华北平原低效率碳固存与长期高水平秸秆还田与保护碳库饱和的关系

IF 6.8 1区 农林科学 Q1 SOIL SCIENCE
Xu Li , Xiaonan Yang , Jingyu Li , Jun Wang , Xin Fu , Zhengping Peng , Hongkai Dang
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引用次数: 0

摘要

在华北平原,秸秆还田作为增加碳(C)固存和维持作物产量的关键措施被广泛采用,但长期施用效果有限。长期不同秸秆还田水平对土壤残碳转化的影响机制和不同保护池的饱和状态尚不清楚。在41年的田间试验中收集土壤样品,秸秆回收率分别为0 kg·ha−1 (CK)、2250 kg·ha−1 (S1)、4500 kg·ha−1 (S2)和9000 kg·ha−1 (S3),并与13c标记的秸秆一起培养300天。测定了不同碳库土壤有机碳(SOC)及其活性组分。培养300 d后,土壤有机碳浓度(14.2 % ~ 26.1 %)和活性碳含量(32.8 % ~ 220.5 %)随秸秆施用量的增加而增加。残渣源颗粒物有机C (POC)、微生物生物量C (MBC)和溶解有机C (DOC)浓度在S3区均高于S1区和S2区,且S2区高于S1区。秸秆还田使不同保护池的有机碳浓度增加了4.2 % ~ 36.0 %,但在所有保护池中,S2与S3之间没有显著差异。残渣衍生的C主要存储在未保护池中,占73.9 %-80.8 %。除受微团聚体保护的有机碳和被遮挡的粉土和粘土组分外,S3的残碳浓度显著高于S1和S2。所有保护池均有碳饱和的迹象,但碳饱和的机制不同。由于微聚集体的限制,物理保护池达到了C固存极限。相比之下,化学和生物化学保护池通过原生有机碳的矿化损失和残碳源C的固定达到稳态平衡。总体而言,华北地区秸秆长期还田后,表层土壤仍保留固碳潜力,但在玉米秸秆中高还田率之间,固碳量无显著差异。从长远来看,将秸秆还田与有针对性的养分管理或多样化种植相结合,是提高秸秆还田固碳能力的关键。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Inefficient C sequestration with long term high-level straw return as linked to protected C pools saturation on the North China Plain
Straw return has been widely used as a key measure to increase carbon (C) sequestration and sustain crop yields on the North China Plain, however, its effects were limited under long-term application. The mechanisms underlying the transformation of residue-derived C in soil and saturation status of different protected pools following long-term different straw return levels remain unclear. Soil samples were collected from a 41-yr field experiment with varying straw return rates: 0 kg·ha−1 (CK), 2250 kg·ha−1 (S1), 4500 kg·ha−1 (S2), and 9000 kg·ha−1 (S3), and incubated with 13C-labeled straw for 300 days. Soil organic carbon (SOC) and its active fractions in different C pools were measured. After 300 days of incubation, SOC concentration (14.2 %-26.1 %) and active C fractions (32.8 %-220.5 %) increased with an increase in straw application rates. Residue-derived particulate organic C (POC), microbial biomass C (MBC), and dissolved organic C (DOC) concentrations were greater in S3 than in S1 and S2, and these values were greater in S2 than in S1. Furthermore, straw return increased SOC concentration in different protected pools by 4.2 %-36.0 %, but no significant differences were found between S2 and S3 for all protected pools. Residue-derived C was primarily stored in the unprotected pool, accounting for 73.9 %-80.8 %. The residue-derived C concentration in S3 was significantly higher than those in S1 and S2 (except for the microaggregate-protected organic C and occluded silt and clay fractions). All protected pools showed signs of C saturation, but the mechanisms of C saturation differed. The physically protected pool reached C sequestration limit due to microaggregate restrictions. In contrast, the chemically and biochemically protected pools reached a steady-state balance through the mineralization loss of native SOC and the fixation of residue-derived C. Overall, after long-term straw return in North China, surface soils still retain C sequestration potential, but no significant differences in C sequestration were observed between medium and high rates of maize straw return. Integrating straw return with targeted nutrient management or diversified planting is essential to enhance the C sequestration capacity of straw return in the long run.
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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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