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Journal of Energy and Environmental Science Research Article 25 min read

Bird Community, Feeding Guilds and Habitat Associations Along the Proposed River Dibombe Hydropower and Transmission Line Project in Nkam and Moungo Divisions, Cameroon

Elah EM*
* Corresponding author
ISSN: 2997-6200  10.23880/jeesc-16000121  Received: April 22, 2025  Published: May 02, 2025
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Keywords
Avian Community Threatened Species Critical Habitat Hydropower Impacts Mitigation Measures
Abstract

Cameroon is endowed with rich biological and natural resources with significant ecological, economic and cultural values. Its water resource has a huge potential for energy production, and the proposed Dibombe Hydropower project aims to add 64.2 megawatts of energy on the national grid contributing to the growth of the electricity sector. To implement this project, the biodiversity as a whole and the avian community in particular on the sites will be impacted. This study was thus designed to determine the baseline community of birds as well as their habitats within the project sites and to assess potential impacts of the projects on the bird community. Points transect counts and mist nets were used. A total of 155 bird species belonging to 39 families were recorded during the survey; 104 and 111 species at the proposed hydropower site and transmission line respectively. 140(90.3%) species were resident species, 12(7.7%) were resident but partially migratory species, 2(1.3%) were palearctic migrants and 1(0.65%) were vagrants. Two globally threatened species were recorded: Yellow-casqued Wattled Hornbill Ceratogymna elata (Vulnerable) and the African Grey Parrot Psittacus erithacus (Endangered). An overall estimate of 170±7 (CI=161.36-190.91) species was obtained from Chao species richness, with 143 species along the transmission line and 113 at the hydropower project site. Rarefaction curves reached near asymptote, indicating that most of the species were detected by the survey. Dominant species were recorded from the family Pycnonotidae (17 species) while 11 families recorded just one species; Phalacrocoracidae, Scopidae, Threskiornithidae, Anatidae, Phasianidae, Rallidae, Burhinidae, Psittacidae, Coliidae, Corvidae and Viduidae. The most dominant feeding guild was the omnivores (26%), while carnivores/insectivores (2%), and carnivores (2%) represented the least feeding guilds. Given that the site is already under severe pressure from anthropogenic activities mainly agricultural encroachment, the proposed hydropower project and transmission line presents additional cumulative impacts, mainly fragmentation and loss of habitat for terrestrial birds while the dam impoundment is likely to attract more aquatic birds. Future monitoring to determine impacts and trends during and after the execution of the project is strongly recommended.

Introduction

There is an ongoing challenge in balancing economic development and environmental protection. Environmental and Social Impact Assessment thus plays a crucial role in promoting a safe environment and ensuring sustainable development. Most international financial institutions have also embraced the ESIA to ensure that their projects contribute to ‘sustainable development’. In essence, for major projects above a certain funding threshold (currently US$10 million), Equator Principal finance institutions must ensure that an impact assessment appropriate to the scale and nature of the project is provided by the applicant [1].

Economic development in Cameroon is partly hindered by insufficient supply of electrical energy despite its rich biological and natural resources with significant ecological, economic and cultural values. Its water resource has a huge potential for hydropower generation, and the proposed Dibombe Hydropower project aims to add 64.2 MW of energy on the national grid contributing to the growth of the energy sector. Hydropower generation is a renewable energy which offers excellent merits against the negative factors of carbon dioxide and other flue gases which contaminate our environment. It’s the least costly way of storing large amounts of electricity, with low cost of operation as advantages. Nevertheless, hydropower implementation comes with social, economic and ecological impacts. From an ecological point of view, the construction and operation of hydro dams and transmission lines can affect avian biodiversity in many ways, among which are habitat degradation and fragmentation, changes in hydrology, introduced species, hunting and harvesting enabled by rights-of-ways (transmission line corridor) and construction of roads.

Overhead power lines are said to have negative impacts on bird populations, mainly through collision and electrocution [2, 3]. On the other hand, power lines may provide benefits for several bird species (e.g. storks, raptors, corvids), as wires and pylons may be used as perches, hunting, solitary resting and communal roosting and nesting sites [4, 5, 6, 7]. This creates a paradox for conservation, since positive and negative impacts on the use of power lines co-exists and the estimation of impacts of these structures at population level will have to take these trade-offs into account. Also, electromagnetic pollution related to power lines has been suggested to decrease reproductive success in several species, from small passerines to storks [8].

Hydroelectric dams can block non-Volant and aquatic animal migratory pathways, introduce alien species and flood surrounding lowland habitat [9, 10]. Furthermore, dam impoundments disrupt wildlife by altering the original environment, thereby hindering wild animals and plants from thriving due to the degradation or loss of habitat [11]

ESIA is a multidisciplinary study involving several taxa amongst which are birds. Birds are good indicator species because they are ecologically versatile and thrive in all kinds of habitat as herbivores, carnivores and omnivores. Their presence is an indication of healthy ecosystem or habitat. The diet of bird species represents a fundamental aspect of its ecological niche and dietary adaptations play an important role in understanding the ecology and evolution of communities [12]. Birds also play an important role in ecosystems as potential pollinators, scavengers and bio- monitors in controlling insect pests and also as excellent ecological indicators [13].

