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Changes in soil carbon and nitrogen cycling along a 72-year wildfire chronosequence in Michigan jack pine forests

机译:密歇根州杰克松林72年野火时序的土壤碳和氮循环变化

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We investigated the changes in soil processes following wildfire in Michigan jack pine (Pinus banksiana) forests using a chronosequence of 11 wild-fire-regenerated stands spanning 72 years. The objective of this study was to characterize patterns of soil nutrients, soil respiration and N mineralization with stand development, as well as to determine the mechanisms driving those patterns. We measured in situ N mineralization and soil respiration monthly during the 2002 growing season and used multiple regression analysis to determine the important factors controlling these processes. Growing-season soil respiration rates ranged from a low of 156 g C/m(2) in the 7-year-old stand to a high of 254 g C/m(2) in the 22-year-old stand, but exhibited no clear pattern with stand age. In general, soil respiration rates peaked during the months of July and August when soil temperatures were highest. We used a modified gamma function to model a temporal trend in total N mineralization (total N mineralization = 1.853-0.276 x age x e-(0.814xage); R-2 = 0.381; P = 0.002). Total N mineralization decreased from 2.8 g N/m(2) in the 1-year-old stand to a minimum value of 0.5 g N/m(2) in the 14-year-old stand, and then increased to about 1.5 g N/m(2) in mature stands. Changes in total N mineralization were driven by a transient spike in N turnover in the mineral soil immediately after wildfire, followed by a gradual accrual of a slow-cycling pool of N in surface organic horizons as stands matured. Thus, in Michigan jack pine forests, the accumulation of surface organic matter appears to regulate N availability following stand-replacing wildfire.
机译:我们使用11个野火再生林分72年的时间序列,对密歇根州杰克松(Pinus bankiana)森林进行野火后土壤过程的变化进行了调查。这项研究的目的是通过林分发育来表征土壤养分,土壤呼吸和氮矿化的模式,并确定驱动这些模式的机制。我们在2002年生长季节每月测量一次原位N矿化和土壤呼吸,并使用多元回归分析来确定控制这些过程的重要因素。生长季节的土壤呼吸速率范围从7岁林分中的最低156 g C / m(2)到22岁林分中的最高254 g C / m(2),但表现出立场年龄没有明确的模式。通常,在土壤温度最高的7月和8月,土壤呼吸速率达到峰值。我们使用修正的伽马函数来模拟总氮​​矿化的时间趋势(总氮矿化= 1.853-0.276 x年龄x e-(0.814xage); R-2 = 0.381; P = 0.002)。总氮矿化度从1年生林分中的2.8 g N / m(2)降至14年生林中的最小值0.5 g N / m(2),然后增加到约1.5 g N / m(2)在成熟林分中。总氮矿化的变化是由野火后矿质土壤中氮素周转量的瞬时峰值驱动的,随后随着表层的成熟,逐渐在表面有机层中缓慢吸收氮素。因此,在密歇根州杰克松林中,表层替代野火后,表面有机质的积累似乎调节了氮的有效性。

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