Lulu Bai , Peng Shi , Jun Xiao , Zhanbin Li , Peng Li , Xiaohuang Liu , Duoxun Xu , Bo Wang
{"title":"溅蚀下土壤团聚体破碎形成对土壤有机碳矿化的驱动机制","authors":"Lulu Bai , Peng Shi , Jun Xiao , Zhanbin Li , Peng Li , Xiaohuang Liu , Duoxun Xu , Bo Wang","doi":"10.1016/j.still.2025.106761","DOIUrl":null,"url":null,"abstract":"<div><div>Splash erosion initiates water erosion and significantly affects soil organic carbon (SOC) dynamics by fragmenting soil particles and influencing SOC mineralization. However, the mechanisms linking soil aggregate turnover to SOC mineralization and CO<sub>2</sub> emissions remain unclear. To investigate the fate of soil aggregates and SOC under erosion conditions, raindrop splash erosion experiments were conducted at rainfall intensities of 60, 90, and 120 mm/h. Four types of rare earth oxides were used to label soil aggregates of various sizes: large (2–5 mm), medium (1–2 mm), small (0.25–1 mm), and micro (<0.25 mm), followed by 56-day soil incubation. The results indicated that the breakdown and formation of soil aggregates were significantly influenced by rainfall intensity. The average cumulative breakdown rate of soil aggregates increased with higher rainfall intensities: 120 mm/h (12.02 %) > 90 mm/h (9.49 %) > 60 mm/h (8.19 %). In contrast, the average cumulative formation rate soil aggregates exhibited the opposite trend: 60 mm/h (12.25 %) > 90 mm/h (10.90 %) > 120 mm/h (8.32 %). The primary mode of soil aggregate breakdown was from medium to small, with the highest breakdown rate on day 0, which increased with rainfall intensity: 120 mm/h (58.49 %) > 90 mm/h (48.07 %) > 60 mm/h (43.61 %). Simultaneously, as rainfall intensity increased, the SOC mineralization rate and associated CO<sub>2</sub> emissions consistently rose, and the total CO<sub>2</sub> emissions were: 120 mm/h (23.853 mg·kg<sup>−1</sup>) > 90 mm/h (21.827 mg·kg<sup>−1</sup>) > 60 mm/h (19.522 mg·kg<sup>−1</sup>). Furthermore, a structural equation model was developed to elucidate the relationship between soil aggregate turnover and SOC dynamics, highlighting that direct soil aggregate breakdown effects on SOC mineralization were significantly greater than its indirect effects via other pathways. This direct effect intensified with increasing rainfall intensity, and its path coefficients followed the order: 120 mm/h (0.625) > 90 mm/h (0.545) > 60 mm/h (0.533). These results underscore the significant role of soil aggregate turnover in driving SOC dynamics, thereby providing a theoretical foundation for soil carbon sequestration strategies and enhancing carbon capture capacity.</div></div>","PeriodicalId":49503,"journal":{"name":"Soil & Tillage Research","volume":"254 ","pages":"Article 106761"},"PeriodicalIF":6.1000,"publicationDate":"2025-07-19","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"0","resultStr":"{\"title\":\"Driving mechanisms of the soil aggregate breakdown-formation on soil organic carbon mineralization under splash erosion\",\"authors\":\"Lulu Bai , Peng Shi , Jun Xiao , Zhanbin Li , Peng Li , Xiaohuang Liu , Duoxun Xu , Bo Wang\",\"doi\":\"10.1016/j.still.2025.106761\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<div><div>Splash erosion initiates water erosion and significantly affects soil organic carbon (SOC) dynamics by fragmenting soil particles and influencing SOC mineralization. However, the mechanisms linking soil aggregate turnover to SOC mineralization and CO<sub>2</sub> emissions remain unclear. To investigate the fate of soil aggregates and SOC under erosion conditions, raindrop splash erosion experiments were conducted at rainfall intensities of 60, 90, and 120 mm/h. Four types of rare earth oxides were used to label soil aggregates of various sizes: large (2–5 mm), medium (1–2 mm), small (0.25–1 mm), and micro (<0.25 mm), followed by 56-day soil incubation. The results indicated that the breakdown and formation of soil aggregates were significantly influenced by rainfall intensity. The average cumulative breakdown rate of soil aggregates increased with higher rainfall intensities: 120 mm/h (12.02 %) > 90 mm/h (9.49 %) > 60 mm/h (8.19 %). In