Introduction

Major coastal erosion represents a management challenge for engineers and interested authorities. The understanding of the mechanisms regulating the erosion advancement and its causes are essential to predicting future development and adequate mitigation measures to protect both nature and private properties, and to deciding on the right investment for the purpose. In broad terms, coastal erosion is the consequence of a combination of two forms of erosion: chronic and acute erosion. Chronic erosion occurs on a regular basis and is the result of waves lifting the sediment and a long-shore current (also generated by the angle of attack of the waves) carrying it away. Summer and winter beach profiles may vary significantly, as we may assist to deposition in summer and erosion in winter, but when the net removal exceeds the net deposition for a long period of time, a beach is said to suffer from chronic erosion. Acute erosion usually happens during storms and generates a sediment transport from the inner to the outer profile. In this situation, the combination of wind, water level and waves drags the material from onshore to offshore. The amount of material is determined, among other things, by wave height, direction and grain size. Other factors can influence the rate of erosion: hard (passive) protection measures such as groins, seawalls, breakwaters transfer the erosion to neighbouring stretches by interfering with the longshore current; increase in storm events such as in connection to climate change anomalies may also increase erosion by changing the wave attack angle to the coast or simply by providing more energy to the sediment transport.

The main objective of this work is to identify the main parameters affecting the erosion at Nørlev Strand on the Danish west coast. To do so, we use two complementary approaches: a historical analysis of wave heights, periods and directions and a comparison with profiles of erosion. The quantification of the erosion is based on numerical simulation at varying parameters and the identification of the most influencing parameter at our location. Finally, by using the long-time records (1981–2011) of storm events and climate change effects in Denmark obtained from the DHI (Danish Hydraulic Institute) records, we make some additional considerations on the costal erosion that may introduce a new parameter to be considered in future studies.

Area of study

Nørlev Strand is a 2.5 km coastal stretch occupied by summer cottages. It is located at the north-west coast of Denmark, bordering on the North Sea (Fig. 1).

Fig. 1
figure 1

Nørlev Strand is located north-west from the city of Hjørring and south-west from the port of Hirtshals. Nørlev Strand is part of the Danish north-west coast

Nørlev Strand is a barred-beach with sandy dunes of heights varying between 6 m and 12 m. While the beach is normally steeper towards the south, the shore face is steeper towards the north. The general trend is for the coastal transects to become steeper with time, and for the dunes to reduce in height. The theoretical depth of closure is estimated to be between 6.2 m for summer events and 8 m for winter events (Baptista et al. 2014) (Dean 2003). Despite this, beach profiles show large temporal variation passed the depth of closure. Dunes and beach fronts are composed mainly by non-cohesive materials such as gravel and sand, deposited during the Yoldia Sea period. Both materials are unconsolidated, thus becoming a material easily erodible. Most of the area is covered by a layer of aeolian sand, which is also easily transported by the wind (GEUS 2017). According to Saye and Pye 2006, the mean sediment size, D50, of the sand in the area is 0.233 mm. There are recordings of intense erosive activity at Nørlev Strand. In December 2015 a powerful storm lead to the destruction of several summer houses located in Morgenvej street. Before this storm, no nourishments had been performed and no hard structures had been installed at Nørlev Strand. However, there are four groins south from the beach of the beach, at Skallerup Klit. Those were built in 1981 to protect the drainage system of the Skallerup Resort. This drainage system is no longer in use, but the groins were never removed. Since there is a consistent northward current along the north coast, it is downstream of the groins where the largest erosion can be found at Nørlev Strand. It is also at this location where Morgenvej is situated. The landowner’s response to the 2015 storm was to point at the groins built upstream of Nørlev Strand as being allegedly increasing chronic erosion and, therefore, leaving the houses further exposed during storms (Fig. 2).

Fig. 2
figure 2

Nørlev Strand. 2nd September 2016. Left: houses in Morgenvej. The dune in front of the houses was nourished after 2015 storm. Right: panoramic view of Nørlev Strand

In Fig. 3, it is marked the location of Morgenvej. Cottages originally built far from the beach are now located atop of the dunes due to progressive erosion. The stretch is being monitored with four profiles spaced 1 km from each other. Profiles 1650 and 1640 enclose Morgenvej. Comparing the evolution of these profiles with transects 1630 and 1620 gives an idea of the rapid evolution of the coastal retreat in front of Morgenvej. In Fig. 4, we have the available profile envelopes at Nørlev Strand for the four transects, from 1973 to 2016. There is retreat along the entire coastal stretch. This is quantified by obtaining the position of the coastal profiles at three heights: 0 m height (coastline), 1 m height and 4 m height (see also Fig. 10, “Climate Change” section).

