亚表层培肥结合地膜覆盖对河套灌区盐碱土壤有机碳和无机碳的影响

Effects of subsurface organic ameliorant combined with film mulching on saline soil organic and inorganic carbon in Hetao Irrigation District

  • 摘要: 土壤有机碳(SOC)和无机碳(SIC)是参与全球碳循环的重要碳库。亚表层(10~30 cm)培肥结合地膜覆盖措施是干旱区优化盐碱土壤物理结构和调控土壤水盐环境的有效措施, 然而关于其如何调控0~60 cm土体SOC、SIC分布及其与土壤相关理化性状的关系尚不明确。本研究基于内蒙古河套灌区盐碱土壤6年的田间微区试验, 设置常规对照(CK)、亚表层(10~30 cm)有机培肥(OM)、地膜覆盖(PM)、亚表层有机培肥+地膜覆盖(OM+PM) 4个处理, 测定了2019—2020年0~60 cm剖面SOC、SIC、全碳(TC)含量以及土壤理化指标(土壤水分、盐分、pH和全氮), 分析了TC、SOC、SIC变化特征及其影响因素。结果表明: OM和OM+PM处理较CK和PM处理显著增加0~40 cm土层SOC含量31.9%~195.6% (P<0.05), 显著增加40~60 cm SOC含量33.7%~49.4% (P<0.05, 仅2020年), 但显著降低0~40 cm SIC含量9.9%~35.0% (P<0.05)。基于SOC和SIC的变化, OM+PM较CK处理显著增加2019年20~60 cm TC含量10.4%~39.4% (P<0.05), 并显著增加2020年0~20 cm TC含量13.0% (P<0.05)。回归分析结果进一步说明, 覆膜条件下补充亚表层培肥, 使总碳库变化的主导因素由SIC转变为SOC。冗余分析结果表明土壤理化性质是影响土壤碳库的主要因素(解释度为60.7%~91.9%), 其中全氮和pH是0~40 cm土壤碳库的主要影响因子, 而40~60 cm土壤碳库主要受盐分和pH影响。相关性分析结果表明SOC与SIC表现为完全相反的变化规律, 其中SOC与全氮极显著正相关, 与盐分和pH呈极显著负相关(P<0.01); SIC与全氮呈极显著负相关, 与pH呈极显著正相关(P<0.01)。因此, 亚表层培肥结合地膜覆盖可以通过增加SOC来弥补SIC的损失进而实现碳积累, 是该区域盐碱地增加固碳潜力的有效措施。

     

    Abstract: Soil organic carbon (SOC) and inorganic carbon (SIC) are important carbon pools involved in the global carbon cycle. Subsurface (10−30 cm) organic ameliorant (OM) combined with film mulching (PM) is an effective measure to optimize the physical structure and regulate water and salt movement of saline soil in arid areas. However, the distribution of SOC and SIC in the 0–60 cm soil layer and their relationship with soil physicochemical properties remain unclear. This study was based on a 6-year micro-field experiment of saline soil at the Yichang Experiment Station, which is located in the Hetao irrigation area of Inner Mongolia. Four treatments were set: conventional control (CK), OM, PM, and OM+PM. The levels of SOC, SIC, total carbon (TC), and soil physicochemical property indexes (soil moisture, salinity, pH, and total nitrogen) in the 0−60 cm (0−20 cm, 20−40 cm, and 40−60 cm) soil layer after the harvest of Helianthus annuus during 2019–2020 were measured, and the variation characteristics and influencing factors of TC, SOC, and SIC were analyzed. The results showed that the TC content in the 0−60 cm soil layer and SOC in the 0−40 cm soil layer were mainly affected by OM treatment compared with PM treatment (P<0.01). The SIC content in the 0−40 cm soil layer was affected by OM treatment (P<0.001), PM treatment (P<0.05, except for the 20−40 cm soil layer in 2019), and their interaction (P<0.001); however, the 40−60 cm soil layer was mainly affected by OM treatment (P<0.05). Compared to CK and PM treatments, OM and OM+PM treatments significantly increased SOC content in the 0−40 cm (0−20 cm and 20−40 cm) soil layer by 31.9%−195.6% (P<0.05), and significantly increased SOC content in the 40−60 cm soil layer by 33.7%−49.4% (P<0.05) only in 2020, but significantly decreased SIC content in the 0−40 cm (0−20 cm and 20−40 cm) by 9.9%−35.0% (P<0.05). Based on the changes in SOC and SIC, compared with CK treatment, OM+PM treatment significantly increased TC content in the 20−60 cm (20−40 cm and 40−60 cm) soil layer in 2019 by 10.4%−39.4% (P<0.05), and the TC content of the 0−20 cm layer in 2020 was significantly increased by 13.0% (P<0.05). The regression analysis results further indicated that the dominant factor of the total carbon pool changed from SIC to SOC with the OM+PM treatment. The results of redundancy analysis showed that soil physicochemical properties were the main factors affecting soil TC, SOC, and SIC (explaining 60.7%−91.9% of the variation), and total nitrogen and pH were the main factors affecting soil TC, SOC, and SIC in the 0−40 cm layer, whereas soil TC, SOC, and SIC in the 40−60 cm layer were mainly affected by salinity and pH. Correlation analysis showed that changes in SOC and SIC were completely opposite. Soil organic carbon was positively correlated with total nitrogen and negatively correlated with salinity and pH (P<0.01). Soil inorganic carbon was negatively correlated with total nitrogen and positively correlated with pH (P<0.01). Therefore, OM combined with PM (OM+PM) could compensate for the loss of SIC and realize carbon accumulation by increasing SOC, which is an effective strategy to increase the carbon sequestration potential of saline soil in this region.

     

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