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 Wind wave-induced erosional effects are among the chief landscape-forming processes in tidal biomorphodynamics. Wave-driven bottom erosion, in fact, controls the equilibrium elevation and dynamics of subtidal and tidal flat surfaces, and the impact of waves against salt marsh margins influences their stability. The relevance of predictive studies projecting wind wave patterns in space and time is thus notable especially in view of the limited insight gained so far. Here we have employed a complete, coupled finite element model accounting for the role of wind waves and tidal currents on the hydrodynamic circulation in shallow basins to analyze the characteristics of combined current- and wave-induced exceedances in bottom shear stress over a given threshold for erosion. The results of our analyses from the Venice Lagoon suggest that wind wave-induced resuspension events can be modeled as a marked Poisson process, thus allowing one to set up a theoretical framework which can be used to model wind wave effects through the use of Monte Carlo realizations. This bears important consequences for quantitative analyses of the long-term biomorphodynamic evolution of tidal landscapes.
 Wind waves and related erosion processes play a critical role in the biomorphodynamic evolution of tidal landscapes. Sediment deposition, wave-induced erosion, and the rate of relative sea level rise determine the equilibrium elevation and dynamics of subtidal platforms and tidal flats [e.g., Allen and Duffy, 1998; Fagherazzi et al., 2006; Green and Coco, 2007; Marani et al., 2010; D'Alpaos et al., 2012]. Moreover, the balance between horizontal progradation of salt marshes and wind wave erosion of their boundaries dictates the position of the marsh edge [e.g., Möller et al., 1999; Mariotti and Fagherazzi, 2010; Marani et al., 2011]. Both in the vertical and in the horizontal planes, temporal and spatial patterns of wind wave bottom shear stresses (BSSs) have important implications on the morphological and biological features of the tidal landscape [e.g., Carniello et al., 2005; Fagherazzi and Wiberg, 2009; Mariotti et al., 2010]. Intense wave-induced BSSs may lead to the disruption of the polymeric microphytobenthic biofilm [e.g., Amos et al., 2004] and promote the resuspension of sediments transported within the basin by tidal currents, thus influencing light availability in the water column [e.g., Lawson et al., 2007] and consequently the stability of sea grass ecosystems [e.g., Carr et al., 2010]. Finally, because of their effect on the equilibrium elevation of tidal flats [e.g., Marani et al., 2010], wave-induced erosion processes contribute to controlling the size of the tidal prism and related morphological features of tidal networks, such as channel cross-sectional areas [e.g., D'Alpaos et al., 2010] and drainage density [e.g., Marani et al., 2003; Stefanon et al., 2012].
 Numerical models provide ways to describe hydrodynamic and wind wave fields in shallow tidal basins [e.g., Umgiesser et al., 2004; Carniello et al., 2005] and their influence on the morphodynamic evolution of tidal landscapes. Modeling tidal landscape morphodynamic evolution over timescales of centuries, however, calls for the use of simplified approaches [e.g., Murray, 2007] due to the numerical burdens involved when using full-fledged models, thus justifying analyses of the type proposed herein. Our aim is to develop a synthetic theoretical framework to represent wind wave-induced resuspension events and account for their erosional effects on the long-term biomorphodynamic evolution of tidal systems. To this end, we have applied a fully coupled wind wave-tidal model (WWTM) [Carniello et al., 2005, 2011] to the Venice Lagoon, the largest Mediterranean brackish water body characterized by an average tidal range of about 1 m, with maximum tidal excursions of ±0.75 m around mean sea level (msl). Our key result, emerging from the analysis of the local, temporal evolution of the modeled BSSs, is that wave-induced resuspensions can be seen as marked Poisson processes, in analogy with the occurrence of precipitation [e.g., Rodriguez-Iturbe et al., 1987, 1988], shallow landslides [e.g., D'Odorico and Fagherazzi, 2003], and fires [e.g., D'Odorico et al., 2006], or with processes obtained censoring Poisson rainfall arrivals via a soil moisture dynamics [e.g., Botter et al., 2007]. A proper statistical mechanics, possibly applied in a predictive manner generating Monte Carlo realizations of long-term evolution of tidal water bodies, is therefore in sight for the biomorphodynamic evolution of tidal landscapes.
