Abstract

Oceanic islands are biologically important for their unique assemblages of species and high levels of endemism and are sensitive to environmental change because of their isolation and small species source pools. Habitat destruction caused by human landscape development is generally accepted as the main cause of extinction on islands, with exotic species invasion a secondary cause of extinction, especially on tropical islands. However, secondary impacts of human development (e.g., general degradation through resource use and exotic species introduction) are understudied on temperate islands. To determine secondary impacts of human development on the understory vegetation community, 90 field sites on Ulleung Island, South Korea, were sampled during the summer of 2016. Understory vegetation was chosen as it is a proxy for ecosystem health. Diversity and percent cover of introduced, native, and endemic species were tested against proximity to developed areas and trail usage using a model selection approach. Diversity was also tested against percent cover of three naturalized species commonly found in survey plots. The main finding was that distance to development, distance to town, and trail usage have limited negative impacts on the understory vegetation community within best-supported models predicting native and introduced cover and diversity. However, endemic species cover was significantly lower on high usage trails. While there are no apparent locally invasive plant species on the island at the time of this study, percent cover of Robinia pseudoacacia, a naturalized tree species, negatively correlated with plot diversity. These findings indicate that forests on Ulleung Island are not experiencing a noticeable invasion of understory vegetation, and conservation efforts can be best spent preventing future invasions.

Highlights

  • Human colonization and landscape development of oceanic islands have caused a loss of global biodiversity through habitat loss and competition with and predation by exotic introduced species (Heywood, 1979; Sax and Gaines, 2008; Vitousek, 1988; Vitousek et al 1995)

  • Average percent cover is high in areas close to towns in the southeast corner of the island, where the majority of the island’s population and tourism occur

  • 87% of plots containing introduced species occur within 500 m of development and 100% of plots containing introduced species occur within 1 km of development

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Summary

Introduction

Human colonization and landscape development of oceanic islands have caused a loss of global biodiversity through habitat loss and competition with and predation by exotic introduced species (Heywood, 1979; Sax and Gaines, 2008; Vitousek, 1988; Vitousek et al 1995). This loss of biodiversity is due to the extinction of endemic species, or species that are found across a limited geographic range. Because of this isolation and lack of regional species source pools, island ecosystems can be more

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