Regional-Scale Environmental Resistance to Non-Native Ant Invasion
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Regional-scale environmental resistance to non-native ant invasion R. J. Warren, M. Candeias, A. Lafferty & L. D. Chick Biological Invasions ISSN 1387-3547 Volume 22 Number 2 Biol Invasions (2020) 22:813-825 DOI 10.1007/s10530-019-02133-3 1 23 Your article is protected by copyright and all rights are held exclusively by Springer Nature Switzerland AG. This e-offprint is for personal use only and shall not be self- archived in electronic repositories. If you wish to self-archive your article, please use the accepted manuscript version for posting on your own website. You may further deposit the accepted manuscript version in any repository, provided it is only made publicly available 12 months after official publication or later and provided acknowledgement is given to the original source of publication and a link is inserted to the published article on Springer's website. The link must be accompanied by the following text: "The final publication is available at link.springer.com”. 1 23 Author's personal copy Biol Invasions (2020) 22:813–825 https://doi.org/10.1007/s10530-019-02133-3 (0123456789().,-volV)( 0123456789().,-volV) ORIGINAL PAPER Regional-scale environmental resistance to non-native ant invasion R. J. Warren II . M. Candeias . A. Lafferty . L. D. Chick Received: 3 February 2019 / Accepted: 9 November 2019 / Published online: 13 November 2019 Ó Springer Nature Switzerland AG 2019 Abstract A successful invasion of novel habitat to the dominant native woodland ant (Aphaenogaster). requires that non-native organisms overcome native We used observational data from long-term plots abiotic and biotic resistance. Non-native species can along the elevation gradient of the Southern Appa- overcome abiotic resistance if they arrive with traits lachian Mountain escarpment to investigate the pat- well-suited for the invaded habitat or if they can terns of B. chinensis invasion, and we used rapidly acclimate or adapt. Non-native species may physiological thermal tolerance, aggression assays co-exist with native species if they require novel, and stable isotope analysis to determine whether underused resources or if they can out-compete similar abiotic or biotic factors explained B. chinensis inva- native species. We investigated abiotic and biotic sion. We found that B. chinensis exhibited an inflex- resistance to the progression of a Brachyponera ible and relatively poor ability to tolerate cold chinensis invasion in the southeastern U.S. relative temperatures, which corresponded with limited suc- cess at higher elevations in the Southern Appalachian Mountains. Though we found native ant resistance to Electronic supplementary material The online version of B. chinensis invasion, it paled in comparison to the this article (https://doi.org/10.1007/s10530-019-02133-3) con- invasive ant’s ability to form huge, cooperating tains supplementary material, which is available to authorized supercolonies that eventually eliminated the native users. ant. Without biotic resistance, susceptible native R. J. Warren II (&) species may only be protected if they can tolerate SUNY Buffalo State, 1300 Elmwood Avenue, Buffalo, abiotic conditions that the invasive species cannot. For NY 14222, USA Aphaenogaster species, high elevations and northern e-mail: [email protected] latitudes beyond B. chinensis’ cold tolerance may be M. Candeias their only refuge. Department of Natural Resources, University of Illinois, W-503 Turner Hall 1102 South Goodwin Ave, Urbana, Keywords Aphaenogaster picea Á Aphaenogaster IL 61801, USA rudis Á Brachyponera chinensis Á Friendly release Á A. Lafferty Southern Appalachian Á Supercolony North Carolina State University, 3210 Ligon Street, Raleigh, NC 27695, USA L. D. Chick Hawken School, 12465 County Line Road, Gates Mills, OH 44040, USA 123 Author's personal copy 814 R. J. Warren II et al. Introduction formation of ‘supercolonies’ in which multiple, inter- connected nests essentially act as one—in contrast Non-native species must overcome native abiotic and with the more common monodomous (workers not biotic resistance to successfully invade novel territory. shared between nests) and monogyne (single queen Non-native species can overcome abiotic resistance if colonies) structure (Holway et al. 2002) in which they are equipped with traits well-suited for the workers enforce individual colony territories with invaded range habitat (Lee and Gelembiuk 2008; intraspecific aggression. Supercolony formation has Schlaepfer et al. 2010; Warren II et al. 2018b)orif been observed in several aggressive non-native they can rapidly adjust (‘niche shift’) to the novel species including: Linepithema humile (Mayr, 1868), habitat (Hill et al. 2013; Moran and Alexander 