Fig. 3
figure 3

Transects in Nørlev Strand and location of Morgenvej. The profile number increases from north to south; 1650 being the closest profile to the groins of Skallerup Resort

Fig. 4
figure 4

Profile envelopes in Nørlev Strand. Top left: profile 1620. Top right: profile 1630. Bottom left: profile 1640. Bottom right: profile 1650

From 1973 to 2016, profiles 1620 and 1630 have retreated at an average rate of 0.7 m/year and 0.6 m/year, respectively. The largest retreat rates per year are found at 1 m height in between 1985 and 1987, which equals −10.2 m/year in profile 1620 and − 12.3 m/year, in profile 1630. At the coastline, the largest retreat was found in the period 1991 to 1993, when profile 1620 retreated at an annual rate of 9.7 m/year and between 2000 and 2003 when profile 1630 retreated at an annual rate of 6.0 m/year at the coastline.

From 1973 to 2006, profile 1640 erodes at a rate of about 1.9 m per year. In the period 1983 to 1985, it happened the largest retreat at the coastline which was 15.9 m/year. At 1 m height, the largest retreat is found between 1977 and 1978 which equals to −11 m/year. At 4 m height, the largest annual retreat happened between 2012 and 2016, equalling 7.5 m/year.

The erosion rate of profile 1650 from 1973 to 2016 has been 3.4 m/year, being the largest of the stretch. It is well-known that the lee side erosion appears downstream of groins. However, at the coastline, the annual erosion rate of profile 1650 has been largest between 1991 and 1993 reaching −15.7 m/year. Between 1977 and 1978, at a height of 1 m, the profile retreated 14.7 m. From 1991 to 1993, the profile at a height of 4 m retreats at 11.1 m/year. If the total retreat from 1973 to 2016 is regarded, profile 1630 erodes the least: only 27 m. It is followed by profile 1620, with a total retreat of 30 m. Profile 1640 erodes 81 m.

Finally, profile 1650 retreats 147 m., clearly being the less resilient part of the coastal stretch. Profiles 1620 and 1630 display the largest annual erosion rates between 2000 and 2008. Profile 1640 worsens gradually in time; the worst period being 2008 to 2016. At last, profile 1650, closer to the groins, suffers the largest erosion rates 10 years after the groins placement, from 1991 to 2000.

Figure 5 shows the wave roses of summer and winter. Besides the predominant western direction, the other two wave directions stand out. Sector [250° - 295°] agglutinates more than 60% of the incoming waves. Almost another 15% of the incoming waves are represented in sector [340° - 25°]. Finally, 10% of the waves come from the sector [25° - 70°]. Nevertheless, this third group is not relevant at Nørlev Strand. Due to its relative position in relation to Hirtshals port, the beach is sheltered from north-east waves. The average significant wave height is 1.14 m, the modal wave direction is 272° and the average peak period is 6.21 s. The standard deviation of the average peak period is small, 2.24 s, which suggests small variability during the analysis period. Indeed, most of the waves come from the west where the fetches are the largest, pointing to a large predominance of swell waves. On the other hand, the standard deviation of the average significant wave height is quite large in comparison, 0.76 m.

Fig. 5
figure 5

Wave roses from the buoy 10,411 located in Hirtshals area. The wave roses contain data for the period August 1999 to August 2012. Left: Hm0 summer. Right: Hm0 winter

Methodology

The study is divided in two parts:

  1. 1.

    One part uses the historical wind and wave data and profile measurements in order to relate measured erosion to significant events.

  2. 2.

    The second part uses a numerical model to quantify the erosion when varying the significant parameters affecting it.

For both parts, the following subsections explains in detail the data and relative analysis..

Data

Wave data is obtained from buoy 1041 located in the western offshore waters of Hirtshals port. It is located at 26 km west from Nørlev Strand, and at 17.5 m depth it is the closest source of data in the area. The UTM coordinates of the buoy are [536,702, 6,374,866]. It contains data from August 1999 to August 2012, but only 11 years of data are fully recorded. The study period is established based on this data. The measurements from the buoy are not directly manipulated, and the 3-h average of the different wave parameters are calculated. The used parameters are significant wave height, Hm0, peak wave period Tp and mean wave direction, θm. The wave data needs to be treated for outliers and missing values. Additionally, another set of data is used, which corresponds to a wave buoy located closer to Hirtshals port, buoy 1012. It contains data from before February 1996 to today. This buoy is about 15 km north from Nørlev Strand. About a 26% of the data is missing from buoy 1041. Data from buoy 1012 is used to complete data gaps in wave heights and to obtain a series from January 1999 to December 2012. Hm0 is well correlated, Tp is poorly correlated due to a failure in buoy 1041 and θm cannot be compared since 1012 contains non-directional data. The linear correlation factor for Hm0 between both buoys is 0.94, and there is a proportionality factor of 0.79, which is used in the completion of data. After data completion, the missing data of Hm0 is reduced to 3% of the total data.

