黄河三角洲退化柽柳湿地土壤无机碳库的变化及其驱动因素

Wetland Degradation of Tamarix Chinensis Induced Changes in Soil Inorganic Carbon Stocks and Related Environmental Factors in the Yellow River Delta

  • 摘要:
      目的  湿地生态系统在土壤碳循环过程中起着至关重要的作用。通过分析退化和自然湿地下0 ~ 100 cm的土壤理化性质、土壤无机碳含量及其储量的变化,探究土壤无机碳储量与土壤和植物性质之间的关系。
      方法  以黄河三角洲盐生植物(柽柳)的退化和自然湿地为研究对象,利用全自动土壤无机碳分析仪测定土壤无机碳含量;基于土壤容重、无机碳含量和土壤深度来估算土壤无机碳储量。
      结果  相比较自然湿地,退化湿地具有较低的交换性钙、镁离子含量和碳酸盐相对含量,而土壤容重和pH的差异不大。退化湿地显著降低了土壤无机碳含量和储量,表明湿地退化不利于无机碳在土壤中的固持。通过分析各个土壤深度无机碳储量与土壤理化性质的相关性,指出土壤无机碳储量与土壤容重、含水量、交换性钙和镁离子含量、土壤无机碳含量和地上植物生物量显著正相关,而与土壤电导率负相关。逐步回归分析表明土壤容重、含水量和阳离子含量是导致 0 ~ 100 cm 土壤无机碳储量变化的主要因素。另外,深层土壤无机碳(40 ~ 100 cm)大约贡献了0 ~ 100 cm 总土壤无机碳储量的60%,表明深层土壤对无机碳库的固持发挥着重要作用。
      结论  湿地退化增加了土壤无机碳的损失,保护和恢复湿地有利于土壤无机碳的存储。因此,通过阐释黄河三角洲退化和自然湿地下土壤无机碳储量的变化,可以从无机碳的角度提高湿地土壤碳汇能力,为实现碳中和目标提供科学依据。

     

    Abstract:
      Objective  Wetlands play the important roles in regulating soil carbon cycling. The objective of this study was to explore how soil physicochemical properties, soil inorganic carbon (SIC) content, and SIC stocks of 0-100 cm responded to degraded-natural wetlands, and to clarify the interaction of SIC stocks with soil and plant parameters in the Yellow River Delta.
      Method  In this study, a typical saline halophytes of Tamarix chinensis was selected. SIC content was measured using Automatic Soil Inorganic Carbon Analyzer. The SIC stocks were evaluated based on soil bulk density, SIC content, and soil depth.
      Result  Compared with natural wetlands, degraded wetlands hold lower soil cation (i.e., Ca2 + and Mg2 + ) content, relative content of carbonate, whereas no change in soil pH. Wetland degradation significantly reduced SIC content and stocks, indicating that degraded wetlands showed negative effects on the retention and storage of inorganic carbon in soil. Linear regression analyses demonstrated that SIC stocks were positively related with soil bulk density, water content, cation (Ca2 + and Mg2 + ) content, carbonate, SIC content, and aboveground biomass, while negatively related with soil electrical conductivity. Multiple regression analysis showed that soil bulk density, soil water content, and cation content were mainly driving factors to change SIC stocks of 0 ~ 100 cm. Additionally, the deep soil of 40-100 cm contributed about 60% of SIC stocks, indicating that deep soil plays an important role in SIC storage.
      Conclusion  The results demonstrated that wetland degradation increased SIC loss, whereas the protection and recovery of wetlands could promote SIC storage. Therefore, clarifying the changes in SIC stocks under degraded and natural wetlands in the Yellow River Delta, can provide scientific basis for improving soil carbon sink of wetlands and achieving carbon neutrality in terms of inorganic carbon.

     

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