1. 西北农林科技大学 理学院, 陕西 杨陵,712100
2. 兰州大学 资源环境学院,甘肃,兰州,730000
纸质出版:2021
移动端阅览
魏宁, 于文竹, 安克俭, 等. 青藏高原高寒草原与草甸土壤可蚀性的关键因子[J]. 水土保持通报, 2021,41(3):87-93.
Wei Ning, Yu Wenzhu, An Kejian, et al. Key Factors of Soil Erodibility for Alpine Grassland and Meadow in Qinghai-Tibet Plateau[J]. Bulletin of Soiland Water Conservation, 2021, 41(3): 87-93.
魏宁, 于文竹, 安克俭, 等. 青藏高原高寒草原与草甸土壤可蚀性的关键因子[J]. 水土保持通报, 2021,41(3):87-93. DOI: 10.13961/j.cnki.stbctb.2021.03.013.
Wei Ning, Yu Wenzhu, An Kejian, et al. Key Factors of Soil Erodibility for Alpine Grassland and Meadow in Qinghai-Tibet Plateau[J]. Bulletin of Soiland Water Conservation, 2021, 41(3): 87-93. DOI: 10.13961/j.cnki.stbctb.2021.03.013.
[目的
]
探讨青藏高原高寒草原与草甸土壤可蚀性特征差异,为高寒草原草甸土壤可蚀性研究提供重要参考。[方法
]
选取18个变化因子作为草原与草甸土壤可蚀性评价的影响因子,运用主成分分析、逐步回归分析以及通径分析法,确定高寒草原与草甸土壤可蚀性的主要影响因素,筛选青藏高原高寒草原与草甸土壤可蚀性的关键因子。[结果
]
高寒草原土壤可蚀性主要受土壤粒径与团聚体特征两方面的影响,高寒草甸土壤可蚀性主要受粒径孔隙分布、有机质、团聚体特征和渗透性能的影响;高寒草原土壤可蚀性的关键因子为:粉粒、团聚体平均质量直径(MWD)、团聚体>2 mm粒级结构体破坏率(PAD
>2
)和>0.25 mm粒级结构体破坏率(PAD
>0.25
),草甸土壤可蚀性关键因子为:粉粒、黏粒、>1 mm粒级结构体破坏率(PAD
>1
)和饱和导水率。[结论
]
草原与草甸土壤主要在颗粒机械组成、有机质含量、含水量等方面表现出较大差异,草甸土壤状态更适合于植被发育。
[Objective] The differences in soil erodibility between alpine grassland and alpine meadow in the Qinghai-Tibet Plateau were determined
in order to provide important reference for soil erodibility in alpine grassland. [Methods] 18 change factors were selected as potential influencing factors of soil erodibility for grassland and meadow. Principal component analysis
stepwise regression analysis
and path analysis were used to determine the main influencing factors of soil erodibility in order to select the key factors. [Results] The soil erodibility of alpine grassland was mainly affected by soil particle size and aggregate characteristics. Soil erodibility of alpine meadow was mainly affected by particle size and pore distribution
organic matter
aggregate characteristics
and permeability. The key factors of soil erodibility in alpine grassland were as follows: silt
mean weight diameter (MWD)
aggregate size > 2 mm processing damage rate (PAD>2)
and aggregate size > 0.25 mm processing damage rate (PAD>0.25). The key factors of soil erodibility in alpine meadow were as follows: silt
clay
aggregates size > 1 mm processing damage rate (PAD>1)
and soil saturated hydraulic conductivity. [Conclusion] Grassland and meadow soil showed great differences in particle mechanical composition
organic matter content
water content
and so on. The state of meadow soil was more suitable for vegetation development.
翟子宁,苏备.土壤可蚀性研究进展[J].土壤通报,2016,47(1):253-256.
黄晓强,赵云杰,信忠保,等.北京山区典型土地利用方式对土壤理化性质及可蚀性的影响[J].水土保持研究,2015,22(1):5-10.
姜小三,潘剑君,杨林章,等.土壤可蚀性
K
值的计算和
K
值图的制作方法研究:以南京市方便水库小流域为例[J].土壤,2004,36(2):177-180.
李英,林圣玉,张龙,等.鄱阳湖生态经济区坡耕地表土抗蚀性评价[J].中国水土保持,2016(7):48-51.
