Invasion History
First Non-native North American Tidal Record: 1985First Non-native West Coast Tidal Record: 1985
First Non-native East/Gulf Coast Tidal Record:
General Invasion History:
Tridentiger bifasciatus (Shimofuri Goby) is native to Asia. It is found in fresh and brackish waters from Hokkaido and northern China to Taiwan and Hong Kong (Matern et al. 1995; Froese and Pauly 2009; Yagi et al. 2011). We have treated it as continental or freshwater species since it has not been reported at salinities above 22 ppt in the field, and does not tolerate salinities above 17 PSU in the laboratory (Matern et al. 1995; Matern 2001). This level of salinity tolerance is comparable to that of many freshwater fishes (Schwartz 1965).
North American Invasion History:
Invasion History on the West Coast:
Tridentiger bifasciatus has only been found outside its native range in California. Initially, it was confused with the marine species T. trigonocephalus, with which it had been lumped by taxonomists. However, when T. bifasciatus was reinstated as a separate species, Matern et al. (1995) reexamined Tridentiger species from fresh and brackish parts of the Sacamento-San Joaquin Delta and found T. bifasciatus (Matern et al. 1995). This goby was first collected in the Delta in 1985. By 1989 it had become the most abundant fish species in Suisun Marsh (Matern et al. 1995). In 1987, a specimen was collected at the John Skinner Delta Fish Protective Facility near Byron, Contra Costa County, on the San Joaquin River. This is the intake for the California Aqueduct, which supplies water to Los Angeles. In 1990, T. bifasciatus was collected in Pyramid Reservoir, at the far end of the aqueduct, 513 km to the south of the Skinner facility. In 1992, some fish were collected below the Pyramid Reservoir, but they had not spread into the Santa Clara or Santa Ynez rivers, which reach the coast (Matern et al. 1995). By 2016, Shimofuri Gobies had been collected in seven southern California reservoirs, from Pyramid Reservoir, east of Oxnard, to Otay Reservoir, east of San Diego. They were collected below dams in the Santa Clara River system, but as of 2015, they have not been found in Santa Clara estuary, where they pose a threat to the endangered Tidewater Goby (Eucyclogobius newberryi) (Howard and Booth 2016).
Invasion History Elsewhere in the World:
In November 2022, 2 specimens of Tridentiger biasciatus were caught in the Gent–Terneuzen canal, Belgium, )at a salinity of 7-8 PSU, These are the first recorded specimens of this fish in Europe. (Verhelst and Verreycken 2023).
Description
Tridentiger bifasciatus (Shimofuri Goby) is a freshwater and estuarine fish. It is morphologically very similar to T. trigonocephalus, with which it was formerly considered conspecific. Ecologically, the biggest difference between the species is that T. bifasciatus is unable to tolerate marine salinities above 17 PSU, while T. trigonocephalus has not been reported from fresh water (Matern and Fleming 1995; Matern 2001).
Tridentiger bifasciatus has the typical features of the family Gobiidae, including the two pelvic fins united to form a conical sucking disk, a spiny anterior and a soft posterior dorsal fin, and eyes near the top of the head. The dorsal fins have 6-7 spines and 11-14 rays, respectively, that are separated by a gap. The uppermost ray of each pectoral fin is attached and smooth (Matern and Fleming 1995). The lateral line is not noticeable. This goby is relatively fat, with a wide flat head. There are small sensory canal pores on the top of the head in the interorbital region (Matern and Fleming 1995). Colors are highly variable, but often dark or light brown, with a row of dark-brown mid-lateral spots. There are small white speckles on the head that extend to the ventral surface. The dorsal and anal fins are edged with orange (Matern and Fleming 1995). This fish reaches a maximum length of 110 mm (Froese and Pauly 2018).