 The WWTM employed herein describes, on the same computational grid, the hydrodynamic flow field together with the generation and propagation of wind waves (see the supporting information and Carniello et al. [2005, 2011] for a detailed description of the model). The hydrodynamic model solves the 2-D shallow water equations using a semi-implicit staggered finite element method based on Galerkin's approach [D'Alpaos and Defina, 2007], thus yielding water levels which are used by the wind wave model to assess wave group celerity and bottom influence on wave propagation. The wind wave model is based on the solution of the wave action conservation equation, parameterized using the zero-order moment of the wave action spectrum in the frequency domain [Carniello et al., 2005, 2011]. The model can also account for the spatial variability of the wind forcing, through an interpolation procedure of the available wind data [e.g., Brocchini et al., 1995; Carniello et al., 2012]. The WWTM has been largely tested against field observations in the Venice Lagoon and the Virginia Coast Reserve lagoons [e.g., D'Alpaos and Defina, 2007; Carniello et al., 2011; Mariotti et al., 2010], thus suggesting that the model is suited to computing temporal and spatial variations of the BSS in shallow microtidal basins. Numerical simulations were carried out on a computational grid which represents the Venice Lagoon and a portion of the Adriatic Sea (see Figure 1) and consists of about 52,000 nodes and about 100,000 triangular elements. The model was forced by using hourly tidal levels measured at the Consiglio Nazionale delle Ricerche (CNR) Oceanographic Platform, located in the Adriatic Sea in front of the Venice Lagoon (see Figure 1), and wind velocities and directions observed at the Chioggia anemometric station, for which various 1 year long time series of wind data were available. We forced the model with the time series recorded in 2005, which was shown to be a “representative” year for the wind characteristics in the Venice Lagoon. The probability distribution of wind velocities for the time series recorded in 2005 was, in fact, the closest to the mean of the probability distributions computed for every year between 2000 and 2008.
 At any location within the Venice Lagoon, we analyzed the temporal evolution of the BSS on the basis of a “Peaks Over Threshold” (POT) method, once a critical shear stress for erosion was chosen [Amos et al., 2004]. Finally, we verified whether or not wind wave resuspension events could be modeled as a Poisson process; i.e., we performed a Kolmogorov-Smirnov (KS) goodness of fit test to test the hypothesis that the interarrival time of resuspension events (the time between two consecutive resuspension occurrences) is an exponentially distributed random variable.
3 Results and Discussion
 We first start by considering three locations (S1, S2, and S3) in the Venice Lagoon for which we provide a detailed description of model results (see Figure 2 for station S3) and the statistical characteristics of wave-induced resuspension events (see Figure 3 for all stations). The three stations (see Figure 1) were selected to represent three different typical environments in the Venice Lagoon: (i) a subtidal platform (depth of 2.0 m below msl) in the deepest part of the lagoon, fetch unlimited to the most frequent and intense wind directions of Bora (blowing from NE) and Scirocco (blowing from SE) (S1); (ii) a very shallow tidal flat (depth of 0.75 m) located in the northern part of the lagoon where large salt marsh areas are present (S2); and (iii) a tidal flat (depth of 1.10 m) in the area between the city of Venice and the Marco Polo Airport (S3). Fluctuating tidal levels (Figure 2b) and the related tidal current velocities control the temporal evolution of current-induced BSSs, τtc (Figure 2c), which however are not strong enough to produce bottom erosion on the unchanneled portions of the tidal basin. Current-induced BSSs, in fact, are well below the critical shear stress for erosion, τc=0.4 Pa [e.g., Amos et al., 2004; Marani et al., 2010; Mariotti et al., 2010], displayed by the continuous red lines in Figures 2c–2e. Wind intensities, together with local fetch and water depths, govern the temporal evolution of wave-induced BSSs, τww (Figure 2d), whereas it is worth noting that the total BSS, τcw, determined by the combined action of currents and waves (Figure 2e), is enhanced beyond the sum of the two contributions [e.g., Soulsby, 1995]. Figure 2f shows the effect of the nonlinear interaction between waves and currents by portraying the temporal evolution of the difference τcw−(τtc+τww) which can be as large as 10% of the total BSS. Although wave-induced BSSs are larger than those induced by tidal currents, the latter play a significant role in modulating the temporal evolution of the total BSS, furthermore increasing peak BSS values by up to 30%, as also observed by Mariotti et al. , thus importantly affecting the occurrence of overthreshold exceedances.