Cameroon like many other countries around the world has institutionalized the ESIA process. As part of the process, baseline data collection is crucial in understanding the existing environmental conditions before a project is implemented. This study was thus designed to establish a baseline of the avian community, their feeding guilds and habitat associations within the project sites and to highlight potential environmental effects of the proposed project on the avian communities which are vital at the outset, for potential impacts can be earmarked and mitigation measures considered.

Materials and Methods

Study Site

Berkley Energy Cameroon has proposed to construct and operate a run-off-river Hydro Power Plant (HPP) on the Dibombe River found in Sole village, Yabassi subdivision in the Littoral region of Cameroon. The site is located between latitude N: 514870 and longitude E: 586590 at an altitude of 101 m to latitude N: 510000 and longitude E: 589000 at an average altitude of 144 m along the river bank to the Mabombe bridge located 8.5 km from the power house location. The proposed transmission line runs from the power house location downstream in Sole village through a corridor of 10.8 km long and 50 m wide to the SONATREL (Société Nationale de Transportation de l’Electricite) substation in Njombé-Penja in the Mungo division. The vegetation around the study area falls within the lowland evergreen rainforests zone of the Congo Basin, consisting of a mosaic of patches of intact forests, secondary forest and plantations. The forest type belongs to the Lower Guinea region of endemism or phytochoria with abundance of leguminous trees (Fabaceae).

The climate in this area is equatorial with eight months of rainfall (April to November) with an average monthly rainfall > 600 mm and four months of dry season with little or no rainfall (December to March) with an average monthly rainfall < 100 mm. Average annual rainfall is 3702 mm while the average annual temperature is 26.5 °C. Agriculture is the main source of subsistence for the local population alongside fishing in the Dibombe River. Some of the crops cultivated in Solé village and other villages along the proposed transmission line include; Palms, cocoa, banana, white pepper and food crops. The soil of the study area is very high in sand and clay contents Figure 1.

Figure 1: Map of study area showing the proposed project site along Dibombe River.
Click to enlarge
Figure 1: Map of study area showing the proposed project site along Dibombe River.

Sampling Design

Six transects where established perpendicular to the River, from the downstream power house location to the intake location and labelled T1 to T6 (Figure 2). The transects were set 1 km apart and each varied between 1 to 1.2 km long depending on the meandering of the river. Another transect labelled T7 extended along the river bank from the intake location to the main road at Mabombe bridge measuring approximated 3.5 km (Figure 2). The transects cut across different habitat types such as farmlands, plantations (cocoa, palms, white pepper, plantains), farm bushes and secondary riverine forest all the way to the river. A transect of 11 km was established along the transmission line corridor, from the power house location to the existing SONATREL substation in Njombé-Penja. Sampling stations were located 200 m apart along each transect. Transects and survey stations were established using a GPS Garmin 60C. Figure 2 below illustrates the sampling design used in this study.

Figure 2: Map illustrating the sampling design with transects (T1 to T7) in black bold lines.
Click to enlarge
Figure 2: Map illustrating the sampling design with transects (T1 to T7) in black bold lines.

Point Transect Count: Field work was conducted in March 2021 at the proposed hydropower construction site and in August 2021 along the proposed transmission line. Surveys were carried out during early mornings from 7:00 am to 11:30 am and later in the evening from 2:30 to 5:30 pm. At each station all birds seen or heard within a radius of 50 meters were identified and recorded for ten minutes duration. In addition, opportunistic observations of birds while walking between stations were added to make a comprehensive checklist of birds for the study area. The abundance of each species per station was also recorded. Binoculars (Verano 10X42 BGA, PC OASIS WP Field 6.0°) were used to visualize details of physical characteristics (colour, shape and size) and the birds were identification using Borrow, et al. [14]. A GPS was used to record the coordinates at the start and end point of each transect as well as survey stations along the transects.

Mist Netting: Mist nets were used especially in forest areas along the established transects to target cryptic species that may be omitted during transect counts. Three mist nets (each 3 m high by 12 m long) of 16 mm mesh size, capable of trapping small and medium size birds were established towards the end of each transect within the river bank forest. Smaller branches and scrubs where sometimes cut in order to ease the installation of the mist nets along the transect. These nets where observed every 45 minutes from it set up time at 8:00 am right up to 5:00 pm when it was removed and the different bird caught where identified, recorded and photographed. The three nets were installed along one transect per day.

Feeding Guilds: The feeding guilds for this study follow Birds of Western Africa by Borrow and Demey (2014): carnivores (CV), carnivores/insectivores (CVIS), frugivores (FV), granivores (GV), insectivores (IS), insectivores/frugivores (ISFV), insectivores/granivores (ISGV), insectivores/piscivores (ISPV), nectarivores (NV) and omnivorous (OV).

