Cichlasoma cyanoguttatum
Rio Grande cichlid
Type Locality
Rio Grande, Brownsville,
Texas. (Baird and Girard 1854).
Etymology/Derivation of Scientific Name
Cichlasoma, Greek for
"body of a wrasse," a similar type of fish; cyanoguttatum Greek for
"blue-spotted" (Tomelleri and Eberle 1990).
Synonymy
Herichthys cyanoguttatus
(H. cyanoguttatum) (C. cyanoguttatus) (Miller et al. 2005; Regan 1905;
1906-1908).
Characters
Maximum size: 30 cm TL
(Page and Burr 1991).
Coloration: Adults are
easily distinguished by their mostly sky blue coloration. Females are less
colorful than males (Stevenson 1976). Dusky to olive above; 4-6 dark
blotches (1st blotch most prominent) along rear half of side,
usually confluent with dusky saddles;black blotch on caudal fin base.
Numerous small white to blue spots on blue-green or gray side. Adults have
iridescent blue-green spots or wavy lines on head, body and fins. Breeding
adults have white head, front half of body; black rear half of body (Page
and Burr 1991).
Pharyngeal teeth count:
Counts: 5 or 6 anal
fin spines (Hubbs et al 1991); 15-18 dorsal fin spines (Stevenson 1976);
10-12 dorsal rays; 9-10 anal rays (Page and Burr 1991).
Body shape: General
oval shape (Fontaine 1938).
Mouth position:
External morphology:
One nostril opening on each side of the head; interrupted lateral line (Itzkowitz
and Nyby 1982) that is doubled for a short distance on the caudal peduncle (Tomerelli
and Eberle 1990). Breeding males have a
prominent nuchal hump (Fontaine 1938; Page and Burr 1991).
Distribution (Native and Introduced)
U.S. distribution:
Native to the United States and Texas only in the Rio Grande and Pecos
drainages, this species is also native to northeastern Mexico (Hubbs et al.
1991).; introduced in Florida (Birkhead 1980). Seasonally cool water
restricts spread of species to the north (Tomerelli and Eberle 1990).
Texas distribution:
Native to the Rio Grande and Pecos drainages (Brown 1953); introduced
northwards to Central Texas in the Edwards Plateau region. (Birkhead 1980).
Populations exist as far north as the San Gabriel River in the Brazos River
system (Hubbs et al. 1991). Hubbs (1957) reported that the species was
essentially limited to the Tamaulipan Biotic Province, in Texas.
Abundance/Conservation status (Federal, State, NGO)
Not threatened (Tomerelli and
Eberle 1990).
Habitat Associations
Macrohabitat: Larger
springs and outflows where winter temperatures are favorable (Birkhead
1980). Ponds, springs, lagoons, creeks, rivers (in pools and backwaters) and
springs (Miller et al. 2005). Along outskirts of its northern limit in the
Edwards Plateau, this species can survive cool winters only in the “cooling
lakes” of power plants or in rivers near the outlets of warm springs (Tomerelli
and Eberle 1990).
Mesohabitat: Minimum
temperature tolerance between 14°C-19°C,
in Colorado River at Austin, Texas (Hubbs 1951). Thriving under lake-like
conditions in slight to strong currents and clear to murky or turbid water;
substrates of boulders, bedrock, stones, mud, sand, clay; vegetation of
green algae, water lilies, and water hyacinth; depths to 2.75 m, usually 1.5
m or less (Miller et al. 2005).
Biology
Spawning season: In
the San Marcos River, Texas, from March to August, with peak reproductive
activity in April (Buchanan 1971). Populations from northeastern Mexico
appear to spawn during late spring based on the condition of the gonads
(Darnell 1962; Birkhead 1980).
Spawning habitat:
Substrate brooders; rocks generally serve as spawning sites; breeding pairs
appear to prefer shallow water (Itzkowitz and Nyby 1982).
