The timneh parrot Psittacus timneh, formerly considered conspecific with the grey parrot Psittacus erithacus, is endemic to five countries in the western Upper Guinea forests of Africa: from Guinea-Bissau and Guinea through Sierra Leone and Liberia to western Côte d'Ivoire (del Hoyo & Collar, Reference del Hoyo and Collar2014). Trapping for the caged bird trade, combined with high rates of forest loss, has caused a major decline of the species across its range (Martin et al., Reference Martin, Perrin, Boyes, Abebe, Annorbah and Asamoah2014). Although both Psittacus species have recently been recategorized as Endangered on the IUCN Red List (BirdLife International, 2018b), P. timneh has the smaller range and population. It has probably disappeared from most of its range (Clemmons, Reference Clemmons2003; Martin et al., Reference Martin, Perrin, Boyes, Abebe, Annorbah and Asamoah2014), but a handful of stronghold areas, such as the Bijagós Archipelago in Guinea-Bissau (Lopes et al., Reference Lopes, Martin, Henriques, Monteiro, Cardoso and Tchantchalam2018a,Reference Lopes, Martin, Henriques, Monteiro, Regalla and Tchantchalamb) and Sapo National Park in Liberia (Freeman et al., Reference Freeman, Dami and Molokwu-Odozi2019), may retain fairly healthy populations of the species (Dändliker, Reference Dändliker1992; Clemmons, Reference Clemmons2003; Lopes et al., Reference Lopes, Martin, Henriques, Monteiro, Regalla and Tchantchalam2018b). Recent surveys in Côte d'Ivoire, however, have indicated dramatic declines across the country, including in the most important forest protected area, Taï National Park (Marsden et al., Reference Marsden, Loqueh, Takuo, Hart, Abani and Ahon2013; Martin et al., Reference Martin, Perrin, Boyes, Abebe, Annorbah and Asamoah2014).
The Gola Rainforest National Park is the Sierra Leonean portion of the 1,500 km2 Gola Transboundary Peace Park shared with Liberia. Since the 1990s the National Park has been managed by the national government in partnership with the UK Royal Society for the Protection of Birds, and in 2015 became West Africa's first verified REDD+ project (Barca et al., Reference Barca, Turay, Kanneh and Tayleur2018b). As such, it constitutes one of the largest and best-managed remnants of the Upper Guinean forest in West Africa. Because of the Park's size and management, and because it lies at the heart of the range of P. timneh, it was believed to host a significant proportion of the species' global population (BirdLife International, 2018b).
Gola Rainforest National Park (Fig. 1) is dominated by lowland moist evergreen high forest, with an annual rainfall of c. 3,000 mm, mostly falling in a single wet season from May to October (Lindsell et al., Reference Lindsell, Klop and Siaka2011). The Park currently consists of two main forest blocks (Gola South, c. 260 km2, and Gola Central, c. 386 km2) and a smaller sector (Gola North, c. 54 km2), surrounded by a 4-km buffer zone (c. 770 km2). Formal agreements with most of the local chiefdoms in the buffer zone support small-scale agriculture, agroforestry and other local livelihood activities aimed at reducing intensive exploitation of the forest. However, illegal gold and diamond prospecting, plus potential concessions to oil palm companies, are an ongoing threat (BirdLife International, 2018a).
From 20 March to 21 April 2018, SV spent 114 hours across 22 days surveying for P. timneh in and around Gola Rainforest National Park, including the two main blocks, with 70.8 hours (across 12 days) inside the Park and 43.2 hours (across 16 days) in the buffer zone. Walking surveys occupied 85% (96 hours) of this time and observations from fixed points 15% (18 hours). Only one site, Gola South, was surveyed twice from the Sileti guest house, for 60 minutes each time. As dense vegetation prevented safe access and because of time constraints, surveys were conducted only along forest trails (63% of survey hours) or transects cut for a previous study of primates (37% of survey hours). Surveys were at all hours of the day from morning to dusk (but were suspended during rain or strong winds), and all P. timneh heard and seen were counted. Encounter rates (groups/h) were subsequently computed for both the National Park and its buffer zone, and from these numbers density was inferred using the calibration in Marsden et al. (Reference Marsden, Loqueh, Takuo, Hart, Abani and Ahon2015). A number of factors (e.g. detectability, observer skill, seasonal variation in group size, local variability in bird mobility) may affect the precision of estimates calculated with this method, resulting in progressively larger confidence intervals at higher densities.
