A group of villagers in Vanuatu are concerned that continuing development pressures are contributing to the over-exploitation of eggs of the Vanuatu Megapode Megapodius layardi. The Vanuatu Megapode or “namalau” as it is known locally, is endemic to the country and classified as Vulnerable. Repeating a previous survey carried out in 1995, the Vanuatu Protected Areas Initiative mapped and classified the burrows at three communal nesting grounds on north-west Ambrym in November 1996. The number of active and probably active burrows on the beach was low compared with 1995, whereas it was higher on both the raised promontories. The beach nesting site had recently been affected by a cyclone, and storm waves had inundated the area with the highest concentration of burrows. There is concern over the high percentage of megapode burrows checked by villagers at Buwoma, as well as the localized impact visitors could be having. Discussions with villagers raised useful points to be included in the proposed protection plan, particularly the support for a protected area.

The Houbara Bustard Chlamydotis undulata macqueenii is a regular winter visitor from northern breeding grounds to the United Arab Emirates (UAE) but the migration routes and origin of these birds are still poorly known. Five bustards were fitted with platform transponder terminals in UAE in the winter of 1996-1997. The overall distances covered by the birds were very variable, ranging from 3,747 km to 11,938 km. The return migration date of Houbara from UAE ranged from 19 March to 2 April 1997, while the outward migration began from 10 September to 7 November 1997. The Houbara spent the summer n i different areas, namely China (north of lake Nor), Kazakhstan (Kyzyl Kum desert and north of the Aral Sea), Uzbekistan (south of the Aral Sea) and north Afghanistan. These results are the first to describe an annual cycle of migration for Houbara Bustards and should aid the development of appropriate conservation measures for this species.

The Houbara Bustard on Fuerteventura uses cultivated fields (gavias) as feeding sites, finding in these a high-level resource of easy access. A total of 521 visits were observed during this study, 81 to abandoned gavias, 139 to cultivated, and 301 to ploughed ones. This use was correlated with the total vegetation cover, as well as with cover by herbaceous plants and by alfalfa Medicago sativa. The relationship with invertebrate abundance was negative. Cultivated gavias were selected in relation to their alfalfa cover, abandoned gavias in relation to their herbaceous cover, and ploughed gavias were selected in relation to total vegetation cover, cover of herbaceous plants, Launaea arborescens and Salsola vermiculata cover, and vegetation height. Figs, present in ploughed gavias only, were a highly favoured food resource. Of the three study localities, Lajares was most visited by Houbaras (357 visits), followed by Triquivijate (105) and Tefía (59). This use was not correlated with the population of Houbaras in each locality but with the resources that were found in them. The gavias were used in all seasons of the year, mainly in summer, and less so in spring. In summer, use was correlated with herbaceous plant cover and associated to the presence of figs, and in winter with herbaceous cover; in autumn there was no overall selection for variables; in spring, selection was negative with respect to invertebrate availability. This predictable food resource is a real advantage for the maintenance of Houbara populations and contributes to the conservation of the species on Fuerteventura.

We examined population and ecosystem patterns hoping to inform conservation strategies for Burrowing Owls Speotyto cunicularia in Canada. The owls chose moderately to heavily grazed grasslands for nesting and roosting, and avoided cultivated fields. Where grassland patches were isolated in 90% cultivation, owls dispersed later, for shorter distances and less often. Mortality rate during the 5-month study was high (adult ratio 0.45, juveniles 0.55), which may contribute to local declines. Additional mortality may occur on migration and during winter. We extrapolate from local effects (loss of grassland habitat with burrows for roosting, and ~2% “incidental” predation) to suggest that such changes detrimental to the owls occur throughout the central Great Plains ecosystem which the owls occupy year-round. The changes include ecosystem processes such as plant succession, owl dispersal and predation. These changes are likely to be irreversible on a scale that would be required to help this owl. The species may face extinction in Canada, at the northern limit of its range.

A survey was undertaken in 1995 to assess the conservation status of the Madeira Laurel Pigeon Columba trocaz, a threatened species endemic to the Island of Madeira. The first large scale survey was carried out 1986, following the cessation of legal hunting of the species, to provide a baseline for future monitoring of population changes. The current study therefore aims to (1) compare population size with those of 1986 and (2) employ distance sampling methods (not used in 1986) to obtain estimates of population density and size. Eighteen transects (13 repeated from the 1986 survey and five new) were conducted in the four main areas of laurel forest. Pigeon numbers had increased on nearly all transects but some of the highest increases, proportionately and often numerically, were in areas with lower numbers in 1986. We estimate the current population to be 10,400 individuals, a considerable increase since 1986, probably due to a ban on hunting. As laurel forest habitat is now very well protected the Madeira Laurel Pigeon is relatively safe from extinction.

Between June and September 1995 estimates were made of the population densities of birds inhabiting fragments of unprotected montane cloud forests in southern Ecuador. The study focused on 10 species: Bearded Guan Penelope barbata, Golden-plumed Parakeet Leptosittaca branickii, Red-faced Parrot Hapalopsittaca pyrrhops, White-capped Parrot Pionus seniloides, Grey-breasted Mountain-Toucan Andigena hypoglauca, Barred Fruiteater Pipreola arcuata, Turquoise Jay Cyanolyca turcosa, Great Thrush Turdus fuscater, Hooded Mountain-tanager Buthraupis montana, and Mountain Cacique Cacicus leucoramphus. Species assemblages and population densities varied greatly between sites, despite the presence of similar habitats and altitudinal ranges. Substantial populations of the threatened Bearded Guan, Grey-breasted Mountain-Toucan and Golden-plumed Parakeet were found in areas previously unstudied, as well as in areas previously known to be important. Currently unprotected areas are important for the conservation of montane cloud forest birds.

The rare and threatened Long-wattled Umbrellabird Cephalopterus penduliger inhabits the canopy and mid-storey level of humid to wet foothill and montane forests (150–1,800 m)of the Andean slopes of south-west Colombia and western Ecuador. Here we report on male activity pattern and display behaviour observed at one of two leks recently discovered in the vicinity of Playa de Oro, Rio Santiago, Esmeraldas Province, north-west Ecuador. Courtship behaviour of C. penduliger is compared with the Central American and Amazonian congeners (Bare-necked Umbrellabird C. glabricollis and Amazonian Umbrellabird C. ornatus). The lek of C. penduliger was active during the whole study period (February 1997 to January 1998), but both lek structure and daytime activity pattern changed markedly within the observation period.

Special Issue: International Galliformes Symposium (Volume 8, Number 4, December 1998)

As a result of an unfortunate technical error, the copyright line at the top of the opening page of each paper in the above contained the wrong year and volume number (Volume 9, 1999). It should read as follows:

Bird Conservation International (1998) 8:000-000, © BirdLife International 1998

We apologise for this error and for the inconvenience caused to both contributors and readers.