Non-Indigenous Invertebrate Species in the Marine Fouling Communities of British Columbia, Canada
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BioInvasions Records (2016) Volume 5, Issue 4: 205–212 Open Access DOI: http://dx.doi.org/10.3391/bir.2016.5.4.03 © 2016 The Author(s). Journal compilation © 2016 REABIC Research Article Non-indigenous invertebrate species in the marine fouling communities of British Columbia, Canada Heidi N. Gartner1,*, Cathryn Clarke Murray2, Melissa A. Frey3, Jocelyn C. Nelson4, Kristen J. Larson5, Gregory M. Ruiz5 and Thomas W. Therriault6 1Royal British Columbia Museum, 675 Belleville St, Victoria, British Columbia, V8W 9W2, Canada 2North Pacific Marine Science Organization (PICES), P. O. Box 6000, Sidney, British Colubia, V8L 4B2, Canada 3Burke Museum of Natural History and Culture, University of Washington, Seattle, Washington, 98195, USA 4Department of Zoology and Biodiversity Research Centre, University of British Columbia, Vancouver, British Columbia, V6T 1Z4, Canada 5Smithsonian Environmental Research Center, 647 Contees Wharf Rd, Edgewater, Maryland, 21037, USA 6Fisheries and Oceans Canada, Pacific Biological Station, 3190 Hammond Bay Road, Nanaimo, British Columbia, V9T 6N7, Canada E-mail addresses: [email protected] (HNG), [email protected] (CCM), [email protected] (MAF), [email protected] (JCN), [email protected] (KJL), [email protected] (GMR), [email protected] (TWT) *Corresponding author Received: 19 May 2016 / Accepted: 30 August 2016 / Published online: 16 September 2016 Handling editor: John Mark Hanson Abstract Marine fouling communities on artificial structures are invasion hotspots for non-indigenous species (NIS). Yet, little is known about NIS in fouling communities of British Columbia (BC), Canada. To determine NIS identity and richness in BC fouling communities, we deployed settlement plates at 108 sites along the coast of BC between 2006 and 2012. Of the 295 invertebrate taxa identified to species, 20 were NIS while an additional 14 were cryptogenic, including several global invaders. This study documents the range expansion of tunicates Botrylloides violaceus Oka, 1927 and Botryllus schlosseri (Pallas, 1766), including the first known records on Haida Gwaii. NIS were detected within each of the six distinct geographic regions with the southern, more populated regions of BC (Straits of Georgia and Juan De Fuca) having the highest NIS richness and frequency of occurrence compared to the less populated northern regions. This study provides a contemporary baseline of invertebrate NIS identity and richness in fouling communities that will allow comparisons through time and a means to focus research and prioritize management efforts. Key words: non-native species, introduced species, invasion, Northeast Pacific, West Coast, North America, biofouling Introduction Zabin et al. 2014). The artificial structures (e.g. docks and pilings) in close proximity to these Globally, there is growing concern regarding the vectors serve as invasion hotspots (Ruiz et al. 2009). ecological and economic impacts of non-indigenous Monitoring fouling communities on these structures species (NIS) (Pimentel et al. 2000; Grosholz 2002; can be valuable for detecting new introductions to an Pimentel et al. 2005). Aquatic species are being area, determining temporal and spatial invasion transported from their native ranges to new areas, patterns, and informing management and policy mediated by a variety of anthropogenic vectors such decisions, including those that aim to mitigate the as aquaculture (Naylor et al. 2001), ballast water ecological and economic impacts of NIS. (Ruiz et al. 1997; Simkanin et al. 2009), and the In British Columbia (BC) Canada, little is known fouling of ship hulls and sea-chests (Coutts and about NIS identity and richness in these fouling Dodgshun 2007; Drake and Lodge 2007). Further, communities. There have been more than 120 non- secondary spread by additional vectors such as indigenous and cryptogenic species documented in recreational boats is contributing to observed invasion the marine and estuarine waters of BC (Levings et patterns at regional scales (Clarke Murray et al. 2011; al. 2002; Gillespie 2007; Lu et al. 2007). However, to 205 H.N. Gartner et al. Figure 1. Site locations (circles) of fouling communities sampled along the coast of British Columbia, Canada between 2006 and 2012. The six regions of the coast sampled are the Strait of Juan de Fuca (n=10), Strait of Georgia (n=28), West Coast of Vancouver Island (n=20), Johnstone Strait (n=23), Haida Gwaii (n=8), and North Coast (n=19). For details see supplementary material Table S1. date, these studies either have primarily focused on Georgia, had settlement plates continuously immersed intertidal environments (Gillespie 2007) or have from the spring of 2006 