Abstract

Feral pigs (Sus scrofa) are an invasive species that disrupt ecosystem functioning throughout their introduced range. In tropical environments, feral pigs are associated with predation and displacement of endangered species, modification of habitat, and act as a vector for the spread of exotic vegetation and disease. Across many parts of their introduced range, the diet of feral pigs is poorly known. Although the remote location and difficult terrain of far north Queensland makes observing feral pig behavior difficult, feral pigs are perceived to seek refuge in World Heritage tropical rainforests and seasonally ‘crop raid’ into lowland sugarcane crops. Thus, identifying how feral pigs are using different components of the landscape is important to the design of management strategies. We used the stable isotope composition of captured feral pigs to determine the extent of rainforest and sugarcane habitat usage. Recently grown hair (basal hair) from feral pigs captured in remote rainforest indicated pigs met their dietary needs solely within this habitat. Stable carbon and nitrogen isotope values of basal hair from feral pigs captured near sugarcane plantations were more variable, with some individuals estimated to consume over 85% of their diet within a sugarcane habitat, while a few consumed as much as 90% of their diet from adjacent forested environments. We estimated whether feral pigs switch habitats by sequentially sampling δ 13C and δ 15N values of long tail hair from a subset of seven captured animals, and demonstrate that four of these individuals moved between habitats. Our results indicate that feral pigs utilize both sugarcane and forest habitats, and can switch between these resources.

Highlights

  • Invasive feral pigs (Sus scrofa) have deleterious effects on ecosystem functioning across their introduced range [1]

  • We found no significant differences between male and female stable isotope compositions of hair (d13C value: Analysis of Variance (ANOVA) F1,39 = 0.04, p.0.5; d15N value: ANOVA F1,39 = 0.87, p = 0.36), there were significant differences in the stable isotope composition of hair between pigs captured in either rainforest, interface, or cane habitat (d13C value: ANOVA F2,38 = 12.92, p,0.001; Figure 3; d15N value: ANOVA F2,38 = 3.9, p = 0.03)

  • The lowest d13C value measured for pig hair was 225%, consistent with an approximately 97% C3 diet assuming a +3% enrichment factor and basline values of 228.5%, and 212.2% for rainforest and sugarcane, respectively. d13C values of basal hair from pigs captured in rainforest habitat displayed a reduced range compared to pigs captured from interface or sugarcane habitats, with only one significant outlier (Figure 3). d15N values of hair range from +4.1 to +11.2% and cannot be attributed to habitat due to variable d15N in habitats and potential diet

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Summary

Introduction

Invasive feral pigs (Sus scrofa) have deleterious effects on ecosystem functioning across their introduced range [1]. In the Australian tropics, feral pigs have been implicated in increased erosion, lowered water quality, shifting litter composition, as well as the modification of biogeochemical cycles, soil invertebrate and seed bank composition, and species successional patterns [4,5,6]. Diggings are the most visible impact of feral pigs in the World Heritage listed tropical rainforests of northern Queensland [4,5,6]. Seedling survival increased in feral pig exclosures, pig diggings did not affect earthworm biomass, litter composition, root mass, or soil moisture levels [5]. Assessing the role of feral pig activity on their surrounding environment requires an understanding of their diet, this aspect of pig ecology is largely unknown in tropical northern Queensland. Laurance and Harrington [4] hypothesized that feral pigs may feed on fungal sporocarps thereby competing with endangered northern bettongs, and recommended feral pig diet become a research priority

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