Birdlife International's Important Bird Areas Programme in Morocco

Magin, C. 2000. Birdlife International's Important Bird Areas Programme in Morocco. Ostrich 71 (1 & 2): 175–176.

BirdLife International's Important Bird Areas programme (IBA) was launched in Morocco in 1995 by a steering committee comprised of three national NGO's, representatives from the Ministries of Agriculture and Environment, the University of Montpelier and BirdLife International. Subsequently the programme's implementation has been overseen by the BirdLife Secretariat. It will result in the publication of a national IBA inventory and the elaboration of plans to promote the conservation of priority IBAs. The selection of IBA sites is discussed and three examples of Moroccan IBAs are given.     

Important Bird Areas in Kenya

Bennun, L. & Njoroge, P. 2000. Important Bird Areas in Kenya. Ostrich 71 (1 & 2): 164–167.

The process of defining Important Bird Areas in Kenya has been underway since January 1995, with financial support from the Royal Society for the Protection of Birds. Literature review has proceeded in parallel with field surveys, which are still ongoing. Some 65 globally Important Bird Areas have so far been identified, and this total is likely to increase. Sites were intitially selected using the criteria of threatened species (37 sites) and congregatory species (15 sites). Additional sites were then identified for biome-restricted and restricted-range species, using information from the Bird Atlas of Kenya; these sites must form part of a regional set. Threatened species sites are concentrated in forests (on the coastal strip, in the central highlands and in western Kenya) and papyrus swamps. Congregatory-species sites are concentrated along the Rift Valley and the coast. The remaining sites are concentrated in semi-arid areas to the immediate north and east of the central plateau, and in highland forest on each side of the Rift Valley. No IBAs have yet been identified in the flat, arid north-eastern sector of the country. A large number of sites require additional protection and/or improved management. Particular priorities include several papyrus IBAs around Lake Victoria, among them Lake Kanyaboli and Yala and Sare Swamps, grassland pockets in Mungatsi and Nambale, Western Province; the Kakamega, South Nandi and North Nandi Forests; the increasingly fragmented coastal forests, including Arabuko-Sokoke Forest; and the Taita Hills. Information on the IBA process and its results is being distributed to decision-makers through a high-level IBA Advisory council, with encouraging intitial results.     

Developing National Conservation Programmes through the IBA Process

Nigussie, A.T. & Dellelegn, Y. 2000. Developing national conservation programmes through the IBA process. Ostrich 71(1 & 2): 162–163.

The history of the Ethiopian Wildlife and Naural History Society (EWNHS) is presented and the background to involvement with BirdLife International and incorporation in the African network as a BirdLife Partner is described. The IBA intitiative has formed the core of the EWNHS BirdLife programme and two years of funding from the European Union has faciliated the launch of a full-scale national IBA inventory and conservation programme. The current state of the analysis of Ethiopia's important sites is presented together with the plan for further site survey work and for action to conserve sites though advocacy and the developmant of local and national capacity to monitor and manage sites.     

Le Projet ‘Zicoma’ ou ‘Zones d'Importance pour la Conservation des Oiseaux a Madagascar’

Rakotonomenjanahary, M.O. & Hawkins, A.F.A. 2000. Le Projet ‘Zicoma’ ou ‘zones d'importance pour la conservation des oiseaux a Madagascar’. Ostrich 71 (1 & 2): 168–171.

Madagascar a seulement 277 espèces d'oiseau recensées jusqu'à maintenant. Mais le niveau d'endémisme est très élevé avec 110 espèces endéemiques, 37 genres endémiques et 5 familles endémiques. Selon les critères internationaux, 45 eqèces sont menacées globalement et 9 autres espèces sont des oiseaux à territoire restreint. Au cours d'un atelier, 37 ornithologues basés à Madagascar ont identifyé 53 sites qui sont considérés comme ZICO confirmé et 52 autres ZICO provisoires. ASITY, la première association pour les ornithologues Malagasy, était constituée pendant I'atelier. Le programme ZICOMA commencera en 1997 avec la formation technique des chercheurs Malagasy pour faire des missions sur le terrain des ZICO nonfirmés.

