Abstract

Disturbance is a primary mechanism structuring ecological communities. However, human activity has the potential to alter the frequency and intensity of natural disturbance regimes, with subsequent effects on ecosystem processes. In Southern California, human development has led to increased fire frequency close to urban areas that can form a positive feedback with invasive plant spread. Understanding how abiotic and biotic factors structure post-fire plant communities is a critical component of post-fire management and restoration. In this study we considered a variety of mechanisms affecting post-fire vegetation recovery in Riversidean sage scrub. Comparing recently burned plots to unburned plots, we found that burning significantly reduced species richness and percent cover of exotic vegetation the first two years following a 100-hectare wildfire. Seed rain was higher in burned plots, with more native forb seeds, while unburned plots had more exotic grass seeds. Moreover, there were significant correlations between seed rain composition and plant cover composition the year prior and the year after. Collectively, this case study suggests that fire can alter community composition, but there was not compelling evidence of a vegetation-type conversion. Instead, the changes in the community composition were temporary and convergence in community composition was apparent within two years post-fire.

Highlights

  • Disturbance is critical to maintaining community composition and diversity [1]

  • In Southern California, human development has led to increased fire frequency close to urban areas that can form a positive feedback with invasive plant spread

  • Comparing recently burned plots to unburned plots, we found that burning significantly reduced species richness and percent cover of exotic vegetation the first two years following a 100-hectare wildfire

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Summary

Introduction

Disturbance is critical to maintaining community composition and diversity [1]. In Mediterranean-type ecosystems, plant communities have evolved with cool, wet winters and warm, dry summers with periodic fire disturbances during the dry season. A variety of fire-adapted functional types have emerged to allow plants to cope with this disturbance [2]. Primarily anthropogenic, changes to the frequency and severity of fire are impacting the effectiveness of fire adaptations [3], causing declines in abundances of many fire-adapted species, in particular long-lived shrubs [4]. The spread of invasive plants, which can increase with the accumulation of available nitrogen, can shift the trajectory of post-fire vegetation regeneration [5]. Understanding how fire alters vegetation in fire-prone ecosystems is important given that

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