“…Improving predictions of wave-vegetation interactions has been an increasing focus of coastal research over the past decade (e.g., Nepf, 2012), which is often motivated by the desire to quantify the coastal protection services provided by aquatic vegetation (e.g., Borsje et al, 2011;Tang et al, 2013). Attenuation of wave energy due to different species of vegetation has been studied both experimentally (e.g., Fonseca & Cahalan, 1992;Möller et al, 2014) and in the field (e.g., Möller & Spencer, 2002;Paul & Amos, 2011), and analytical models have been developed based on conservation of wave energy to predict wave attenuation across a given aquatic vegetation canopy for both monochromatic (Dalrymple et al, 1984;Kobayashi et al, 1993) and irregular waves (Jacobsen et al, 2019;Mendez & Losada, 2004;Suzuki et al, 2012).…”
The physical roughness (canopies) formed by organisms within aquatic ecosystems (e.g., seagrass, kelp, and mangroves) modifies the local wave‐driven hydrodynamics within coastal and estuarine regions. In wave‐dominated environments, an understanding of the mean wave‐driven flows generated within and above canopies is important, as it governs material transport (e.g., of nutrients, sediment, and biota). However, until recently the effect of submerged canopies on wave‐current interactions and the resulting mean (wave‐averaged) flow dynamics has received relatively little attention. In this study, a combination of wave flume experiments and numerical modeling is used to investigate the wave‐induced mean flow profiles in the presence of a submerged canopy. The measured velocities and vegetation forces were used to derive bulk drag and inertia coefficients, and to validate a nonhydrostatic 2DV wave‐flow model. The numerical model results were used to conduct an in‐depth analysis of the mean horizontal momentum terms responsible for driving the mean (horizontal) flow within and above the submerged canopies. We show that the mean canopy hydrodynamics are driven by vertical gradients in wave and turbulent Reynolds stresses, balanced by the mean canopy drag forces. The wave Reynolds stress gradient is the dominant force driving the in‐canopy mean flow and is directly related to the vorticity that is generated when the wave orbital motions become rotational near the canopy interface. This study provides new insight in the mechanisms responsible for wave‐driven mean flows within submerged canopies and guidance for how these hydrodynamics can be predicted in coastal wave‐circulation models.
“…Improving predictions of wave-vegetation interactions has been an increasing focus of coastal research over the past decade (e.g., Nepf, 2012), which is often motivated by the desire to quantify the coastal protection services provided by aquatic vegetation (e.g., Borsje et al, 2011;Tang et al, 2013). Attenuation of wave energy due to different species of vegetation has been studied both experimentally (e.g., Fonseca & Cahalan, 1992;Möller et al, 2014) and in the field (e.g., Möller & Spencer, 2002;Paul & Amos, 2011), and analytical models have been developed based on conservation of wave energy to predict wave attenuation across a given aquatic vegetation canopy for both monochromatic (Dalrymple et al, 1984;Kobayashi et al, 1993) and irregular waves (Jacobsen et al, 2019;Mendez & Losada, 2004;Suzuki et al, 2012).…”
The physical roughness (canopies) formed by organisms within aquatic ecosystems (e.g., seagrass, kelp, and mangroves) modifies the local wave‐driven hydrodynamics within coastal and estuarine regions. In wave‐dominated environments, an understanding of the mean wave‐driven flows generated within and above canopies is important, as it governs material transport (e.g., of nutrients, sediment, and biota). However, until recently the effect of submerged canopies on wave‐current interactions and the resulting mean (wave‐averaged) flow dynamics has received relatively little attention. In this study, a combination of wave flume experiments and numerical modeling is used to investigate the wave‐induced mean flow profiles in the presence of a submerged canopy. The measured velocities and vegetation forces were used to derive bulk drag and inertia coefficients, and to validate a nonhydrostatic 2DV wave‐flow model. The numerical model results were used to conduct an in‐depth analysis of the mean horizontal momentum terms responsible for driving the mean (horizontal) flow within and above the submerged canopies. We show that the mean canopy hydrodynamics are driven by vertical gradients in wave and turbulent Reynolds stresses, balanced by the mean canopy drag forces. The wave Reynolds stress gradient is the dominant force driving the in‐canopy mean flow and is directly related to the vorticity that is generated when the wave orbital motions become rotational near the canopy interface. This study provides new insight in the mechanisms responsible for wave‐driven mean flows within submerged canopies and guidance for how these hydrodynamics can be predicted in coastal wave‐circulation models.
