Alligator gar Atractosteus spatula is the largest freshwater fish in Texas and one of the
largest species in North America, yet has received little attention from anglers or fisheries
managers. Although gars (family Lepisosteidae) have long been considered a threat to sport
fishes in the United States (summarized by Scarnecchia 1992), attitudes are changing.
Recreational fisheries for alligator gar are increasing, and anglers from around the world now
travel to Texas for the opportunity to catch a trophy. Because little data exist, it is unknown how
current exploitation is affecting size structure and abundance of alligator gar in Texas. In many
areas, alligator gar populations are declining (Robinson and Buchanan 1988; Etnier and Starnes
1993; Pflieger 1997; Ferrara 2001). Concerns by biologists and anglers about alligator gar
populations in Texas have led the Texas Parks and Wildlife Department (TPWD) to consider
management options for this species. In addition to this review, the TPWD has recently initiated
several studies to learn more about Texas alligator gar populations. The purposes of this
document are to 1) summarize alligator gar life history and ecology, 2) assess alligator gar status
and management activities throughout their range, and 3) make recommendations for future
alligator gar management in Texas.
Life History
In the United States, alligator gar spawn from April through June (Etnier and Starnes
1993; Ferrara 2001), coinciding with seasonal flooding of bottomland swamps (Suttkus 1963).
Documented reports of alligator gar spawning are limited, though it is thought to occur in
flooded backwater areas (Mendoza Alfaro et al. 2008). Spawning was recently observed in a
shallow, vegetated-backwater area of Lake Texoma, Oklahoma. Snedden et al. (1999) found that
lateral spawning migrations of spotted gar Lepisosteus oculatus onto floodplain areas were
correlated with increased river stage and increased temperature. Because spawning is likely
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linked to seasonal flooding, successful recruitment may be infrequent. Fecundity of alligator gar
is highly variable, with means of 157,000 eggs per female and 4.1 eggs/g body weight (Ferrara
2001).
Juvenile alligator gar likely remain in backwater spawning areas as they develop. Sakaris
et al. (2003) reported that tagged juvenile alligator gar demonstrated strong site fidelity to
protected backwater areas and remained near their site of capture (thought to be a spawning
area), whereas adults were more mobile. Robertson et al. (2008) also captured juvenile alligator
gar from backwater oxbow habitats, whereas adults were collected in the river channel. Ferrara
(2001) hypothesized that juvenile alligator gar utilize shallow embayments and tributaries, and
suggested that identification and protection of such nursery areas may be critical to the recovery
of alligator gar populations in areas with limited nursery habitats.



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