Invasion History
First Non-native North American Tidal Record: 2000First Non-native West Coast Tidal Record: 2000
First Non-native East/Gulf Coast Tidal Record: None
General Invasion History:
Schizoporella variabilis was first described from Rhode Island by Joseph Leidy in 1855. a warmer waters (Hayward and Ryland 1999; Hayward and McKinney 2002). As an encrusting organism it is readily transported in fouling. In British waters, it occurs sporadically on ships (Hayward and Ryland 1999). Its worldwide range and its occurrences in the Pacific are poorly documented because of confusion with many similar Schizoporella species, and also found in New Jersey. This speciesnbds from the Gulf of Maine to Cape Hatters (Winston and Hayward 2012).
The identity of the widely introduced Pacific forms of Schizoporella has been uncertain (Judith Winston, pers. comm.). Global morphological and molecular surveys will be required to determine the identity of apparently introduced Schizoporella species. Currently, Smithsonian Environmental Research Center consulting taxonomists (Matthew Dick; Judith Winston) have definitely identified S. variabilis from plates in San Francisco Bay, but not from other West coast localities. (Winsotn and HaywARD 2012).
North American Invasion History:
Invasion History on the West Coast:
he invasion of Schizoporella japonica, identified then as S. unicornis, was widely reported with Puget Sound, in 1927, reaching San Francisco Bay in 1963, with many reports (Powell 1970; Carlton 1979; Banta 1963, cited by Cohen and Carlton 1995). However, the occurrence of a second species, possibly S. errata in southern California had been suspected (Powell 1979; Carlton 1979; Cohen and Carlton 1995). Taxonomists working with the SERC invasion group (Judith Winston, Matthew Dick) think that one type of Schizoporella in San Francisco Bay matched European type specimens sufficiently well to be identified as S.errata'. "S. errata' was identified from San Francisco Bay, at least as early as 2000 (Ruiz et al. unpublished data). In 2006, unusual spherical, tube-like and foliaceous structures were found on muddy substrates in the Central and South Bays. These structures were, formed of bryozoan colonies cemented with sand and mud (bryoliths). The bryozoans forming these structures were originally identified as S. errata, based on morphology and molecular comparison of cytochrome oxidase subunit I (COI). Further examination of the bryozoans by Linda McCann and Judith Winston have re-identified them as the closely related species S. variabilis from the Northwest Atlantic. This bryozoan was also found in Mission Bay in 2011, Humboldt Bay (2015), and Bodega and/or Tomales Bay (California Department of Fish and Wildlife 2014; Ruiz and Geller 2018; Ruiz and Geller 2021). However, establishment in these bays is uncertain.
Invasion History in Hawaii:
One or more species of Schizoporella have been introduced to the Hawaiian Islands, variously identified as either S. variabilis or S. unicornis. Hawaiian material requires re-examination before names can be applied (Carlton and Eldredge 2009).
Invasion History Elsewhere in the World:
In the Pacific, Schizoporella variabilis has been found at Pago Pago Harbor, American Samoa (Coles et al. 2003). In New Zealand, it was reported to occur sporadically, first found in Auckland Harbor in 1960, and occurring on the hull of a yacht in the Bay of Islands in 1988 (Gordon and Mawatari 1992), but recently occurring in surveys of several New Zealand harbors (Inglis et al. 2005b). Its date of first occurrence in Australia is unknown, owing to confusion with S. unicornis, but it is known from Sydney Harbor (Piola and Johnston 2006; Glasby et al. 2007), Port Phillip Bay (Hewitt et al. 2004), and Geraldton and Shark Bay, Western Australia (Wyatt et al. 2005; http://www.civgeo.rmit.edu.au/bryozoa/cheilostomata/schizoporellidae/schierr.html).
