草业学报 ›› 2026, Vol. 35 ›› Issue (5): 85-98.DOI: 10.11686/cyxb2025230
连佳丽1(
), 陈婧1, 杨雪琴1, 赵莹1, 罗叙1, 韩翠1, 李建平1,2(
)
收稿日期:2025-06-09
修回日期:2025-08-08
出版日期:2026-05-20
发布日期:2026-03-11
通讯作者:
李建平
作者简介:Corresponding author. E-mail: lijianpingsas@163.com基金资助:
Jia-li LIAN1(
), Jing CHEN1, Xue-qing YANG1, Ying ZHAO1, Xu LUO1, Cui HAN1, Jian-ping LI1,2(
)
Received:2025-06-09
Revised:2025-08-08
Online:2026-05-20
Published:2026-03-11
Contact:
Jian-ping LI
摘要:
研究降水对荒漠草原生态系统土壤有机碳(SOC)动态的调控机制,对于深入理解脆弱干旱环境下的碳循环过程和稳定机制具有重要意义。以宁夏盐池县荒漠草原为研究对象,采用遮雨棚技术模拟5个降水梯度,分别为正常降水的33%、66%、100%、133%和166%(记为P33、P66、PCK、P133、P166),探讨荒漠草原土壤有机碳(SOC)分布格局及碳(C)库稳定性在不同降水变化模式下的演变动态,揭示降水变化对土壤C库稳定性的影响机制。结果表明:1)各降水处理下,SOC、土壤可溶性有机碳(DOC)及土壤微生物生物量碳(MBC)含量均随土层深度增加而递减,表层(0~10 cm)含量最高;同一土层中,增水处理显著提高了SOC、土壤易氧化有机碳(EOC)及MBC含量,而DOC含量在减水处理下显著升高;2)土壤有机C库稳定性指标显示,增水处理显著提升了碳库活度(CA)、碳库管理指数(CPMI),其中P133处理的CPMI达192.49%,表明适度增水可增强C库稳定性;3)Pearson相关性分析和结构方程表明,降水通过影响土壤水分与土壤酶活性对活性SOC组分产生影响,进而影响CPMI,其中DOC对CPMI的影响为主要通路。因此,增水处理可有效提高荒漠草原活性SOC组分及CPMI,活性SOC对于降水变化极为敏感,可作为表征降水变化对荒漠草原土壤C库稳定性影响的重要参数。
连佳丽, 陈婧, 杨雪琴, 赵莹, 罗叙, 韩翠, 李建平. 降水变化对荒漠草原土壤有机碳分布与有机碳库稳定性的影响[J]. 草业学报, 2026, 35(5): 85-98.
Jia-li LIAN, Jing CHEN, Xue-qing YANG, Ying ZHAO, Xu LUO, Cui HAN, Jian-ping LI. Effects of precipitation changes on the soil organic carbon distribution and stability of organic carbon pool in desert steppe[J]. Acta Prataculturae Sinica, 2026, 35(5): 85-98.
图1 研究区概况a: 荒漠草原野外试验区位置、设计和降水调控装置Location, design and precipitation control device of desert grassland field test area; 该地图基于宁夏回族自治区标准地图服务网站宁S(2022)第001号标准地图制作,底图边界无修改。This map was made based on the standard map of Ningxia Hui Autonomous Region’s Standard Map Service Website [宁S(2022)第001号], and the boundaries didn’t modified. b: 1981-2023年宁夏盐池县降水量和气温变化Precipitation and air temperature changes in Yanchi County of Ningxia from 1981 to 2023; c: 荒漠草原40 a间(1981-2023年)降水概率密度函数和2020-2023年模拟降水处理的统计变化The probability density function of precipitation in desert steppe for 40 years (1981-2023) and the statistical changes of simulated precipitation treatment from 2020 to 2023.
Fig.1 Profile of the study area
处理 Treatment | 土壤有机碳 Soil organic carbon | 土壤全氮 Soil total nitrogen | 土壤全磷 Soil total phosphorus |
|---|---|---|---|
| P33 | 1.64±0.47b | 0.16±0.05b | 0.21±0.04a |
| P66 | 1.87±0.61b | 0.20±0.06b | 0.22±0.03a |
| PCK | 2.51±1.02ab | 0.26±0.13ab | 0.24±0.04a |
| P133 | 2.14±0.63b | 0.20±0.07b | 0.23±0.02a |
| P166 | 3.08±1.36a | 0.33±0.18a | 0.25±0.05a |
表1 研究区降水处理6 a(2018-2023)后的土壤理化性质
Table 1 Soil physical and chemical properties after 6 years of precipitation treatment (2018-2023) in the study area (g·kg-1)
处理 Treatment | 土壤有机碳 Soil organic carbon | 土壤全氮 Soil total nitrogen | 土壤全磷 Soil total phosphorus |
|---|---|---|---|
| P33 | 1.64±0.47b | 0.16±0.05b | 0.21±0.04a |
| P66 | 1.87±0.61b | 0.20±0.06b | 0.22±0.03a |
| PCK | 2.51±1.02ab | 0.26±0.13ab | 0.24±0.04a |
| P133 | 2.14±0.63b | 0.20±0.07b | 0.23±0.02a |
| P166 | 3.08±1.36a | 0.33±0.18a | 0.25±0.05a |
图3 降水变化下各土层有机碳及其组分含量不同大写字母表示同一土层不同处理间差异显著(P<0.05);不同小写字母表示同一处理不同土层间差异显著(P<0.05)。下同。Different capital letters indicate significant differences at the 0.05 level among different treatments of the same soil layer; different lowercase letters indicate significant differences at the 0.05 level among different soil layers of the same treatment. The same below.
