Abstract. Mature tropical forests at agricultural frontiers are of global conservation concern as the leading edge of global deforestation. In the Ituri Forest of DRC, as in other tropical forest areas, road creation associated with selective logging results in spontaneous human colonization, leading to the clearing of mature forest for agricultural purposes. Following 1-3 years of cultivation, farmlands are left fallow for periods that may exceed 20 years, resulting in extensive secondary forest areas impacted by both selective logging and swidden agriculture. In this study, we assessed forest structure, tree species composition and diversity and the regeneration of timber trees in secondary forest stands (5-10 and ~40 years old), selectively logged forest stands, and undisturbed forests at two sites in the Ituri region. Stem density was lower in old secondary forests (~40 years old) than in either young secondary or mature forests. Overall tree diversity did not significantly differ between forest types, but the diversity of trees >10 cm dbh was substantially lower in young secondary forest stands than in old secondary or mature forests. The species composition of secondary forests differed from that of mature forests, with the dominant Caesalpinoid legume species of mature forests poorly represented in secondary forests. However, in spite of prior logging, the regeneration of high value timber trees such as African mahoganies (Khaya anthotheca and Entandrophragma spp.) was at least 10 times greater in young secondary forests than in mature forests. We argue that, if properly managed and protected, secondary forests, even those impacted by both selective logging and small-scale shifting agriculture, may have high potential conservation and economic value.

Accepted ArticleThis article is protected by copyright. All rights reservedThe growth and survival of individual trees determine the physical structure of a forest with important consequences for forest function. However, given the diversity of tree species and forest biomes, quantifying the multitude of demographic strategies within and across forests and the way that they translate into forest structure and function remains a significant challenge. Here, we quantify the demographic rates of 1,961 tree species from temperate and tropical forests and evaluate how demographic diversity (DD) and demographic composition (DC) differ across forests, and how these differences in demography relate to species richness, aboveground biomass, and carbon residence time.We find wide variation in DD and DC across forest plots, patterns that are not explained by species richness or climate variables alone. There is no evidence that DD has an effect on either aboveground biomass or carbon residence time.Rather, the DC of forests, specifically the relative abundance of large statured species, predicted both biomass and carbon residence time. Our results demonstrate the distinct demographic compositions of globally distributed forests, reflecting biogeography, recent history, and current plot conditions. Linking the demographic composition of forests to resilience or vulnerability to climate change, will improve the precision and accuracy of predictions of future forest composition, structure and function.

1. Organisms of all species must balance their allocation to growth, survival and recruitment. Among tree species, evolution has resulted in different life-history strategies for partitioning resources to these key demographic processes.

All species must balance their allocation to growth, survival and recruitment. Among trees, evolution has resulted in different strategies of partitioning resources to these key demographic processes, i.e. demographic trade-offs. It is unclear whether the same demographic trade-offs structure tropical forests worldwide. Here, we used data from 13 large-scale and long-term tropical forest plots to estimate the principal trade-offs in growth, survival, recruitment, and tree stature at each site. For ten sites, two trade-offs appeared repeatedly. One trade-off showed a negative relationship between growth and survival, i.e. the well-known fast−slow continuum. The second trade-off distinguished between tall-statured species and species with high recruitment rates, i.e. a stature−recruitment trade-off. Thus, the fast-slow continuum and tree stature are two independent dimensions structuring most tropical tree communities. Our discovery of the consistency of demographic trade-offs and strategies across forest types in three continents substantially improves our ability to predict tropical forest dynamics worldwide.

Les forêts tropicales de la République démocratique du Congo sont menacées par la déforestation et la dégradation forestière, qui affectent la structure et la diversité arborée. Cette étude a pour objectif de quantifier les pertes de biomasse et de diversité liées à la déforestation et à la dégradation, en se concentrant sur la réserve de biosphère de Yangambi. Quatre parcelles de 50 m x 50 m ont été inventoriées dans chacun des huit types d’utilisation des terres identifiés : la forêt mature mixte, la forêt mature à Gilbertiodendron dewevrei, les champs des cultures vivrières, les jachères (5 à 10 ans), les forêts secondaires (20 à 40 ans), les plantations de cacaoyers, les plantations de caféiers et les plantations de palmiers à huile. Les stocks de biomasse dans les forêts matures s’élèvent à environ 400 et 380 Mg/ha respectivement pour la forêt à G. dewevrei et la forêt mixte. Les résultats montrent que la forêt mature perd 50, 70 et 90 % de sa biomasse aérienne quand elle est convertie en plantations de cacaoyers, caféiers et palmiers, respectivement, et la quasi-totalité (99 %) lorsqu’elle est convertie en champs de cultures vivrières ; mais quand le champ est abandonné, la biomasse se reconstitue progressivement à 7,5 % après 5 à 10 ans et à 38,8 % après 20 à 40 ans. La diversité est aussi impactée par la conversion, et, bien que la richesse spécifique semble se reconstituer plus rapidement que la biomasse, la composition est fondamentalement modifiée. Ces résultats fournissent des informations essentielles pour quantifier les impacts des solutions « naturelles » pour lutter contre le changement climatique : la protection des forêts matures, l’amélioration de la gestion forestière et le reboisement ; même si l’approche doit être étendue à plus grande échelle.