Description
Schizoporella variabilis is a heavily calcified encrusting bryozoan, sometimes rising as a double layer with knobs or tubular extensions and growing from rigid or flexible surfaces such as worm tubes and algae. The thickness of a colony is dependent upon its age. Many-layered encrustations of 1 cm thick are common. Its color varies from pink, to orange to brick red. The young zooecia are hexagonal, with older ones being quadrilateral or irregularly polygonal. The frontal wall is opaque and covered with circular pits, each containing a round pore. The orifice is roughly semi-circular, with a central U-shaped sinus on the proximal, roughly straight, edge . It is often not centered and is closer to one side of the zooid. The sinus is surrounded by several tab-like condyles. There are single or paired avicularia on the right or left side of the sinus. The zooecia lack spines and the ovicells are globular, with a radiating pattern or pores and a rough textureIts calcification thickens and the pores deepen with later development. The ancestrula is oval, without pores, and with a large, semicircular orifice, surrounded by four pairs of spines (description from: Leidy 1855; Verrill and Smith 1873; Winston and Hayward 2012).
In California, S. variabilis tends to be rather pale, with dark spotty pigment blotches, whereas S. japonica is bright orange in color. The former can also have adventitious, large, frontal avicularia, though they may be rare. Schizoporella variabilis is often rare on panels, but quite abundant in San Francisco Bay as bryoliths (unattached, living colony masses) (Zabin et al. ,2010) whereas S. japonica is very abundant on panels, but has never been seen to form bryoliths (Linda McCann, personal communication 2009)..
Schizoporella variabilis is closely related to the warm-water Mediterranean and East Atlantic S. errata and was formerly identified as this species (Ryland et al. 2014). . However, it differs in shape of the ovicell, and in the shape andnumber of avicularia. Schizoporella variabilis' avicularia have more incurved rostrum and a broader palate. Schizoporella variabilis is associated with colder water than S. errata (Winston and Hayward 2012).
Taxonomy
Taxonomic Tree
Kingdom: | Animalia | |
Phylum: | Bryozoa | |
Class: | Gymnolaemata | |
Order: | Cheilostomata | |
Suborder: | Ascophora | |
Family: | Schizoporellidae | |
Genus: | Schizoporella | |
Species: | variabilis |
Synonyms
Hippothoa variabilis (Verrill, 1875)
Schizoporella unicornis (Osburn, 1912)
Schizopodrella unicornis (Osburn, 1932)
Schizoporella varaibilis (Waters, 1878)
Potentially Misidentified Species
(Osburn, 1914) A Northwest Atlantic form, formerly considered conspecific with S. errata (Hayward and Ryland 1999).
Schizoporella errata
(Waters 1878) Described from Naples, and appears to be native to the Mediterranean, but is now widespread in the world's warmer waters (Hayward and Ryland 1999;
Schizoporella japonica
(Ortmann 1890) A Northwest Pacific species, formerly considered conspecific with S. unicornis (Dick et al. 2005).
Schizoporella pseudoerrata
(Soule, Soule, and Chaney 1995). 'This very similar species, newly described by Soule et al in 2005, is known from California fouling communities, and may be a redescription of a form of a previously described Schizoporella. It is not likely to be a native species.' (James T. Carlton, personal communication, 2013).
Schizoporella unicornis
(Johnston 1874) A northeast Atlantic species, described from England. Its present range is uncertain, due to the presence of related cryptic species, such as S. japonica (Tompsett et al. 2009).
Ecology
General:
Life History- Schizoporella variabilis is an encrusting, calcified bryozoan composed of many individual zooids. Zooids can reproduce asexually through diviision. Zooids are herrmophroditic, and also reproduce sexually, to produce larvae which are brooded and then released. Larvae of S. errata are lecithotrophic, and have a short planktonic period (less than 1 day, Hayward and Ryland 1999). The zooids feed by extending the ciliated tentacles of the lophophore as a funnel, creating a current, and driving food particles into their mouths. The food is guided along the tentacles and through the pharynx by the cilia. Larger food particles can be moved or captured by flicking or contracting the tentacles (Barnes 1983). Larvae settle on a substrate and metamorphose into the first zooid of a colony, an ancestrula (Barnes 1983).