The most uncut parameters are Hmax, Tp and Tz. To derive Hm0 from HMAX it is used the derived expression (Liu and Frigaard 1999):

$$ {H}_{m0}=1.07\bullet 1.94\ {H}_{MAX} $$
(3.1)

In the same line, according to Badulin 2014, Ta, the mean over spectrum period defined by Hwang et al. 1998 is equivalent to the Tz. Moreover, Badulin 2014 states that all periods are related by a certain coefficient. In the case of TP and Tz, the relation according to Hwang et al. 19987 is

$$ \frac{T_P}{T_Z}=1.29\pm 0.14 $$
(3.2)

The following filters are applied to the data:

  • The data is first checked for negative wave height and period values, and for too high or too small period values. Wind generated waves, as these, have wave periods in between 1 s and 30 s, Andersen 2016.

  • Where possible, wave height and wave period relations are used to check the existence of outliers.

  • Measured waves are stable; in other words, they are not breaking either by depth, neither by steepness. Under storm, waves with steepness, H/L, larger than 1/10 are hardly ever found. Waves also become unstable when the relation HS/h ≤ 1/10 is met, Andersen et al. 2014

No continuous water level measurements of the necessary resolution are available around Nørlev Strand; therefore, the water level will not be analysed thoroughly during the study period. Tide data, instead, is obtained from the Danish Meteorological Institute (DMI). The data is recorded at Hirtshals port. According to the 2017 tide tables from the DMI, the maximum spring tide has a magnitude of 0.4 m while the minimum spring tide has a magnitude of −0.4 m. Regarding current data, there has not been any measurements in the area for more than 20 years. Thus, it is not considered in this study. Wind speed and direction are measured at Hirtshals port, with UTM coordinates [557,550, 6,383,950], from February 1996 until December 2017. Wind data is used to understand climate variability in the area. Finally, profile measurements are collected every two to 4 years using total station, GPS and echo sound technology. Data under water is taken approximately every 2 m, while data measured over water is taken according to the morphology. The transect data is interpolated using a linear function to obtain equally spaced data points.

Evaluation of the average wave climate

The different wave parameters change both temporally and spatially, i.e. in the different seasons and depending on the geography. With the purpose of dealing with homogeneous events in the description of the average climate, wave records are first divided into eight groups based on their direction, to account for the geographic variability, and subsequently divided in winter and summer events. Based on the oceanographic definition of winter and summer, winter ranges from October to March, while summer ranges from April to September. This division was also done by Li et al. 2014. This division is made for wave height, wave period and, subsequently, wave direction.

The average value of wave height and period is calculated for each direction and for winter and summer. Since waves coming from the north and the west account for 75% of the incoming waves, the average wave climate depiction is based mostly on these two groups of data. In the case of the direction, the mean value is not calculated, but the mode. Variations of the mode of every direction sector are analysed.

Incident wave height – Significant events

Climate change may be responsible for increase in numbers and intensity of storm events as discussed in Graeme 2011 and as warned by the Intergovernmental Panel on Climate Change (IPCC). The incidence of medium to large wave height and wind events is analysed. These events, from now on referred to as significant events, are defined as those independent events that exceed a certain threshold, and they are obtained by using the principles of extreme value analysis (Morton and Bowers 1996).

In the case of wave heights, the threshold is established as the125% of the average significant wave height calculated from the wave time-series. This value is 1.43 m. Regarding the independence criterion, two events are independent if there are at least 24 h between them. If there are less than 24 h between two wave heights that surpass the threshold, they belong to the same cluster of data (pp. 42–43, Liu and Frigaard 1999). A similar criterion is applied to wind; however, the threshold is selected as the 155% of the average wind speed calculated from the wave time-series. This is done to obtain several events of the same order as the number of wave events. The threshold value is 11.4 m/s.

Numerical simulations

To assess the effects of the above-mentioned parameters on the erosion, a numerical model is used. By running the model, it is possible to determine which parameter has larger influence on the alongshore sediment transport of Nørlev Strand. A value of reference is taken for each parameter, and the model is run with it. This value of reference is, in principle, the actual quantity which can be found at Nørlev Strand. From this simulation, a reference net sediment transport for that parameter is obtained. Consecutively, the model is run again with the reference value varied in a fix magnitude, and a new figure of the sediment transport is obtained. The used increments are ±10%, ±25%, ±50%, ±75% and + 100%. −100% is not considered, as it implies the input parameters is 0 which in most cases makes no physical sense or creates model instabilities. In the case where wave direction is tested, making percentage increments does not suit the study; thus, the model is run for directions every 15°. It is important to note that only the parameter under analysis varies, while the rest remain constant.

