Gabon’s green gold: a bibliographical review of thirty years of research on okoumé ( Aucoumea klaineana Pierre)

Introduction.


INTRODUCTION
Aucoumea klaineana Pierre is the most harvested tree in Central Africa (FRMi, 2018) and it plays a key role in the economy of Gabon for more than a century (Meunier et al., 2015).Its commercial name is "okoumé" in French and "gaboon" in English (ATIBT, 2016).Its wood is mainly used for peeling, plywood manufacture and interior joinery.It has several qualities that favour its use, including its straight grain, large log size, low and uniform density (Peguy et al., 2019).
This tree is present at the top of the coat of arms of the Gabonese republic and contributes to the daily life of rural populations.They use it to build their houses, make their dug-out canoes, torches and treat various illnesses.It produces an aromatic, inflammable oleoresin with antioxidant and antiseptic properties (Obame et al., 2014;Aboughe Angone et al., 2015;DeCarlo et al., 2019;Peguy et al., 2020).
Aucoumea klaineana is considered "Vulnerable" since 1998 by the IUCN (https://www.iucnredlist.org/species/33213/9766796) because its population is assumed to have been reduced by at least 50% as a result of logging (criterion A1).However, this statement is only based on five broad-based references while detailed monographs (Leroy Deval, 1974, 1976a, 1976b;Brunck et al., 1990) and more recent publications have been omitted.
Given the economic importance of A. klaineana, it is essential to reassess its conservation status based on the most recent work.Consequently, the objective of this review is to synthesize the knowledge that can influence the population dynamics of the species.It focuses more specifically on its ecology, silviculture and exploitation.It also highlights issues that need to be better studied in order to ensure sustainable management of A. klaineana populations.It was conducted using the keywords "okoumé" and "aucoumea" in the following search engines: Orbi (ULiège), Libnet (ULiège), Scopus, Google Scholar, the archives of the FORAFRI project (CIRAD) and the archives of the Gembloux Agro-Bio Tech tropical forestry laboratory.

TAXONOMY AND BOTANICAL DESCRIPTION
Aucoumea is a monotypic genus belonging to the pantropical Burseraceae family.Aucoumea klaineana can reach 50-60 m in height, 2 m in diameter and live up to 300 years.The bole is cylindrical with a base either widened or with buttresses which can reach up to 3 m height (Figure 1a) (Meunier et al., 2015).The slice is pink and exudes a characteristic oleoresin (Figure 1b).Its foliage is diffuse.The leaves are hairless, compound and imparipinnate (Figure 1c).The rachis is up to 40 cm long, inserted on a hollow grooved petiole.The veins are joined in an arch near the margin of the leaf.The petiole is 3 to 4 cm long, swollen at the end.Leaflets, 7 to 13 in number, are ovate to oblong, opposite and rounded at the base.The young leaves are red and turn grey-green after a week.The tree is dioecious.Inflorescences can carry a few hundred female flowers or more than a thousand male flowers (Figure 1d).From the outside, flowers are composed by a calyx with five sepals which are tomentose and brownish, triangular in shape and about 5 mm long.The five petals of about 7 mm are also tomentose and brownish.Inside, five orange bilobed nectaries form a crown in the center.In male flowers, the ten stamen filaments are thicker and the gynoecium is attenuated.In the female flowers, the anthers are empty and the pistil is more voluminous.A detailed description of flowers of both types can be found in Aubréville (1962) and Grison (1978).The fruit is a dehiscent capsule with five valves (Figure 1e).On opening, it releases spoon-shaped tough parts containing five seeds of 3 to 4 cm each, enclosed in the winged endocarp (Figure 1f) (Aubréville, 1962).The germination is phanerocotyl and epigea.Cotyledons are foliaceous, rapidly turning green (Figure 1g).The cotyledons persist up to 4 months after sowing (Mapaga et al., 2002).
The development of A. klaineana roots is complex (Leroy Deval, 1974).Lateral roots appear from 10 to 12 weeks.After 10 years and when the typical litter of A. klaineana stands has developed, the taproot atrophies and secondary roots move up towards the shallow soil horizons, between 0 to 25 cm and spread up to 20 m around the trees.In mature stands, the secondary roots thicken to form buttresses. Fine roots build up a dense network in the litter.Tertiary roots can form directly at the base of the buttresses, where litter accumulates heavily.Roots of A. klaineana are coarse and shallow, with few branches, but with fine, long and short pear-shaped elements (Figure 6).The root systems form mechanical and functional root fusions called root anastomoses (See 4.5.).

