Scientific Name:  Alligator mississippiensis
Classification:   State Threatened and Federally Threatened due to Similarity of Appearance
Abundance:  Common in some coastal areas of the state

Species Profile (PDF)
Coexisting with Alligators (PDF)


General Description

The American alligator resembles a large lizard, but reaches a much larger size, has a thicker body and tail, and is strongly associated with wetlands. Adults range in color from black or dark gray to dark olive. Juveniles are born with bright yellow bands that encircle their bodies. These bands gradually fade over time.

Alligators can live 40 or more years in the wild (Wilkinson et al. 2016), but captive animals have been documented to live more than 70 years (Weigl 2014). Upper size limits for males, which grow larger than females, are typically 13-14 feet (396 - 427 cm) in length, while females reach 9-10 feet (274 – 305 cm) (Woodward et al. 1995; Brunell et al. 2013; Brunell et al. 2015). Adult males can reach weights more than 500 pounds (227 kg), while females do not usually exceed 200 pounds (91 kg). Per Palmer and Braswell (1995), the largest male alligator ever examined in North Carolina was 12.5 feet long (382 cm total length) and weighed 475 pounds (215.5 kg), while the largest female was just over 8 feet (246 cm total length, weight unknown). External sexual characters are minimal for the alligator, but mature males do develop a swollen area under the tail around the vent during the breeding season.



There are currently 24 described species of crocodilians in the world (IUCNCSG 2017). The genus Alligator includes the only two extant species that can endure temperate climates, the American Alligator (Alligator mississippiensis) and the Chinese Alligator (Alligator sinensis). A. mississippiensis (see Table 1) has existed in North America for at least 7 million years (Whiting 2016). Fossils of prehistoric crocodilians and their ancestors dating back to 231 MYA have been discovered in North Carolina, which contains the northernmost portion of the American alligator’s present-day range.















Table 1. Taxonomy of Alligators.


Prehistoric Presence of Crocodilians and Their Ancestors in North Carolina

Following the Permian-Triassic extinction event that took place approximately 252 million years ago (MYA), a newly evolved group of animals referred to as archosaurs became the dominant land vertebrates. Modern crocodilians and their extinct relatives belong to a group of archosaurs known as crocodylomorphs. Carnufex carolinensis, one of the oldest and earliest diverging crocodylomorphs described to date, was discovered in 2003 from the Carnian Pekin Formation (~231 MYA) in Chatham County, North Carolina (Zanno et al. 2015). While small-bodied crocodylomorphs had previously been unearthed by paleontologists from late Triassic excavations (Drymala and Zanno 2016, Sues et al. 2003), Carnufex was much more formidable at 3 meters long and boasting a skull length of 50 cm. This find reveals that crocodylomorphs filled top predator roles in the equatorial regions of Pangea prior to the global dominance of dinosaurs in the early Jurassic period.

Descendants of the crocodylomorphs that had survived the Triassic-Jurassic extinction event, alligatoroids were the first group of crocodilians to evolve by the Campanian period of the late Cretaceous epoch (~72-83 MYA). Fossils of Deinosuchus rugosus, one of the earliest-known alligatoroids, were uncovered at Phoebus Landing and the Black Creek Formation site in Bladen and Sampson counties of North Carolina around the time of the Civil War (Schwimmer 2002). Considerably larger than any living crocodilians, D. rugosus would have typically measured 8 meters long and weighed in at approximately 2.3 tons.


Life History and Ecology


Sexual maturity in alligators is directly related to body size. Both genders tend to be capable of reproduction at 6 feet (183 cm) in length. Males in North Carolina are thought to take 14-16 years to reach sexual maturity, while females require 18-19 years (Doerr and Hair 1983); this is longer than the amount of time required for alligators from more southern locales. For example, in South Carolina, researchers have estimated that male alligators reach sexual maturity at about 11.6 years of age, while females require approximately 15.8 years (Wilkinson et al. 2016; see Table 2). Due to slower growth rates, juvenile alligators in North Carolina require more time to outgrow a vulnerability to predation (Doerr and Hair 1983). Immature alligators are much less susceptible to predators upon reaching 3 feet (91 cm) in length.


