Description
Potentially Misidentified Species - Ambloplites cavifrons (Roanoke Bass) is endemic to the Chowan, Roanoke, and Neuse drainages (VA-NC), but has been unsuccessfully introduced to the upper James (Jenkins and Burkhead 1993).
Taxonomy
Kingdom | Phylum | Class | Order | Family | Genus |
---|---|---|---|---|---|
Animalia | Chordata | Osteichthyes | Perciformes | Centrarchidae | Ambloplites |
Synonyms
Invasion History
Chesapeake Bay Status
First Record | Population | Range | Introduction | Residency | Source Region | Native Region | Vectors |
---|---|---|---|---|---|---|---|
1949 | Established | Stable | Introduced | Boundary Resident | North America | North America | Fisheries(Fisheries Intentional) |
History of Spread
Ambloplites rupestris (Rock Bass) is native to the St. Lawrence - Great Lakes, Hudson Bay and Mississippi drainages, Quebec-Saskatchewan, south to north GA, north AL and MO (Page and Burr 1991). It was introduced by United States Fish Commission (USFC) starting in 1889 to Atlantic drainages and some western states. Shipments and stocking by the United States Fish Commission continued to 1936. Many state agenicies continue to stock this fish.
A. rupestris was introduced in Atlantic drainages from NH south to the Roanoke River in NC-VA, in the Missouri and Arkansas River drainages in MO, AR, KS, and OK, and in some western states including CA, WA, CO and WY (Hardy 1978, Fuller et al. 1999; Page and Burr 1991). On the East Coast, Rock Bass reached the Hudson River estuary by 1843, via the Erie Canal (Mills et al. 1997). On the West Coast, stockings in the San Francisco Bay drainage in 1874 and later were unsuccessful (Cohen and Carlton 1995), but Rock Bass are established in the Chehalis River drainage in WA (Fuller et al. 1999). At present, this species has introduced to non-native drainages in 23 states, and is established in most of those locations (Fuller et al. 1999). They have aso been introduced to England, France, Mexico, and Puerto Rico, but are known to be established only in France (Lever 1996).
In the Chesapeake Bay drainage, A. rupestris was introduced in PA by Pennsylvania Fish Commission (PFC) before 1880 (Creveling 1881). In VA (and probably also in southern MD) most stockings on the Coastal Plain and lower Piedmont were unsuccessful, probably due in part to high summer temperatures, turbidity and siltation (Jenkins and Burkhead 1993).
James, York, Rappahannock Rivers- Ambloplites rupestris was stocked in 1887-1902, mostly in the Coastal Plain and the lower Piedmont, but these low-elevation introductions seem to have been unsuccessful. The first verified collections occurred in 1928-1944, but these captures were all above Fall-Line, and mostly in upper Piedmont (Jenkins and Burkhead 1993).
Potomac River- Ambloplites rupestris was stocked by the USFC in 1887-1908. The first verified record is 1911 (Jenkins and Burkhead 1993). By 1916, it was 'not uncommon' in the C&O canal at Seneca Creek (Montgomery County, MD), above the Fall-Line (Radcliffe and Welsh 1916). Jenkins and Burkhead's map shows no captures below the Fall Line.
Patuxent River - Two hundred A. rupestris were planted at Sandy Springs 1897 on the nontidal river (Ravenel 1900). Ambloplites rupestris is 'a Piedmont plateau species', and occurs in reservoirs near the headwaters of the Patuxent, but is not found in the estuary (Mansueti 1950).
Susquehanna River - A. rupestris was stocked by the PFC before 1880, but the locations were not specified (Creveling 1881). 'Its existence in the Susquehanna has been known for about twenty years' (Bean 1893). A. rupestris were found 'in fair numbers at most stations' along the river in PA (Bielo 1963). A specimen was collected at Conowingo Dam in 1949 (U.S. National Museum of Natural History 2001), but A. rupestris had probably reached the tidal river long before then.
