1. Introduction
Extreme events such as tsunamis, flooding, and erosion have significantly increased in recent times. These events have caused massive economic losses globally, especially in the EU's coastal regions. One such event was Hurricane Nadine, which caused severe flooding and erosion, affecting communities and critical infrastructure along hundreds of miles of shoreline. Experts predict that climate change will cause a rise in extreme coastal events, and the resulting increase in sea levels may worsen their effects. [
1]. The quality of coastal water is deteriorating because of microbial pathogens, fertilizers, pesticides, and heavy metal contamination. Coastal events cause these and threaten the ecosystem and human health. In nearshore regions, various processes such as physical, biological, and chemical activities can affect human and ecosystem health. These regions are also impacted by disruptive economic activities like recreation, tourism, habitat, and ecosystem services, which need to be maintained for the well-being of future generations [
2]. By exploring this research theme, we can enhance our comprehension of the physical mechanisms involved in extreme events. This, in turn, can lead to the development of more effective models for managing flooding, erosion, and recovery through natural means. Solutions require collaboration between scientists and engineers, nearshore communities, academicians, governments, and the coordinated development of nearshore coastal process observational and modeling research infrastructure to create novel nature-based solutions. By studying nearshore processes and exploring green mitigation solutions, we can gain new insights and develop better models for understanding this vital area. Collaborative transfer research involves stakeholders from knowledge institutes, communities, industries, and governments, using resources like a flume lab for testing and a scale-up to living lab sites that will provide the needed solutions to develop the best nature and soft engineering technology to protect future coasts.
Traditional hard engineering to protect the coast using concrete did not account for climate impact during the design. It is more likely that most structures will not live through their lifetime design year [
3]. Therefore, there is a need to develop a system for climate change adaptation that will provide solutions to climate-induced risk. Growing seaweed to dampen incoming waves to the coast is one way to address and mitigate this risk [
112].
This review focuses on technology to plant seaweed as a nature-based solution that leverages efforts, avoids redundancy, and moves science and engineering rapidly forward, improving technology while protecting the natural ecosystem. A model test experiment followed the review, and the finding was published in [
112]. Seaweed and seagrass green eco-engineering eco-technology systems will be designed for future deployment and tested in selected troubled coasts to assess mitigation that a natural-base and ecological approach can provide coastal protection and ensure environmental conservation. Research on nearshore processes involving societal needs and scientific challenges has been categorized into three main themes. These themes involve the interplay and exchange between hydrodynamics, morphodynamics, anthropogenic interactions, and geological, meteorological, hydrological, and biological processes [
3].
To develop the nature-based infrastructure that addresses current climate-induced coastal and nearshore challenges, the paper proposes building a sustained integrated nature-based solution system. Our approach to tackling the issues of climate and ocean challenges involves researching nearshore processes. This will aid in understanding and predicting long-term coastal change, flooding, erosion from extreme storm events, nearshore pollution, and water quality evolution. We will achieve this by developing innovative nature-based infrastructure, including observations and modeling. Incorporating community participation and awareness will help foster and sustain the operation of the novel system and technology [
4]. Besides using sea space for transportation and natural gas exploration, farming the sea and the ocean for other nature-based products is necessary. Cultivating seaweed and seagrass protects the coast from erosion, mitigates climate change, and provides bioremediation [
5]. There are many seaweed species, and distinct species grow in different waters, so cultivation is essential.
This paper explores the cultivation of macroalgae that can provide ecosystem services, including eco-hydraulic coastal protection and bioremediation for coastal cities and islands and circular use of the harvested plants for bio-based raw materials (i.e., bioplastics and bio-textiles). [
6,
7,
8]. This paper explores how seaweed farms can be an effective nature-based solution for mitigating environmental issues. This method offers more farming areas, which helps to meet the growing need for seaweed and seagrass as a natural resource. Wave impact damping by seaweed types and farming structures in controlled laboratory experiments was conducted [
112].