Ecology- Schizoporella variabilis is known from eelgrass beds, oyster beds, pilings, shells, rocks,, floats and ship hulls (Verrill and Smith 1873; Ryland 1965; Winston 1986; Hayward and Ryland 1999)..In San Francisco Bay, S. variabilis fomed solid globular, tubular, and foliaceous structures on mudflats (Zabin et al. 201). It is tolerant of brackish water (Verill and Smith 1873, though the lower limit of its tolerance is not known.
Food:
Phytoplankton, detritus
Trophic Status:
Suspension Feeder
SusFedHabitats
General Habitat | Rocky | None |
General Habitat | Coarse Woody Debris | None |
General Habitat | Oyster Reef | None |
General Habitat | Marinas & Docks | None |
General Habitat | Grass Bed | None |
General Habitat | Unstructured Bottom | None |
Salinity Range | Polyhaline | 18-30 PSU |
Salinity Range | Euhaline | 30-40 PSU |
Vertical Habitat | Epibenthic | None |
Life History
Tolerances and Life History Parameters
Maximum Temperature (ºC) | 26.6 | Field, US East & West Coast marinas (Lord et al. 2015) |
Maximum Salinity (‰) | 35 | Typcial marine salinity |
Broad Temperature Range | None | Warm temperate-Tropical |
Broad Salinity Range | None | Polyhaline-Euhaline |
General Impacts
Economic Impacts- Schizoporella spp. are common fouling organisms on ship hulls, docks, and other hard surfaces (Woods Hole Oceanographic Institution 1952; Ryland 1965; Hayward and McKinney 2002). Ryland (1971) suggests that the calcareous layers produced by the bryozoans may actually protect pilings and docks from borers.
Ecological Impacts- Schizoporella spp. frequently dominates the fouling community on man-made structures and on rocks, shells, and algae (Ryland 1965; Powell 1970; Sutherland 1981; Hayward and McKinney 2002).
Regional Impacts
NEP-V | Northern California to Mid Channel Islands | Ecological Impact | Habitat Change | ||
Schizoporella errata forms bryoliths (large, rounded, mulilaminar, unattached nodules), creating hard reef-like structures, colonized by at least 34 species, 25 of them non-indigenous (Zabin et al. 2010). | |||||
P090 | San Francisco Bay | Ecological Impact | Habitat Change | ||
Schizoporella variabilis, initially identified as S. errata, created a variety of solid structures on mudflats. These were colonized by a wide variety of native, introduced, and cryptogenic invertebtates (Zabin et al. 2010). | |||||
CA | California | Ecological Impact | Habitat Change | ||
Schizoporella errata forms bryoliths (large, rounded, mulilaminar, unattached nodules), creating hard reef-like structures, colonized by at least 34 species, 25 of them non-indigenous (Zabin et al. 2010)., Schizoporella variabilis, initially identified as S. errata, created a variety of solid structures on mudflats. These were colonized by a wide variety of native, introduced, and cryptogenic invertebtates (Zabin et al. 2010). |
Regional Distribution Map
Bioregion | Region Name | Year | Invasion Status | Population Status |
---|---|---|---|---|
NEP-IV | Puget Sound to Northern California | 2015 | Non-native | Established |
P130 | Humboldt Bay | 2015 | Non-native | Established |
P112 | _CDA_P112 (Bodega Bay) | 2014 | Non-native | Established |
P030 | Mission Bay | 2011 | Non-native | Unknown |
NEP-VI | Pt. Conception to Southern Baja California | 2011 | Non-native | Unknown |
P090 | San Francisco Bay | 2000 | Non-native | Established |
