Department of Geography, University of Zurich, Winterthurerstrasse 190, Zürich 8057, Switzerland.
Glob Chang Biol. 2014 May;20(5):1629-42. doi: 10.1111/gcb.12459. Epub 2014 Aug 8.
Pyrogenic organic matter (PyOM) decomposes on centennial timescale in soils, but the processes regulating its decay are poorly understood. We conducted one of the first studies of PyOM and wood decomposition in a temperate forest using isotopically labeled organic substrate, and quantified microbial incorporation and physico-chemical transformations of PyOM in situ. Stable-isotope (¹³C and ¹⁵N) enriched PyOM and its precursor wood were added to the soil at 2 cm depth at ambient (N0) and increased (N+) levels of nitrogen fertilization. The carbon (C) and nitrogen (N) of added PyOM or wood were tracked through soil to 15 cm depth, in physically separated soil density fractions and in benzene polycarboxylic acids (BPCA) molecular markers. After 10 months in situ, more PyOM-derived C (>99% of initial 13C-PyOM) and N (90% of initial ¹⁵N-PyOM) was recovered than wood derived C (48% of 13C-wood) and N(89% under N0 and 48% under N+). PyOM-C and wood-C migrated at the rate of 126 mm yr ⁻¹ with 3-4% of PyOMC and 4-8% of wood-C recovered below the application depth. Most PyOM C was recovered in the free light fraction(fLF) (74%), with 20% in aggregate-occluded and 6% in mineral associated fractions – fractions that typically have much slower turnover times. In contrast, wood C was recovered mainly in occluded (33%) or dense fraction (27%).PyOM addition induced loss of native C from soil (priming effect), particularly in fLF (13%). The total BPCA-C content did not change but after 10 months the degree of aromatic condensation of PyOM decreased, as determined by relative contribution of benzene hexa-carboxylic acid (B6CA) to the total BPCA C. Soil microbial biomass assimilated 6-10% of C from the wood, while PyOM contributions was negligible (0.14–0.18%). The addition of N had no effect on the dynamics of PyOM while limited effect on wood.
热解有机物质(PyOM)在土壤中需要百年时间才能分解,但目前对控制其衰减的过程知之甚少。我们使用同位素标记的有机底物,对温带森林中的 PyOM 和木质分解进行了首次研究之一,并原位量化了 PyOM 的微生物掺入和理化转化。稳定同位素(¹³C 和 ¹⁵N)富集的 PyOM 及其前体木材被添加到土壤中,深度为 2 厘米,氮施肥水平分别为环境(N0)和增加(N+)。添加的 PyOM 或木材的碳(C)和氮(N)通过物理分离的土壤密度分数和苯多羧酸(BPCA)分子标记追踪到 15 厘米深。在原位 10 个月后,从 PyOM 衍生的 C(初始 ¹³C-PyOM 的> 99%)和 N(初始 ¹⁵N-PyOM 的 90%)的回收量超过了木质衍生的 C(13C-wood 的 48%)和 N(N0 下的 89%和 N+下的 48%)。PyOM-C 和木质-C 的迁移速度为 126mm yr ⁻¹,有 3-4%的 PyOMC 和 4-8%的木质-C 回收量低于施用量。大多数 PyOM C 被回收在自由轻组分(fLF)(74%)中,20%在团聚体封闭组分和 6%在矿物相关组分中-这些组分的周转率通常较慢。相比之下,木质 C 主要回收在封闭(33%)或致密(27%)组分中。PyOM 的添加诱导了土壤中天然 C 的损失(启动效应),特别是在 fLF 中(13%)。总 BPCA-C 含量没有变化,但 10 个月后,PyOM 的芳香化程度降低,这是由苯六羧酸(B6CA)对总 BPCA C 的相对贡献决定的。土壤微生物生物量同化了木材中 6-10%的 C,而 PyOM 的贡献可以忽略不计(0.14-0.18%)。氮的添加对 PyOM 的动态没有影响,而对木材的影响有限。