Abstract

Plant litter decomposition is a crucial ecosystem process that regulates nutrient cycling, soil fertility, and plant productivity and is strongly influenced by increased nitrogen (N) deposition. However, the effects of exogenous N input on litter decomposition are still poorly understood, especially in temperate shrublands, which hinders predictions of soil C and nutrient dynamics under the context of global change. Temperate shrub ecosystems are usually N-limited and particularly sensitive to changes in exogenous N input. To investigate the responses of Vitex negundo and Spiraea trilobata litter decomposition to N addition, we conducted a field experiment in Vitex- and Spiraea-dominated shrublands located on Mt. Dongling in Beijing, North China. Four N treatment levels were applied: control (N0; no N addition), low N (N1; 20 kg⋅N⋅ha–1⋅year–1), moderate N (N2; 50 kg⋅N⋅ha–1⋅year–1), and high N (N3; 100 kg⋅N⋅ha–1⋅year–1). The litter decomposition in V. negundo was faster than that in S. trilobata, which may be due to the differences in their nutrient content and C/N ratio. N addition increased the amount of remaining N in the two litter types but had no effect on the remaining mass, C, or P. Nitrogen treatment did not affect the litter decomposition rates (k) of either litter type; i.e., N addition had no effect on litter decomposition in temperate shrublands. The neutral effect of N addition on litter decomposition may be primarily explained by the low temperatures and P limitation at the site as well as the opposing effects of the exogenous inorganic N, whereby exogenous N inhibits lignin degradation but promotes the decomposition of readily decomposed litter components. These results suggest that short-term N deposition may have a significant impact on N cycling but not C or P cycling in such shrub ecosystems.

Highlights

  • Litter decomposition plays a key role in the global carbon (C) and nitrogen (N) balance (Vivanco and Austin, 2011) and is an important process that controls C and nutrient cycling in most terrestrial ecosystems (Mo et al, 2004)

  • Plant litter decomposition is controlled by climate and litter quality (Sun et al, 2004; Cornwell et al, 2008; Zhang et al, 2008); at the local scale, it is regulated by litter chemical properties and site soil conditions

  • A repeated-measures analysis of variance (ANOVA) showed that N addition did not influence the amount of remaining mass in the litter samples

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Summary

Introduction

Litter decomposition plays a key role in the global carbon (C) and nitrogen (N) balance (Vivanco and Austin, 2011) and is an important process that controls C and nutrient cycling in most terrestrial ecosystems (Mo et al, 2004). Litter Decomposition and Nutrient Dynamics and nutrient release pattern are dependent on abiotic factors (e.g., climate conditions and soil physical and chemical properties) and biotic factors (e.g., litter quality and microbial community composition) (Prescott, 2005; Yu et al, 2015; Song et al, 2018; Lin et al, 2019). Plant litter decomposition is controlled by climate and litter quality (Sun et al, 2004; Cornwell et al, 2008; Zhang et al, 2008); at the local scale, it is regulated by litter chemical properties and site soil conditions N fertilization may change the soil pH and/or influence decomposer community, microbial, and soil enzyme activity (Carreiro et al, 2000; Chen et al, 2013; Lu et al, 2014; Yu et al, 2015), which affect litter decomposition

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