3. Extreme Events, Climate Stressors, and Nearshore Problems
The UN Atlas of the Oceans reports that over 40% of people worldwide live within a 150 km distance from a coastline. Coastal regions, both inland and at sea, are experiencing rapid population growth and increasing tourism [
9]. Nearly one billion people across the globe reside at elevations that are within 10 meters of the current sea level. Communities, infrastructure, ecosystems, and habitats are at risk due to long-term erosion. Additionally, extreme storms can lead to billions of dollars in damage and degraded water quality, negatively impacting the ecosystem and human health [
10,
11]. Nearshore processes refer to the intricate interactions among water, sediment, biota, and humans. Understanding the nearshore processes helps to predict and manage the vulnerable nearshore environment. This includes the causes of additional hazards leading to flooding inland. Coastal flooding and sea level rise are expected to accelerate due to the warming climate [
12,
13]. Over the last five decades, observing nearshore processes and different solutions has provided insight into improved methods. As coastal urbanization continues to rise and threats of future climate change loom, the demands of society are increasing. However, significant scientific obstacles still need to be overcome [
14]. Climate change can result in more frequent coastal extreme events, rising sea levels, and a corresponding increase in the impact of these events [
1,
15]. The challenges of today are increased pressure on biodiversity due to environmental pollution, climatic change, and coastal squeeze, while the growing population needs higher productivity and protection from disasters. The ability of both land and water ecosystems to provide necessary services to humans is at risk due to the impact of climate change, which is a natural response [
16,
17]. This can negatively affect the integrity of these ecosystems [
10].
Therefore, it is imperative to assess the risk and vulnerability of coastal hazards and biodiversity losses, including current and future typhoons, monsoons, tsunamis, sea level rise scenarios, associated impact and damage to critical infrastructure, and analysis in terms of the damage that are detrimental to the economy and disruptive to the local community.
This statement holds particularly true when considering worldwide climate change and rising sea levels. To limit warming to 1.5° C and consequential sea level rise, several intergovernmental organizations and governments have agreed to restrict global greenhouse gas (GHG) emissions [
18]. Nonetheless, annual greenhouse gas (GHG) emissions are continuously rising [
19]. Emanating climate change and coastal changes are an increased damage potential on critical infrastructure and detrimental effects on biodiversity, as well as socioeconomic effects and the disruption of local community activities. Some challenges facing today’s society include risk and resilience of coastal communities, species biodiversity and inclusiveness, growing population, an increasing need for biomaterial, and damages detrimental to the economy and disruptive to the local community. Additionally, estuarine and coastal waters are highly vulnerable to pollution from non-point and point sources, which are often carried by rivers and streams [
20,
21]. Riverine transport is the primary mechanism for the direct impact of terrestrial human activities on the nearshore marine environment [
22,
23]. Pollutants such as excess nutrients and sediments carried by rivers pose a severe threat to the coastal and marine ecosystems [
24,
25]. Changes in wastewater discharge, modification of physiographic features, and fluctuation in the amount and distribution of freshwater inflow are essential factors to consider [
26,
27].
Figure 2 shows the IPCC report warns about rising sea levels and coastal ecosystem threats.
4. Threat of Climate Change, SLR, and Threat to Sustainable Development
Recently time has seen environmental calamity and abnormal environmental behavior where the consensus of scientists has agreed to be linked to human activities. The connectivity and interdependency of the planetary system revealed uncertainty in the dynamics of air, water, and soil [
28]. Especially the wave setup from the middle of the ocean involves a combination of temperature and wind, which in one way or another, imposes more energy on waves propagating inland. Global warming has various effects, such as rising sea levels, alteration of precipitation patterns, and growth of deserts in subtropical regions. Rising temperatures also have the potential to increase societal stress caused by natural disasters such as earthquakes and floods. Climate change involves climate variability and the statistical distribution of weather over a long time. The increase of greenhouse gases in the atmosphere, including water vapor, carbon dioxide (CO2), methane, and nitrous oxide, is caused by human activities that contribute to climate change. Ozone GHG emissions have increased over the years; however, the accuracy of the increase is limited because of the environmental differences associated with all places. [
29], reported the potential of seaweed and seagrass carbon sequestration.
The causes of climate change are atmospheric composition, including concentrations of greenhouse gases. The movement of tectonic plates leads to alterations in the position and quantity of continental and oceanic crust on the Earth's surface. This impacts wind and ocean currents, changes in solar output, the orbital dynamics of the Earth-Moon system, and volcanic activity such as eruptions of impact volcanoes [
30]. Oral traditions and climate proxies such as ice cores, tree rings, sub-fossil pollen, boreholes, corals, and lake and ocean sediments report climate changes over shorter periods [
31]. The increasing amount of greenhouse gas emissions is resulting in the warming of the ocean, leading to coral bleaching, loss of ecosystems, extreme weather events, and a constant rise in sea levels. The ocean's increasing temperature has led to the melting of glaciers and a reduction in snow cover. This has caused warm-adapted plant and animal species to move higher up the slope, while cold and snow-adapted species face a higher risk of extinction. The melting of the cryosphere is anticipated to impact leisure pursuits, tourism, and cultural resources. As the ocean warms, the mixing between water layers decreases, which results in a reduced supply of oxygen and nutrients for marine life.
