Root processes counteract the suppression of nitrogen-induced priming effects by enhancing microbial activity and catabolism in greenhouse vegetable production systems

IF 6.8 1区 农林科学 Q1 SOIL SCIENCE
Jinshan Lian , Sébastien Massart , Guihua Li , Jianfeng Zhang
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引用次数: 0

Abstract

Nitrogen (N) fertilization regulates soil organic carbon (SOC) decomposition by altering the priming effect (PE) and root activities, affecting subsequently soil carbon sequestration and crop productivity. However, the effects of long-term N fertilization on the direction and magnitude of SOC and underlying mechanisms priming in the rhizosphere compared with bulk soils remain unclear. In this study, paired rhizosphere and bulk soil samples were collected from a 15-year greenhouse tomato production system under four chemical N fertilizer treatments: 0 (N0), 102 (N1), 327 (N2), and 552 (N3) kg N ha–1 yr–1, in addition to uniform manure and straw amendment at 123 kg N ha-1 yr-1. These samples were incubated for 49 days with or without the addition of 13C-labeled glucose, and the incorporation of glucose-derived 13C into CO2 and phospholipid fatty acids (PLFAs) was monitored to elucidate the mechanisms underlying the PE. The results showed a significant interaction between N fertilization and soil niche. The relative PE was significantly higher under the N0 treatment (1.82–2.02 %) compared with the strongly negative values observed under N1–N3 treatments (-0.81 % to -10.18 %) in both rhizosphere and bulk soils, indicating that increased N availability suppressed SOC decomposition. However, rhizosphere soils exhibited significantly weaker negative PE (-2.66 %) than bulk soils (-4.36 %), primarily due to lower dissolved organic nitrogen (DON) levels and higher microbial abundance and activity, suggesting that rhizosphere processes partially counteracted the suppressive effect of N fertilization. A reduction in relative PE correlated with increases in dissolved organic nitrogen (DON), glucose-derived microbial biomass carbon (13MBC), and microbial carbon use efficiency (CUE). Overall, long-term N fertilization suppressed SOC priming by enhancing soil N availability and microbial C assimilation capacity. However, root-mediated microbial legacy effects in the rhizosphere counteracted this suppression, highlighting the importance of N–soil niche interactions in regulating SOC turnover. These findings offer novel insights into soil carbon cycling dynamics and have implications for targeted soil carbon sequestration strategies in intensive greenhouse agriculture.
根系过程通过增强温室蔬菜生产系统中的微生物活性和分解代谢来抵消氮诱导的启动效应的抑制
氮肥通过改变土壤启动效应(PE)和根系活动调节土壤有机碳(SOC)分解,进而影响土壤固碳和作物生产力。然而,与散装土壤相比,长期施氮对根际土壤有机碳方向和大小的影响及其引发机制尚不清楚。本研究在一个15年的温室番茄生产系统中,收集了4种化学氮肥处理(0 (N0)、102 (N1)、327 (N2)和552 (N3) kg N ha-1年-1,以及施用123 kg N ha-1年-1的均匀肥料和秸秆)的根际和土壤样品。这些样品分别在添加或不添加13C标记的葡萄糖的情况下孵育49天,并监测葡萄糖衍生的13C与二氧化碳和磷脂脂肪酸(PLFAs)的结合情况,以阐明PE的机制。结果表明,氮肥与土壤生态位之间存在显著的交互作用。在根际和体土中,N0处理的相对PE(1.82 ~ 2.02 %)显著高于n1 ~ n3处理(-0.81 % ~ -10.18 %),说明氮素有效性的增加抑制了有机碳分解。然而,根际土壤的负PE(-2.66 %)明显弱于普通土壤(-4.36 %),这主要是由于较低的溶解有机氮(DON)水平和较高的微生物丰度和活性,表明根际过程部分抵消了氮肥的抑制作用。相对PE的降低与溶解有机氮(DON)、葡萄糖衍生的微生物生物量碳(13MBC)和微生物碳利用效率(CUE)的增加相关。总体而言,长期施氮通过提高土壤氮有效性和微生物碳同化能力来抑制有机碳的启动。然而,根际介导的微生物遗留效应抵消了这种抑制,突出了n -土壤生态位相互作用在调节有机碳周转中的重要性。这些发现为土壤碳循环动力学提供了新的见解,并对集约化温室农业中有针对性的土壤碳固存策略具有重要意义。
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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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