Invasion History
First Non-native North American Tidal Record: 1946First Non-native West Coast Tidal Record: 1946
First Non-native East/Gulf Coast Tidal Record:
General Invasion History:
Monocorophium uenoi was described from the Sea of Japan and is also known from locations on Japan's Pacific coast and the Seto Inland Sea (Nagata 1960; Hirayama 1965; Aikins and Kikuchi 2002). It also occurs on the coast of China, along the East China Sea, and Hong Kong (Huang 2001; Hirayama 1986). Monocorophium uenoi has been introduced to the Northeast Pacific from Humboldt Bay, California to Bahia San Quintin, Mexico (Barnard and Reish 1959; Carlton 1979; Bousfield and Hoover 1997; Boyd et al. 2002; Chapman 2007). This species is also reported from Chile (Gonzalez 1991), and was recently found associated with oysters in the Netherlands (Faasse 2014). Likely vectors for its spread include ballast water, hull fouling, and exports of Pacific oysters (Crassostrea gigas) from Japan (Barnard and Reish 1959; Carlton 1979; Faasse 2014).
North American Invasion History:
Invasion History on the West Coast:
The earliest reported collection of Monocorophium uenoi is from Newport Bay, California (CA) in 1946 (USNM specimen, cited by Carlton 1979). The distribution of this amphipod along the West coast is spotty, and mostly occurs where oysters have been planted in the past (Newport Bay) or are actively cultured. It was collected in 1950 in Morro Bay, CA (Barnard 1952, cited by Carlton 1979), but was not found in a 2005 survey (Needles and Wendt 2013). This species was reported from Monterey Harbor, CA (Barnard 1966, cited by Carlton 1979); Elkhorn Slough, CA in 1977 (Carlton 1979; Wasson et al. 2001); Bolinas Lagoon, CA (Page and Stenzel 1975, cited by Carlton 1979); Tomales Bay, CA in 1964 (Johnson and Juskevice 1965, cited by Carlton 1979); Bodega Harbor, CA (Standing 1975, cited by Carlton 1979); and Humboldt Bay, CA in 2000 (Boyd et al. 2002). In San Francisco Bay, M. uenoi was collected in 1976 (CAS-IZ 123419.00, California Academy of Sciences 2015), from South San Francisco Bay, but was not reported in subsequent large invasion inventories (e.g. Carlton 1979; Cohen and Carlton 1995). It was found at Coast Guard Island in the central Bay in 2004 (Cohen et al. 2005) and San Pablo Bay in 2011 (Foss 2011). Graening et al. (2012) list records from the Sacramento River, as well. While most records are from bays with oyster culture, occurrences from Goleta, Gaviota, and Point Conception are from kelp beds on the open coast (Barnard 1961, cited by Carlton 1979), perhaps due to ship or boat fouling, ballast water (Carlton 1979) or natural dispersal.
Invasion History Elsewhere in the World:
Monocorophium uenoi was reported from several locations on the coast of central Chile by Gonzales (1991), but does not give information on specific dates, habitats, or possible vectors. However, this region is an area of intense aquaculture (Castilla et al. 2005). In 2012, M. uenoi was found closely associated with Pacific Oysters in Yeserke, the Netherlands, but was not found in other nearby locations (Faasse 2014).
Description
Monocorophium uenoi has a slender, depressed body with small, separated coxal plates, a fused urosome segment, and a distinct dorso-lateral notch. In males, the rostrum is long, ending about equally or just beyond the optical lobes, and Antenna 2 is longer and heavier than Antenna 1. In females, the rostrum is short, not exceeding the anterior lobes, and Antenna 2 is only slightly longer, but more robust than Antenna 1. In males, segment 1 of the peduncle of Antenna 1 is bluntly serrate and has 3 ventral spines. In the female, segment 1 has 3 stout spines, and segments 1-3 have many more setae than in the male. In males, segment 4 is somewhat inflated and has a very large distal tooth on the posterior side and 1-2 smaller teeth. Segment 5 (male) also has a distal process, but it is triangular and blunt. In females, segment 4 has 3 pairs of strong spines on the posterior surface and segment 5 has a stout median spine.
