Abstract

AbstractThroughout the Sierra Nevada, nearly a century of fire suppression has altered the tree species composition, forest structure, and fire regimes that were previously characteristic of montane forests. Species composition is fundamentally important because species differ in their tolerances to fire and environmental stressors, and these differences dictate future forest structure and influence fire regime attributes. In some lower montane stands, shade‐tolerant, fire‐sensitive species have driven a threefold increase in tree density that may intensify the risk of high‐severity fire. In upper montane forests, which were historically characterized by longer fire return intervals, the effects of fire exclusion are both less apparent and less studied. Although land managers have been reintroducing fire to lower and upper montane forests for >4 decades, the potentially restorative effects of these actions on species composition remain largely unassessed. We used tree diameter and species data from 51 recently burned and 46 unburned plots located throughout lower and upper montane forests in Yosemite National Park and Sequoia & Kings Canyon National Parks to examine the effects of low‐ to moderate‐severity (hereafter, lower‐severity) fire on the demography of seven prevalent tree species. The density of Abies concolor <30 cm diameter at breast height (dbh) was significantly lower in burned plots than unburned plots; densities of A. concolor 30–45 cm dbh, A. magnifica <30 cm dbh, and Calocedrus decurrens <15 cm dbh were lower in burned plots than unburned plots at a marginal level of significance. These diameter thresholds represent the maximum size at which each species is likely to experience significant mortality from lower‐severity fire. We overlaid these thresholds on historical and contemporary diameter distributions to show that: (1) lower‐severity fire has reduced mean tree density to historical levels for A. concolor but not for C. decurrens, and (2) variability in tree density among plots that burned at lower severity exceeded the range of tree densities reported in historical data sets. High proportions of shade‐tolerant species in some postfire stands may increase the prevalence of shade‐tolerant species in the future, a potential concern for managers who seek to minimize ladder fuels and promote forest structure that is less prone to high‐severity fire.

Highlights

  • Across the dry forests of western North America, a century of fire suppression has resulted in widespread change in tree species composition and structure, driven by greater abundance of fire-s­ ensitive, shade-t­olerant tree species (Parsons and DeBenedetti 1979, Dolanc et al 2014, Stephens et al 2015)

  • The A. concolor centroid was centrally located, marking the convergence of two lower montane and two mid-e­ levation forest alliances, Pinus ponderosa–Calocedrus decurrens, Abies concolor–Pinus lambertiana, Abies magnifica–Abies concolor, and Pinus jeffreyi, and reflecting that A. concolor was present in more plots (63) than any other species (Fig. 2A)

  • We examined the effects of fire reintroduction on tree species communities at the broad scale of the v www.esajournals.org central Sierra Nevada, using the relatively undisturbed forests of Yosemite and Sequoia & Kings Canyon National Parks

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Summary

Introduction

Across the dry forests of western North America, a century of fire suppression has resulted in widespread change in tree species composition (i.e., the proportion and abundance of tree species; hereafter, composition) and structure (i.e., the density, basal area, and spatial arrangement of stems), driven by greater abundance of fire-s­ ensitive, shade-t­olerant tree species (Parsons and DeBenedetti 1979, Dolanc et al 2014, Stephens et al 2015). 2016), fire reintroduction is hindered by accumulations of ground and ladder fuel that increase the risk of high-­severity fire (Thode et al 2011). Management objectives in this context have focused on restoring fire, reducing fuels, and creating forest structure that can support a low-­ severity fire regime (North et al 2007, Schwilk et al 2009). Species composition affects the trajectory and pace of forest structural development (Kobe et al 1995) and should factor in to management strategies to reduce tree density

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