NEP-V | Northern California to Mid Channel Islands | 2000 | Non-native | Established |
Occurrence Map
OCC_ID | Author | Year | Date | Locality | Status | Latitude | Longitude |
---|---|---|---|---|---|---|---|
697089 | Introduced Species Study | 2010 | 2010-07-12 | Ferry Terminal Pier | Non-native | 37.7945 | -122.3917 |
697560 | Ruiz et al., unpublished data | 2000 | Corinthian Harbor/Tiburon Ferry Terminal, San Francisco Bay | Non-native | 37.8727 | -122.4559 | |
697830 | Introduced Species Study | 2010 | 2010-06-03 | Berkeley Marina | Non-native | 37.8676 | -122.3172 |
698076 | Introduced Species Study | 2010 | 2010-07-29 | San Mateo Bridge | Non-native | 37.5806 | -122.2543 |
698113 | Introduced Species Study | 2011 | 2011-05-04 | Hilton Resort Dock | Non-native | 32.7788 | -117.2127 |
698322 | Introduced Species Study | 2010 | 2010-07-01 | Loch Lomond Marina Area | Non-native | 37.9720 | -122.4832 |
699123 | Introduced Species Study | 2010 | 2010-07-14 | Paradise Cay | Non-native | 37.9146 | -122.4776 |
699220 | Introduced Species Study | 2010 | 2010-06-03 | Treasure Island | Non-native | 37.8149 | -122.3702 |
699398 | Introduced Species Study | 2010 | 2010-06-13 | Coyote Point | Non-native | 37.5920 | -122.3210 |
699647 | Introduced Species Study | 2010 | 2010-07-12 | Pier 45 | Non-native | 37.8111 | -122.4196 |
699751 | Introduced Species Study | 2010 | 2010-06-14 | Aquatic Park | Non-native | 37.8080 | -122.4216 |
699884 | Introduced Species Study | 2010 | 2010-05-31 | Redwood Creek - Marina | Non-native | 37.5021 | -122.2130 |
699922 | Introduced Species Study | 2010 | 2010-05-31 | Dumbarton Bridge | Non-native | 37.5070 | -122.1168 |
700029 | Introduced Species Study | 2010 | 2010-07-12 | Cruise Ship Pier | Non-native | 37.8085 | -122.4060 |
700193 | Ruiz et al., unpublished data | 2000 | Port of Redwood, San Francisco Bay | Non-native | 37.4969 | -122.2194 | |
700801 | Introduced Species Study | 2010 | 2010-06-01 | Sea Plane Harbor | Non-native | 37.6349 | -122.3848 |
702081 | Introduced Species Study | 2010 | 2010-07-01 | Corinthian Marina | Non-native | 37.8726 | -122.4563 |
702685 | Introduced Species Study | 2010 | 2010-07-12 | Potrero Point | Non-native | 37.7521 | -122.3790 |
704302 | Ruiz et al., unpublished data | 2000 | East Harbor Marina (Gas House Cove), San Francisco Bay | Non-native | 37.8069 | -122.4331 | |
704598 | Introduced Species Study | 2010 | 2010-06-01 | Sierra Point Marina | Non-native | 37.6740 | -122.3792 |
772195 | Ruiz et al., 2021a | 2018 | 2018-09-20 | San Leandro Marina, San Francisco Bay, California, USA | Non-native | 37.6981 | -122.1907 |
772202 | Ruiz et al., 2021a | 2018 | 2018-09-20 | San Leandro Marina, San Francisco Bay, California, USA | Non-native | 37.6981 | -122.1907 |
772223 | Ruiz et al., 2021a | 2018 | 2018-09-20 | San Leandro Marina, San Francisco Bay, California, USA | Non-native | 37.6981 | -122.1907 |
772232 | Ruiz et al., 2021a | 2018 | 2018-09-20 | San Leandro Marina, San Francisco Bay, California, USA | Non-native | 37.6981 | -122.1907 |
772243 | Ruiz et al., 2021a | 2018 | 2018-09-20 | San Leandro Marina, San Francisco Bay, California, USA | Non-native | 37.6981 | -122.1907 |
772554 | Ruiz et al., 2021a | 2018 | 2018-09-19 | Sausalito Marine Harbor, San Francisco Bay, California, USA | Non-native | 37.8609 | -122.4855 |
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