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Decadal fates and impacts of nitrogen additions on temperate forest carbon storage: a data–model comparison
oleh: S. J. Cheng, P. G. Hess, W. R. Wieder, W. R. Wieder, R. Q. Thomas, K. J. Nadelhoffer, J. Vira, D. L. Lombardozzi, P. Gundersen, I. J. Fernandez, P. Schleppi, M.-C. Gruselle, F. Moldan, C. L. Goodale
| Format: | Article |
|---|---|
| Diterbitkan: | Copernicus Publications 2019-07-01 |
Deskripsi
<p>To accurately capture the impacts of nitrogen (N) on the land carbon (C) sink in Earth system models, model responses to both N limitation and ecosystem N additions (e.g., from atmospheric N deposition and fertilizer) need to be evaluated. The response of the land C sink to N additions depends on the fate of these additions: that is, how much of the added N is lost from the ecosystem through N loss pathways or recovered and used to increase C storage in plants and soils. Here, we evaluate the C–N dynamics of the latest version of a global land model, the Community Land Model version 5 (CLM5), and how they vary when ecosystems have large N inputs and losses (i.e., an open N cycle) or small N inputs and losses (i.e., a closed N cycle). This comparison allows us to identify potential improvements to CLM5 that would apply to simulated N cycles along the open-to-closed spectrum. We also compare the short- (< 3 years) and longer-term (5–17 years) N fates in CLM5 against observations from 13 long-term <span class="inline-formula"><sup>15</sup>N</span> tracer addition experiments at eight temperate forest sites. Simulations using both open and closed N cycles overestimated plant N recovery following N additions. In particular, the model configuration with a closed N cycle simulated that plants acquired more than twice the amount of added N recovered in <span class="inline-formula"><sup>15</sup>N</span> tracer studies on short timescales (CLM5: <span class="inline-formula">46±12</span> %; observations: <span class="inline-formula">18±12</span> %; mean across sites <span class="inline-formula">±1</span> standard deviation) and almost twice as much on longer timescales (CLM5: <span class="inline-formula">23±6</span> %; observations: <span class="inline-formula">13±5</span> %). Soil N recoveries in simulations with closed N cycles were closer to observations in the short term (CLM5: <span class="inline-formula">40±10</span> %; observations: <span class="inline-formula">54±22</span> %) but smaller than observations in the long term (CLM5: <span class="inline-formula">59±15</span> %; observations: <span class="inline-formula">69±18</span> %). Simulations with open N cycles estimated similar patterns in plant and soil N recovery, except that soil N recovery was also smaller than observations in the short term. In both open and closed sets of simulations, soil N recoveries in CLM5 occurred from the cycling of N through plants rather than through direct immobilization in the soil, as is often indicated by tracer studies. Although CLM5 greatly overestimated plant N recovery, the simulated increase in C stocks to recovered N was not much larger than estimated by observations, largely because the model's assumed C:N ratio for wood was nearly half that suggested by measurements at the field sites. Overall, results suggest that simulating<span id="page2772"/> accurate ecosystem responses to changes in N additions requires increasing soil competition for N relative to plants and examining model assumptions of <span class="inline-formula">C:N</span> stoichiometry, which should also improve model estimates of other terrestrial C–N processes and interactions.</p>