Abstract

Quantification of roughness effects on free surface flows is unquestionably necessary when describing water and material transport within ecosystems. The conventional hydrodynamic resistance formula empirically shows that the Darcy–Weisbach friction factor f~(r/hw)1/3 describes the energy loss of flowing water caused by small-scale roughness elements characterized by size r (<<hw), where hw is the water depth. When the roughness obstacle size becomes large (but <hw) as may be encountered in flow within canopies covering wetlands or river ecosystem, the f becomes far more complicated. The presence of a canopy introduces additional length scales above and beyond r/hw such as canopy height hv, arrangement density m, frontal element width D, and an adjustment length scale that varies with the canopy drag coefficient Cd. Linking those length scales to the friction factor f frames the scope of this work. By adopting a scaling analysis on the mean momentum equation and closing the turbulent stress with a first-order closure model, the mean velocity profile, its depth-integrated value defining the bulk velocity, as well as f can be determined. The work here showed that f varies with two dimensionless groups that depend on the canopy submergence depth and a canopy length scale. The relation between f and these two length scales was quantified using first-order closure models for a wide range of canopy and depth configurations that span much of the published experiments. Evaluation through experiments suggests that the proposed model can be imminently employed in eco-hydrology or eco-hydraulics when using the De Saint-Venant equations.

Highlights

  • The modeling of urban constructed wetlands requires routing an inflow hydrograph through vegetated canopies, where the vegetation may be emergent or submerged [1,2,3,4,5]

  • It can be seen that conditions of the experiments weremodel used in first-order reasonably collapses the first-order closure model results

  • In comparison with small-scale roughness values, canopies introduce additional complications and length scales above and beyond r/hw such as canopy height, arrangement density, frontal element width, and drag coefficient. To link those length scales to the friction factor, scaling analysis aided by first-order closure model calculations were adopted

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Summary

Introduction

The modeling of urban constructed wetlands requires routing an inflow hydrograph through vegetated canopies, where the vegetation may be emergent or submerged [1,2,3,4,5]. These ‘distortions’ to the classic flow structure within the vegetation is considerably more complicated than small-scale roughness. The velocity profile for the entire flow depth is complicated and varies with the using first-order closure model calculations that utilizes the mixing length scales in Equations (3)–(5). The bulk velocity as well as the friction factor derived using this approach are compared to a large velocity profile and the possibility of deriving a general expression for friction to be used in corpus of published experiments where the parameters needed for experimentally computing the operational models (such as the SVE) for submerged vegetation frame the scope of this study. Beyond the vegetation properties (m, D, hv ), Equation (6) requires two flow-rate parameters describing the effects of vegetation elements on the flow: The drag coefficient Cd and reference velocity of vegetated region Uv

Drag Coefficient
Reference Velocity
A Friction Formula
First-Order Closure Models
Laboratory Experiments
First-Order Closure Model Runs
Scale Analysis
Scale Analysis with Vegetation Attributes
Expression for the Combined Influences of Submergence and Vegetation
Model Validation
Findings
Conclusions
Full Text
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