Spawning Behavior:
Pair-forming substrate brooders; monogamous. During the egg stage the male
and female alternate in the performance of major parental responsibilities.
Males spend more time patrolling and the female spend more time in close
proximity to and attending to the offspring. Pair formation occurs before
territory establishment. Established pairs will travel up to 3 m to harass
newly formed pairs (Itzkowitz and Nyby 1982). Fontaine (1938) observed
spawning in an aquarium, noting that the female would swim over the cleaned
nest, touching it with her vent (with breeding tube protruding ¼ - 3/8
inch); female expelled 1 – 5 eggs at a time; male followed female, spraying
seminal fluid through tube similar to the females, while hovering over the
eggs; process continued until 2500 – 3000 eggs had been laid and fertilized.
Fecundity: Unmolested
eggs hatched in 26 hours at temperature of 84 degrees F, in 30 hours at 80
degrees F, and in 60 hours at 75 degrees F (Fontaine 1938).
Age at maturation:
About 100 mm SL, after one year of growth (Buchanan 1971).
Migration:
Growth and Population
structure: Males typically larger than females (Itzkowitz and Nyby
1982).
Longevity:
Food habits:
Individuals from constant temperature headwaters of San Marcos River in
central Texas were almost exclusively herbivorous; those from Rio Grande
valley in south TX were omnivorous; speculation that dietary shifts may have
occurred in response to competition from ecologically equivalent
centrarchids (Buchanan 1971). The strong, cutting teeth make it chiefly
carnivorous, feeding mostly on fish eggs, insects, and small fishes (Tomerelli
and Eberle 1990). Darnell (1962) and Birkhead (1980) note that
populations from northeastern Mexico were found to be detritivorous.
Phylogeny and morphologically similar fishes
United States populations are
the northernmost representative of neotropical family Cichlidae (Birkhead
1980). Species varies greatly across range
in morphology and color pattern (Miller et al. 2005). Superficially
resembles the sunfishes but differs in several obvious respects as well as
in skeletal structure (Tomerelli and Eberle 1990). This cichlid can easily
be distinguished from all species of the genus Lepomis, which it resembles,
by the presence of blue or blue-green iridescent to whitish spots all over
the head and body, the presence of 1 nostril opening on each side of the
head and an interrupted lateral line (Itzkowitz and Nyby 1982).
Cichlasoma cyanoguttatum similar to the convict cichlid (C.
nigrofasciatum), but C. nigrofasciatum has 9-11 anal spines, and
7 intense black bars along side (Page and Burr 1991).
Host Records
Crassicutis sichlasomae,
Cesntrocestus formosanus, Clinosomum complanatum,
Diplostomum sp., Posthodiplostomum minimum, Bothriochephalus
acheilognathi, Neoechinorhynchus golvani, Rhabdochona kidderi,
Contracecum sp. (Salgado-Maldonado et al. 2004).
Commercial or Environmental Importance
This species is a
pollution-tolerant omnivorous species used by San Antonio River Authority
biologists as an indicator of an unbalanced or stressed ecosystem. Has been
observed to displace native Centrarchidae and dominate when aquatic
conditions are less than optimal (Gonzales and Moran 2005).
[Additional literature
noting collection of this species from Texas locations includes, but is not
limited to the following: lower Rio Grande River (Robinson 1959)Branson
(1961); Rio Grande River at Mission, TX (Kornfield and Koehn 1975); Hidalgo
Co. (Atkinson and Judd 1978); Edwards (1978); Devil’s River (Harrell 1978);
Upper San Marcos River (Underwood and Dronen 1984); lower Rio Grande River
(Edwards and Contreras-Balderas 1991); Pecos River (Rhodes and Hubbs 1992);
Pinto Creek (Edwards 2003; Garrett et al. 2004); Independence Creek (Rio
Grande drainage, Terrell Co.; Bonner et al. 2005).]
References
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