The impact of climate change can be felt by individuals, ecosystems, and livelihoods, emphasizing the importance of implementing measures to limit global warming to 1.5° C instead of 2° C. Seagrass meadows and kelp forests, among other coastal ecosystems, are at a moderate to high risk at this temperature. Since the era before industrialization, human activities have been responsible for about 1.0° C of global warming. As a result, there have been adverse effects on people, nature, and livelihoods [
32]. Due to climate change, the ocean has absorbed over 90% of the excess heat in the atmosphere. As a result, there has been a rise in ocean acidity. The oceans have absorbed the emissions to 20 to 30%, and this ongoing absorption will further worsen the situation. The occurrence of marine heat waves can cause significant damage to warm-water corals, kelp forests, and the distribution of marine life. The expected impacts on the ecosystem include the reduction of habitats and biodiversity, as well as the deterioration of the functions of the ecosystem. Currently, coral reefs are facing significant threats due to increasing water temperatures. The heated water also evaporates from oceans into the atmosphere leading to heavy rainfall and flooding inland; alternatively, in other locations, the heat has caused dry land, heatwaves, drought, and wildfires. In this mechanism, oceans control the temperature, humidity, and weather [
31,
33].
The rise in sea level results from elevated ocean temperatures, which in turn are caused by the emissions of greenhouse gases. This phenomenon has a reciprocal impact on marine life. In the 20th century, the average sea level worldwide increased, resulting in a rise of approximately 15cm in the global mean sea level. The rate of sea level rise has experienced more than a twofold increase, and in the absence of substantial emissions reductions, the phenomenon is expected to accelerate further. Projections indicate that by the year 2100, the sea level will attain a height of 1.10m. It is infrequent for extreme sea level events to occur during high tides; however, there is an anticipated increase in the frequency of intense storms. By the year 2050, many coastal cities and small islands situated at low elevations will face the risk of annual flooding and land loss, particularly if they lack effective adaptation measures. This poses a serious threat to these areas and highlights the pressing need for comprehensive and sustainable solutions to minimize the impact of climate change on vulnerable communities [
18]. These events resulted in creating of an Intergovernmental Panel on Climate, which aims to offer an unbiased scientific perspective on climate change and its effects on politics and the economy. The climate tipping point is the change from a stable state to an irreversible condition. The aim of the United Nations Climate Change Conference (COP) is to prevent climate tipping points.
Figure 3 shows that sea level rise risk outpaces current technology.
Natural variability has an impact and strong connectivity on the water cycle. To design effective climate change mitigation and adaptation strategies, it is crucial to have a comprehensive understanding of uncertainty. This knowledge can help determine the most efficient path forward. Forests and other vegetated lands can capture and store carbon in their biomass and the soil [
34]. Within the marine environment, various vegetated systems, such as salt marshes, mangroves, and seagrass meadows, function similarly to land-based flora by sequestering and storing carbon [
35]. Adopting the blue-green future approach is increasingly gaining traction as a viable option for adaptation. The ocean, which covers 70% of our planet, plays a crucial role in mitigating the impacts of climate change. It serves as a buffer and provides us with essential resources such as food, energy, medicine, and employment. Moreover, it is responsible for the production of oxygen, which is vital for our survival. The world’s ocean and cryosphere have been absorbing climate change for decades, and this has been causing high consequences to nature and society. Taking care of ecosystems and managing natural resources can lower risks and benefit the community. It's essential to protect and restore these resources.