**Statistical analyses**

Data was analysed using R software version 4.1.0 (R Core Team, 2021). The following add-ons packages were used: iNEXT (Hsieh et al., 2016) libraries for interpolating and extrapolating species diversity; readxl [15] libraries for reading excel files into R; prettyR [16] libraries for descriptive statistics; ggplot2 [17] for plotting graphs. Significant testing was done at 5% probability.

The avifauna diversities were computed and expressed in the most unified diversity of the Hill numbers with orders (q=0, q=1, q=2) [18, 19], which integrate both species richness and relative abundance. This diversity is defined mathematically [20] as:

$$q^D = \left( \sum_{i=1}^{s} p_i^q \right)^{1/(1-q)}$$

Where, S is the number of species in the assemblage, and the relative abundance of the $i^{th}$ species is Pi (i=1, 2, ..., S). The parameter q is an integer (0≤q≤2) determining the sensitivity of the measure to the relative frequencies. When q = 0, 0D is simply species richness; as q tends to 1,1D is the exponential of the familiar Shannon index, known here as Shannon diversity:

$$1^D = \lim_{q \to 1} q = \exp\left(-\sum_{i=1}^{s} p_i \log p_i\right)$$

When q = 2, 2D becomes the inverse of the Simpson diversity:

$$2^D = 1/\sum_{i=1}^{s} p_i^2$$

With q=0, the diversity is of all the species; with q=1 the diversity is of “typical” species; and with q=2, the diversity is of abundant species.

We also assessed species diversity from how equitably or evenly the relative abundances of species were distributed (Carlo H. R. H, 1998) using the Pielou’s evenness or equitability (J) index given as (Carlo H. R. H, 1998):

$$J = H/\ln(S)$$

Where, S is the number of species and H is the Shannon–Weaver index (H)

**Results**

A total of 155 bird species belonging to 39 families were recorded during the survey; 104 species at the proposed hydropower construction site and 111 species along the proposed transmission line. Overall, the most dominant species were recorded from the family Pycnonotidae (17 species, 10%) while 11 families recorded just one species; Phalacrocoracidae, Scopidae, Threskiornithidae, Anatidae, Phasianidae, Rallidae, Burhinidae, Psittacidae, Collidae, Corvidae and Viduidae representing 0.6% each. Two globally threatened species were recorded: African Grey Parrot *Psittacus erithacus* (Endangered) and the Yellow-casqued Wattled Hornbill *Ceratogymna elata* (Vulnerable). Of these species, 140(90.3%) species where resident species, 12(7.7%) species where resident but partially migratory species, 2(1.3%) species where palearctic migrants and 1(0.65%) where vagrants.

**Species Richness and Diversity of the Sites**

From the randomised rarefaction and extrapolation curve, the overall estimate of Chao species richness in the areas was 170±7 (CI=161.36 - 190.91), with 91% of the total species expected to be found in the study site caught by our sampling effort (observed richness =155). The curves for species richness (q = 0) reached asymptote for an estimated 113 species for the hydropower construction site and an estimated 143 species for the transmission line site (Figure 3). For an extrapolated random sample of 1000 individuals, both the rare species (indicated by q=0 curve) and common/typical species (indicated by q=1 and q=2 respectively) would all be detected in the project site, whereas only the common/typical species would all be detected in the transmission line site. Irrespective of the site, sampling was sufficiently adequate as the rarefaction curves have reached near asymptote; indicating, therefore, that most of the species were detected by the survey.

Figure 3: Average randomized rarefaction (solid line) and extrapolation (dotted line) curves showing species diversity, based on the three Hill measurements (q=0, richness; q=1, Shannon; and q=2, Simpson), for a unit increase in sample effort (number of individuals) in the two avifauna assemblages (Hydropower project site = Project; Transmission line corridor=Transmission), along with 95% confidence intervals based on a bootstrap method with 200 replicates.
Click to enlarge
Figure 3: Average randomized rarefaction (solid line) and extrapolation (dotted line) curves showing species diversity, based on the three Hill measurements (q=0, richness; q=1, Shannon; and q=2, Simpson), for a unit increase in sample effort (number of individuals) in the two avifauna assemblages (Hydropower project site = Project; Transmission line corridor=Transmission), along with 95% confidence intervals based on a bootstrap method with 200 replicates.

Figure 3: Average randomized rarefaction (solid line) and extrapolation (dotted line) curves showing species diversity, based on the three Hill measurements (q=0, richness; q=1, Shannon; and q=2, Simpson), for a unit increase in sample effort (number of individuals) in the two avifauna assemblages (Hydropower project site = Project; Transmission line corridor=Transmission), along with 95% confidence intervals based on a bootstrap method with 200 replicates.

Results on the Shannon and Simpson Indices for Both Sites

The relative abundances of bird species in both (project and transmission line) sites were similar and evenly distributed (JProject site = 0.870 and JTransmission line site = 0.869 respectively).

