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	Campostoma anomalum   
	central stoneroller 
	  
	  
	Type Locality 
	Licking River, Kentucky 
	(Rafinesque 1820). 
	  
	Etymology/Derivation of Scientific Name  
	Campostoma meaning 
	“curved mouth,” anomalum meaning “extraordinary” (Becker 1983). 
	  
	Synonymy 
	Rutilus 
	anomalum Rafinesque 1820:52 
	
	Campostoma anomalum Cook 1959:95 
	
	Campostoma anomalum pullum Burr and Cashner 
	1983:115. 
	(Ross 
	2001). 
	  
	Characters 
	Maximum size: 287 mm 
	(11.3 in) 
	TL (Lennon and Parker 1960). 
	
	  
	Coloration: Dark 
	olivaceous above, grading to whitish on the underside; sides of most adults 
	marked by randomly scattered, small, dark spots which represent regenerated 
	scales; fins colorless (Miller and Robison 2004). Breeding males develop 
	striking color patterns, the entire dorsum becoming dark slate-gray; 
	undersides of body and lower fins are pale, sometimes yellowish; dorsal, 
	anal, and pelvic fins with black pigment (Miller 1962). 
	Peritoneum lining black  
	(Goldstein and Simon 1999). 
	  
	Pharyngeal teeth count: 
	0,4-4,0 or 1,4-4,1 (Page and Burr 1991), usually 0,4-4,0(Burr and Cashner 1983; 
	Miller and Robison 2004). 
	
	  
	Counts: 49-57 lateral 
	line scales; scales around the body 39-46; 8 dorsal fin soft rays; 7 
	anal fin soft rays; 8 pelvic fin soft rays (Miller and Robison 2004).  
	
	  
	Body shape:  Terete 
	and stout. 
	
	  
	Mouth position: 
	Subterminal. 
	
	  
	Morphology:  
	Lower jaw with cartilaginous ridge (Hubbs et al. 1991). Mature males have 
	large, slightly hooked whitish tubercles on top of head between nape and 
	nostrils, grading into smaller tubercles on the entire dorsum (tubercles 
	lost shortly after spawning; Miller 1962).  Intestine very long, 
	spirally-wound completely 
	around air bladder (Hubbs et al. 1991; 
	Goldstein and Simon 1999). 
	  
	Distribution (Native and Introduced) 
	U.S. distribution: 
	Widespread throughout the eastern United States (Hubbs et al. 1991). 
	Isolated populations in Rio San Juan, Mexico, and smaller tributaries of 
	Thames River, ON (Burr 1980). 
	  
	Texas distribution: 
	Found primarily in streams of the Edwards Plateau and occurs as far west as 
	the Devils River and Sycamore Creek (Hubbs et al. 1991; Edwards 1997). 
	Warren et al. (2000) listed the following drainage units for distribution of 
	this species in the state: Red River (from the mouth upstream 
	to and including the Kiamichi River), Galveston Bay (including minor coastal 
	drainages west to mouth of Brazos River), Brazos River, Colorado River, San 
	Antonio Bay (including minor coastal drainages west of mouth of Colorado 
	River to mouth of Nueces River), Nueces River. Hubbs (1957) reported that 
	the species has been taken in the Red River Drainage of eastern Texas but 
	not from the Sabine; is common in limestone waters to the west; further, 
	this species inhabits the entire Balconian Biotic Province and parts of the 
	Rio Grande system. 
	  
	[Additional literature 
	noting collection of this species from Texas locations includes, but is not 
	limited to the following: Hubbs (1954); Hubbs and Hettler (1958); 
	Lundberg (1967); Whiteside and McNatt (1972); Edwards (1978); Rose and 
	Echelle (1981); Gold (1984); Linam and Kleinsasser (1987).] 
	  
	Abundance/Conservation status (Federal, State, Non-government 
	organizations):
	 
	Currently secure in the 
	southern Unites States (Warren 2000). 
	  
	Habitat Associations 
	Macrohabitat: Small to 
	medium sized streams (Burr 1980). 
	
