Long-lasting effects on nitrogen cycling 12 years after treatments cease despite minimal long-term nitrogen retention

被引:47
作者
Clark, Christopher M. [1 ]
Hobbie, Sarah E. [2 ]
Venterea, Rodney [3 ]
Tilman, David [2 ]
机构
[1] Arizona State Univ, Sch Life Sci, Tempe, AZ 85287 USA
[2] Univ Minnesota, Dept Ecol Evolut & Behav, St Paul, MN 55108 USA
[3] USDA ARS, Soil & Water Management Unit, St Paul, MN 55108 USA
基金
美国国家科学基金会; 美国安德鲁·梅隆基金会;
关键词
eutrophication; nitrogen deposition; net N mineralization; N retention; recovery; MINNESOTA OLD FIELDS; FOREST ECOSYSTEMS; ATMOSPHERIC NITROGEN; INCREASED DEPOSITION; SATURATED FOREST; GRASSLAND SOILS; PLANT DOMINANCE; UPLAND MOOR; CARBON; INPUT;
D O I
10.1111/j.1365-2486.2008.01811.x
中图分类号
X176 [生物多样性保护];
学科分类号
090705 ;
摘要
Atmospheric deposition of biologically active nitrogen (N) has increased dramatically over the past 60 years, with far-reaching impacts on the structure and function of many ecosystems. Much research has examined the initial impacts of N enrichment; however, few studies have been multidecadal, and even fewer long-term studies have examined the longevity of N-induced impacts on N cycling after inputs cease. Here, we address this gap by reporting the state of key N pools and fluxes in a Minnesota grassland for plots that received N addition for 10 years and then none for 12 years, in comparison with plots that received annual N treatment for the entire 22 years. We found weak evidence for long-term N retention in plots that ceased receiving treatment; and in plots that continued to receive N over the 22-year period, retention that was high after 12 years (50-100% of inputs) was greatly reduced after 22 years (to 15%). In spite of this, net N mineralization rates remained elevated in plots that ceased receiving treatment 12 years prior, likely because N-rich litter maintained higher N-cycling rates. These results suggest (1) some systems do not retain much deposited N, with potentially large impacts on downstream habitats; (2) the previously reported high retention efficiencies for this and many other terrestrial ecosystems may be relatively short-lived as N sinks become saturated over time; and (3) the effects of even small amounts of retained N in N-limited environments may be particularly long-lasting. In total, these findings highlight the importance of long-term studies in evaluating the impacts of chronic N deposition to ecosystems, and urge additional research examining dynamics following N cessation to evaluate the reversibility of these impacts.
引用
收藏
页码:1755 / 1766
页数:12
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