Relative Abundance of Feeding Guilds

The major dietary guilds were insectivore (IS), carnivore (CV), omnivore (OV), nectarivore (NV), granivore and frugivore (FV). The other dietary guilds were carnivore/ insectivore (CVIS), insectivore/granivore (ISGV), insectivore/ frugivore (ISFV), insectivore/piscivore. The highly dominant dietary guild was omnivore (26%) followed by insectivore (18%) and directly by Insectivores/Granivores (ISGV) (12%) and Insectivorous/frugivores (ISFV) (12%) while the guild with the least number of species in the area were carnivores (CV) (2%), carnivores/insectivores (CVIS) (2%) and insectivores/piscivores (ISPV) (3%) Figure 4.

Figure 4: Dietary guild structure of avifauna in the study site during study period (March to August 2021).
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Figure 4: Dietary guild structure of avifauna in the study site during study period (March to August 2021).

Habitat Associations

The vegetation structure was similar in both sites but with different composition; in the project site we had, big trees (33.1%, n=1195), shrubs (26.9%, n=970), small trees (21.9%, n=789) and herbs (18.1%, n=655); while in the transmission line site we had, small trees (12.1%, n=847), big trees (20.9%, n=1472), shrubs (31.3%, n=2200) and herbs (35.7%, n=2510).There was a significant difference in the abundance of the different vegetation types within both sites: Project site (𝑋2 = 182.05, df = 3, 𝑃 < 0.001) and transmission line corridor (𝑋2 = 951.82, df = 3, 𝑃 < 0.001) as a result a difference in avian richness and composition, with the project site being more diverse in species than the transmission line site since within the project site, big trees were the most abundant while herbs were the least vegetation type; conversely, herbs were the most abundant vegetation type in the transmission line site while small trees were the least abundant vegetation type as illustrated in Figure 5 below.

Figure 5: Overlaid bar plots showing the vegetation profile (BT=Big trees, ST= small trees) with the error bars representing to the 95% confidence intervals.
Click to enlarge
Figure 5: Overlaid bar plots showing the vegetation profile (BT=Big trees, ST= small trees) with the error bars representing to the 95% confidence intervals.

Three main ecologically degrading human activities were identified in the study area: farming, logging and bushfire, all of these activities directly affecting the intact forest through habitat lost, where up to 10% of the Dibombe river surrounding forest is affected by bushfire mainly done by farmers to facilitate farm clearings and another 7% by logging activities use for building houses and wood for cooking in traditional kitchens. Farming being the principal activity of the inhabitants surrounding these sites, 15% of the surrounding forest along the Dibombe river is lost to farming and 50% of the transmission line will be cutting across various individual farms like cocoa, plantains, white pepper, pawpaw, food crops and Banana plantation owned by PHP (plantation Haute Pendja). The diversity of the avifauna was significantly affected by local anthropogenic activities: the 95% confidence intervals for the corresponding rarefied- extrapolated curves do not overlap (See Figure 6). With the highest asymptote for the three Hill measurements (q=0, q=1 and q=2), the site with farming activities was the most diverse in species (richness=158±12.91, Shannon index=4.27, Simpson index=0.978) whereas the site with bushfire had significantly the least species diversity (richness=61±9.69, Shannon index=3.675, Simpson index=0.961)). Estimation for Logging was 111±13.66 species (Shannon index=4.227, Simpson index=0.977). Notwithstanding, bird detection (sampling effort) was more efficient in the farmland than elsewhere as indicated by the asymptote of the rarefaction curve.

Figure 6: Average randomized rarefaction (solid line) and extrapolation (dotted line) curves showing species diversity, based on the three Hill measurements (q=0, richness; q=1, Shannon; q=2, Simpson), for a unit increase in sample effort (number of individuals) within the three avifauna assemblages (bushfire, farming and logging lands), along with 95% confidence intervals based on a bootstrap method with 200 replicates.
Click to enlarge
Figure 6: Average randomized rarefaction (solid line) and extrapolation (dotted line) curves showing species diversity, based on the three Hill measurements (q=0, richness; q=1, Shannon; q=2, Simpson), for a unit increase in sample effort (number of individuals) within the three avifauna assemblages (bushfire, farming and logging lands), along with 95% confidence intervals based on a bootstrap method with 200 replicates.

Figure 6: Average randomized rarefaction (solid line) and extrapolation (dotted line) curves showing species diversity, based on the three Hill measurements (q=0, richness; q=1, Shannon; q=2, Simpson), for a unit increase in sample effort (number of individuals) within the three avifauna assemblages (bushfire, farming and logging lands), along with 95% confidence intervals based on a bootstrap method with 200 replicates.

Discussion

The checklists generated at the end of the study (Table 1) shows a great diversity in terms of bird communities as well as the species population assessed in the two sites. Generally, 170 species of birds where encountered belonging to 39 families among which 86 of them falls within the Guineo-Congolian forest biome (Lowland Forests: LF). Of the 32 globally threatened bird species listed in Cameroon according to the IUCN status 2018, only three where observed within the designated study area during this survey representing 9.4%, consequently, considering criterion A1, this area can be qualified as an Important Bird Area (IBA) as it does harbor three globally threatened bird species. The sites does not qualify according to criterion A2, as it does not hold any of the restricted range species, i.e. species with a total world range less than 50.000 km2. And again, No congregational species was recorded during this survey thus the sites do not qualify under category A4 as an IBA.