2014). Myrmica rubra (Linnaeus, 1758), Solenopsis invicta Once established, non-native species may co-exist (Buren, 1972), Wasmannia auropunctata (Roger, with native species if the invader requires novel 1863) and Brachyponera chinensis [Emery, 1895] resources, essentially occupying an ‘empty niche,’ (Eyer et al. 2018; Holway 1998; Krushelnycky et al. resulting in low interspecific competition (Stachowicz 2010; Warren II et al. 2018a). A lack of intraspecific and Tilman 2005); for example, non-native species competition and low territoriality allows non-native often thrive in anthropogenically altered habitat that is ant supercolonies to reach abundances far greater than relatively inhospitable for native species (King and co-occurring native ants, and observational studies Tschinkel 2008; Moles et al. 2012). Where non-native suggest that it gives the non-native ants an advantage species come in conflict with native species for shared against native ants (Holway et al. 1998; Suarez et al. resources, the non-native species often prevail because 2001; Tsutsui et al. 2000). Warren II et al. (2018a) they bring superior competitive abilities and are experimentally demonstrated that low intraspecific released from the burden of negative species interac- competition in non-native ants worked as a mecha- tions, such as predation, herbivory, disease and nism for invasive ant dominance given that intraspeci- territoriality (Callaway and Ridenour 2004; Liu and fic competition [ interspecific competition, which Stiling 2006; Warren II et al. 2018a). violates the key assumption of coexistence theory Ants are cosmopolitan (sans Antarctica) and crit- (Chesson 2000; Clark et al. 2012). As such, low ¨ ical components of the world’s biodiversity (Holl- intraspecific competition may give the ants a ‘‘friendly dobler and Wilson 1990). They are ecosystem release’’ that is as important for invasion success as engineers, predators, herbivores, scavengers, seed greater competitive ability or lack of enemies (Warren dispersers, pests and farmers (del Toro et al. 2012; II et al. (2018a) With that success, the dense, extensive Folgarait 1998; Warren II and Bradford 2012; Warren ant invasions coincide with considerable decreases in II and Giladi 2014) with distributions and behavior native ants and other invertebrates, as well as disrup- often delineated by large- and small-scale temperature tions of ecosystem services such as seed dispersal gradients (Diamond et al. 2017; Dunn et al. 2007; (Lach and Hooper-Bui 2009; Nelder et al. 2006; Warren II and Chick 2013). Their distributions also are Rodriguez-Cabal et al. 2012). impacted by human economic activity as ants travel Here, we examine abiotic and biotic influences on internationally via agricultural materials (McGlynn the progression of a B. chinensis invasion in the 1999; Suarez et al. 2005). As such, approximately 200 southeastern U.S. relative to the dominant forest ants ant species reside in habitats where they were intro- of the Aphaenogaster genus. We used observational duced outside their native range and, of those, data from long-term plots along the elevation gradient approximately 20 have spread profusely—negatively of the Southern Appalachian Mountain escarpment impacting native biodiversity as they move across the (northern Georgia, northwestern South Carolina and landscape (Bertelsmeier et al. 2017; Holway et al. southwestern North Carolina) and experimental data 2002; Suarez et al. 2010; Wetterer 2015). from physiological thermal tolerance analysis, aggres- Invasive ant populations typically share some sion assays and isotopic diet analysis to elucidate the general characteristics: most are omnivorous, unicolo- mechanisms behind the observed invasion. Given that nial (multiple nests share workers) and polygynous co-occurring Aphaenogaster ants exhibit an increased (multiple queens in nests) (Holway et al. 2002). Ants ability to tolerate cold temperatures with increased from unicolonial, polygynous colonies support the elevation (Warren II and Chick 2013), we expected 123 Author's personal copy Regional-scale resistance 815 similar thermal plasticity in B. chinensis along the (Guenard and Dunn 2010; Ipser et al. 2004; Smith same gradients. Alternately, given that the invaded- 1934). Brachyponera chinensis typically invades range B. chinensis appears to originate from a small forest habitat, living in downed wood, but also has portion of its native range (Yashiro et al. 2010), it may been found in suburban and urban settings (Guenard have underwent a bottleneck or founder effect and lack and Dunn 2010; Pecarevic et al. 2010; Rice and the thermal plasticity to acclimate or adapt to colder Silverman 2013). Brachyponera chinensis forms high elevation temperatures. Given that Warren II polydomous nests that can contain thousands of et al. (2015)