Yucheng Comprehensive Experiment Station, Key Laboratory of Ecosystem Network Observation and Modeling, Institute of Geographic Sciences and Natural Resources Research, Chinese Academy of Sciences, Beijing 100101, China.
Environ Sci Process Impacts. 2016 Mar;18(3):330-41. doi: 10.1039/c5em00446b.
Soil organic carbon (SOC) mineralization is important for the regulation of the global climate and soil fertility. Decomposition of SOC may be significantly affected by the supply of plant-derived labile carbon (C). To investigate the impact of plant-derived dissolved organic matter (DOM) and urea (N) additions on the decomposition of native SOC as well as to elucidate the underlying mechanisms of priming effects (PEs), a batch of incubation experiments was conducted for 250 days by application of (13)C-labeled plant-derived DOM and urea to soils. The direction of PE induced by the addition of DOM was different from the addition of N, i.e. it switched from negative to positive in DOM-amended soils, whereas in the N-treated soil it switched from positive to negative. Adding DOM alone was favorable for soil C sequestration (59 ± 5 mg C per kg soil), whereas adding N alone or together with DOM accelerated the decomposition of native SOC, causing net C losses (-62 ± 4 and -34 ± 31 mg C per kg soil, respectively). These findings indicate that N addition and its interaction with DOM are not favorable for soil C sequestration. Adding DOM alone increased the level of dissolved organic carbon (DOC), but it did not increase the level of soil mineral N. Changes in the ratio of microbial biomass carbon (MBC) to microbial biomass nitrogen (MBN) and microbial metabolic quotient (qCO2) after the addition of DOM and N suggest that a possible shift in the microbial community composition may occur in the present study. Adding DOM with or without N increased the activities of β-glucosidase and urease. Changes in the direction and magnitude of PE were closely related to changes in soil C and N availability. Soil C and N availability might influence the PE through affecting the microbial biomass and extracellular enzyme activity as well as causing a possible shift in the microbial community composition.
土壤有机碳(SOC)矿化对于调节全球气候和土壤肥力非常重要。SOC 的分解可能会受到植物来源的易分解碳(C)供应的显著影响。为了研究植物来源的溶解有机物质(DOM)和尿素(N)添加对原生 SOC 分解的影响,并阐明激发效应(PE)的潜在机制,通过应用(13)C 标记的植物来源的 DOM 和尿素进行了为期 250 天的一批培养实验。添加 DOM 引起的 PE 的方向与添加 N 的方向不同,即在 DOM 处理的土壤中从负变为正,而在 N 处理的土壤中从正变为负。单独添加 DOM 有利于土壤 C 固存(每公斤土壤 59±5mg C),而单独添加 N 或与 DOM 一起添加会加速原生 SOC 的分解,导致净 C 损失(分别为-62±4 和-34±31mg C 每公斤土壤)。这些发现表明,N 添加及其与 DOM 的相互作用不利于土壤 C 固存。单独添加 DOM 会增加溶解有机碳(DOC)的水平,但不会增加土壤矿质氮的水平。添加 DOM 和 N 后微生物生物量碳(MBC)与微生物生物量氮(MBN)和微生物代谢商(qCO2)的比例变化表明,在本研究中可能会发生微生物群落组成的变化。单独添加 DOM 或添加 DOM 和 N 会增加β-葡萄糖苷酶和脲酶的活性。PE 的方向和幅度的变化与土壤 C 和 N 供应的变化密切相关。土壤 C 和 N 供应可能会通过影响微生物生物量和胞外酶活性以及引起微生物群落组成的可能变化来影响 PE。