FamilyScientific NameCommon NameIUCNDistributionFeeding Guild
PhalacrocoracidaePhalacrocorax africanusLong-tailed CormorantLCRpMCV
ScopidaeScopus umbrettaHamerkopLCRISPV
ThreskiornithidaeBostrychia hagedashHadada IbisLCRCVIS
AnatidaePlectropterus gambensisSpur-winged GooseLCRpMISPV
AccipitridaeMilvus migransYellow-billed kiteLCPMCV
Gypohierax angolensisPalm-nut VultureLCRCV
Dryotriorchis spectabilisCongo Serpent EagleLCRCV
Polyboroides typusAfrican Harrier HawkLCRCV
Accipiter tachiroAfrican GoshawkLC
Accipiter castaniliusChestnut-flanked
Sparrowhawk
LCRCV
Accipiter melanoleucusBlack SparrowhawkLCRCV
Urotriorchis macrourusLong-tailed HawkLCRCV
Kaupifalco monogrammicusLizard BuzzardLCRCV
Buteo rufinusLong-legged BuzzardLCRCV
Lophaetus occipitalisLong-crested EagleLCRCV
Stephanoaetus coronatusCrowned EagleNTRCV
PhasianidaeFrancolinus squamatusScaly FrancolinLCROV
RallidaeSarothrura pulchraWhite-spotted FlufftailLCRFV
BurhinidaeGlareola nuchalisRock PratincoleLCRpMOV
ColumbidaeTreron calvaAfrican Green PigeonLCRFV
Turtur tympanistriaTambourine DoveLCRFV
Turtur aferBlue-spotted Wood DoveLCRFV
Streptopelia semitorquataRed-eyed DoveLCRFV
PsittacidaePsittacus erithacusGrey ParrotENRFV
MusophagidaeCorythaeola cristataGreat Blue TuracoLCRFV
Tauraco macrorhynchusYellow-billed TuracoLCRFV
CuculidaeCuculus solitariesRed-chested CuckooLCRpMOV
Cercococcyx olivinusOlive Long-tailed CuckooLCROV
Chrysococcyx cupreusAfrican Emerald CuckooLCROV
Chrysococcyx klaasKlaas’s CuckooLCROV
Chrysococcyx capriusDidric CuckooLCROV
Ceuthmochares aereusYellowbillLCROV
Centropus leucogasterBlack-throated CoucalLCROV
Centropus senegalensisSenegal CoucalLCROV
Centropus monachusBlue-headed CoucalLCROV
ApodidaeRhaphidura sabiniSabine’s SpinetailLCRIS
Neafrapus cassiniCassin’s SpinetailLCRIS
Cypsiurus parvusAfrican Palm SwiftLCRIS
Apus affinisLittle SwiftLCRIS
ColiidaeColius striatusSpeckled MousebirdLCRFV
AlcedinidaeHalcyon malimbicaBlue-breasted KingfisherLCRISPV
Halcyon senegalensisWoodland KingfisherLCRISPV
Ceyx leconteiAfrican Dwarf KingfisherLCRISPV
Ceyx pictaAfrican Pygmy KingfisherLCRpMISPV
Alcedo cristataMalachite KingfisherLCRISPV
Ceryle rudisPied KingfisherLCRISPV
MeropidaeMerops pusillusLittle Bee-eaterLCRIS
Merops variegatusBlue-breasted Bee-eaterLCRIS
Merops albicollisWhite-throated Bee-eaterLCVIS
CoraciidaeEurystomus gularisBlue-throated RollerLCRCVIS
Eurystomus glaucurusBroad-billed RollerLCRpMCVIS
BucerotidaeTockus albocristatusWhite-crested HornbillLCROV
Tockus camurusRed-billed Dwarf HornbillLCROV
Tockus fasciatusAfrican Pied HornbillLCROV
Ceratogymna fistulatorPiping HornbillLCROV
Ceratogymna albotibialisWhite-thighed HornbillLCROV
Ceratogymna atrataBlack-casqued Wattled
Hornbill
LCROV
Ceratogymna elataYellow-casqued Wattled
Hornbill
VUROV
CapitonidaeGymnobucco bonaparteiGrey-throated BarbetLCRISFV
Gymnobucco peliBristle-nosed BarbetLCRISFV
Gymnobucco calvusNaked-faced BarbetLCRISFV
Pogoniulus scolopaceusSpeckled TinkerbirdLCRISFV
Pogoniulus atroflavusRed-rumped TinkerbirdLCRISFV
Pogoniulus subsulphureusYellow-throated TinkerbirdLCRISFV
Pogoniulus bilineatusYellow-rumped TinkerbirdLCRISFV
Buccanodon duchailluiYellow-spotted BarbetLCRISFV
Trachyphonus purpuratusYellow-billed BarbetLCRISFV
IndicatoridaeProdotiscus insignisCassin’s HoneybirdLCRIS
Indicator exilisLeast HoneyguideLCRIS
PicidaeCampethera cailliautiiGreen-backed WoodpeckerLCRIS
Dendropicos fuscescensCardinal WoodpeckerLCRIS
Dendropicos elliotiiElliot’s WoodpeckerLCRIS
HirundinidaePseudhirundo griseopygaGrey-rumped SwallowLCRpMIS
Hirundo abyssinicaLesser Striped SwallowLCRpMIS
Hirundo preussiPreuss’s Cliff SwallowLCRpMIS
Hirundo smithiiWire-tailed SwallowLCRIS
Hirundo aethiopicaEthiopian SwallowLCRpMIS
Hirundo rusticaBarn SwallowLCPMIS
MotacillidaeMotacilla aguimpAfrican Pied WagtailLCRIS
Anthus leucophrysPlain-backed PipitLCRIS
Anthus pallidiventrisLong-legged PipitLCRIS
CampephagidaeCoracina azureaBlue Cuckoo-ShrikeLCRIS
PycnonotidaeAndropadus virensLittle GreenbulLCROV
Andropadus gracilisLittle Grey GreenbulLCROV