 In order to provide a statistical characterization of wave-induced resuspension events, we have analyzed the time series of computed total BSSs, τcw, on the basis of a POT method. This allowed us to identify times of cross-up and cross-down of BSS with respect to the critical value (and therefore single resuspension events), the interarrival times of resuspension events (the time between two consecutive cross-ups), their maximum intensity (the peak excess, defined as the largest excess in a cluster of overthreshold BSSs, (τcw−τc)max), and duration (time between a cross-up and the following cross-down, during which the BSS stays over the threshold). The time series of BSSs were preliminarily low-pass filtered through a moving average operation (with a 6 h span) in order to remove short-term fluctuations, leading to spurious upcrossing and downcrossing of the fixed threshold, without losing the modulation given by the semidiurnal tidal oscillation. Such a procedure is necessary to meet the assumptions embedded in our analysis which require resuspension events to be independent (see the supporting information for further details). Figure 3 compares the computed exceedance probabilities (circles) of interarrival times (Figures 3a–3c), maximum intensities of overthreshold events (Figures 3d–3f), and durations of overthreshold events (Figures 3g–3i) with the theoretical exponential trend (solid lines), for the three selected locations (S1, S2, and S3).
 We first note that the interarrival time of resuspension events is described by an exponential distribution (Figures 3a–3c). The parameter λt of the exponential distribution is the mean rate of occurrence of wave-induced resuspension events; i.e., 1/λt is their mean interarrival time. This observation is quantitatively supported by the results of the KS test which is satisfied in all the cases (sites S1, S2, and S3) at significance level α=0.05. We also note that both the peak excess (τcw−τc)max and the duration of the resuspension events reveal to be exponentially distributed random variables, with mean 1/λe and 1/λd, respectively (Figures 3d–3f and 3g–3i, respectively). The KS test performed for those probability distributions is satisfied in all the cases, at significance level α=0.05. The mean interarrival times for the three considered locations range between about 9 and 16 days, whereas the mean durations range between 13 and 16 h, and the mean peak excesses characterizing the resuspension events range between 0.15 and 0.21 Pa. The parameters of the exponential distributions display some spatial variability as we show in Figure 4.
 Before analyzing the spatial variability of mean interarrival times, peak excesses, and durations, it is worthwhile recalling that the shear stress induced on the bottom by wind waves generally depends on wind velocity, fetch, and water depth. For any prescribed wind intensity and fetch, the relationship between BSS and water depth is represented by a curve peaking at some intermediate water depths: For both small and large depths, wind waves do not induce appreciable BSSs. As wind velocity increases (for a fixed fetch), the BSS increases and peaks at progressively lower water depths; as fetch increases (for a fixed velocity), the BSS increases and peaks at progressively larger water depths [e.g., Fagherazzi et al., 2006; Marani et al., 2010]. Water depth is a function of basin bathymetry and local tidal levels, whereas fetch depends on basin morphology (for the sheltering effect of, e.g., salt marshes on adjacent downwind flats) and water depth. The observations above suggest that the characteristics of resuspension events display complex spatial patterns, as it emerges from Figure 4 which portrays the mean interarrival time (Figure 4a), peak excess (Figure 4b), and duration of overthreshold events (Figure 4c) at any location within the Venice Lagoon in which the KS test, made in order to verify that the mentioned variables are exponentially distributed random variables, is satisfied at significance level α = 0.05 (Figure 4d).
