Short communicationIndirect impacts of invaders: A case study of the Pacific sheath-tailed bat (Emballonura semicaudata rotensis)
Introduction
Global conservation for bats is needed: 15% of species are listed as extinct or threatened, 17% do not have a threat status owing to insufficient data, and over half have unknown population trends (IUCN, 2015). Moreover, bats are an oddity among mammals in that roughly a quarter of species are island endemics (Jones et al., 2009), making them important members of island communities. Given uncertainty regarding population viability and their significant contribution to island diversity, research on threats to bats is a priority for conservation (Mickleburgh et al., 2002).
Endangerment and extinction occur disproportionately on islands, in part owing to island systems vulnerability to invaders (Gimeno et al., 2006). Biological invasion can have profound ecological and socioeconomic impacts of isolated ecosystems (reviewed in Reaser et al., 2007). Studies on how biological invasions affect bats have focused on direct interactions, such as predation and epidemiology of introduced pathogens (e.g., Fritts and Rodda, 1993, Rodriquez-Duran et al., 2010). Few have evaluated indirect effects — how interactions between coexisting species are affected by another species (Strauss, 1991) — on bats.
The Pacific sheath-tailed bat (Emballonura semicaudata) is a small insectivore designated “endangered” because its geographic area is < 5000 km2 and highly fragmented (Bonaccorso and Allison, 2008). Emballonura semicaudata rotensis is a subspecies formerly distributed across limestone islands of Guam and the Commonwealth of the Northern Mariana Islands (CNMI) but now present only on the uninhabited island of Aguiguan (Wiles et al., 2011). The estimated 500 individuals of E. s. rotensis are commonly detected in forests and roost primarily in three caves (Wiles et al., 2011). Consequently, E. s. rotensis is highly vulnerable to stochastic demographic and environmental events.
Unconfirmed threats to E. s. rotensis include invasive species (Berger et al., 2005). Shrub covers at least 20% of Aguiguan (150 ha) and is dominated by lantana (Lantana camara) (Amidon, 2009), a “top 100” invasive species (IUCN, 2001). Many studies have shown that lantana can greatly alter native community structure (see review by Sharma et al., 2005), though its impacts on Aguiguan remain unstudied. Feral goats (Capra hircus) were introduced to Aguiguan during the mid-1800s (Butler, 1992), and their density has reached over 200 individuals per square kilometer (Esselstyn et al., 2002), earning Aguiguan the nickname “Goat Island”. The detrimental effects of goats on Aguiguan's native species are largely anecdotal.
Here, we consider the conservation of E. s. rotensis to illustrate indirect impacts of invasion. We hypothesized that goat browsing and lantana spread indirectly impact E. s. rotensis by altering habitat structure and prey abundances. To evaluate our hypotheses, we ask: (1) Do bats behave differently in lantana shrub than in native forest, and what factors account for this pattern? and (2) Does native understory cover indicate goat browsing, and is bat activity related to the structural complexity of native forest?
Section snippets
Study system
We conducted this study on Aguiguan, CNMI, (14°51′N, 145°33′E) from May 28 to June 14, 2013. The 7.09 km2 island consists of three concentric limestone plateaus (Fig. 2). Native limestone forest occurs primarily along the smaller terraces of the island and on steep slopes. The dominant native tree species are Pisonia grandis, Cynometra ramiflora, and Guamia mariannae (Esselstyn et al., 2002). Exotic grasses, Jatropha gossypiifolia, and Chromolaena odorata seedlings are interspersed with lantana
Do bats behave differently in lantana shrub than in native forest, and what factors account for this pattern?
Bats were more active in native forest than lantana shrub (probability of recorded calls in native forest > lantana shrub = 0.993; Table A2; Fig. A1), though bats were not detected at every native forest site (Fig. A2). Considerable differences in bat activity across native forest sites support the hypothesis that within-habitat structure is an important consideration for species management (Sharma et al., 2005). Bats were relatively inactive in lantana shrub when temperature was high (ρ = − 0.198, P =
Conclusion
To improve management of endangered species, a first step is to identify and alleviate ongoing threats. Although indirect impacts of invasive species on native populations are plausible in many cases, most proposed consequences of invasion lack supporting research. Our results indicate that indirect impacts of lantana on the population of E. s. rotensis have been underestimated. Bats are largely inactive in lantana shrub, where the microclimate is harsh and prey are scarce, making remaining
Acknowledgments
We thank the following for their expertise and logistical assistance on this project: Gary McCracken, Tammy Mildenstein, Haldre Rodgers, Ton Castro, Anthony Deleon Gurrero, Commonwealth of the Northern Mariana Islands Department of Fish and Wildlife, Mayor's Office of Tinian. We thank Zach Marion, St. Thomas LeDoux, and anonymous reviewers for assistance with the manuscript. Funding: This work was supported by Sigma Xi [grant number G20120315161439]; Bat Conservation International [grant number
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