Abstract

Fire disturbance is considered a major factor in the promotion of non-native plant species. Non-native grasses are adapted to fire and can alter environmental conditions and reduce resource availability in native coastal sage scrub and chaparral communities of southern California. In these communities persistence of non-native grasses following fire can inhibit establishment and growth of woody species. This may allow certain native herbaceous species to colonize and persist beneath gaps in the canopy. A field manipulative experiment with control, litter, and bare ground treatments was used to examine the impact of non-native grasses on growth and establishment of a native herbaceous species, Cryptantha muricata. C. muricata seedling survival, growth, and reproduction were greatest in the control treatment where non-native grasses were present. C. muricata plants growing in the presence of non-native grasses produced more than twice the number of flowers and more than twice the reproductive biomass of plants growing in the treatments where non-native grasses were removed. Total biomass and number of fruits were also greater in the plants growing in the presence of non-native grasses. Total biomass and reproductive biomass was also greater in late germinants than early germinants growing in the presence of non-native grasses. This study suggests a potential positive effect of non-native grasses on the performance of a particular native annual in a southern California ecosystem.

Highlights

  • The decline of native plant species in disturbed areas has been linked to effects of competition for light and soil resources with non-natives [1], [2], [3]

  • There was no difference among sites, there was a significant difference among treatments in overall soil water potential (Table 1)

  • Cryptantha muricata plants surrounded in the control treatment by non-native grasses with 100% cover and height of 0.5 m60.2 SE performed differently in many respects from those in plots where grasses were removed

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Summary

Introduction

The decline of native plant species in disturbed areas has been linked to effects of competition for light and soil resources with non-natives [1], [2], [3]. Most coastal sage scrub and chaparral species are adapted to intense but infrequent fires [8] In such conditions the ephemeral post-fire native community, consisting primarily of annual (60%) and perennial (20%) herbaceous species, is able to dominate for only one to three years before the shrub canopy closes [9]. With an increase in fire frequency, recruitment of fire-adapted native woody species may be hindered, slowing the formation of a closed woody canopy [9], [7]. Under these conditions non-native grasses and other herbaceous species persist longer after fire, and grasses may dominate patches in mature coastal sage scrub and chaparral communities [8]. The exact role of non-native grasses during recovery of these plant communities from fire remains unclear

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