An instance of this would be the discernible pattern in the statistical analysis of flash flood events, which implies that they occur with increasing frequency [
36,
41]; (
Figure 4). Between 2012 and 2016, there was a discernible increase in the frequency of flash floods caused by extreme weather events. This trend exhibited an annual rise of 100%, which is statistically significant and noteworthy [
37,
38]. Only two years have hurricanes exceeded the standard labeling system of 21. 2020 is one of those years, with 30 hurricane occurrences [
39,
40]. Besides the frequency of storms and connected flash flood events, their impact on coastal areas is expected to increase with a rising sea level, regarding damage to critical infrastructure and ecological injuries like salinization [
41,
42]. Anthropogenic interferences can increase local risks if shorelines, river regulations, or extended land use alterations can influence natural floodplains or the nearshore hydrodynamic behavior of waves [
43,
44]. The need for alternative methods is increasing. Utilizing nature-based techniques such as tree belts, mangrove forests, and seaweed can offer protection against high-energy wave events and flash floods. Additionally, these methods can regulate local biodiversity and create habitats for fish, thus maintaining the health of local ecosystems [
17,
45,
46]. In
Figure 5, we can observe how close we are to the ocean and how we deal with coastal events. We also see an upward trend in coastal flooding and a heightened risk of damage in these areas due to population growth, climate change, and the inadequacies of traditional mitigation tactics [
45,
46].
5. Ecosystem and Biodiversity Degradation
Since 1970, humanity’s ecological footprint has been higher than the world’s biocapacity, i.e., more environmental resources and services are in demand that can be regenerated by natural systems [
47]. Coastal ecosystems have endured significant seagrass losses over a prolonged period. The principal causes of these losses encompass eutrophication, turbidity from industrial activities, dredging, catchment run-off, and natural disturbances[
48]. Seagrass loss has been estimated at 12,000 km2 between the mid-1980s and mid-1990s. This loss devastates marine ecosystems, including habitat loss and reduced water quality[
49]. Protecting seagrass ecosystems is crucial. Many replanting restoration programs have been initiated due to the decline of seagrass [
49,
50]. According to traditional restoration principles, it is crucial to carefully choose the location for habitat transplantation and perfect the transplantation methods to reverse habitat degradation effectively [
51,
52]. Thus, they lack recommendations for ecosystem services for native species. New research has highlighted the significance of ecosystem engineering in enhancing seagrass beds. Studies have recommended utilizing native species' ecosystem services to boost efficiency, as described by [
53], [
54], and [
55]. As a result, these findings should be considered a new guideline for future restoration projects [
56]. Other issues related to ecosystems and biodiversity are presented in
Table 1.
6. Coastal Process and Wave Impact
Nearshore water levels exhibit dynamic characteristics, such as wave setup, run-up, and overtopping of sandy beaches and natural or constructed barriers. These characteristics vary based on meteorological conditions like wind, air pressure, sea, and swell. Periodic deformations of the air-sea and internal interface are called waves. Water waves are created when the wind blows over large bodies of open water, transferring energy to the water's surface. The amount of energy transferred from wind to water is significant and increases exponentially with the fourth wind speed power.
Because of a tsunami's long wavelength, which can be hundreds of miles, it is barely noticeable in the deep ocean and is rarely more than three feet (one meter) high; however, when it enters shallow water close to land, most tsunamis slow down. Tsunamis are created by earthquakes and can be shallow or long waves. Tides caused by astronomical forces can take the form of shallow water or long waves. [
78,
79]. Wave energy and dynamic frequency range are presented in
Figure 6.
The coastal process represents the feedback response to energy-driven waves to the shore. Wave setup propagation and run-up contribute to severe wave forces and damage potential along the coast. To promote sustainability in nearshore areas, it is essential to create predictive models to monitor water and sediment-based pollutants in real time. We must enhance our understanding of the physics, chemistry, and biology involved in the nearshore wave dynamics and processes to achieve this. They need to be more resilient coastal communities. We can reap numerous benefits by implementing the best solutions, such as enhanced beach safety, healthier ecosystems, and better mitigation and regulatory policies. [
80] Assessing the long-term evolution of coastal regions is crucial. This involves examining the impact of both natural and manufactured processes, including global climate change, sea level fluctuations, storm patterns, and the rise of coastal urbanization. Enhancing our understanding of long-term morphological, ecological, and societal processes and how they interact is crucial. By utilizing modeling and simulation, we can evaluate the need for improving coastal stability and develop proactive approaches to increase resilience. This will provide better guidance for reducing coastal vulnerability. [
81].
