Ictiobus niger
black buffalo
Type Locality
Ohio River (Rafinesque 1820).
Etymology/Derivation of Scientific Name
Ictiobus: bull-like
fish; niger: black (Ross 2001).
Synonymy
Catostomus niger
Rafinesque 1820:56.
Ictiobus niger Cook
1959:81.
Characters
Maximum size: 929 mm
TL (Carlander 1969).
Coloration: Blue-gray
to dark brown above, light brown laterally, and yellowish white below
(Miller and Robison 2004). Normally the darkest and most slaty-colored of
the buffalofishes; light colored only when collected from very turbid
waters. Spring males are often blackish (Trautman 1981). Piller et al.
(2003) reported that the body coloration of breeding male and female fish
from Citico Creek, Tennessee was blue-gray in color; venter was white or
cream colored; all paired and median fins were darker in color than the rest
of the body.
Teeth count: About 195
per arch (Becker 1983).
Counts: Fewer than 45
lateral line scales; 22-30 dorsal fin rays (Hubbs et al. 1991); fewer than
60 gill rakers in the first arch (Miller and Robison 2004); 8-10 anal fin rays; 15-16 pectoral fin rays; and 9-11 pelvic fin
rays (Ross 2001).
Body shape: Body more
elongate, greatest depth contained 2.6 to 3.3 times in standard length;
thickness of head contained fewer than five times in standard length; eye
nearer tip of snout than back of head; head gradually slenderer than body
(Hubbs et al.1991).
Mouth position: Small
and only slightly oblique; upper jaw
distinctly shorter than snout; upper lip well below lower margin of orbit;
lips thick and coarsely striate (Hubbs et al 1991).
External morphology:
Distance from posterior tip of maxillary to front of mandible greater than
eye length (about twice eye length in large adults);
subopercle broadest at middle, subsemicircular; cheek shallow and
foreshortened (distance from eye to posteroventral angle of preopercle
three-quarters of distance to upper corner of gill slit); dorsal fin base
more than one-third standard length (Hubbs et al. 1991). Entire body of
nuptial males from Citico Creek, Tennessee were covered by small whitish
tubercles, most pronounced on cheek and opercular region; tubercles tended
to be smaller, less numerous on posterior half of body than on anterior
half; body tuberculation most pronounced below lateral line, with scales
containing 10-16 tubercles; above the lateral line, tubercles smaller and
less numerous; tubercles present on all fins; fin tuberculation most
pronounced on anal and caudal fins, with tubercles running along entire
length of anterior rays (rays 1-6), but confined to distal portions of more
posterior rays; only anterior portion of dorsal fin tuberculate (Piller et
al. 2003).
Internal morphology:
Gut much elongated, with loops running parallel to body axis (Becker 1983;
Goldstein and Simon 1999). Pharyngeal teeth short, narrow, and fragile,
about 195 per arch; well developed crown of tooth with cusp at anterior
edge; arch moderately strong, with large honeycomb spaces on anterior edge;
the symphysis short, on moderately long stems of the arch (Becker 1983).
Distribution (Native and Introduced)
U.S. distribution:
Occurs throughout the Mississippi, Ohio, Missouri, and adjacent basins
(Hubbs et al. 1991).
Texas distribution:
Scattered records known from throughout the state, including from the Rio
Grande, Colorado, Brazos, Sabine, and Red basins (Hubbs et al 1991). Early
taxonomic difficulties in recognizing this species, its unusually disjunct
distribution pattern, and its apparent rarity in the state of Texas suggest
a possible introduction of this species at many localities (Conner 1977), or
many intermediate records have been published that are misidentifications of
the common smallmouth buffalo, I. bubalus (Shute 1980; Hubbs et al.
1991). Warren et al. (2000) list the following drainage units for
distribution of Ictiobus niger in the state: Red River (from the
mouth upstream to and including the Kiamichi River), and the Colorado River.
Abundance/Conservation status (Federal, State, NGO)
Populations in the southern
United States are currently secure (Warren et al. 2000).
Habitat Associations
Macrohabitat: Often
found in strong currents and large rivers (Shute 1980). Species seems to
favor flowing waters to a greater extent than do Ictiobus bubalus
(smallmouth buffalo) or I. cyprinellus (bigmouth buffalo; Cross 1967;
Becker 1983; Miller and Robison 2004); preferred habitat of I. niger seems
to be intermediate between the other two buffalo species (Trautman 1981).
