晋南典型丘陵沟壑区退耕还林16年后土壤物理性质变化
Changes of Soil Physical Properties after Returning Farmland to Forest for 16 Years in Typical Hilly and Gully Regions of Southern Shanxi
摘要: 退耕还林可以在一定程度上改善土壤的物理性质。本文选取晋南典型丘陵沟壑区退耕还林16年后形成的三种不同植被类型:自然恢复山杨林(Populus davidiana)、油松刺槐(Pinus tabuliformis Carriere × Robinia pseudoacacia L.)人工混交林、刺槐(Robinia pseudoacacia L.)人工纯林,并以玉米耕地作为对照,采用野外调查与实验室分析相结合的方法对不同土层深度土壤容重、土壤总孔隙度、土壤毛管孔隙度进行对比分析。结果显示:自然恢复林和两种人工林较耕地相比,土壤容重显著变化分别发生在0~80 cm土层和0~60 cm土层(P < 0.05)。与耕地相比,自然恢复林、混交林、纯林的土壤容重分别平均增加33.96%、17.27%、12.94%;变化程度最大的土层为20~40 cm。与耕地相比,3种退耕林地的土壤总孔隙度在0~80 cm土层显著增加(P < 0.05),自然恢复林、混交林、纯林分别平均增加36.96%、14.02%、17.76%。变化程度最大的土层为20~40 cm。与耕地相比,自然恢复林和两种人工林土壤毛管孔隙度在0~80 cm土层和0~60 cm土层显著增加(P < 0.05)。自然恢复林、混交林、纯林分别平均增加41.70%、13.28%、12.76%。变化程度最大的土层在40~60 cm处。本研究表明退耕还林16年后的自然恢复山杨林和两种人工林都可以有效地改良土壤物理性质,但是自然恢复林的影响程度更大。
Abstract: Returning farmland to forest can improve the physical properties of the soil to a certain extent. The purpose of this paper is to study the physical properties of the soil after returning farmland to forest for 16 years in typical hilly and gully areas of southern Shanxi. In this paper, three different vegetation types were formed after returning farmland to forest for 16 years in typical hilly and gully areas of southern Shanxi. They were natural restoration of Populus davidiana forest, artificial mixed forest of Pinus tabuliformis and Robinia pseudoacacia, and pure plantation of Robinia pseudoacacia, using corn arable land as a control and field survey. The method combined with la-boratory analysis was used to compare and analyze soil bulk density, total soil porosity and soil capillary porosity at different soil depths. The results showed that: 1) Compared with cultivated land, the soil bulk density of the naturally restored forest and the two artificial forests changed significantly in 0~80 cm soil layer and 0~60 cm soil layer (P < 0.05). Compared with cultivated land, the soil bulk density of naturally restored forest, mixed forest and pure forest increased by 33.96%, 17.27% and 12.94%, respectively; the soil layer with the greatest degree of change was 20~40 cm. 2) The total soil porosity of the three kinds of converted farmland was significantly increased in the 0~80 cm soil layer compared with the cultivated land (P < 0.05), and the natural forest, mixed forest and pure forest increased by 36.96%, 14.02% and 17.76 %. The soil layer with the greatest degree of change is 20~40 cm. 3) Compared with the two cultivated lands, the natural restoration forest significantly increased the porosity of soil capillaries in 0~80 cm soil layer and 0~60 cm soil layer (P < 0.05). Naturally restored forest, mixed forest, and pure forest increased by 41.70%, 13.28%, and 12.76%, respectively. The soil layer with the greatest degree of change was at 40~60 cm. This study showed that the natural restoration of Populus davidiana forest after returning farmland to forest for 16 years had the greatest impact on soil physical properties and could effectively improve soil physical properties.
文章引用:周佳佳, 郝小玲, 吴洁, 张咪咪, 张粉果, 王永吉. 晋南典型丘陵沟壑区退耕还林16年后土壤物理性质变化[J]. 世界生态学, 2021, 10(1): 70-79. https://doi.org/10.12677/IJE.2021.101007

参考文献

[1] 高健翎, 张建国, 朱莉莉, 等. 黄土丘陵沟壑区水土保持关键措施变化特征[J]. 水土保持通报, 2019, 39(3): 114-118.
[2] 朱燕琴, 赵志斌, 齐广平. 黄土丘陵区植被类型和降雨对坡面侵蚀产沙的影响[J]. 水土保持学报, 2019, 33(2): 9-16.
[3] 郭宇, 王树森, 马迎梅, 等. 植被毯对内蒙古清水河县黄土丘陵沟壑区黄土边坡产流产沙量的影响[J]. 水土保持学报, 2019, 33(6): 61-71.
[4] 李裕元, 邵明安, 陈洪松, 等. 水蚀风蚀交错带植被恢复对土壤物理性质的影响[J]. 生态学报, 2010, 30(16): 4306-4316.
[5] 张希彪, 上官周平. 人为干扰对黄土高原子午岭油松人工林土壤物理性质的影响[J]. 生态学报, 2006, 26(11): 3685-3695.
[6] 连勰, 黄峰. 伊洛河上游流域退耕还林/还草对蓝水绿水分配的影响[J]. 中国生态农业学报, 2019, 27(9): 1409-1420.
[7] 王一超, 郝海广, 翟瑞雪, 等. 农户退耕还林生态补偿预期及其影响因素——以哈巴湖自然保护区和六盘山自然保护区为例[J]. 干旱区资源与环境, 2017, 31(8): 69-75.
