Description
Synonymy- The name Diplosoma macdonaldi was widely used for North American populations, both on the East and West Coast, (e.g., Van Name 1945), before Kott's (1990) revsion, which synonymized many of the worldwide populations.
Taxonomy
Kingdom | Phylum | Class | Order | Family | Genus |
---|---|---|---|---|---|
Animalia | Chordata | Ascidiacea | Aplousobranchia | Didemnidae | Diplosoma |
Synonyms
Invasion History
Chesapeake Bay Status
First Record | Population | Range | Introduction | Residency | Source Region | Native Region | Vectors |
---|---|---|---|---|---|---|---|
2001 | Established | Unknown | Introduced | Regular Resident | Western Atlantic | Unknown-Marine | Shipping(Fouling Community) |
History of Spread
The colonial tunicate Diplosoma listerianum was first described from the English Channel by Milne-Edwards in 1841. This species was described, under different names, from many different places around the world, such as Australia (D. rayneri Macdonald 1859) Brazil (D. macdonaldi Herdman 1886), and Japan (D. mitsakurii Oka 1892). These and many other names were synomized by Kott (1990; 2001). In most parts of its present range, including the West Coast (NE Pacific, San Diego CA to Vancover Island, British Columbia) (Lambert and Lambert 2001), and Southeast Coast of North America, (south of Cape Hatteras) D. listerianum has long been considered native. Gretchen Lambert now considers D. listerianum to be a species possibly of Northeast Atlantic origin, probably introduced over most of its range by the beginning of the 20th century (Lambert 2004, personal communication). However, recent invasions of this tunicate are documented on the Northeastern Coast of North America (Gulf of Maine to the Chesapeake Bay). Populations on several Pacific Islands (Pearl Harbor, Oahu, HI), Guam, and New Zealand, are considered to be introduced (Coles et al. 1999; Cranfield et al. 1998; Lambert 2002).
On the East Coast, D. listerianum was collected in 1880 in the Atlantic Ocean off SC, and subsequently found from NC to FL, in the Gulf of Mexico (U.S. National Museum of Natural History 2002; Van Name 1921). Its first reported occurrence north of Cape Hatteras was in Long Island Sound (Groton CT) around 1990 (Whitlach et al. 1995). It was found in Narragansett Bay RI and Vineyard Sound MA in 1998 (Whitlach and Osman 2000), in the southern Gulf of Maine, at Star Island NH, in 1996 (Harris and Tyrell 2001), in Great Bay, near Portsmouth NH in 1997 (Blezard 1999), Cape Neddick ME in 1999, and Portland ME in 2000 (Harris and Tyrell 2001; MIT Sea Grant 2003).
There are no published records of D. listerianum between Long Island Sound and Cape Hatteras. However, specimens of this tunicate were found on fouling plates in lower Chesapeake Bay near Cape Charles VA in 2001, and again in 2002. Identifications were confirmed by Gretchen Lambert. At this site, these colonies appeared to be abundant. In 2002, this tunicate was also found in Lynnhaven Bay, Virginia Beach VA (Ruiz et al., unpublished data).
References- Blezard 1999; Coles et al. 1999; Cranfield et al. 1998; Harris and Tyrell 2001; Kott 1990; Kott 1998; Kott 2001; Lambert and Lambert 1998; Lambert 2002; U.S. National Museum of Natural History 2002; Van Name 1921; Whitlach et al. 1995; Whitlach and Osman 2000
Invasion Comments
Ecology
Environmental Tolerances
For Survival | For Reproduction | |||
---|---|---|---|---|
Minimum | Maximum | Minimum | Maximum | |
Temperature (ºC) | -1.0 | 10.0 | 25.0 | |
Salinity (‰) | 24.0 | 40.0 | ||
Oxygen | ||||
pH | ||||
Salinity Range | poly-eu |
Age and Growth
Male | Female | |
---|---|---|
Minimum Adult Size (mm) | ||
Typical Adult Size (mm) | 50.0 | |
Maximum Adult Size (mm) | 50.0 | |
Maximum Longevity (yrs) | 10.0 | 10.0 |
Typical Longevity (yrs | 4.5 | 4.5 |
Reproduction
Start | Peak | End | |
---|---|---|---|
Reproductive Season | |||
Typical Number of Young Per Reproductive Event |
|||
Sexuality Mode(s) | |||
Mode(s) of Asexual Reproduction |
|||
Fertilization Type(s) | |||
More than One Reproduction Event per Year |
|||
Reproductive Startegy | |||
Egg/Seed Form |
Impacts
Economic Impacts in Chesapeake Bay
The abundance and distribution of the colonial tunicate Diplosoma listerianum is unknown in Chesapeake Bay, as are its economic impacts.