The gnathopods are not especially large or conspicuous in this genus. Segment 5 of Gnathopod 1 is slightly longer than segment 6, and the dactyl (segment 7) is twice as long as the palm of segment 6. On Gnathopod 2, segment 2 is longer than segment 5 and the dactyl bears 3 prominent, unequal teeth. Pereiopods 3 and 4 are very short, with a very broad segment 5, which partially covers segment 6. As noted above, the urosome segments are fused, but with a prominent lateral notch. Uropod 1 has short, unequal rami, each with 3-4 outer marginal spines. Uropod 2 is short, with the rami unequal, and the inner ramus often bare. Uropod 3 is uniramous, with the ramus longer than the peduncle. Adults are 2-5 mm long (Hirayama 1986; Chapman 2007). Centers of the pleonites and the segments of Antenna 2 are dark brown, mottled with white. There is a patch of pigment between the eyes, but it does not extend to the back of the head. The borders of the pleonites and most of the appendages are white (as shown in Faasse 2014). The description is based on: Crawford 1937, Hirayama 1986, Bousfield and Hoover 1997, Chapman 2007, and Faasse 2014.
Taxonomy
Taxonomic Tree
Kingdom: | Animalia | |
Phylum: | Arthropoda | |
Subphylum: | Crustacea | |
Class: | Malacostraca | |
Subclass: | Eumalacostraca | |
Superorder: | Peracarida | |
Order: | Amphipoda | |
Suborder: | Gammaridea | |
Family: | Corophiidae | |
Genus: | Monocorophium | |
Species: | uenoi |
Synonyms
Monocorophium uenoi (Bousfield and Hoover, 1997)
Potentially Misidentified Species
A species of uncertain taxonomic status, not reported from the Northeast Pacific, possibly a parthenogenetic form of M. acherusicum or M. insidiosum, reported from high latitudes of the Northern and Southern Hemispheres, including the Northwest Pacific (Bousfield and Hoover 1997, Chapman 2007).
Monocorophium acherusicum
Native to the North Atlantic, introduced to Pacific (Bousfield and Hoover 1997; Chapman 2007).
Monocorophium californiensis
A species of uncertain taxonomic status, not reported from northeast Pacific, possibly a parthenogenetic form of M. acherusicum or M. insidiosum, reported from high latitudes of the Northern and Southern Hemispheres, inlduding the northWest Pacific (Bousfield and Hoover 1997, Chapman 2007).
Monocorophium carlottensis
Northeast Pacific native, Puget Sound to Prince William Sound (Bousfield and Hoover 1997; Chapman 2007)
Monocorophium insidiosum
Native to the North Atlantic, introduced to the Pacific (Bousfield and Hoover 1997; Chapman 2007).
Monocorophium oaklandense
Possibly an intersex form of M. insidiosum (Chapman 2007)
Ecology
General:
Monocorophium uenoi is a gammarid amhipod which inhabits soft and hard substrates, as epifauna and infauna (Hirayama 1986; Larson et al. 2009; Faasse 2014). Gammarid amphipods have separate sexes, brooded embryos, and direct development (Bousfield 1973).
In its native range, M. uenoi tolerates a wide range of temperatures, including temperatures as high as 30 C (Hirayama 1986; Aikins and Kikuchi 2002). The extent of its salinity tolerance is not clear, but it has been collected from a range of locations. For instance, it was collected in parts of Humboldt Bay receiving freshwater drainage (Boyd et al. 2002), and in San Pablo Bay and the lower Sacramento River (Graening et al. 2012), as well as 'open sea' locations off southern California (Barnard 1969b). Habitats include intertidal muddy sandflats, oyster beds, mussel beds, seaweeds (Hirayama 1986; Larson 2009, Faasse 2014), and kelp holdfasts on the open coast (Barnard 1969b). Corophiid amphipods secrete threads of 'amphipod silk', to which the detritus is attached, to form its tubes. When the amphipods are abundant, the tubes form a mass in which the openings point outward or upward (Barnard et al. 1988). The tubes can be formed on the sediment surface, or attached to fouling on vertical surfaces such as rocks or pilings, or other fouling organisms (Barnard 1958).
Like other corophiid amphipods, M. uenoi is probably capable of feeding on phytoplankton, detritus and benthic microalgae on the sediment surface, and grazing on filamentous epiphytic algae growing on seaweeds and seagrasses (Bousfield 1973). In the Gamo Lagoon, Japan, M. uenoi fed on diatoms growing on the surface of the red alga Gracilaria vermiculophylla (Aikins and Kikuchi 2002). Fishes and shrimps are likely predators.