Based on
Figure 5, it is evident that the energy within the wave is contained between the wave's peak and a depth of roughly half the wavelength. Once the water depth reaches half the wavelength, the wave transforms into a shallow-water wave. When the depth of the water decreases, the wave increases in height as its potential energy is converted into kinetic energy, resulting in a breaking wave. The energy of the wave moves, but the water remains in place. As the waves pass, the water particles move in small circular motions. As we go further beneath the wave, the circular motion reduces in size and eventually stops at a depth equivalent to half the wavelength [
82]. Wind waves are waves that travel across the surface of the ocean. As they move, every point on the surface goes up and down in a regular pattern and also moves horizontally. When a progressive wave encounters a barrier, it creates a second wave that moves in the opposite direction with the same amplitude. When two waves come together, they create a standing wave. Tide is standing waves in deep water; they involve oscillatory movement that does not create horizontal displacement [
83].
7. Coastal System Breaking Wave and Impact
The coastal regions are essential to the nation's economic, security, and commercial well-being. Engaging in recreational activities affected by natural and artificial stressors, such as high population density, can increase the risks posed by sea level rise, erosion over time, severe storms, and human influences. [
12,
85]. Wave action in sandy areas or Long Strand can lose up to 10 m of the dune in a single storm and have short-term damage because accretion allows soft sediments to be replenished. Rocky, hard soil areas are subject to long-term effects of coastal erosion [
86].
Figure 7 shows the wave-breaking Iribarren number [
87].
Inshore waves are affected by shoaling and breaking, creating steady and dynamic conditions. Various parameters influence these processes, including the sea's steepness and the bathymetry's slope. To consider all critical factors, a set of graphs was presented by [
87] to identify the most significant and most crucial wave heights (Hmax and Hs) for sloping bathymetries at ratios of 1:10, 1:20, 1:30, and 1:100 [
46]. To calculate the breaker parameter, surf similarity, or Iribarren number, use the formula Jm-1,0 = tanA/(Hm0/Lm-1,0)^(1/2). In the equation, A represents the slope of the structure's front face, and Lm-1,0 is the deep-water wavelength, which can be calculated using the formula gT2m-1,0/2π. The structure slope and wave steepness combination determine the type of wave breaking.
Coastal problems can lead to the disruption of economic activities near the coast, and this includes recreation, commerce, and safety. Over the years, numerous coastal communities have faced challenges coping with natural fluctuations and related risks. The dynamics of waves and wave-driven hydrodynamics on a sloping beach and the response of an erodible bottom to those motions have been defined using the predictive system and physics of the coastal system. Researchers studying coastal areas typically concentrate on fluid dynamics and how sediments respond to natural motions. The critical processes arise from the dynamic energy of waves that move across the beach's profile and topology [
88].
Improving the modeling of nature-based infrastructure involves enhancing process representation, coupling bio-physics models more effectively, integrating data assimilation techniques, and testing real-time models. Recently, we have witnessed failures of cliffs in the North Sea predominantly happening in the winter because the trees cannot withdraw soil water during that season, causing the ground to become wetter. According to the study, there are significant impacts on the environment due to summers that are wetter or drier than average. In 2017, there were 65 incidents recorded despite an increase of 126% in the usual amount of rainfall. During the summer of 2018, a severe drought resulted in only 51% of the average rainfall. As a result, there were only 11 cliff failure events in the subsequent winter [
89].
Figure 8 shows the erosion impact in the South China Sea and North Seas.
8. Hard Coastal Structures vs. Nature-Based Solutions
Hard coastal structures, such as sea dikes and seawalls, build a barrier between sea and land, thus protecting the hinterland against flooding. Hard building materials, such as concrete or stone revetments or grass covers, provide surface protection of the coastal structures against the prevailing hydraulic loads: wave impacts, run-up, overtopping, and currents [
91,
92]. Coastal dunes provide a similar flood protection function but are more prone to the loads from the sea because the building materials (sand, often vegetated) are less erosion resistant. They are regularly nourished before and after storm surges to restore the coastal protection function. Coastal dunes are considered a (managed) natural coastal protection solution. Sea dikes and seawalls are classified as “grey” infrastructure. While incorporating nature-based solutions, grey infrastructure can be ecologically enhanced or integrated into a hybrid system, i.e., a combination of grey and natural structures [
93]. However, there is little experience in establishing and managing coastal ecosystems and uncertainties concerning the constant, long-term coastal protection function, as shown in
Figure 9 [
94,
95].