Reported Length of Time (in Years) Required for American Alligators to Reach Sexual Maturity




# of Alligators



6 - 10

8 - 13


Rootes et al. (1991)


8.9 – 12.4


Fujisaki et al. (2007)




Saalfeld et al. (2008)

South Carolina




Wilkinson et al. (2016)

North Carolina

14 - 16

18 - 19


Doerr and Hair (1983)

Table 2. Reported Length of Time (in Years) Required for American Alligators to Reach Sexual Maturity


Alligators typically mate from mid-May to early-July in North Carolina (Klause 1984), after which females construct mound nests of vegetation and mud on the shore. They lay an average of 35 eggs, then cover them with additional vegetation to properly incubate for 9-12 weeks until hatching. The sex of young alligators is not determined at conception; rather, it is determined by nest temperatures during the thermosensitive period (TSP) of incubation. Lang and Andrews (1994) reported that the TSP occurs from stages 21 to 24 of embryonic development (in the middle third of the incubation period), during which nests with high or low temperatures produce females, while males are predominantly produced at intermediate temperatures (approximately 32-34°C or 90-93°F). Findings from a more recent study have expanded our understanding of this mechanism and demonstrated that the TSP begins by stage 15, and potentially earlier (McCoy et al. 2015).

After 60-80 days of incubation, the young hatch out at about 9 inches (23 cm) long. While hatching they instinctively call out to attract the mother, who scratches open the nest mound and carries the hatchlings in her mouth to the edge of the water (Hunt 1987). Females have also been observed gently picking up eggs and rolling them in their mouth to aid in the hatching process (Kushlan and Simon 1981). Unlike most reptiles, female alligators protect their offspring from predators throughout incubation and into their early years of life. Juveniles generally congregate together in pods for the first few years, during which the mother will respond to distress calls made by the young when threatened (Hunt and Watanabe 1982, Kushlan 1973).



During their first years of life, alligators eat primarily snails, frogs, crayfish, insects, and other small invertebrates. Larger alligators may eat smaller alligators, turtles, snakes, fish, waterbirds, beavers, raccoons, and otters. Given the opportunity, alligators can prey upon dogs, cats, and other small domestic animals, such as goats and pigs. Alligators in North Carolina grow more slowly than alligators to the south because our water temperatures do not stimulate feeding for as long a period each year.

Alligators create small wetlands using their snouts, feet, and tail to excavate “gator holes” the size of small backyard pools. Because these holes provide critical pockets of aquatic habitat to many other species during periods of drought, the alligator is considered a keystone species within the coastal communities they inhabit (Palmer and Mazzotti 2004).

A mutualistic relationship between alligators and long-legged wading birds has been documented by researchers (Nell et al. 2016). Large colonies of these birds choose to nest high up in trees near alligators because the presence of alligators is a strong deterrent for mammalian nest predators, such as raccoons and opossums. In return for their protection, the resident alligators have an opportunity to scavenge nestlings that fall from the nests, which can be a substantial food source for alligators. Because the birds forage in other locations, this relationship also facilitates the transfer of nutrients from other ecosystems to these wetlands (Nell and Frederick 2015).

As an apex predator, alligators play an important role in ecosystems by regulating mesopredator populations. In salt marsh food webs, for example, predation on blue crabs by alligators results in the increased survival of a keystone marsh grazer (the Periwinkle snail, Littoraria irrorata) and a Spartina cordgrass-facilitating mutualist (the Atlantic ribbed mussel, Geukensia demissa) (Nifong and Silliman 2013).



Alligators usually remain in the same area where they were hatched for two to three years before establishing their own territories. Hagan (1982) reported that annual home ranges of alligators at Lake Ellis-Simon (Craven County, NC) ranged from 7.4 acres (3.0 ha) to 3,555 acres (1,439 ha) and that male home ranges were significantly larger than those of females.

