceedings of the National Academy of Sciences of the United States of America (PNAS) analyzes how new approaches to managing wildfire and fuels and promoting fire-adapted communities can yield tremendous benefits in the coming years as westerners adapt to growing wildfire risks and costs.
Wildfire activity in western North America has increased significantly during the past three decades with longer fire seasons, more wildfire, increased home losses, and more lives at risk. This trend will continue with expected further warming.
Current approaches focus primarily on fighting fires and protecting forests through thinning. These approaches alone are inadequate to address a new era of western wildfires. Wildfire policy and management require a new approach that hinges on helping communities and ecosystems adapt to more wildfire in the West. A new approach is needed which shifts away from over-reliance on suppression, widespread federal thinning, and restoration of forests to historical conditions, to implementing more wild and prescribed fire, targeted thinning, management for future conditions, and planning to make communities safer.
This recent paper is related to earlier research from 2016 when ten wildfire experts authored a paper (reprinted below) an effort to share important insights from fire science with decision makers. Congress, for example, is considering a number of policy and fiscal changes concerning federal wildfire programs. While the paper is hosted at this url, as well as Frames.gov and PNAS, it is a summary work from all authors.
The full 2016 paper is posted below. A printable version of this paper also is available.
Insights from wildfire science: a resource for fire policy discussions, 2016 paper
Tania Schoennagel1, Penny Morgan2, Jennifer Balch1, Philip Dennison3, Brian Harvey1, Richard Hutto4, Meg Krawchuk5, Max Moritz6, Ray Rasker7, and Cathy Whitlock8
1University of Colorado-Boulder, 2University of Idaho, 3University of Utah, 4University of Montana, 5Oregon State University, 6University of California-Berkeley, 7Headwaters Economics, 8Montana State University
[KEYWORDS: forests, shrublands, wildfire, climate change, fire management, fuel reduction treatments, prescribed fire, restoration, fire-adapted, bark beetles, land-use planning, fire-adapted communities]
Record blazes swept across parts of the US in 2015, burning more than 10 million acres. The four biggest fire seasons since 1960 have all occurred in the last 10 years, leading to fears of a ‘new normal’ for wildfire. Fire fighters and forest managers are overwhelmed, and it is clear that the policy and management approaches of the past will not suffice under this new era of western wildfires. In recent decades, state and federal policymakers, tribes, and others are confronting longer fire seasons (Jolly et al. 2015), more large fires (Dennison et al. 2014), a tripling of homes burned, and a doubling of firefighter deaths (Rasker 2015). Federal agencies now spend $2 to $3 billion annually fighting fires (and in the case of the US Forest Service, over 50% of their budget), and the total cost to society may be up to 30 times more than the direct cost of firefighting. If we want to contain these costs and reduce risks to communities, economies, and natural systems, we can draw on the best available science when designing fire management strategies, as called for in the recent federal report on Wildland Fire Science and Technology. Here, we highlight key science insights that can contribute to the public discourse on wildfire policy and associated management of forests, woodlands, and shrublands. This information is fundamental to decisions that will promote resilient communities and landscapes facing more fire in the future.
1. Fire size and frequency will increase under a warmer and drier climate
Weather and climate are the primary determinants of the total acreage burned in nearly all western forests, woodlands and shrublands (Littell et al. 2009, Jolly et al. 2015, Jin et al. 2015). While past human activities—like fire suppression or logging—can fuel bigger, hotter fires, these effects are small compared to the role of drought, temperature and wind on annual area burned. Centuries of evidence of past fire activity from tree-ring and lake-sediment records clearly show that more total area burns during warm periods than during intervals with cool or average climate conditions (Kitzberger et al. 2007, Marlon et al. 2012, Calder et al. 2015). As the climate continues to warm, our knowledge of the past tells us that more area will burn across the West. Because climate’s influence on wildfire is so strong, we are facing an inevitable trend of increasing annual area burned, and will need to learn how to adapt to more wildfire.
