Atractosteus spatula
alligator gar
Type Locality
None given (Lacepède
1803:333).
Etymology/Derivation of Scientific Name
Atractosteus: spindle
bone; spatula: spatula, in reference to the broad, elongate snout
(Ross 2001).
Synonymy
Lepisosteus spatula
Lacepède 1803:333; Cook 1959:60.
Lepidosteus spatula
Wailes 1854:333.
Atractosteus tristoechus
Hay 1881:333.
Lepisosteus tristoechus
Evermann 1899:304; Hildebrand and Tower
1928:113 (Ross 2001).
Characters
Maximum size: Up to
3,000 mm (118 in) TL (Lee and Wiley 1980). In 1951, a 127 kg (278 lb) fish
from the Rio Grande in Texas holds the U.S. hook-and-line record (IGFA 1999).
Coloration: Dark olivaceous brown above and white to yellowish beneath (individuals in
aquaria may be nearly black dorsally). Numerous dark spots may be present on
sides, but only below lateral line anteriorly. Rays of all fins brown,
with darker spots on the dorsal, anal and caudal fins. Young have a light
mid-dorsal stripe which is bordered by a dark brown area, extending from
tip of snout to origin of dorsal fin, and from posterior insertion of dorsal
fin to
upper base of caudal fin; dark irregular mid-lateral band may be present (Suttkus
1963).
Counts: 58-62 lateral
line scales; 59-66 gill rakers; 7-10 dorsal soft fin rays; 7-10 anal soft
fin rays (Suttkus
1963).
Body shape: Long and cylindrical.
Mouth position: . Terminal (Goldstein and Simon 1999).
Morphology: Ganoid scales; origin of dorsal fin posterior to
origin of anal fin; abbreviated heterocercal caudal fin.
Snout short and broad. Large teeth in upper jaw in two rows on each side (Hubbs et al. 1991; 2008).
Distribution (Native and Introduced)
U.S. distribution:
Gulf of Mexico drainages from Florida to Mexico including Ohio and Missouri
rivers of the Mississippi River drainage (Suttkus 1963; Wiley 1976); a
disjunct population reported from the Rio Sapoa and Lake Nicaragua (Wiley
1976).
Texas distribution:
Coastal streams from the Red River to the Rio Grande (Hubbs et al. 2008).
Warren et al. (2000) listed the following drainage units for distribution of
alligator gar in the state: Red River (from the mouth upstream
to and including the Kiamichi River), Sabine Lake (including minor coastal
drainages west to Galveston Bay), 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.
[Additional literature
noting collection of this species from Texas locations includes, but is not
limited to the following: Linam and Kleinsasser (1987); Gelwick et al.
(2001); Morgan (2002).]
Abundance/Conservation status (Federal, State,
Non-governmental organizations)
Listed as Vulnerable by the
American Fisheries Society; categories of threats: present or threatened
destruction, modification, or reduction of habitat or range; and
over-exploitation for commercial, recreational, scientific, or educational
purposes including intentional eradication or indirect impacts of fishing
(Jelks et al. 2008). Vulnerable in southern US (Warren et al. 2000). Some
states are listing alligator gar as a game fish to regulate harvest. Species
appears to be declining in the upstream segment of the lower Rio Grande
(Edwards and Contreras-Balderas 1991).
Habitat Associations
Macrohabitat:
Large rivers, bays, and coastal marine waters (Suttkus 1963; Lee and
Wiley 1980).
Mesohabitat: Generally
associated with near surface habitats in slack water and backwater habitats
of rivers. Preferred pool, pool-bank snag, pool-channel snag, pool-snag
complex, pool-edge, and pool-vegetation habitat groups, in the Sulphur
River, Texas (Gelwick and Morgan 2000). Zueg et al. (2005) reported
collection of four specimens in the Middle Brazos River, Texas and one in a
deep, frequently connected oxbow. Robertson et al. (2008) collected
specimens from the Middle Brazos River, Texas and associated oxbow lakes;
abundance significantly greater in oxbow habitats during a wet year. All
specimens collected from oxbows were juveniles, while only
adults were captured in the river channel; this perhaps due
to large individuals escaping capture in oxbow sampling, as evidenced by
large holes in gillnet and the visual record of a large individual in an
oxbow during flooding. Adults may move into oxbows during flooding to
exploit abundant prey, returning to the river channel later. Factors
including enhanced foraging, growth and survival may influence juveniles to
remain in oxbows for extended periods (Robertson et al. 2008). Knapp (1953)
noted that adults are abundant in brackish waters and in coastal harbors
where they feed on refuse from fish cleaning houses; young fish taken in
freshwater. Prior to 1955, large adults frequently taken from middle and
upper parts of the Red River arm of Lake Texoma (Oklahoma-Texas); only a few
captured annually since that time; no young known to have been taken in the
lake (Riggs and Bonn 1959). May and Echelle (1968) reported collection of
three young-of-the-year from shallow, turbid water in Wilson Creek cove
(Red River arm of Lake Texoma), in July 1965. McCarley and Hill (1979)
reported collection of two young-of-the-year specimens from a stockpond that
connects to the main body of Lake Texoma when the lake level is high, and
capture of a single young-of-the-year specimen from a cove in Lake Texoma
(Red River arm), in July 1978. In May 1950, six larval gar were collected
from a backwater slough off Red River (Oklahoma; Moore et al. 1970).