Economic Impacts Outside of Chesapeake Bay
In many parts of the world, the colonial tunicate Diplosoma listerianum is an abundant fouling organism (Lambert 2002), known from docks, buoys, floats, and ship hulls (Woods hole Oceanographic Institution 1951)..
Fisheries- Diplosoma listerianum has been reported to foul cultured shellfish in the United Kingdom (Isle of Man), Croatia, Japan, and Hong Kong (Ross et al. 2004, Igic 1972, Arakawa 1990, Huang 2003, cited by da Rocha et al. 2009). Da Rocha et al. suggest that the impact might be small, because of the thinness of the colonies.
Ecological Impacts on Chesapeake Native Species
The present impacts of the colonial tunicate Diplosoma listerianum on native biota in Chesapeake Bay are unknown, since we know little of its distribution and abunance in the Bay. In experiments in Long Island Sound, Diplosoma listerianum significantly reduced recruitment of Spirorbis spp., Bugula spp., and Balanus spp., mostly through overgrowth of newly settled individuals (Osman and Whitlach 1995).
References- Whitlach and Osman 1995
Ecological Impacts on Other Chesapeake Non-Native Species
The present impacts of the colonial tunicate Diplosoma listerianum on exotic or cryptogenic biota in Chesapeake Bay are unknown, since we know little of its distribution and abundance in the Bay.
Competition- Ecological Impacts- In experiments in Long Island Sound, Diplosoma listerianum significantly reduced recruitment of native Spirorbis spp., Bugula spp., and Balanus spp., mostly through overgrowth of newly settled individuals (Osman and Whitlach 1995). Diplosoma listerianum also significantly reduced recruitment of non-indigenous Botryllus schlosseri and Botrylloides violaceus, mostly through overgrowth of newly settled individuals (Osman and Whitlach 1995). Disturbance enhanced the spread of D. listerianum (Altman and Whitlach 2007). Diplosoma listerianum was a strong competitor in filling up empty space on fouling plates (Stachowicz et ak. 2002). In Eel Pond, Woods Hole, Massachusetts, Diplosoma listerianum outgrew Botrylloides violaceus and other organisms on fouling plates, covering ~72% of the plates at the end of the experiment. In cooler water, north of Cape Cod, in Lynn Harbor, Massachusetts Bay, , D. listerianum achieved a stand-off with B. violaceus, becoming co-dominant, covering ~37% of the plates at thepeak of its growth (Agius 2007). Schnmidt and Warner (1986), working in the English Channel, found that D. listerianum outcompeted Trididemnurn tenerurn,Botryllus schlosseri and Botrylloides leachii in 39% of trials on fouling plates and reached stand-offs in 61%. Vance et al. (2008) observed that D. listerianum rapidly overgrew other fouling organisms on plates in newly colonized regions on the North sea cast of England. Diplosoma listerianum was one of several invasive fouling species which showed increased growth (% coverage) at temperatures 3.5 and 4.5 C above the ambient temperature in Bodega Harbor (13.5 C), while tha native Distaplia occidentalis showed reduced survival (Sorte et al. 2010). Diplosoma listerianum has been reported to foul cultured shellfish in the United Kingdom (Isle of Man), Croatia, Japan, and Hong Kong (Ross et al. 2004, Igic 1972, Arakawa 1990, Huang 2003, cited by da Rocha et al. 2009).. Da Rocha et al. suggest that the impact might be small, because of the thinness of the colonies.
