Abstract:[Background] Preferential flow is prevalent in field conditions, and quantitative differentiation of matrix and preferential flow can provide basic data for soil infiltration process and hydrologic cycle of Shaximiao purple soil.[Methods] We used a surface ring infiltration meters and selected Shaximiao purple soil area in Chongqing as the research object to measure soil matrix infiltration rate (im), total infiltration rate (it), and to calculate the preferential infiltration rate (ip). The success of matrix infiltration measurement was determined by excavating wetted soil via matrix infiltration. The feasibility of replacing the preferential flow process with the matrix infiltration process of adjacent soil was verified by calculating the spatial variability of matrix infiltration. On this basis, the quantitative relationship between matrix infiltration and preferential flow was analyzed, and the experimental results were compared with previous studies to verify the rationality of the method.[Results] 1) For im, the initial one is in 480.0-900.0 mm/h, the steady one is in 341.4-403.2 mm/h, the average one is 416.3-513.7 mm/h, and the cumulative infiltration is 657.2-805.9 mm. For it, the initial one is 984.0-2 470.8 mm/h, the steady one is 359.4-720.0 mm/h, the average one is 648.2-1 239.3 mm/h, and the cumulative infiltration is 966.2-1 898.1 mm. For ip, the initial one is 504.0-1 570.8 mm/h, the steady one is 18.0-316.8 mm/h, the average one is 231.3-725.8 mm/h, and the cumulative infiltration is 309.0-1 092.7 mm. 2) Among the infiltration model fitting parameters (S, K, a, b), im and cumulative infiltration (CI) characterizing soil matrix infiltration process, the coefficient of variation (CV) for S is maximum 15.6%. The spatial variation coefficient of steady infiltration and cumulative infiltration rate is 8.9% and 10.4%, respectively, indicating that the spatial variation coefficient of im is small. 3) In the initial stage (0-10 min), ip/im is 1.1-1.7, the preferential flow infiltration is dominant. As the infiltration continues (10-60 min), ip/im decreases, ip/im is 0.5-1.6. In the steady infiltration stage (60-90 min), ip/im is 0.2-1.0, and the matrix infiltration is dominant. 4) Using the Philip and Kostiakov infiltration models to fit the matrix infiltration process of the experimental sites, R2 is 0.88 and 0.93, respectively, P<0.01, these two models fit well for the im.[Conclusions] Soil matrix and preferential flow play an equally important role in the hydrological cycle of purple soil. The surface ring infiltration meters can be well used for measuring the infiltration performance of Shaximiao purple soil in Chongqing.
LILI M, BRALTS V F, YINGHAU P, et al. Methods for measuring soil infiltration:State of the art[J]. International Journal of Agricultural & Biological Engineering, 2008, 1(1):22.
[2]
雷廷武, 张婧, 王伟, 等. 土壤环式入渗仪测量效果分析[J]. 农业机械学报, 2013,44(12):99. LEI Tingwu, ZHANG Jing, WANG Wei, et al. Assessment on soil infiltration rates measured by ring infiltrometer[J]. Transactions of the CSAM, 2013, 44(12):99.
[3]
PRIEKSAT M A, ANKENY M D, KASPAR T C. Design for an automated, self-regulating, single-ring infiltrometer[J]. Soil Science Society of America Journal, 1992, 56(5):1409.
[4]
GERMANN P F, BEVEN K. Kinematic wave approximation to infiltration into soils with sorbing macropores[J]. Water Resources Research, 1985, 21(7):990.
[5]
JIANG Xiaojing, CHEN Chunfeng, ZHU Xiai, et al. Use of dye infiltration experiments and HYDRUS-3D to interpret preferential flow in soil in a rubber-based agroforestry systems in Xishuangbanna, China[J]. Catena, 2019(178):120.
[6]
GERMANN P F. Hydromechanics and kinematics in preferential flow[J]. Soil Science, 2018, 183(1):1.
[7]
WATANABE N, KUSANAGI H, SHIMAZU T, et al. Local non-vuggy modeling and relations among porosity, permeability and preferential flow for vuggy carbonates[J]. Engineering Geology, 2018(248):197.
[8]
张婧. 土壤入渗与优先流测量方法研究[D]. 北京:中国农业大学, 2017:63. ZHANG Jing. Study on measurement methodology of soil infiltration and preferential flow[D]. Beijing:China Agricultural University, 2017:63.
[9]
黄永超, 陈晓燕, 韩珍, 等. 紫色土耕层土壤基质与优先流入渗的定量计算[J]. 中国水土保持科学, 2018,116(5):30. HUANG Yongchao, CHEN Xiaoyan, HAN Zhen, et al. Quantitative calculation of matrix infiltration and preferential infiltration in the tillage layer of purple soil[J]. Science of Soil and Water Conservation, 2018,116(5):30.
[10]
中国科学院成都分院土壤研究室. 中国紫色土:上篇[M]. 北京:科学出版社, 1991. Soil Laboratory, ChengDu branch, Chinese Academy of Sciences. Purple soils in China (1)[M]. Beijing:Science Press, 1991.
