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Impacts of a Non-Native Gastropod with a Limited Distribution; Less Conspicuous Invaders Matter Too

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Impacts of a Non-Native Gastropod with a Limited Distribution; Less Conspicuous Invaders Matter Too Vol. 537: 151–162, 2015 MARINE ECOLOGY PROGRESS SERIES Published October 14 doi: 10.3354/meps11469 Mar Ecol Prog Ser FREEREE ACCESSCCESS Impacts of a non-native gastropod with a limited distribution; less conspicuous invaders matter too Jason P. Hendrickx1, Robert G. Creese2, Paul E. Gribben3,* 1Plant Functional Biology and Climate Change Cluster, and School of the Environment, University of Technology, Sydney, NSW 2007, Australia 2New South Wales Department of Primary Industries, Port Stephens Fisheries Institute, Nelson Bay, NSW 2315, Australia 3Centre for Marine BioInnovation, and School of Biological, Earth and Environmental Sciences, University of New South Wales, Sydney, NSW 2052, Australia ABSTRACT: Most studies focus on fast-spreading invasive species with high impacts, whilst invasive species with restricted distributions tend to be neglected in the ecological literature. The New Zealand gastropod, Zeacumantus subcarinatus, introduced into the Sydney region during the 1920−1930s, typically occurs in rock pools in the mid- to high intertidal. Surveys conducted in 2004 indicated Z. subcarinatus had a restricted distribution, but little is known about whether it is spreading, the environmental conditions that may promote or inhibit its spread, or its interactions with native species. Surveys conducted in 2012 and 2015 showed Z. subcarinatus maintained a similar distribution to that described in 2004. However, rock pools at sites where Z. subcarinatus was present or absent differed in key characteristics. Rock pools at sites lacking Z. subcarinatus had higher cover of macroalgae, reduced cover of bare substratum and higher densities of native gastropods. At invaded sites, there was a significant negative relationship between Z. subcarina- tus and native gastropod densities. Experimental manipulation of Z. subcarinatus confirmed negative effects on the colonization of rock pools by the native gastropod Bembicium nanum, possibly via competition for resources. Impacts on B. nanum were discernable at low and high densities of Z. subcarinatus. By contrast, Z. subcarinatus responded positively to density manipu- lations of B. nanum — possibly higher densities of B. nanum indicate higher resource availability. We have shown that invasive species that have restricted distributions can have significant effects on native fauna and that they potentially deserve more research and management consideration than they currently receive. KEY WORDS: Invasive species · Zeacumantus subcarinatus · Impact · Competition · Density- mediated interactions · Distribution · Environmental characteristics · Gastropod Resale or republication not permitted without written consent of the publisher INTRODUCTION to native communities, possibly resulting in an underestimation of their impacts on native biota or Most studies on invasive species focus on fast- the ecosystems in their introduced ranges. Clearly, spreading species with high impacts. Much less is the study of invasion ecology and the management of known about invasive species that do not spread rap- invasive species would benefit from a broader under- idly, that do not have broad distributions, or whose standing of the processes determining the spread impacts (negative or positive effects on abundance, and impacts not just of species of noted concern (e.g. fitness and/or life-history traits) on native biota may those on the top 100 most invasive species list, Lowe be more subtle. Such a research bias may lead to the et al. 2000) but also for the vast majority of non-native misleading assumption that invasive species with species that are considered less of a threat to the limited distributions are merely innocuous additions native species and ecosystems they invade. *Corresponding author: [email protected] © Inter-Research 2015 · www.int-res.com 152 Mar Ecol Prog Ser 537: 151–162, 2015 Once introduced into a new community, environ- Invasive marine invertebrates have a diverse range mental characteristics (biotic and abiotic) can influ- of impacts in their exotic ranges. Invasive crabs and ence the subsequent spread and ultimately the range starfish are often voracious predators (Grosholz et al. of invasive species. For example, disturbed environ- 2000, Ross et al. 2002, 2004), and invasive habitat- ments often promote the spread of invasive species forming bivalves and ascidians can enhance biodiver- (Hobbs & Huenneke 1992, Burke & Grime 1996, sity by providing habitat (Crooks 1998, Castilla et al. Valentine & Johnson 2003, Bulleri & Benedetti- 2004) but also outcompete native invertebrates. Al- Cecchi 2008). By contrast, more species-rich, undis- though