Numerical modelling is used to analyse how the variation of simple hydrodynamic and morphological parameters affects alongshore transport at Nørlev Strand. Changes in flux patterns can be linked to changes in the erosive or sedimentary potential in the coast (Silva et al. 2016) (Davidson-Arnott and Pollard 1980). The technical information about the numerical model used in this section is based on the user manual of Littoral Processes FM, from the Danish Hydraulic Institute, DHI 2016. The parameters investigated have mean grain size, water level, wave height, wave period, duration of the wave event, bed roughness and wave direction. According to the recommendations of the user manual, the latter parameter is tested in the model by keeping a constant wave direction input and varying the coastline alignment.

Littoral Processes FM is a 1D model that simulates alongshore transport. The tool agglutinates four different numerical models: transport in a point, littoral drift, table generation and coastal evolution. For this study will only use littoral drift. It consists of two main operations. First, it solves the hydrodynamic equations, including wave propagation towards the coast, shoaling and breaking and calculation of driven forces. These forces come from the radiation stress gradient and the momentum balance equation in the cross- and longshore direction. Second, it calculates the sediment transport from the generated hydrodynamic conditions and the sediment characteristics. The following assumptions are made:

  • Sediments are purely granular and non-cohesive.

  • Morphological changes in the cross-shore directions are negligible.

  • Bathymetry contours are quasi-parallel to the coastline and the profiles are perpendicular to them.

  • The predominant current direction is longshore.

Hydrodynamic inputs

The inputs are root mean square wave height, Hrms, zero up-crossing wave period, Tz, mean wave direction, θm, spreading factor, wave duration in percentage of the year, water level and currents. The spreading factor is set as the default value, 0.5. Hrms, and Tz are calculated from Hm0 and Tp respectively. The relation between Tp and Tz was enunciated in Eq. (3.2). Hrms is obtained from Hm0 using (Liu and Frigaard 1999):

$$ {\displaystyle \begin{array}{c}{H}_{rms}=1.13\ \overline{H}\\ {}{H}_S=1.6\ \overline{H}\\ {}{H}_{m0}=1.07\bullet {H}_S\end{array}} $$
(3.3)

These variables can be set as constants during the simulation or as variables. In this study, the variables are set as constant, using bulk statistics calculated in the wave climate analysis. Since there is neither water level nor current data, in the case of the water level it is only the tidal variation that is considered as model input; as for the currents, the model calculates wave generated currents. The model uses the Rayleigh spectral description for individual wave heights (user decision). Rayleigh is a conservative formulation since it does not take into consideration wave breaking due to limited water depth (Liu and Frigaard 1999). Therefore, the waves that propagate towards the coast are larger.

Morphological input

The bathymetry of the coastal stretch is described in the model by using only cross-shore profile data. Since the model does not consider morphological changes when calculating sediment transport, the input is simplified to only one cross-shore profile. The actual sediment transport at Nørlev Strand is not sought for, and by having a uniform description of the coastal stretch, computational time is reduced, and the focus of the investigation remains on the variation of the aforementioned parameters. Other morphological inputs include critical Shield’s parameter, Nikuradse bed roughness and fall velocity.

The critical Shields parameter θc depends on the sediment fluid parameter:

$$ {S}_w=\frac{D_{50}\sqrt{\left(s-1\right)\bullet g\bullet {D}_{50}}}{4\nu } $$
(3.4)

Having determined a value of the sediment fluid parameter, θc can be read from the Shields diagram. The value obtained of the critical Shields parameter is very close to the default value (0.0045), which the user manual recommends using.

The formulation used to calculate the Nikuradse bed roughness is based on Liu 1999. Bed roughness is defined as the interval:

$$ {H}_r\le \kappa \le 4\bullet {H}_r $$
(3.5)

which depends on the ripple steepness Hr:

$$ \frac{H_r}{L_r}=0.182-0.24\bullet {\left(\theta \prime \right)}^{\raisebox{1ex}{$3$}\!\left/ \!\raisebox{-1ex}{$2$}\right.} $$
(3.6)

where θ’ is the effective Shields parameter calculated in Eq. (A.1), and Lr is the ripple length.

$$ {L}_r=2\bullet A $$
(3.7)