Rakotonomenjanahary, M.O. & Hawkins, A.F.A. 2000. The Important Bird Areas programme in Madagascar. Ostrich 71 (1 & 2): 168–171.

Madagascar does not have a rich avifauna, with 277 species recorded to date. However, the level of endemism is very high: 110 endemic species, 37 endemic genera, and 5 endemic families. Following international criteria, 45 species are globally threatened and a further 9 qualify as restricted area species. A workshop involving 37 Madagascar-based ornithologists identified 53 confirmed IBA's, and a further 52 possible IBA's. ASITY, the first Malagasy ornithological society, was founded during this meeting. The Zicoma project, commencing in 1997, will focus on the assessment of the unconfirmed IBA sites, and on the training of local personnel.     

Protected area gap analysis of important bird areas in Tanzania

Analyses of gaps in protected area (PA) coverage of species distributions have been carried out extensively for the past two decades, aiming to better locate new PAs and conserve species. In this study, progress to close gaps in the protection of the Important Bird Areas (IBAs) of Tanzania is assessed between 2002 and 2009, with a detailed GIS analysis from 2007 to 2009. Remaining gaps are ranked according to biological factors such as numbers of red list and restricted range avian species and social pressures such as human population, agriculture and density of the road network. Results show that there has been a 5.3% increase (7615.1 km²) in protection of IBAs between 2007 and 2009. Of the 27 remaining IBA protection gaps, three are of high, nine of medium and fifteen of low priority for action. The current IBA ‘gap area’ of 17,133.3 km² contains around 26% forest, 13% shrubland, 9% grassland, 36% wetland and 12% agricultural land. This analysis provides a simple template for defining where further action to protect remaining IBA sites in Tanzania would lead to enhanced conservation of avian biodiversity in that country and provides a methodology for analysis leading to conservation action elsewhere in Africa.     

Ethiopian Wildlife and Natural History Society,the Important Bird Areas Programme and other projects

Nigussie. A.T. 2000. Ethiopian Wildlife and Natural History Society, the Important Bird Areas Programme and other projects. Ostrich 71 (1 & 2): 181–182.

The BirdLife International Partner in Ethiopia is the Ethiopian Wildlife and Natural History Society (EWNHS), established in 1966. The aims of the society are mentioned and projects run by the EWNHS, within the framework of the ‘Conservation for Survival’ agenda, are described. These projects include the Important Bird Areas Project, the Environmental Education Support Publications, School's Environmental Education Project, Plant Locally and Nurture Trees project and The Indoor/Outdoors Activities project.     

Monitoring Important Bird Areas in Africa: Towards a Sustainable and Scaleable System

The need for effective global monitoring of biodiversity is clearer than ever, but our measurements remain patchy and inadequate. In the biodiversity-rich tropics, a central problem is the sustainability of monitoring schemes. Locally-based, participatory approaches show promise in overcoming this problem, but may not contribute effectively to monitoring at larger scales. BirdLife International’s framework for monitoring Important Bird Areas (IBAs) in Africa is designed to be simple, robust and locally-grounded, but to produce scaleable results that can be compiled into national or regional indices. Focusing on key sites for bird conservation, identified according to standard criteria, the framework institutionalises monitoring in site management authorities and Site Support Groups (community-based organisations of local people working for conservation and sustainable development). A small, central monitoring unit co-ordinates the programme nationally, compiles, analyses and manages data, and provides feedback. ‘Basic’ monitoring (taking place at all sites) involves scoring of state, pressure and response trends using site information submitted on simple forms. ‘Detailed’ monitoring (taking place at a selected sub-set of sites) involves more intensive measurement of particular variables that relate to site management targets. IBA monitoring is now underway in at least 10 African countries, with implementation of the framework most advanced (thanks to a pilot project) in Kenya. The 2004 IBA monitoring report for Kenya provides extensive information on individual IBAs, plus indices for national trends in state, pressure and response, based on data from 49 out of 60 sites. The experience in Kenya shows that institutionalisation is vital, but takes considerable time and effort; that adequate co-ordination (including timely feedback) is key; and that participatory monitoring has many valuable benefits beyond the data collected. Further work is being undertaken to refine the process, improve its scientific underpinning, and strengthen the feedback loop from data and analysis to action on the ground.     

