Ministry of Agriculture Key Laboratory of Crop Nutrition and Fertilization, Institute of Agricultural Resources and Regional Planning, Chinese Academy of Agricultural Sciences, Beijing, P.R.China.
College of Resources and Environmental Sciences, China Agricultural University, Beijing, China.
PLoS One. 2018 Apr 18;13(4):e0195144. doi: 10.1371/journal.pone.0195144. eCollection 2018.
Microbial mechanisms associated with soil organic carbon (SOC) decomposition are poorly understood. We aim to determine the effects of inorganic and organic fertilizers on soil labile carbon (C) pools, microbial community structure and C mineralization rate under an intensive wheat-maize double cropping system in Northern China. Soil samples in 0-10 cm layer were collected from a nine-year field trial involved four treatments: no fertilizer, CK; nitrogen (N) and phosphorus (P) fertilizers, NP; maize straw combined with NP fertilizers, NPS; and manure plus straw and NP fertilizers, NPSM. Soil samples were analyzed to determine labile C pools (including dissolved organic C, DOC; light free organic C, LFOC; and microbial biomass C, MBC), microbial community composition (using phospholipid fatty acid (PLFA) profiles) and SOC mineralization rate (from a 124-day incubation experiment). This study demonstrated that the application of chemical fertilizers (NP) alone did not alter labile C fractions, soil microbial communities and SOC mineralization rate from those observed in the CK treatment. Whereas the use of straw in conjunction with chemical fertilizers (NPS) became an additional labile substrate supply that decreased C limitation, stimulated growth of all PLFA-related microbial communities, and resulted in 53% higher cumulative mineralization of C compared to that of CK. The SOC and its labile fractions explained 78.7% of the variance of microbial community structure. Further addition of manure on the top of straw in the NPSM treatment did not significantly increase microbial community abundances, but it did alter microbial community structure by increasing G+/G- ratio compared to that of NPS. The cumulative mineralization of C was 85% higher under NPSM fertilization compared to that of CK. Particularly, the NPSM treatment increased the mineralization rate of the resistant pool. This has to be carefully taken into account when setting realistic and effective goals for long-term soil C stabilization.
与土壤有机碳 (SOC) 分解相关的微生物机制尚未被充分理解。本研究旨在确定在华北地区一种集约化的小麦-玉米轮作系统下,无机和有机肥料对土壤易分解碳(C)库、微生物群落结构和 C 矿化速率的影响。从一个为期九年的田间试验中采集了 0-10cm 土层的土壤样本,该试验涉及四种处理:不施肥(CK);氮 (N) 和磷 (P) 肥料(NP);玉米秸秆与 NP 肥料结合(NPS);以及粪肥加秸秆和 NP 肥料(NPSM)。对土壤样本进行分析以确定易分解 C 库(包括溶解有机碳(DOC)、轻自由有机碳(LFOC)和微生物生物量 C(MBC))、微生物群落组成(使用磷脂脂肪酸(PLFA)谱)和 SOC 矿化速率(来自 124 天的培养实验)。本研究表明,单独施用化肥(NP)不会改变 CK 处理中观察到的易分解 C 分数、土壤微生物群落和 SOC 矿化速率。然而,秸秆与化肥结合使用(NPS)成为额外的易分解基质供应,降低了 C 限制,刺激了所有与 PLFA 相关的微生物群落的生长,并导致与 CK 相比,C 的累积矿化率提高了 53%。SOC 及其易分解分数解释了微生物群落结构变化的 78.7%。在 NPSM 处理中,在秸秆顶部进一步添加粪肥并没有显著增加微生物群落丰度,但与 NPS 相比,它通过增加 G+/G- 比来改变微生物群落结构。与 CK 相比,NPSM 施肥下 C 的累积矿化率提高了 85%。特别是,NPSM 处理增加了抗性库的矿化率。在设定长期土壤 C 稳定的实际和有效目标时,需要对此加以仔细考虑。