Although adult alligators are usually solitary, they are known to congregate during the breeding season. Both males and females vocalize. The male calls with a loud, throaty bellow and may hiss and inflate to impress a mate. Females bellow and grunt, too, but less loudly.



Genetic studies of alligators in Louisiana, Alabama, South Carolina, and Florida have revealed geographic patterns of genetic variation and population differentiation (Glenn et al., 1998; Davis et al., 2000). The results of a study in Texas indicated limited levels of gene flow between and among both coastal and inland populations of alligators (Ryberg et al. 2002). These findings suggest that alligators in North Carolina could exhibit genetic differentiation between geographically isolated metapopulations.


Distribution and Population Status

American Alligator Distribution

The range of the alligator includes areas from the southern tip of Texas through the northern coastal areas of North Carolina.






















Alligator Distribution and Abundance in North Carolina

In North Carolina, the alligator occurs just north of Albemarle Sound, south along the eastern Coastal Plain, and west as far as Robeson County (Palmer and Braswell 1995; Gardner et al. 2016). The aquatic habitats that alligators occupy vary widely across their range in North Carolina and from season to season. Alligators tend to prefer fresh to brackish waters, although they can tolerate higher levels of salinity for short periods of time. They inhabit swamps, creeks, rivers, tidal marshes, canals, ponds, lakes, and reservoirs.

A recent study of alligators in North Carolina (Gardner et al. 2016) showed that alligator populations are likely stable or slightly increasing and their current distribution appears to be relatively consistent with the results of a study conducted 30 years ago (O’Brien and Doerr 1986). Although these results did not indicate a population decline, the researchers noted that alligators occur in patchy distributions and very low densities across much of their North Carolina range. Alligators were more abundant closer to the coastline, further south, and in locations that limit access by people and provide more protection for alligators.


Historic and Ongoing Conservation Efforts

Chiefly driven by the commercial market for alligator skin products, alligator populations were greatly diminished by the mid-twentieth century because of unregulated harvest throughout their range. Under the 1966 Endangered Species Preservation Act, the very first list of endangered species compiled in 1967 (32 FR 4001) included the American Alligator. This act authorized the use of federal funds for the acquisition of lands inhabited by listed species, but take (“to harass, harm, pursue, hunt, shoot, wound, kill, trap, capture, or collect, or to attempt to engage in any such conduct”) of these species was not prohibited by federal law until Congress passed the Endangered Species Act of 1973. In 1969, Congress amended The Lacey Act to include reptiles, perhaps the most important legislation related to the recovery of American Alligator. The Lacey Act prohibits interstate commerce of illegally obtained wildlife. In 1973, governments of 80 countries signed a treaty—the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES). The international export of alligator skins was banned by CITES in 1975. Owing to these and state-level protections, alligator populations rebounded rapidly in many parts of their range. This recovery prompted the U.S. Fish and Wildlife Service to reclassify alligators range-wide in 1987 (52 FR 21059) as Threatened Due to Similarity of Appearance to the American Crocodile (Crocodylus acutus), which was federally listed as Endangered in 1979 (44 FR 75074) and down-listed to Threatened in 2007 (72 FR 13027). Under this classification, the U.S. Fish and Wildlife Service continues to regulate interstate trade of alligators today. Illegal trade of alligators or alligator parts is generally thought to seldom occur.

With the rare exception of individuals taken by WRC employees or permitted Wildlife Damage Control Agents (e.g., if an alligator poses a threat to public safety), there was no legal harvest of alligators in North Carolina prior to the first regulated hunting season in 2018. Although relatively uncommon, relocation of alligators occurs far more often than euthanization when “problem” alligators are found in locations that could be a safety hazard to humans or their pets. In many cases, private citizens are provided with information about alligators and encouraged to allow the alligator to move on its own, which typically occurs within a few hours to a couple of weeks.