[11]
李清, 何潇, 谢世友. 川东平行岭谷区自然景观垂直分异规律及综合分区:以重庆北碚区为例[J]. 资源开发与市场, 2005,21(3):210. LI Qing, HE Xiao, XIE Shiyou. Vertical diversity of natural landscape and comprehensive regionalization in paralleled ridge-valley of East Sichuan[J]. Resource Development & Market, 2005,21(3):210.
[12]
刘刚才, 朱波, 代华龙, 等. 四川低山丘陵区紫色土不同土地利用类型的水蚀特征[J]. 水土保持学报, 2001,115(6):96. LIU Gangcai, ZHU Bo, DAI Hualong, et al. Study of water erosion features of purple soil under different land utilization in hilly and low mountain area of Sichuan[J]. Journal of Soil and Water Conservation, 2001,115(6):96.
[13]
GUPTA S D, MOHANTY B P, KÖHNE J M. Soil hydraulic conductivities and their spatial and temporal variations in a vertisol[J]. Soil Science Society of America Journal, 2006, 70(6):1872.
[14]
LASSABATÈRE L, ANGULO-JARAMILLO R, SORIA UGALDE J M, et al. Beerkan estimation of soil transfer parameters through infiltration experiments-BEST[J]. Soil Science Society of America Journal, 2006, 70(2):521.
[15]
REYNOLDS W D, ZEBCHUK W D. Use of contact material in tension infiltrometer measurements[J]. Soil Technology, 1996, 9(3):141.
[16]
NOBLES M M, WILDING L P, MCINNES K J. Submicroscopic measurements of tracer distribution related to surface features of soil aggregates[J]. Geoderma, 2004, 123(12):83.
[17]
KODESOVA R, NEĚMECEK K, KODES V. Using dye tracer for visualization of preferential flow at macro-and microscales[J]. Vadose Zone Journal, 2012,11(1):1.
[18]
刘继龙, 马孝义, 张振华. 土壤入渗特性的空间变异性及土壤转换函数[J]. 水科学进展, 2010, 21(2):214. LIU Jilong, MA Xiaoyi, ZHANG Zhenhua. Spatial variability of soil infiltration characteristics and its pedotransfer functions[J]. Advances in Water Science, 2010, 21(2):214.
[19]
王伟, 张洪江, 程金花, 等. 四面山阔叶林土壤大孔隙特征与优先流的关系[J]. 应用生态学报, 2010, 21(5):1217. WANG Wei, ZHANG Hongjiang, CHEN Jinghua,et al. Macropore characteristics and its relationships with the preferential flow in broadleaved forest soil of Simian Mountains[J]. Chinese Journal of Applied Ecology, 2010, 21(5):1217.
[20]
HU Xia, LI Zongchao, LI Xiaoyan, et al. Quantification of soil macropores under alpine vegetation using computed tomography in the Qinghai Lake Watershed, NE Qinghai Tibet Plateau[J]. Geoderma, 2016(264):244.
[21]
李叶鑫, 郭宏忠, 史东梅, 等. 紫色丘陵区不同弃土弃渣下垫面入渗特征及影响因素[J]. 环境科学学报, 2014,34(5):1292. LI Yexin, GUO Hongzhong, SHI Dongmei, et al. Infiltration characteristics and its influencing factors of different underlying surfaces from disturbed soils in purple hilly area[J]. Acta Scientiae Circumstantiae, 2014,34(5):1292.
[22]
李雪垠, 李朝霞, 王天巍, 等. 紫色土中砾石夹层对土壤水分入渗的影响[J]. 水科学进展, 2016, 27(5):662. LI Xueyin, LI Zhaoxia, WANG Tianwei, et al. Rock interbed containment effect on infiltration processes in purple soil regions[J]. Advances in Water Science, 2016, 27(5):662.
[23]
姚晶晶, 程金花, 张洪江, 等. 入渗水量对重庆四面山草地优先流影响的定量评价[J]. 水土保持学报, 2018,132(2):45. YAO Jingjing, CHEN Jinghua, ZHANG Hongjiang, et al. Quantitative evaluation of effects of infiltration amounts on preferential flow in grassland in Simian Mountain of Chongqing[J]. Journal of Soil and Water Conservation, 2018,132(2):45.
[24]
陈晓冰, 张洪江, 程金花, 等. 基于数量生态学的农地优先路径水平分布特征研究[J]. 农业机械学报, 2015, 46(7):130. CHEN Xiaobing, ZHANG Hongjiang, CHEN Jinghua, et al. Horizontal distribution characteristics of preferential flow paths in farmland based on quantitative ecology[J]. Transactions of the CSAM, 2015, 46(7):130.
[25]
ALLAIRE-LEUNG S E, GUPTA S C, MONCRIEF J F. Water and solute movement in soil as influenced by macropore characteristics:2. macropore tortuosity[J]. Journal of Contaminant Hydrology, 2000, 41(3):303.