	  
	Mesohabitat: 
	Associated with gravel substrate in clear to turbid riffles and pools in 
	higher-gradient streams (Burr 1980). In Texas, and elsewhere, generally 
	found in small, clear streams with gravel, rubble, or exposed bedrock 
	(Edwards 1997); often the most abundant species in small streams and schools 
	may contain several hundred individuals (Miller 1962; Becker 1983; Matthews et al. 
	1987; Edwards 1997). Species collected exclusively in the tailwaters of 
	Possum Kingdom Reservoir, Texas (Anderson et al. 1983). Riggs and Bonn 
	(1959) reported the species as common in Buncombe and Briar creeks and other 
	rocky, sandy tributaries on the Oklahoma side of Lake Texoma. Commonly found 
	in tailwater tributaries of the Kiamichi River, Oklahoma, and in smaller 
	less permanent streams; typically occurring in gravelly or rocky riffles 
	(Echelle and Schnell 1976). Mundahl and Ingersoll (1989) collected specimens 
	from pools and riffles in a small Ohio stream. Commonly found in smaller 
	creeks maintaining at least some current throughout the majority of the 
	year, especially during spring spawning season (Edwards 1997). Newly hatched 
	central stonerollers school and feed near vegetated stream margins and in quiet warm 
	backwaters in the late spring and early summer; juveniles frequently inhabit 
	swifter waters around vegetated riffles during the summer and fall, and are 
	commonly found in midstream habitats in pools having algal mats and 
	moderately flowing currents (Theodorakis 1987; Leonard and Orth 1988; 
	Mundahl and Ingersoll 1989; Edwards 1997).  Central stonerollers display some intolerance 
	to heavy siltation or pollutants which may affect quantity of available 
	algae in pool and riffle habitats (Edwards 1997). 
	  
	Biology 
	Spawning season:  In 
	Texas, nest building from early February through early July, spawning from 
	mid-February through mid-July (Edwards 1997). 
	
	  
	Spawning location: 
	 Pools adjacent to riffles (Burr 1980). In smaller creeks, sites located at 
	the upstream portions of pools in slow-moving areas, frequently in 
	association with significant quantities of sand, gravel, and abundant algal 
	mats (Edwards 1997). In Great Smokey Mountain National Park, central 
	stonerollers 
	constructed nests in gravel in the tailwater of pools and at the heads of 
	riffles in the main stream as well as small tributaries (Lennon 
	and Parker 1960). 
	
	  
	Reproductive strategy: 
	Nonguarders; brood hiders; lithophils – rock and gravel spawners that do not 
	guard their eggs (Reed 1958; Miller 1962; Simon 1999). Males build pits in 
	gravel riffles by “rolling” larger stones away; eggs adhesive and attached 
	to stones in nest; males defend nests (Miller 1962). This species will spawn 
	over the nests of Semotilus atromaculatus (creek chub), but may also 
	be displaced from the nest by this larger species of cyprinid. Central 
	stoneroller nests may also be used by other cyprinid fishes (Miller 
	1962; Miller 1964). 
	
	  
	Fecundity: Estimated 
	200 – 4800 eggs per female, with females ranging in size from 65-130 mm 
	(2.56-5.11 in) SL 
	(Schmulbach 1957). Mature egg measures 2.0 mm (0.08 in)diameter, and measures 2.4 mm 
	(0.09 in) diameter when placed in water (at which time chorion is released 
	from yolk and slowly fills with water); unfertilized eggs are sphere-shaped 
	and dull gray in appearance; fertilized eggs bright yellow and adhesive 
	(Reed 1958); hatching occurs in approximately 69-72 hours (Reed 1958; Hiltibran 1967). 
	
	  
	Age at maturation:
	Likely by age 1. Hubbs and Cooper (1936) estimated that maturity is 
	reaches during the 2nd or 3rd summer. In Wisconsin, 
	breeding fish are age 2 or 3 (Becker 1983). In Great Smokey Mountain 
	National Park, majority of fish reached maturity in their 3rd or 
	4th year of life (Lennon and Parker 1960).  
	
