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Published online 1 August 2007
Published in Vadose Zone J 6:436-445 (2007)
DOI: 10.2136/vzj2006.0060
© 2007 Soil Science Society of America
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Modeling Water Movement in Heterogeneous Water-Repellent Soil: 1. Development of a Contact Angle–Dependent Water-Retention Model

J. Bachmanna,*, M. Deurerb and G. Aryec

a Institute of Soil Science, Univ. of Hannover, Herrenhaeuser Str. 2, 30419 Hannover, Germany
b Sustainable Land Use Group, HortResearch, Tennent Dr., P.O. Box 11030, Palmerston North, New Zealand
c Dep. of Environmental Sciences, Univ. of California, Riverside, CA 92521, USA


Figure 1
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FIG. 1. Dispersive {sigma}sD (circles) and nondispersive {sigma}sND (squares) surface free energy components as a function of the gravimetric water content (Fig. 1a) for a clay mineral (data from Chassin et al., 1986) and for a peat soil as a function of the water vapor humidity (Fig. 1b; data from Michel et al. 2001). Schematically shown is the equilibrium film pressure component {pi} as a function of moisture content.

 

Figure 2
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FIG. 2. Relation between the advancing contact angle {kappa}a and the common logarithm of the water drop penetration time, WDPT (a, m, n, t, tt, and c are empirical fitting parameters). Data from Bachmann et al. (2003) and Woche et al. (2005).

 

Figure 3
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FIG. 3. Water drop penetration time (WDPT) as a function of water content and organic matter content (SOM) in a sandy soil (top). Figures at bottom show the corresponding data after conversion of WDPT to contact angle with the function displayed in Fig. 4. Plot recalculated after data presented in Täumer et al. (2005).

 

Figure 4
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FIG. 4. Advancing and receding CA of air dry silt hydrophobized with dichlorodimethylsilane. Also shown are time-dependent contact angles (CAs) measured in a constant immersion depth. Soil was dried after wetting for 10 d in water, and CAs were measured with the Wilhelmy plate method (WPM).

 

Figure 5
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FIG. 5. Cosine of the contact angle {kappa} of a humus sand from a topsoil of a forest stand after three repeated wetting–drying cycles. In each cycle samples were remoistured to approximately field capacity and dried either to oven-dryness, to air-dryness, to pF 4.2, or to freeze-dried. Contact angles (CAs) were measured with the capillary rise method. Average standard deviation of CA determinations approx. 4 to 5°.

 

Figure 6
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FIG. 6. Water entry pressure as a function of the cosine of the contact angle for three different soils.

 

Figure 7
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FIG. 7. Schematic representation of the contact angle (CA) model. Location of node is indicated by i and j, time by t, contact angle by {kappa}; {alpha} is the water retention parameter of the van Genuchten equation, and {theta}WP indicates the water content at the permanent wilting point. REV = representative elementary volume.

 

Figure 8
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FIG. 8. Schematic representation of the dynamic decrease of the water content-dependent contact angle with time t (Fig. 7a) and positive pressure h (Fig. 7b) in the vicinity of a wetting front. Parameters used were {theta}crit = 2 Vol.-%, {theta}FK = 18 Vol.-%, {kappa}max = 110°, {kappa}min = 0, characteristic rewetting time to = 30 d, breakthrough pressure ho = 30 cm.

 

Figure 9
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FIG. 9. Water tension–saturation relations (imbibitions) for a wettable soil ({kappa} = 0) used as reference soil (Ref. soil) to calculate the contact angle (CA) for hydrophobic soils with various contact angles. The 3.1% and 5% are the ratio of mixing of a bulk artificially hydrophobized quartz sand (100% hydrophobic) with a pure wettable quartz sand ({kappa} = 0) (Recalculated after data from Bauters et al., 1998). The ORC and EQL soils are naturally occurring hydrophobic sandy soils located under orange orchard and eucalyptus cover, respectively. Ignition of these soils (400 °C for 8 h) was used to establish a completely wettable reference soil (data taken from Arye et al., 2007). (VG function = van Genuchten function.)

 





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