Alligators are usually quite shy and secretive in nature. If fed by people, they can lose their natural fear of humans and learn to associate people with an easy meal. In 2007, the North Carolina General Assembly passed a law, GS § 113 291.11, that prohibits the feeding of alligators. The NC Wildlife Resource Commission has published a document titled Coexist with Alligators that highlights how important it is for people to refrain from feeding alligators.


Literature Cited

Brunell, Arnold M., J. Patrick Delaney, Richard G. Spratt, Dwayne A. Carbonneau, and Jason E. Waller. 2013. Record total lengths of the American alligator in Florida. Notes of the Southeastern Naturalist 12(4): N9-N17.

Brunell, Arnold M., Thomas R. Rainwater, Michael Sievering, and Steven G. Platt. 2015. A new record for the maximum length of the American alligator. Notes of the Southeastern Naturalist 14(3): N38-N43.

Davis, L.M., T.C. Glenn, R.M. Elsey, I.L. Brisbin, Jr., W.E. Rhodes, H.C. Dessauer, and R.H. Sawyer. 2000. Genetic structure of six populations of American alligators: a microsatellite analysis. Crocodilian Biology and Evolution: 38-50.

Doerr, P. D., J. D. Hair, P. C. Smithson, M. K. Fuller, J. M. Hagan III, T. G. O’Brien, and S. E. Klause. 1983. Status of the American alligator in North Carolina. Report issued to the North Carolina Wildlife Resources Commission by North Carolina State University, Raleigh, NC. 599 pages.

Drymala, Susan M. and Lindsay E. Zanno. 2016. Osteology of Carnufex carolinensis (Archosauria: Psuedosuchia) from the Pekin Formation of North Carolina and Its Implications for Early Crocodylomorph Evolution. PLoS One 11(6): e0157528. doi:10.1371/journal.pone.0157528.

Fujisaki, Ikuko, Kenneth G. Rice, Allan R. Woodward, and H. Franklin Percival. 2007. Possible generational effects of habitat degradation on alligator reproduction. The Journal of Wildlife Management 71(7): 2284-2289.

Gardner, Beth, Lindsey A. Garner, David T. Cobb, and Christopher E. Moorman. 2016. Factors affecting occupancy and abundance of American alligators at the northern extent of their range. Journal of Herpetology, 50(4):541-547.

Glenn, Travis C., Herbert C. Dessauer, and Michael J. Braun. 1998. Characterization of Microsatellite DNA Loci in American Alligators. Copeia 3: 591-601.

Hagan, John M., III. 1982. Movement habits of the American alligator (Alligator mississippiensis) in North Carolina. Thesis, NCSU, Raleigh, USA.

Hunt, R. Howard and Myrna E. Watanabe. 1982. Observations on maternal behavior of the American alligator, Alligator mississippiensis. Journal of Herpetology 16(3): 235-239.

Hunt, R. Howard. 1987. Nest excavation and neonate transport in wild Alligator mississippiensis. Journal of Herpetology 21(4): 348-350.

International Union for the Conservation of Nature Crocodile Specialist Group [IUCNCSG]. 2017. IUCNCSG Crocodilian Species page. <>. Accessed 24 Mar 2017.

Klause, Stephen E. 1984. Reproductive characteristics of the American alligator (Alligator mississippiensis) in North Carolina. Thesis, NCSU, Raleigh, USA.

Kushlan, James A. 1973. Observations on maternal behavior in the American alligator, Alligator mississippiensis. Herpetologica 29(3): 256-257.

Kushlan, James A., and Jeffrey C. Simon. 1981. Egg manipulation by the American alligator. Journal of Herpetology 15(4): 451-454.

Lang, Jeffrey W. and Harry V. Andrews. 1994. Temperature-dependent sex determination in crocodilians. Journal of Experimental Zoology 270: 28-44.

