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    毛乌素沙地黑沙蒿群落多尺度呼吸的季节动态和影响因素

    Seasonal dynamics and influencing factors of multi-scale respiration in Artemisia ordosica community in Mu Us Sandy Land of northern China

    • 摘要:
      目的 比较不同观测尺度呼吸对环境因素的响应,特别是对温度和水分的响应,理解多尺度呼吸作用的影响机制,以期提升跨观测尺度呼吸模型模拟精度。
      方法 在宁夏盐池选取典型黑沙蒿群落,于2022年5—10月,在固定样地原位连续监测黑沙蒿叶片、土壤与生态系统呼吸速率(即RlRsRe),拟合呼吸与温度、水分之间的关系,了解多尺度呼吸的季节动态特征及其环境影响因素。
      结果 (1)观测期内,Rl主要受温度调控(R2为63.5%),温度敏感性(Q10)为1.48,Rl日均值最大为5.96 μmol/(m2·s),出现在7月;RsRe季节变化均受水分调控(R2分别为44.4%和50.9%),Q10分别为1.23和1.08,RsRe最大日均值均出现在8月,分别为2.94 μmol/(m2·s)和4.07 μmol/(m2·s)。(2)温度–水分双变量经验模型对RlRsRe的解释能力相较于单变量模型提升程度有限,平均R2分别增加了0.09、0.05和0.02。(3)水分条件是不同观测尺度呼吸温度敏感性是否趋于一致的关键因素。当土壤水分条件较差时(相对土壤含水量WRE < 0.4时),RlRsRe对温度的响应有显著差异,Q10分别为1.34、0.63和0.84;当土壤水分条件较好时(WRE ≥ 0.4),RlRsRe对温度的响应趋于一致,Q10约1.8。
      结论 不同观测尺度呼吸季节变化的调控因素存在差异,而双变量模型对提升不同观测尺度呼吸模拟的精确性作用有限,充分考虑不同观测尺度以及同尺度水分条件的差异是未来准确模拟干旱或半干旱地区呼吸作用的关键。

       

      Abstract:
      Objective By comparing the responses of respiration at different observation scales to environmental factors, especially the similarities and differences in temperature and water responses, we aimed to understand the impact mechanism of multi-scale respiration and improve the simulation of cross observation scale respiration models.
      Method This study selected a typical Artemisia ordosica community in Yanchi, Ningxia of northwestern China as a research site, and conducted continuous observation of Artemisia ordosica leaf, soil, and ecosystem respiration (i.e., Rl, Rs and Re) characteristics from May to October, 2022 using fixed plot measurement and in situ continuous monitoring. By fitting nonlinear and linear equations to the relationship between respiration and temperature and moisture content, we can better understand the seasonal dynamic characteristics of multi-scale respiration and its environmental influencing factors.
      Result (1) The study found that during the observation period, the maximum value of Rl was 5.96 μmol/(m2·s), which occurred in July and was primarily regulated by temperature (R2 = 63.5%) with a temperature sensitivity (Q10) of 1.48. The maximum values of both Rs and Re occurred in August, at 2.94 μmol/(m2·s) and 4.07 μmol/(m2·s), respectively, and their seasonal changes were regulated by moisture (R2 of 44.4% and 50.9%, respectively), with Q10 values of 1.23 and 1.08. (2) The explanatory power of temperature moisture bivariate empirical model for Rl, Rs and Re was limited compared with the univariate model, with an average R2 increase of 0.09, 0.05, and 0.02, respectively. (3) Water availability was the key factor influencing whether the temperature sensitivity of different observation scale respiration tends to be consistent. When soil moisture conditions were poor (relative extractable soil water, WRE < 0.4), there were significant differences in the response of Rl, Rs and Re to temperature, with Q10 values of 1.34, 0.63 and 0.84, respectively; when the soil moisture conditions were sufficient (WRE ≥ 0.4), the response of Rl, Rs and Re to temperature tended to be consistent, with Q10 values ≈ 1.8.
      Conclusion Our study emphasizes the differences in the regulatory factors of seasonal changes in respiration at different observation scales, while the bivariate model has a limited role in improving the accuracy of respiration simulation at different observation scales. Fully considering the differences in observation scale and water conditions is the key to accurately simulating respiration in arid or semiarid areas in the future.

       

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