Taxonomy
Taxonomic Tree
Kingdom: | Animalia | |
Phylum: | Chordata | |
Subphylum: | Vertebrata | |
Superclass: | Osteichthyes | |
Class: | Actinopterygii | |
Subclass: | Neopterygii | |
Infraclass: | Teleostei | |
Superorder: | Acanthopterygii | |
Order: | Perciformes | |
Suborder: | Gobioidei | |
Family: | Gobiidae | |
Genus: | Tridentiger | |
Species: | bifasciatus |
Synonyms
Potentially Misidentified Species
Can be confused as larvae or early juveniles.
Tridentiger trigonocephalus
Long considered conspecific, but morphologically different, and stenohaline-marine (Matern et al. 1995)
Ecology
General:
Tridentiger bifasciatus ranges from cold-temperate to warm-temperate climates in fresh and brackish waters (Matern et al. 1995; Froese and Pauly 2018). It tolerates gradual temperature increases up to 37 C and gradual salinity increases up to 17 PSU, making dispersal through marine waters unlikely (Matern 2001). It is most abundant in freshwater and low-salinity habitats (Matern and Fleming 1995). Habitats include marshes, freshwater reservoirs, and probably natural and artificial structures that provide shelter (Matern and Fleming 1995). The Shimofuri Goby is a generalist predator. Prey in Suisun Marsh, in the San Francisco estuary, is amphipods and copepods, but it also preys on introduced hydroid Cordylophora caspia, and the cirri of the introduced barnacle Amphibalanus improvisus (Matern et al. 2005). In the laboratory it is aggressive towards the endangered Tidewater Goby, Eucyclogobius newberryi (Matern 2010).
Food:
Amphipods, Polychaetes, Oligochaetes; Hydroids
Trophic Status:
Carnivore
CarnHabitats
General Habitat | Fresh (nontidal) Marsh | None |
General Habitat | Grass Bed | None |
General Habitat | Nontidal Freshwater | None |
General Habitat | Tidal Fresh Marsh | None |
General Habitat | Salt-brackish marsh | None |
General Habitat | Unstructured Bottom | None |
General Habitat | Canals | None |
Salinity Range | Limnetic | 0-0.5 PSU |
Salinity Range | Oligohaline | 0.5-5 PSU |
Salinity Range | Mesohaline | 5-18 PSU |
Tidal Range | Subtidal | None |
Vertical Habitat | Nektonic | None |
Vertical Habitat | Epibenthic | None |
Life History
Tridentiger bifasciatus (Shimofuri Goby) is a freshwater and estuarine fish. In the laboratory, males are territorial and guard nests in plastic tubes, attracting females (Matern and Fleming 1995). They nest in freshwater or brackish-water clam shells (Corbula; , Corbicula) as well as cans, bottles, and other trash. Eggs hatch in 9 days, at 20 C, and are guarded by the male (Matern and Fleming 1995). Females in an introduced freshwater population has 2300 to 18,000, with a mean of 8,200 eggs (Qin et al. 2020).Larvae are planktonic and probably use vertical migration for retention in the estuary (Bennett et al. 2001). Comparisons between a Chinese freshwater introduced population and the San Francisco estuary population suggest that this species has great plasticity in its life history (Qin et al. 2020).
Tolerances and Life History Parameters
Maximum Temperature (ºC) | 37 | Temperature was increased by 0.1 C per minute (Critical Temperature Maximum; The endpoint was loss of equilibrium) (Matern 2001). |
Minimum Salinity (‰) | 0 | This is a freshwater species. |
Maximum Salinity (‰) | 17 | Salinity was increased by 1 ppt per 12h; the endpoint was loss of equilibrium (Matern 2001). This level of salinity tolerance is typical for a stenohaline freshwater fish. |
Minimum Reproductive Salinity | 0 | Field and lab Matern et al. 1995 |
Maximum Reproductive Salinity | 5 | Lab, Matern et al. 1995 |
Maximum Length (mm) | 110 | Froese and Pauly 2014 |
Broad Temperature Range | None | Cold temperate-Subtropical |
Broad Salinity Range | None | Nontidal Limnetic-Mesohaline |
General Impacts
Tridentiger bifasciatus (Shimofuri Goby) is a rapidly spreading invader in fresh and estuarine waters in California. It is regarded as a potential competitor with the endangered native Tidewater Goby (Eucylogobius newberryi) (Matern and Fleming 1995; Matern 2001). It is probably an important prey item for native and introduced predatory fishes.