McCoy, Jessica A., Benjamin B. Parrott, Thomas R. Rainwater, Phillip M. Wilkinson, and Louis J. Guillette, Jr. 2015. Incubation history prior to the canonical thermosensitive period determines sex in the American alligator. Reproduction 150(4): 279-287.

Nell, Lucas A. and Peter C. Frederick. 2015. Fallen nestlings and regurgitant as mechanisms of nutrient transfer from nesting wading birds to crocodilians. Wetlands 35: 723-732.

Nell, Lucas A., Peter C. Frederick, Frank J. Mazzotti, Kent A. Vliet, and Laura A. Brandt. 2016. Presence of breeding birds improves body condition for a crocodilian nest protector. PLoS ONE 11(3): e0149572.

Nifong, James C. and Brian R. Silliman. 2013. Impacts of a large-bodied, apex predator (Alligator mississippiensis Daudin 1801) on salt marsh food webs. Journal of Experimental Marine Biology and Ecology 440: 185-191.

O'Brien, Timothy G. and Phillip D. Doerr. 1986. Night count surveys for alligators in coastal counties of North Carolina. Journal of Herpetology 20: 444-448.

Palmer, William M., and Alvin L. Braswell. 1995. The Reptiles of North Carolina. Chapel Hill: University of North Carolina Press.

Palmer, Michelle L. and Frank J. Mazzotti. 2004. Structure of Everglades alligator holes. Wetlands 24(1): 115-122.

Rootes, William L., Robert H. Chabreck, Vernon L. Wright, Bobby W. Brown, and Thomas J. Hess. 1991. Growth rates of American alligators in estuarine and palustrine wetlands in Louisiana. Estuaries 14(4): 489-494.

Ryberg, Wade A., Lee A. Fitzgerald, Rodney L. Honeycutt, and James C. Cathey. 2002. Genetic Relationships of American Alligator Populations Distributed Across Different Ecological and Geographic Scales. Journal of Experimental Zoology 294(4): 325-33.

Saalfeld, David T., Kevin K. Webb, Warren C. Conway, Gary E. Calkins, and Jeffrey P. Duguay. 2008. Growth and condition of American alligators (Alligator mississippiensis) in an inland wetland of east Texas. Southeastern Naturalist 7(3): 541-550.

Schwimmer, David R. 2002. King of the Crocodylians: The Paleobiology of Deinosuchus. Indiana University Press, USA.

Sues, Hans-Dieter, Paul E. Olsen, Joseph G. Carter, and Diane M. Scott. 2003. A new crocodylomorph archosaur from the Upper Triassic of North Carolina. Journal of Vertebrate Paleontology 23(2): 329-343.

Weigl, Richard. 2014. Longevity of crocodilians in captivity. International Zoo News 61(5): 363-373.

Wilkinson, Philip M., Thomas R. Rainwater, Allan R. Woodward, Erin H. Leone, and Cameron Carter. 2016. Determinate growth and reproductive lifespan in the American alligator (Alligator mississippiensis): Evidence from long-term recaptures. Copeia 104(4): 843-852.

Whiting, Evan T., David W. Steadman, and Kent A. Vliet. 2016. Cranial polymorphism and systematics of Miocene and living Alligator in North America. Journal of Herpetology 50(2): 306-315.

Woodward, Allan R., John H. White, and Stephen B. Linda. 1995. Maximum size of the alligator (Alligator mississippiensis). Journal of Herpetology 29(4): 507-513.

Zanno, Lindsay E., Susan Drymala, Sterling J. Nesbitt, and Vincent P. Schneider. 2015. Early crocodylomorph increases top-tier predator diversity during rise of dinosaurs. Scientific Reports 5(9276). DOI: 10.1038/srep09276.

At its February 2018 meeting, the North Carolina Wildlife Resources Commission (NCWRC) adopted a rule to allow limited take of American alligators (H6) as prescribed by the North Carolina Alligator Management Plan (Plan). In accordance with the Plan, hunting for American alligators will initially be limited to population reduction hunts at the request of cities, towns, and villages within Alligator Management Unit 1 (Brunswick, Carteret, Columbus, Craven, Hyde, Jones, New Hanover, Onslow, Pamlico, and Pender counties). A municipality requesting a population reduction hunt will work with Commission staff to assess alligator numbers, define areas of public safety concern, and identify those areas where alligator take could be conducted by hunters.

