1. 西北农林科技大学 草业与草原学院, 陕西 杨凌,712100
2. 中国科学院 水利部 水土保持研究所, 陕西 杨凌,712100
3. 甘肃省科学院地质自然灾害防治研究所,甘肃,兰州,730000
纸质出版:2023
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帕力夏提·格明, 王龙, 徐学选, 等. 林草植被恢复类型对黄土团聚体稳定性和入渗特性的影响[J]. 水土保持通报, 2023,43(1):24-31.
Palixiati·Geming, Wang Long, Xu Xuexuan, et al. Effects of Forest and Grass Restoration Types on Aggregate Stability and Infiltration Characteristics of Loess[J]. Bulletin of Soiland Water Conservation, 2023, 43(1): 24-31.
帕力夏提·格明, 王龙, 徐学选, 等. 林草植被恢复类型对黄土团聚体稳定性和入渗特性的影响[J]. 水土保持通报, 2023,43(1):24-31. DOI: 10.13961/j.cnki.stbctb.2023.01.004.
Palixiati·Geming, Wang Long, Xu Xuexuan, et al. Effects of Forest and Grass Restoration Types on Aggregate Stability and Infiltration Characteristics of Loess[J]. Bulletin of Soiland Water Conservation, 2023, 43(1): 24-31. DOI: 10.13961/j.cnki.stbctb.2023.01.004.
[目的
]
对比不同林草植被恢复类型下黄土团聚体稳定性和入渗特性的差异,为黄土高原地区生态恢复模式的合理优化提供理论支持。[方法
]
以黄土区撂荒地(C
1
,对照)、苜蓿地(C
2
)、天然草地(C
3
)、油松+侧柏混交林(L
1
)、刺槐+侧柏混交林(L
2
)为对象,采用萨维诺夫法和单环双水头法分别测定了水稳性团聚体组成状况、饱和导水率(K
s
)。以平均质量直径(MWD)、几何直径(GMD)、颗粒分形维数(D)、破坏率(PAD)、>0.25 mm水稳性团聚体占比(M
w
)和饱和导水率为评价指标,分析了不同林草植被恢复类型的土壤团聚体稳定性和入渗特性差异及其影响因素。[结果
]
①0—30 cm土层范围内,C
1
的GMD和MWD最低,林草植被恢复类型的GMD,MWD表现为L
1
和C
3
>L
2
和C
2
,而PAD和D则相反。 ②0—10 cm土层,L
1
的>0.25 mm水稳定团聚体含量最高(47.24%),其次是C
3
和L
2
,C
1
最低(24.00%);而10—30 cm土层,C
3
的>0.25 mm水稳定团聚体含量最高(10—20 cm处为35.41%,20—30 cm处为27.96%),L
2
最低(10—20 cm处为11.46%,20—30 cm处为8.00%)。 ③不同林草植被恢复类型的表层土壤入渗特性变异系数均介于0.001~0.360,L
1
的K
s
(0.307 cm/min)最大,C
1
的K
s
(0.044 cm/min)最小。 ④团聚体稳定性指标(PAD除外)和K
s
均与有机质、孔隙度、容重呈现显著或极显著相关。[结论
]
林草植被恢复有助于改善黄土团聚体稳定性和入渗特性,长期林地恢复类型(L
1
)的团聚体稳定性和入渗特性优于天然草地(C
3
),而短期林地恢复类型(L
2
)却不如天然草地(C
3
),植被恢复应注重时间的积累。
[Objective] The differences in aggregate stability and infiltration characteristics of loess under different forest and grass vegetation restoration types were compared in order to provide a theoretical basis for the optimization of ecological restoration patterns in the Loess Plateau. [Methods] Abandoned land (C1
control)
alfalfa land (C2)
natural grassland (C3)
mixed forest land of Pinus tabuliformis and Platycladus orientalis (L1)
and mixed forest land of Robinia pseudoacacia and P. orientalis (L2) were used to investigate differences in aggregate stability and infiltration characteristics and their exogenous factors. Water-stable aggregate composition and saturated hydraulic conductivity were determined by the Savinov method and a single-ring two-ponding depth infiltrometer
respectively. Mean weight diameter (MWD)
geometric mean diameter (GMD)
fractal dimension (D)
percentage of aggregate destruction (PAD)
water-stable macroaggregate content (>0.25 mm
Mw)
and saturated hydraulic conductivity sample (Ks) were used as evaluation indicators. [Results] ① In the 0—30 cm soil layer
C1 had the lowest GMD and MWD
and GMD and MWD in forest and grass vegetation restoration types followed the order of 〔L1 and C3〕>〔L2 and C2〕
respectively
whereas PAD and D showed the opposite order. ② In the 0—10 cm soil layer
L1 dominated the highest macroaggregate (>0.25 mm) content (47.24%)
followed by C3 and L2
while C1 had the lowest content (24.00%). In the 10—30 cm soil layer
C3 dominated the highest macroaggregate (>0.25 mm) content (35.41% at 10—20 cm; 27.96% at 20—30 cm)
while L2 had the lowest content (11.46% at 10—20 cm; 8.00% at 20—30 cm). ③ The variation coefficients of topsoil infiltration characteristics for different restoration types ranged from 0.001 to 0.360. The Ks (0.307 cm/min) of L1 was the highest
while the Ks (0.044 cm/min) of C1 was the lowest. ④ Aggregate stability indicators (except PAD) and Ks were significantly correlated with soil organic carbon
porosity
and bulk density. [Conclusion] The restoration of forest and grass vegetation was beneficial for improving aggregate stability and infiltration performance. Compared with natural grassland
long-term forest restoration exhibited better aggregate stability and infiltration characteristics
but those characteristics were worse for short-term forest restoration than for natural grassland. Time accumulation should be emphasized when evaluating the effects of vegetation restoration.
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