Raptor Declines in West Africa: Comparisons Between Protected, Buffer and Cultivated Areas
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Oryx Vol 41 No 3 July 2007 Raptor declines in West Africa: comparisons between protected, buffer and cultivated areas Jean-Marc Thiollay Abstract Since 1970 there has been a dramatic decline were not found outside protected areas. Within the of large raptors and terrestrial birds in West African 1.4 million ha of protected areas in and around south- savannahs. Comparative dry season transect counts east Burkina Faso, six species of eagles and vultures over 4,697 km of driven transects were performed in have estimated populations of c. 100–200 pairs, five spe- 2004–2005 in south-eastern Burkina Faso to assess the cies c. 50–100 pairs, five species have populations of abundance of 41 raptor species and large terrestrial ,50 pairs, and the secretary bird Sagittarius serpentarius species in four National Parks and surrounding hunting was not recorded. No specific reason for the collapse of zones and cultivated areas. Population sizes were esti- large raptors in non-protected areas (which account for mated for larger taxa in protected areas using distance 99% of the area of the countries studied) has been sampling and nest searching. Most large vultures and identified, but the consequences of fast human popula- eagles were generally found only in protected areas, tion growth and habitat changes, overhunting, distur- with fewer individuals in the surrounding buffer zones bances and poisoning may have played a critical role. and nearly none elsewhere. Conversely, the abundance Updating information on the conservation status of of most of the smaller species was not different between these species would be an important first step towards protected and cultivated areas, and three species were their long-term conservation. more abundant in cultivated areas. Helmeted guinea- fowl Numida meleagris, Stanley’s bustard Neotis denhami Keywords Burkina Faso, distribution, population size, and Abyssinian ground hornbill Bucorvus abyssinicus protected areas, raptors, savannah, West Africa. Introduction National Parks across the south-eastern border of Bur- kina Faso. Although it was not possible to assess other Diurnal raptors (Falconiforms) are large predators that components of population viability, such as breeding are widespread and diversified in most habitats but and mortality rates, documenting the quantitative and sensitive to pollutants and disturbances and therefore geographical scale of population collapse and fragmen- good indicators of ecosystem health and biodiversity. tation may give an insight into the future and the Using large-scale comparative roadside counts in West vulnerability of raptor populations. These data will help Africa over .30 years I have documented the severe to define a general conservation strategy for raptors in decline of several species (Thiollay, 2001, 2006a,b). this region, and also indicate the need to review the Eagles and vultures have almost disappeared from conservation status of some species that were consid- non-protected areas but maintain significant popula- ered widespread or common until recently but may tions in National Parks. soon become threatened. The first objective of the present study was to assess the relative conservation value of protected areas for large raptors in central West Africa compared to the Study area non-protected countryside. The second objective was to The area surveyed was in south-east Burkina Faso from estimate the breeding population size of these species, as Ouagadougou south to the borders of Ghana and Benin an indicator of their long-term viability, within the and east to Niger (Fig. 1). The protected areas it encom- passed were: (1) the Nazinga game ranch, a 93,000 ha hunting reserve; (2) the 76,000 ha Arli National Park Jean-Marc Thiollay Museum National d’Histoire Naturelle, CERSP, 55 rue de along the Benin border and the contiguous 275,000 ha Buffon, 75005 Paris, France. E-mail [email protected] Pendjari National Park (referred to here as Arli-Pendjari); Received 22 August 2005. Revision requested 8 June 2006. (3) the 957,000 ha W National Park across the borders of Accepted 24 October 2006. Burkina Faso, Niger and Benin. The surrounding, little 322 ª 2007 FFI, Oryx, 41(3), 322–329 doi:10.1017/S0030605307000809 Printed in the United Kingdom Downloaded from https://www.cambridge.org/core. IP address: 170.106.202.58, on 27 Sep 2021 at 16:16:35, subject to the Cambridge Core terms of use, available at https://www.cambridge.org/core/terms. https://doi.org/10.1017/S0030605307000809 Raptor declines in West Africa 323 Fig. 1 Study area in Burkina Faso and across its south-eastern border, showing villages and protected areas. The simplified roads shown on the map were used as the main transects outside protected areas. inhabited buffer zones included, respectively: (1) the cultivation of cotton, with heavy pesticide use, is heavily poached 155,000 ha Kabore´ Tambi National spreading at the expense of traditional crops. Park, north of Nazinga; (2) the 600,000 ha Singou, Arli, Pama