The Mauritius Kestrel (Falco punctatus) is a bird of prey from the family Falconidae endemic to the forests of Mauritius, where it is restricted to the southwestern plateau’s forests, cliffs, and ravines.
It is the most distinct of the Indian Ocean kestrels. It colonized its island home to evolve into a distinct species probably during the Gelasian (Late Pliocene). It is the most distant living species among the western Indian Ocean kestrels (Groombridge et al. 2002, qv Réunion Kestrel).
It can reach a size between 26 and 30.5 cm. The weight is up to 250 grams. The males are slightly smaller than the females. The wing is approximately 45 cm and are rounded, unlike those of other falcons.
The lifespan is 15 years in captivity.
Diet / Feeding
The Mauritius Kestrel hunts by means of short, swift flights through forests.
It is carnivorous, eating geckos, dragonflies, cicadas, cockroaches, crickets, and small birds.
The story of this bird is one of the most remarkable conservation stories. In pre-colonial time the population was estimated between 175 and 325 breeding pairs.
This small population was caused most likely by deforestation in the 18th century and by cyclones. But the most severe decline was in the 1950s and 1960s due to indiscriminate DDT use and invasive species like cats, mongooses and Crab-eating Macaques which killed the kestrels and their eggs.
What was probably this species’ closest relative in recent times, the Réunion Kestrel, became extinct around 1700 for fairly mysterious reasons.
The recorded population dropped to an all-time low of only 4 individuals in 1974 and it was considered the rarest bird in the world. Stanley Temple from the Cornell University studied this species for two years and the first attempt in 1973 to breed this birds in captivity failed because the hatchling died when the incubator had a breakdown.
Though conservation measures were immediately undertaken with the help of a breeding programme by the Jersey Zoo (now called Durrell Wildlife) the efforts to rescue this species initially failed because the eggs were not fertile.
In 1979 a new attempt was undertaken. With the help of Gerald Durrell, the Welsh biologist Carl G. Jones established a wildlife sanctuary on Ile aux Aigrettes.
He climbed on the trees and removed the eggs from the nests. This time the eggs were fertile, and Jones was able to rear the hatchlings in incubators.
The wild kestrels’ diet was supplemented so they would be able to lay a new egg after the first one was removed, averting any negative impact on the wild population. Slowly the population increased and during a census in 1984 50 individuals were estimated.
Techniques for breeding, release, and “hacking” of young birds (allowed to go wild as they learn enough how to hunt for itself) were improved, the captive breeding center becoming a pioneering research institution for tropical raptor and small falcon conservation.
The captive breeding programme was scaled back in the early 1990s as a self-sustaining population was established. Since 1994, the programme serves only as a safeguard, should some catastrophe befall the wild population, and other rare endemics are now being cared for at the station (such as the Pink Pigeon or the Mauritius Fody).
Today there are more than 800 mature birds, with numbers rising; it is estimated that the remaining habitat allows for a carrying capacity of maybe 50-150 more (BirdLife International 2006a,b).
They occur in the remaining forests of the island, especially in the Black River Gorges region. The species was downlisted to Vulnerable by the IUCN in 1994 as releases of captive-bred birds became unnecessary.
Little conservation action was deemed necessary only a two decades – in Mauritius Kestrel terms, a long lifetime or maybe 4-5 generations – after the species had stood at the very brink of extinction.
Today, apart from routine monitoring to be able to assist individual couples that fail to establish breeding territories for lack of nesting facilities – a major limiting factor, the ongoing control of introduced predators is basically all that is being done to assist the species’ survival (BirdLife International 2006a,b).
While some apparent inbreeding depression was noted in the captive birds, it was certainly lower than might be expected given that the effective population size was maybe 5 individuals during the mid-1970s.
It is known that several genetic lineages of Mauritius Kestrels have disappeared entirely during the 20th century population decline.
However, the debilitating effects of DDT accumulation on the birds’ health, and not inbreeding, are considered to have been the major cause for the failure of Temple’s breeding program.
The evolutionary history of the birds seems to hold clues as to why (Groombridge et al. 2002): Mauritius is a volcanic island, and although the colonization of the island by kestrels cannot be dated with high precision, it was almost certainly some time before volcanic activity died down.
The Mauritius Kestrel population seems to have survived a prolonged period of volcanic activity, which must have kept the population small and fluctuating as habitat, food, and kestrels were destroyed by volcanic eruptions time and again.
As near-panmictic conditions were sustained for many generations, alleles that might cause inbreeding depression were steadily removed by means of natural selection.
The phenomenon that effective population sizes as low as 4-5 can be tolerated without pronounced inbreeding depression is also known from other small-island birds, such as the Black Robin Petroica traversi or the Laysan Duck.
The classification as a Vulnerable species is due to the same fact: on an island as small as Mauritius, chance events like volcanic eruptions (hardly likely in our time) or storms (common and possibly increasing in frequency and strength) can always wipe out major parts of a species’ population (BirdLife International 2006a,b).
The IUCN classification VU D1+D2 reflects this, translating into a population size of less than 1000 mature individuals, and less than 20 km² of occupied habitat.