Due to lack of data to define the grading coefficient according to the specifications of the software, the sand is assumed uniform. For uniform sand it is required to input fall velocity. According to Ahrens 2000, the following formulations lead us to a determination of the fall velocity with a small error. First, the fall velocity is defined as:

$$ \omega =\frac{C_1\bullet \varDelta \bullet g\bullet {d}^2}{\nu }+{C}_t\sqrt{\varDelta \bullet g\bullet d} $$
(3.8)

where A is the Archimedes buoyancy index, and d is the characteristic diameter, in this case taken as D50. The Archimedes buoyancy is defined as:

$$ A=\frac{\Delta \bullet g\bullet {d}^3}{\nu^2} $$
(3.9)

Finally, the coefficients C1 and Ct are:

$$ {\displaystyle \begin{array}{l}{C}_1=0.055\ \mathit{\tanh}\left(12{A}^{-0.59}\bullet {e}^{-0.0004\bullet A}\right)\\ {}{C}_t=1.06\ \mathit{\tanh}\left(0.016\bullet {A}^{0.5}\right)\end{array}} $$
(3.10)

Appendix A.1 contains the equations used to obtain the effective Shield’s parameter, which is used to calculate the Nikuradse rough parameter.

Analysis

This session presents the results of the analysis of the historical wind and wave data. Besides the study of wave heights, periods and directionality, we include considerations of climate change, particularly discussing the increase in the number of significant wave events from 1999 to 2011, but also by looking at national storm records from 1981 to 2011.

Wave height

The first characteristic analysed is the evolution of the annual average significant wave height, Hm0. Figure 6 is divided in two plots. The top plot contains the evolution in time of Hm0 for waves coming from directions 250° to 295°, while the bottom plot contains waves coming from directions 340° to 25°. There is a relatively constant trend for the wave heights in both plots. Westerly waves vary around 1.3 m, while northerly waves vary around 1.1 m. For westerly waves, the dispersion is also smaller than for northerly waves. The largest waves come generally from the west, with some exceptions, like the winters 2005 and 2010, and the summers 1999, 2001, 2008 and 2010. These larger events linked to a direction, other than the principal one, could be related to erosive processes. Since the coastline form is adapted to the principal direction, waves with a different angle of incidence arrive with a more oblique angle which induces longshore transport. Finally, the largest average winter and summer Hm0 are registered from 1999 to 2001, while the milder years are 2002 and 2012.

Fig. 6
figure 6

Annual values of mean Hm0 divided into winter (blue cross), summer (yellow triangle) and all data events (red circle). Top: sector [250°-295°]. Bottom: sector [340°-25°]

Wave period

Waves coming from the west have larger periods than waves coming from the north, see Fig. 7. This is in line with the fact that the largest fetches are found in the sector [250°-295°]. Larger fetch leads to loss of energy and elongation of the wave period. Waves coming from the north are more locally generated, and their periods are generally shorter. In the relation winter-summer, winter waves present larger periods than summer waves. In 2010, the largest average period from northerly waves was measured, while in 1999 the largest one for westerly waves was measured. The shortest average period was registered in 2002 for northerly waves, and in 2012 for westerly waves.

Fig. 7
figure 7

Annual values of mean Tp divided into winter, summer and all data events. Top: sector [250°-295°]. Bottom: sector [340°-25°]

Wave direction

To characterize wave directions, mode per sector is used instead of the average, see Fig. 8. The mode in the sector [250°-295°] is very stable around 270°. However, there is a shift in the mode of winter waves from 1999 to 2001. Regarding sector [340°-25°], most of the waves concentrate in between 0° and 25°, with a large dispersion within. It seems that both summer and winter modes tend to shift from 20° to 5° during the study period. In 2001 in both sectors, there is a large shift in the mode of the wave direction from summer to winter. This shift is of about 25° in the west sector and 15° in the north sector.

Fig. 8
figure 8

Annual mode of mean wave direction separated in winter and summer event. Top: sector [250°-295°]. Bottom: sector [340°-25°]

Frequency of significant events

The number of significant wave height events (as defined in “Methodology” section) seems to increase continually from 1999 to 2012 in Hirtshals, while the significant wind events decrease. As there is a very strong correlation between wind and waves, the difference between the two trends can only be explained (minus errors) by the directionality. While the number of significant events for wind speeds did not increase when looking at all wind directions, the number of significant events with wind directions affecting the formation of the waves reaching the coast has increased, generating a rise in significant wave events shown in Fig. 9.

Fig. 9
figure 9

Left: frequency of wave height exceedance in Hirtshals. Right: frequency of wind speed exceedance in Hirtshals

It is not in the scope of this paper to find the increase in the number of significant events, but to find out whether there is a tendency which could explain the increasing erosion experienced at Nørlev Strand.

