长白山自然保护区生态系统碳平衡研究

运用已建立的EPPML生物地球化学循环模型,对1995年长白山自然保护区生态系统的碳平衡状况进行了模拟.模拟结果表明,该保护区植被的年净初级生产力NPP(碳量)]为1.332×10⁶t·a^-1,以阔叶红松林和云冷杉林最高,分别为0.540×10⁶t·a^-1和0.428×10⁶t·a^-1.这2种林型是长白山面积最大、生产力最高的林型,其生产力的模拟结果对整个保护区的碳循环和碳平衡影响最大,前者的准确性决定了后者的可靠性.总的来说,模拟值不仅在整个保护区不同植被带和气候带的相对比较中是符合常规的,而且在与相当分散的实测数据的绝对比较中也是比较准确的.该保护区的植被具有明显的碳汇功能,主要表现为植被碳量的增长,每年增长约1.058×10⁶t·a^-1.阔叶红松林的年碳量增长最大(0.452 × 10⁶t·a^-1),云冷杉林其次(0.339×10⁶t·a^-1)这2种林型对整个保护区的碳汇功能起着至关重要的决定性作用.其它依次为:长白落叶松林、阔叶林、草甸、灌丛、高山苔原、岳桦林和高山流砾滩草类.1995年该保护区土壤有机质的分解碳量比凋落物碳量高0.169×10⁶t·a^-1,除草灌土壤出现有机质的积累,高山苔原和高山流砾滩土壤有机质的分解与积累处于近似平衡状态外,乔木林下土壤有机质的分解量均为凋落物量的1.5～2.0倍.

Carbon Budget of Ecosystem in Changbai Mountain Natural Reserve

The study used EPPML, a biological geochemistry cycle model that was built, to simulate the carbon budget for ecosystems in Changbai Mountain Natural Reserve. The results indicated that the annual net primary productivity NPP (carbon)] of the natural reserve was 1.332×10⁶t·a^-1. The annual NPP of mixed broad-leaved and Korean pine forest and spruce-fir forest were maximal, 0.540×10⁶t·a^-1 and 0.428×10⁶t·a^-1 respectively. The area and productivity of the two stands were maximal in Changbai Mountain, therefore, the simulating productivity of the two stands most greatly affect carbon cycle and carbon budget of the natural reserve, and the veracity of the former decides the security of the latter. To sum up, not only did the simulations accord with routines in the relative comparisons between different vegetation belts and climate belts in the whole natural reserve, but also was exact in the absolute comparisons with very disperse data from field survey. Vegetations in the natural reserve had evident carbon sink functions, mainly exhibiting in the increasing of carbon, about 1.058×10⁶t·a^-1 . The annual carbon of mixed broad-leaved and Korean pine forest increased greatest (0.452×10⁶t·a^-1), secondly spruce-fir forest (0.339×10⁶t·a^-1). The two stands played crucial roles in the carbon sink for Changbai Mountain, others being Changbai larch forest, broad-leaved forest, meadow, shrub, alpine tundra, subalpine Betula ermanii forest and alpine grass. In 1995, the decomposing carbon of soil organic matter was 0.169×10⁶t·a^-1higher than the littering carbon in the natural reserve. There was accumulation of organic matter in the meadow soil and shrub soil. The decomposition and accumulation of soil organic matter was in the nearly balancing condition in the alpine tundra soil and alpine grass soil. The decomposition of organic matter was as one and a half time or double as litterfall in the arbor forest soil.