Abstract

Anthropogenic nitrogen deposition is currently causing a more than twofold increase of reactive nitrogen input over large areas in the tropics. Elevated 15N abundance (δ15N) in the growth rings of some tropical trees has been hypothesized to reflect an increased leaching of 15N-depleted nitrate from the soil, following anthropogenic nitrogen deposition over the last decades. To find further evidence for altered nitrogen cycling in tropical forests, we measured long-term δ15N values in trees from Bolivia, Cameroon, and Thailand. We used two different sampling methods. In the first, wood samples were taken in a conventional way: from the pith to the bark across the stem of 28 large trees (the “radial” method). In the second, δ15N values were compared across a fixed diameter (the “fixed-diameter” method). We sampled 400 trees that differed widely in size, but measured δ15N in the stem around the same diameter (20 cm dbh) in all trees. As a result, the growth rings formed around this diameter differed in age and allowed a comparison of δ15N values over time with an explicit control for potential size-effects on δ15N values. We found a significant increase of tree-ring δ15N across the stem radius of large trees from Bolivia and Cameroon, but no change in tree-ring δ15N values over time was found in any of the study sites when controlling for tree size. This suggests that radial trends of δ15N values within trees reflect tree ontogeny (size development). However, for the trees from Cameroon and Thailand, a low statistical power in the fixed-diameter method prevents to conclude this with high certainty. For the trees from Bolivia, statistical power in the fixed-diameter method was high, showing that the temporal trend in tree-ring δ15N values in the radial method is primarily caused by tree ontogeny and unlikely by a change in nitrogen cycling. We therefore stress to account for tree size before tree-ring δ15N values can be properly interpreted.

Highlights

  • The rate of natural nitrogen input in tropical forests generally ranges between 2 and 20 kgN ha−1 year−1, depending on the amount of reactive nitrogen created by lighting and by heterotrophic soil microbes and rhizobia associated with legumes (Vitousek and Sanford, 1986; Galloway, 2004; Pons et al, 2007)

  • We found a significant increase of tree-ring δ15N across the stem radius of large trees from Bolivia and Cameroon, but no change in tree-ring δ15N values over time was found in any of the study sites when controlling for tree size

  • We only focused on 1950– 2010 because this is the period during which changes in nitrogen cycling due to anthropogenic nitrogen depositions might have occurred

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Summary

Introduction

The rate of natural nitrogen input in tropical forests generally ranges between 2 and 20 kgN ha−1 year−1, depending on the amount of reactive nitrogen created by lighting and by heterotrophic soil microbes and rhizobia associated with legumes (Vitousek and Sanford, 1986; Galloway, 2004; Pons et al, 2007). Estimates of anthropogenic N deposition vary greatly, but in large regions N deposition reaches 5–10 kgN ha−1 year−1, which is about a doubling of natural rates (Galloway et al, 2008; Hietz et al, 2011). The consequences of this increased input are still largely unclear (Galloway et al, 2008). There is general agreement that nitrogen isotopes (δ15N) in plant material reflect the δ15N signature of the available N sources under most field conditions (Evans et al, 1996; Högberg et al, 1999) and can provide valuable information on changes in nitrogen cycling in terrestrial ecosystems

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