北京林业大学水土保持学院,水土保持国家林业局重点实验室,北京市水土保持工程技术研究中心,林业生态工程教育部工程研究中心,北京,100083
纸质出版:2017
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刘 凯, 贺康宁, 田 赟, 等. 青海高寒山区5种林分土壤特性及其水源涵养功能[J]. 水土保持学报, 2017,(3):141-146.
Soil Characteristics and Water Conservation Function of Five Forest Types in Qinghai Alpine Region[J]. 2017, (3): 141-146.
刘 凯, 贺康宁, 田 赟, 等. 青海高寒山区5种林分土壤特性及其水源涵养功能[J]. 水土保持学报, 2017,(3):141-146. DOI: 10.13870/j.cnki.stbcxb.2017.03.025.
Soil Characteristics and Water Conservation Function of Five Forest Types in Qinghai Alpine Region[J]. 2017, (3): 141-146. DOI: 10.13870/j.cnki.stbcxb.2017.03.025.
为定量评价青海省大通县高寒山区不同森林的土壤特性和水源涵养功能,从而为森林的合理空间配置提供理论依据,采用浸水法、环刀法、定水头法、硫酸重铬酸钾法,分别测定5种林分的枯落物性质和0—40 cm土层的孔隙度、渗透性及养分状况等。结果表明:(1)枯落物总储量及最大持水量依次为云杉白桦混交林>云杉落叶松混交林>青海云杉林>华北落叶松林>白桦林。(2)0—40 cm土层的土壤有机质含量平均值依次为云杉落叶松混交林>云杉白桦混交林>白桦林>青海云杉林>华北落叶松林。(3)土壤容重随着深度增加而增大,0—40 cm土层均值依次为白桦林>华北落叶松林>云杉白桦混交林>青海云杉林>云杉落叶松混交林。(4)土壤总孔隙度随土层加深而降低,0—40 cm土层均值依次为云杉落叶松混交林>青海云杉林>云杉白桦混交林>华北落叶松林>白桦林。(5)0—40 cm土层的土壤平均初渗速率和稳渗速率大小依次为白桦林>云杉白桦混交林>云杉落叶松混交林>华北落叶松林>青海云杉林。(6)依林地总贮水量评价的水源涵养功能依次为云杉落叶松混交林(4 427.40 t/hm2)>青海云杉林(4 365.33 t/hm2)>云杉白桦混交林(4 055.04 t/hm2)>华北落叶松林(3 729.64 t/hm2)>白桦林(2 650.31 t/hm2)。
In order to quantitatively evaluate the soil characteristics and water conservation function of different forests in the alpine mountainous areas of Datong County of Qinghai Province and to provide a theoretical basis for reasonable spatial allocation of forests
immersion method
cutting ring method
fixed head method and sulfuric acid potassium dichromate method were used to determine litter properties
soil porosity
soil permeability and soil nutrient status of the 0-40 cm soil layers of five kinds of forest. The results showed that there were significant differences in soil properties and water conservation function among forest types. (1) The litter size and the maximum water holding capacity of the litter in the five forest types were in the order of Picea crassifolia-Betula platyphylla > P. crassifolia-Larix principis-rupprechtill > P. crassifolia forest > L. principis-rupprechtii forest > Betula platyphylla forest. (2) In the 0-40 cm soil layer
the average soil organic matter content was in the order of P. crassifolia –L. principis-rupprechtill > P. crassifolia-B. platyphylla > B. platyphylla forest > P. crassifolia forest > L. principis-rupprechtii forest. (3) In the 0-40 cm soil layer
soil bulk density of five kinds of forest types increased with the increment of soil depth
and followed the order of B. platyphylla forest > L. principis-rupprechtii forest > P. crassifolia-B. platyphylla > P. crassifolia forest > P. crassifolia-L. principis-rupprechtill. (4) In the 0-40 cm soil layer
total porosity of the soil under five forest types decreased with the increment of soil depth. The mean value of soil total porosity was in the order of P. crassifolia-L. principis-rupprechtill > P. crassifolia forest > P. crassifolia-B. platyphylla > L. principis-rupprechtii forest > B. platyphylla forest. (5) In the 0-40 cm soil layer
soil average infiltration rate of the five types of forests was in the order of B. platyphylla forest > P. crassifolia-B. platyphylla > P. crassifolia-L. principis-rupprechtill > L. principis-rupprechtii forest > P. crassifolia forest. (6) Based on the total water-holding capacity of litter and soil
water conservation function of the five types of forests followed the order of P. crassifolia-L. principis-rupprechtill (4 427.40 t/hm2) > P. crassifolia forest (4 365.33 t/hm2) > P. crassifolia-B. platyphylla (4 055.04 t/hm2) > L. principis-rupprechtii forest (3 729.64 t/hm2) > B. platyphylla forest (2 650.31 t/hm2).
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