From energy to (soil organic) matter

被引:208
作者
Gunina, Anna [1 ,2 ]
Kuzyakov, Yakov [3 ,4 ]
机构
[1] Univ Kassel, Dept Environm Chem, D-37213 Witzenhausen, Germany
[2] Tyumen State Univ, Tyumen, Russia
[3] Univ Goettingen, Dept Soil Sci Temperate Ecosyst, Dept Agr Soil Sci, Gottingen, Germany
[4] Peoples Friendship Univ Russia, RUDN Univ, Moscow, Russia
关键词
carbon and nutrient cycling; energy and matter fluxes; enzyme activity; microbial turnover; oxidation and reduction processes; priming effect mechanisms; soil organic matter; FATTY-ACIDS; PLANT INPUTS; CARBON; SUBSTRATE; NITROGEN; DECOMPOSITION; MECHANISMS; TURNOVER; STABILIZATION; PURIFICATION;
D O I
10.1111/gcb.16071
中图分类号
X176 [生物多样性保护];
学科分类号
090705 ;
摘要
In this concept paper, we propose a new view on soil organic matter (SOM) formation: microorganisms use most of the organics entering the soil as energy rather than as a source of carbon (C), while SOM accumulates as a residual by-product because the microbial energy investment in its decomposition exceeds the energy gain. During the initial stages of decomposition, the nominal oxidation state of C (NOSC) in remaining litter decreases, and the energy content increases. This reflects the rapid mineralization of available compounds with positive and neutral NOSC (carboxylic acids, sugars, some amino acids). Consequently, the NOSC of the remaining compounds drops to -0.3 units, and the oxidation rate decreases due to the residual relative accumulation of aromatic and aliphatic compounds (which are hydrolized later) and entombment of the necromass. Ultimately, incompletely decomposed plant residues will have 1%-2.5% more energy per C unit than the initial litter. The linear decrease in energy density of a broad range of organic substances by 106 kJ mol(-1) C per NOSC unit upon oxidation is supported by experimental data on litter decomposition. Preferential recycling of energy-rich reduced (lipids, aromatics, certain amino acids, amino sugars) and the microbial degradation of oxidized compounds (carboxylic acids) also energetically enrich SOM. Despite the high energy content, the availability of energy stored in SOM is lower than in litter. This explains why SOM is not fully mineralized (thermodynamically unfavorable), especially in the absence of plant C to provide new energy (e.g., in bare soil). Energy from litter activates decomposers to mine nutrients stored in SOM (the main ecological function of priming effects) because the nutrient content in SOM is 2-5 times higher than that of litter. This results in only 0.4%-5% year(-1) of litter-derived C being sequestered in SOM, whereas SOM stores 1%-10% year(-1) of the total litter-derived energy. Thus, the energy captured by photosynthesis is the main reason why microorganisms utilize organic matter, whereby SOM is merely a residual by-product of nutrient storage and a mediator of energy fluxes.
引用
收藏
页码:2169 / 2182
页数:14
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