Distribution
Aucoumea klaineana is found everywhere in Gabon except in the northeastern third, limited from a line passing through Okondja in the east and between Mitzic and Oyem in the north (Brunck et al., 1990), at all altitudes from sea level to near the summit of Mount Iboundji, one of the highest point in the country (980 m).It is also found in Equatorial Guinea (Río Muni), in south-western Congo and in the extreme south-west of Cameroon (Figure 2).
This current distribution of natural populations of A. klaineana (Figure 2) corresponds remarkably with the so-called "Gabonese" region (Philippon et al., 2018).This is characterised by (i) on average, only 109 W . m -2 of incident solar irradiation, a large quantity of dark mornings and dark days with a minimum from June to September (80 W . m -2 ), i.e. the great dry season; (ii) rainfall of less than 1 mm .day -1 in July and August; (iii) generally colder temperatures and (iv) higher relative humidity in the dry seasons than the rest of Central Africa.
Artificially planted, A. klaineana is found in its native range but also in other regions of Cameroon, Côte d'Ivoire, DRC, Ghana, Madagascar, Indonesia, Malaysia, Suriname and French Guiana.However, the poor performance of A. klaineana plantations outside its natural range seems to confirm that climate is a determining factor for the health of its populations (Brunck et al., 1990).

Genetic distribution of populations
A study of the chloroplast DNA of A. klaineana revealed a geographical structuring which suggested a historic separation into two populations: one in the north, confined to the Cristal Mountains, and the other in the south, on the Chaillu massif.This structuring is thought to be linked to the presence of forest refuges in these areas during glacial periods (Muloko-Ntoutoume  et al., 1999) and is also shown by some mammals such as Mandrillus sphinx L. (Telfer et al., 2003) and Gorilla gorilla gorilla Savage (Anthony et al., 2007).Born et al. (2011) isolated and used ten polymorphic microsatellites from the nuclear DNA of A. klaineana to undertake a finer analysis, revealing two other distinct genetic units that appear to correspond to two additional refuge areas: the "Doudou" and "Mayombe" massifs (Born et al., 2011) (Figure 3).

Temperament
Aucoumea klaineana has a pioneering and strictly light-demanding temperament.It colonises open environments of natural (e.g.savanna or forest openings) or anthropic origin (e.g.fallow lands), often in dense patches.As such, A. klaineana is generally considered to be a gregarious species.
Leroy Deval (1973) demonstrated that individuals in a population are not simply in close proximity to each other but also establish root fusions (See 4.5.).
In an even-aged stand, stratification takes place from an early age and it appears that the dominant tree in the population retains higher radial growth than the other trees.Thanks to root anastomoses, it benefits from an extension of its rhizosphere and in exchange, it provides water, nutrients and minerals to suppressed trees and stumps which are still alive.