Biology
Spawning season: In
Louisiana, April to June (Suttkus 1963; Lee and Wiley 1980); from early to
mid-May, in Oklahoma (May and Echelle 1968); and late May, in Mississippi
(Cook 1959).
Spawning Habitat:
Phytophils; plant material nesters that have adhesive eggs and free embryos
that attach to plants by cement glands (Simon and Wallus 1989; Simon 1999).
Spawning behavior:
Nonguarders; open substratum spawners (Simon and Wallus 1989; Simon 1999).
Cook (1959) observed spawning, noting that fish splashed the surface of the
water frequently.
Fecundity: Mean
fecundity 157,291 eggs; mean egg diameter 2,060 microns (Ferrara 2001).
Lifetime reproductive output = 90.4 female offspring per female, in Alabama
(Ferrara 2001).
Age at maturation:
Ferrara (2001) reported age of maturation to be 14 years.
Migration: No
information at this time.
Growth and Population
Structure: Unknown; first year growth is rapid (Douglas 1974).
Longevity:
Long-lived. 50 years, in Alabama (Ferrara 2001).
Food habits: First and
second trophic classifications are carnivore and whole body, respectively;
trophic mode – ambush; very opportunistic predator (Goldstein and Simon
1999), consuming a variety of food items; primarily fishes (Bonham 1941) and
crabs (Darnell 1958, 1961; Lambou 1961; Suttkus 1963);
also birds (Raney 1942) and refuse
(Goodyear 1967). Based on a limited sample
size, shad and Suckers (Catastomidae) were the most important prey for this
species in the Middle Brazos River, Texas (Robertson et al. 2008).
Phylogeny and
morphologically similar fishes
Previously placed in
Lepisosteus by Suttkus (1963); placed by Wiley (1976) in the genus
Atractosteus (Lee and Wiley 1980). Species is separable from
Lepisosteus osseus (longnose gar) and L. oculatus (spotted gar)
by its large size and broad, short snout (Suttkus 1963); young A. spatula
distinguishable from young of L. oculatus, L. osseus, and
L. platostomus (shortnose gar) by the light dorsal stripe versus a dark
middorsal streak (Suttkus 1963; Simon and Wallus 1989).
Hybridization between A.
spatula and L. osseus has been reported (Gilbert 1992).
Herrington et al. (2008) provided conclusive evidence of intergeneric
hybridization in A. spatula and L. osseus and described hybrid
specimens spawned in an aquarium: body coloration and transverse scale rows
were similar to those of longnose gar; snout length and shape intermediate
between those of longnose and alligator gars; two rows of teeth on the upper
jaw as seen in alligator gar.
Descriptions of postlarval
A. spatula provided by Moore et al. (1973), and juveniles described by
Suttkus (1963) and May and Echelle (1968). Early development of specimens
from Lake Texoma (Oklahoma-Texas) described by Simon and Wallus (1989).
Host Records
Cestoda:
Proteocephalus ambloplitis. Trematoda: Clinostomum,
Rhipidocotyle lepisostei. Nemata: Contracaecum
spiculigerum, Dechelyne lepisosteus (Wardle 1990;
Mayberry et al. 2000), and Crustacea: Ergalis versicolor (Hoffman
1967).
Commercial or Environmental Importance
Popular recreational target
for bowfishing; some populations sustain a commercial harvest. With their
large size, large teeth, and opportunistic feeding behavior, alligator gars
are intimidating and often a concern to human swimmers. Attacks on humans
have not been confirmed. However, one credible account was described by an
old fisherman from the Rio Grande Valley. As a young boy, he and his
brother were swimming in a deep, slack water area of the Rio Grande near a
makeshift dock. While swimming, he felt something grasp and scrap his leg.
Feeling pain, he turned and swum toward the dock. Halfway to the dock, he
felt something attempt to grasp and then scrap his bare chest. He
immediately grabbed for the attacker, feeling the mouth and head of a gar.
After reaching the dock, he called for his brother to get out of the water.
By this time his leg and chest were superficially scraped and bleeding
although the gar’s teeth did not penetrate the dermis layer of his skin. He
and his brother waited for a few minutes on the dock and visually confirmed
the presence of an alligator gar in the immediate vicinity of the attack.
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