News  |  08.07.2022

Scientific field data for the next Cites Conference

The project "Updating the Vulnerability Status of Timber Species Exploited in Central Africa" will contribute to the information provided to the 19th meeting of the Conference of the Parties of CITES, which will take place from 14 to 28 November 2022 in Panama.

Scientific field data for the next Cites Conference

The Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES) aims to ensure that international trade does not threaten their survival. Similarly, the IUCN Red List provides extinction risk assessments for over 80,000 species. It has become an important tool for conservation and for informing natural resource policy and management.

In Central Africa, the last assessments of some logged tree species are often more than 20 years old. These assessments are generally poor in information on the abundance of the species, their ecology, and the changing nature of the threats they face. In addition, some assessments lack a robust scientific approach. An update of the IUCN conservation status of the main exploited species is therefore urgent. This is particularly urgent given that there are regular calls for a boycott of tropical timber without any solid arguments. Such an update would lead to the identification, on recent scientific bases, of (i) non-threatened species, whose exploitation can be continued according to current standards, and (ii) truly threatened species, whose exploitation should be more strictly controlled.

A total of 20 species were selected according to the age of their last evaluation on the IUCN red list (more than 20 years ago) as well as their economic importance estimated from the traded timber volumes. These are Aucoumea klaineana (Okoumé), Afzelia bipindensis (Doussié), Bobgunnia fistuloides (Pao rosa), Cylicodiscus gabunensis (Okan), Dacryodes igaganga (Igaganga), Entandrophragma candollei (Kosipo), Entandrophragma cylindricum (Sapelli), Entandrophragma utile (Sipo), Erythrophleum suaveolens (Tali), Erythrophleum ivorense (Tali), Lophira alata (Azobe), Milicia excelsa (Iroko), Millettia laurentii (Wenge), Microberlinia bisulcata or Microberlinia brazzavillensis (Zingana), Prioria balsamifera (Agba), Pterocarpus soyauxii (Padouk), Terminalia superba (Fraké), Testulea gabonensis (Izombé), Tieghemella africana (Douka) and Triplochiton scleroxylon (Ayous).

The IUCN Ade criterion (Annex 2; IUCN, 2001) is primarily used to assess the vulnerability status of the 20 selected species. This involves assessing the expected population reduction (EPR), inferred or assumed in the future (over a maximum of 100 years) based on (i) an index of abundance adapted to the taxa, (ii) the reduction in area of occupancy (AOO), (ii) reduction in area of occupancy (AOO), area of occurrence (EOO) and/or habitat quality, (iii) actual or potential levels of exploitation, and (iv) effects of introduced taxa, hybridization, pathogens, pollutants, competing species or parasites.

For each species, range-wide EPR is estimated for three types of land use: (1) EPR within production forests, (2) EPR within forests covered by protected areas, and (3) EPR within areas occupied by the non-permanent domain.

  1. For production forests, management inventory data from 98 forest concessions in five (05) countries (Cameroon, Congo, Gabon, Central African Republic, and Democratic Republic of Congo) were obtained for an area of 21,433,767 ha, or 40% of the total area of all forest concessions in Central Africa. Through these management inventory data, the population structure of each species is defined using the number of trees per ha and by diameter class (from 20 cm). In addition, demographic (growth, mortality and recruitment) and phenological data are mobilized for each species through the DYNAFAC Collective. The evolution of the population of each species within these forests is simulated using a model integrating the initial population, the demographic parameters (growth, mortality and recruitment), the fertility diameter obtained through the phenological data and the exploitation parameters (minimum exploitation diameter, exploitation coefficient, and the exploitation damage rate) and calculated as the difference between the initial population and the final population of trees for each species
  2. Within protected areas, it is assumed that the tree population of each species is kept stable in the future. Thus, over 100 years, the EPR within protected areas is equal to 0.

iii.          In the non-permanent domain, anthropogenic disturbance is the main threat and the EPR is calculated using the rate of deforestation.

The overall EPR over the range of each species is estimated by calculating the weighted average of the EPRs of the different land use types. According to IUCN criterion A4, when the EPR in the future (over a maximum of 100 years) is greater than or equal to 30%, the species is considered Vulnerable. On the other hand, if the EPR ≥ 50%, it is considered Endangered, and Critically Endangered if EPR ≥ 80%. Data analyses are still in progress and initial results show the robustness of the quantitative data methodological approach to quantify the vulnerability status of each species exploited.

This study is funded by the COMIFAC Program for the Promotion of Certified Logging (PPECF) and Gembloux Agro-Bio Tech. It is implemented by Gembloux Agro-Bio Tech (University of Liège) in collaboration with Nature+, ATIBT, the Missouri Garden Botanic (Africa section), Parcs Gabon, and the consulting firms TEREA, FRMi, and SylvAfrica.