2. Fuel reduction on federal lands will do little to reduce acreage burned and homes lost
Efforts to “thin the threat” and expand fuels reduction treatments (e.g. thinning and/or prescribed fire) on federal lands are often promoted to reduce the flammability of wildlands and save homes. Increasing the pace and extent of fuel treatments is a valuable goal because treatments can sometimes reduce fire severity and assist tactical firefighting locally (Hudak et al. 2011). However, the costs of thinning are high and the operational challenges are considerable, limiting where, and the extent to which, treatments are feasible (Calkin et al. 2015, North et al. 2015, Boer et al. 2015). Furthermore, federal fuel management programs do not have jurisdiction to directly mitigate fire risk on private lands, where the threat to public safety and property is most acute. By some estimates, private land accounts for 52 million acres of forests considered to be at highest fire risk across the Western states (American Forest Foundation, 2015) and most land in and around western communities is private, limiting federal agency ability to treat near homes (Schoennagel et al. 2009). We will never be able to treat enough land to alter the trend of increasing acreage burned, but prioritizing federal fuel treatments around communities and creating better mechanisms for reducing fuels on private land can help reduce home loss and better protect communities.
3. Not all forests need restoration
The need for forest restoration to undo the effects of past fire suppression is often invoked in fire policy discussions, yet only some landscapes need such restoration (Schoennagel et al. 2004). Restoration is often appropriate in dry forests where logging and fire suppression since the 1950s have shifted open, park-like forests to less patchy, dense forests today. The increased and more continuous fuel loads have shifted fires from past frequent low-severity to present-day high-severity events (Stephens et al. 2013, Hessburg et al 2015). For example, in some forests dominated by ponderosa pine, thinning and prescribed fire can help restore low tree density, reduce fuel continuity, lower fire severity, and provide important ecosystem services such as watershed protection, climate modulation, wildlife habitat, scenery, recreational opportunities, and wood products.
Not all western forests need restoration to remedy effects of past fire suppression. In contrast to dry and formerly open low-elevation forests, moister and cooler high-elevation forests naturally support high tree densities and fires of mostly high severity. Here, forest densities have changed little from their pre-suppression-era condition; therefore, such restoration is not needed. A large portion of western forests fall in between these two extremes, and the restoration need in such mid-elevation, mixed-severity-fire forests is highly variable and the subject of active debate. Climate change may also render restoration less important than adaptation and mitigation in many natural systems, since future environmental conditions may or may not resemble those of the past. In short, not all forests are equally “out of whack” due to past fire suppression, and the need for restoration is not universal.
4. High severity fires often have ecological benefits
High-severity fires are the norm in many systems, such as chaparral, lodgepole pine and spruce-fir forests. While it is easy to understand why humans perceive severe fires as “catastrophic”, severely burned landscapes are neither “destroyed” nor “lifeless” in terms of their ecological integrity. Many plant and animal species require recently blackened forests of standing dead trees to persist (Bond et al. 2012, Hutto et al. 2015) and are clearly adapted to high-severity fire. For example, the black-backed woodpecker’s association with blackened trees is reflected in its jet-black coloration, and its prey (the jewel beetle) detects newly burned forest using its infrared heat sensors. These animals, and others, reflect a long evolutionary history between organisms and severe wildfire.
Such adaptations also confirm what we know from tree-ring and lake-sediment records, namely, that severely burned conditions have occurred for millennia across a broad range of shrublands and forests throughout the West (Whitlock et al. 2008, Keeley et al. 2011). Large severe fires often create complex patterns in which much of the burned area is close to unburned seed sources. In these landscapes, trees and/or shrubs naturally re-establish soon after fire without active post-fire restoration efforts (Turner et al. 1994, Kemp et al. 2015). Severe fire is not necessarily ecologically catastrophic, but rather a natural mechanism of renewal and diversity.