Population dynamics and structure
Aucoumea klaineana can form almost monospecific stands.Its populations are said to follow man, because they regenerate in the post-cultivation fallow (Hymas, 2015).It was nicknamed "the son of cassava" by Aubréville (1948).It is also a coloniser of savannas, with wind dispersed seeds that will carry over 100 m.Delègue et al. (2001) recorded an annual rate of encroachment into savanna of 1 m .yr -1 by analysing carbon 13 and 14 isotopes in soils.Favier et al. (2004) proposed an empirical model to study the A. klaineana rate of progression at the edge of savannas by linking the age and diameter of the individuals.
Aucoumea klaineana also colonises roadsides, and is sometimes found in large light gaps, but does The points of occurrence in grey are taken from the databases of the Global Biodiversity Information Facility (GBIF, 2020) and the RAINBIO database (Dauby et al., 2016).The yellow line depicts the current range of the species -Les points d'occurrence en gris proviennent des bases de données du Global Biodiversity Information Facility (GBIF, 2020) et de la base de données RAINBIO (Dauby et al., 2016).La ligne jaune délimite l'aire de répartition actuelle de l'espèce.(Doucet et al., 2004).Fuhr et al. (1998Fuhr et al. ( , 2001) ) distinguish three stages of floristic composition following the colonisation of the coastal savannas in Gabon.From settlement to 15-20 years, A. klaineana accounts for 45-70% stems.From 15-20 years to 30-40 years, it dominates other colonising species reaching 80% dominance.From the third stage of colonisation (> 40 years), most of the other colonising species have disappeared and A. klaineana reaches a peak of between 90 and 95% of the dominant stratum.
In central Gabon, Marantaceae play a fundamental role in the stand dynamics.Present in the undergrowth of the A. klaineana monodominant forests, they take advantage of the slightest windfall to develop exuberantly.In doing so, they prevent or delay the regeneration of other woody species (White & Abernethy, 1996;Fuhr et al., 2001).
At the country scale, the average density of A. klaineana is 6.90 stems .ha -1 (dbh ≥ 20 cm) and the distribution of individuals by diameter class is globally balanced with a greater abundance of small diameter trees (Doucet et al., 2021).However, locally in the oldest forests, the distribution follows a Gaussian curve (Figure 4).Biraud (1959) linked it to the regression of human populations who once lived in the forest.Indeed, from the 1930's onwards the Colonial administration forced villages to resettle along roads and major waterways, resulting in a reduction in the spatial influence of slash-and-burn agriculture (Pourtier, 1989;Engone Obiang et al., 2014) and a reduction in sites favourable to the regeneration of A. klaineana and other pioneer longlived light-demanding species (Morin-Rivat et al., 2017).
In Gabon, A. klaineana flowers at the beginning of the long rainy season, in October (Doucet, 2003).Although it can be fertile from 23 cm diameter, full flowering is observed from 55 cm diameter (Doucet, 2003).It is pollinated by social (Apidae: Apinae, Meliponinae) and solitary bees (Xylocopidae) and by flies (Diptera: Calliphoridae, Syrphidae) (Brunck et al., 1990).According to Gautier-Hion (1997), Apis mellifera bees can carry out the pollination of two individuals separated by a maximum of 1.5 km.
Fruiting is episodic and supra-annual (Hecketsweiler, 1992).On average, there is only one year of abundant fruiting every three years (Leroy Deval, 1976a).
In Gabon, female trees of A. klaineana start to bear fruit at the end of December, during the short dry season.A "good seed carrier" gives an average of 10 to 30 litres of seeds (there are 800 to 850 seeds per litre).Production depends on the diameter and height of the tree; some dominant trees could produce up to 100 litres (Leroy Deval, 1976a).
Dispersal is by wind.The seeds of a tree of 50 to 60 cm in diameter, with a well-developed crown can be dispersed up to 100 m (Doucet, 2003).Dominant winds thus play a decisive role in the spatial distribution of seeds.

Natural regeneration
In contrast to the rest of the life cycle of A. klaineana, germination can take place in the shade and usually 5 to 6 days after sowing.The germination rate drops sharply after 2 to 3 weeks in natural conditions.
A number of factors determine good regeneration (Biraud, 1959): -a sufficient number of seed trees (4 to 8 per hectare); -abundant fruiting and sowing; -a large gap (minimum a quarter hectare); -perfectly clear soil at the time of sowing.
These conditions can be met in savannas or in cassava and banana field fallows, as harvesting can match the fruiting periods of A. klaineana (Figure 5).Monospecific stands established naturally can have a density ranging from 6,000 (De Kam et al., 1996) to 35,000 seedlings per hectare (Fuhr et al., 1998).At six years, Mapaga et al. (2002) cite a natural stand of 2,650 stems per hectare.By contrast, seedlings and saplings are rare in mature forest stands.They can only be observed in some large openings caused by storms or landslides.
In production forests, logging, which results in an average removal of one to two stems per hectare, does not create sufficient disturbances to allow a significant regeneration of the species.Doucet (2003) surveyed an average of 110 seedlings of A. klaineana per hectare in old-growth secondary forests logged four years earlier.On average, the density of young trees of more than 2 m in height does not exceed three individuals per hectare of logging gap (Doucet, 2003).Abundant regeneration is only observed along the main roads and in old log yards (Biraud, 1959;Doucet, 2003).This is said to be due to the elimination of competing species from the soil seed bank (Doucet, 2003;Doucet et al., 2004).Doucet (2003) observed average densities of 11 stems (dbh ≥ 10 cm) of A. klaineana per hectare along 20-year-old logging roads.