Upper Bay- A. rupestris were not collected in early upper Bay surveys (Fowler 1917; Fowler 1933; Hildebrand and Schroeder 1928; Radcliffe and Welsh 1917), but were found below Conowingo Dam (McKeown 1984) and on Susquehanna Flats (Howarth et al. 1960). A collection was made from Worton Point, south of Sassafras River mouth (Musick 1972a), but this fish is apparently only occasional in the upper Bay.
Delaware River - Introductions of A. rupestris were made in 1890-1904, 1922, and 1927 (Raasch and Altemus 1991). It is considered an estuarine resident in tidal freshwater by Horwitz (1986), but apparently is rare.
History References - Bean 1893; Bielo 1963; Cohen and Carlton 1995; Cope 1879; Elser 1960; Fowler 1917; Fowler 1933; Fuller et al. 1999; Hardy 1978; Hildebrand and Schroeder 1928; Horwitz 1986; Jenkins and Burkhead 1993; Lever 1996)Mansueti 1950; McKeown 1984; Mills et al. 1997; Musick 1972a; Page and Burr 1991; Raasch and Altemus 1991; Radcliffe and Welsh 1916; Ravenel 1900; Smith and Bean 1898; U.S. National Museum of Natural History 2001
Invasion Comments
Ecology
Environmental Tolerances
For Survival | For Reproduction | |||
---|---|---|---|---|
Minimum | Maximum | Minimum | Maximum | |
Temperature (ºC) | 0.0 | 35.0 | 15.6 | 26.0 |
Salinity (‰) | 0.0 | 0.0 | 0.0 | |
Oxygen | well-oxygenated | |||
pH | 5.0000000000 | |||
Salinity Range | fresh-oligo |
Age and Growth
Male | Female | |
---|---|---|
Minimum Adult Size (mm) | 176.0 | 176.0 |
Typical Adult Size (mm) | 203.0 | 203.0 |
Maximum Adult Size (mm) | 373.0 | 373.0 |
Maximum Longevity (yrs) | 13.0 | 13.0 |
Typical Longevity (yrs | 6.0 | 6.0 |
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
Ambloplites rupestris (Rock Bass) may have had impacts in nontidal rivers, but this species is rare below the Fall-Line, and only an occasional straggler in tidal waters (Jenkins and Burkhead 1993; Musick 1972a).
Fisheries - A. rupestris is rare in tidal waters but may be important in the nontidal Susquehanna (Bielo 1963). It is a good sports fish for its size, but competitive and prolific and is a possible competitor with Lepomis auritis (Redbreast Sunfish) and Micropterus dolomieu (Smallmouth Bass), trout, and other sport fish (Carlander 1977; Jenkins and Burkhead 1993).
References- Bielo 1963; Carlander 1977; Jenkins and Burkhead 1993; Musick 1972a
Economic Impacts Outside of Chesapeake Bay
Ambloplites rupestris (Rock Bass) is a good sports fish for its size, but competitive and prolific. It may displace native or more desirable fishes (Carlander 1977; Jenkins and Burkhead 1993). It has been widely stocked in the US, and is well established in Atlantic Slope drainages from the Connecticut River south to mountain regions of GA (Fuller et al. 1999).
References- Carlander 1977; Fuller et al. 1999; Jenkins and Burkhead 1993
Ecological Impacts on Chesapeake Native Species
Ambloplites rupestris (Rock Bass) may have had impacts in nontidal rivers, but this species is rare below the Fall-Line, and only an occasional straggler in tidal waters (Jenkins and Burkhead 1993; Musick 1972a).
Predation - This species may be an important predator on small and juvenile fishes in nontidal streams in the Chesapeake watershed (Angermeir 1992).
Competition - Juveniles of A. rupestris in Lake St. Clair, MI generally preferred larger Diptera and Trichoptera over other prey while Lepomis gibbosus (Pumpkinseed) had no clear prey preference. Lepomis gibbosus was much more efficient than A. rupestris at foraging under a canopy of submersed vegetation; gut fullness in A. rupestris decreased with increasing vegetation surface area (French 1988).