“…Wu and Marsooli (2012) developed a shallow water model for simulating long waves on vegetation zone under breaking and non-breaking conditions, and the numerical results showed that vegetation along the coastal shoreline has a positive benefit in reducing wave run-up on sloping beaches, whereas vegetation in open channels causes conflicting impacts: reducing inundation in the downstream areas, but increasing flood risk in a certain distance upstream. Tang et al (2013) developed a model for investigating the effects of damping due to vegetation on solitary water wave runup, that was based on the nonlinear shallow water equations and its numerical results showed that vegetation can effectively reduce the velocity of solitary wave propagation and that solitary wave run-up is decreased with increases of plant height in water and also diameter and stem density. Ma et al (2013) developed a non-hydrostatic RANS model to investigate wave propagation through a finite patch of vegetation in the surf zone and its numerical results showed that the presence of a finite patch of vegetation may generate strong pressure-driven nearshore currents, with an onshore mean flow in the unvegetated zone and an offshore return flow in the vegetated zone.…”
“…is also one of the coastal defensive measures against the tsunami waves (e.g., Dahdouh-Guebas et al, 2006;Danielsen et al, 2005;Mcadoo et al, 2011). Numerical models have been proven to be powerful tools to investigate tsunami wave interaction with the mangrove forests (e.g., Huang et al, 2011;Maza et al, 2015;Tang et al, 2013, and many others). Comparatively Y. Yao et al: LES modeling of tsunami-like solitary wave processes over fringing reefs speaking, their applications in modeling coral reefs subjected to tsunami waves are still very few.…”
Section: Introductionmentioning
confidence: 99%
“…Among various approaches for modeling wave dynamics over reefs, two groups of models are the most pervasive. The first group focuses on using the phase-averaged wave models and the nonlinear shallow water equations to model the waves and the flows, respectively, in field reef environments, and typically the concept of radiation stress (Longuet-Higgins and Stewart, 1964) or vortex force (Craik and Leibovich, 1976) is used to couple the waves and the flows (e.g., Douillet et al, 2001;Kraines et al, 1998;Lowe et al, 2009bLowe et al, , 2010Van Dongeren et al, 2013;Quataert et al, 2015). As for modeling tsunami waves at a field scale, we are only aware of Kunkel et al's (2006) implementation of a nonlinear shallow water model to study the effects of wave forcing and reef morphology variations on the wave run-up.…”
Abstract. Many low-lying tropical and subtropical reef-fringed coasts are vulnerable
to inundation during tsunami events. Hence accurate prediction of tsunami
wave transformation and run-up over such reefs is a primary concern in the
coastal management of hazard mitigation. To overcome the deficiencies of
using depth-integrated models in modeling tsunami-like solitary waves
interacting with fringing reefs, a three-dimensional (3-D) numerical wave
tank based on the computational fluid dynamics (CFD) tool
OpenFOAM® is developed in this study. The Navier–Stokes
equations for two-phase incompressible flow are solved, using the large eddy simulation (LES) method for turbulence closure and the volume-of-fluid (VOF)
method for tracking the free surface. The adopted model is firstly validated
by two existing laboratory experiments with various wave conditions and reef
configurations. The model is then applied to examine the impacts of varying
reef morphologies (fore-reef slope, back-reef slope, lagoon width,
reef-crest width) on the solitary wave run-up. The current and vortex
evolutions associated with the breaking solitary wave around both the reef
crest and the lagoon are also addressed via the numerical simulations.
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