Context
The Nachtigal Hydropower Project is located on the Sanaga River in Cameroon within the Northern Congolian Forest Savanna Mosaic ecoregion and Africa Freshwater ecoregion, as these regions are defined by WWF. The project is not located in any of Conservation International’s Biodiversity Hotspot or High Biodiversity Wilderness Area, or within an Endemic Bird Area. There are no Protected Areas or Internationally recognized areas for biodiversity within or near the project area, either upstream or downstream. The area consists of humid semi-deciduous forest and savanna, with many areas of savanna and forest mosaic. Much of the forest areas have evidence of human intervention or consist of secondary forest. No invasive alien species were noted in the project area, except for water hyacinth, which is a common risk in hydropower reservoirs. This risk is addressed under PS3.
Several Ecosystem Services were identified within the project area, including fishing, sand mining, traditional medicines, wood collection, bushmeat hunting, and freshwater. Mitigation actions to address project impacts on these ecosystem services are outlined in the Biodiversity Action Plan (BAP) through community conservation actions (COPAL, see more details below under Terrestrial Fauna and Flora) and are also addressed under PS5.
In January 2016, the flow rate of the Sanaga River was significantly altered by the commencement of operation of the Lom Pangar regulation reservoir located about 250 km upstream of Nachtigal HPP. The Sanaga’s flow rate has been changed to an average minimum flow of 650 m3/s, which is much higher than the minimum natural flow rates on the Sanaga which were often below 300 m3/s. Due to the likely impacts of this change on aquatic biodiversity communities, the aquatic habitat within the project area is classified as Modified Habitat.
Terrestrial Habitat, Fauna and Flora
Terrestrial Habitats within the project area consist of humid semi-deciduous forest and savanna ecosystems. Terrestrial Habitats in the DUPs were classified as 1119 ha Natural Habitat and 262 ha Modified Habitat (per PS6). Much of the forest areas have evidence of human intervention or consist of secondary forest. The project will impact 675 ha of Natural Habitat including 524 ha of forest and 151 ha of savanna. No terrestrial biodiversity values qualify as Critical Habitat.
As a complementary study to the ESIA, the project commissioned an inventory of the flora and fauna in 2014 to determine if endangered, endemic or migratory species are present in the project area of influence. The inventory identified several priority biodiversity values (but none that trigger Critical Habitat) including giant pangolin (Smutsia gigantean – VU), common pangolin (Phataginus tricuspis – VU), hippopotamus (Hippopotamus amphibious – VU), dwarf crocodile (Ostealeamus tetracus – VU), Bannerman’s turaco (Tauraco bannermani – EN), Martial Eagle (Polemaetus bellicosus – VU), and the terrestrial plant Hymenodictyon pachyantha – EN (Cameroon IUCN Red List Assessment). No migratory species were identified in the area.
The project developed an ESMP and a Biodiversity Action Plan (BAP) to outline mitigation measures to avoid and minimize predicted negative impacts on terrestrial biodiversity, and to deliver No Net Loss where feasible for terrestrial Natural Habitat and its terrestrial biodiversity values. Mitigation actions include a biodiversity offset where NHPC will provide financial support to the Mpem et Djim National Park (80 km North from the project site) and the community forest Coopérative des Paysans de la Lekié (COPAL) (20 km East from the project site) during construction and the 35-year operation concession. These sites were selected after consultation with national and local stakeholders, including government agencies (MINFOF-Direction de la Faune et des Aires Protégées, MINEPDED-Service Biodiversité, Director of Mpem et Djim National Park), NGOs (WWF, UICN), international cooperation organizations (CIRAD, CIFOR, GIZ), and local communities (COPAL). NHPC will provide support to the Mpem et Djim National Park for anti-poaching activities, control of illegal logging, and restoration of 100 ha of forest degraded by illegal logging activities. Additionally, the following management activities are proposed for enhanced protection and restoration of biodiversity values in COPAL: (i) protection of a core of 250 ha inside a non-degraded 1150 ha of forests initially intended to be logged; (ii) protection of 250 ha of riparian vegetation; (iii) creation of 200 ha of agroforestry plantations acting as buffer zones around the two protected areas; and (iv) enrichment plantations in 1,100 ha. To ensure the effectiveness of the BAP, NHPC has engaged qualified experts to (i) detail the activities to be implemented in the Mpem et Djim National Park and COPAL; (ii) define the biodiversity monitoring and evaluation plan; (iii) monitor forest cover in the project area of influence, the Mpem et Djim National Park and COPAL during the project life.
Aquatic Habitat, Fauna and Flora
Aquatic Habitat within the study area (upstream and downstream) covers 663 ha.The river is classified as Modified Habitat due to the extreme changes in minimum flow rate resulting from operation of the Lom Pangar regulation reservoir upstream of the project (see more on this below under Aquatic Plants). The construction of the dam will i) transform 264 ha of free flowing river (lotic ecosystem) into a slow flowing reservoir habitat (lentic ecosystem), ii) dewater 198 ha of river in the right bank reaches downstream of the dam (which will receive water only between September and November when the river flow is above Nachtigal HPP’s design flow of 980 m3/s), and iii) reduce the flow rate in 179 ha of river in the left bank reaches downstream of the dam (EFlow from 25 to 47 m3/s). The presence of a 15 m high weir will also block fish movement between downstream and upstream of the project.
