Lepomis cyanellus
green sunfish
Type Locality:
Ohio River (Rafinesque
1819).
Etymology/Derivation of Scientific Name
Lepomis, Greek,
meaning “scaled gill cover”; cyanellus, Greek, meaning “blue” (Pflieger
1975).
Synonymy
Lepomis cyanellus:
Rafinesque 1819:420; Forbes and Richardson 1908:248-250; Smith 1965:9
Telipomis cyanellus:
Nelson 1876:37
Apomotis
cyanellus: Jordan 1878:45; Large 1903:24;
O’Donnell 1935:486
Characters
Maximum size: Up to
250 mm TL (Lee 1980).
Life colors: Dark spot
at posterior base of dorsal fin; black spot on dorsal fin without a pale
margin (Hubbs et al 1991). Head olivaceous; cheeks randomly spotted and
streaked with bluish green; back olivaceous to brownish; sides greenish with
7-12 indistinct dark, vertical bars; opercle black with light margin;
abdomen whitish yellow. Dorsal, caudal, and anal fins with a yellowish white
border and a dark basal spot on second dorsal and anal; all fin membranes
dusky with randomly scattered light spots. Yellowish white border of dorsal,
caudal, and anal fins intensified in breeding male (Sublette et al. 1990).
Dominant fish are generally lighter colored (Howard 1974). Color mutation is
the Texas golden green sunfish, appearing golden in color (White 1971).
Counts: 35-55 scales
on complete lateral line; 3 anal spines; 6-13 dorsal fin spines; 6 or 7
branchiostegals (Hubbs et al 1991); 10-1 dorsal rays; 9-10 anal rays; 13-14
pectoral rays (Ross 2001).
Body shape: Strongly
compressed laterally (Sublette et al. 1990). Body depth usually contained
two to two and one-half times in standard length (Hubbs et al 1991).
Mouth
position: Terminal oblique. Palantine teeth are
present (Goldstein and Simon 1999), in older individuals (Sublette et al.
1990).
External morphology:
Gill rakers in adults long, when depressed reaching beyond base of second
raker below; supramaxilla two-thirds width of maxilla; opercle stiff to its
margin (not including membrane); posterior edge of opercle within opercular
membrane smooth; pectoral fins short and rounded; pectoral fin contained
3.75 or more times in standard length; lateral line present; scales ctenoid
(Hubbs et al 1991).
Internal morphology:
Intestine long and well differentiated; peritoneum white to silvery; pyloric
caeca present (Goldstein and Simon 1999).
Distribution (Native and Introduced)
U.S. distribution:
Restricted originally to east-central North America, west of the
Appalachians chain southward into Mexico; widely introduced elsewhere in
United States (Lee 1980).
Texas distribution:
Occurs throughout the state (Hubbs et al 1991). Warren et al. (2000) list
the following drainage units for distribution of Lepomis cyanellus 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.
Abundance/Conservation status (Federal, State, NGO)
Populations in the southern
United States are currently secure (Warren et al. 2000).
Habitat Associations
Macrohabitat:
Ecologically tolerant of many habitats, but does not normally occur in
brackish water (Lee 1980). Common in ponds and streams, lakes, and in areas
of river with little flow (Sublette 1990; Ross 2001).
Mesohabitat: Preferred
sites have low velocity within the temperature range of 26-31 degrees C
(Stuber et al. 1982). Laboratory studies indicate a preferred temperature of
28.2 degrees C (Beitenger et al. 1975). Species will tolerate alkalinities
up to 2,000 mg/1. In California area, abundant in small intermittent streams
at lower elevations, especially in warm, turbid, muddy-bottomed pools with
large amounts of vegetation and with Micropterus salmoides and
Gambusia affinis (Carlander1977). Collected from Sister Grove Creek, an
intermittent prairie stream in N-central Texas (Meador and Matthews 1992).
Lepomis cyanellus common in many of the clearer
tributaries of Lake Texoma (Oklahoma and Texas; Riggs and Bonn 1959).
Captured in both the saline and freshwater reaches of the Pecos River,
Texas, but highest capture rate was in freshwater reach (Rhodes and Hubbs
1992). Baughman (1946) collected L. cyanellus from residual pools of
a recently drained rice canal near Barbour’s Hill (Chambers Co.), Texas.
Biology
Spawning Season:
Begins in spring and continues until late summer in water temperatures
between 15-31 degrees C (Hubbs and Cooper 1935; Tin 1982; Stuber et al.
1982).
Spawning Location:
Nest spawners. Polyphils; miscellaneous substrate and material
nesters that have adhesive eggs either attached or occur in clusters on any
available substrate (Simon 1999). Eggs are laid in nests scooped out of
gravel or sandy silt by the male in depths of 4-355 cm (Stuber et al. 1982).
Nests built in large colonies in less than 40 cm water, on gravel with
maximum sunshine (Carlander 1977). Nests seldom located in water deeper than
35 cm; small males may construct nests in water as shallow as 4 cm; nests
built in rocks, logs, clumps of grass, or occasionally abandoned sunfish
nests (Hunter 1963).
Reproductive Strategy:
Males fan out a depression in shallow water. Males actively court females by
rushing out toward them, and then returning rapidly to the nest. Gruntlike
sounds produced by nesting males to attract females (Gerald 1971, Ross
2001). Guarders (Simon 1999); nests are defended by male until larvae emerge
(Sublette et al. 1990).
Fecundity: Fertilized
eggs are demersal, adhesive, and range from 1.0-1.4 mm in diameter. Larvae
hatch at about 4.2 mm TL (Meyer 1970; Taubert 1977).
