Abstract

In mixed-conifer forests inhabited by California spotted owls, land managers hypothesize that without human intervention natural conifer regeneration will take many decades or longer to begin within interior areas of large high-severity fire patches, due to long distances from live tree seed sources. As a result, widespread post-fire logging, followed by sprayed application of herbicides and planting of conifer seedlings, are used to create tree plantations. These are activities routinely conducted in spotted owl territories following fires, despite current data that indicate this approach has adverse impacts on spotted owl occupancy. Land managers acknowledge such impacts, but continue these forest management practices, assuming they are a necessary harm, one that is warranted to ensure the later return of mature conifer forests used by spotted owls for nesting and roosting. However, few data have been gathered to test this hypothesis. At 5 years post-fire, we surveyed field plots on a grid within large high-severity fire patches in spotted owl habitat within the Rim fire of 2013 in the Sierra Nevada, California. In our analysis the percentage of plots lacking conifer regeneration decreased significantly with larger plot sizes, a finding contrary to previous studies which assumed vast “deforested” areas in wildland fires, a bias created by small plot size. We found higher conifer regeneration closer to live-tree edges, but we consistently found natural post-fire conifer regeneration at all distances into interior spaces of large high-severity fire patches, including >300 m from the nearest live trees. Distance from live-tree edges did not affect pine dominance in post-fire regeneration. The post-fire natural conifer regeneration reported in our results suggests that the adverse effects of current post-fire management in spotted owl habitat are not necessary practices that can be justified.

Highlights

  • In ponderosa pine (Pinus ponderosa) and mixed-conifer forests inhabited by California spotted owls (Strix occidentalis occidentalis) in the Sierra Nevada mountains, historical fire regimes were characterized by a mix of fire severities, comprised primarily of low/moderate-severity effects and including substantial occurrence of high-severity fire (Mallek et al, 2013; Baker, 2014; Odion et al, 2014; Doerr and Santín, 2016; Baker and Hanson, 2017), in which most or all live trees become snags (Miller and Thode, 2007)

  • While it is clear from numerous lines of evidence that large high-severity fire patches occurred historically in relatively frequent-fire forest types like ponderosa pine and mixed-conifer in the Sierra Nevada (Leiberg, 1902; Baker, 2014; DellaSala and Hanson, 2019), debate remains about the historical frequency of occurrence of large patches of high-severity fire in these forests and concern exists about the Impacts of Postfire Management Unjustified response of forest ecosystems to some large fires that have occurred in recent years (Stephens et al, 2013; Hessburg et al, 2016; Stevens et al, 2016)

  • We investigated natural post-fire conifer regeneration in highseverity fire areas within spotted owl habitat by surveying plots on a grid within large high-severity fire patches in the Rim fire of 2013 within ponderosa pine and mixed-conifer forests inhabited by California spotted owls (Lee and Bond, 2015)

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Summary

Introduction

In ponderosa pine (Pinus ponderosa) and mixed-conifer forests inhabited by California spotted owls (Strix occidentalis occidentalis) in the Sierra Nevada mountains, historical fire regimes were characterized by a mix of fire severities, comprised primarily of low/moderate-severity effects and including substantial occurrence of high-severity fire (Mallek et al, 2013; Baker, 2014; Odion et al, 2014; Doerr and Santín, 2016; Baker and Hanson, 2017), in which most or all live trees become snags (Miller and Thode, 2007). Other research has reported substantial and heterogeneous natural post-fire conifer regeneration in large high-severity fire patches, even hundreds of meters away from surviving trees, due to a combination of wind dispersal of seeds and dispersal by native birds and small mammals (Owen et al, 2017; Hanson, 2018)

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