Food:
Detrtius; Benthic Diatoms
Trophic Status:
Suspension Feeder
SusFedHabitats
General Habitat | Unstructured Bottom | None |
General Habitat | Oyster Reef | None |
General Habitat | Grass Bed | None |
General Habitat | Coarse Woody Debris | None |
Salinity Range | Polyhaline | 18-30 PSU |
Salinity Range | Euhaline | 30-40 PSU |
Salinity Range | Mesohaline | 5-18 PSU |
Tidal Range | Subtidal | None |
Tidal Range | Low Intertidal | None |
Vertical Habitat | Epibenthic | None |
Tolerances and Life History Parameters
Maximum Temperature (ºC) | 30 | Field, Gamo Lagoon, Japan (Aikins and Kikuchi 2002) |
Maximum Length (mm) | 4.6 | Adult female (Hirayama 1986) |
Broad Temperature Range | None | Cold temperate-Warm temperate |
Broad Salinity Range | None | Mesohaline-Euhaline |
General Impacts
No impacts have been reported for Monocorophium uenoi in its introduced habitats.Regional Distribution Map
Bioregion | Region Name | Year | Invasion Status | Population Status |
---|---|---|---|---|
P093 | _CDA_P093 (San Pablo Bay) | 2003 | Non-native | Established |
NEP-IV | Puget Sound to Northern California | 2000 | Non-native | Established |
P130 | Humboldt Bay | 2000 | Non-native | Established |
P090 | San Francisco Bay | 1976 | Non-native | Established |
P095 | _CDA_P095 (Tomales-Drakes Bay) | 1975 | Non-native | Established |
P112 | _CDA_P112 (Bodega Bay) | 1975 | Non-native | Established |
P080 | Monterey Bay | 1966 | Non-native | Established |
P110 | Tomales Bay | 1965 | Non-native | Established |
P065 | _CDA_P065 (Santa Barbara Channel) | 1961 | Non-native | Established |
P070 | Morro Bay | 1950 | Non-native | Unknown |
NEP-V | Northern California to Mid Channel Islands | 1950 | Non-native | Established |
NEP-VI | Pt. Conception to Southern Baja California | 1946 | Non-native | Established |
P040 | Newport Bay | 1946 | Non-native | Established |
Occurrence Map
OCC_ID | Author | Year | Date | Locality | Status | Latitude | Longitude |
---|---|---|---|---|---|---|---|
755548 | Introduced Species Study | 2010 | 2010-06-13 | Coyote Point | Non-native | 37.5920 | -122.3210 |
755549 | Introduced Species Study | 2010 | 2010-06-30 | Rodeo Marina | Non-native | 38.0394 | -122.2717 |
755550 | Introduced Species Study | 2010 | 2010-07-15 | San Pablo Bay Pumphouse | Non-native | 38.0446 | -122.4326 |
758700 | Museum record: United States National Museum (No Collection Number given), cited in Carlton 1979a | 1946 | Newport Bay | Non-native | 33.6092 | -117.9067 | |
758701 | Barnard 1959b | 1949 | 1949-06-28 | Upper Newport Bay | Non-native | 33.6473 | -117.8861 |
758702 | Barnard 1952 | 1950 | 1950-02-02 | Chorro Creek, south of bridge (Morro Bay) | Non-native | 35.3535 | -120.8286 |
758703 | Barnard 1952 | 1950 | 1950-02-02 | Morro Bay, Station 4 | Non-native | 35.3444 | -120.8264 |
758704 | Barnard 1960 | 1957 | 1957-01-17 | R/V Velero IV Station 4822, 11 miles E of Point Conception | Non-native | 34.4542 | -120.2458 |
758705 | Barnard 1966 | 1959 | 1959-09-30 | Monterey Bay, Station 6425 | Non-native | 36.6150 | -121.8744 |
758706 | Reish and Barnard 1967 | 1960 | 1960-08-25 | Morro Bay | Non-native | 35.3500 | -120.8500 |
758707 | Barnard 1969b | 1961 | 1961-07-02 | Coal-Oil Point | Non-native | 34.4069 | -119.8785 |
758708 | Johnson and Juskevice 1965 | 1965 | White Gulch, Tomales Bay | Non-native | 38.1939 | -122.9458 | |
758709 | Johnson 1970 | 1967 | Lawson's Flat, Tomales Bay | Non-native | 38.2327 | -122.9732 | |
758710 | Standing et al. 1975 | 1975 | Bodega Harbor | Non-native | 38.3262 | -123.0495 | |
758711 | California Academy of Sciences Invertebrate Zoology Collection Database | 1976 | 1976-08-26 | South of Coyote Hills Slough mouth | Non-native | 37.5582 | -122.1280 |