5. Insect outbreaks do not necessarily make fires worse
In the last 15 years, tiny, native insects called bark beetles have killed trees on more than 47 million acres of forest in the western US. But just like fires do not burn every tree, beetle outbreaks vary widely in their impacts, with many areas only lightly affected. Beetle outbreaks have occurred periodically for millennia, and forests that have co-evolved with these insects recover well from outbreaks without management intervention. Expensive programs to remove insect-attacked trees, even in remote areas, have been proposed out of understandable fear that the dead trees will fuel large fires. However, data show that bark beetles have little influence on the occurrence (Hart et al. 2015) or severity of forest fires in the 10 to 15 years after the trees have died (Harvey et al. 2014). In high-elevation and high-latitude forests (where many of the worst outbreaks have occurred), high-severity wildfires are the norm, so bark beetle activity rarely makes those fires more severe than fires occurring in the absence of bark beetle outbreaks. In general, weather and climate are the key drivers of fire occurrence; large severe fires are more likely when it’s hot, dry and windy, regardless of beetle outbreaks.
6. Land-use planning can reduce wildfire risk
Most firefighting risks and costs are directly related to protecting communities from active wildfires, especially during warm dry years, when widespread fires threaten many communities at the same time (Morgan et al. 2008, Rasker 2015). However, most fire policy and management to date has focused on taming fire risk in relatively undeveloped landscapes, not on directly reducing risk to communities. Better community planning efforts and homeowner practices will keep people and structures out of harm’s way (Moritz et al. 2014, Calkin et al. 2014). Strengthening national programs like Fire Adapted Communities, Fire Adapted Communities Learning Network, and FIREWISE, will help homeowners select fire-resistant building and landscaping materials and encourage routine yard maintenance within ~200 feet of their homes. Social science indicates stronger incentives for builders and local governments will create more fire defensible developments that would ultimately reduce costs to taxpayers (Rasker 2015).
Some cities have already adopted community planning tools to reduce wildfire risk: San Diego enforces strict brush management regulations, the Flagstaff fire department uses a successful Wildland Urban Interface development code to protect properties, and Santa Fe applies stringent fire-safe regulations on new developments to protect its watershed. There’s ample opportunity for land-use planning to play a positive role—84% of Wildland Urban Interface lands in the West do not yet have homes (Gude et al. 2008), and future fire risk greatly depends on how or if such areas get developed.
7. Managing more fires to burn safely can reduce risk and increase ecological benefit
Fire fighters suppress at least 95% of all fires, but managing some fires to burn safely is one important way to reduce future wildfire threat and increase ecological benefit (Calkin et al. 2015, North et al. 2015). Natural or prescribed fire today can help prevent worse fires tomorrow—flames consume debris and live fuel, often limiting the places where new fires can burn (Prichard et al. 2014,Parks et al. 2015). Monitoring and managing fires that occur under moderate climate conditions can restore landscapes, aid vegetation recovery, and may reduce the risk of large severe fires during extreme conditions. Strategic planning for future fires is a crucial part of integrated fire management, where fire can restore and maintain healthy natural systems with minimal threat to people, their homes, and the places they value.
Conclusion: Learning to live with wildfire
We can live with fire (Moritz et al. 2014, Hessburg et al. 2014) and we must. As the West is demonstrating, wildfire is part of our past and will also be an important part of our future. Relevant wildfire science can help us plan for and adapt to living with wildfire.
As wildfire scientists, we want to share relevant insights from fire science as a resource to policy makers. We take our ‘social contract’ as scientists seriously (Lubchenco 1998), and seek to contribute information in support of a policy process that helps promote resilient communities and landscapes facing more fire in the future. Research indicates that wildfire will continue to increase in frequency and extent as the climate warms. Targeted fuel reduction treatments can help reduce risk to residential communities and restore landscapes affected by past fire suppression, but cannot overcome the increasing trend in acreage burned. Science indicates that past beetle outbreaks do not significantly increase the chance or severity of fire.
Because fire is a mechanism of ecological renewal and diversity, allowing space and time for fire-adapted forests and shrublands to burn and recover from fire is important to maintain the landscapes we and other species depend on. Given the natural role of fire in the West, managing prescribed and naturally ignited fires to burn will help reduce future wildfire threats and increase ecological benefits in many systems. Better fire and forest management is part of the solution, but the most effective changes in terms of protection of people and property, will be near homes and on private property. Fire-smart land-use planning, building, and landscaping are essential to creating fire-adapted communities that can survive and thrive despite inevitable wildfire. Policy guidelines such as the National Cohesive Strategy are beginning to recognize fire as fundamental to healthy landscapes. Further integration of relevant insights from wildfire science can lead to more robust policy and practice.