Fig.3 The content of organic carbon and its components in each soil layer under the change of precipitation
处理 Treatment | 土壤碳库活度 Carbon pool activity (CA) | 碳库活度指数 Carbon pool activity index (CAI) | 碳库指数 Carbon pool index (CPI) | 碳库管理指数 Carbon pool management index (CPMI, %) |
|---|---|---|---|---|
| P33 | 0.30±0.06b | 0.66±0.32c | 0.72±0.25b | 49.90±35.37b |
| P66 | 0.32±0.14b | 0.62±0.21c | 0.83±0.31ab | 53.84±34.55b |
| PCK | 0.54±0.24b | 1.00±0.00bc | 1.00±0.00ab | 100.00±0.00b |
| P133 | 2.19±2.05a | 2.88±2.32a | 0.88±0.33ab | 192.49±96.53a |
| P166 | 0.93±0.58b | 2.05±1.99ab | 1.36±0.74a | 190.07±157.09a |
表2 降水变化下的土壤碳库管理指数
Table 2 Soil carbon pool management index under the change of precipitation
处理 Treatment | 土壤碳库活度 Carbon pool activity (CA) | 碳库活度指数 Carbon pool activity index (CAI) | 碳库指数 Carbon pool index (CPI) | 碳库管理指数 Carbon pool management index (CPMI, %) |
|---|---|---|---|---|
| P33 | 0.30±0.06b | 0.66±0.32c | 0.72±0.25b | 49.90±35.37b |
| P66 | 0.32±0.14b | 0.62±0.21c | 0.83±0.31ab | 53.84±34.55b |
| PCK | 0.54±0.24b | 1.00±0.00bc | 1.00±0.00ab | 100.00±0.00b |
| P133 | 2.19±2.05a | 2.88±2.32a | 0.88±0.33ab | 192.49±96.53a |
| P166 | 0.93±0.58b | 2.05±1.99ab | 1.36±0.74a | 190.07±157.09a |
图4 降水变化下各土层的土壤酶活性变化BG: β-1,4-葡萄糖苷酶β-1,4-glucosidase; CBH: 纤维二糖水解酶Cellobiose hydrolase; NAG: β-1,4-N-乙酰氨基葡萄糖苷酶β-1,4-N-acetylglucosaminidase; AKP: 碱性磷酸酶Alkaline phosphatase. 下同The same below.
Fig.4 Changes in soil enzyme activity with each soil layer under the change of precipitation change
图5 土壤理化性质、酶及有机碳组分与土壤碳库稳定性的相关性分析CA: 碳库活度Carbon pool activity; CAI: 碳库活度指数Carbon pool activity index; CPMI: 碳库管理指数Carbon pool management index; SOC: 土壤有机碳Soil organic carbon; EOC: 易氧化有机碳Easily oxidized organic carbon; DOC: 可溶性有机碳Dissolved organic carbon; MBC: 微生物生物量碳Microbial biomass carbon; M: 土壤水分Soil moisture; T: 土壤温度Soil temperature; TP: 全磷Total phosphorus; TN: 全氮Total nitrogen. *: P<0.05; **: P<0.01。下同The same below.
Fig.5 Correlation analysis between soil physical and chemical properties, soil enzymes, soil organic carbon components and soil carbon pool stability
图6 降水变化对土壤碳库管理指数影响的结构方程模型和标准化总效应Precipitation: 降水量变化Precipitation change; Enzyme: 4种土壤酶活性Activity of four kinds soil enzymes (BG, CBH, NAG, AKP); CPMI: 碳库管理指数Carbon pool management index; GOF: 模型拟合度Goodness-of-fit. 图中单箭头表示假设的因果关系方向,实线和虚线分别代表正向和负向路径,线的粗细反映效应程度。The single arrows in the figure represent the hypothesized direction of causality. The solid and dotted lines represent positive and negative pathways, respectively. The thickness of the line reflects the extent of the effect. ***: P<0.001.
Fig.6 The structural equation model analysis (SEM) and standardized total effect for the effects of precipitation change on the carbon pool management index
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