758712 | Nybakken et al. 1977; J. Nybakken, pers. comm., 1977, in Carlton 1979a | 1977 | Elkhorn Slough General Location | Non-native | 36.8086 | -121.7856 | |
758713 | Boyd et al. 2002 (Humboldt Bay Report) | 2002 | Klopp Lake | Non-native | 40.8553 | -124.0919 | |
758714 | Boyd et al. 2002 (Humboldt Bay Report) | 2002 | South Eureka Marina | Non-native | 40.8017 | -124.1807 | |
758715 | Boyd et al. 2002 (Humboldt Bay Report) | 2002 | Southport Landing | Non-native | 40.6952 | -124.2494 | |
758716 | Cohen et al. 2005 (SF Bay Area RAS) | 2004 | 2004-05-24 | Coast Guard Island Marina, San Francisco Bay | Non-native | 37.7812 | -122.2458 |
767318 | Ruiz et al., 2015 | 2012 | 2012-08-13 | Coast Guard, Bodega Bay, California, USA | Non-native | 38.3126 | -123.0512 |
767327 | Ruiz et al., 2015 | 2012 | 2012-08-14 | Spud Point South, Bodega Bay, California, USA | Non-native | 38.3281 | -123.0574 |
767342 | Ruiz et al., 2015 | 2012 | 2012-08-21 | Lucas/Tides, Bodega Bay, California, USA | Non-native | 38.3284 | -123.0445 |
767383 | Ruiz et al., 2015 | 2012 | 2012-08-15 | Tomales- Call Box 401, Bodega Bay, California, USA | Non-native | 38.1793 | -122.9104 |
767973 | Ruiz et al., 2015 | 2012 | 2012-08-24 | Richmond Marina Bay Yacht Harbor, San Francisco Bay, CA, California, USA | Non-native | 37.9134 | -122.3523 |
767995 | Ruiz et al., 2015 | 2012 | 2012-08-23 | Sausalito Marine Harbor, San Francisco Bay, CA, California, USA | Non-native | 37.8609 | -122.4853 |
768014 | Ruiz et al., 2015 | 2012 | 2012-08-28 | San Francisco Marina, San Francisco Bay, CA, California, USA | Non-native | 37.8071 | -122.4341 |
768027 | Ruiz et al., 2015 | 2012 | 2012-08-27 | Port of San Francisco Pier 31, San Francisco Bay, CA, California, USA | Non-native | 37.8078 | -122.4060 |
768096 | Ruiz et al., 2015 | 2012 | 2012-08-29 | Coyote Point Marina, San Francisco Bay, CA, California, USA | Non-native | 37.5877 | -122.3174 |
768118 | Ruiz et al., 2015 | 2012 | 2012-09-04 | Redwood City Marina, San Francisco Bay, CA, California, USA | Non-native | 37.5023 | -122.2130 |
768143 | Ruiz et al., 2015 | 2012 | 2012-09-06 | Loch Lomond Marina, San Francisco Bay, CA, California, USA | Non-native | 37.9736 | -122.4802 |
768159 | Ruiz et al., 2015 | 2012 | 2012-09-05 | Port of Oakland, San Francisco Bay, CA, California, USA | Non-native | 37.7987 | -122.3228 |
768184 | Ruiz et al., 2015 | 2012 | 2012-09-07 | Jack London Square Marina, San Francisco Bay, CA, California, USA | Non-native | 37.7940 | -122.2787 |
768206 | Ruiz et al., 2015 | 2012 | 2012-08-31 | Glen Cove Marina, San Francisco Bay, CA, California, USA | Non-native | 38.0663 | -122.2130 |
768219 | Ruiz et al., 2015 | 2012 | 2012-09-13 | San Leandro Marina, San Francisco Bay, CA, California, USA | Non-native | 37.6962 | -122.1919 |
768324 | Ruiz et al., 2015 | 2013 | 2013-08-23 | Loch Lomond Marina, San Francisco Bay, CA, California, USA | Non-native | 37.9723 | -122.4829 |
770285 | Ruiz et al., 2021b | 2017 | 2017-08-03 | Balboa Bay Resort, Newport Bay, California, USA | Non-native | 33.6147 | -117.9138 |
771029 | Ruiz et al., 2021a | 2017 | 2017-09-19 | Richmond Marina Bay Yacht Harbor, San Francisco Bay, California, USA | Non-native | 37.9129 | -122.3494 |
771352 | Ruiz et al., 2021a | 2017 | 2017-09-21 | San Leandro Marina, San Francisco Bay, California, USA | Non-native | 37.6977 | -122.1912 |
771359 | Ruiz et al., 2021a | 2017 | 2017-09-21 | San Leandro Marina, San Francisco Bay, California, USA | Non-native | 37.6977 | -122.1912 |
772424 | Ruiz et al., 2021a | 2018 | 2018-09-28 | Loch Lomond Marina, San Francisco Bay, California, USA | Non-native | 37.9723 | -122.4818 |
772489 | 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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