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Estuaries are found along many of the world’s coastlines irrespective of geological setting, energy regime, and depositional environment (). They also represent one of Earth’s most dynamic sedimentary environments because they lie at the interface of the terrestrial and marine spheres, and evolve in response to the interaction of fluvial, coastal (tidal) and marine (wave) processes. The genetic classification of estuaries has focused on the interaction of processes in these fluvial, coastal, and marine environments (e.g. ; , although in practice the processes influencing estuary morphodynamics vary along the length of the estuary, with tidal state, and over different time-spans. Estuaries are therefore not homogeneous sedimentary systems: their fluvial, coastal and marine environmental regimes are all subject to change in their intrinsic characteristics and their interactions over different scales of time and space, particularly in response to changes in climate and relative sealevel (RSL) (). It can be argued, therefore, that the estuaries found along present-day coasts worldwide are both environmentallysensitive and geologically-transient phenomena.

The coast of Ireland, located on the paraglacial shelf of the north-east Atlantic (), is well placed to respond dynamically to external forcing factors in the marine and onshore environments. These factors include eustatic changes in relative sea-level (RSL) driven by glacial cycles on 3 and 4 order (Milankovitch) time-scales; changes in shelf, nearshore, coastal, estuarine, dune and fluvial sediment storage and supply; changes in North Atlantic wind and wave climates; and the effects of high-magnitude events such as storms, storm surges and sea floods (). In addition, formerly paraglacial coasts and shelves in particular are subject to a range of environmental factors impacting on present-day shelf stratigraphy and sediment dynamics. These factors include sediment supply to continental shelves, and 4 order (glacioisostatic-driven) changes in RSL (; ; ; ). In western Britain, late Devensian (Wisconsinan; ∼ 25-13 kyr BP) ice spread outwards from dispersal centres in upland areas of Scotland, Wales, northern England, and northern and western Ireland (). This ice spread generally radially onto adjacent lowlands and offshore shelves in the North Atlantic, North Sea and Irish Sea (including the Northern Ireland coast) which were dry due to 4 order eustatically-driven RSL fall ().

Due to the increasing demand for clean water, recreation areas, and healthy ecosystems the management of watersheds has become an issue of increasing importance. This demand has increased the need for detailed inventories of the present state of watersheds and the understanding of related processes. In 1996, the New York State Department of Environmental Conservation (DEC) initiated an effort to map the benthic habitat of the Hudson River Estuary as part of a larger Hudson River Action Plan. This project includes extensive mapping using sidescan sonar, subbottom profiling, single and multi-beam bathymetry, as well as collecting ground truth data with sediment cores, grab samples, and sediment profiling imagery (SPI). The goal of the project is the creation of a comprehensive data set that includes detailed interpretive maps of sediment distribution, grain size, bed forms, and benthic habitats ().

Over the past 10 to 15 years the use of Geographical Information Systems (GIS) in the analysis of coastal and marine systems has expanded dramatically. One of the reasons for this is the fact that GIS is an ideal means to analyse and visualize the complex spatial and temporal evolution of morphologically complex areas (). Most environmental data in dynamic coastal areas are complex and show variations in location, depth, and time (; ), raising the problem of finding suitable ways to represent environmental phenomena ().

New Inlet formed on 2 January 1987 when a northeasterly storm passed over the southern portion of Cape Cod, Massachusetts, USA (Fig. 1). Breaching of Nauset Spit during this event presented an excellent opportunity to describe and understand how tidal inlets evolve hydrodynamically and morphologically after their formation (, ; ). In this study an analysis of the evolution of a newly formed, frictionally-dominated bay is conducted and results are compared to two well-documented inlet systems.

Puerto Galván (Fig. 1) is one of the five harbors that form the BahÍa Blanca Harbor System, the largest and deepest of Argentina. The harbors are all located along the Canal Principal of the BahÍa Blanca Estuary, a mesotidal, coastal plain environment () formed by a series of major NW-SE trending channels separating extensive tidal flats, low salt marshes and islands. The geomorphology and physical characteristics of the estuary are described in detail elsewhere () including a recent review of its major environmental features ().

