稻-油轮作农田油菜生长季土壤呼吸作用及其影响因素分析

Soil respiration and its influencing factors in rice-rape rotation fields during rape growing season

  • 摘要: 本文以西南地区稻 油轮作农田为研究对象, 于2009年11月-2010年4月油菜生长期间采用静态暗箱法进行了土壤呼吸速率的观测, 通过选择植株生长处、株间及行间3个样点研究土壤呼吸速率的时间变化及空间异质性, 综合分析了土壤温度、土壤湿度、根系生物量、土壤有机碳以及C/N对土壤呼吸作用的影响。结果表明, 油菜季土壤呼吸速率的日变化为单峰型, 最大值出现在下午15:00。土壤呼吸速率的季节变化显著, 呈现为先降低后升高的变化趋势, 最低值出现在2010年1月。在植株尺度上, 土壤呼吸作用存在明显的空间异质性, 较高的土壤呼吸速率通常出现在靠近油菜植株的地方, 表现为: 植株生长处(336.71 mg·m-2·h-1)>株间(248.48 mg·m-2·h-1)>行间(141.77 mg·m-2·h-1)。土壤呼吸作用中根呼吸作用所占比例的季节变化呈单峰型, 表现为生长初期小于生长中期和后期。在整个油菜生长季, 根呼吸对土壤呼吸的贡献为25.78%~72.61%, 平均为51.03%。土壤呼吸速率受多个环境因子的影响, 与地表温度呈显著指数关系, 与根系生物量呈显著线性关系, 与土壤微生物生物量碳、易氧化有机碳及颗粒有机碳存在显著或极显著正相关。

     

    Abstract: Soil is a major biosphere for carbon (C) reserve, containing globally twice C as much as the atmosphere and three times as much as vegetation. After photosynthesis, soil respiration remains the second largest carbon flux in the ecosystem, accounting for 60%~90% of total ecosystem respiration. Small changes in soil respiration across large areas have been reported to produce significant effects on CO2 atmospheric concentrations. This has led to potential positive feedbacks between increasing temperature and enhanced soil respiration that in turn accelerate global warming. Therefore, soil respiration has become a critical research field in global carbon cycle. Soil respiration in specific ecosystems has been characterized in terms of magnitude, and temporal and spatial variability. Detail on soil respiration and the controlling factors have been critical for constraining ecosystem C budget and understanding soil response to global climate change. In this paper a rice-rape rotation field in Southwest China was used to study the spatial and temporal variations in soil respiration during rape growth season in November 2009 through April 2010. Soil respiration rates were measured on monthly basis using the closed chamber technique and three measurement positions (on-plant, inter-plants and inter-rows) selected. The results showed that diurnal patterns of soil respiration followed uni-humped curves. Maximum soil respiration rates appeared at 15:00 and minimum at 7:00. Soil respiration rates showed significant seasonal changes: initially declined and then increased during the experimental period. The order of daily average soil respiration rates was March 27, 2010 (293.25 mg·m-2·h-1) > April 17, 2010 (275.22 mg·m-2·h-1) > February 28, 2010 (186.25 mg·m-2·h-1) > January 28, 2010 (164.44 mg·m-2·h-1) > November 22, 2009 (140.25 mg·m-2·h-1) > December 20, 2009 (102.07 mg·m-2·h-1). There were significant spatial variations in soil respiration patterns at the plant scale. Higher soil respiration rates tended to occur near rape plants during growth season. On-plant soil respiration rates were highest (336.71 mg·m-2·h-1), followed by inter-plant (248.48 mg·m-2·h-1) and then inter-row (141.77 mg·m-2·h-1). Soil respiration was calculated as the sum of root and microbial respiration. The contribution of each group required thorough understanding in order to evaluate the implications of environmental changes for soil carbon cycling and sequestration. In this study, direct microbial respiration rates were observed in inter-row plots without roots. Therefore root respiration was the difference between soil respiration rates of planted and unplanted soils. Average contribution of root respiration to soil respiration was 51.03%, with a range of 25.78%~72.61%. Soil respiration rate was affected by several environmental factors. It was exponentially correlated with soil temperature, linearly correlated with root biomass, and positively correlated with soil microbial biomass carbon. Soil respiration was also readily affected by oxidized carbon and particulate organic carbon.

     

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