Dams hold back sediments resulting in the erosion of the downstream riverbed and riverbanks many kilometers below the dam, which may result in the loss of important habitat for fish species to complete their life histories. Nevertheless, a complementary study to the ESIA conducted by Artelia in 2014, determined that sand mining activities in the area have already depleted sand stocks and the area is already degraded in terms of sand availability for the maintenance of fish and invertebrate habitats.
Fish
An ichthyologic study to identify fish species composition and abundance was performed from January to October 2014. Monthly semi-quantitative fish catches were performed at 12 stations along the Sanaga river, and one-time catches were performed at 9 stations along the Sanaga’s tributaries. The taxonomic inventory identified 65 fish species and the bibliographic research identified an additional 21 species as potentially present in the area. Out of the 86 species, 13 are endemic to the Sanaga riverand among them three are endangered or vulnerable. Discrete Management Units (DMU) for these 13 fish species were established corresponding to approximately 20% of the Sanaga watershed. Based on the presence and abundance of the species in the DMU, the project has determined (and IFC concurs) the DMU as Critical Habitat (CH) for the following 9 fish species: (i) Labeobarbus mbami – EN,(ii) Chrysichthys longidorsalis – VU, (iii)Marcusenius sanagaensis – VU, (iv)Doumea sanaga – LC, (v) Labeo nunensis – LC, (vi) Labeo sanagaensis – LC, (vii) Synodontis rebeli – LC, (viii) Campylomormyrus phantasticus – LC, and (ix) Petrocephalus similis – LC.
No anadromous (migrate from the sea up into freshwater to spawn) or catadromous (migrate from freshwater down into the sea to spawn) fish have been identified. On the other hand, potamodromous species (migrate laterally or longitudinally along the river) are numerous. Among the CH species there is the suggestion that Labeobarbus mbami – ENmigrates from the Sanaga to the tributaries to spawn in flooded forests. Other CH fish with potamodromous migratory behavior are Synodontis rebeli – LC (adults migrate to tributaries to spawn), Marcusenius sanagaensis – VU(adults search breeding areas in lotic environments), and potentially Chrysichthys longidorsalis – VU.
To mitigate the project’s construction impacts on aquatic habitat and fish, NHPC will (i) avoid the degradation of fish habitat through the prevention of sediment input and untreated effluents into the Sanaga river during construction; and (ii) minimize fish mortality during construction through fish rescue from dewatered river sections. To mitigate for the operation impacts on aquatic habitat and fish, the project will implement the following mitigation measures: (i) maintenance of an environmental flow (EFlow) between 25 and 47 m3/s in the left bank (179 ha of aquatic habitat) of the dewatered river reach downstream of the dam; (ii) restoration of 156 km of Sanaga tributaries (corresponding to approximately 203 ha of aquatic habitat); (iii) enhancement of 395 km of river reaches inside the Mpem et Djim National Park (corresponding to 408 ha of aquatic habitat); and (iv) implementation of an awareness program to reduce the use of ichthyotoxic products for fishing inside the Mpem et Djim National Park. NHPC will engage partners with adequate expertise for the implementation of these measures.
A feasibility analysis for the construction of a fish passage at the dam concluded that a fish ladder would be a challenge due to the high number of fish species with varying migratory inclinations and abilities. In addition, the waterfalls of Nachtigal located just downstream from the proposed dam are already a natural barrier for upstream migration of most species. The report concludes that the optimal mitigation action to maintain the genetic mixing of the various species is a catch-and-release program. International experts have been retained by NHPC to test the use of electrofishing and develop a fish catch-and-release program. NHPC shall provide the results of the experimental electrofishing, details of the proposed catch-and-release program, and assess program effectiveness and efficiency to achieve long term genetic mixing of fish stocks upstream and downstream of the proposed dam (see ESAP action no. 25). Additionally, NHPC shall appoint an independent fish and biodiversity expert for at least 3 years to evaluate if the catch-and-release program is sufficient to maintain the genetic diversity of the fish populations and maintain the migratory fish populations. The independent fish expert shall also provide ongoing advice on the Biodiversity Action Plan for Fish (BAP-Fish) and monitoring of Net Gainfor CH fish species. (ESAP action no. 26).If the catch-and-release program is deemed to be insufficient, NHPC will design and build a fish passage before commissioning of the dam.
The mitigation measures described above will be implemented to achieve Net Gain for the 9 CH fish species. These measures are described more fully in the BAP-Fish that has been disclosed together with this ESRS.
