With the advance of urbanisation in coastal regions comes an increase in armoured shorelines and the destruction of coastal marine habitats. To combat this, ECOncrete Tech Ltd has developed a new eco-friendly armour unit, the CoastaLock. With its ecological advantages proven, its hydraulic performance is still largely unknown. This thesis aims to do the first exploratory research into the stability, reflection and overtopping performance of this CoastaLock armour unit, through a literature study and physical model tests. Data is gathered during physical model tests on a deep-water impermeable slope with different wave steepnesses, armour unit spacings, underlayer thicknesses and block orientations. The mechanism of breathing is witnessed in tests with CoastaLock armour units. This mechanism shows the armour layer repeatedly getting lifted up from the slope and placed back on it as a result of pressure differences over the top layer during maximum wave run down. This mechanism causes movement of granular material in the underlayer, with large under deformations as a result. This thesis, therefore, advocates for listing the breathing mechanism as a failure mechanism. The CoastaLock armour units show stability numbers of approximately 2 when tested at armour spacings below 10%, and stability numbers larger than 4 when tested at armour spacings larger than 10% for a wave steepness of 3.5%. Wave steepness is shown to be of a minor influence too, with the influence of underlayer thickness and unit orientation being negligible. The reflection coefficient is shown to be mainly dependent on wave steepness, and minorly on armour spacing. Reflection coefficients of approximately 0.8 to 0.5 are measured for wave steepnesses between 1.5% and 4.5%. Overtopping is shown not to play a role in situations with armour spacings lower than 10%, as the layer fails before overtopping can become an issue. For the more stable spacings, those larger than 10%, the overtopping discharge is quantified and the roughness factor is shown to vary from 0.732 for 10% spacing to 0.61 for 25% spacing. Factors other than the spacing are of a minor to negligible influence. The CoastaLock armour units show promising results for situations with a short leakage length and large armour spacings, i.e. situations where the pressure differences over the top layer are small. However, this research is the first exploratory research into these armour units and should therefore be interpreted as no more than an indication of the behaviour of CoastaLock. It is recommended to expand the research into these units, both on the units in different situations as on the failure mechanisms of the units and the solutions thereto.

Fieldwork Hydraulic Engineering’ is a course given at Delft University of Technology for the MSc Hydraulic Engineering. In collaboration with local experts Boyan Savov and Traian Marin, a team of 8 students guided by Mark Voorendt was sent to investigate the local conditions at Asparuhovo beach in Varna, Bulgaria, for purely educational purposes. Before 2019, Asparuhovo beach used to have a stable coastline with some seasonal variations. However in 2019, the Karantinata port was constructed and disturbed the equilibrium state of the beach. Rapid sedimentation occurred near the port and the port entrance. Due to this excessive sedimentation near the port entrance, the fishing port has lost almost all of its intended functionality, as minimum water depths in the port entrance approach 0.3m. The port was originally designed for larger fishing boats, which are currently not able to enter and making the port lose functionality. It is yet unknown how this sedimentation trend is formed with the construction of the fishing port. The main objective of the research was to examine the current sedimentation near Karantinata port by executing a measuring campaign during the Hydraulic Fieldwork and by setting up a 5 year monitoring program for the marine environment. By doing so, the processes which lead to sedimentation can be understood and a model can be made. With this model, adjustments to the port layout can be examined which are potentially needed for the port to operate at full functionality. To tackle these problems, the students performed the fieldwork. With 2 days of beach and foreshore measurements the research question was assessed. With the acquired data of the system, supported by additional lab sieving analysis, data processing and modelling in Delft, the students formed theories on the origin of the sedimentation problem. With these insights, recommendations for the area can be suggested. The measurements are performed on multiple locations and at each location multiple variables were researched. For Asparuhovo beach and foreshore these are the bathymetry, waterline position, wave climate, beach profile, sediment characteristics and ecology. At the fishing port Karantinata these are the port characteristics such as functions, planning and infrastructure, port entrance, bathymetry and breakwater design. At the Asparuhovo breakwater it is the top protection layer, damage assessment and measures of improvement. At