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Effects of nitrogen deposition and fertilization on N transformations in forest soils: a review

机译:氮沉降和施肥对森林土壤氮素转化的影响研究进展

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摘要

Understanding how process-specific nitrogen (N) transformations in natural forest soils are modified by N deposition and fertilization is critically important to gain mechanistic insights on the links between global N deposition and N enrichment and loss in forest soils. Here we identify the general characteristics and the main mechanisms of N deposition- and fertilization-induced modifications in multiple N transformations, including N immobilization, N mineralization, nitrification (autotrophic nitrification and heterotrophic nitrification), and denitrification, in forest soils by literature survey. Overall, N status, soil C/N ratios, C availability, and soil pH are key factors separately and/or interactively affecting the effects of N deposition and fertilization on forest soil N transformations. In the N-limited stage, N deposition and fertilization can act as a stimulator of N mineralization by removing microbial N limitation and reducing the C/N ratios of the substrate being decomposed. In the N-unlimited stage, N added to forest ecosystems can retard N mineralization, which may primarily be a result of decreased microbial activity due to soil acidification and low C availability. The changes in N mineralization may drive a corresponding change in N immobilization, autotrophic nitrification, and denitrification. Despite the fact that ammonia-oxidizing archaea (AOA) has a higher affinity than ammonia-oxidizers (AOB) for low-concentration ammonia (NH3), low NH3 availability may still limit the rate of ammonia oxidation (autotrophic nitrification) in acidic forest soils even in the case of high NH4 (+) input. Heterotrophic nitrification, however, may be favored if soil C/N ratios and pH decrease with N deposition and fertilization. The responses of denitrification and N2O emission to N deposition and fertilization in forests may be nonlinear, with a trend of stimulation in the short term but a decline over time, partly because soil pH has a contrast effect on denitrification capacity and N2O emission. There are various effects of N deposition and fertilization on forest soil N transformations; thus, their responses to N deposition are still not well characterized and understood. N deposition- and fertilization-induced modifications in soil N transformations have important implications for N enrichment, N loss, and soil acidification in forest ecosystems. In the future, more research is required to investigate on dissimilatory nitrate reduction to ammonium (DNRA) process and link microbial community characteristics and functions of microbial extracellular enzymes with these rate processes in forest soils to narrow the uncertainty in evaluating and predicting ecosystem responses to global N deposition.
机译:了解自然森林土壤中特定于过程的氮(N)转化如何通过氮的沉积和施肥来改变,对于获得有关全球氮沉降与森林土壤中氮富集与损失之间联系的机械洞察力至关重要。在这里,我们通过文献调查确定了森林土壤中多种N转化中N沉积和施肥引起的修饰的一般特征和主要机理,包括N固定,N矿化,硝化(自养硝化和异养硝化)和反硝化。总体而言,氮素状况,土壤碳氮比,碳有效性和土壤pH值是分别和/或交互影响氮素沉降和施肥对森林土壤氮素转化影响的关键因素。在N限制阶段,N的沉积和施肥可以通过消除微生物对N的限制并降低被分解基质的C / N比来促进N矿化。在氮素无限期,向森林生态系统添加的氮素可延缓氮素矿化,这可能主要是由于土壤酸化和低碳可利用性导致微生物活性下降的结果。氮矿化的变化可能会导致固氮,自养硝化和反硝化的相应变化。尽管事实证明氨氧化古细菌(AOA)对低浓度氨(NH3)具有比氨氧化剂(AOB)更高的亲和力,但较低的NH3利用率仍可能限制酸性森林土壤中氨的氧化速率(自养硝化)即使在高NH4(+)输入的情况下。但是,如果土壤碳/氮比和pH随氮的沉降和施肥而降低,则可能有利于异养硝化。森林中反硝化和N2O排放对氮沉降和施肥的响应可能是非线性的,短期内有增加的趋势,但随着时间的推移而下降,部分原因是土壤pH对反硝化能力和N2O排放具有相反的影响。氮沉降和施肥对森林土壤氮转化的影响多种多样。因此,它们对氮沉积的反应仍未很好地表征和理解。氮的沉积和施肥引起的土壤氮转化的改良对森林生态系统中的氮富集,氮损失和土壤酸化具有重要意义。将来,需要进行更多的研究以研究异化硝酸盐还原为铵盐(DNRA)过程,并将微生物群落特征和微生物细胞外酶的功能与森林土壤中的这些速率过程联系起来,以缩小评估和预测生态系统对全球土壤响应的不确定性。 N沉积。

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