2011
DOI: 10.1111/j.1469-8137.2010.03640.x
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Declining foliar and litter δ15N diverge from soil, epiphyte and input δ15N along a 120 000 yr temperate rainforest chronosequence

Abstract: Summary Patterns in the natural abundance of nitrogen (N) isotopes (15N and 14N) can help in the understanding of ecosystem processes along environmental gradients, because some processes fractionate against the heavier isotope. We measured δ15N in many components of the Franz Josef soil chronosequence in New Zealand to see how each component varied along the sequence and within sites, and to see what this variation can tell us about how ecosystem processes such as N losses change with soil age. We analyzed … Show more

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Cited by 35 publications
(29 citation statements)
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References 88 publications
(286 reference statements)
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“…Foliar 15 N and 13 C values generally increased similarly for all species as retrogression proceeded, consistent with previous studies on these islands (Hyodo and Wardle 2009) and retrogressive chronosequences in Hawaii (Vitousek et al 1989) and California (Brenner et al 2001), but not New Zealand (Menge et al 2011). The increasing d 15 N signature on smaller islands has been attributed to increased biological N-fixation and greater dependency of plants on organic N (Brenner et al 2001).…”
Section: Discussionsupporting
confidence: 84%
“…Foliar 15 N and 13 C values generally increased similarly for all species as retrogression proceeded, consistent with previous studies on these islands (Hyodo and Wardle 2009) and retrogressive chronosequences in Hawaii (Vitousek et al 1989) and California (Brenner et al 2001), but not New Zealand (Menge et al 2011). The increasing d 15 N signature on smaller islands has been attributed to increased biological N-fixation and greater dependency of plants on organic N (Brenner et al 2001).…”
Section: Discussionsupporting
confidence: 84%
“…Total ecosystem d 15 N was initialized at 4.75% at the beginning of simulations, and after only 50 years of red alder N 2 -fixation, total ecosystem d 15 N declined to 2.40% and N capital nearly doubled from *8,600 to 14,400 kg N ha -1 . This rapid decadal-scale shift in ecosystem N and d 15 N highlights the need for dynamic simulation of N input-output balances that are far from equilibrium, and contrasts with conditions where N inputs and losses are relatively small and close to balanced (Houlton et al 2006;Menge et al 2011). As more N was fixed and diluted into an increasingly large ecosystem N pool, simulated ecosystem d 15 N exhibited smaller shifts, consistent with field observations showing that red alder has less impact on soil d 15 N signatures in N-rich sites (Binkley et al 1985).…”
Section: Discussionmentioning
confidence: 98%
“…Observed ranges of natural abundance of 15 N in other Podocarpaceae , e.g. δ 15 N of −8 to −3‰ for P. hallii and P. urbanii 4950, suggest that such associated nitrogen fixation is certainly not a general feature of Podocarpaceae , however, or at least its contribution may not always be significant. For L. fonkii , specifically the following findings support an effective and specific association: (i) high N 2 fixation rates, confirmed by both 15 N 2 uptake and active acetylene reduction (ii) molecular evidence of nitrogenase gene expression predominated by Beijerinckiaceae compared to a diverse diazotroph community in the surrounding rhizopheric peat soil (Fig.…”
Section: Discussionmentioning
confidence: 99%