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Mycorrhizas and ecosystem processes in tropical rain forest: implications for diversity

Ian J. Alexander, S. S. Lee

Open publisher page 82 citations

Abstract

Introduction The roots of almost all species of tropical rainforest trees contain mycorrhizal fungi (Alexander 1989a). Our aim here is to demonstrate that not only are these fungi central to ecosystem processes such as carbon- and nutrient-cycling, but that they also have the potential to influence biotic interactions between species, and so help to shape the structure and composition of forest communities. As such, they should be of interest to all ecologists, not just those who are primarily concerned with nutrient dynamics. Mycorrhizas have continued to be the subject of intensive research in the 15 years since we last reviewed their role in tropical rain forest (Alexander 1989a). The processes by which mycorrhizal fungi access mineral nutrients in natural substrates are more fully understood, and important functional differences between types of mycorrhiza have been recognized (Read & Perez-Moreno 2003). There have been major advances in our understanding of the role of mycorrhizal fungi in forest carbon cycles. In boreal forest, for example, 20%–30% of current assimilate is consumed by mycorrhizal fungi (Söderström 2002), over 50% of CO 2 released from soils is accounted for by the respiration of tree roots and their associated mycorrhizal fungi (Högberg et al . 2001) and 30% of the soil microbial biomass is the extraradical hyphae of mycorrhizal fungi (Högberg & Högberg 2002). There is also growing evidence that mycorrhizal associations are multifunctional, and that benefit to the host may not accrue solely or entirely through enhanced capture of mineral nutrients (Newsham et al . 1995a).

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Introduction The roots of almost all species of tropical rainforest trees contain mycorrhizal fungi (Alexander 1989a). Our aim here is to demonstrate that not only are these fungi central to ecosystem processes such as carbon- and nutrient-cycling, but that they also have the potential to influence biotic interactions between species, and so help to shape the structure and composition of forest communities. As such, they should be of interest to all ecologists, not just those who are primarily concerned with nutrient dynamics. Mycorrhizas have continued to be the subject of intensive research in the 15 years since we last reviewed their role in tropical rain forest (Alexander 1989a). The processes by which mycorrhizal fungi access mineral nutrients in natural substrates are more fully understood, and important functional differences between types of mycorrhiza have been recognized (Read & Perez-Moreno 2003). There have been major advances in our understanding of the role of mycorrhizal fungi in forest carbon cycles. In boreal forest, for example, 20%–30% of current assimilate is consumed by mycorrhizal fungi (Söderström 2002), over 50% of CO 2 released from soils is accounted for by the respiration of tree roots and their associated mycorrhizal fungi (Högberg et al . 2001) and 30% of the soil microbial biomass is the extraradical hyphae of mycorrhizal fungi (Högberg & Högberg 2002). There is also growing evidence that mycorrhizal associations are multifunctional, and that benefit to the host may not accrue solely or entirely through enhanced capture of mineral nutrients (Newsham et al . 1995a).

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Available abstract

Introduction The roots of almost all species of tropical rainforest trees contain mycorrhizal fungi (Alexander 1989a). Our aim here is to demonstrate that not only are these fungi central to ecosystem processes such as carbon- and nutrient-cycling, but that they also have the potential to influence biotic interactions between species, and so help to shape the structure and composition of forest communities. As such, they should be of interest to all ecologists, not just those who are primarily concerned with nutrient dynamics. Mycorrhizas have continued to be the subject of intensive research in the 15 years since we last reviewed their role in tropical rain forest (Alexander 1989a). The processes by which mycorrhizal fungi access mineral nutrients in natural substrates are more fully understood, and important functional differences between types of mycorrhiza have been recognized (Read & Perez-Moreno 2003). There have been major advances in our understanding of the role of mycorrhizal fungi in forest carbon cycles. In boreal forest, for example, 20%–30% of current assimilate is consumed by mycorrhizal fungi (Söderström 2002), over 50% of CO 2 released from soils is accounted for by the respiration of tree roots and their associated mycorrhizal fungi (Högberg et al . 2001) and 30% of the soil microbial biomass is the extraradical hyphae of mycorrhizal fungi (Högberg & Högberg 2002). There is also growing evidence that mycorrhizal associations are multifunctional, and that benefit to the host may not accrue solely or entirely through enhanced capture of mineral nutrients (Newsham et al . 1995a).

Key concepts: Rainforest, Ecosystem, Ecology, Nutrient cycle, Tropical rainforest, Forest ecology, Carbon cycle, Nutrient

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