Veteran beach this is the soil samples for grain size distribution. At Martsiana quarry the length to thickness ratio, blockiness were researched, as well as the diameter to check if potentially suitable for breakwater material. With this information, a preliminary model in Delft3D has been set up with the land boundaries, grid and bathymetry file. With knowledge of the coastal processes and the processed data, potential causes of sedimentation are speculated on. It is unlikely that such large amounts of sediment are coming from outside of Asparuhovo beach system, as there are no sediment rich rivers nearby, the sedimentation occurred in a very short period of two years and the sediment would mostly not be able to cross the deep navigation channel as it would settle due to lower flow velocities. It is expected that large parts of the settled sediment near the port entrance is from the beach itself. This is also more likely due to the two closed boundaries of the beach, the Asparuhovo breakwater and the Karantinata port. This was checked by analyzing the grain size diameter compared to other locations at the beach and looking at the waterline developments. It was found that the grain size at the middle of the beach was 1.8 mm and at the port entrance between 0.2 and 0.3 mm. It was suspected that the fine sediments of the middle of the beach are eroded and deposited at the port entrance as the sediment can settle at the Southeastern part behind the port breakwater due to sheltered conditions. The mechanisms that could have induced this are: rip currents, longshore currents and the different wave patterns. To examine and validate these findings, a monitoring plan for the coming 5 years is proposed. This is very important to create an understanding of the systems parameters and behaviour. Without monitoring, adjustments to the port cannot be tested in a correctly calibrated model. The parameters which need continuous measurement are the wave parameters, sea level measurements and visual beach observations. Biannual measurements are needed for currents, hydrographic works, visual observations with a drone, bathymetry and sediment parameters. Before the port is fully operational again, the port entrance needs dredging. This can be done in this time span of 5 years to ensure the passage of fishing boats. After dredging a short survey of the area needs to be performed to incorporate the changes into the model. These are the bathymetric survey, visual observations and sediment samples all around the dredging area. There are three potential solutions incorporated in the report, which can be modelled with the findings of the monitoring plan. The first potential solution to make the port fully operational again is relocating the port entrance with a curved breakwater stretching into the sea. The second solution is a combination of the entrance relocation and water flow through the port. The third is a blocking groyne stretching from Asparuhovo beach into the sea, blocking the sedimentation going into the port entrance. For all these potential solutions, dredging works are needed to reensure the required water depth for the vessel draught. The least costly and most promising is the relocation of the port entrance design. It can be noted that continuous dredging is not a sustainable solution as the sedimentation keeps occurring near the port entrance as the hydrodynamic conditions will not change. It is recommended to first find the source of the settled sediment by comparing control volumes of sediment on the beach over the years. Then a model should be set up of the Asparuhovo beach and foreshore and Karantinata port to give insights in the processes. This model needs to be validated and calibrated with input from a monitoring campaign. With a working model, the causes of sedimentation can be found and further research can be done whether the potential solutions are appropriate.

ECOncrete®‘s Coastalock is an ecologically designed armour unit, providing an alternative and/or a complement to traditional armour layers with ecologically enhanced armouring that provides shoreline stabilization, while also creating well-defined local ecosystems that mimic natural rock pools. The 2D physical model tests performed at TU Delft focused on the stability, reflection and overtopping of a slope with regularly placed single layer Coastalock armour. The 2V:3H slope had an impermeable core, no wave breaking on the foreshore and no rock toe. The stability was seen to double, with stability number Ns (Ns= Hs/ΔDn50) increasing from roughly 2 to 4 and above, by increasing the porosity between the blocks from spacing the units from 0percent to 25percent. So less concrete use led to more stability. The mean overtopping discharge could be characterized by a roughness factor of gamma_f = 0.610 (for 25percent spacing). A key goal of the Coastalock development is to demonstrate that with the use of innovative eco-engineered armour unit design it is now possible to add ecological considerations into the design process to promote biodiversity and provide ecosystem services, achieving both structural and ecological goals.@en