Soil and rhizosphere
Soil and litter.Aucoumea klaineana grows on all types of soil.From the sandy, poorly drained soils of the estuary of Gabon to the drier, more clay-rich continental soils.Soil type has a minor influence on the establishment of A. klaineana populations compared to climatic and biotic factors (Leroy Deval, 1974).
In the tropics, mineral elements come directly from the litter and not from deep in the soil (Midoko Iponga et al., 2019).Aucoumea klaineana "creates" its own soil, drawing most of its resources from the litter formed by its own fallen fragments (Midoko Iponga et al., 2019), which can be up to 25 cm thick (Leroy Deval, 1974).Different categories of microorganisms, including mycorrhizal fungi, contribute to rapid nutrient renewal in the litter.
During savanna colonisation, the soil is dry and poor in litter and the roots of A. klaineana go deep into the soil.During the cycle until the formation of an old forest, there is a simultaneous evolution of the plant cover, the moisture content of the soil, the accumulation of litter on the surface, fostered by the presence of other species in the understory, and an upward movement of the rhizosphere of A. klaineana towards the more superficial horizons (Leroy Deval, 1974).
Floristic composition therefore plays an important role in the prosperity of A. klaineana.Commensal species improve litter quality (Leroy Deval, 1974).Reduced leaf turnover in well-formed tree crowns and the removal of secondary species under continuous canopy cover could therefore favor the decline of stands in old-growth forests (Leroy Deval, 1974).
In A. klaineana, root anastomoses were first described by Catinot (1962) and detailed by Leroy Deval (1973).Stump healing was observed in 5-15% of cases in natural forests and in 30% of cases in the plantations studied (Leroy Deval, 1973).The survival of these individuals over a long period after felling (up to 42 years [DIARF et al., 2000]) supposes the transfer of photoassimilates by their neighbours reaching the canopy through root anastomoses or by mycorrhizal associations.
According to Leroy Deval (1973), soil type has no influence on root grafts.However, given that the root system of a tree extends wider in sand compared to clay (Kozlowski & Pallardy, 1997), soil texture may have an influence on the establishment of fusions between trees at different distances.
The establishment of anastomoses occurs from the age of 4 to 6 years, when there is a differentiation between the dominant and dominated strata and fusions only form between individuals of different social classes.The growth of the dominant stratum is not affected by variations in the density of the dominated stratum (Leroy Deval, 1973).
Mycorrhizal symbioses.Knowledge of the mycorrhizal status of A. klaineana is very limited.Only one paper on the topic was found (Onguene et al., 2002).According to the authors, who observed symbiosis in plantations and in natural regeneration in southern Cameroon (outside the species range), all trees are related to different species of Glomales (arbuscular mycorrhizal fungi) now reclassified in the Glomerales order (Schüβler et al., 2001).Up to the age of 15 years mycorrhizal colonisation rate increases but then decreases in a non-significant manner.However, the quantities of septate hyphae and arbuscles are low.The highest rates of arbuscles are found in young individuals undergoing natural regeneration.In Burseraceae, Bechem et al. (2018) also found AMF on Dacryodes edulis (G.Don) H.J.Lam.
Although the ectomycorrhizal families of tropical Africa do not include the Burseraceae (Bâ et al., 2011), it should be noted that the particular morphology of the fine roots of A. klaineana is very similar to pear-or club-shaped structures induced by ectomycorrhizal fungi (Figure 6).