Andropadus ansorgeiAnsorge’s GreenbulLCROV
Andropadus curvirostrisCameroon Sombre GreenbulLCROV
Andropadus latirostrisYellow-whiskered GreenbulLCROV
Calyptocichla serinaGolden GreenbulLCROV
Baeopogon indicatorHoneyguide GreenbulLCROV
Ixonotus guttatusSpotted GreenbulLCROV
Chlorocichla simplexSimple GreenbulLCROV
Thescelocichla leucopleuraSwamp Palm BulbulLCROV
Pyrrhurus scandensLeafloveLCROV
Phyllastrephus icterinusIcterine GreenbulLCROV
Phyllastrephus xavieriXavier’s GreenbulLCROV
Bleda notatusLesser BristlebillLCROV
Criniger chloronotusEastern Bearded GreenbulLCROV
Criniger calurusRed-tailed GreenbulLCROV
Pycnonotus barbatusCommon BulbulLCROV
TurdidaeStiphrornis erythrothoraxForest RobinLCROV
Alethe diademataFire-crested AletheLCROV
Alethe poliocephalaBrown-chested AletheLCROV
Neocossyphus poensisWhite-tailed Ant ThrushLCROV
Neocossyphus fraseriRufous Flycatcher-ThrushLCROV
Turdus peliosAfrican ThrushLCROV
SylviidaeBathmocercus rufusBlack-faced Rufous WarblerLCRISGV
Cisticola anonymusChattering CisticolaLCRISGV
Apalis nigricepsBlack-capped ApalisLCRISGV
Apalis rufogularisBuff-throated ApalisLCRISGV
Camaroptera brachyuranGrey-backed CamaropteraLCRISGV
Camaroptera superciliarisYellow-browed CamaropteraLCRISGV
Camaroptera chloronotaOlive-green CamaropteraLCRISGV
Macrosphenus flavicansYellow LongbillLCRISGV
Macrosphenus concolorGrey LongbillLCRISGV
Eremomela badicepsRufous-crowned EremomelaLCRISGV
Sylvietta virensGreen CrombecLCRISGV
Sylvietta dentiLemon-bellied CrombecLCRISGV
Phylloscopus sibilatrixWood WarblerLCRpMISGV
Hylia prasinaGreen HyliaLCRISGV
MuscicapidaeMuscicapa cassiniCassin’s FlycatcherLCRISGV
Muscicapa adustaAfrican Dusky FlycatcherLCRISGV
Muscicapa comitataDusky-blue FlycatcherLCRISGV
Myioparus plumbeusLead-coloured FlycatcherLCRISGV
MonarchidaeErythrocercus mccalliiChestnut-capped FlycatcherLCRIS
Terpsiphone viridisAfrican Paradise FlycatcherLCRIS
Terpsiphone rufiventerRed-bellied Paradise
Flycatcher
LCRIS
PlatysteiridaeDyaphorophyia castaneaChestnut Wattle-eyeLCRIS
Platysteira cyaneaScarlet-spectacled Wattle-eyeLCRIS
Batis poensisBioko BatisLCRIS
NectariniidaeNectarinia coccinigasterSplendid SunbirdLCRNV
Anthreptes fraseriFraser’s SunbirdLCRNV
Anthreptes rectirostrisGreen SunbirdLCRNV
Anthreptes collarisCollared SunbirdLCRNV
Nectarinia olivaceaOlive SunbirdLCRNV
Nectarinia cyanolaemaBlue-throated Brown SunbirdLCRpMNV
Nectarinia fuliginosaCarmelite SunbirdLCRNV
Nectarinia rubescensGreen-throated SunbirdLCRNV
Nectarinia adelbertiBuff-throated SunbirdLCRNV
Nectarinia chloropygiaOlive-bellied SunbirdLCRNV
Nectarinia minullaTiny SunbirdLCRNV
Nectarinia cupreaCopper SunbirdLCRNV
Nectarinia superbaSuperb SunbirdLCRNV
OriolidaeOriolus oriolusEuropean Golden OrioleLCPMOV
Oriolus nigripennisBlack-winged OrioleLCROV
MalaconotidaeDryoscopus senegalensisBlack-shouldered PuffbackLCRFV
Nicator chlorisWestern NicatorLCRFV
DicruridaeDicrurus atripennisShining DrongoLCRIS
Dicrurus modestusVelvet-mantled DrongoLCRIS
CorvidaeCorvus albusPied CrowLCROV
SturnidaeLamprotornis purpureusPurple Glossy StarlingLCPMIS
Lamprotornis splendidusSplendid Glossy StarlingLCRIS
PloceidaePloceus nigricollisBlack-necked WeaverLCRIS
Ploceus ocularisSpectacled WeaverLCRIS
Ploceus nigerrimusVieillot’s Black WeaverLCRIS
Ploceus cucullatusVillage WeaverLCRIS
Ploceus tricolorYellow-mantled WeaverLCRIS
Malimbus nitensBlue-billed MalimbeLCRIS
Malimbus malimbicusCrested MalimbeLCRIS
Malimbus scutatusRed-vented MalimbeLCRIS
Malimbus rubricollisRed-headed MalimbeLCRIS
EstrildidaeParmoptila woodhouseiRed-headed AntpeckerLCRGV
Nigrita canicapillaGrey-crowned NegrofinchLCRGV
Nigrita luteifronsPale-fronted NegrofinchLCRGV
Nigrita bicolorChestnut-breasted NegrofinchLCRGV
Nigrita fusconotaWhite-breasted NegrofinchLCRGV
Spermophaga haematinaWestern BluebillLCRGV
Estrilda melpodaOrange-cheeked WaxbillLCRGV
Estrilda nonnulaBlack-crowned WaxbillLCRGV
Lonchura cucullataBronze MannikinLCRGV
Lonchura bicolorBlack-and-white MannikinLCRGV
ViduidaeVidua macrouraPin-tailed WhydahLCRGV