References
Agius, Brad P. (2007) Spatial and temporal effects of pre-seeding plates with invasive ascidians: Growth, recruitment and community composition., Journal of Experimental Marine Biology and Ecology 342: 30-39Altman, Safra; Whitlatch, Robert B. (2007) Effects of small-scale disturbance on invasion success in marine communities., Journal of Experimental Marine Biology and Ecology 342: 15-29
Blezard, David J. (1999) Salinity as a refuge from predation in a nudibranch-hydroid relationship within the Great Bay estuary. system., , Durham, New Hampshire. Pp.
Brunetti, R.; Bressan, M.; Marin, M.; Libralato, M. (1988) On the ecology and biology of Diplosoma listerianum (Ascidiacea, Didemnidae), Vie et Milieu 38: 123-131
Coles, S. L.; DeFelice, R. C.; Eldredge, L. G.; Carlton, J. T. (1999b) Historical and recent introductions of non-indigenous marine species into Pearl Harbor, Oahu, Hawaiian Islands., Marine Biology 135: 147-158
Cranfield, H.J.; Gordon, D.P.; Willan, R.C.; Marshall, B.A; Battershill, C.N.; Francis, M.P.; Nelson, W.A.; Glasby, C.J.; Read, G.B. (1998) Adventive marine species in New Zealand., , New Zealand. Pp.
da Rocha, Rosana M.; Kremer, Laura P.; Baptista, Mariah S.; Metri, Rafael (2009) Bivalve cultures provide habitat for exotic tunicates in southern Brazil., Aquatic Invasions 4: 195-205
Harris, Larry; Tyrrell, Megan (2001) Changing community states in the Gulf of Maine., Biological Invasions 3: 9-21
Kaplan, Eugene H. (1988) A Field Gude to Southeastern and Caribbean Seashores, In: (Eds.) . , Boston. Pp.
Kott, P. (1998) Tunicata, Zoological Catalogue of Australia 34: 51-252
Kott, Patricia (1990) The Australian Ascidiacea, part 2, Aplousobranchia (1), Memoirs of the Queensland Museum 29: 1-266
Kott, Patricia (2001) The Australian Ascidiacea, part 4, Aplousobranchia (3), Didemnidae., Memoirs of the Queensland Museum 47: 1-407
Lambert, Gretchen (2002) Nonindigenous ascidians in tropical waters., Pacific Science 56: 191-298
2003-2008 Introduced and cryptogenic species of the North Atlantic. http://massbay.mit.edu/exoticspecies/exoticmaps/introduced.html
Osman, Richard W.; Whitlatch, Robert B. (1995) The influence of resident adults on recruitment: a comparison to settlement., Journal of Experimental Marine Biology and Ecology 190: 169-198
Sorte, Cascade, J. B.; Williams, Susan L.; Zerebecki, Robyn A. (2010) Ocean warming increases threat of invasive species in a marine fouling community, Ecology 91: 2198-2204
Stachowicz, John J.; Fried, Heather; Osman, Richard W.; Whitlatch, Robert B. (2002a) Biodiversity, invasion resistence, and marine ecosystem function: reconciling pattern and process., Ecology 83: 2575-2590
2002-2021 Invertebrate Zoology Collections Database.
Van Name, Willard G. (1921) Ascidians of the West Indian region and southeastern United States., Bulletin of the American Museum of Natural History 44: 283-494
Van Name, Willard G. (1945) The North and South American ascidians, Bulletin of the American Museum of Natural History 84: 1-462
Vance, Thomas; Lauterbach, Lars; Lenz, Mark;Wahl, Martin; Sanderson, Roy A.; Thomason, Jeremy C. (2008) Rapid invasion and ecological interactions of Diplosoma listerianum in the North Sea, UK., Occasional Papers of the Bishop Museum None: 1-5
Whitlatch, Robert B.; Osman, Richard (2000) Geographical distributions and organism-habitat associations of shallow water introduced marine fauna in New England., In: Pederson, Judith(Eds.) Marine Bioinvasions. , Cambridge MA. Pp. 61-65
Whitlatch, Robert B.; Osman, Richard W.; Frese, Annette, Malatesta, Richard, Mitchell, Patricia, Sedgwick, Lynn (1995) The ecology of two introduced marine ascidians and their effects on epifaunal organisms in Long Island Sound, In: Balcom, N. C.(Eds.) Proceedings of the Northeast Conference on Non-Indigenous Aquatic Nuisance Species. , Groton, CT. Pp. 28-29