Age at maturation:
Occurs at age one in Missouri, Illinois, Iowa, but not until age three in
Michigan; mature males reported as 76 mm and 45 mm and females at 66 mm and
6 – 10 g (Carlander 1977). Texas golden green sunfish reaches sexual
maturity in less than 6 months (White 1971).
Migration:
Longevity: In Bull
Shoals Reservoir (Arkansas and Missouri) no fish lived to the end of their 6th
year (Applegate et al. 1967). 7.5 years in captivity (Carlander 1977).
Growth and Population
Structure: In Bull Shoals Reservoir (Arkansas and Missouri)
Lepomis cyanellus reached 45.7 mm TL after one year and 71.1 mm, 91.4
mm, 109.2 mm, and 121.9 mm TL for years 2-5, respectively (Applegate et al.
1967). Males generally larger than females (Hubbs and Cooper 1935). A study
showed most older fish were males (Carlander 1977). Lepomis cyanellus
have a well-developed social system with dominant and subordinate
individuals. Dominant fish are generally lighter colored and are usually the
largest individuals (Howard 1974).
Food habits: Trophic
classifications: Invertivore/carnivore; drift/whole body feeder. Trophic
mode: water column/ambush. Main foods are insects, mollusks, and small
fishes (Goldstein and Simon 1999). Species has larger mouth than most other
sunfish of same size and eats larger food items. Young feed on zooplankton.
Adults feed on insects, crayfish, terrestrial arthropods, Micropterus
salmoides eggs and fry, other fishes including Gambusia affinis (Carlander
1977); aquatic and terrestrial insects appear to be most important food item
(Stuber et al. 1982). In Bull Shoals Reservoir (Arkansas and Missouri) fish
smaller than 48 mm TL feed primarily on aquatic insects and small
crustaceans (copepods and cladocerans); from 51-76 mm TL, major prey include
large aquatic insects such as mayfly larvae; fish longer than 102 mm TL feed
heavily on large crustaceans such as crayfishes (Applegate et al. 1967);
Applegate (1966) noted L. cyanellus feeding on bryozoans (Fredericella
sultana). In streams where L. cyanellus is not native, species
has been implicated in causing the disappearance of several native minnows (Lemly
1985).
Phylogeny and morphologically similar fishes
Lepomis cyanellus
possibly most primitive species of typical Lepomis. It is similar to
L. gulosus (warmouth; Branson and Moore 1962;
Lee 1980), but may be separated from this species, L. megalotis
(longear sunfish), and L. macrochirus (bluegill) by a large mouth;
short, rounded pectoral fins; anal fins with three spines; and the tongue
(except in older individuals) and pterygoids without teeth (Sublette et al.
1991). Known to hybridize with at least five other Lepomis (Lee
1980), including L. macrochirus (bluegill; Childers and Bennett
1961), L. megalotis (longear sunfish), L. humilis (orangespotted
sunfish), L. auritis (redbreast sunfish), and L. microlophus (redear
sunfish; Childers 1967).
Host Records
Gyrodactylus macrochiri
host (Hoffman and Putz 1964; Harris et al 2004). Cestoda: Bothriocephalus
claviceps, Proteocephalus amblopliti; Trematoda: Actinocleidus
fergusoni, Actinocleidus flagellatus, Actinocleidus fusiformes,
Actinocleidus gracilis, Actinocleidus longus, Actinocleidus maculatus,
Bucephalus elegans, Caecincola parvulus, Cercaria flexicorpa, Cleidodiscus,
Cleidodiscus bedardi, Cleidodiscus diversis, Cleidodiscus globus,
Cleidodiscus robustus, Cleidodiscus similis, Crepidostomum
cooperi, Haplocleidus dispar, Haplocleidus furcatus,
Oncocleidus cyanellus, Pisciamphistoma reynoldsi,
Pisciamphistoma stunkardi, Posthodiplostomum minimum,
Posthodiplostomum minimum centrarchi, Urocleidus attenuatus,
Urocleidus chaenobryttus, Urocleidus cyanellus, Urocleidus
dispar, Urocleidus ferox, Urocleidus grandis,
Urocleidus principalis; Nemata: Camallanus oxycephalus,
Camallanus trispinosus, Capillaria, Contracaecum,
Contracaecum spiculigerum, Spinitectus carolini, Spinitectus
gracilis, Spinitectus micracanthus, Spiroxys contorta;
Acanthocephala: Eocollis arcanus, Leptorhynchoides thecatus,
Neoechinorhynchusconstrictus, Neoechinorhynchus clyindratum
(Allison 1967 ; McGraw and Allison 1967 ; Meade and Bedinger
1972 ; Underwood and Dronen 1984 ; Mayberry et al. 2000).
Commercial or Environmental
Importance
White (1971) notes the golden
color of Texas golden green sunfish may make it particularly susceptible to
predation and a good forage fish. Lepomis cyanellus found to be major
food source for Micropterus salmoides (largemouth bass) in a desert
impoundment (Biggins 1968). Usually
individuals do not become large enough to interest anglers. Species is
easily handled and make good bioassay animals (Carlander 1977).
[Additional literature
noting collection of this species from Texas locations includes, but is not
limited to the following: Brazos County (Bonham 1946); lower Rio Grande
River (Robinson 1959); Horkel and Pearson (1976); Colorado River System
(Echelle et al 1977); Devils River (Harrell 1978); Hillebrandt Bayou (Linam
and Kleinsasser 1987); Oyster Creek (Linam and Kleinsasser 1987); lower Rio
Grande River (Edwards and Contreras-Balderas 1991); Matthews et al. (1996);
Bosque, Leon, and Lampasas River watersheds (Middle Brazos River Basin;
Armstrong 1998).]
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