References - Angermeir 1992; French 1988; Jenkins and Burkhead 1993; Musick 1972a
Ecological Impacts on Other Chesapeake Non-Native Species
Ambloplites rupestris (Rock Bass) may have had impacts in nontidal rivers, but this species is rare below the Fall-Line, and only an occasional straggler in tidal waters (Jenkins and Burkhead 1993; Musick 1972a).
Competition - In the nontidal Potomac, MD, A. rupestris and Lepomis auritus (Redbreast Sunfish, native) biomass were inversely correlated with growth rates of juvenile Micropterus dolomieu (Smallmouth Bass, introduced) (Carlander 1977; Sanderson 1958). In the Niagara River NY, some overlap in food and habitat occurred between young of the year of A. rupestris and M. dolomieu, but A. rupestris preferred more vegetated sites, and ate more small prey (amphipods, copepods, cladocerans) while juvenile M. dolomieu ate more fish (George and Hadley 1979).
References - Carlander 1977; George and Hadley 1979; Jenkins and Burkhead 1993; Musick 1972a; Sanderson 1958)
References
Angermeier, Paul L. (1992) Predation by rock bass on other stream fishes: Experimental effects of depth and cover, Environmental Biology of Fishes 34: 171-180Bean, Tarleton H. (1893) The fishes of Pennsylvania, In: (Eds.) . , Harrisburg PA. Pp.
Bielo, Robert J. (1963) A fishery investigation of the Susquehanna River in Pennsylvania, In: (Eds.) . , Newark. Pp.
Carlander, Kenneth D. (1977) Handbook of Freshwater Fishery Biology. , In: (Eds.) Handbook of Freshwater Fishery Biology, Volume Two: Life History Data on Centrarchid Fishes of the U.S & Canada. , Ames. Pp. Ames
Cohen, Andrew N.; Carlton, James T. (1995) Nonindigenous aquatic species in a United States estuary: a case study of the biological invasions of the San Francisco Bay and Delta, , Washington DC, Silver Spring MD.. Pp.
Cope, Edward Drinker (1879) The Fishes of Pennsylvania, In: (Eds.) Report of the State Commisioners of Fisheries. , Harrisburg. Pp.
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Eaton, John G.; Swenson, William A.; McCormick, J. Howard; Simonson, Timothy D.; Jensen, Kathleen M. (1992) A field and laboratory investigation of acid effects on largemouth bass, rock bass, black crappie, and yellow perch, Transactions of the American Fisheries Society 121: 644-658
Elser, Harold J. (1960) Creel results on the Northeast River, Maryland, 1958, Chesapeake Science 1: 41-47
Fowler, Henry W. (1917) Notes on fishes from New Jersey, Pennsylvania, and Maryland, Proceedings of the Academy of Natural Sciences of Philadelphia 69: 108-126
Fowler, Henry W. (1933) Notes on Maryland fishes, The Fish Culturist 13: 8-9
French, John R. P. (1988) Effect of submersed aquatic macrophytes on resource partitioning in yearling rock bass (Ambloplites rupestris) and pumpkinseeds (Lepomis gibbosus) in Lake St. Clair, Journal of Great Lakes Research 14: 291-300
Fuller, Pam. L.; Nico, Leo; Williams, J. D. (1999) Nonindigenous fishes introduced into inland waters of the United States, , Bethesda MD. Pp.
George, Elinor L.; Hadley, Wayne F. (1979) Food and habitat partitioning between rock bass (Ambloplites rupestris) and smallmouth bass (Micropterus dolomieui) young of the year., Transactions of the American fisheries society 108: 253-261
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Lee, David S.; Norden, Arnold; Gilbert, Carter, R.; Franz, Richard (1976) A list of the freshwater fishes of Maryland and Delaware, Chesapeake Science 17: 205-211
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Mills, Edward L.; Scheuerell, Mark D.; Carlton, James T.; Strayer, David (1997) Biological invasions in the Hudson River: an inventory and historical analysis., New York State Museum Circular 57: 1-51
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1996-2014 NMNH Fish Collection Database.. http://collections.nmnh.si.edu/search/fishes/