黄土高原不同盖度生物结皮土壤呼吸特征及其影响因素
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国家自然科学基金青年项目(42407362);河北省自然科学基金项目(D2021205011);河北师范大学科技类基金项目(L2021B28);中央高校基本科研业务费(Z1090324158)


Characteristics of biocrust soil respiration with different cover and their influencing factors on the Chinese Loess Plateau
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    摘要:

    生物结皮是旱地土壤碳排放的重要参与者,但不同盖度的生物结皮土壤呼吸特征可能存在明显差异。针对黄土高原风沙土发育的藓结皮,以裸土为对照,分别设置了5%、25%、50%、75%和100%的生物结皮盖度,通过测定不同盖度下的生物结皮土壤呼吸速率和土壤性质,对比分析了其土壤呼吸速率和土壤性质的差异,并基于结构方程模型进一步探究了其土壤呼吸速率差异的内在机制。结果表明:(1)不同盖度生物结皮土壤呼吸速率的日变化趋势基本一致,且日际变化主要受降雨的影响。不同盖度的生物结皮土壤呼吸速率日变化均呈先升高(7:00-13:00,)后降低(13:00-17:00)的趋势,其范围为0.66-4.058 μmol m-2 s-1,且雨后激发效应随生物结皮盖度的增加而增大。(2)生物结皮的土壤呼吸速率随其盖度的增加而明显升高。与裸土(1.09 μmol m-2 s-1)相比,生物结皮盖度由高到低其土壤呼吸速率的增幅分别为28.2%、17.1%、9.3%、4.9%和0.6%;且生物结皮盖度越高其土壤呼吸速率的温度敏感性越强。(3)生物结皮盖度的增加通过提高土壤含水量、藓生物量、细颗粒含量(黏粉粒)直接对土壤呼吸速率产生显著的正影响(P<0.05),同时还能通过提高藓生物量对土壤有机碳产生正影响进而间接促进土壤呼吸速率。综上,黄土高原生物结皮土壤呼吸速率对其盖度变化具有明显响应,生物结皮盖度的增加通过提高土壤含水量、改善土壤机械组成以及增加苔藓生物量等明显促进了土壤碳排放速率。因此,未来气候变化加剧下生物结皮盖度的变化会引起其碳排放速率的差异,这在准确估算黄土高原碳排放量时应该被充分考虑。

    Abstract:

    Biocrusts,as key participants in the carbon (C) cycle of drylands,can substantially influence dryland C emissions via respiration. However,the respiration rate (Rs) of biocrusts may differ significantly among different cover levels,and this remains poorly understood. In this study,we set up 5%,25%,50%,75%,and 100% cover on moss biocrusts developed in the aeolian sandy soil on the Chinese Loess Plateau,with bare soil as the control. Biocrust Rs were continuously monitored using a soil C flux system (Li-870). We measured soil properties (e.g.,soil temperature,moisture,and soil organic C). We further analyzed the differences in Rs and soil properties among different biocrust cover levels as well. Finally,we elucidated the mechanism underlying the differences in Rs among different biocrust cover levels through the construction of a structural equation model. Our results showed that: (i) the daily trends in Rs of different biocrust cover were generally consistent and their Rs were mainly influenced by rainfall. The daily variation of Rs of biocrusts with different cover levels showed a trend of increasing (7:00-13:00) and then decreasing (13:00-17:00),which ranged from 0.66 to 4.06 μmol m-2 s-1. The excitation effects following rainfall intensified as biocrust cover levels increased. (ii) Rs of biocrusts increased significantly with their cover. Compared with bare soil (1.09 μmol m-2 s-1),the increase in Rs were 28.2%,17.1%,9.3%,4.9%,and 0.6% for 100%,75%,50%,25%,and 5% biocrust cover,respectively. Meanwhile,the temperature sensitivity of Rs of higher biocrust cover was stronger. (iii) An increase in biocrust cover significantly enhanced Rs directly by elevating soil water content,moss biomass,and fines content (clay and silt particles). Also,an increase in biocrust cover positively affected soil organic C by increasing moss biomass and indirectly promoted Rs. In summary,the Rs of the biocrust responded significantly to the change of its cover,and the increase of the biocrust cover contributed significantly to the soil C emission rate by increasing the soil water content,improving the soil mechanical composition,and increasing the moss biomass. Consequently,changes in biocrust cover may occur under future climate change intensification which could lead to differences in C emission and should be taken into account when accurately estimating C emissions in the Loess Plateau of China.

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李兵强,姚小萌,孟凡,窦韦强.黄土高原不同盖度生物结皮土壤呼吸特征及其影响因素.生态学报,2025,45(8):3887~3897

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