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Macropores and water flow in soils revisited

TLDR
It is suggested that the topic has still not received the attention that its importance deserves, in part because of the ready availability of software packages rooted firmly in the Richards domain, albeit that there is convincing evidence that this may be predicated on the wrong experimental method for natural conditions.
Abstract
The original review of macropores and water flow in soils by Beven and Germann is now 30 years old and has become one of the most highly cited papers in hydrology. This paper attempts to review the progress in observations and theoretical reasoning about preferential soil water flows over the intervening period. It is suggested that the topic has still not received the attention that its importance deserves, in part because of the ready availability of software packages rooted firmly in the Richards domain, albeit that there is convincing evidence that this may be predicated on the wrong experimental method for natural conditions. There is still not an adequate physical theory linking all types of flow, and there are still not adequate observational techniques to support the scale dependent parameterizations that will be required at practical field and hillslope scales of application. Some thoughts on future needs to develop a more comprehensive representation of soil water flows are offered.

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References
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Changing ideas in hydrology — The case of physically-based models

TL;DR: This paper argues that there are fundamental problems in the application of physically-based models for practical prediction in hydrology result from limitations of the model equations relative to a heterogeneous reality; the lack of a theory of subgrid scale integration; practical constraints on solution methodologies; and problems of dimensionality in parameter calibration.
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On kinematic waves I. Flood movement in long rivers

TL;DR: In this article, the theory of a distinctive type of wave motion, which arises in any one-dimensional flow problem when there is an approximate functional relation at each point between the flow q and concentration k (quantity passing a given point in unit time) and q remains constant on each kinematic wave.
Book

Shape and Structure, from Engineering to Nature

Adrian Bejan
TL;DR: In this paper, the authors propose a model of the natural form, questioning, and theory of the human body and the structure of a human body in terms of the following: 1. Natural Form, questioning and theory 2. Mechanical structure 3. Thermal structure 4. Heat trees 5. Fluid trees 6. Ducts and rivers 7. Turbulent structure 8. Convective trees 9. Structure in time: rhythm 11. Transportation and economics structure 12. Shapes with constant resistance
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A dual-porosity model for simulating the preferential movement of water and solutes in structured porous media

TL;DR: In this paper, a dual-porosity model was developed for the purpose of studying variably saturated water flow and solute transport in structured soils or fractured rocks, where water in both pore systems is assumed to be mobile.
Journal ArticleDOI

A review of non-equilibrium water flow and solute transport in soil macropores: principles, controlling factors and consequences for water quality

TL;DR: The potential for non-equilibrium water flow and solute transport at any site depends on the nature of the macropore network, which is determined by the factors of structure formation and degradation as mentioned in this paper.
Related Papers (5)
Frequently Asked Questions (13)
Q1. What contributions have the authors mentioned in the paper "Macropores and water flow in soils revisited" ?

This paper attempts to review the progress in observations and theoretical reasoning about preferential soil water flows over the intervening period. It is suggested that the topic has still not received the attention that its importance deserves, in part because of the ready availability of software packages rooted firmly in the Richards domain, albeit that there is convincing evidence that this may be predicated on the wrong experimental method for natural conditions. 

Because neither velocity nor acceleration occurs, hydrostatic conditions are assumed according to the material-specific retention curve. 

Tensiometers and time domain reflectrometry (TDR) [see, for instance, Topp et al., 1980] were used to record capillary potentials and volumetric water contents at nine depths. 

Since the inverse methods applied can be highly susceptible to overfitting without adequate noise assessment then one can risk misinterpretation of preferential flow when the true cause is inappropriate assessment of signal to noise. 

Various techniques of tomographic imaging have been applied to the study of preferential flow in soil including X-ray (CT), electrical resistance (ERT), radar and ultrasound. 

Infiltration into reconstructed soils was mainly through the soil matrix because no macropores had formed since reconstruction.[24] 

In smaller pores, capillarity and capillary gradients can play a role in controlling water movement, but the authors expect the range of such effects to be small scale and local. 

At both profile and hillslope scales, there is also a need to combine flow measurements with tracer experiments to test whether assumptions about flow velocities can equally reproduce the celerities controlling the hydrograph. 

This is because in order to fully characterize the response of a plot, a field, a hillslope or a catchment, both data types, hydrograph and tracer concentrations are required to allow the differentiation of celerity effects that control the hydrograph response and the distributions of pore water velocities that control the tracer response. 

Where the soil is saturated, this can be achieved by the propagation of pressure waves through the system, such that the build up of pressure in an upslope macropore link will cause the displacement of stored water into a pathway further downslope. 

As noted earlier one of the primary drivers for interest in preferential flows and macropores in soils was the problem of explaining how pesticides and other sorbing pollutants were being transported to field drains, groundwaters and rivers [Flury, 1996]. 

The issues in developing an adequate theory to representingwater flow in soils with preferential flow are those of the three functional requirements set out above, in this case for flows dominated by gravity and viscosity rather than capillarity effects. 

It might be difficult to extend knowledge at the hillslope scale to larger catchment scales because of the variability of responses in space and time and the potential for deeper flow pathways to become more significant at the catchment scale [Uchida et al., 2005b; Tromp-van Meerveld et al., 2007; Bachmair and Weiler, 2013].