Fertilization effects on soil organic matter chemistry

IF 6.1 1区 农林科学 Q1 SOIL SCIENCE Soil & Tillage Research Pub Date : 2024-10-31 DOI:10.1016/j.still.2024.106346
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Abstract

Despite the close interactions between carbon (C) and nutrients like nitrogen (N), phosphorus (P), and potassium (K), the consequences of N fertilization alone or in combination with P and K on soil organic matter (SOM) chemical composition remain unclear. Using solid-state 13C nuclear magnetic resonance spectroscopy data from 45 field studies, we meta-analyzed the effects of N alone and NPK fertilization on SOM content and chemical composition. Generally, mineral fertilization affects the SOM content and composition via three indirect processes: i) increasing litter input and rhizodeposition, ii) accelerating microbial decomposition of SOM, and iii) modifying the preservation of SOM by soil minerals. NPK fertilization (+12 %) increased organic C content more than N fertilization alone (+8.6 %). Alkyl and O-alkyl C increased at low-N rates (<50 kg N ha−1 yr−1) or after short-term (0–5 yrs) N fertilization alone, likely because improved N availability promoted bacterial residues rich in long-chain aliphatic C formation and carbohydrate-rich matter inputs. High-rate (>200 kg N ha−1 yr−1) or long-term (>25 yrs) NPK fertilization increased alkyl C but decreased aromatic C, likely due to reduced nutrient limitations and acidification. These factors promote aliphatic C-rich microbial biomass, accelerate the decomposition of stable compounds, and decrease the mineral protection of aromatic acids. The SOM chemical composition (excluding aromatic C) response to NPK fertilization decreased with increasing initial level. In contrast, the response of SOM raised with increasing initial content under N fertilization alone. The increase in organic C content was strongly linked to changes in SOM chemistry under NPK fertilization but not under N fertilization alone. In conclusion, NPK fertilization modified SOM chemistry and increased organic C accumulation more effectively than N fertilization alone, which was mediated by increasing plant growth, raising microbial biomass and activity, altering mineral protection, and initial soil C levels. Our findings provide critical insights for optimizing fertilization strategies to improve soil C sequestration capacity and fertility.
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施肥对土壤有机质化学的影响
尽管碳(C)与氮(N)、磷(P)和钾(K)等养分之间存在密切的相互作用,但单独施肥或与磷、钾肥一起施肥对土壤有机质(SOM)化学成分的影响仍不清楚。利用来自 45 项实地研究的固态 13C 核磁共振光谱数据,我们对单独施氮和氮磷钾施肥对 SOM 含量和化学成分的影响进行了元分析。一般来说,矿物肥料通过三个间接过程影响 SOM 的含量和组成:i) 增加枯落物输入和根瘤沉积;ii) 加速 SOM 的微生物分解;iii) 改变土壤矿物对 SOM 的保存。施用氮磷钾肥(+12%)比单独施用氮肥(+8.6%)更能增加有机碳含量。在低氮肥施用率(50 千克氮/公顷-年-1)或短期(0-5 年)单独施用氮肥后,烷基和 O-烷基 C 增加了,这可能是因为氮肥供应的改善促进了富含长链脂肪族 C 的细菌残留物的形成和富含碳水化合物物质的输入。高施肥量(每公顷 200 千克氮)或长期(25 年)氮磷钾施肥增加了烷基碳,但减少了芳香族碳,这可能是由于养分限制减少和酸化所致。这些因素促进了富含脂肪族 C 的微生物生物量,加速了稳定化合物的分解,并降低了对芳香族酸的矿物质保护。SOM 化学成分(不包括芳香族碳)对氮磷钾施肥的响应随着初始施肥量的增加而降低。相反,在只施用氮肥的情况下,SOM 的响应随着初始含量的增加而提高。在施用氮磷钾肥的情况下,有机碳含量的增加与 SOM 化学成分的变化密切相关,而在单独施用氮肥的情况下则不然。总之,施用氮磷钾肥比单独施用氮肥更有效地改变了 SOM 化学性质并增加了有机碳积累,而这是通过增加植物生长、提高微生物生物量和活性、改变矿物质保护和土壤初始碳含量来实现的。我们的研究结果为优化施肥策略以提高土壤固碳能力和肥力提供了重要启示。
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来源期刊
Soil & Tillage Research
Soil & Tillage Research 农林科学-土壤科学
CiteScore
13.00
自引率
6.20%
发文量
266
审稿时长
5 months
期刊介绍: Soil & Tillage Research examines the physical, chemical and biological changes in the soil caused by tillage and field traffic. Manuscripts will be considered on aspects of soil science, physics, technology, mechanization and applied engineering for a sustainable balance among productivity, environmental quality and profitability. The following are examples of suitable topics within the scope of the journal of Soil and Tillage Research: The agricultural and biosystems engineering associated with tillage (including no-tillage, reduced-tillage and direct drilling), irrigation and drainage, crops and crop rotations, fertilization, rehabilitation of mine spoils and processes used to modify soils. Soil change effects on establishment and yield of crops, growth of plants and roots, structure and erosion of soil, cycling of carbon and nutrients, greenhouse gas emissions, leaching, runoff and other processes that affect environmental quality. Characterization or modeling of tillage and field traffic responses, soil, climate, or topographic effects, soil deformation processes, tillage tools, traction devices, energy requirements, economics, surface and subsurface water quality effects, tillage effects on weed, pest and disease control, and their interactions.
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