As waves move closer to the shore and reach shallow water, their wavelength decreases, causing their speed to slow down—however, the wave energy and height increase [
96]. When water particles come into contact with the seabed, friction causes energy loss. When there is a meadow of vegetation close to the surface, it weakens the energy of the waves and causes them to break. In cases where there exist areas of mud accumulation, large quantities of seaweed, clusters of debris, or submerged trees, the resulting disruption of wave motion can lead to turbulence and an energy reduction. Studies have been conducted to determine how effectively coastal vegetation reduces wave intensity. These studies have examined the internal wave attenuation caused by coastal kelp stands [
97], the wave damping resulting from local energy losses due to a cluster of cylinders (which represents a dense stand of giant kelp) [
98], the velocity and turbulence intensity profiles observed in eelgrass beds in a large seawater flume, and water flow in a Spartina maritime salt-marsh in southern Portugal [
99,
100], and researched how to decrease turbulence and reduce the speed of orbiting in a Spartina Anglica salt marsh located in the eastern part of England. [
101] Experiments in the laboratory to measure how synthetic and almost emergent wetland plants affected wave attenuation under various wave conditions and stem densities. A study in a large-scale flume facility investigated the impact of submergence ratio on wave attenuation, transmission, and energy dissipation using a model of seagrass known as
Posidonia Oceanica. [
102]. According to a meta-analysis conducted by [
103], it was found that salt marshes and coral reefs experience an average reduction of 72% and 70% in wave height, respectively. On the other hand, seagrass and mangroves experience an average decrease of 36% and 31% in wave height. The wave-damping capacities of coastal ecosystems depend, amongst others, on the wave conditions (wave height and length) and the ecosystem properties (width, height, and habitat density). Additional analyses for extreme events are necessary to fully consider design cases, as the study only used average values for water depths and wave heights.
Wave damping is highest when the plants occupy the entire water column. Seagrass grows shallow so that the relative height (ratio of vegetation height/water level) is relatively low. It is expected that the wave-damping capacities of seagrass are low during extreme events with increased water levels and high waves. However, seagrass can also affect morphodynamics and thus contributes to coastal protection. Seagrasses increase sediment deposition by flow reduction, trap particles, and stabilize sediments [
104,
105]. The presence of kelp beds can have multiple benefits. They can decrease the strength of longshore currents and wave energy while generating onshore currents that help move sediment toward the shore. [
106].
Figure 10A shows the concept of seaweed and seagrass, and
Figure 9B shows the seaweed bed system for coastal protection.
Sea dikes, seawalls, coastal dunes, and associated coastal protection structures present the main coastal protection structures along the North Sea. With increasing design conditions due to climate change [
107] and the aging of the infrastructure [
108], a continuous costly adaptation of the structures is required. Recently, rising environmental awareness among the population has led to a reassessment of the typical coastal protection approaches towards more nature-based solutions, including hybrid solutions, i.e., a combination of natural and built infrastructure [
93].
Foreshore ecosystems provide ecosystem services with coastal protection functions, such as wave damping [
103], and thus can reduce the wave loads on coastal structures and the maintenance required [
109]. Risk and economic analyses for future climate scenarios reveal the necessity and costs for prospective coastal adaptations at the investigated site. The influence of the foreshore structures on the hydraulic loads at the coastal structure is analyzed, providing innovative design guidance for coastal structures regarding foreshore ecosystem services. Cost-benefit analyses can give important information on the cost-effectiveness of hybrid coastal protection systems and provide a planning tool for design processes.
Climate change calls for sustainable adaptation strategies for coastal protection. Using nature-based solutions presents an innovative measure that integrates the three pillars of sustainability (society, economy, ecology) into coastal engineering [
45]. At this, foreshore ecosystems provide ecosystem services that lead to ecological and socio-economic effects by strengthening existing coastal protection and thus reducing flood risk [
110]. Yet, using foreshore ecosystems for coastal protection is limited to small-scale projects. With the current project, the basics for the design and upscaling of foreshore seagrass, seaweed, and an offshore aquaculture platform shall be obtained to promote the large-scale implementation of nature-based solutions for coastal adaptation with positive effects on the environment and humankind.
The coastal protection function and effects of foreshore seagrass, seaweed, and an offshore aquaculture platform on hydrodynamics and, thus, on the design and maintenance of coastal structures are investigated in physical, numerical, and in situ experiments with natural and artificial structures. The results are the input for elaborating design guidance for hybrid coastal structures. Wave damping capacities of the foreshore ecosystems and the effect on the hydraulic loads at the structure are analyzed and processed to provide planning instructions for engineers. The tasks are completed with standard design manuals [
46] and in consultation with the site authorities to ensure practical handling and implementation.
