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美国缅因州贝尔布鲁克流域的土壤化学和物理性质。

Soil chemical and physical properties at the Bear Brook Watershed in Maine, USA.

机构信息

Institute of Arctic and Alpine Research, University of Colorado, 1560 30th St., Boulder, CO 80303, USA.

出版信息

Environ Monit Assess. 2010 Dec;171(1-4):111-28. doi: 10.1007/s10661-010-1531-3. Epub 2010 Jun 18.

Abstract

Acidic deposition leads to the acidification of waters and accelerated leaching and depletion of soil base cations. The Bear Brook Watershed in Maine has used whole-watershed chemical manipulations to study the effects of elevated N and S on forest ecosystem function on a decadal time scale. The objectives of this study were to define the chemical and physical characteristics of soils in both the reference and treated watersheds after 17 years of treatment and assess evidence of change in soil chemistry by comparing soil studies in 1998 and 2006. Results from 1998 confirmed depletion of soil base cation pools and decreased pH due to elevated N and S within the treated watershed. However, between 1998 and 2006, during a period of declining SO4(2-) deposition and continued whole-watershed experimental acidification on the treated watershed, there was little evidence of continued soil exchangeable base cation concentration depletion or recovery. The addition of a pulse of litterfall and accelerating mineralization from a severe ice storm in 1998 may have had significant effects on forest floor nutrient pools and cycling between 1998 and 2006. Our findings suggest that mineralization of additional litter inputs from the ice storm may have obscured temporal trends in soil chemistry. The physical data presented also demonstrate the importance of coarse fragments in the architecture of these soils. This study underscores the importance of long-term, quantitative soil monitoring in determining the trajectories of change in forest soils and ecosystem processes over time.

摘要

酸性沉降导致水体酸化,并加速土壤碱基阳离子的淋溶和损耗。缅因州的 Bear Brook 流域采用全流域化学处理方法,研究了在数十年的时间尺度上,升高的 N 和 S 对森林生态系统功能的影响。本研究的目的是在经过 17 年的处理后,定义参考流域和处理流域土壤的化学和物理特性,并通过比较 1998 年和 2006 年的土壤研究,评估土壤化学变化的证据。1998 年的结果证实,由于处理流域内 N 和 S 的升高,土壤碱基阳离子库枯竭,pH 值降低。然而,在 1998 年至 2006 年期间,在处理流域的 SO4(2-)沉积下降和持续的全流域实验酸化期间,几乎没有证据表明土壤可交换碱基阳离子浓度继续减少或恢复。1998 年严重冰暴导致的凋落物的脉冲添加和加速矿化,可能对森林地被层养分库和 1998 年至 2006 年之间的循环产生了重大影响。我们的研究结果表明,冰暴中额外凋落物输入的矿化可能掩盖了土壤化学的时间趋势。所提出的物理数据还表明了粗碎片在这些土壤结构中的重要性。本研究强调了长期、定量土壤监测在确定森林土壤和生态系统过程随时间变化轨迹方面的重要性。

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