[8] Deng, L., Liu, G.B. and Shangguan, Z.P. (2014) Land-Use Conversion and Changing Soil Carbon Stocks in China’s “Grain-for-Green” Program: A Synthesis. Globe Change Biology, 20, 3544-3556. [Google Scholar] [CrossRef] [PubMed]
[9] 李建明, 王志刚, 王爱娟, 等. 退耕还林恢复年限对岩溶槽谷区石漠化土壤物理性质的影响[J]. 农业工程学报, 2020, 36(1): 99-108.
[10] 陈鹏, 郭建英, 董智, 等. 砒砂岩区不同退耕还林措施土壤颗粒及交换性能分布特征[J]. 水土保持学报, 2019, 33(3): 43-50.
[11] Wang, L., Mu, Y., Zhang, Q.F., et al. (2012) Effects of Vegetation Restoration on Soil Physical Properties in the Wind-Water Erosion Region of the Northern Loess Plateau of China. CLEAN—Soil, Air, Water, 40, 7-15. [Google Scholar] [CrossRef
[12] 王艳芳, 刘领, 悦飞雪, 等. 退耕还林工程对河南省森林地上碳储量的影响[J]. 浙江农林大学学报, 2019, 36(3): 507-514.
[13] 李永宁, 王忠禹, 王兵, 等. 黄土丘陵区典型植被土壤物理性质差异及其对导水特性影响[J]. 水土保持学报, 2019, 33(6): 176-181.
[14] Arshad, M.A., Lowery, B. and Grossman, B. (1996) Physical Tests for Monitoring Soil Quality. In: Doran, J.W. and Jones, A.J., Eds., Methods for Assessing Soil Quality, SSSA Special Publications, Vol. 49, Soil Science Society of America, Madison, 123-141. [Google Scholar] [CrossRef
[15] Boix-Fayos, C., Calvo-Cases, A., Imeson, A.C., et al. (2001) In-fluence of Soil Properties on the Aggregation of Some Mediterranean Soils and the Use of Aggregate Size and Stability as Land Degradation Indicators. Catena, 44, 47-67. [Google Scholar] [CrossRef
[16] 刘欣, 彭道黎, 邱新彩. 华北落叶松不同林型土壤理化性质差异[J]. 应用与环境生物学报, 2018, 24(4): 735-743.
[17] 张晓霞, 杨宗儒, 查同刚, 等. 晋西黄土区退耕还林22年后林地土壤物理性质的变化[J]. 生态学报, 2017, 37(2): 416-424.
[18] 张恒硕, 查同刚, 张晓霞. 晋西黄土区退耕年限对土壤物理性质的影响[J]. 北京林业大学学报, 2020, 42(6): 123-133.
[19] 李庆云, 余新晓, 信忠保, 等. 黄土高原典型流域不同土地利用类型土壤物理性质分析[J]. 水土保持研究, 2010, 17(6): 106-114.
[20] 闫烨琛, 赵廷宁, 张艳, 等. 不同植物恢复措施对采石矿废弃地土壤物理性质的改良效果及评价[J]. 浙江农林大学学报, 2019, 36(6): 1062-1068.
[21] 侯宁宁, 苏晓琳, 杨钙仁, 等. 桉树造林的土壤物理性质及其水文效应[J]. 水土保持学报, 2019, 33(3): 101-107.
[22] 姚甜甜, 张鹏, 万丹, 等. 藏东南色季拉山迎风坡土壤物理性质垂直梯度差异性分析[J]. 北方园艺, 2019(24): 94-102.
[23] 邢菊香, 郭建英, 赵杏花, 等. 黄土丘陵区退耕还林后土壤物理性质恢复特征的研究——以陕西省吴起县为例[J]. 内蒙古农业大学学报, 2010, 31(1): 41-46.
[24] 李朝英, 郑路. 利用环刀法测定土壤水分精度的影响因素[J]. 水土保持通报, 2019, 39(2): 118-123.
[25] Cuevas, E., Brown, S. and Lugo, A.F. (1991) Above and Belowground Organic Matter Storage and Production in a Tropical Pine Plantation and a Paired Broadleaf Secondary Forest. Plant Soil, 135, 257-268. [Google Scholar] [CrossRef
[26] Montagnini, F., Ramstad, K. and Sancho, F. (1993) Litter Fall, Litter Decomposition and the Use of Mulch of Four Indigenous Tree Species in the Atlantic Lowlands of Costa Rica. Agro-forestry Systems, 23, 39-61. [Google Scholar] [CrossRef
[27] Roggy, J.C., Prevost, M.F., Gourbiere, F., et al. (1999) Leaf Natural 15N Abundance and Total N Concentration as Potential Indicators of Plant N Nutrition in Legumes and Pioneer Species in a Rain Forest of French Guiana. Oecologia, 120, 171-182. [Google Scholar] [CrossRef] [PubMed]
[28] 庞学勇, 包维楷, 江元明, 等. 九寨沟和黄龙自然保护区原始林与次生林土壤物理性质比较[J]. 应用与环境生物学报, 2009, 15(6): 768-773.
[29] Li, X.G., Li, F.M., Zed, R., et al. (2007) Soil Physical Properties and Their Relations to Organic Carbon Pools as Affected by Land Use in an Alpine Pastureland. Geoderma, 139, 98-105. [Google Scholar] [CrossRef
[30] Zhao, H.L., Guo, Y.R., Zhou, R.L., et al. (2011) The Effects of Plantation Development on Biological Soil Crust and Topsoil Properties in a Desert in Northern China. Geoderma, 160, 367-372. [Google Scholar] [CrossRef
[31] 杨士凯, 周运超, 黄磊, 等. 杉木成熟林土壤容重空间变异特征[J]. 森林与环境学报, 2020, 40(1): 30-38.
[32] 彭文英, 张科利, 陈瑶, 等. 黄土坡耕地退耕还林后土壤性质变化研究[J]. 自然资源学报, 2005, 20(2): 272-278.