Climate change

The Danish Meteorological Institute, DMI, released a report in 2012 that included a list of storm events in Denmark since 1891. Here, storm events are classified in four classes based on wind speeds (class I: 17–21 m/s, class II: 21–24.5 m/s, class III: 24.5–26.5 m/s and class IV: above 26.5 m/s). We have here transposed the storm data into a diagram in order to give an overview on the historical situation in Denmark. An average over the storm classes for each year is made and the duration reflects only the number of days reported for the same storm condition (low accuracy in terms of hours of duration). We have then added the average coastal retreat obtained as an average of the three values at three heights: 0 m height (coastline), 1 m height and 4 m height as presented in “Area of study” section (Fig. 10).

Fig. 10
figure 10

Average over storm classes for each year. The duration (top, in blue) reflects only the number of days reported for the same storm condition. (top, orange: intensity). For the early 1970s, we present the evolution of the average annual erosion for the four profiles considered in “Area of study” section

We can see a good correlation between storm events and coastal retreat, with no erosion present between 1995 and 1999 as consequence of a lack of storm events.

In the same report, climate variations are reported in terms of temperature, accumulated precipitation and cloud cover. While it seems that climate change has not significantly affected the number of storm events or their intensity over the past 120 years, if we consider that our data at location runs from the early 1970s to the present, we may see an increase in duration and number of events today compared to the early records at Nørlev Strand. We do not here consider increase in duration and number of events as effect of climate change; however, the accumulated precipitation does seem to be increasing instead (Fig. 11). Given the geological and morphological characteristics of the coast, heavier rain fall may increase water table elevation at the foreshore and decrease the cohesion of the sand in cliff and facilitate landslides and erosion. This possibility was first investigated by Bryant 1985 and backed up more recently in Jenkins et al. 2008. Because of the geology of the Danish west coast – dominated by different types of sands – this hypothesis may play an important role, and there should be consideration on implementations into prediction models that take precipitation into account in the erosion evolution.

Fig. 11
figure 11

Annual accumulated precipitation in Denmark from 1874 to 2011. Source: DMI

Results

Based on the described methodology, the results from the numerical model for a specific parameter are presented as the curve of the variation of sediment transport with the specific parameter. A zero in the curve indicates no variation with respect to the reference value. If the net sediment transport becomes −100%, this should be understood as no net sediment transport being generated. A negative increment below −100% represents sediment transport in the opposite direction.

Mean grain size and fall velocity

The reference mean grain size, D50, is 0.233 mm, which is that of Nørlev Strand. Since the fall velocity is dependent on the mean grain size, they are considered together (Eq. 3.8) (Fig. 12). With very small grain sizes, the waves wash away all sediments. This can be seen in the left part of the plot where the curve tends to infinity. Continuing the curve development, there is a critical part in which, with increasing grain size, the sediment transport decreases until a minimum. This minimum corresponds to 25% larger than the reference D50. After this point, it increases again and becomes quite stable, showing minimal growth rate. This could be caused by the increment in bed friction due to a larger grain size, which leads to more wave breaking. D50 has a major influence in the configuration of the beach that cannot be estimated with these numerical simulations. First, the beach profile shape is very sensitive to D50; a larger sediment grain size results in a steeper profile (see Eq. 4.1, Dean 2003). This is well-known in beach nourishment practice, where it is common to use a slightly larger mean grain size to achieve smaller refill volumes.

$$ {\displaystyle \begin{array}{l}h(y)=A\bullet {y}^{\raisebox{1ex}{$2$}\!\left/ \!\raisebox{-1ex}{$3$}\right.}\\ {}A=0.067\bullet {\omega}^{0.44}\end{array}} $$
(4.1)

where h is the water depth at a distance y from the shoreline, both in in m; A is the profile scale parameter in m1/3, and ω is the fall velocity in cm/s. Equation 4.1 is the beach equilibrium profile, which depends on the mean grain size through the fall velocity. According to this equation, the larger the mean grain size, the larger the water depth in the profile equilibrium. Subsequently, the effect of water depth change must be added to the effect of the grain size variation.

Fig. 12
figure 12

Increment of net sediment transport in relation to mean grain size

Second, the type of wave breaking depends on the beach slope (see Eq. 4.2, USACE 2002), which becomes steeper with larger mean grain size and milder with smaller grain mean size.

$$ {\xi}_0= tan\beta {\left(\frac{H_0}{L_0}\right)}^{\raisebox{1ex}{$-1$}\!\left/ \!\raisebox{-1ex}{$2$}\right.} $$
(4.2)

where β is beach slope, H0 and L0 are wave height and wave length in deep water, and ξ0 is known as the Iribarren number, or surf similarity parameter. It predicts the way that waves break. The steeper the beach, the larger ξ0, and the more turbulent the breaking becomes (USACE 2002). Turbulent breaking implies more stirring, and more sediment in suspension, which increases potential transport, see Fig. 13.

