新疆师范大学地理科学与旅游学院,乌鲁木齐,830054
纸质出版:2017
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马国飞, 满苏尔·沙比提. 托木尔峰自然保护区台兰河上游森林植被水源涵养功能[J]. 水土保持学报, 2017,31(3):147-153.
MA Guofei, MANSUR Sabit. Water Conservation Function of Forest Ecosystems in the Upper Tailan River in the Mount Tumor Nature Reserve[J]. 2017, 31(3): 147-153.
马国飞, 满苏尔·沙比提. 托木尔峰自然保护区台兰河上游森林植被水源涵养功能[J]. 水土保持学报, 2017,31(3):147-153. DOI: 10.13870/j.cnki.stbcxb.2017.03.026.
MA Guofei, MANSUR Sabit. Water Conservation Function of Forest Ecosystems in the Upper Tailan River in the Mount Tumor Nature Reserve[J]. 2017, 31(3): 147-153. DOI: 10.13870/j.cnki.stbcxb.2017.03.026.
为定量评价托木尔峰自然保护区森林的水源涵养能力,利用综合蓄水能力法,对台兰河上游雪岭云杉森林生态系统的林冠层截留量(C)、枯落物持水量(L)、土壤层蓄水量(S)及综合水源涵养能力进行估算和分析。结果表明:(1)研究区4样地中,林冠层截留量表现为中海拔云杉林(29.94 mm)>较高海拔云杉林(20.56 mm)>高海拔云杉林(11.72 mm)>低海拔云杉杨树混交林(5.84 mm),而茎流量则与之相反。(2)除中海拔云杉林外,各样地枯枝落叶未分解层平均厚度均大于半分解层;其中,未分解层的平均蓄积量中高海拔云杉林最大(79.32 t/hm2),半分解层中海拔云杉林最大(59.47 t/hm2)。整体来看,枯枝落叶层的最大持水量大小依次为中海拔云杉林(32.55 mm)>高海拔云杉林(31.05 mm)>较高海拔云杉林(30.78 mm)>低海拔云杉杨树混交林(12.84 mm)。(3)4样地平均土壤容重变动范围为0.73~1.06 g/cm3;土壤孔隙度的平均值大小均为中海拔云杉林>较高海拔云杉林>高海拔云杉林>低海拔云杉杨树混交林;林下土壤自然含水率随海拔高度的增加呈不断上升趋势。不同样地30 cm深土层的非毛管孔隙持水量表现为:中海拔云杉林(37.6 mm)>较高海拔云杉林(30.7 mm)>高海拔云杉林(25.73 mm)>低海拔云杉杨树混交林(13.92 mm)。(4)研究区森林生态系统的水源涵养能力在171.27~280.84 mm之间,低海拔云杉杨树混交林的总持水量最小,中海拔云杉林最大。土壤层水源涵养贡献率最大,占比在77.75%~89.10%之间;总有效蓄水量虽远小于总持水量,但能够很好地发挥水源涵养功能和水土保持作用。
To evaluate the water conservation capacity of forests in the Mount Tumor Nature Reserve quantitatively
comprehensive water storage capacity method was used to investigate the canopy interception capacity (C)
litter water-holding capacity (L)
soil water storage capacity (S) of Picea schrenkiana forest ecosystems in the upper Tailan River
then a comprehensive evaluation of its water conservation function was made. The results showed that: ① In the four sample areas
the canopy interception capacity followed the order og the middle altitude spruce forest (29.94 mm) > higher altitude spruce forest (20.56 mm) > high altitude spruce forest (11.72 mm) > low altitude mixed?broad leaf-conifer?forest (5.84 mm)
and the stem flow showed the opposite order. ② Except for the middle altitude spruce forest
the average?thickness of un-decomposed litter was thicker than that of the?intermediately decomposed layer. The high altitude spruce forest had the largest average volume of decomposed layer (79.32 t/hm2)
while the middle altitude spruce forest had the largest intermediately decomposed layer (59.47 t/hm2). On the whole
the rank of the maximum water holding capacity was the middle altitude spruce forest (32.55 mm) > the high altitude spruce forest (31.05 mm) > the higher elevation spruce forest (30.78 mm) > the low altitude mixed?broad leaf-conifer?forest (12.84 mm). ③ Soil bulk density in the four sampled forests ranged from 0.73 to 1.06 g/cm3. Both the average soil porosity and water holding capacity of capillary pore in the 30-cm soil layer were in the order of the middle altitude spruce forest > the higher altitude spruce forest > the high altitude spruce forest > the low altitude mixed?broad leaf-conifer?forest. Overall
soil moisture content of natural forests increased with the increase of the altitude. The average water holding capacity of non-capillary pore in the 30-cm soil layer followed the order of the middle altitude spruce forest (37.6 mm) > the higher altitude spruce forest (30.7 mm) > the high altitude spruce forest (25.73 mm) > the low altitude mixed?broad leaf- conifer?forest (13.92 mm). ④ Comprehensive water conservation capacity of the forest ecosystems in the study area was bwteen 141.12 and 280.84 mm
with the low altitude mixed?broad leaf-conifer?forest and the middle altitude spruce forest having the smallest and largest water holding capacity
respectively. The soil layer contributed the most to water conservation
accounting for 77.75%-86.96%. Comprehensive effective water storage capacity was far less than the theoretical total capacity
but could work well in the water conservation function as well as water and soil conservation effect.
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