Occurrence Map
OCC_ID | Author | Year | Date | Locality | Status | Latitude | Longitude |
---|---|---|---|---|---|---|---|
697398 | Swift et al. 1993; Matern & Fleming 1995 | 1990 | Pyramid Reservoir (General Location) | Non-native | 34.6560 | -118.7717 | |
699056 | Introduced Species Study | 2010 | 2010-07-13 | Petaluma River Turning Basin | Non-native | 38.2344 | -122.6354 |
701957 | Swift et al. 1993; Matern & Fleming 1995; FishNet2 Database 2018 | 1992 | 1992-06-25 | Piru Creek (below Pyramid Reservoir), CFG Section 5 | Non-native | 34.6311 | -118.7482 |
761841 | Raquel 1988; Matern and Fleming 1995 | 1987 | 1987-03-05 | John E. Skinner Delta Fish Protective Facility | Non-native | 37.8257 | -121.5957 |
761842 | Hess et al. 1995 | 1995 | O'Neill Forebay, at influx of Delta-Mendota Canal water | Non-native | 37.0971 | -121.0484 | |
761843 | FishNet2 Database 2018 | 1992 | 1992-07-23 | Piru Creek (below Pyramid Reservoir), CFG Section 3 | Non-native | 34.6352 | -118.7565 |
761844 | California Academy of Sciences Ichthyology Collection Database 2018 | 1994 | 1994-04-19 | Suisun Slough, Suisun Marsh | Non-native | 38.1786 | -122.0473 |
761845 | California Academy of Sciences Ichthyology Collection Database 2018 | 1994 | 1994-06-10 | Denverton Slough, Suisun Marsh | Non-native | 38.2099 | -121.9070 |
761846 | California Academy of Sciences Ichthyology Collection Database 2018 | 1995 | 1995-04-21 | Denverton Slough, Suisun Marsh | Non-native | 38.2099 | -121.9070 |
761847 | Howard and Booth 2016; FishNet2 Database 2018 | 2013 | 2013-08-20 | Lower Piru Creek below Santa Felicia Dam | Non-native | 34.4578 | -118.7510 |
761848 | Howard and Booth 2016 | 2015 | 2015-07-07 | Lake Piru, near the Penstock Intake | Non-native | 34.4621 | -118.7542 |
761849 | Howard and Booth 2016 | 2016 | 2016-04-20 | Lower Piru Creek below Santa Felicia Dam Outlet | Non-native | 34.4593 | -118.7523 |
761850 | Howard and Booth 2016 | 2016 | 2016-05-09 | Lower Piru Creek below Santa Felicia Dam Outlet | Non-native | 34.4593 | -118.7523 |
761851 | Howard and Booth 2016 | 2014 | 2014-03-05 | Vern Freeman Diversion Dam, Migrant Fish Trap (Santa Clara River) | Non-native | 34.2991 | -119.1083 |
761852 | Howard and Booth 2016 | 2014 | 2014-03-06 | Vern Freeman Diversion Dam, Migrant Fish Trap (Santa Clara River) | Non-native | 34.2991 | -119.1083 |
761853 | Howard and Booth 2016 | 2014 | 2014-03-08 | Vern Freeman Diversion Dam, Migrant Fish Trap (Santa Clara River) | Non-native | 34.2991 | -119.1083 |
761854 | Howard and Booth 2016 | 2014 | 2014-03-11 | Vern Freeman Diversion Dam, Migrant Fish Trap (Santa Clara River) | Non-native | 34.2991 | -119.1083 |
761855 | Howard and Booth 2016 | 2014 | Castaic Lake | Non-native | 34.5279 | -118.6007 |
References
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DOI: 10.1111/jfb.15362