American Forest Foundation. 2015. Western water threatened by wildfire: it’s not just a public lands issue. American Forest Foundation. Washington D.C. 28 pp.
Boer, M.M., O.F. Price, R.A. Bradstock. 2015. Wildfires: Weigh policy effectiveness. Science. 350 (6263): 920.
Bond, M. L., R. B. Siegel, R. L. Hutto, V. A. Saab, and S. A. Shunk. 2012. A new forest fire paradigm: The need for high-severity fires. Wildlife Professional. 6:46-49.
Calder, J.W., D. Parker, C.J. Stopka, G. Jiménez-Moreno, and B.N. Shuman. 2015. Medieval warming initiated exceptionally large wildfire outbreaks in the Rocky Mountains. Proceedings of the National Academy of Sciences. 112 (43) 13261-13266.
Calkin, D.E., Cohen, J.D., Finney, M.A., and Thompson, M.P. 2014. How risk management can prevent future wildfire disasters in the wildland-urban interface. Proceedings of the National Academy of Sciences. 111(2): 746-751.
Calkin, D.E., M.P. Thompson, and M.A. Finney 2015. Negative consequences of positive feedbacks in US wildfire management. Forest Ecosystems, 2:9. DOI 10.1186/s40663-015-0033-8
Dennison, P.E., S.C. Brewer, J.D. Arnold, and M.A. Moritz, 2014. Large wildfire trends in the western United States, 1984-2011. Geophysical Research Letters. 41, 2928–2933.
Gude, P., Rasker, R., & Van den Noort, J. 2008. Potential for future development on fire-prone lands. Journal of Forestry. 106(4): 198-205.
Hart, S.J., Schoennagel, T., Veblen, T.T., & Chapman, T.B. 2015. Area burned in the western United States is unaffected by recent mountain pine beetle outbreaks. Proceedings of the National Academy of Sciences. 112(14): 4375-4380.
Harvey, B.J., Donato, D.C., Turner, M.G. 2014. Recent mountain pine beetle outbreaks, wildfire severity, and postfire tree regeneration in the US Northern Rockies. Proceedings of the National Academy of Sciences. 111(42): 15120-15125.
Hessburg, P.F., A.J. Larson, D.J. Churchill, R.D. Haugo, C. Miller, T.A. Spies, M.P. North, N.A. Povak, R.T. Belote, P.A. Singleton, W.L. Gaines, R.E. Keane, G.H. Aplet, S.L. Stephens, P. Morgan, P.A. Bisson, B.E. Rieman, R.B. Salter, G.H. Reeves. 2015. Restoring fire-prone Inland Pacific landscapes: Seven core principles. Landscape Ecology. 30:1805–1835.
Heyerdahl, E.K., McKenzie, D., Daniels, L.D., Hessl, A.E., Littell, J.S. and Mantua, N.J., 2008: Climate drivers of regionally synchronous fires in the inland northwest (1651-1900). International Journal of Wildland Fire. 17: 40-49
Hudak, A.T, I. Rickert, P. Morgan, E. Strand, S.A. Lewis, and P.R. Robichaud. 2011. Review of fuel treatment effectiveness in forests and rangelands and a case study from the 2007 megafires in central, Idaho. USA. Gen. Tech. Rep. RMRS-GTR-252. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station. 60 p.
Hutto, R. L., M. L. Bond, and D. A. DellaSala. 2015. Using bird ecology to learn about the benefits of severe fire. Pages 55-88 in D. A. DellaSala and C. T. Hanson, editors. The ecological importance of mixed-severity fires: Nature’s phoenix. Elsevier: Amsterdam. 450 pp.
Jin, Y., M. L. Goulden, N. Faivre, S. Veraverbeke, F. Sun, A. Hall, M. S. Hand, S. Hook, and J. T. Randerson. 2015. Identification of two distinct fire regimes in Southern California: Implications for economic impact and future change. Environmental Research Letters. 10:94005-94016.
