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长江中下游滩地抑螺防病林生态系统碳水通量及碳贮量研究
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摘要
抑螺防病林作为一种森林类型,其巨大的碳汇功能一直是研究的空白点,本论文选择其两种林分结构类型运用涡相关系统研究其碳、水通量变化及其与影响因子的响应关系,在时间和空间尺度上计量碳源汇值,具体研究内容与结论如下:
     1.抑螺防病林生态系统碳通量规律性动态变化
     白天从7:30左右系统开始吸收CO_2,中午12点左右达到全天的碳汇最高峰,随后开始降低,到18点左右系统逐渐转入碳源作用,系统放出CO_2。这种日变化规律随着季节变化。从全年的尺度上看,3月末4月初,杨树开始展叶,系统整体开始表现为碳汇作用,到10、11月杨树落叶,光合作用基本停止,系统转入碳源作用。
     2.系统碳通量与生态因子的关系:
     1)光合有效辐射 两个系统碳通量与光合有效辐射的关系相同,在白天(PAR>1),系统碳通量与光合有效辐射符合Michaelis-Menten模型,呈双曲线关系。当有效辐射达到1000μmol/m~2.s以上时,系统光合与呼吸都较大,且湖南比安徽的系统光饱和点要高。
     2)温度 安徽站全年夜间碳通量月平均值与气温呈较强的线性相关,即气温升高,夜间碳通量增大。全年夜间碳通量与土壤5cm处温度呈指数递增;湖南站气温对系统碳通量的影响,从月平均值拟合情况来看,气温与碳通量呈对数相关,夜间碳通量与5cm土壤温度的相关性表现为显著的指数关系,y=0.03361e~(0.06684x),相关系数R~2=0.6328。
     3)土壤含水量 湖南站夜间碳通量与15cm处的土壤含水量呈三次多项式规律变化,即土壤含水量在小于0.56(土壤水分与土壤的体积百分比)的时候,含水量增加,系统呼吸量增加,到土壤含水量越过0.56的时候,系统呼吸就会随含水量的增加而快速下降。安徽系统碳通量与土壤含水是量没有得到较好的相关关系。
     4)土壤热通量 安徽站夜间碳通量月平均值与土壤2cm处的热通量呈指数相关,响应方程为:y=0.2697e~(0.0596Gs),相关系数R~2=0.3877;湖南站夜间碳通量还与2cm处土壤热通量呈显著指数相关,响应方程为:y=0.5843e~(0.199Gs),相关系数R~2=0.7516。夜间土壤与外界大气的热交换绝对值越小,系统的呼吸量就越大。
     3.系统碳通量源汇计量
     从2005年4月到2006年3月,安徽站5月为最大碳汇月,累计碳汇值为-2.35×10~5mg/m~2,最大碳源值出现在2月为0.163×10~5mg/m~2;年通量值为-10.16×10~5mg/m~2.a;湖南站6月为最大碳汇月,碳汇值为-1.09×10~5mg/m~2,11月为最大碳
The carbon sink of Snail Control and Schistosomiasis Prevention Forest in the middle and lower reaches of Yangtz River had not been researched. The dissertation analyzed the change law of the carbon and water flux and the relationship of flux and environmental factors and carbon sink and source in different time and space scales in two types of Snail Control and Schistosomiasis Prevention Forest of different structure by the eddy-covariance system. The main contents and conclusions were as follows:
    1. The carbon flux was well-regularited change everyday in the two forests of Anhui and Hunan Province.
    In daytime, the ecosystem began to absorb CO_2 at about 7:30 am, and reached to the Max. about 12:00 at noon, then went down slowly, at about 18:00, the ecosystem began to release CO_2. The value of carbon sink or source varied owing to different season and forest ecosystem. In whole year, from end of March and early of April, the Popular began to unfold leaves, and the forest ecosystem started to absorb CO_2, namely carbon sink. Then at end of October and early of November, the photosynthesis of leaves stopped by defoliation, at the same time, the forest ecosystem became a carbon source nearly.
    2. The relationships of carbon flux of forest ecosystem and environmental factors were as follows:
    1) PAR The relationship of carbon flux and PAR accorded with the model of Michaelis-Menten, namely hyperbolic relationship which carbon sink increased with the accretion of PAR. In Anhui station, when the PAR was upwards 1200 μ mol/m~2.s, the dots dispersed and net CO_2 exchange was among -1.0~-1.5 mg/m~2.s. In Hunan station, when the PAR reached about 1600μ mol/m~2.s, the curve came to the Max. of carbon flux, about -1.2~-1.3mg/m~2.s.
    2) Temperature In Anhui station, monthly average carbon flux of nighttime and air temperature had linear correlation, namely when the air temperature arose, the carbon flux of nighttime augmented. The nighttime flux would increase with soil temperature in 5cm deep by exponential correlation. In Hunan station, the model of the monthly average carbon flux and air temperature was the relationship of logarithmic correlation, i.e. when the plant came to growing season with the air temperature uprising, the forest ecosystem turnaround from carbon source to carbon sink. And the
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