During surveys P. timneh was encountered 20 times (on 11 of 22 days; eight times in Gola Rainforest National Park, 12 times in the buffer zone), with a total of 38 individuals recorded (16 in the National Park, 22 in the buffer zone); the Nomo Faama Chiefdom, in the buffer zone, accounted for most encounters and individuals (Table 1). Parrots were only recorded in small groups (mean 1.9 ± SD 0.6). Overall encounter rate was 0.2 groups/h (0.1 in the National Park, 0.3 in the buffer zone), which approximates to 1 individual per km2 (95% CI 0–8) in the National Park, and 3 per km2 (95% CI 0–10) in the buffer zone.
This study, although brief, is the most extensive survey of P. timneh conducted in and around Gola Rainforest National Park. We found densities much lower than those of reasonably healthy populations of the congeneric grey parrot (Marsden et al., Reference Marsden, Loqueh, Takuo, Hart, Abani and Ahon2015), although they were similar to the 2.2 individuals per km2 found in the Liberian portion of the Transboundary Peace Park where, however, a flock of 70 birds was seen on one occasion (Marsden et al., Reference Marsden, Loqueh, Takuo, Hart, Abani and Ahon2013, Reference Marsden, Loqueh, Takuo, Hart, Abani and Ahon2015). The Gola Rainforest National Park is considered a probable stronghold of the species and has benefited from long-term, effective conservation management, as manifest by its extensive well-preserved forest and healthy populations of frugivore species such as the Vulnerable yellow-casqued hornbill Ceratogymna elata (Valle et al., Reference Valle, Collar and Marsden2018) and Endangered Upper Guinea red colobus Piliocolobus badius (Barca et al., Reference Barca, Tayleur and Turay2018a). We do not know whether P. timneh has always had a low density in the National Park or has suffered recent declines, but the sparse evidence points to the latter. Anecdotal reports of large numbers of birds formerly roosting in the Nomo Faama Chiefdom (PD, pers. obs.) and of previous heavy trapping suggest that harvest for the pet trade may have played a major role in reducing the area's population. We found no indication that parrots are currently trapped there for the pet trade. Surveys in 2006 yielded similarly low encounter rates (Dowsett-Lemaire & Dowsett, Reference Dowsett-Lemaire and Dowsett2007) and in 2011 P. timneh was recorded at only one locality outside the National Park, on the border with Liberia (Demey, Reference Demey2012). The highest number of encounters was recorded in the Nomo Faama Chiefdom; this could be because exploitation there is more focused on gold mining than on agriculture (i.e. disturbance and forest clearing are less extensive). There were a similar number of records in the National Park and its buffer zone, suggesting that a matrix of habitats may be beneficial for the species (Valle et al., Reference Valle, Collar, Harris and Marsden2017), although we do not yet know how the species uses each area (e.g. for feeding, roosting or nesting).
Given the large area of protected forest within Gola Transboundary Peace Park (1,500 km2) and its buffer zones, even low-density estimates (mean density 1.6 parrots per km2) indicate a reasonable population size. We suggest that the population within the Peace Park itself may be c. 2,400 individuals, with a currently unknown but perhaps substantial number in the buffer zones around the Park. However, the true population size could be smaller because of the imprecision associated with our method. There is strong evidence that the species has disappeared from the majority of its range (Martin et al., Reference Martin, Perrin, Boyes, Abebe, Annorbah and Asamoah2014), and the future for wild P. timneh rests largely in Gola, along with the Bijagós Islands, Guinea-Bissau (where there are c. 1,000 individuals: Lopes et al., Reference Lopes, Martin, Henriques, Monteiro, Cardoso and Tchantchalam2018a,Reference Lopes, Martin, Henriques, Monteiro, Regalla and Tchantchalamb) and Sapo National Park, Liberia (c. 37,000 individuals: Freeman et al., Reference Freeman, Dami and Molokwu-Odozi2019). Although it now seems likely that the global population is lower than the estimated > 100,000 (BirdLife International, 2018b), further research on the species in Liberia and Sierra Leone, within and outside protected areas, including measures to boost productivity if further evidence emerges of recent trapping, is a priority.
Acknowledgements
We thank Eric Vignot and the Parrot Wildlife Foundation for generously funding this research, Mohamed Nyallay for assistance in the field, Brima Sheku Turay and Pietro Sandini for support with logistics, Gola Rainforest National Park for permission to carry out research, and two anonymous reviewers for their valuable comments.
Author contributions
Study design and fieldwork: SV, SM; data analysis: SV, SM; writing: SV, NC, BB, SM.
Conflicts of interest
None.
Ethical standards
This research abided by the Oryx guidelines on ethical standards.