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Malgré l’amélioration de nos connaissances sur les processus biologiques influençant la répartition des espèces et des communautés de petits mammifères et de coléoptères durant la succession forestière, plusieurs questions n’ont pas été abordées et d’autres ont surgi au cours de l’étude. Par exemple, l’objectif du chapitre 1 était de comprendre l’impact des perturbations anthropiques sur la composition et la structuration des communautés le long de la succession. Néanmoins, les principales perturbations naturelles de l’aire d’étude sont les feux de forêts (Bouchard et al., 2008), une perturbation que je n’ai pas échantillonnée. Puisque les stratégies de gestion écosystémique des forêts tentent de maintenir la biodiversité de l’écosystème en développant des pratiques sylvicoles similaires aux perturbations naturelles (Gauthier et al., 2010b), il serait intéressant d’avoir plus d’informations sur les processus régissant la répartition des espèces durant la succession après un feu de forêt, et de pouvoir comparer ces processus avec ceux après coupe. De plus, on sait que le paysage adjacent peut influencer les coléoptères (Janssen et al., 2009), il est donc possible que l’hétérogénéité naturelle de la matrice de paysage contribuent à la diversité des communautés de coléoptères et des petits mammifères en forêt boréale. On pourrait donc également prendre en compte la matrice environnante dans les analyses de communautés.

Nous n’avons pas observé de différences dans les assemblages de coléoptères et de petits mammifères entre les coupes de 5 à 20 ans après coupes et les peuplements non coupés. La similarité dans les communautés que nous avons observée entre les coupes récentes et les forêts anciennes suggère que les assemblages d'espèces dans les jeunes coupes seraient composés principalement de populations résiduelles d'espèces

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forestières matures (Niemelä et al., 1993; Pohl et al., 2007). On pourrait éventuellement échantillonner sur cet intervalle de temps en particulier pour avoir plus de détails, ou il serait également intéressant de faire un suivi temporel de la biodiversité dans nos sites de coupes récentes pour mieux comprendre les changements des communautés et des processus biologiques les structurant.

Notre compréhension des interactions entre le campagnol à dos roux et ses prédateurs durant la succession repose en grande partie sur des études qui ne sont pas toutes conduites en forêt boréale de l’Est du Canada (Halle, 1988; Widén, 1994; Sulkava & Huhtala, 1997) Or, il pourrait y avoir d’importantes différences dans les facteurs qui influencent la dynamique des populations régionales et la répartition du campagnol. Il serait intéressant de réaliser des études sur les prédateurs aviaires et terrestres afin de déterminer le rôle précis que jouent les prédateurs dans la régulation des populations de campagnols et de souris durant les différents stades de succession de la forêt boréale. Par exemple, les campagnols sont-ils plus efficacement prélevés par les prédateurs aviaires en début de succession caractérisée par une canopée peu dense qui semble offrir une faible protection ; ou au contraire cela permet-il de les détecter plus facilement ? De même, les prédateurs terrestres sont-ils plus efficaces que les prédateurs aviaires en fin de succession ? Des études portant sur le taux de survie, la reproduction et les causes de mortalité du campagnol et de la souris durant les différents stades de succession dans les forêts boréales pourraient grandement améliorer notre compréhension des processus qui contribuent aux variations observées dans la dynamique des populations du campagnol.

Bien qu’il reste de nombreuses questions de recherche à prendre en compte, mes travaux ont permis de mieux comprendre comment les processus stochastiques, l’hétérogénéité de l’habitat, la prédation, la compétition inter- et intraspécifiques peuvent influencer la répartition des espèces et l’organisation des communautés le long d’un gradient de succession après coupe forestière. Toutes ces questions soulevées devraient nous permettre d’encore mieux comprendre les processus régissant la biodiversité en forêt boréale.

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