Measuring techniques and average growth rates in diameter
Thousands of increment measurements have been carried out on A. klaineana since the 1950s (FAO, 1981;Rocek, 1981;Brunck et al., 1990;Fuhr, 1999;DIARF et al., 2000).Mean values are generally reported in the literature, but measurement techniques (permanent plot and ring analysis) may give different results (Détienne et al., 1998).
Engone Obiang et al. (2013) compiled the average growth rate for A. klaineana since 1961 in permanent plots established in natural stands.Average annual increases in diameter and per individual ranged from 0.1 to 2.33 cm .yr -1 .This compilation shows that the information is not always comparable between sites, because the diameter classes considered are different (from 0 to > 100 cm) and the numbers of observations are sometimes insufficient.This results in very high standard errors.
Ring counts were tested on A. klaineana in the early 1960s by Mariaux and Catinot (Mariaux, 1967).Gabonese (and Congolese) climate generally has four seasons: a long and a short rainy season and a long and short dry season.This alternation makes it possible to observe biennial rings in A. klaineana under optimal conditions and thus to trace its growth dynamics (Détienne et al., 1998).However, measurements are reported to be easy to difficult depending on the growth rate of the tree (Rivière, 1992;Détienne et al., 1998).Ring analyses gave the following average annual diameter increments: 9,4 mm (Sindara, Gabon), 7 to 15 mm (Oyane, Gabon) and 5 to 6 mm (interior Gabon).
By synthesizing all available data (plots and ring analysis) on A. klaineana growth, Picard & Gourlet-Fleury ( 2011) obtain an average annual increase of 8 mm in unlogged forests.However, according to some authors, A. klaineana grows faster in coastal areas than in the interior of Gabon (Brunck et al., 1990;Durrieu de Madron et al., 2000).According to Mapaga et al. (2002), the dominant and codominant individuals in the coastal zone grow an average of 10 mm .yr -1 in diameter compared to 6 mm .yr -1 in the continental zone.Growth rate is said to be a maximum at 10 years.According to other authors, there are no differences between coastal and continental areas (Croisé & Fabbri, 1991).
Local factors such as stand structure (density, age, mix, etc.) and disturbances (logging, fire, competition, etc.) are sources of significant variations in the growth of A. klaineana (Engone Obiang et al., 2013).Durrieu de Madron et al. (2000) report that A. klaineana in mixed stands grows more rapidly below 30 cm (dbh) and that this speed decreases from 40 cm (dbh) onwards.But, according to Nasi (1997), the rate of growth increases constantly for even-aged stands.
Engone Obiang et al. (2013) developed a lognormal rate formula for stands from six sites.The model estimates the growth rate (A, in cm .yr -1 ) including the diameter of the studied tree (D, in cm), the stand density (N, per hectare) and the basal area of the stand (B, in m² .ha -1 ).The last two parameters concern all species in the vicinity of the tree studied, which gives information on its biotic environment: By using the average values of basal area and density calculated from the Gabonese national inventory data (25 m² .ha -1 and 410 stems .ha -1 ; Poulsen et al., 2020), the diameter growth of A. klaineana peaks between 40 and 70 cm and then decreases (Figure 7).

Artificial regeneration
The history of A. klaineana silviculture in Gabon is detailed by Brunck et al. (1990).The main results are summarized hereafter.

