Abstract

A monitoring programme was initiated in 2006 to detect invasive tunicates, especially Ciona intestinalis, Botryllus schlosseri, Didemnum vexillum, Botrylloides violaceus and Styela clava, in Atlantic Canada. Collectors were deployed at 11–21 monitoring stations in the southwestern New Brunswick portion of the Bay of Fundy from 2006-2009, starting in late May with some retrieved in August while others remained in the water until later in the fall. There was large variability between years and sites. C. intestinalis was detected through much of the southwest New Brunswick area, including Grand Manan Island, but not in the area from Dipper Harbour to Saint John. B. schlosseri was observed to be concentrated in the Dipper/Beaver Harbour areas and Grand Manan Island, St. Andrews Harbour, Fairhaven (Deer Island), and Harbour de Loutre (Campobello Island), with greatest settlement observed in 2009. During the study period, B. violaceus was first detected in 2009 and at only one location, Head Harbour, Campobello Island. S. clava and D. vexillum have not been detected from our sampling collectors to date. As the invasive colonial tunicate, D. vexillum, has rapidly extended its range in the northeastern United States of America and is within 2 km of Canadian waters, a rapid assessment was conducted around Deer Island and Campobello Island in September 2009 and failed to detect the species.

Highlights

  • There has been increased attention and documentation of the number and extent of the spread of aquatic invasive species (AIS) in the past several years (Carlton and Geller 1993; Leppäkoski et al 2002; Ricciardi and MacIsaac 2008)

  • Carver et al (2006a) documented C. intestinalis in a number of regions of Atlantic Canada including the south shores of Nova Scotia and Prince Edward Island

  • B. violaceus has been observed in adjacent areas such as Eastport, Maine (Osman and Whitlatch, 1995; as B. diegensis by Ritter and Forsyth, 1917; Dijkstra et al 2007a), Nova Scotia and Prince Edward Island

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Summary

Introduction

There has been increased attention and documentation of the number and extent of the spread of aquatic invasive species (AIS) in the past several years (Carlton and Geller 1993; Leppäkoski et al 2002; Ricciardi and MacIsaac 2008). D. vexillum has been documented as an aggressive and invasive colonial ascidian that is spreading along the New England coast (Bullard et al 2007a; Dijkstra et al 2007b; Lengyel et al 2009; Osman and Whitlatch 2007).

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