Abstract

Few studies have reported the estimation of nitrogen (N) deposition, including dissolved organic N (DON) fluxes, through water flows and the contribution of snowfall in Asia. In this study, the concentrations and fluxes of DON and dissolved inorganic N (DIN) in bulk precipitation (BP), the throughfall (TF) of trees and understory dwarf bamboo, and stemflow (SF) were evaluated in a cool-temperate forest over three years to clarify N fluxes via precipitation and responses of trees and understory canopies to N deposition. The input of N to the study site in BP was 11.1 ± 1.71 kg N ha−1 year−1, with a significant contribution from DON (78%). Snowfall fluxes contributed up to 46% of the total N input, with variations related to the amount of snowfall (2.08–5.52 kg N ha−1 year−1). The forest canopy enriched DON (2.11 ± 0.42 kg N ha−1 year−1) but consumed NO3 + NO2–N (−0.73 ± 0.19 kg N ha−1 year−1). In contrast, through the understory bamboo canopy, DON (−1.02 ± 0.55 kg N ha−1 year−1) decreased while DIN (0.35 ± 0.44 kg N ha−1 year−1) increased. This study indicates that DON and snowfall should not be neglected when evaluating total N deposition into forest ecosystems, especially in remote regions. The canopy processes related to the dissolved N in the presence of understory plants might have significant implications for the internal N cycle in forest ecosystems.

Highlights

  • Nitrogen (N), which is considered an essential nutrient for plants, can be deposited into forest ecosystems from the atmosphere via the hydrological pathway or dry deposition process.Anthropogenic N generated from intensive human activities amounted to more than 160 Tg N per year in the 1990s [1]

  • The average monthly concentration of dissolved organic N (DON) in bulk precipitation (BP) followed a clear seasonal pattern in each year, The average monthly concentration of DON in BP followed a clear seasonal pattern in each with the highest concentrations in spring (May to June) followed by a tendency to decrease over time year, with the highest concentrations in spring (May to June) followed by a tendency to decrease (Figure 3a)

  • Our results show that N deposition amounted to 11.1 ± 1.71 kg N ha−1 year−1, with a high contribution of DON (78%) and low contribution of dissolved inorganic N (DIN) (22%)

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Summary

Introduction

Nitrogen (N), which is considered an essential nutrient for plants, can be deposited into forest ecosystems from the atmosphere via the hydrological pathway or dry deposition process.Anthropogenic N generated from intensive human activities amounted to more than 160 Tg N per year in the 1990s [1]. With increasing N pollution of the atmosphere, N deposition into forest ecosystems shows an increasing trend. It has been estimated that N deposition in 2050 will be approximately two-fold greater than that in 1990 at the global scale [2]. Atmospheric N deposition has been highlighted as a significant concern in terms of its impact on forest ecosystems [3,4,5]. Multiple studies have focused on the estimation of dissolved inorganic N (DIN) to comprehend the effects of N deposition on forest ecosystems [6,7,8,9,10]. Tree carbon storage has been estimated to increase due to N deposition [12]. N load thresholds have been reported for temperate deciduous forests, such as 10–15 kg N ha−1 year−1 across Europe [13] and Forests 2019, 10, 631; doi:10.3390/f10080631 www.mdpi.com/journal/forests

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