Yermakov Zhanna, Rothstein David E
Department of Forestry, Michigan State University, East Lansing, MI 48824-1222, USA.
Oecologia. 2006 Oct;149(4):690-700. doi: 10.1007/s00442-006-0474-4. Epub 2006 Jun 28.
We investigated the changes in soil processes following wildfire in Michigan jack pine (Pinus banksiana) forests using a chronosequence of 11 wildfire-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/m2 in the 7-year-old stand to a high of 254 g C/m2 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=1.853-0.276xagexe-0.814xage; R2=0.381; P=0.002). Total N mineralization decreased from 2.8 g N/m2 in the 1-year-old stand to a minimum value of 0.5 g N/m2 in the 14-year-old stand, and then increased to about 1.5 g N/m2 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.
我们利用11个野火再生林分的时间序列,跨度达72年,研究了密歇根短叶松(Pinus banksiana)森林野火后土壤过程的变化。本研究的目的是描述土壤养分、土壤呼吸和氮矿化随林分发育的模式,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原位氮矿化和土壤呼吸,并使用多元回归分析来确定控制这些过程的重要因素。生长季节土壤呼吸速率范围从7年生林分的低至156 g C/m²到22年生林分的高至254 g C/m²,但与林分年龄没有明显的模式。一般来说,土壤呼吸速率在7月和8月土壤温度最高时达到峰值。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×年龄×e^(-0.814×年龄); R² = 0.381; P = 0.002)。总氮矿化从1年生林分的2.8 g N/m²下降到14年生林分的最小值0.5 g N/m²,然后在成熟林分中增加到约1.5 g N/m²。总氮矿化的变化是由野火后矿质土壤中氮周转的短暂峰值驱动的,随后随着林分成熟,表层有机层中缓慢循环的氮库逐渐积累。因此,在密歇根短叶松森林中,表层有机质的积累似乎在替代林分的野火后调节氮的有效性。