contrast, the average cumulative formation rate soil aggregates exhibited the opposite trend: 60 mm/h (12.25 %) > 90 mm/h (10.90 %) > 120 mm/h (8.32 %). The primary mode of soil aggregate breakdown was from medium to small, with the highest breakdown rate on day 0, which increased with rainfall intensity: 120 mm/h (58.49 %) > 90 mm/h (48.07 %) > 60 mm/h (43.61 %). Simultaneously, as rainfall intensity increased, the SOC mineralization rate and associated CO<sub>2</sub> emissions consistently rose, and the total CO<sub>2</sub> emissions were: 120 mm/h (23.853 mg·kg<sup>−1</sup>) > 90 mm/h (21.827 mg·kg<sup>−1</sup>) > 60 mm/h (19.522 mg·kg<sup>−1</sup>). Furthermore, a structural equation model was developed to elucidate the relationship between soil aggregate turnover and SOC dynamics, highlighting that direct soil aggregate breakdown effects on SOC mineralization were significantly greater than its indirect effects via other pathways. This direct effect intensified with increasing rainfall intensity, and its path coefficients followed the order: 120 mm/h (0.625) > 90 mm/h (0.545) > 60 mm/h (0.533). These results underscore the significant role of soil aggregate turnover in driving SOC dynamics, thereby providing a theoretical foundation for soil carbon sequestration strategies and enhancing carbon capture capacity.</div></div>\",\"PeriodicalId\":49503,\"journal\":{\"name\":\"Soil & Tillage Research\",\"volume\":\"254 \",\"pages\":\"Article 106761\"},\"PeriodicalIF\":6.1000,\"publicationDate\":\"2025-07-19\",\"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/S0167198725003150\",\"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/S0167198725003150","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}
Driving mechanisms of the soil aggregate breakdown-formation on soil organic carbon mineralization under splash erosion
Splash erosion initiates water erosion and significantly affects soil organic carbon (SOC) dynamics by fragmenting soil particles and influencing SOC mineralization. However, the mechanisms linking soil aggregate turnover to SOC mineralization and CO2 emissions remain unclear. To investigate the fate of soil aggregates and SOC under erosion conditions, raindrop splash erosion experiments were conducted at rainfall intensities of 60, 90, and 120 mm/h. Four types of rare earth oxides were used to label soil aggregates of various sizes: large (2–5 mm), medium (1–2 mm), small (0.25–1 mm), and micro (<0.25 mm), followed by 56-day soil incubation. The results indicated that the breakdown and formation of soil aggregates were significantly influenced by rainfall intensity. The average cumulative breakdown rate of soil aggregates increased with higher rainfall intensities: 120 mm/h (12.02 %) > 90 mm/h (9.49 %) > 60 mm/h (8.19 %). In contrast, the average cumulative formation rate soil aggregates exhibited the opposite trend: 60 mm/h (12.25 %) > 90 mm/h (10.90 %) > 120 mm/h (8.32 %). The primary mode of soil aggregate breakdown was from medium to small, with the highest breakdown rate on day 0, which increased with rainfall intensity: 120 mm/h (58.49 %) > 90 mm/h (48.07 %) > 60 mm/h (43.61 %). Simultaneously, as rainfall intensity increased, the SOC mineralization rate and associated CO2 emissions consistently rose, and the total CO2 emissions were: 120 mm/h (23.853 mg·kg−1) > 90 mm/h (21.827 mg·kg−1) > 60 mm/h (19.522 mg·kg−1). Furthermore, a structural equation model was developed to elucidate the relationship between soil aggregate turnover and SOC dynamics, highlighting that direct soil aggregate breakdown effects on SOC mineralization were significantly greater than its indirect effects via other pathways. This direct effect intensified with increasing rainfall intensity, and its path coefficients followed the order: 120 mm/h (0.625) > 90 mm/h (0.545) > 60 mm/h (0.533). These results underscore the significant role of soil aggregate turnover in driving SOC dynamics, thereby providing a theoretical foundation for soil carbon sequestration strategies and enhancing carbon capture capacity.
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.