through the spring of 2007, been geographically limited to areas such as ports with sets retrieved every four months. In 2007 and (Richoux et al. 2006; Lu et al. 2007). There have 2011, settlement plates were deployed along the BC been no comprehensive studies of fouling communi- coast (at 81 and 24 sites, respectively) with the ties of the BC coast, including remote and seemingly settlement plates installed in the spring or early pristine locations. This study aims to provide an summer and retrieved the subsequent fall. In inventory of invertebrate NIS identity and richness addition, ports in Vancouver (4 sites; 2008–2012), of fouling communities along the BC coast. Victoria (6 sites; 2009–2012) and Prince Rupert (1 site; 2011) were monitored with settlement plates Methods installed in the spring or early summer and retrieved the subsequent fall. All plates installed in the spring Study area or early summer and retrieved the subsequent fall typically had 3 to 6 months for species recruitment The BC coastline spans more than 27,000 km along and community development. a complex of inlets, straits, passes, sounds, and narrows. There are six geographic regions where differences Settlement structures in oceanographic and physical features can influence the community composition of invertebrate fouling To characterize invertebrate fouling communities in communities (Thomson 1981; Zacharias and Roff BC, we deployed multiple settlement plates from 2001; Gillespie 2007). Between 2006 and 2012, we floating structures that were located primarily in sampled 108 sites within all six regions of the province: harbours and embayments. We used two settlement Strait of Juan de Fuca, Strait of Georgia, West Coast plate designs over the course of this study: 1) a plastic of Vancouver Island, Johnstone Strait, Haida Gwaii, circular base (30 cm diameter), with four plastic, and the North Coast (Figure 1; supplementary material circular Petri dishes (9 cm diameter) attached to Table S1). Eight sites, primarily in the Strait of each base, or 2) a single polyvinyl chloride (PVC) 206 Non-indigenous species in BC fouling communities square plate (14.5 × 14.5 cm). Each circular design 1935; Botrylloides violaceus Oka, 1927; and had two levels, with the first base suspended 15 cm Botryllus schlosseri (Pallas, 1766) (Table 1). Both S. below the surface and the second base 1 m below the japonica and C. mutica were present in all geographic first. Each PVC design had only one level that was regions, and were found at 42 (38.9%) and 34 (31.5%) suspended 1 m below the surface. In 2010, both plate sites, respectively. B. violaceus and B. schlosseri designs were deployed together at six sites (n = 97) were present in all geographic regions except the with no significant difference in species richness NC, and were found at 36 (33.3%) and 24 (22.2%) detected between the circular (mean = 12.49, SD = sites, respectively. 7.25) and square plate (mean = 11.38, SD = 7.83) design (t-test, t = 0.70, df = 95, p = 0.49). Cryptogenic species We detected cryptogenic species at 80 sites (74.1%) Sample processing and within each of the geographic regions of the Upon collection, the fouling community on each province (Table 1, Figure 3). Haida Gwaii had the settlement plate was immediately preserved in either highest proportion of sites with cryptogenic species formalin (10%) or ethanol (70%). In the laboratory, (87.5%), though this represents a wide distribution we sorted and identified all invertebrates larger than by a low number (n = 3) of cryptogenic species. The 1 mm to the lowest taxonomic level possible. Algae West Coast of Vancouver Island had the lowest occasionally grew in low abundance, mainly on the (60.0 %) proportion of sites with cryptogenic species. edges and top of the plates, but were not identified The most common cryptogenic species were: due to inappropriate preservation and lack of available Celleporella hyalina (Linnaeus, 1767); Obelia expertise. All invertebrate taxa were categorized as dichotoma (Linnaeus, 1758); Alcyonidium polyoum “NIS” (not native to the region), “cryptogenic” (Hassall, 1841); and Amathia gracili (Leidy, 1855) (unknown origin), “native” (native to the region) or (Table 1). Both C. hyalina and O. dichotoma were “unknown” (including taxa identified to genus or present in all geographic regions, and were found at higher, and those whose origin remains unclear). 54 (50.0%) and 49 (45.4%) sites, respectively. In Identification and status were determined using addition, A. polyoum, and A. gracilis were present in taxonomic descriptions and keys and correspondence all geographic regions except for Haida Gwaii, and with global experts (see Acknowledgements). We were present at 35 (32.4%) and 28 (25.9%) sites, listed taxa according to the World Register of respectively. It is important to