Table 1: List of bird species, feeding guilds, distribution status and IUCN categorization along the proposed River Dibombe hydro

RpM= resident but partially migratory, PM= palearctic migrant, V= vagrant) Table 1: List of bird species, feeding guilds, distribution status and IUCN categorization along the proposed River Dibombe hydropower and transmission line project (LC= least concern, VU= vulnerable, EN= endangered, R=resident, While a total of 170 species of birds representing 17.6% of birds in Cameroon can be considered relatively low for a country like Cameroon with a bird species richness of 968, it should be noted that the area has no protected status and is heavily impacted by human activities thus the coming of the proposed hydropower project presents an additional cumulative impact of habitat loss for terrestrial bird and an additional habitat for aquatic birds after the construction of the dam, in a local area and within the lowland of Cameroon where avian species are unique but not particularly rich in diversity.

According to world commission on dams 2000, Hydropower is one of the most proficient technologies for energy generation, which is carbon free and produces energy continuously. Hydropower projects have impacts on the environment in general and birds in particular [21]. Change in water flow regimes, electrocution, collision, ecological differences, migratory barriers, fragmentation, degradation and loss of biodiversity are some of the identified potential ecological impacts of the proposed Dibombe HPP on bird communities within the sites while flow regulations, biotope amendment, noise reduction, use of bird friendly power lines, Flight diverters and construction of migration corridors are some of the alternative proposed actions for mitigating the negative impacts of the projects in the course of implementing Dibombe HPP. Therefore, to meet the increasing demands of energy and ensure sustainable development, the different mitigation and enhancement measures need to be incorporated at the early stage of the project lifecycle.

