Fate of atmospherically deposited NH 4 + and NO 3 - in two temperate forests in China: temporal pattern and redistribution.

The impacts of anthropogenic nitrogen (N) deposition on forest ecosystems depend in large part on its fate. However, our understanding of the fates of different forms of deposited N as well as the redistribution over time within different ecosystems is limited. In this study, we used the ¹⁵ N-tracer method to investigate both the short-term (1 week to 3 months) and long-term (1-3 yr) fates of deposited NH ₄ ⁺ or NO ₃ ^- by following the recovery of the ¹⁵ N in different ecosystem compartments in a larch plantation forest and a mixed forest located in northeastern China. The results showed similar total ecosystem retention for deposited NH ₄ ⁺ and NO ₃ ^- , but their distribution within the ecosystems (plants vs. soil) differed distinctly particularly in the short-term, with higher ¹⁵ NO ₃ ^- recoveries in plants (while lower recoveries in organic layer) than found for ¹⁵ NH ₄ ⁺ . The different short-term fate was likely related to the higher mobility of ¹⁵ NO ₃ ^- than ¹⁵ NH ₄ ⁺ in soils instead of plant uptake preferences for NO ₃ ^- over NH ₄ ⁺ . In the long-term, differences between N forms became less prevalent but higher recoveries in trees (particularly in the larch forest) of ¹⁵ NO ₃ ^- than ¹⁵ NH ₄ ⁺ tracer persisted, suggesting that incoming NO ₃ ^- may contribute more to plant biomass increment and forest carbon sequestration than incoming NH ₄ ⁺ . Differences between the two forests in recoveries were largely driven by a higher ¹⁵ N recovery in the organic layer (both N forms) and in trees (for ¹⁵ NO ₃ ^- ) in the larch forest compared to the mixed forest. This was due to a more abundant organic layer and possibly higher tree N demand in the larch forest than in the mixed forest. Leachate ¹⁵ N loss was minor (<1% of the added ¹⁵ N) for both N forms and in both forests. Total ¹⁵ N recovery averaged 78% in the short-term and decreased to 55% in the long-term but with increasing amount of ¹⁵ N label (re)-redistributed into slow turn-over pools (e.g., trees and mineral soil). The different retention dynamics of deposited NH ₄ ⁺ and NO ₃ ^- may have implications in environmental policy related to the anthropogenic emissions of the two N forms.
(© 2019 by the Ecological Society of America.)