Monospecific plantations
Density.A density of between 625 and 950 stems .ha -1 seems optimal until a first thinning at 4 years, which reduces the density of the plantation to 350 stems .ha -1 .This range makes it easy to find a good compromise between bole quality and plantation cost price (Leroy Deval, 1976a).A lower density can lead to higher mortality related to the lack of root anastomoses in the stand because of the distance between roots and to a greater competition with various species depending on the region of the plantation (Louppe et al., 2000).
Considering the biology of the species, Louppe et al. (2000) propose to plant the species in plots with a density of 9 to 16 plants disposed at 1 m apart to promote the formation of root anastomoses.Spacing these plots 12 x 12 m or 10 x 15 m apart should yield 70 stems .ha -1 .
Thinning.Fuhr et al. (2001) assume that thinning should not take place too late because, after 10 years, the growth gain does not compensate for the loss in basal area.Other authors also advocate thinning out at around 10 years (Leroy Deval, 1974;Bibani, 1987, cited by Onguene et al., 2002).However, Onguene et al. (2002) suggest undertaking only a single thinning around 15 years.Thinning before this age would damage a possible mycorrhizal network and thus the carbon capture.
Leroy Deval (1973) recommends two thinnings, between 8 and 15 years of age, in order to promote the good health of the plantation while maintaining good bole conformation.
Costs.Louppe et al. (2000) compare clear-cutting and monospecific natural or artificial regeneration to selective harvesting every 30 years above 60 or 70 cm in diameter.Not conclusive for either method, they state that in the case of clearcutting, harvesting allows natural or artificial regeneration of A. klaineana immediately afterwards.However, the operation releases a large amount of carbon and the market for A. klaineana wood is not suitable for small-diameter stems.In the case of selective logging, they specify that after the 3 rd cutting cycle, an enrichment or a new plantation is essential because the trees exploited will not have formed openings large enough for the species to regenerate by itself.Exploitation by clear-cutting would cost 1,641,200 FCFA .ha -1 (2,502 € .ha -1 ) against 295,500 FCFA .ha -1 (450 € .ha -1 ) for enrichment after selective cutting (conversions from FCFA to euro are in relation to 2020).

Multi-species plantations
Multi-species plantation tests on thirteen species were carried out at the Ekouk experimental site between 1988and 1994(Koumba Zaou et al., 1998).Planting was carried out either after clearcutting and clearing of the soil, or using the undergrowth method, by clearing the shrub and herbaceous layers and ringing trees of little interest.
The study showed that A. klaineana grows faster in diameter in clearcutting (about 2.3 cm .yr -1 compared to 2 cm .yr -1 in undergrowth), while the undergrowth method favours better tree form and at a lower cost (about half that of clearcutting).In both cases, it grows in height by about 2.4 m .yr -1 .Basal area, reached 9.2 m² .ha -1 in clearcutting after six years, compared to 6.9 m² .ha -1 in undergrowth.Koumba Zaou et al. (1998) cite costs of about 800,000 FCFA .ha -1 (1,219 €) for clearcutting and 316,000 FCFA .ha -1 (481 €) for the undergrowth method.Doucet et al. (2004) tested an assisted natural regeneration technique in 10 plots ranging from 0.3 to 1.6 ha.These plots were centred on well-formed, A. klaineana stems with healthy fruit crops just before the seeds were released.The undergrowth was removed with a machete.Then, trees and shrubs of noncommercial species were felled.

Assisted natural regeneration
The results obtained were very cheering.After six months, the density of A. klaineana seedlings was 0.38 m -2 .The average annual growth in height of the seedlings was 86 cm, reaching 196 cm for the dominant ones.In 2003, the costs were estimated at 233,000 FCFA .ha -1 (356 €) (without depressing or clearing).

FOREST MANAGEMENT
In Central Africa, logging is subject to legislation aimed at ensuring the sustainable management of forest resources.Trees must reach a minimum cutting diameter (MCD) before they can be exploited.In Gabon and Congo, the MCD of A. klaineana is set at 70 cm (Decree No. 1993-11285, Law 1-82 [Gabon]; Decree n˚2002-437 [Congo]), while it is 80 cm in Cameroon (ONADEF, 1992).
This MCD may need to be revised upwards in order to meet national standards in terms of recovery rates.For A. klaineana, this rate must be at least 75% in Gabon and 50% in Cameroon.In Congo, the rates are calculated by species group and not individually.These rates are calculated for a cutting cycle.This time is a minimum of 20 years in Gabon (Law n°016/01), 25 to 30 years in Congo (Karsenty et al., 2016) and 30 years in Cameroon (ONADEF, 1992).

Use
The characteristics of A. klaineana wood are described in Gérard et al. (2016).It is one of the best timbers for veneer and plywood production.The exploitation of A. klaineana was once very selective.It was limited to the best shaped trees for the wood peeling industry.With the new market demands to process lower-quality logs by sawing, the proportion of A. klaineana actually exploited sharply increased in some concessions in Gabon, from 30-40% during the 1990s to 65-75% today (FRMi, 2018).The physicomechanical characteristics of plantation woods are very close to those of natural forests (Ngavoura, 1998;Medzegue et al., 2007).

