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胶州湾滨海湿地土壤无机CO2通量析因分析及其吸收机理

Flux factorial analysis and the absorption mechanism of soil inorganic CO2 in coastal wetland of Jiaozhou Bay

  • 摘要: 为了探究滨海湿地土壤无机CO2通量(Rio)特征及土壤对CO2的无机吸收机理,采集胶州湾光滩、盐地碱蓬(Suaeda salsa)沼泽和芦苇(Phragmites australis)沼泽3种典型湿地的土壤,基于室内控制试验,分析了土壤Rio特征;通过构建多因素析因模型,识别了土壤Rio影响因素的主效应及交互效应,并结合同位素示踪技术明确了CO2被土壤吸收后的去向。研究结果表明,胶州湾3种湿地土壤均存在无机吸收CO2的现象,且不同湿地土壤Rio差异显著,其中芦苇沼泽土壤Rio平均值最高,为−0.171 mg/(kg·d),盐地碱蓬沼泽−0.230 mg/(kg·d)和光滩湿地−0.274 mg/(kg·d)的Rio平均值依次减小。土壤Rio与pH显著负相关(r=0.82,p<0.05);析因分析结果表明,pH是解释土壤Rio变化的最主要因素;而土壤pH与电导率的交互作用对土壤Rio影响最强。δ13C同位素示踪试验结果显示,土壤将吸收的δ13C-CO2转化为土壤溶解性无机碳(DIC)和土壤无机碳(SIC),在试验开始之后的1~24 h内,土壤中约10%的DIC转化为SIC,以固态的形式直接固定于土壤中。

     

    Abstract: To explore the characteristics of inorganic CO2 flux (Rio) in coastal wetland soil and the inorganic absorption mechanism of CO2 in soil, soils from three representative wetland types of mudflat, Suaeda salsa marsh, and Phragmites australis marsh in Jiaozhou Bay were collected. Based on the laboratory-controlled experiments, the characteristics of soil Rio were analyzed. The main influencing factors of Rio and their interactions were identified through the construction of a multifactor factorial model. In addition, the distribution of the absorbed CO2 in wetland soil was clarified by isotope tracer technology. Results showed that the CO2 absorption process existed in different types of soils in Jiaozhou Bay coastal wetland and the difference of Rio was significant, with the specific order of Phragmites australis marsh (average Rio of −0.171 mg/(kg·d)), Suaeda salsa marsh (average Rio of −0.230 mg/(kg·d)), mudflat (average Rio of −0.274 mg/(kg·d)). The soil Rio was negatively correlated with pH (r=0.82, p<0.05). Results of multifactor factorial model showed that the pH was the most significant influence for soil Rio in coastal wetland, and the interaction between pH and EC was the most intense. The 13C isotope tracer showed that the absorbed CO2 was converted into soil dissolved inorganic carbon and soil inorganic carbon. In addition, within 1 - 24 h of the reaction, about 10% of dissolved inorganic carbon in the soil was converted to soil inorganic carbon, fixed directly into the soil in a solid form.

     

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