Implications of forest utilisation on bird conservation

Waiyaki, E. & Bennun, L.A. 2000. The avifauna of coastal forests in southern Kenya: status and conservation. Ostrich 71 (1 & 2): 247–256.

The biological importance and uniqueness of East African coastal forests is widely recognised; they form an Endemic Bird Area. Important remnants of this fragmented habitat OCCUT on the southern Kenyan coast, but their avifauna has been little studied. In October 1992, September 1993 and May-August 1994, we systematically assessed the avifauna of fifteen South Coast forest fragments (and the threats facing them) using mist-netting, timed species counts and direct observations. Sixty forest-dependent bird species were recorded, amongst them three that are globally threatened (Sokoke Pipit Anthus sokolcensis, Spotted Ground Thrush Turdus fischeri, East Coast Akalat Sheppardia gunningi) three that are near-threatened (Southern Banded Snake Eagle Circaetus fasciolatus, Fischer's Turaco Tauraco fischeri, Plain-backed Sunbird Anthrepres reichenowi) and four that are ‘restricted-range’ (Fischer's Turaco, Sokoke Pipit, Mombasa Woodpecker Campethera mombassica, Uluguru Violet-backed Sunbird Anthreptes neglectus). Globally or regionally threatened and near-threatened species were relatively rare and were patchily distributed across forests. In contrast, most other forest species were widely distributed, being present in most or all fragments. The breakdown of traditional conservation systems, selective logging, encroachment by cultivation and fire-maintained grassland, fragmentation, allocation of land for urban development, pole cutting, charcoal burning, hunting and trapping, prospective mining, bark stripping and elephant damage are the major threats to the continued survival of these forests. Shimba Hills (Mkongani & Longomagandi), Gandini, Mrima, Marenji, Dzombo, Waa, Buda and Gongoni forests met the criteria for Globally Important Bird Areas set by Birdlife International. A number of urgent steps are needed for improved forest management if these important sites are to survive and retain their biological diversity.     

Key sites for the conservation of waterbirds in Uganda

Arinaitwe, J., Byaruhanga, A. & Mafabi, P. 2000. Key sites for the conservation of waterbirds in Uganda. Ostrich 71 (1 &2): 102–105.

Uganda has a rich bird diversity with 1 008 species including 28 listed species (Collar et al. 1994) and 207 species of regional conservation concern (Bennun & Njoroge 1996). Over 240 species are waterfowl, of which nine are globally threatened, 45 are regionally threatened and five are considered to be of national conservation interest. This high waterbird diversity corresponds to a large wetland area covering about 10% of the land area of Uganda. However, only 6% of the wetlands fall under gazetted protected areas and only one site is recognised as of global importance under the terms of the Ramsar Convention. Three recent activities of JA, the National Wetlands Programme and East Africa Natural History Society (Uganda), have produced new information on distribution and abundance of waterbirds in Uganda. Concurrent with these activities, criteria for the identification of globally threatened species (Collar et al. 1994), species of regional conservation concern (Bennun & Njoroge 1996) and nationally important species (National Wetlands Programme, in press) have been developed. Also, criteria for selection of sites at the global (Ramsar and IBA), regional (IBA) and national (National Wetlands Programme) levels have become available. This paper reviews the advances in the knowledge of waterbirds in Uganda and applies the above criteria to highlight sites that are crucial for conservation at global, regional and national levels.     

Abundance and habitat choice as an indication of colonisation history in Comoro Land birds

Louette, M., Stevens, J. & Neri, F. 2000. Abundance and habitat choice as an indication of colonisation history in Comoro Land birds. Ostrich 71 (1 & 2): 345–346.

We measured bird abundance and habitat parameters by point transect counts. Bird abundance is different for a number of species among the four Comoro islands (Louette, M. et al. 1993. Oiseau 63: 115–126), and among sites on a given island (especially in the case of forest birds, such as on Grand Comoro, an island with great variation in habitat).     

