Abstract

In the Pacific Northwest of North America, endangered Garry oak ecosystems have a complex history that integrates effects of Holocene climate change, Indigenous land management, and colonial settlement during the Anthropocene. In western Canada, Garry oak and Douglas fir recruitment corresponds with the end of the Little Ice Age (LIA; ca. 1870), after the collapse of Indigenous populations but in some cases prior to European settlement. We examined establishment patterns at three sites in southwest British Columbia, each with different edaphic characteristics based on slope, exposure, and drainage. At our Somenos Marsh site on Vancouver Island, we see a clear relationship between Indigenous occupation, subsequent European settlement, and development of an oak woodland, indicating that Indigenous land management was important for development of many Garry oak ecosystems. However, at the Tumbo Cliff site (Tumbo Island, BC), shallow soil xeric conditions, regional climate, and periodic fire were likely drivers of stand and ecosystem development. Finally, at the deep soil Tumbo Marsh site, Garry oak established and grew quickly when conditions were favorable, following the early twentieth century conversion of a saltwater tidal flat into a freshwater marsh. Combining site level historical records, site characteristics, and dendrochronological data provides a greater understanding of the local and regional factors that shape the unique structures of Garry oak ecosystems at each site. This information can be integrated into restoration and fire management strategies for Garry oak ecosystems as well as elucidate the timing of European settler and climate change impacts on these ecosystems.

Highlights

  • Garry oak (Quercus garryana) associated ecosystems are home to more than 100 threatened or endangered species (GOERT 2011) and are identified as a critically endangered ecosystem in North America (Noss et al 1995)

  • Several factors contribute to the decline of these ecosystems, including: (1) fragmentation and habitat loss (e.g., MacDougall et al 2004; Lea 2006; Bjorkman and Vellend 2010); (2) exotic and invasive species (e.g., Fuchs 2001; MacDougall and Turkington 2005; Devine and Harrington 2006; MacDougall et al 2010; Bennett et al 2013); (3) ungulate browsing (e.g., Gonzales and Arcese 2008; MacDougall 2008); (4) changes in historic disturbance regimes (e.g., Agee and Dunwiddie 1984; Gedalof et al 2006; Pellatt et al 2007; Smith 2007; McDadi and Hebda 2008; Dunwiddie et al 2011); and (5) climate change during and after the Little Ice Age (LIA) (e.g., Pellatt et al 2007)

  • These combined threats have degraded the ecological integrity of Garry oak ecosystems in British Columbia (BC) (Pellatt et al 2007) and left a mosaic of scattered single remnant trees or patchy stands (Erickson 2000; Fuchs 2001)

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Summary

Introduction

Garry oak (Quercus garryana) associated ecosystems are home to more than 100 threatened or endangered species (GOERT 2011) and are identified as a critically endangered ecosystem in North America (Noss et al 1995). A 378-year fire scar chronology from nearby Waldron Island in Washington, USA, indicates that fires were more frequent in Garry oak ecosystems prior to European settlement (Sprenger and Dunwiddie 2011) This idea is supported by evidence of cyclical burning practices by Indigenous peoples (Boyd 1999) and the dominance of fire adapted vegetation in intact Garry oak ecosystems (MacDougall 2005; Pellatt and Gedalof 2014). Combined with the effects of fire exclusion enforced by European settlers, the eventual canopy infilling by Garry oak and encroachment of conifer tree species occurred

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