Fig. 13
figure 13

Relation between water depth at 10 m distance from the shoreline and grain sediment size

For the sake of simplicity, it is assumed that the distribution of the particle is uniform in the cross-shore profile. This is not necessarily true. In fact, there is a tendency for the particles to be sorted by size across the profile, both spatially and temporarily (Medina et al. 1994). Typically, the coarser grain particles are located in the breaker zone, while the finest particles can be found towards both offshore and onshore, depending on the energy dissipated (Wang et al. 1998). As there is no available data to characterize sorting, the mean grain size distribution at Nørlev Strand is assumed uniform.

The effects of the main grain size variation on the sediment transport cannot be properly quantified, but Fig. 13 gives an idea of what to expect if nourishment projects are carried out in the area.

Water level variation

The relation between the water level variation and the net sediment transport is not linear, but they are proportional (Fig. 14). The smaller the water level variation considered, the smaller the sediment transport obtained. The reference value is taken as the spring tide 0.40 m.

Fig. 14
figure 14

Increment net sediment transport with respect to water level

The curve displayed in Fig. 14 is, unfortunately, showing odd results, which can be due to set up errors. It is expected that larger water levels lead to larger sediment transport without the presence of breaks in the curve. The plot is expected to have a parabolic shape, with the same gradient it shows currently.

A higher water level allows for larger wave heights to approach the coast. The water depth increases, and waves that would usually break offshore will move forward onshore. The waterline reaches a higher point, potentially generating erosion at the dune foot.

Wave height

The net sediment transport is very sensitive to the wave height, see Fig. 15. As seen from the CERC formula (Eq. 4.3), the term correspondent to the breaking wave height is to the power of 2.5

$$ Q=\frac{5}{8}\frac{H_b^{\raisebox{1ex}{$3$}\!\left/ \!\raisebox{-1ex}{$2$}\right.}\sqrt{\frac{g}{k}}}{\left(1-p\right)\bullet \left(s-1\right)}\bullet \frac{\mathit{\sin}\left(2\bullet \left(\beta -{\alpha}_b\right)\right)}{2} $$
(4.3)
Fig. 15
figure 15

Increment of net sediment transport with respect to the significant wave height

In Fig. 10, the relation in between H and the net sediment transport has an exponential tendency. The reference wave height is 1.4 m. The highest transport is obtained by doubling the wave height. Doubling the wave height has implied quadruplicating the net sediment transport.

The wave height is the main variable when referring to the energy content of the waves, and at the same time, in the simulations the main input source are the waves. The total energy density per unit area of the water waves is defined as (Andersen et al. 2014):

$$ E=\frac{1}{8}\bullet \rho \bullet g\bullet {H}^2 $$
(4.4)

where, again, the wave height term appears to the power of 2.

Wave period

According to the results of the sensitivity analysis (Fig. 16), in principle the net sediment transport increases with increasing wave period. Van Gent et al. 2008 have also shown this effect. The reference peak period is 4.7 s. This relation is not completely clear, and Fig. 16 shows some odd behaviour for small periods. With substantial periods, the waves will become more stable and their Iribarren number will also decrease. Consequently, breaking is less turbulent, reducing the erosive tendency.

Fig. 16
figure 16

Increment of net sediment transport vs the wave peak period

Event duration

The event duration is linearly proportional with the net sediment transport. The larger the event, the larger the energy associated to it, and therefore the transport, see Fig. 17.

Fig. 17
figure 17

Increment of net sediment transport with respect to the event duration

Bed roughness

The values of the bed roughness are previously calculated using theoretical formulations. From this calculation, a range of possible values are obtained, going from 0.0087 until 0.0869. These are obtained by using wave heights of the average wave climate. As seen in Fig. 18, bed roughness and sediment transport are inversely proportional. The larger the bed roughness, the larger the friction with the bottom and the more wave energy is dissipated.

Fig. 18
figure 18

Increment of net sediment transport with respect to bed roughness

Coastline alignment

In this simulation, the waves always come from a constant direction, and it is the coastline that changes its angle. Testing coastline alignment variation is, in turn, the way of testing the impact of wave direction in the sediment transport in this numerical model. Directions are tested every 15°, including 310°, which is the reference value. The reference wave forms an angle of 275° with respect to the true north. This means that the angle of incidence of an average wave is 35°.