Recent papyrus swamp habitat loss and conservation implications in western Kenya

Papyrus Cyperus papyrus swamps are characteristic of many wetlands of tropical Africa. Like most wetland habitats worldwide, they are under human pressure due to harvesting and reclamation for agriculture. Changes in papyrus cover were assessed using aerial photographs at three Important Bird Areas (IBAs) in the Kenyan sector of Lake Victoria. Papyrus area losses of 50% (Dunga), 47% (Koguta) and 34% (Kusa) occurred between 1969 and 2000. The habitat loss and degradation at the sites appeared purposeful, driven by demand for agricultural land and other papyrus products. Cleared papyrus and cultivated areas around all sites increased over the same period. If papyrus habitat loss continues at current rates, papyrus swamps at Dunga and Koguta will disappear by 2020, and Kusa will be reduced to only 19% of its 1969 area. Human population growth around the sites, with concomitant increase in land use activities and papyrus harvesting are the major factors that account for papyrus area reductions. Loss of total habitat is accompanied by deterioration in habitat quality within remaining areas. Papyrus physical structure (height and density) inversely correlate to human disturbances that include footpaths, cutting, burning, grazing and farming. The continued papyrus habitat loss and degradation represents a significant threat to biodiversity conservation particularly for papyrus-specialist birds and other papyrus-reliant species in western Kenya. The observed pattern of papyrus extents and land use changes at all sites provide the site-scale information necessary for papyrus conservation planning. In particular, conservation action is needed most urgently at Dunga and Koguta as they face severe land use pressures.     

The Foraging Ecology of the Endangered Cape Verde Shearwater,a Sentinel Species for Marine Conservation off West Africa

Large Marine Ecosystems such as the Canary Current system off West Africa sustains high abundance of small pelagic prey, which attracts marine predators. Seabirds are top predators often used as biodiversity surrogates and sentinel species of the marine ecosystem health, thus frequently informing marine conservation planning. This study presents the first data on the spatial (GPS-loggers) and trophic (stable isotope analysis) ecology of a tropical seabird—the endangered Cape Verde shearwater Calonectris edwardsii–during both the incubation and the chick-rearing periods of two consecutive years. This information was related with marine environmental predictors (species distribution models), existent areas of conservation concern for seabirds (i.e. marine Important Bird Areas; marine IBAs) and threats to the marine environment in the West African areas heavily used by the shearwaters. There was an apparent inter-annual consistency on the spatial, foraging and trophic ecology of Cape Verde shearwater, but a strong alteration on the foraging strategies of adult breeders among breeding phases (i.e. from incubation to chick-rearing). During incubation, birds mostly targeted a discrete region off West Africa, known by its enhanced productivity profile and thus also highly exploited by international industrial fishery fleets. When chick-rearing, adults exploited the comparatively less productive tropical environment within the islands of Cape Verde, at relatively close distance from their breeding colony. The species enlarged its trophic niche and increased the trophic level of their prey from incubation to chick-rearing, likely to provision their chicks with a more diversified and better quality diet. There was a high overlap between the Cape Verde shearwaters foraging areas with those of European shearwater species that overwinter in this area and known areas of megafauna bycatch off West Africa, but very little overlap with existing Marine Important Bird Areas. Further investigation on the potential nefarious effects of fisheries on seabird communities exploiting the Canary Current system off West Africa is needed. Such negative effects could be alleviated or even dissipated if the ‘fisheries-conservation hotspots’ identified for the region, would be legislated as Marine Protected Areas.     

Distribution and abundance of forest birds in Ghana

Ntiamoa-Baidu, Y., Owusu, E.H., Asamoah, S. & Owusu-Boateng, K. 2000. Distribution and abundance of forest birds in Ghana. Ostrich 71 (1 & 2): 262–268.

