Natural 15 N abundance in two nitrogen saturated forest ecosystems

Natural N abundance values were measured in needles, twigs, wood, soil, bulk precipitation, throughfall and soil water in a Douglas fir (Pseudotsuga menziesii (Mirb.) and a Scots pine (Pinus sylvestris L.) stand receiving high loads of nitrogen in throughfall (>50 kg N ha  year ). In the Douglas...

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Bibliographic Details
Published inOecologia Vol. 111; no. 4; pp. 470 - 480
Main Authors Koopmans, C J, Dam, D Van, Tietema, A, Verstraten, J M
Format Journal Article
LanguageEnglish
Published Germany 08.08.1997
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Summary:Natural N abundance values were measured in needles, twigs, wood, soil, bulk precipitation, throughfall and soil water in a Douglas fir (Pseudotsuga menziesii (Mirb.) and a Scots pine (Pinus sylvestris L.) stand receiving high loads of nitrogen in throughfall (>50 kg N ha  year ). In the Douglas fir stand δ N values of the vegetation ranged between -5.7 and -4.2‰ with little variation between different compartments. The vegetation of the Scots pine stand was less depleted in N and varied from -3.3 to -1.2‰δ N. At both sites δ N values increased with soil depth, from -5.7‰ and -1.2‰ in the organic layer to +4.1‰ and +4.7‰ at 70 cm soil depth in the Douglas fir and Scots pine stand, respectively. The δ N values of inorganic nitrogen in bulk precipitation showed a seasonal variation with a mean in NH -N of -0.6‰ at the Douglas fir stand and +10.8‰ at the Scots pine stand. In soil water below the organic layer NH -N was enriched and NO -N depleted in N, which was interpreted as being caused by isotope fractionation accompanying high nitrification rates in the organic layers. Mean δ N values of NH and NO were very similar in the drainage water at 90 cm soil depth at both sites (-7.1 to -3.8‰). A dynamic N cycling model was used to test the sensitivity of the natural abundance values for the amount of N deposition, the N ratio of atmospheric N deposited and for the intrinsic isotope discrimination factors associated with N transformation processes. Simulated δ N values for the N saturated ecosystems appeared particularly sensitive to the N ratio of atmospheric N inputs and discrimination factors during nitrification and mineralization. The N-saturated coniferous forest ecosystems studied were not characterized by elevated natural N abundance values. The results indicated that the natural N abundance values can only be used as indicators for the stage of nitrogen saturation of an ecosystem if the δ N values of the deposited N and isotope fractionation factors are taken into consideration. Combining dynamic isotope models and natural N abundance values seems a promising technique for interpreting natural N abundance values found in these forest ecosystems.
ISSN:0029-8549
1432-1939
DOI:10.1007/s004420050260