Journal of Desert Research ›› 2021, Vol. 41 ›› Issue (6): 169-178.DOI: 10.7522/j.issn.1000-694X.2021.00100
Feiyao Liu1,2(), Quangang You1(
), Siyuan Wu3, Cuihua Huang1, Jing Pan1, Shaoxiu Ma1, Xiaojie Chen1,2, Xian Xue1
Received:
2021-04-12
Revised:
2021-08-09
Online:
2021-11-20
Published:
2021-12-17
Contact:
Quangang You
CLC Number:
Feiyao Liu, Quangang You, Siyuan Wu, Cuihua Huang, Jing Pan, Shaoxiu Ma, Xiaojie Chen, Xian Xue. Effects of abandonment and recultivation of farmland on soil hydraulic properties in a typical oasis of arid regions[J]. Journal of Desert Research, 2021, 41(6): 169-178.
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URL: http://www.desert.ac.cn/EN/10.7522/j.issn.1000-694X.2021.00100
土地类型 | 深度/cm | 黏粒/% | 粉粒/% | 砂粒/% | 有机质/(g·kg-1) | 大孔隙度/% | 容重/(g·cm-3) |
---|---|---|---|---|---|---|---|
耕地 | 5 | 20.01±0.35aB | 40.68±0.76aB | 39.31±0.99aA | 10.23±0.09aA | 20.20±0.65aB | 1.40±0.03bA |
20 | 22.22±0.65aA | 42.81±1.04aB | 34.97±1.69aA | 9.23±0.07bA | 13.46±0.70bB | 1.52±0.02aA | |
40 | 22.31±0.30aB | 42.61±0.36aA | 35.08±0.38aA | 7.73±0.21cA | 17.39±0.70aA | 1.46±0.02abA | |
撂荒地 | 5 | 21.92±0.63aAB | 43.74±0.83aAB | 34.34±1.44aAB | 9.76±0.59aA | 25.13±0.24aA | 1.39±0.02cA |
20 | 22.88±0.22abA | 44.29±0.75aAB | 32.83±0.54aAB | 7.52±0.11bB | 21.78±0.18bA | 1.44±0.01bB | |
40 | 24.68±0.22aA | 41.54±0.26aA | 33.78±0.18aA | 6.58±0.13bC | 19.25±0.04cA | 1.49±0.01aA | |
复耕地 | 5 | 24.11±0.52aA | 45.91±0.52aA | 29.98±1.01aB | 9.51±0.12aA | 19.92±1.23aB | 1.41±0.03aA |
20 | 24.79±0.45aA | 48.65±1.02aA | 26.56±1.30aB | 8.60±0.03bB | 16.65±1.08aB | 1.52±0.01aA | |
40 | 25.50±0.27aA | 45.40±1.02aA | 29.10±1.24aB | 7.13±0.23cAB | 15.30±0.28aB | 1.49±0.02aA |
Table 1 Soil particle composition, soil organic matters, microporosity and bulk density of cultivated land, abandoned land and recultivated land
土地类型 | 深度/cm | 黏粒/% | 粉粒/% | 砂粒/% | 有机质/(g·kg-1) | 大孔隙度/% | 容重/(g·cm-3) |
---|---|---|---|---|---|---|---|
耕地 | 5 | 20.01±0.35aB | 40.68±0.76aB | 39.31±0.99aA | 10.23±0.09aA | 20.20±0.65aB | 1.40±0.03bA |
20 | 22.22±0.65aA | 42.81±1.04aB | 34.97±1.69aA | 9.23±0.07bA | 13.46±0.70bB | 1.52±0.02aA | |
40 | 22.31±0.30aB | 42.61±0.36aA | 35.08±0.38aA | 7.73±0.21cA | 17.39±0.70aA | 1.46±0.02abA | |
撂荒地 | 5 | 21.92±0.63aAB | 43.74±0.83aAB | 34.34±1.44aAB | 9.76±0.59aA | 25.13±0.24aA | 1.39±0.02cA |
20 | 22.88±0.22abA | 44.29±0.75aAB | 32.83±0.54aAB | 7.52±0.11bB | 21.78±0.18bA | 1.44±0.01bB | |
40 | 24.68±0.22aA | 41.54±0.26aA | 33.78±0.18aA | 6.58±0.13bC | 19.25±0.04cA | 1.49±0.01aA | |
复耕地 | 5 | 24.11±0.52aA | 45.91±0.52aA | 29.98±1.01aB | 9.51±0.12aA | 19.92±1.23aB | 1.41±0.03aA |
20 | 24.79±0.45aA | 48.65±1.02aA | 26.56±1.30aB | 8.60±0.03bB | 16.65±1.08aB | 1.52±0.01aA | |