The Commission does not plan to issue permits to take American alligators, outside of municipality requested population reduction hunts, until further research is conducted to determine the conditions under which alligator populations would be sustained while allowing limited harvest.

In addition to publication on NCWRC’s website, any opportunities that become available for hunters to apply for alligator hunting permits will be announced through NCWRC news releases and Wildlife Update emails.


Municipalities can find information about requesting a population reduction hunt under the Management tab.


If you know of someone poaching, harming, harassing, or intentionally feeding alligators in North Carolina, please call our Wildlife Enforcement hotline at 1-800-662-7137.

At its October 2017 meeting, the N.C. Wildlife Resources Commission adopted a plan to guide alligator management in North Carolina. The N.C. Alligator Management Plan was developed by the N.C. Alligator Task Force, as established by resolution of the Commission.

Download the NC Alligator Management Plan (PDF


Download Addendum 1 (PDF)


Resources for Municipalities

Alligator Management Options for Municipalities (PDF)

Municipality Application for Alligator Population Reduction Hunt (PDF)

For more information about alligator management options for municipalities, including population reduction hunts, please call (919) 707-4087 or email

American alligators occur naturally in North Carolina, inhabiting bay lakes, rivers, creeks, marshes, swamps and ponds, with local populations distributed in patches along the entire coast. Alligators become less common in coastal NC as you move from south to north. Climate, specifically the number of cold weather days, limits their “growing season” and their ability to survive and reproduce. Coastal NC is considered the northern extent of their range, and alligators in NC have much slower growth rates, reproduce less frequently, and populations are more vulnerable to local extinctions than other more southern states. It is unlawful for the public to kill, harm or harass an alligator in NC.


Preventing Conflicts with Alligators 

Although seeing an alligator for the first time may be scary, North Carolina alligators rarely pose a threat to humans. If an alligator is seen on private or public property it is not immediate cause for alarm.

Follow these common-sense tips and in the majority of cases, these native reptiles will remain shy and secretive and move on.


Common Sense Safety Tips

  • Do not intentionally feed an alligator no matter what its size.
  • Do not throw food into waters where alligators may be found.
  • Fishermen should dispose of fish scraps in garbage cans, and not throw them into the water.
  • Do not feed ducks, geese, other waterfowl or fish in areas where alligators have been seen.
  • Follow local leash laws or otherwise keep pets on a leash in areas where alligators could potentially occur.
  • Never leave children unattended near any body of water.
  • Don’t allow pets to swim, exercise or drink in or near waters that may contain alligators.
  • Be particularly cautious between dusk and dawn when alligators are most active.
  • Do not harass or provoke any alligator.
  • Children and adults should never approach an alligator or any other large wild animal
  • If the alligator is in a residence or place of business, or interrupting traffic on a public road, call WRC at 800-662-7137.


Long-term Exclusion and Environment Options

  • Install a fence with a minimum height of 4.5 feet around retention ponds, lakes, or other bodies of water that might attract alligators
  • Install bulkhead along edges of lakes and waterways 
  • Add grates to culvert pipes 
  • Fence causeways between ponds 
  • Minimize vegetation growing in water or near the water’s edge


How to Help Your Neighbors Become Alligator Aware

  • Hang alligator flyers

Coexisting with Alligators

  • Erect Do Not Feed Alligator signs near water access points
  • Share information with your neighbors
  • Host an alligator workshop
  • Take part in neighborhood message boards


For technical assistance with exclusion or habitat modification call 866-318-2401 or 919-707-4011.

Alligator hunting or otherwise killing an alligator is prohibited in North Carolina. Only authorized wildlife biologists and wildlife officers can remove problem alligators.