Species occurs in large rivers, back waters, and sloughs (Ross 2001);
although generally uncommon in the lower Mississippi River (Baker et al.
1991), fish have been collected in coves adjacent of the main channel (Ross
2001). In Lake Texoma, Oklahoma and Texas,
species was very rare, but was the most common of the genus in the
tailwaters (Riggs and Bonn 1959). Taken from Mountain Fork River and was
numerous in cutoff lakes sampled in the Little River drainage area,
McCurtain Co., Oklahoma; found over bottoms which were composed of one or
more of the following: silt, gravel, mud, detritus, bedrock, rubble, and
fallen timber; collected from clear to turbid waters (Finnel et al. 1956).
Mesohabitat: Species
found in water of varying turbidity over a wide variety of bottoms (Becker
1983). In Kansas, species collected in deep, fast riffles where river
channel narrows (Cross 1967). In Ohio, occasionally abundant in turbid,
mud-bottomed, shallow, overflow ponds and sloughs (Trautman 1981). In the
Sulphur River, Texas, species was most abundant in pool-vegetation habitat
(Gelwick and Morgan 2000). Pigg and Gibbs (1995) noted that Ictiobus
niger preferred a stronger current than other buffalo fishes, and
reported collection of fish from the mainstem of the North Canadian River
near Wetumka, Oklahoma in deeper, swift currents.
Biology
Spawning season: In
Citico Creek, Tennessee, spawning occurs yearly in April, and is often 4-5
days in duration (Piller et al. 2003). Probably occurs in April and May,
although a tuberculate male was captured from the lower Wisconsin River in
mid-June (Becker 1983). In Mississippi, Yeager (1936) observed spawning in
April.
Spawning location:
Lithopelagophils, rock and gravel spawners with pelagic free embryos (Simon
1999). In Citico Creek (Little Tennessee River system), a small upland
stream in Tennessee, fish spawned in the upper portion of water column and
adhesive eggs were broadcast over a variety of substrates from gravel to
bedrock; spawning mainly occurred in runs and pools (75% of observations),
but sometimes occurred in deep riffles (25% of observations; Piller et al.
2003); eggs found over the stream bottom even in cascading riffles,
suggesting that they were carried some distance downstream from the spawning
site. In the Mississippi River, spawning observed in shallow water along
margin of a flooded swamp (Yeager 1936). Perry (1976) reported spawning in
brackish ponds with salinities of 16-18 mg/l.
Reproductive strategy:
Non-guarders; open substratum spawners (Simon 1999). Piller et al. (2003)
observed spawning in Citico Creek, Tennesee: species predominately spawned
in trios of one female, and two males, and did not prepare substrate or
employ territorial defense. Prior to spawning males were evenly spaced
throughout spawning area, while the largest females were mainly concentrated
in slack areas along shore. Spawning was initiated by female swimming away
from bank and moving among males at mid-channel, with males eventually
swimming alongside the female. Female swam upward in the water column while
eggs were released, this action drawing additional males to the group (from
5-10). Vigorous splashing was produced as backs and tails of the group of
fish broke the water surface, and as the fish quivered as males attempted to
crowd in near to the female. On occasion, males were observed to dive over
the top of the spawning group. Spawning act was brief, lasting from 2-4
seconds. The group swam to the stream bottom and slowly dispersed after the
spawning act, with males and females resuming pre-spawning positions in the
stream. A small number of males remained near the female for a time, nudging
the female as if to induce more egg laying. No evidence of post-spawning
mortality was observed. In the Mississippi River, spawning was observed in
shallow water: individuals were active at the water surface splashing,
leaping from the water, and making quick forward movements over short
distances (Yeager 1936) in a manner very similar to that described as the
“spawning rush” for a similar species, Ictiobus cyprinellus (bigmouth
buffalo; Ross 2001).
Fecundity: Small
number of specimens examined by Piller et al. (2003) suggested that
fecundity is substantially more than 9,000 eggs (number of eggs that
remained in the ovaries of a mostly spent female) and that all of the eggs
are spawned. Fertilized eggs are demersal, adhesive; eggs average 1.8-2.4 mm
in diameter; hatching occurs in 24-36 hours at 19-24 degrees C (Ross 2001).
Age/Size at maturation:
In the south, age 2 (Perry 1976). In Illinois, Barnickol and Starrett (1951)
reported smallest ripe female to be 470 mm (18.5 in) long (Becker 1983).
