The amount of plastic in the aquatic environment is rapidly growing, with plastic litter having been reported in almost every marine environment. Understanding plastic dispersion is a key knowledge gap for plastic litter management and cleaning. It is widely assumed that the main source of plastic litter to the oceans is terrestrial and, therefore, the dominant plastic pathway from land sources to the ocean is via coastal regions. However, although there is relatively good knowledge on how the plastic particles move by oceanic currents, it is not clear how the plastic particles are transported by highly nonlinear coastal waves (see van Sebille et al., 2020, for a recent review on the physical plastic transport). Indeed, most of the existing global numerical models predicting plastic fluxes do not explicitly consider the plastic motion in coastal regions including the potential plastic beaching (i.e., plastic being washed ashore) (Neumann et al., 2014). The hydrodynamics controlling the motion of plastic in intermediate and shallow water is dominated by nonlinear gravity waves propagating toward the shoreline (wave motions and wave-induced currents). A particle floating on the free surface of a periodic gravity wave experiences a net drift in the direction of wave propagation termed Stokes drift (Stokes, 1847). The Stokes drift velocity is explained by the difference between the average Lagrangian velocity experienced by the particle and the average Eulerian flow velocity of the fluid (Longuet-Higgins, 1953; van den Bremer & Breivik, 2017). The Stokes drift is a second order velocity (Longuet-Higgins, 1953) of smaller magnitude than the magnitude of the wave orbital motion but,