Abstract

Fire is an ecologically significant process in the fire-prone ponderosa pine and mixed conifer forests of the northern Sierra Nevada. Fire regimes are influenced by processes that operate over a range of scales that can be grouped broadly as bottom-up (e.g., topography, forest type) or top-down (e.g., climate variation, human land use) controls. To identify the bottom-up versus top-down controls on fire regimes, we quantified spatial and temporal variation in fire occurrence and extent using fire-scar dendrochronology. Inter-annual climate variability and human land use patterns strongly influenced fire regimes. Years of widespread burning and fire-free years were associated with dry and wet years, respectively. Variation in fire activity was also associated with variation in the El Nino-Southern Oscillation (ENSO) and the Pacific Decadal Oscillation (PDO). Widespread burning occurred during La Nina years (cool ENSO) and during positive conditions of the PDO (warm PDO). Fire occurrence declined with Euro-American settlement in the nineteenth century and only two fires were recorded in the study area after 1905, the date fire suppression was implemented. Fire regimes were also influenced by bottom-up controls. Fire return intervals (FRI) were shorter in pine-dominated low-elevation forests than in high-elevation fir-dominated mixed conifer forests, although FRI did not vary by slope aspect.

Highlights

  • Wildfire is the most ecologically significant process affecting fire-prone ponderosa pine and mixed conifer forests of the Sierra Nevada (Skinner and Chang 1996)

  • A total of 301 fires were identified in the 180 cross-dated wood samples from live

  • We determined the season of fire occurrence for 1345 (68 % of total) fire scars

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Summary

Introduction

Wildfire is the most ecologically significant process affecting fire-prone ponderosa pine and mixed conifer forests of the Sierra Nevada (Skinner and Chang 1996). In turn, are controlled by processes that operate over a range of spatial and temporal scales. Bottom-up controls such as variation in vegetation type or slope aspect (e.g., Taylor 2000, Heyerdahl et al 2001), or time since last fire (e.g., Taylor and Skinner 2003, Scholl and Taylor 2010) influence the type, arrangement, moisture, and connectivity of forest fuels, and fire occurrence at local scales. Determining the relative influence of bottom-up and top-down controls requires analyses of fire regimes at both fine and coarse spatial scales (Heyerdahl et al 2001, Taylor and Skinner 2003, Taylor et al 2008)

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