Xu Li , Xiaonan Yang , Jingyu Li , Jun Wang , Xin Fu , Zhengping Peng , Hongkai Dang
{"title":"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","authors":"Xu Li , Xiaonan Yang , Jingyu Li , Jun Wang , Xin Fu , Zhengping Peng , Hongkai Dang","doi":"10.1016/j.still.2025.106766","DOIUrl":null,"url":null,"abstract":"<div><div>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<sup>−1</sup> (CK), 2250 kg·ha<sup>−1</sup> (S1), 4500 kg·ha<sup>−1</sup> (S2), and 9000 kg·ha<sup>−1</sup> (S3), and incubated with <sup>13</sup>C-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.</div></div>","PeriodicalId":49503,"journal":{"name":"Soil & Tillage Research","volume":"255 ","pages":"Article 106766"},"PeriodicalIF":6.8000,"publicationDate":"2025-07-29","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"Inefficient C sequestration with long term high-level straw return as linked to protected C pools saturation on the North China Plain\",\"authors\":\"Xu Li , Xiaonan Yang , Jingyu Li , Jun Wang , Xin Fu , Zhengping Peng , Hongkai Dang\",\"doi\":\"10.1016/j.still.2025.106766\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<div><div>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<sup>−1</sup> (CK), 2250 kg·ha<sup>−1</sup> (S1), 4500 kg·ha<sup>−1</sup> (S2), and 9000 kg·ha<sup>−1</sup> (S3), and incubated with <sup>13</sup>C-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.</div></div>\",\"PeriodicalId\":49503,\"journal\":{\"name\":\"Soil & Tillage Research\",\"volume\":\"255 \",\"pages\":\"Article 106766\"},\"PeriodicalIF\":6.8000,\"publicationDate\":\"2025-07-29\",\"publicationTypes\":\"Journal Article\",\"fieldsOfStudy\":null,\"isOpenAccess\":false,\"openAccessPdf\":\"\",\"citationCount\":\"0\",\"resultStr\":null,\"platform\":\"Semanticscholar\",\"paperid\":null,\"PeriodicalName\":\"Soil & Tillage Research\",\"FirstCategoryId\":\"97\",\"ListUrlMain\":\"https://www.sciencedirect.com/science/article/pii/S0167198725003204\",\"RegionNum\":1,\"RegionCategory\":\"农林科学\",\"ArticlePicture\":[],\"TitleCN\":null,\"AbstractTextCN\":null,\"PMCID\":null,\"EPubDate\":\"\",\"PubModel\":\"\",\"JCR\":\"Q1\",\"JCRName\":\"SOIL SCIENCE\",\"Score\":null,\"Total\":0}","platform":"Semanticscholar","paperid":null,"PeriodicalName":"Soil & Tillage Research","FirstCategoryId":"97","ListUrlMain":"https://www.sciencedirect.com/science/article/pii/S0167198725003204","RegionNum":1,"RegionCategory":"农林科学","ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q1","JCRName":"SOIL SCIENCE","Score":null,"Total":0}
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.
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.