	  
	Migration: Smith 
	(1935) observed this species in streams forming part of the Susquehanna 
	drainage, principally in Catatonk, Jackson, and Newtown Creeks, New York, 
	reporting that it is essentially a migratory fish, ascending smaller streams 
	to spawn in early spring; relatively few fish remain in small streams all 
	year. 
	
	  
	Longevity:
	3 to 4 years (Edwards 1997). Lennon and Parker (1960) reported 
	collection of specimens up to 6 years old, in Great Smokey Mountains 
	National Park. 
	
	  
	Food habits: Primarily 
	herbivorous, using its cartilaginous lower jaw to feed on filamentous algae, 
	diatoms, aquatic insects (Fowler and Tabor 1985, McNeely 1987). Young fish 
	feed on rotifers, filamentous algae, and microcrustacea (Edwards 1997). 
	Matthews et al. (1986) observed schools of fish grazing over rocks or on 
	limestone ledges, and reported that distinctive grazing scars were left on 
	areas as a result of feeding on algae. Goldstein and Simon (1999) listed 
	first and second level trophic classifications for this species as herbivore 
	and particulate feeder, respectively; trophic mode: grazer; feeding 
	behavior: grazing minnow. 
	
	  
	Growth: Up to 
	65 mm (2.56 in) SL by age 1 and 110 mm (4.33 in) SL by age 2 (Edwards 1997). 
	In Big Creek, Great Smokey Mountains National Park, the length range of age 
	groups were recorded as: 0 – 56mm (2.20 in), I – 79-104 mm  
	(3.11-4.09 in), II – 117-132 
	mm (4.60-5.20 in), III – 127-206 mm (5.00-8.11 in), IV – 165-239 mm 
	(6.50-9.41 in), and V – 173-226 mm (6.81-8.90 in) (Lennon and Parker 1960; 
	Becker 1983).  
	  
	Phylogeny and morphologically similar fishes: 
	Campostoma form a 
	monophyletic group with Dionda and Hybognathus (Coburn and 
	Cavender 1992).  In Texas, C. anomalum closet extant relative is 
	C. ornatum (Mexican stoneroller).  Campostoma anomalum has larger 
	scales than C. ornatum (Hubbs et al. 1991) with the gas bladder 
	completely enclosed by the spirally-wound intestine; Campostoma ornatum 
	has a gas bladder only partially enclosed by the spirally-wound intestine.
	C. anomalum and C. ornatum differ further in that C. 
	anomalum has 49-57 lateral line scales (Miller and Robison 2004), and 
	36-46 scales around body at dorsal fin origin, while C. ornatum has 
	58-77 lateral scales, and has 47-60 scales around body at dorsal fin origin 
	(Page and Burr 1991). 
	  
	Host Records: 
	Monogenetic 
	trematodes: Dactylogyrus acus, D. georgiensis, D. 
	katherineae, D. semotilus (Mizelle and McDougal 1970). 
	  
	Commercial or Environmental 
	Importance 
	According to Lennon and 
	Parker (1960), in Great Smokey Mountains National Park, central 
	stonerollers destroy redds of Salmo gairdneri (rainbow trout), 
	consequently limiting trout reproduction. 
	  
	References 
	
	Anderson, K.A., T.L. Beitinger, and E.G. Zimmerman. 1983. Forage fish 
	assemblages in the Brazos River upstream and downstream from Possum Kingdom 
	Reservoir, Texas. Journal of Freshwater Ecology 2(1):81-88. 
	
	Becker, G.C. 1983. Fishes of Wisconsin.  The University of Wisconsin Press, 
	Madison. 1052 pp. 
	
	Burr, B.M. 1980. Campostoma anomalum (Rafinesque), Stoneroller. 
	pp.143 in D. S. Lee, et al.  Atlas of North American Freshwater Fishes.  N. 
	C. State Mus. Nat. Hist., Raleigh. i-r+854 pp.  
	