Wang Bin, Zheng Fenli, Romkens M J M, et al. Soil erodibility for water erosion:A perspective and Chinese experiences[J]. Geomorphology, 2013,187:1-10.
李鹏,李占斌,郑郁.不同土地利用方式对干热河谷地区土壤可蚀性的影响[J].水土保持研究,2011,18(4):16-19.
朱乐红,唐科明,李豪,等.土壤理化性质对土壤侵蚀影响研究综述[J].现代农业科技,2018(14):189-191.
徐燕,龙健.贵州喀斯特山区土壤物理性质对土壤侵蚀的影响[J].水土保持学报,2005,19(1):157-159,175.
刘小梅,吕殿青.土壤容重对红壤坡地降雨侵蚀和入渗的影响[J].长沙大学学报,2013,27(2):13-15,18.
张玉斌,郑粉莉.近地表土壤水分条件对坡面土壤侵蚀过程的影响[J].中国水土保持科学,2007,5(2):5-10,17.
张向炎,史学正,于东升,等.前期土壤含水量对红壤坡面产流产沙特性的影响[J].水科学进展,2010,21(1):23-29.
龚杰,罗麟,周海燕.前期土壤含水量对坡面产流产沙起始时间的影响[J].人民长江,2011,42(9):102-104.
殷庆元,王章文,谭琼,等.金沙江干热河谷坡改梯及生物地埂对土壤可蚀性的影响[J].水土保持学报,2015,29(1):41-47.
杨文利,朱平宗,程洪,等.马尾松人工林地浅沟表层土壤颗粒的空间分布特征[J].水土保持学报,2018,32(4):158-162.
Sun Caili, Liu Guobin, Xue Sha. Natural succession of grassland on the Loess Plateau of China affects multifractal characteristics of soil particle-size distribution and soil nutrients[J]. Ecological Research, 2016,31(6):891-902.
仲亚婷,张文太,李建贵,等.用人工模拟降雨研究不同土壤类型的产沙特征[J].安徽农业大学学报,2017,44(3):465-470.
陈佩岩.不同雨型下坡面侵蚀过程及其与土壤可蚀性定量关系[D].北京:北京林业大学,2019.
Levy G J, Miller W P. Aggregate stabilities of some southeastern US soils[J]. Soil Science Society of America Journal, 1997,61(4):1176-1182.
Six J, Bossuyt H, Degryze S, et al. A history of research on the link between(micro)aggregates, soil biota, and soil organic matter dynamics[J]. Soil and Tillage Research, 2004,79(1):7-31.
吴媛媛,杨明义,张风宝,等.添加生物炭对黄绵土耕层土壤可蚀性的影响[J].土壤学报,2016,53(1):81-92.
王根绪,丁永建,王建,等.近15年来长江黄河源区的土地覆被变化[J].地理学报,2004,59(2):163-173.
杜际增, 王根绪, 李元寿. 近45年长江黄河源区高寒草地退化特征及成因分析[J].草业学报,2015,24(6):5-15.
赵恒策.青海省江河源区草地土壤可蚀性关键因子研究[D].甘肃兰州:兰州大学,2019.
郑纪勇,邵明安,张兴昌.黄土区坡面表层土壤容重和饱和导水率空间变异特征[J].水土保持学报,2004,18(3):53-56.
郭军玲,王虹艳,卢升高.亚热带土壤团聚体测定方法的比较研究[J].土壤通报,2010,41(3):542-546.
彭新华,张斌,赵其国.红壤侵蚀裸地植被恢复及土壤有机碳对团聚体稳定性的影响[J].生态学报,2003,23(10):2176-2183.
安韶山,张扬,郑粉莉.黄土丘陵区土壤团聚体分形特征及其对植被恢复的响应[J].中国水土保持科学,2008,6(2):66-70,82.
贺强,崔保山,胡乔木,等.水深环境梯度下柽柳种群分布格局的分形分析[J].水土保持通报,2008,28(5):70-73.
刘目兴,聂艳,于婧.不同初始含水率下粘质土壤的入渗过程[J].生态学报,2012,32(3):871-878.
郭伟,史志华,陈利顶,等.红壤表土团聚体粒径对坡面侵蚀过程的影响[J].生态学报,2007,27(6):2516-2522.
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