The BAP-Fish includes detailed studies to develop a robust monitoring programto monitor the impacts of Nachtigal HPP on the 9 CH fish species and the effectiveness of mitigation and habitat restoration measures. The monitoring program includes indicators of fish species composition and abundance and fish habitat quality. Results of the analysis of these data will be used to quantify net gain for the 9 CH fish species. Data collection will commence before construction of the dam and will extend throughout the 35-year operation concession. The monitoring program will include an updated biophysical baseline (dry and wet season) to (i) differentiate the impacts of Nachtigal HPP from the impacts of Lom Pangar HPP which started operating in 2016 (see ESAP action no. 27); and (ii) determine the presence and abundance of CH fish species in the Mpem et Djim National Park and targeted tributaries. In addition to the BAP-Fish, NHPC will provide financial support to the Ministry in charge of fisheries to control the access of local fishermen to the reservoir.
Aquatic Flora
The 2014 inventories of flora and fauna also revealed the presence of three aquatic plant species that are listed on the Cameroon IUCN Red List: Marsdenia abyssinica – Critically Endangered (CR), Ledermanniella sanagaensis – CR, andLedermanniella thalloidea – Endangered (EN). In addition to their endangered status, both Ledermanniella species are endemic to Cameroon. The DMU for two of the aquatic plant species has been determined as Critical Habitat: (i) Ledermanniella sanagaensis – CR, and (iii) Ledermanniella thalloidea – EN. Particularly important is the occurrence of Ledermanniella sanagaensis, whose distribution is restricted to the project area based on current evidence (Tier 1 Critical Habitat).
To better understand and mitigate impacts on the two Critical Habitat aquatic plant species, NHPC has retained local and international plant experts to conduct a detailed inventory and design the mitigation measures. Ledermanniella is a genus of flowering plants in the family Podostemaceae; there are at least 44 species, all native to tropical Africa. Ledermanniella is an aquatic plant that requires a period of emersion for its reproductive cycle. Emersion of the Ledermanniella in the project area used to occur between the months of January and April when the flow of the Sanaga river was below 375 m3/s (before flow regulation by Lom Pangar).
The project commissioned studies by a local plant expert to inventory the stations (sites) of Ledermanniellain the area impacted by the project and study its phenology in 2015 (Pre-Lom Pangar HPP operation), and then in 2016 and 2017 (Post-Lom Pangar HPP operation). In 2015, the inventory documented 35 stations of Ledermanniella (both species) within the project area. In January 2016, the Lom Pangar regulation reservoir located upstream from Nachtigal started partial commissioning. Between January and April 2016 Lom Pangar released an average minimum flow of 450 m3/s, and the flow was below 375 m3/s only during two weeks. Field surveys conducted from February to March 2016 were able to locate only five (5) Ledermanniella stations, all the others being submerged. As Lom Pangar is now fully operational, releasing a minimum flow of 650 m3/s, the last field survey conducted in January 2017 was not able to locate any of the previously identified Ledermanniella stations.
Operation of Nachtigal HPP will modify the flow rate in a way that will benefit the Ledermanniella species. Nachtigal HPP will be able to replicate the alternation of periods of immersion and emersion in the dewatered section of the river below the weir, which may allow the Ledermanniella to complete its reproductive cycle again. This is predicted by experts to allow the survival of 12 Ledermanniella stations located on the left bank of the dewatered section that will receive an EFlow of 25-47 m3/s, as long as the Ledermanniella is able to survive four to five years of total submersion. Other mitigation measures to be implemented by the project include the transplant of Ledermanniella stations located in the right bank of the dewatered section that will not receive the EFlow (or from the Mbam river in case Sanaga stations disappear) to the left bank of the dewatered stretch or tributaries of the Sanaga with adequate conditions.
While the feasibility of Nachtigal is dependent on Lom Pangar, this reservoir serves not only Nachtigal but two existing and six additional planned HPPs. Therefore, as the changes in the quantity and timing of downstream water flow, and the consequent modification of the Ledermanniella habitat, were not caused by NHPC or by the GoC in anticipation of this specific project, Lom Pangar is not considered an associated facility under IFC PS 1. Thus NHPC is required to achieve Net Gain with regards to the number of Ledermanniella stations that still emerge despite the flow regulation effect by Lom Pangar. IFC and NHPC have agreed that the project shall achieve Net Gain with respect to the stations identified in the 2017 field surveys. IFC considers therefore that the proposed mitigation measures described above are adequate to achieve Net Gain with regards to the loss of Critical Habitat for Ledermanniella sanagaensis and Ledermanniella thalloidea. Additional mitigation measures will also include the collection and conservation of seeds in Cameroon at the National Herbarium and at the Botanical Conservatory in Brest, France. NHPC has identified international experts to act as advisors to increase the likelihood of success of all mitigation measures. Mitigation measures and the monitoring plan are described more fully in the Biodiversity Action Plan for Ledermanniella (BAP-Ledermanniella) that has been disclosed together with this ESRS. The BAP-Ledermanniella shall be regularly adapted based on the monitoring results.