Determining temporal and spatial variations of suspended sediments and other water column physical properties (e.g. temperature, salinity, turbidity) in estuarine systems require high-resolution observations over several scales of space and time (; ; ; ). Although obtaining these types of measurements can be difficult due to time, equipment and monetary constraints, they are important for developing a fundamental scientific understanding of many estuarine processes, such as primary and secondary productivity, the transport and fate of contaminants, nutrient cycling, or sedimentation (; ; ; ; ; ; ; ; ). Accordingly, numerous studies have been conducted over the last several decades that seek to describe and quantify basic estuarine physics and sedimentological processes (see ; ; Eisma, 1993, and for reviews). For instance, it has been long understood that the combination and balance of freshwater input from rivers and tidal energy controls or strongly influences net non-tidal circulation (density driven), water column stratification, and sedimentation (; ; ; ; ; ; ; ; ; ).

Research into the dynamics of estuary morphology has been stimulated by increasing commercial, environmental and legislative pressures and by the accumulated impacts of human intervention (; ). Of particular concern in the UK is the impact on estuaries of sea-level rise and large-scale interventions associated with dredging and port development, flood defence and habitat restoration. Prediction of estuary response to such changes requires an understanding of present-day processes and their interaction with morphologies that are often shaped by past human activities. As Pye and Allen (2000) note, estuarine research has hitherto been characterised by narrow disciplinary foci, such that research fronts in engineering, geomorphology and Quaternary science have rarely converged. The UK Estuaries Research Programme (; ) has advocated a more holistic and interdisciplinary perspective, combining ‘bottom up’ studies of short-term hydrodynamics and sediment movement with ‘top down’ models of larger-scale morphodynamic behaviour, such that the predictive power of physically-based simulation may be realised within a conceptual framework provided by geomorphological analysis of longer-term sedimentary function. Few estuaries have been monitored in the spatial and temporal detail needed for integrated modelling of this kind and there is a need for intensive studies encompassing a greater variety of natural and anthropogenic contexts.

Over the past several decades, estuaries have earned a reputation as sediment sinks through the theoretical and empirical works of many scientists (e.g. ; ; , , ; ; ; ; ; ). These studies have documented the combined roles of sediment influx rates, sea-level rise, climate, and estuarine circulation as the dominant controls on estuarine infilling (). However, aspects of most of these models (e.g. distance-velocity asymmetry and settling lag and scour lag) only consider the movement of fine-grained sediments (<100 µm) capable of suspension or transport-limited systems in which estuarine sediment supply is greater than the transport capacity (). Much less is known about the dynamics (i.e. estuarine processes and time scales responsible for sediment fluxes) within fluvial-estuarine transition zones with respect to bedload sediment transport ()

Although it is widely stated in the literature that estuarine river mouths are sediment sinks, northern New England estuaries are an exception to this model because they export coarse-grained sediment to the nearshore. The traditional view is that estuaries fill with sediment ranging from mud to gravel derived from fluvial or upland sources as well as from the inner continental shelf and adjacent shorelines. Fluvial sediments are deposited primarily in the inner and central portions of an estuary, although fluvial mud can be deposited in the outer estuary in some tide-dominated systems (e.g. sections of the Gironde River (France), ; Fly River (Papua New Guinea), ). The deposition of sediment in the inner and central portions of an estuary is due to the combined influences of a downstream decrease in the riverine current strength and clay flocculation produced by fresh and saltwater mixing. In estuaries having high sediment loads, fluidized mud can be an important component of estuarine sedimentation (, ). Marine sediments enter the outer estuary due to residual, flood-oriented bottom currents and stronger flood than ebb tidal currents. This former flow pattern is caused by the seaward-flowing freshwater advecting the underlying saltwater producing a mass balance deficit of saltwater ().