and Madjoari hunting areas, north and west of Methods Arli; (3) the .200,000 ha hunting areas north (Tapoa- Census techniques Djerma) and south-west (Kondio-Kourtiagou) of W National Park. In Benin only the Pendjari National Park, Transect counts were performed in the mid dry season and not the .300,000 ha hunting areas south of this and (late December to mid February) of 2004 and 2005, i.e. W National Parks, were surveyed. Latitudinally, the when most raptors are breeding. The counts were used study area ranged between 11°N (Pendjari) and 13°N to calculate an abundance index and estimate density (south of Niamey, Niger), i.e. all within the Sudan (Bibby et al., 2000). Transects were road segments cross- vegetation zone. ing a uniform habitat type and long enough (.30 km) The natural vegetation of these areas is an open to include a sufficient number of records to offset the 10–20 m high savannah woodland dominated by partly de- stochastic variation of bird sightings. They were driven ciduous trees (Burkea, Crossopteryx, Piliostigma, Isoberlinia, slowly (,50 km h-1) by car, with two non-driving Combretum, Pterocarpus, Afzelia). Gallery forests along observers, with stops to search for raptors at lookouts permanent or seasonal streams include large trees (Khaya, and to identify distant birds, in fine weather from after Kigelia, Terminalia, Anogeissus) with a denser understorey sunrise to before sunset. Most transects were driven (Vitex, Cola, Prosopis). Locally baobabs (Adansonia) are twice in the same year, and were used as single counts in common in grasslands, Borassus palms in floodplains, which the maximum number of individuals of each and Mitragyna in seasonally inundated zones. At the species recorded in any one passage was retained. When northern edge of the area thorny trees (Acacia, Balanites) the same transect was repeated in different seasons become frequent. The grass cover (Hyparrhenia, Andro- it was considered as two separate counts. All birds, pogon, Loudetiopsis, Pennisetum) usually reaches 1.2-1.8 m perched or flying, detected within eyesight range on during the rainy season (April-September) and is burnt either side, even during stops, were counted, using in the dry season (October-March). 10 * 42 binoculars. Age, position (using a geographical Outside protected or hunting areas the countryside positioning system), grouping, behaviour and distance is inhabited and cultivated, with only remnants of to the track of perched birds (estimated by eye after degraded woodlands. Traditionally fields of millet, training sessions) were recorded. In all 3,714 individual sorghum, maize, groundnut or yam are dotted with raptors were counted over 4,697 km of transects. large trees (Butyrospermum, Parkia, Tamarindus, Bombax, Because the objective was to assess the relative con- Acacia). During the dry season the stubble is grazed servation value of protected areas, the transects were by cattle. Because of land scarcity, fallow areas are divided into three categories: (1) National Parks (Arli, decreasing in size and duration laid to fallow. Intensive Pendjari, W) or equivalent reserve (Nazinga); (2) buffer ª 2007 FFI, Oryx, 41(3), 322–329 Downloaded from https://www.cambridge.org/core. IP address: 170.106.202.58, on 27 Sep 2021 at 16:16:35, subject to the Cambridge Core terms of use, available at https://www.cambridge.org/core/terms. https://doi.org/10.1017/S0030605307000809 324 J.-M. Thiollay areas, i.e. peripheral zones around protected areas that Density was also estimated using all 89 (1–12 per are little disturbed, 10-50 km wide, devoted to sport species) occupied vulture and eagle nests found in hunting, with few isolated fields and villages; (3) all protected areas (there were insufficient records else- other areas, cultivated and inhabited. where) and 70 (1–14 per species) additional pairs of During counts our average speed tended to be higher adults far from these nests. These were recorded within on roads outside than inside protected areas. Moreover, the maximum ESW (500 m) on either side of the transects. the latter, designed for wildlife viewing, tended to Locations from different days were excluded when they follow gallery forests along rivers and open grasslands were ,2 km from each other This density was extrap- and pools, i.e. usually the richest areas for raptors. These olated to the total area of the protected areas. factors could have resulted in an overestimate of the abundance of some species in protected areas, or of population size when extrapolated to entire parks. Results Conversely, the detection of raptors may have been Number of species higher in cultivated areas, which are more open than natural woodlands. The behaviour and detectability of Overall, 37 species were recorded in two or more study raptors change with time of day but the three habitat areas (Table 1). Four additional species were seen only categories were surveyed throughout the day and there once (palm-nut vulture Gypohierax angolensis, African was no overall difference between them in the daily cuckoo hawk Aviceda cuculoides, short-toed snake eagle distribution of counts.