模拟氮沉降对石栎和苦槠幼苗土壤呼吸的影响
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国家重点基础研究发展规划(973)项目(2005CB422207,2005CB422208,2010CB428503);国家自然科学基金项目(4067113);科技部重大国际合作项目(2008DFA31810);科技部重大基础性项目(2007FY110300-8);浙江省重大科技专项(2008C13042)


Effect of simulated nitrogen deposition on the soil respiration of Lithocarpus glabra and Castanopsis sclerophylla
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    摘要:

    用LI-8100开路式土壤碳通量测量系统测定模拟氮沉降4种不同处理水平(0、60、120\,240 kg · hm-2 · a-1)下石栎(Lithocarpus glabra)和苦槠(Castanopsis sclerophylla)幼苗的土壤呼吸速率及土壤温度、含水量对其土壤呼吸的影响。结果表明,氮沉降对土壤呼吸的影响根据施氮水平和幼苗的种类不同而异。低氮(60 kg · hm-2 · a-1)处理下石栎和苦槠的土壤呼吸速率平均值分别为(4.014±0.812)μmol · m-2 · s-1和(5.170±0.689)μmol · m-2 · s-1,比对照组(0 kg · hm-2 · a-1)土壤呼吸速率平均值(3.802±0.948)μmol · m-2 · s-1和(3.557±0.906)μmol · m-2 · s-1分别高5%和45%;两树种在中、高氮处理下均出现对土壤呼吸明显的抑制。其中石栎中、高氮实验组的土壤呼吸速率分别为(2.653±0.681)μmol · m-2 · s-1、(2.592±0.736)μmol · m-2 · s-1, 比对照组低27%和29%。苦槠中、高氮实验组的土壤呼吸速率为(3.563±0.402)μmol · m-2 · s-1、(3.466±0.994)μmol · m-2 · s-1, 比对照组低7%和8%;石栎在高氮(240 kg · hm-2 · a-1)处理水平下,其土壤呼吸速率同10cm土壤温度之间呈现显著的指数关系(R2=0.811,P=0.001),而在低、中氮实验均未发现有明显指数关系。苦槠各处理水平下其土壤呼吸与土壤温度之间均未发现有明显的指数关系;在土壤呼吸与5cm土壤含水量的相关性方面,仅有苦槠高氮实验组表现出明显的二次方程关系(R2=0.722),而其低、中氮实验组及石栎各实验组均未有明显的相关性;与单因素(温度、含水量)拟合它们与土壤呼吸速率的方程相比,多元回归分析得到的土壤呼吸速率同土壤温度和含水量之间的拟合方程在P=0.05水平上能更好地解释土壤呼吸的变化情况。石栎和苦槠在氮沉降处理下的土壤呼吸温度系数Q10值分别为2.29、1.95、1.59和1.46、1.41、1.76,同对照组2.64和1.78相比,均有明显降低,且两者Q10值的变化分别呈递减和先减小后增大的趋势,表明氮沉降是影响石栎和苦槠土壤CO2通量的一个重要因素。

    Abstract:

    To investigate the response of soil respiration of Lithocarpus glabra and Castanopsis sclerophylla seedlings for increased nitrogen deposition, a field experiment with 4 simulated nitrogen deposition levels, 0kg · hm-2 · a-1, 60 kg · hm-2 · a-1, 120 kg · hm-2 · a-1 and 240 kg · hm-2 · a-1, were conducted. The measurement of soil respiration was made by a LI-8100 soil CO2 efflux system. The soil temperature at 10 cm depth and soil moisture at 5 cm depth also were recorded at the same time. Results show that: (1) The soil respiration rate of Lithocarpus glabra and Castanopsis sclerophylla seedlings were fluctuated significantly under different nitrogen deposition levels. To Lithocarpus glabra seeedling, the mean rate of soil respiration was (4.014±0.812)μmol · m-2 · s-1 under 60 kg · hm-2 · a-1 level and increased 5% comparing with control level (0 kg · hm-2 · a-1). The mean rate of soil respiration were (2.653±0.681)μmol · m-2 · s-1 and (2.592±0.736)μmol · m-2 · s-1 under 120 kg · hm-2 · a-1 and 240 kg · hm-2 · a-1 level, and reduced 27% and 29% respectively comparing with control level (0 kg · hm-2 · a-1). The mean rate of soil respiration of Castanopsis sclerophylla seedling, was (5.170±0.689)μmol · m-2 · s-1 under 60 kg · hm-2 · a-1 level and increased 45% comparing with control level ( 0 kg · hm-2 · a-1). The mean rate of soil respiration were (3.563±0.402)μmol · m-2 · s-1 and (3.466±0.994)μmol · m-2 · s-1 under 120 kg · hm-2 · a-1 and 240 kg · hm-2 · a-1level, as well as reduced 7% and 8% respectively. (2) The relationship between soil respiration and soil temperature at 10 cm of Lithocarpus glabra seedling was significant (R2=0.811,P=0.001) under 240 kg · hm-2 · a-1 level, which could be described by exponential equation. While, under the 4 simulated nitrogen deposition levels, the relationships between soil respiration and soil temperature at 10 cm of Castanopsis sclerophylla were not significant. However, both of Lithocarpus glabra and Castanopsis sclerophylla, the relationship between soil respiration and soil moistures at 5 cm depth also were not significant. The relationships between soil respiration and soil temperature at 10 cm and soil moisture at 5 cm depth were analyzed by multiple regression equation. The regression equations had more predicative capability than those using only temperature or moisture as a single independent variable at the P=0.05 level,. The regression equations of Lithocarpus glabra and Castanopsis sclerophylla soil respiration can interpret the results 89.9%-85.4% and 87.9%-78.7% respectively. the R2 values of Lithocarpus glabra seedling soil respiration tended to decrease with nitrogen deposition, but the R2 values of Castanopsis sclerophylla soil respiration tended to increase with nitrogen deposition in 60 kg · hm-2 · a-1 and 120 kg · hm-2 · a-1, and decrease with 240 kg · hm-2 · a-1. (3) The Q10 values at four different nitrogen treatment levels of Lithocarpus glabra and Castanopsis sclerophylla seedlings were 2.29、1.95、1.59 and 1.46、1.41、1.76 respectively. Compared with which at control level, the Q10 values of Lithocarpus glabra seedling soil respiration tended to decrease with nitrogen deposition, but the Q10 values of Castanopsis sclerophylla seedling soil respiration tended to decrease with nitrogen deposition in 60 kg · hm-2 · a-1 and 120 kg · hm-2 · a-1, and increased with 240 kg · hm-2 · a-1. But Lithocarpus glabra and Castanopsis sclerophylla soil respiration, the Q10 are all lower than the control level (0 kg · hm-2 · a-1). Both of them, the Q10 values at control level are 2.64 and 1.78 respectively. The results indicated that nitrogen deposition is an important factor in affecting soil CO2 efflux of Lithocarpus glabra and Castanopsis sclerophylla seedlings.

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李凯,江洪,由美娜,曾波.模拟氮沉降对石栎和苦槠幼苗土壤呼吸的影响.生态学报,2011,31(1):82~89

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