Market
In Gabon, in 2007, A. klaineana accounted for 930,000 m³ of wood entering factories, 82% of Gabon's total production (de Wasseige et al., 2009).In 2010, the Gabonese government banned the export of logs.This strongly encouraged local wood processing (Yoan et al., 2018) and the export of veneers to the European market which reached 142,000 m³ in 2017 (ITTO, 2019).On the other hand, other producing countries (Congo and Equatorial Guinea) have taken advantage of this ban to export more logs to China.For example, Congo increased its exports of A. klaineana logs by 20% between 2016 and 2017 to reach 940,000 m³ (ITTO, 2019).Since July 2020, Congo has also banned the export of logs except "logs of heavy and hardwood species whose processing requires specific technology" (art. 97, Law No. 33-2020).In 2018, sawn timber was mainly directed to China (61%), Vietnam (15%) and Belgium (6%) (ITTO, 2019).

CONCLUSIONS AND STUDY PERSPECTIVES
Aucoumea klaineana is classified by the IUCN as "Vulnerable" under criterion A1.This criterion considers the past reduction of the species' population over a period of three generations.Given their long lifespan, this criterion is difficult to objectivise for tree species.Like populations of other light-demanding colonising taxa, it is even likely that A. klaineana populations have increased over the past few centuries as explained in this review.Furthermore, with an average of 6,9 trees (dbh ≥ 20 cm) per hectare, the species is not rare and its regeneration is not problematic at the level of its distribution range.Finally, in logging concession, the exploitation leaves enough seed trees because the legal cutting diameter is well above the fruiting diameter.Therefore, we do not believe that A. klaineana is vulnerable under criterion A1.
While logging is not a concern for the survival of the species, the reduction in the quality of the logs due to decades of exploitation focused on the best shaped trees, could have unfortunate consequences on the quality of the production.
Optimising A. klaineana silviculture and thus maintaining its trade is essential for the economic future of Gabon and bordering regions.This species remains the leader in a niche market which is the production of veneer sheets by peeling.
It has been shown that the wood quality of A. klaineana in plantations is comparable to that of natural forest wood (Medzegue et al., 2007).The success of plantations should make it possible to keep a low pressure on the natural resource by concentrating production on small areas.Furthermore, the lightdemanding temperament as well as the rapid growth of the species should ensure that A. klaineana is a prime choice for regenerating degraded forests and recreating a habitat suitable for restarting the forest dynamics.
To improve stand management and ensure sufficient regeneration of the species, it is important to understand the determinants of its growth.This synthesis has revealed a high variability in the growth and productivity of natural and artificial stands of A. klaineana.It also highlighted the lack of knowledge about the role of the rhizosphere in the dynamics of the species populations.To be effective, silviculture of A. klaineana should take these aspects into account to a greater extent (Leroy Deval, 1976a).
Mycorrhizal symbiosis in A. klaineana roots has never been observed in its area of origin.However, it could explain the mixed productivity of the species, in comparison with other light-demanding species in plantations.
The phenomenon of root anastomoses could also be a determining factor in the dynamics of A. klaineana populations by promoting strata differentiation in stands and extending the rhizosphere of dominant trees while providing photoassimilates to the dominated.This phenomenon could be complementary with mycorrhizae.It is therefore necessary to improve our knowledge of the rhizosphere of populations of the most exploited woody species in Central Africa.

Figure 4 .
Figure 4. Diametric distribution of Aucoumea klaineana in 35 logging concessions in Gabon, covering 7,3 millions of hectares.The graph on the bottom left shows the average diametric structure at the country scale.Diameter classes start from 20 cm, have a 10 cm range and are incremented of 10 cm per class -Distribution diamétrique d'Aucoumea klaineana dans 35 concessions forestières du Gabon couvrant un total de 7,3 millions d'hectares.Le graphique en bas à gauche montre la structure diamétrique moyenne de l'essence à l'échelle du pays.Les classes de diamètres commencent à partir de 20 cm, ont une amplitude de 10 cm et sont incrémentées de 10 cm par classe.

Figure 7 .
Figure 7. Illustration of the growth model used -Illustration du modèle de croissance utilisé.