	Burr, B.M., and R.C. Cashner. Campostoma pauciradii, a new cyprinid 
	fish from southeastern United States, with a review of related forms. Copeia 
	1983(1):101-116. 
	
	Cook. F.A. 1959. Freshwater fishes in Mississippi. Mississippi Fame and Fish 
	Commission, Jackson. 239 pp. 
	
	Echelle, A.A., and G.D. Schnell. 1976. Factor analysis of species 
	associations among fishes of the Kiamichi River, Oklahoma. Trans. Amer. 
	Fish. Soc. 105(1):17-31. 
	
	Edwards, R.J.  1997.  Ecological Profiles for Selected Stream-Dwelling Texas 
	Freshwater Fishes.  Texas Water Development Board, Report.  89 pp.   
	
	Edwards, R.J. 1978. The effect of hypolimnion reservoir releases on fish 
	distribution and species diversity. Trans. Amer. Fish. Soc. 107(1):71-77. 
	
	Fowler, J.F. and C.A Taber.  1985.  Food habits and feeding periodicity in 
	two sympatric stonerollers (Cyprinidae).  American Midland Naturalist, 
	113(2):217-224. 
	
	Gold, J.R. 1984. Silver-staining and heteromorphism of chromosomal nucleolus 
	organizer regions in North American cyprinid fishes. Copeia 1984(1):133-139. 
	
	Goldstein, R.M., and T.P. Simon. 1999. Toward a united definition of guild 
	structure for feeding ecology of North American freshwater fishes. pp. 
	123-202 in T.P. Simon, editor. Assessing the sustainability and 
	biological integrity of water resources using fish communities. CRC Press, 
	Boca Raton, Florida. 671 pp. 
	
	Hiltibran, R.C. 1967. Effects of some herbicides on fertilized fish eggs and 
	fry. Trans. Amer. Fish. Soc. 96(4):414-416. 
	
	Hubbs, C. 1954. Corrected distributional records for Texas freshwater 
	fishes. Texas Journal of Science 1954(3):277-291. 
	
	Hubbs, C., and W.F. Hettler. 1958. Fluctuations of some central Texas fish 
	populations. The Southwestern Naturalist 1(1/4):13-16. 
	
	Hubbs, C. 1957. Distributional patterns of Texas fresh-water fishes. The 
	Southwestern Naturalist 2(2/3):89-104. 
	
	Hubbs, C., R. J. Edwards, and G. P. Garrett.  1991.  An annotated checklist 
	of the freshwater fishes of Texas, with keys to identification of species.  
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	Hubbs, C.L., and G.P. Cooper. 1936. Minnows of Michigan. Cranbrook Inst. of 
	Sci., Bull. 8. 84 pp. 
	
	Lennon, R.E. and P.S. Parker. 1960. The stoneroller minnow, Campostoma 
	anomalum (Rafinesque), in Great Smoky Mountains National Park.  Trans. 
	Amer. Fish. Soc. 89:263-270. 
	
	Leonard, P.M., and D.J. Orth. 1988. Use of habitat guilds of fishes to 
	determine instream flow requirements. N. Amer. J. Fish. Manage. 
	8(4):399-409. 
	
	Linam, G.W., and L.J. Kleinsasser. 1987. Fisheries use attainability study 
	for the Bosque River. River Studies Report No. 4. Resource Protection 
	Division, Texas Parks and Wildlife Department, Austin. 24 pp. 
	
	Lundberg, J.G. 1967. Pleistocene fishes of the Good Creek Formation, Texas. 
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	Matthews, W.J., M.E. Power, and A.J. Stewart. 1986. Depth distribution of 
	Campostoma grazing scars in an Ozark stream. Environmental Biology of 
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	Matthews, W.J., A.J. Stewart, and M.E. Power. 1987. Grazing fishes as 
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	McNeely, D.L.  1987.  Niche relations within an Ozark stream cyprinid 
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	Miller, R.J. 1964. Behavior and ecology of some North American cyprinid 
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	Mundahl, N.D., and C.G. Ingersoll. 1989. Home range, movements, and density 
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