less well documented, exotic marine gas- turbed environments may more efficiently utilise tropods also affect native marine biota. The common available resources such as space and food and limit periwinkle Littorina littorea is one of the most abun- the establishment and spread of invasive species (i.e. dant molluscs in its invaded range in the Northwest species-rich environments may provide biotic resist- Atlantic, reaching densities of several hundred indi- ance to invasion) (Stachowicz et al. 1999, Kennedy et viduals per square meter (e.g. Petraitis 1987, Carlson al. 2002). In addition, the availability of suitable habi- et al. 2006). By ‘bulldozing’ fine depositional sedi- tat can also limit the spread of invasive species (Byers ments from hard substrata and consuming the shoots 2002). Thus we may predict that environmental con- of saltmarsh, L. littorea changes communities from ditions — biotic, abiotic or both — differ at sites that those indicative of soft-sediment habitats to those rep- are occupied and unoccupied by invasive species. resentative of rocky shores (Bertness 1984). In north- Although determining the mechanisms underpin- ern California, high conversion efficiency of resources ning the spread of invasive species can be challeng- by the invasive mudsnail Batillaria atramentaria leads ing, quantitative surveys comparing environmental to competitive exclusion of the native mudsnail characteristics at sites where invasive species have Cerithidea californica (Byers 2000), although facilita- established compared to those where they are absent tion of native species by invasive Batillarids (e.g. B. can provide valuable insights into the processes that atramentaria and B. australis) has also been observed may promote or limit their spread and potential (Wonham et al. 2005, Thyrring et al. 2013). impacts. Such surveys are necessary for developing Another intertidal Batillarid, Zeacumantus subcari- and testing hypotheses regarding processes that may natus, has colonised intertidal rocky habitat (in par- underpin the success or failure of non-native species. ticular rock pools) in Sydney, Australia (Andrews et Once established, invasive species can have broad- al. 2010). Native to New Zealand (Morton & Miller ranging effects on native communities (Mack et al. 1968), Z. subcarinatus was introduced into the Syd- 2000, Levine et al. 2003, Thomsen et al. 2009, ney Region in the 1920s or 1930s, probably via trans- Gribben et al. 2013). Studies often employ invader Tasman shipping (Powell 1979). Z. subcarinatus has presence/absence experiments, comparing treat- not been recorded as an invader anywhere else in ments with no invader with those of high invader the world. The only formal survey of Z. subcarinatus density to understand their interactions with native around the Sydney Metropolitan Region was con- species (e.g. Neira et al. 2006, Wright & Gribben ducted in 2004 and it was present at 9 out of 32 sur- 2008, Gribben et al. 2009, Byers et al. 2010). Impor- veyed sites (Andrews et al. 2010). Comparison of this tantly, the impacts of invasive species can change survey with records held at the Australian Museum with their density (Thomsen et al. 2011, Gribben et al. suggests that it had disappeared from 8 sites where it 2013) and even low densities of invasive species can had been previously recorded and had established in affect native species (Bulleri et al. 2010, Elgersma & one previously unrecorded site (Australian Museum Ehrenfeld 2011). However, we still know little about Malacological Database; see Andrews et al. 2010 for whether the impacts of invasive species are consistent detailed introduction history; their Fig. 1). Z. subcari- with increases in invader density, and the potential natus was twice as abundant in rock pools containing for invasive species to have significant impacts at higher levels of coarse sand and shell material, much lower densities than are commonly manipu- although few environmental attributes were meas- lated. Multiple density treatments are necessary for ured, and the abundance of some littorinids was not only advancing our understanding of the relation- approx. 3 times lower in rock pools containing Z. sub- ships between native and invasive species, but also carinatus compared to rock pools where they were for making informed decisions. For example, if the ef- absent (Andrews et al. 2010). However, little is fects of invasive species manifest at low densities, known about whether Z. subcarinatus is spreading, then appropriate management actions may need to the environmental characteristics (abiotic or biotic) occur at lower, not just higher, invader densities. that may promote or inhibit its distribution, or how it Hendrickx et al.: Impacts of an invasive gastropod 153 interacts with native biota. These are the key issues addressed in this study. We used quantitative surveys to investigate
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