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首页> 外文期刊>Global change biology >Biotic and abiotic immobilization of ammonium, nitrite, and nitrate in soils developed under different tree species in the Catskill Mountains, New York, USA
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Biotic and abiotic immobilization of ammonium, nitrite, and nitrate in soils developed under different tree species in the Catskill Mountains, New York, USA

机译:美国纽约州卡茨基尔山脉不同树种发育的土壤中铵,亚硝酸盐和硝酸盐的生物和非生物固定化

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摘要

Nitrogen retention in soil organic matter (SOM) is a key process influencing the accumulation and loss of N in forest ecosystems, but the rates and mechanisms of inorganic N retention in soils are not well understood. The primary objectives of this study were to compare ammonium (NH4+), nitrite (NO2-), and nitrate (NO3-) immobilization among soils developed under different tree species in the Catskill Mountains of New York State, and to determine the relative roles of biotic or abiotic processes in soil N retention. A laboratory experiment was performed, where N-15 was added as NH4+, NO2-, or NO3- to live and mercury-treated O horizon soils from three tree species (American beech, northern red oak, sugar maple), and N-15 recoveries were determined in the SOM pool. Mercuric chloride was used to treat soils as this chemical inhibits microbial metabolism without significantly altering the chemistry of SOM. The recovery of N-15 in SOM was almost always greater for NH4+ (mean 20%) and NO2- (47%) than for NO3- (10%). Ammonium immobilization occurred primarily by biotic processes, with mean recoveries in live soils increasing from 9% at 15 min to 53% after 28 days of incubation. The incorporation of NO2- into SOM occurred rapidly (<15 min) via abiotic processes. Abiotic immobilization of NO2- (mean recovery 58%) was significantly greater than abiotic immobilization of NH4+ (7%) or NO3- (7%). The incorporation of NO2- into SOM did not vary significantly among tree species, so this mechanism likely does not contribute to differences in soil NO3- dynamics among species. As over 30% of the (NO2-)-N-15 label was recovered in SOM within 15 min in live soils, and the products of NO2- incorporation into SOM remained relatively stable throughout the 28-day incubation, our results suggest that NO2- incorporation into SOM may be an important mechanism of N retention in forest soils. The importance of NO2- immobilization for N retention in field soils, however, will depend on the competition between incorporation into SOM and nitrification for transiently available NO2-. Further research is required to determine the importance of this process in field environments.
机译:土壤有机质中的氮保留是影响森林生态系统中氮的积累和损失的关键过程,但是对土壤中无机氮的保留速率和机理尚不十分了解。这项研究的主要目的是比较在纽约州卡茨基尔山的不同树种下发育的土壤中的铵(NH4 +),亚硝酸盐(NO2-)和硝酸盐(NO3-)固定化,并确定土壤中氮的生物或非生物过程。进行了实验室实验,其中将N-15以NH4 +,NO2-或NO3-的形式添加到来自三种树种(美洲山毛榉,北部红橡树,糖枫)和N-15的活水和汞处理的O地平线土壤中在SOM库中确定回收率。氯化汞用于处理土壤,因为该化学品抑制微生物的代谢,而不会显着改变SOM的化学性质。 NH4 +(平均20%)和NO2-(47%)中SOM中N-15的回收率几乎总是比NO3-(10%)中的高。铵固定化主要通过生物过程发生,在温育土壤中的平均回收率从15分钟时的9%增加到孵化28天后的53%。通过非生物过程,NO2-迅速并入SOM(<15分钟)。非生物固定化NO2-(平均回收率58%)明显大于非生物固定化NH4 +(7%)或NO3-(7%)。在树木中,NO2-掺入SOM的变化不大,因此这种机制可能不会导致物种间土壤NO3-动力学差异。由于在15分钟内在土壤中的SOM中回收了超过30%的(NO2-)-N-15标签,并且在整个28天的培养过程中,NO2-掺入SOM的产物保持相对稳定,我们的结果表明NO2 -掺入SOM可能是森林土壤中氮保留的重要机制。但是,固定NO2-对于田间土壤中氮保留的重要性将取决于将SOM掺入和硝态氮对瞬时可用NO2-的竞争。需要进一步研究以确定该过程在现场环境中的重要性。

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