The effect of anthropogenic disturbance on avian communities has been highlighted in many studies [9]. From the assessment done in the project site and the transmission linecorridor on human activities, many bird species are of target to local hunters like Palm-nut Vulture (Gypohierax angolensis), African Fish Eagle (Haliaeetus vocifer), Great- blue turaco (Corythaeola cristata) and hornbills by villagers to supplement their protein source and the use of their body parts like feathers and bones for traditional purposes. Some of these species, especially hornbills, are frugivores, travelling long distances daily looking for fruiting trees, thus, placing them among the most important seed-dispersers of trees and lianas as confirmed by Holbrook, et al. [22]. This species rely heavily on intact tropical forest and large fruiting trees, their movements can expand significantly if this forest is fragmented with the transmission line corridor. Owing to the vulnerability of the hornbills to habitat fragmentation and occasional electrocution on power lines, we proposed that more fruiting trees should be planted dispersedly within the surrounding forest along the Dibombe River, and flight diverters installed all along the 10.8Km power line running from Sole village to the SONATREL substation in Njombe- penja. The loss of these species through over-hunting, bush fire, deforestation through logging, habitat fragmentation, through creation of access roads and habitat destruction for farm lands coupled with the coming of the proposed HPP and its transmission line corridor could have a significant effect on the regeneration of these sites. The direct threat to the communities of these birds is habitat degradation through farming, bush fire and logging. In areas where the degree of disturbance like the presence of plantations and farmlands was high, they were very poor in community composition of birds, A change in the vegetation on which these birds depends (that is from forest to plantations and farmlands) is been caused by clearing for agriculture and illegal logging, this is in line with Danjuma [23, 24, 25, 26, 27, 28, 29]. The neighboring villages to these sites like Sole, Mabombe, Lamba, Boneko, Njanga and Pendja depends on this forest for survival, they take advantage of the fertile soil for agriculture and also hunt some of these bird species and other animals therein for protein as well as cut down trees for building and energy. These first of all constitutes a threat for the bird communities within this area, thus the coming of the hydropower project and it’s transmission line is surfacing as a buster to further reduce this community of birds to their minimum. Insectivorous and nectarivorous birds that constitute 29% of birds on these sites decreases with an increase in the modification of their habita. This confirms that these groups of bird are vulnerable to deforestation and land use .This is the case under which the surrounding forest along the Dibombe River will be subjected tied with the coming of the hydropower project and its transmission line given that the area is already facing an enormous pressure as a result of farming and an additional pressure from poachers and loggers [30, 31, 32, 33, 34, 35].

The distribution of birds within these sites varies greatly between the project site and the transmission line corridor, just like the variation in terms of number of species and their composition, the transmission line is a linear infrastructure of 50m wide running for a distance of 10.8 Km from the intake to the SONATREL Substation in Njombe-Pendja, its cuts across so many habitats from forest to farmlands, grassland and plantations. The distribution of birds along this line is linear [36, 37, 38, 39, 40, 41]. An average of 20 bird species were recorded per station and a total number of 127 species were recorded all along the transmission line, thus as a result its implementation will warrant this birds to look for the next best available habitat along the line to ensure their continuity. With regard to the project site covering an area of almost 10.5Km², the distribution of birds within this zone is quite even and uniform holding to the fact of the uniform nature of the site too, from forest along the river back, to farm bushes, farmlands and finally to plantations. Birds within these zones have become adapted despite human disturbance in the said zone; a further disturbance by the project is simply coming as an addition to the already existing nuisance suffered by these birds and their habitats. A total of 154 resident bird species (R), 13 residents but partially migratory (RpM) species, 2 palearctic migrants (PM) and 1 vagrants (V) were recorded (Table 1). During the study period three species listed by IUCN Red List (2018) were recorded on the sites. Yellow-casqued Wattled Hornbill (Ceratogymna elata) under the ‘vulnerable’ category, Crowned Eagle (Stephanoaetus coronatus) under the “near threatened” category and Grey Parrot (Psittacus erithacus) under the ‘endengered’category, 167 of the remaining species where least concern (LC) [42, 43, 44, 45, 46, 47].

Conclusion

This study concludes that the present sites need more investigations and monitoring to bring out the complete biodiversity of birds in this area. The presence of endangered, near threatened and vulnerable birds species needs urgent monitoring to determine the trends. The findings of the present study indicate feeding guild pattern, diversity of avian fauna, their distribution status and IUCN categorization of birds within the sites. The results of this study showed that Dibombe river forest and the zone linking the forest to the SONATREL substation in Njombe-Penja is a highly productive habitat and harbors a wide range of bird species even though the area is not an intact forest crisscrossed by patches of cultivated lands at some areas by the local population for subsistence.

Acknowledgments

Authors are thankful to Pinnacle Group Cameroon for supporting the field work for this study. We are grateful to the local field guides for their collaboration and local knowledge of the site during the field work and lastly to the villagers at the site in Sole for their hospitality throughout the exercise.

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Cite this article

BibTeX
APA
RIS
@article{elah2025,
  title   = {Bird Community, Feeding Guilds and Habitat Associations Along 
the Proposed River Dibombe Hydropower and Transmission Line 
Project in Nkam and Moungo Divisions, Cameroon},
  author  = {Elah EM},
  journal = {Journal of Energy and Environmental Science},
  year    = {2025},
  volume  = {3},
  number  = {1},
  doi     = {10.23880/jeesc-16000121}
}
Elah EM (2025). Bird Community, Feeding Guilds and Habitat Associations Along 
the Proposed River Dibombe Hydropower and Transmission Line 
Project in Nkam and Moungo Divisions, Cameroon. Journal of Energy and Environmental Science, 3(1). https://doi.org/10.23880/jeesc-16000121
TY  - JOUR
TI  - Bird Community, Feeding Guilds and Habitat Associations Along 
the Proposed River Dibombe Hydropower and Transmission Line 
Project in Nkam and Moungo Divisions, Cameroon
AU  - Elah EM
JO  - Journal of Energy and Environmental Science
PY  - 2025
VL  - 3
IS  - 1
DO  - 10.23880/jeesc-16000121
ER  -