In the 1930s, Louisiana’s coastal marshlands began a slow collapse. The cause was traced to a semi-aquatic rodent imported from South America, which multiplied rapidly and fed on the root systems that held the wetlands together. Over time, the state lost significant portions of its coastline to erosion. The eventual solution involved a species that had been hunted nearly to extinction: the American alligator. Through a program that combined regulated commercial hunting with captive breeding, the state turned the predator into a managed resource that helped stabilize the marsh and brought the rodent population under control.
The animal at the center of the problem was the nutria. It weighs up to 16 pounds, has webbed hind feet, and distinctive orange incisors. It was brought to Louisiana by Edward Avery McIlhenny, known as Monsieur Ned, an heir to the Tabasco pepper sauce fortune. McIlhenny was a conservationist who had worked to protect snowy egrets on his Avery Island estate, but he also saw commercial potential in nutria fur. Despite warnings from the Federal Bureau of Biological Survey about the risks of introducing the species, he imported the rodents, bred them, and released them into the wild. A later account suggested they escaped during a hurricane, but McIlhenny’s business records indicate the release was deliberate.

The nutria’s impact was severe. They reach sexual maturity at six months and breed year-round, with females producing several litters annually. More importantly, their feeding habits were destructive. Unlike native muskrats, which graze on the tops of marsh plants, nutria dig down and consume the root mats that hold wetland soil together. When these roots are destroyed, the soil disintegrates, tides wash it away, and salt water moves in. The process, known as an eat-out, converts vegetated marsh into open water. By the late 1950s, Louisiana was losing between 25 and 35 square miles of coastline each year.
During that same period, the American alligator, the one native predator capable of controlling the nutria, was nearing extinction. Decades of unregulated leather poaching had reduced its population to below 100,000. The marsh had lost both its structural anchor and its natural enforcer at the same time.
For a time, the international fur trade provided some relief. Trappers harvested more than a million nutria annually during the 1960s and 1970s, keeping the population in check. But when the fur market collapsed in the 1980s, the annual harvest fell from 1.2 million to fewer than 30,000. The nutria population rebounded, and more than 100,000 acres of marsh were stripped of vegetation.
In 1962, the Louisiana Department of Wildlife and Fisheries closed all alligator hunting in the state. The moratorium was led by Ted Joanen and Larry McNease, two field biologists at the Rockefeller Wildlife Refuge in Grand Chenier. They spent years studying alligator behavior in the marsh, capturing animals and tracking their movements with radio collars. Their research showed that female alligators retreat into interior marshes to nest in late summer, while males and juveniles stay in open canals and deeper water. This natural segregation suggested that a carefully timed hunting season, restricted to September and limited to accessible waterways, could target primarily males while leaving breeding females undisturbed.
In 1972, they tested the approach. A 13-day experimental season in Cameron Parish issued 6,100 tags. Of the animals harvested, 80.29 percent were male. The breeding population was left largely intact.
The second major step came in 1986 with an egg ranching program. In the wild, about 83 percent of alligator hatchlings die before reaching four feet, due to predation, flooding, and cannibalism. Joanen and McNease proposed collecting viable eggs from wild nests, incubating them in controlled facilities, and raising the hatchlings in captivity. Under these conditions, the alligators grew faster and survived at higher rates. Research by Joanen and Mark Ferguson found that incubation temperature determines the sex of hatchlings, giving farmers control over their stock.
The program came with a condition: farmers had to return a percentage of healthy juveniles to the marsh where the eggs were collected, initially 17 percent and later 12 percent as wild populations recovered. Every returned animal was measured, sexed, tail-notched, and tagged. No juvenile entered the wild without being tracked.
The economic incentive proved important. Landowners had previously viewed alligators as pests and sometimes allowed poachers to remove them. But once alligators became a valuable commodity through legal skin and meat sales, landowners had a financial reason to protect both the animals and the wetland habitat they required. The same market that had nearly driven the alligator to extinction was now funding its recovery.
The American alligator was removed from the endangered species list in 1987, roughly 25 years after the moratorium began. As alligator populations grew, their effect on the nutria became apparent. Adults over five feet in length shifted their diet to mammalian prey. Stomach content analyses showed that nutria made up as much as 60 percent of the total dietary weight of large alligators. The predation was density dependent: the more nutria, the more heavily they were targeted. This created a self-sustaining biological control system that required no human labor or funding.
The state also launched a nutria control program in 2002, paying a $6 bounty per tail. Annual nutria removal reached 400,000 per season. Documented marsh damage dropped from 100,000 denuded acres to roughly 16,000 by 2018.
Alligators also contributed to the landscape in other ways. Using their snouts, claws, and tails, they excavate depressions in the marsh substrate, sometimes down to limestone bedrock. These ponds, known as alligator holes, retain water during dry seasons and serve as habitat for fish, amphibians, turtles, and wading birds. The alligators maintain the holes continuously, clearing vegetation and cycling nutrients into the soil.
In 2024, a study of 649 soil core samples from the Smithsonian’s Coastal Carbon Network found that wetlands store more carbon when alligators are present. By suppressing herbivores and allowing vegetation to grow, the predators increased the carbon sequestration capacity of the coastline, an effect that had not been previously documented.
The economic scale of the program is substantial. Over its history, more than 11 million wild eggs were collected, and more than 7 million farm-raised alligators entered commerce. Cumulative revenues exceeded $988 million. The program also provided coastal storm surge protection, nursery habitat for commercial fisheries, and other ecosystem services.
Efforts to replicate the model elsewhere have had mixed results. In the United Kingdom, authorities hired trappers to remove feral nutria from the Norfolk Broads, eliminating 97,000 animals. But without a native apex predator to maintain pressure, the approach required continuous human intervention. In the Florida Everglades, alligators play a similar ecological role, but Burmese pythons, an invasive species released through the pet trade, have reduced raccoon populations by 99.3 percent and opossums by 98.9 percent. Pythons and alligators can consume each other, and neither species has been able to suppress the other, leaving the system in a stalemate.
Louisiana’s program succeeded because of a specific alignment: a native predator adapted to consume the invader, combined with an economic framework that made habitat preservation profitable for private landowners.
The program now faces a new challenge. Feral hogs, illegally released by sport hunters, have discovered alligator eggs as a food source. A 2011 survey found that more than half of Louisiana’s alligator farmers had suffered nest destruction from feral swine, with 590 nests destroyed in a single season. Game camera data from Texas confirmed that roughly half of all monitored nests were predated by hogs.
The alligator program continues to generate revenue while providing coastal protection and carbon storage. It operates as a commercially driven conservation model, one whose long-term viability depends on managing the new threats to the alligator’s reproductive cycle.