Migration: In a study
of Ictiobus niger from Citico Creek, Tennessee, fish migrated from a
reservoir into a small, swift-flowing, cool-water stream to spawn (Piller et
al. 2003).
Longevity: 24 year-old
fish reported from Illinois (Carlander 1969).
Food habits: Consumes
plankton, insect larvae, and vegetation; snails and other small mollusks are
diet items, often in large quantities (Shute 1980; Miller and Robison 2004).
In Arizona reservoirs, main food item was the introduced Asiatic clam (Corbicula
manilensis), while blue-green algae, diatoms, and crustaceans were also
ingested (Minkley et al. 1970).
Growth and Population
structure: In the Southeast, growth fairly rapid with fish averaging 134
mm TL after their first year, and 236 mm TL, 330 mm TL, 399 mm TL, 468 mm
TL, 504 mm TL, 563 mm TL, and 589 mm TL after years 2-8, respectively
(Carlander 1969; Ross 2001). In Citico Creek, Tennessee, the sex ratio
appeared to strongly favor males, as they dominated spawning bouts by as
much as 10 to 1. A collection of 12 specimens (not spawning at time of
capture) yielded 9 males and 3 females, though this may have been due to
females entering and leaving the creek at different times during the
spawning run (Piller et al. 2003).
Phylogeny and morphologically similar fishes
Ictiobus niger is most
similar to I. bubalus (smallmouth buffalo), but differs in body depth
proportions (more than 2.9 versus less than 2.8 times into SL; Ross 2001).
Young I. niger, less than 305 mm, are difficult to distinguish from
I. bubalus (smallmouth buffalo; Trautman 1981). However, Etnier and
Starnes (1993) listed ratios of measurement that may be useful in
differentiating I. niger and I. bubalus (niger listed
first): eye diameter in head length 5.1-7.4 vs. 4.4-5.9; eye diameter in
snout length 2-2.5 vs.1.5-2; maximum head width in standard length 4.7-5.5
vs. 5.2-6.1; maximum body depth in standard length 2.9-3.4 vs. 2.4-2.8.
I. niger differs from I. cyprinellus (bigmouth buffalo) in having
a subterminal (versus terminal) mouth and in having lower GR counts on the
lower limb of the first arch (less than 35 versus more than 40; Ross 2001).
Moore (1968) reported hybridization between I. niger and I.
bubalus (smallmouth buffalo) in some impoundments; offspring were not
able to be identified. Experimental I. niger X I. cyprinellus
hybrids reported (Stevenson 1964; Hollander and Avault 1975).
Host Records
Trematoda
(1), Cestoda (2), Acanthocephala (1; Hoffmann 1967). Cestoda: Glaradacris
confusus; Trematoda: Lissorchis gullaris, Nematobothrium
texomensis (Mayberry et al. 2000).
Commercial or Environmental
Importance
Although
apparently not an important factor limiting the reproductive success of
Ictiobus niger, Piller et al. (2003) reported that Ambloplites
rupestris (rock bass) was one of four species found to heavily predate
I. niger eggs, in a Tennessee stream. Crossman and Nepszy (1979)
reported the first Canadian record of I. niger captured in Lake Erie,
in June 1978. This species often referred to by commercial fisherman
as “rooters” due to their bottom-feeding habits (Ross 2001).
References
Baker, J.A., K.J. Kilgore, and R.L. Kasu. 1991. Aquatic habitats and fish
communities in the lower Mississippi River. Rev. Aqat. Sci. 3(4):313-356.
Barnickol, P.G., and W.C. Starett. 1951. Commercial and sport fishes of the
Mississippi River between Caruthersville, Missouri, and Dubuque, Iowa. Ill.
Nat. Hist. Surv. Bull. 25(5):263-350.
Becker, G.C. 1983. Fishes of Wisconsin. University of Wisconsin Press,
Madison. 1052 pp.
Carlander, K.D. 1969. Handbook of Freshwater Fishery Biology. Ames, The Iowa
State University Press. 752 pp.
Conner, J.V. 1977. Zoogeography of freshwater fishes in western Gulf slope
drainages between the Mississippi and the Rio Grande. Unpublished Ph.D.
dissertation, Tulane Univ., New Orleans, Louisiana. 280 pp.
Cook, F. A. 1959. Freshwater fishes in Mississippi. Mississippi Game and
Fish Commission, Jackson. 239 pp.