A net sediment transport of −200% means that a certain coastline alignment has led to a value of net sediment transport of equal magnitude as the original, but with an opposite direction. This is the only case where this behaviour is displayed, see Fig. 19. The maximum of the net transport is found when the normal vector to the coastline forms an angle of 235° with true north, and it is a southern directed transport. This is opposite to the predominant transport direction. In that case, the coastline alignment forms approximately 40° with the reference wave direction.

Fig. 19
figure 19

Variation of the sediment transport in relation to the coastline alignment

When the waves from both north and west affect the coast during the same period, there is gross transport flowing both towards the north and the south. Consequently, the net sediment transport is reduced during those periods. This could be the case in years when the average wave height from northerly waves increased.

When the normal to the coastline alignment forms in between 190° and 85°, the wave input in the model comes “from land”. Therefore, the sediment transport is zero. When the angle is smaller than 85°, and until it reaches 0°, only fractions of the waves coming from the north have an effect on the coast, and therefore, there is small transport. This transport tends to be zero when the coastline becomes perpendicular to northerly waves.

The maxima for northerly directed transport is achieved with a coastline alignment of 325°, which means that the angle of incidence of the test wave is 55°. It is expected that a larger transport would have been achieved by testing a coastline alignment of 320°.

To conclude, it can be expected that shifts in the mean wave direction, particularly towards south, enhance the magnitude of the net sediment transport and the erosive potential.

Conclusions

At Nørlev Strand, as the morphology of the coast is experiencing irreversible changes, intensification of climatic events is translated into greater risk of damage of the properties in the coast. In terms of engineering protection works, the construction of revetments, for example, can protect the houses from the effects of the storms, but it does not prevent the relapse of the coastline, which means that without a constant campaign of beach nourishments, the revetment toe will eventually erode and fail.

This study has looked into the influence of different parameters on the costal erosion in Nørlev Strand.

We conclude that some parameters are, at present, contributing to the erosion; others have a potential influence, no influence or unknown influence. As the erosion in Nørlev is a superimposition of different factors, we tried to quantify the influence of each one of them with numerical simulations.

  • The first most important parameter influencing erosion is, not surprisingly, the wave height.

The data analysis at the location for the past 70 years did not reveal an overall increase in wave heights, but there was a constant increase in frequency of significant events recorded. Winter events are 1 m to 1.5 m larger than summer events, and therefore winter events are more relevant in the quantification of sediment transport. Therefore, this parameter is currently increasing erosion at the location. Additionally, the numerical analysis showed that an increase in wave height of 25% would increase the sediment transport of 80% approximately, following an exponential trend. This implies that if wave heights increase (increased storminess events combined with higher water levels), the significant wave height will increase at location in the next years, and so will the erosion induced by wave height with the trend showed in this study.

  • The second most important parameter affecting the costal erosion is the wave period, presenting an almost linear trend with the increment in sediment transport.

The study shows that an increase in peak period of 25% generates an increase in sediment transport of 18% at location. No clear trend has been found in the peak period variations during the past 70 years, i.e. no change from the past; this parameter has the potential to further influence erosion at the location.

  • The influence of the wave attack angle was studied numerically with the variation of coast alignment. The sector [250°-295°] is stable around 270°, while within sector [340°-25°] most of the waves concentrate in between 0° and 25°, with a large dispersion within and both summer and winter modes tend to shift from 20° to 5° during the studied period.

A shift towards north, as it was measured based on wave records, implies a larger relative angle in between coastline and mean wave direction, and therefore a smaller transport. Thus, this shift in direction attenuates the sediment transport so the wave attack angle currently mitigates erosion effects at Nørlev Strand.

  • Increasing depths in the offshore contours of the beach allows for larger wave heights to approximate the coastline.

It is estimated that for an increment of water level of 25% we have an increase of sediment transport of circa 2–3%. This, added to an increasing trend in the sea level rise, would lead to more pronounced and more frequent wave attacks to the beach dunes and to the houses protected by those dunes. The increasing depth has a potential to worsen costal erosion at the location with the trends presented in this study.

  • The other parameters considered (gran size and seabed roughness) have a secondary influence on the sediment transport. The event duration seems to be an important parameter with a linear relation between increment in duration and increment in sediment transport, but further analysis is necessary in order to obtain a reliable description.

Finally, it is concluded that in a coastline like the one under examination, the accumulated precipitation (which is also increasing under the effect of climate change as 200 years national records suggest) must be of relevance in the stability of the sand dunes and sand cliffs. Future work should be conducted to quantify and model the influence of this parameter on beach erosion and sediment transport.