Jolly, W.M., Cochrane, M.A., Freeborn, P.H., Holden, Z.A., Brown, T.J., Williamson, G.J., & Bowman, D.M.J.S. 2015. Climate-induced variations in global wildfire danger from 1979 to 2013. Nature Communications. 6: 7537 doi: 10.1038/ncomms8537.
Keeley, J. E., Pausas, J. G., Rundel, P. W., Bond, W. J., & Bradstock, R. A. (2011). Fire as an evolutionary pressure shaping plant traits. Trends in Plant Science. 16(8), 406-411.
Kemp, K.B., P.E. Higuera, and P. Morgan. 2015. Fire legacies impact conifer regeneration across environmental gradients in U.S. northern Rockies. Landscape Ecology. doi: http//dx.doi.org/10.1007/s10980-015-0268-3
Kitzberger, T., P. M. Brown, E. K. Heyerdahl, T. W. Swetnam, and T. T. Veblen. 2007. Contingent Pacific-Atlantic Ocean influence on multi-century wildfire synchrony over western North America. Proceedings of the National Academy of Sciences. 104: 543-548.
Littell J.S., D. McKenzie, D.L. Peterson, and A.L. Westerling. 2009. Climate and wildfire area burned in western US ecoprovinces, 1916–2003. Ecological Applications. 19:1003–1021.
Lubchenco, J. 1998. Entering the century of the environment: A new social contract for science. Science. 279 (5350): 491-497.
Marlon, J.R., P.J Bartlein, C. Long, D.G. Gavin, R.S.Anderson, C. Briles, K.J. Brown, D. Colombaroli, D.J. Hallett, M.J. Power, E.A. Scharf, and M.K. Walsh. 2012. A long-term perspective on wildfires in the western U.S. Proceedings of the National Academy of Sciences. 109: E535-E543.
Morgan, P., E.K. Heyerdahl, and C.E. Gibson. 2008. Multi-season climate synchronized widespread forest fires throughout the 20th-century, Northern Rocky Mountains, USA. Ecology. 89(3):717-728.
Moritz, M.A., E. Batllori, R.A. Bradstock, A.M. Gill, J. Handmer, P.F. Hessburg, J. Leonard, S. McCaffrey, D.C. Odion, T. Schoennagel and A.D. Syphard. 2014. Learning to coexist with wildfire. Nature. 515(7525): 58-66.
North, M.P., S. L. Stephens, B. M. Collins, J. K. Agee, G. Aplet, J. F. Franklin, and P. Z. Fulé. 2015. Reform forest fire management. Science. 18 September 2015: 1280-1281.
Rasker, R. 2015. Resolving the increasing risk from wildfires in the American West. Solutions. 6(2): 48-55.
Schoennagel, T., T.T. Veblen, W.H. Romme. 2004. The interaction of fire, fuels and climate across Rocky Mountain forests. BioScience. 54(7) 661-676.
Schoennagel, T., C.R. Nelson, D.M. Theobald, G. Carnwath, T.B. Chapman. 2009. Implementation of National Fire Plan fuel treatments near the wildland-urban interface in the western U.S. Proceedings of the National Academy of Sciences. 160: 10706-10711.
Stephens, S.L., J. K. Agee, P. Z. Fulé, M. P. North, W. H. Romme, T. W. Swetnam, M. G. Turner, 2013. Managing forests and fire in changing climates. Science. 342 (6154):41-42.
Turner M.G., Hargrove W.H., Gardner R.H., Romme W.H. 1994. Effects of fire on landscape heterogeneity in Yellowstone National Park, Wyoming. Journal of Vegetation Science. 5: 731–742. doi:10.2307/3235886.
Whitlock, C., Marlon, J., Briles, C., Brunelle, A., Long. C., and Bartlein, P.J. 2008. Long-term relations among fire, fuels, and climate in the northwestern U.S. based on lake-sediment studies. Journal of International Wildfire Research. 17 (1): 72-83.
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