Cross, F.B. 1967. Handbook of Fishes of Kansas. Univ. Kans. Mus. Nat. Hist.
Misc. Publ. 45. 357 pp.
Crossman, E.J., and S.J. Nepszy. 1979. First Canadian record of the black
buffalo (Osteichthyes: Catostomidae). Canadian Field-Naturalist
93(3):304-305.
Etnier, D.A., and W.C. Starnes. 1993. The Fishes of Tennessee. The
University fo Tennessee Press, Knoxville. 681 pp.
Finnel, J.C., R.M. Jenkins, and G.E. Hall. 1956. The fishery resources of
the Little River System, McCurtain County, Oklahoma. Oklahoma Fishery
Research Laboratory Report 55. 81 pp.
Gelwick, F.P., and M.N. Morgan. 2000. Microhabitat use and community
structure of fishes downstream of the proposed George Parkhouse I and Marvin
Nichols I reservoir sites on the Sulphur River, Texas. Report to the Texas
Water Development Board. 124 pp.
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.
Hoffman, G.L. 1967. Parasites of North American Freshwater Fishes.
University of California Press, Berkeley. 486 pp.
Hollander, E.E., and J.W. Avault, Jr. 1975. Effects of salinity on survival
of buffalo fish eggs through yearlings. Progressive Fish-Culturist
37(1):47-51.
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.
Texas Journal of Science, Supplement 43(4):1-56.
Mayberry, L.F., A.G. Canaris, and J.R. Bristol. 2000. Bibliography of
parasites and vertebrate host in Arizona, New Mexico, and Texas (1893-1984).
University of Nebraska Harold W. Manter Laboratory of Parasitology Web
Server pp. 1-100.
Miller, R.J., and H.W. Robison. 2004. Fishes of Oklahoma. University of
Oklahoma Press, Norman. 450 pp.
Minckley, W.L., J.E. Johnson, J.N. Rinne, and S.E. Willoughby. 1970. Foods
of buffalofishes, genus Ictiobus, in central Arizona reservoirs.
Trans. Amer. Fish. Soc. 99:33-342.
Perry, W.G. 1976. Black and bigmouth buffalo spawn in brackish water ponds.
Progressive Fish-Culturist 38(2):81.
Pigg, J., and R. Gibbs. 1995. Occurrences of Catostomid fishes (suckers) in
the North Canadian River and Lake Eufaula, Oklahoma. Proc. Okla. Acad. Sci.
75:7-12.
Piller, K.R., H.L. Bart, Jr., and J.A. Tipton. 2003. Spawning in the black
buffalo Ictiobus niger (Telostomi: Catostomidae). Ichthyological
Explorations of Freshwater 14:145-150.
Rafinesque, C.S. 1820. Ichthyologia Ohiensis, or natural history of the
fishes inhabiting the River Ohio and its tributary streams, preceded by a
physical description of the Ohio and its branches. W. G. Hunt, Lexington,
Ky.
Riggs, C.D., and E. W. Bonn. 1959. An annotated list of the fishes of Lake
Texoma, Oklahoma and Texas. The Southwestern Naturalist 4(4):157-168.
Ross, S.T. 2001. The Inland Fishes of Mississippi. University Press of
Mississippi, Jackson. 624 pp.
Simon, T.P. 1999. Assessment of Balon’s reproductive guilds with application
to Midwestern North American Freshwater Fishes, pp. 97-121. In:
Simon, T.L. (ed.). Assessing the sustainability and biological integrity of
water resources using fish communities. CRC Press. Boca Raton, Florida. 671
pp.
Stevenson, J.H. 1964. Fish farming experimental station – Stuttgart,
Arkansas. U.S. Fish Wild. Serv. Circular 178:79-100.
Trautman, M.B. 1981. The Fishes of Ohio. Rev. Ed., Ohio State Univ. Press,
Columbus. 782 pp.
Warren, M.L.,
Jr., B.M. Burr, S.J. Walsh, H.L. Bart, Jr., R.C. Cashner, D.A. Etnier, B.J.
Freeman, B.R. Kuhajda, R.L. Mayden, H.W. Robison, S.T. Ross, and W.C.
Starnes. 2000. Diversity, Distribution, and Conservation status of the
native freshwater fishes of the southern United States. Fisheries
25(10):7-29.
Yeager, L.E. 1936. An observation of spawning bufffalofish in Mississippi.
Copeia 1936(4):716-728.
|