Forest reserves within the Ghanaian rain forest have been classified into categories (Condition I-VI) on the basis of their botanical importance and status of the vegetation. We present data on the distribution and abundance of avifauna of 28 Condition II and III forest reserves in southern Ghana based on line transect counts and mist-net captures. A total of 227 species were recorded for all the sites; species records for individual sites ranged from 78–119. The dominant groups in the overall survey were Muscicapidae (represented by 40 species), Pcynonotidae (21) and Cuculidae (12). The most abundant bird species in the Ghanaian forests were Yellow-whiskered Greenbul, Green Hylia, Green Pigeon and Olive Sunbird. Species encounter rates ranged from 16.7 to 50.7 species per km with individual bird encounter rates of 27.9 to 172.0 birds per km. Capture rates in mist-nets ranged from 1.2 to 3.9 birds per 100 metre net-hr (mnh). A total of 183 species were recorded in Condition II forest as compared with 167 in Condition III forests. The effects of forest condition and vegetation types on the total number of species recorded were, however, not statistically significant. The Similarity Index for bird communities within Condition II and III forests was 0.72. Bird species composition in the two forest types also differed: e.g., seven primary forest species, as well as 40% of the species associated with primary and matured secondary forest which were recorded in Condition II forests, were absent from Condition III forests. Bird communities of Moist Evergreen, Upland Evergreen and Moist semi-Deciduous were more similar than communities in the Wet Evergreen forest type. The implication of the results for conservation of the Ghana's forests is discussed.     

云南蒙自坝区湖泊越冬水鸟组成和变化趋势初报

第264号国际重点鸟区位于云南蒙自坝区,但缺乏系统的鸟类数据。2006-2014 年,每年1月下旬至2月上旬,在蒙自坝区的三个湖泊长桥海、大屯海和三角海（简称“三湖”）进行水鸟调查,累计记录到水鸟12科33属63种。其中有国家I级保护动物1种（黑鹳Ciconia nigra）,国家II级保护动物2种（白琵鹭Platalea leucorodia,彩鹮Plegadis falcinellus）,极危（CR）鸟类1种（青头潜鸭Aythya baeri）,近危（NT）鸟类4种。在长桥海记录的水鸟种类和数量最多,但Shannon-Wiener多样性指数较低,优势度指数较高。在三角海记录到的鸟类种类较多,Shannon-Wiener多样性指数较高而优势度指数较低。在大屯海记录到的鸟种和数量都很少。分别对三湖越冬水鸟种数、数量和雁形目、骨顶鸡和鹳形目水鸟数量变化趋势进行了Man-Kendall检验,发现调查期间,三湖越冬水鸟种数和数量无显著变化,骨顶鸡数量无显著变化趋势,雁形目水鸟略有下降趋势,而鹳形目水鸟有显著下降趋势。鉴于三角海记录到的国家一、二级保护动物和鹳形目水鸟数量,建议扩大第264号国际重点鸟区范围,将其纳入。     

Breeding distribution,population size and conservation of the Greyheaded Gull Larus cirrocephalus in southern Africa

Brooke, R.K., Allan, D.G., Cooper, J., Cyrus, D.P., Dean, W.R.J., Dyer, B.M., Martin, A.P. & Taylor, R.H. 1999. Breeding distribution, population size and conservation of the Greyheaded Gull Larus cirrocephalus in southern Africa. Ostrich 70 (3&4): 157–163.

The Greyheaded Gull Larus cirrocephalus occurs throughout southern Africa, both coastally and inland, and has bred at one time or another at 67 known localities since the 1860s. Most of these sites have been occupied by small numbers of birds, even single pairs, and for only one or a few years. The two principal breeding areas are the East Rand in Gauteng and Lake St Lucia in KwaZulu-Natal, both in South Africa. The next most important sites are Walvis Bay, Namibia and Lake Ngami, Botswana. The total southern African breeding population is estimated as about 2000 pairs. The Greyheaded Gull is not a threatened species in southern Africa, with 27 breeding sites supporting more than half the breeding population within formally conserved areas.     

Seasonal pattern of breeding by Cape and Crowned Cormorants off western South Africa

Crawford, R.J.M., Dyer, B.M. & Upfold, L. 1999. Seasonal pattern of breeding by Cape and Crowned Cormorants off western South Africa. Ostrich 70(3&4): 193–195.

At Bird Island, Lambert's Bay, and Malgas Island, South Africa, small numbers of Cape Cormorants Phalacrocorax capensis may breed at any time of the year, but the main breeding season is from September to February. At Malgas Island, Crowned Cormorants P. coronatus may also breed throughout the year, but mostly from December to March. Counts of the breeding population of Cape Cormorants should be undertaken between October and December, and of Crowned Cormorants in January or February.     