 Interestingly, we note that portions of the lagoon in which wind wave-induced resuspension events cannot be modeled as a Poisson process are mostly represented by salt marshes and tidal channel networks (Figure 4d). No exceedances over the fixed threshold, τc, tend to occur over salt marsh platforms because of the reduced water depth [e.g., Carniello et al., 2005; Möller et al., 1999]. Within the channel network, exceedances do tend to occur but these are mostly related to peak excesses promoted by tidal currents, which cannot be modeled as a Poisson process (Figure 4d). Large interarrival times (Figure 4a) are found leeward of spits, marsh platforms, islands, or artificial structures (see, e.g., the Liberty Bridge in Figure 1) which provide a sheltering effect particularly to Bora wind, the most intense and morphologically significant wind in the Venice Lagoon. This occurs, in particular, at sites sheltered by marshes and the mainland in the northeastern part of the Venice Lagoon and in its western portions (see Figure 1). On the contrary, short interarrival times characterize fetch-unlimited portions of the lagoon with depths around 1.5 m below msl at which wave-induced BSSs are known to reach their maximum intensity [e.g., Fagherazzi et al., 2006; Carniello et al., 2009]. Portions of the lagoon much deeper or much shallower than 1.5 m below msl, or characterized by smaller fetch, display intermediate interarrival times (Figure 4a).
 Overthreshold peak intensities (Figure 4b) and durations (Figure 4c) are much larger in the central and southern parts of the Venice Lagoon, than in its northern part, which is sheltered by the mainland from Bora winds and is characterized by the presence of very shallow flats and large salt marsh portions which also provide sheltering effects. Overthreshold peak intensities and durations display their maximum values in the fetch-unlimited central portions of the lagoon characterized by water depths around 1.5 m. Large overthreshold peak intensities and long durations are also found to occur in the southern part of the lagoon. This agrees with recent observations emphasizing a critical erosive trend for the tidal flats and subtidal platforms in the central-southern part of the Venice Lagoon, where fine sediments are eroded from the bottom during intense storm events and transported toward the inlets where they are flushed out of the lagoon [e.g., Amos et al., 2004; Carniello et al., 2009; D'Alpaos, 2010].
 Finally, we observe that if detailed bed compositions were known over the domain, together with the spatial distribution of sea grasses, microphytobenthos, and halophytic vegetation, the proposed framework would allow one to account for related spatial variabilities in the threshold shear stress. We also recall that the POT formulation of the extreme value theory prescribes that for increasing censoring thresholds, the exceedances must be Poisson distributed [Cramer and Leadbetter, 1967]. As the threshold increases, the process is therefore known to remain Poisson, but obviously, longer and longer simulations are required in order to contrive meaningful statistics, owing to the progressively rarer events producing a BSS larger than τc. This is true as long as the threshold can still be exceeded. In the case of decreasing thresholds, the process remains Poisson provided that the threshold is high enough to exclude “deterministic” exceedances, such as those related to tidal currents, in our case (see the supporting information for detailed discussion on the effects of different threshold values).
 We believe that our analyses may help refine our understanding of the effect of wave-driven erosion processes on the biomorphodynamic evolution of the tidal landscape, demonstrating, in particular, that these processes can be described as marked Poisson processes with exponentially distributed interarrival times, intensities, and durations. We speculate that the importance of our approach for long-term biomorphodynamic studies lies in the technical possibility put forward to generate Poissonian sequences of forcings through which Monte Carlo realizations of relevant morphological evolutions can be computed. Ensemble averages of possible realizations will thus allow significantly accurate predictions of long-term morphologies and their expected uncertainty.
 This work was supported by the CARIPARO Project titled “Reading signatures of the past to predict the future: 1000 years of stratigraphic record as a key for the future of the Venice Lagoon.” A.D. thanks “Thetis spa” for financial support, L.C. thanks “Fondazione Vajont” for financial support. The authors thank two anonymous reviewers for their comments.
 The Editor thanks two anonymous reviewers for their assistance in evaluating this paper.