40 | 25.50±0.27aA | 45.40±1.02aA | 29.10±1.24aB | 7.13±0.23cAB | 15.30±0.28aB | 1.49±0.02aA |
黏粒 | 粉粒 | 砂粒 | 有机质 | 土壤容重 | θs-θ33 | θs | θ33 | θ1500 | θ33-θ1500 | Ks | |
---|---|---|---|---|---|---|---|---|---|---|---|
黏粒 | 1 | 0.596** | -0.838** | -0.571** | 0.148 | 0.092 | 0.090 | 0.545** | 0.643** | 0.376 | 0.286 |
粉粒 | 1 | -0.937** | -0.051 | -0.139 | -0.140 | 0.107 | 0.345 | 0.223 | 0.422* | 0.088 | |
砂粒 | 1 | 0.283 | 0.030 | 0.055 | -0.111 | -0.471* | -0.430* | -0.449* | -0.184 | ||
有机质 | 1 | -0.473* | -0.389* | .052 | -0.389* | -0.587** | -0.141 | -0.341 | |||
土壤容重 | 1 | 0.975** | -0.639** | 0.665** | 0.753** | 0.488** | -0.156 | ||||
θs-θ33 | 1 | 0.874** | -0.780** | -0.738** | -0.720** | -0.109 | |||||
θs | 1 | -0.378 | -0.366 | -0.340 | -0.049 | ||||||
θ33 | 1 | 0.934** | 0.934** | -0.155 | |||||||
θ1500 | 1 | 0.744** | -0.034 | ||||||||
θ33-θ1500 | 1 | -0.255 | |||||||||
Ks | 1 |
Table 2 The correlation between soil-hydraulic properties and soil text and structural properties
黏粒 | 粉粒 | 砂粒 | 有机质 | 土壤容重 | θs-θ33 | θs | θ33 | θ1500 | θ33-θ1500 | Ks | |
---|---|---|---|---|---|---|---|---|---|---|---|
黏粒 | 1 | 0.596** | -0.838** | -0.571** | 0.148 | 0.092 | 0.090 | 0.545** | 0.643** | 0.376 | 0.286 |
粉粒 | 1 | -0.937** | -0.051 | -0.139 | -0.140 | 0.107 | 0.345 | 0.223 | 0.422* | 0.088 | |
砂粒 | 1 | 0.283 | 0.030 | 0.055 | -0.111 | -0.471* | -0.430* | -0.449* | -0.184 | ||
有机质 | 1 | -0.473* | -0.389* | .052 | -0.389* | -0.587** | -0.141 | -0.341 | |||
土壤容重 | 1 | 0.975** | -0.639** | 0.665** | 0.753** | 0.488** | -0.156 | ||||
θs-θ33 | 1 | 0.874** | -0.780** | -0.738** | -0.720** | -0.109 | |||||
θs | 1 | -0.378 | -0.366 | -0.340 | -0.049 | ||||||
θ33 | 1 | 0.934** | 0.934** | -0.155 | |||||||
θ1500 | 1 | 0.744** | -0.034 | ||||||||
θ33-θ1500 | 1 | -0.255 | |||||||||
Ks | 1 |
土壤水分常数 | 方法 | RMSE/% | R2 | P |
---|---|---|---|---|
θs | 线性回归 | 0.0091 | 0.6175 | <0.01 |
神经网络 | 0.0179 | 0.4752 | <0.01 | |
Rosetta模型 | 0.0142 | 0.3707 | <0.05 | |
θ33 | 线性回归 | 0.0049 | 0.7409 | <0.01 |
神经网络 | 0.0057 | 0.7569 | <0.01 | |
Rosetta模型 | 0.0045 | 0.0164 | >0.1 | |
θ1500 | 线性回归 | 0.0015 | 0.9640 | <0.01 |
神经网络 | 0.0079 | 0.9489 | <0.01 | |
Rosetta模型 | 0.0046 | 0.3381 | <0.05 |
Table 3 Comparison of predicted errors of the three pedotransfer functions
土壤水分常数 | 方法 | RMSE/% | R2 | P |
---|---|---|---|---|
θs | 线性回归 | 0.0091 | 0.6175 | <0.01 |
神经网络 | 0.0179 | 0.4752 | <0.01 | |
Rosetta模型 | 0.0142 | 0.3707 | <0.05 | |
θ33 | 线性回归 | 0.0049 | 0.7409 | <0.01 |
神经网络 | 0.0057 | 0.7569 | <0.01 | |
Rosetta模型 | 0.0045 | 0.0164 | >0.1 | |
θ1500 | 线性回归 | 0.0015 | 0.9640 | <0.01 |
神经网络 | 0.0079 | 0.9489 | <0.01 | |
Rosetta模型 | 0.0046 | 0.3381 | <0.05 |
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