Ensemble models predict Important Bird Areas in southern Africa will become less effective for conserving endemic birds under climate change

Aim  To examine the impacts of climate change on endemic birds, which are of global significance for conservation, on a continent with few such assessments. We specifically assess projected range changes in relation to the Important Bird Areas (IBAs) network and assess the possible consequences for conservation.
Location  South Africa, Lesotho and Swaziland.
Methods  The newly emerging ensemble modelling approach is used with 50 species, four climate change models for the period 2070–2100 and eight bioclimatic niche models in the statistical package biomod . Model evaluation is done using the receiver operating characteristic and the recently introduced true skill statistic. Future projections are made considering two extreme assumptions: species have full dispersal ability and species have no dispersal ability. A consensus forecast is identified using principal components analysis. This forecast is interpreted in terms of the IBA network. An irreplaceability analysis is used to highlight priority IBAs for conservation attention in terms of climate change.
Results  The majority of species (62%) are predicted to lose climatically suitable space. Five species lose at least 85% of their climatically suitable space. Many IBAs lose species (41%; 47 IBAs) and show high rates of species turnover of more than 50% (77%; 95 IBAs). Highly irreplaceable regions for endemic species become highly localized under climate change, meaning that the endemic species analysed here experience similar range contractions to maintain climate niches.
Main conclusions  The South African IBAs network is likely to become less effective for conserving endemic birds under climate change. The irreplaceability analysis identified key refugia for endemic species under climate change, but many of these areas are not currently IBAs. In addition, many of these high-priority areas that are IBAs fall outside the current formal protected areas network.     

Birdlife International: who we are and where we have come from

Rands, M. 2000. Birdlife International: who we are and where we have come from. Ostrich 71 (1 & 2): 148–149.

The International Council for Bird Preservation (ICBP)—the forerunner of BirdLife International—was founded in 1922 by a small and dedicated group of individuals. It has grown into a world-wide network of Partner organisations and individuals committed to achieving the conservation of the world's birds and other biological diversity. The evolution and some major achievements of the organisation are outlined, from the early days of ICBP, to the current status of BirdLife International, actively represented in 80 countries world-wide. The BirdLife Vision, the mission of the Partnership, the regional structures and some of the personalities behind the conservation action are presented as the organisation looks forward to the challenge of conserving the world's birds in the 21st century.     

Evaluating the effectiveness of conservation site networks under climate change: accounting for uncertainty

We forecasted potential impacts of climate change on the ability of a network of key sites for bird conservation (Important Bird Areas; IBAs) to provide suitable climate for 370 bird species of current conservation concern in two Asian biodiversity hotspots: the Eastern Himalaya and Lower Mekong. Comparable studies have largely not accounted for uncertainty, which may lead to inappropriate conclusions. We quantified the contribution of four sources of variation (choice of general circulation models, emission scenarios and species distribution modelling methods and variation in species distribution data) to uncertainty in forecasts and tested if our projections were robust to these uncertainties. Declines in the availability of suitable climate within the IBA network by 2100 were forecast as ‘extremely likely’ for 45% of species, whereas increases were projected for only 2%. Thus, we predict almost 24 times as many ‘losers’ as ‘winners’. However, for no species was suitable climate ‘extremely likely’ to be completely lost from the network. Considerable turnover (median = 43%, 95% CI = 35–69%) in species compositions of most IBAs were projected by 2100. Climatic conditions in 47% of IBAs were projected as ‘extremely likely’ to become suitable for fewer priority species. However, no IBA was forecast to become suitable for more species. Variation among General Circulation Models and Species Distribution Models contributed most to uncertainty among forecasts. This uncertainty precluded firm conclusions for 53% of species and IBAs because 95% confidence intervals included projections of no change. Considering this uncertainty, however, allows robust recommendations concerning the remaining species and IBAs. Overall, while the IBA network will continue to sustain bird conservation, climate change will modify which species each site will be suitable for. Thus, adaptive management of the network, including modified site conservation strategies and facilitating species' movement among sites, is critical to ensure effective future conservation.