The distribution of Tahitian landbirds in the early twentieth century and at presented here together with maps. Three categories may be recognized: (1) species with a declining distribution owing to changes in habitats (Green-backed Heron), (2) stable or increased species, including local and earlier introduced species, and (3) newly introduced species (Zebra Dove, Red-vented Bulbul, Silvereye and Crimson-backed Tanager). Moreover, owing to their low population numbers, two species, the Pacific Pigeon and the Tahiti Monarch, are on the verge of extinction even if their distribution has not changed notably during this century.

Les repartitions des oiseaux terrestres reproducteurs de Tahiti, au début et à la fin du 20e siècle, sont présentées sous forme de cartes. Trois catégories d'espèces sont dis-tinguées: (1) espèce dont la répartition est en déclin a la suite des modifications d'habitats (Héron vert), (2) espèces stable ou en légère augmentation, chez qui on trouve des oiseaux locaux et des oiseaux introduits, et enfin (3) les espèces introduites durant le 20e siècle (Tourterelle striée, Bulbul à ventre rouge, Zosterops à poitrine grise et Tangara cramoisi). II apparaît que deux espèces, le Carpophage du Pacifique et le Monarque de Tahiti, sont aujourd'hui très menacées, même si leur répartition n'a pas régressé d'une façon significative.

Between June 1989 and October 1990 casual records of rare birds were made in Sabah and on Sipadan Island, Malaysia, and on Luzon, Negros, Bohol and Mindanao, Philippines, with additional observations on Palawan and Tawitawi, Philippines, in August and September 1991. Key sites for bird conservation profiled here are the Angat watershed, Quezon National Park and Candaba Marsh (all on Luzon), Mt Canlaon (Negros), Rajah Sukituna National Park (Bohol), Mt Katanglad (Mindanao), remaining forest on both Tawitawi and Sipadan, and the Danum Valley in Sabah. Notes are provided on 31 species of bird, 17 already considered threatened, three near-threatened. While one threatened species (Nicobar Pigeon Caloenas nicobarica) should be downlisted, at least six species (Spotted Imperial-pigeon Ducula carola, Blue-winged Racquet-tail Prioniturus verticalis, Blue-naped Parrot Tanygnathus lucionensis, McGregor's Cuckoo-shrike Coracina mcgregori, Falcated Wren-babbler Ptilocichla falcata and Palawan Flycatcher Ficedula platenae) should be elevated to threatened status. Records for other species supplement and reinforce current assessments of threat or indicate new distributional or taxonomic information on non-threatened forms.

The Aldabra White-throated Rail Dryolimnas cuvieri aldabranus is confined to Middle Island (c. 7,700 birds), lie Polymnie (c. 270) and De aux Cèdres (c. 80) on Aldabra Atoll (now a World Heritage Site) in the Seychelles. It uses all available terrestrial habitats, but chiefly occurs in scrub cover and particularly in the densest types, where leaf-litter (and hence litter fauna) is richest. Its extinction on Assumption, Astove and Cosmoledo is attributable to widespread habitat loss and disturbance, and to human utilization as food; the extent to which rats and cats affect the form, which is flightless, is debatable.

The last flightless bird of the western Indian Ocean, Dryolimnas cuvieri aldabranus survives only on Aldabra. Its population numbered some 8,000 in 1973–1976. Surveys suggest numbers remained roughly constant between 1968 and 1988 (with a fluctuation of only 4% in responses to call playback between 1983 and 1988), but distribution continued to contract. Longevity can reach over 8.5 years (but is probably lower on average), and some birds remain within 100 m of the site of ringing for at least five years. Feral predators remain a threat, and captive populations are recommended. The monitoring procedure may have value for other Gruiformes.

Cyclonic storms, variously called typhoons, cyclones, or hurricanes (henceforth, hurricanes), are common in many parts of the world, where their frequent occurrence can have both direct and indirect effects on bird populations. Direct effects of hurricanes include mortality from exposure to hurricane winds, rains, and storm surges, and geographic displacement of individuals by storm winds. Indirect effects become apparent in the storm's aftermath and include loss of food supplies or foraging substrates; loss of nests and nest or roost sites; increased vulnerability to predation; microclimate changes; and increased conflict with humans. The short-term response of bird populations to hurricane damage, before changes in plant succession, includes shifts in diet, foraging sites or habitats, and reproductive changes. Bird populations may show long-term responses to changes in plant succession as second-growth vegetation increases in storm-damaged old-growth forests.

The greatest stress of a hurricane to most upland terrestrial bird populations occurs after its passage rather than during its impact. The most important effect of a hurricane s i the destruction of vegetation, which secondarily affects wildlife in the storm's aftermath. The most vulnerable terrestrial wildlife populations have a diet of nectar, fruit, or seeds; nest, roost, or forage on large old trees; require a closed forest canopy; have special microclimate requirements and/or live in a habitat in which vegetation has a slow recovery rate. Small populations with these traits are at greatest risk to hurricane-induced extinction, particularly if they exist in small isolated habitat fragments.

Recovery of avian populations from hurricane effects is partially dependent on the extent and degree of vegetation damage as well as its rate of recovery. Also, the reproductive rate of the remnant local population and recruitment from undisturbed habitat patches influence the rate at which wildlife populations recover from damage.

Fieldwork aimed at censusing Gumey's Pitta Pitta gumeyi in Peninsular Thailand was carried out over three field seasons. Fourteen sites were surveyed, at four of which the species was found. The main site (where it had been rediscovered in 1986) held 24–34 pairs, 12–18 of which were in the 500 ha study area. A second site held 3-6 pairs (but it is thought unlikely that this population still exists today), whilst the other two sites held only two pairs each and were thought to have negligible chances of survival. All territories were in semi-evergreen rainforest, below 150 m altitude. The current population i s probably some 20–30 pairs, with territories still being lost annually to deforestation. This is currently the total known world population; it is possible that the species may survive in southern Burma, but no recent surveys have been undertaken there. Furthermore, massive deforestation caused by Thai timber companies has been reported from Burma during 1988–1993. The interpretation of census results are discussed, particularly with reference to social organization and calling seasonality. The determined protection of the one remaining site supporting a viable population will be essential if the species is to survive into the next century.