Figure 10A and
Figure 10B show the concept of coastal protection by integrating hard and soft engineering. Attenuating hydraulic loads on the coastal structure from foreshore ecosystems reduces the stress on the infrastructure and thus reduces maintenance requirements and prolongs lifetime. The effects on maintenance efforts and the structure's lifetime are quantified in cooperation with the accountable site authorities. Furthermore, considering the coastal protection function of the investigated foreshore structures, the costs for future adaptation of the coastal structure are determined and compared to those without ecosystem-based foreshore engineering using cost-benefit analyses. The findings provide a new decision-making tool for planning processes and facilitate the broader use of nature-based solutions under consideration of socio-economic factors.
Coastal engineers are facing new challenges regarding nature-based solutions for coastal protection as design guidance still needs to be provided, and knowledge gaps exist [
95]. The long-term, continuous coastal protection function of ecosystems and the effect on adjacent infrastructure is mainly unexplored. The review provides a new understanding of the interaction of ecosystem engineers, the environment, and coastal structures. It offers coastal engineers’ quantifiable information on the coastal protection services of the investigated foreshore ecosystems as a base for the design process of coastal structures and a decision-making tool for future planning processes.
Seaweed is a water plant with many applications. Growing seaweed can provide a natural way for adaptation that can help curb the increasing sea level rise and associated risk. Another benefit of seaweed aquaculture is its ability to reduce emissions from agriculture. By improving soil quality and minimizing methane emissions from feed, seaweed aquaculture can play a role in mitigating greenhouse gas emissions [
96,
97]). Seaweed farming can aid in adapting to climate change by reducing the energy of waves near shorelines and increasing pH levels and oxygen supply in the surrounding waters. This localized effect can help mitigate the impacts of ocean acidification and deoxygenation. Seaweed aquaculture encounters various challenges, including finding appropriate sites, designing engineering systems that can endure harsh offshore conditions, and dealing with the growing demand for seaweed products in the market [
98,
99]. The ongoing climate change and extensive anthropogenic interferences in the ecosystems of coastal areas will further amplify the risk and damage of high-energy wave events, e.g., due to sea level rise and increased frequency of extreme weather events like cyclones.
9. Result - Hydrodynamic Model Test of Storm Surge Mitigation using Seaweed
Tests are conducted on models to gather important information about a system's behavior. This information determines the hydrodynamic coefficient that will be used in designing a functional system. The model test is conducted at the IWW Flume lab to examine the damping effect of seaweed. Samples of seaweed obtained from the North Sea (
Figure 11) are attached to the flume, and the fluid pump at different speeds is imposed on the model.
The hydrodynamic force exerted on the seaweed is defined as the sum of drag and inertia forces and can be described by the Morison equation.
Where variable ‘F’ represents the overall force on the vegetation, C
D is the drag coefficient, ρ is the water density, A
v is the area of the vegetation that is normal to the streamwise flow direction, u is the flow velocity, C
M is the inertia coefficient, and V
v is the volume of the vegetation element. The first part of the equation refers to the drag force; the second part describes the inertia force. Usually, the second part, inertia force, is generally smaller than the drag force and is, therefore, often neglected in studies.
Figure 11.
Experimental setup for wave mitigation at IWW; RWTH Aachen, IWW Lab (A) Hydrodynamic experiment (11B) Experiment setup.
Figure 11.
Experimental setup for wave mitigation at IWW; RWTH Aachen, IWW Lab (A) Hydrodynamic experiment (11B) Experiment setup.
Figure 12 shows a sample of seaweed used for the investigation. The seaweed model imitates the Froude-scaled properties indicated by the number (Fr).
Where v is the velocity [m/s], g is the gravitational acceleration [m/s
2], and l is the length [m]. Models scaled with Froude scaling law keep inertial and gravity forces similar.
Figure 12.
Clumps of wet seaweed species from the North Sea species (a: Ascophyllum nodosum, b: Codium fragile).
Figure 12.
Clumps of wet seaweed species from the North Sea species (a: Ascophyllum nodosum, b: Codium fragile).
Figure 13 shows the experiment finding involving a model of 2 lines of seaweed plantation. Local operating environment based on the North Sea site conditions that consider Metaocean and hydrodynamic interaction of the sites. Metaocean data include historical data (tidal elevation, velocity, velocity, current speed, current direction, temperature, and salinity).
Figure 14 shows the equivalent sensitivity force ratio.