J.E.A. Storms
Please Note
23 records found
1
Modelling shoreline development in a wave dominated delta
Validation of ShorelineS model using case study of Rhône delta, France
This study analyses the applicability of ShorelineS for simulation of a shoreline with a river mouth. To this extent a synthetic case of a shoreline with a river mouth is set up to analyse the model behaviour of ShorelineS in a simplified environment. The effect of many input parameters on the shoreline development is analysed. These parameters include wave parameters, channel parameters, transport parameters, model parameters, and relative sea level rise. The applicability is further tested in a more complex environment with a real-world case. For this, a hindcast is set up. The location of the hindcast is the shoreline of the Rhône delta. This is a wave dominated, sandy coast with a negligible tidal range. Data on the shoreline, the wave climate, the sediment budget, and the shoreline profile were required to get a successful hindcast.
The implementation of a river mouth in ShorelineS is done through specifying the river flow path as well as to what extent the channel should be kept. The sediment discharge is then approximated by a nourishment in the flow path that is pushed out to the shore. This approach was found to work well in a simplified environment through analysis of results from the synthetic case. The different simulations resulted in the expected model behaviour and the simulations were stable.
The results of the hindcast are mostly positive. The hindcast gets a good skill score and the simulations are mostly stable. The biggest differences between the simulated shoreline and the actual shoreline of the Rhône delta can be explained by the existence of relict sediment lobes along the shoreline. These lobes are the result of the combination of progradation and avulsion in the Rhône delta. They make the shoreline profile variable and provide time limited sediment sources.
ShorelineS cannot account for these naturally occurring lobes because of the assumption of the constant profile angle along the shoreline. Combining this with the fact that ShorelineS is incapable of simulating processes related to river dynamics such as avulsion and the forming of mouth bars limits the applicability of ShorelineS in environments governed by natural processes, such as the Rhône delta.
However, there is enough applicability for ShorelineS outside of these environments. When the shoreline is not governed by natural processes but is instead regulated by humans, a canal for instance, the results of the ShorelineS simulations will only get better. The big difference in time and cost efficiency compared to other models makes ShorelineS uniquely suited for applicability where the demand for accuracy of the simulation is lower. For instance, in data limited environments or on a global scale. ...
This study analyses the applicability of ShorelineS for simulation of a shoreline with a river mouth. To this extent a synthetic case of a shoreline with a river mouth is set up to analyse the model behaviour of ShorelineS in a simplified environment. The effect of many input parameters on the shoreline development is analysed. These parameters include wave parameters, channel parameters, transport parameters, model parameters, and relative sea level rise. The applicability is further tested in a more complex environment with a real-world case. For this, a hindcast is set up. The location of the hindcast is the shoreline of the Rhône delta. This is a wave dominated, sandy coast with a negligible tidal range. Data on the shoreline, the wave climate, the sediment budget, and the shoreline profile were required to get a successful hindcast.
The implementation of a river mouth in ShorelineS is done through specifying the river flow path as well as to what extent the channel should be kept. The sediment discharge is then approximated by a nourishment in the flow path that is pushed out to the shore. This approach was found to work well in a simplified environment through analysis of results from the synthetic case. The different simulations resulted in the expected model behaviour and the simulations were stable.
The results of the hindcast are mostly positive. The hindcast gets a good skill score and the simulations are mostly stable. The biggest differences between the simulated shoreline and the actual shoreline of the Rhône delta can be explained by the existence of relict sediment lobes along the shoreline. These lobes are the result of the combination of progradation and avulsion in the Rhône delta. They make the shoreline profile variable and provide time limited sediment sources.
ShorelineS cannot account for these naturally occurring lobes because of the assumption of the constant profile angle along the shoreline. Combining this with the fact that ShorelineS is incapable of simulating processes related to river dynamics such as avulsion and the forming of mouth bars limits the applicability of ShorelineS in environments governed by natural processes, such as the Rhône delta.
However, there is enough applicability for ShorelineS outside of these environments. When the shoreline is not governed by natural processes but is instead regulated by humans, a canal for instance, the results of the ShorelineS simulations will only get better. The big difference in time and cost efficiency compared to other models makes ShorelineS uniquely suited for applicability where the demand for accuracy of the simulation is lower. For instance, in data limited environments or on a global scale.
To address the above-mentioned questions, we apply and progressively refine compaction formulations within the Delft3D 4 - FLOW code. This approach focuses on mechanical compaction because it contributes to the largest sediment volume reduction compared to biological and chemical compaction. Additionally, it mainly operates within the active part of the delta top. This type of compaction occurs in two phases, primary and secondary compaction, driven by overburden weight and simulated time. Both phases lead to pore fluid expulsion, resulting in sediment volume reduction and lowering of the bed surface (subsidence). By switching compaction on and off in model simulations, the effects of syn-depositional compaction on delta development are assessed. Quantitative metrics are developed to enable comparison between simulations, including changes in delta geometry, sediment mass distribution, accommodation generation, and sediment erodibility.
Modelling results show that syn-depositional compaction generates additional accommodation during delta development, which alters delta morphology. Morphological changes are more prominent in mud-rich deltas than in sand-rich deltas, which experience larger compaction-induced volume reduction for the same compaction rate scenario. In higher compaction rate scenarios, accommodation increases at the delta top, leading to more sedimentation and more evenly distributed sediment at the delta top. This results in a less significant area increase and a wider delta top with a smoother coastline. These morphological responses emerge from feedback between compaction-induced additional accommodation, sedimentation, and channel dynamics.
Additional accommodation generated by syn-depositional compaction also affects the distribution of sediment mass across delta depositional areas. Modelling results show that increased accommodation on the delta plain promotes sedimentation in this area, thereby reducing sediment delivery to the mouth bar and beyond. Further increases in accommodation lead to enhanced lateral sediment redistribution associated with channel relocation, with sedimentation mainly occurring in the mouth bar. Changes in sedimentation within a depositional area are accompanied by compensating changes elsewhere, indicating interdependencies within the delta-wide sediment budget influenced by syn-depositional compaction. These results demonstrate that compaction-induced accommodation redistributes sediment beyond the immediate subsidence area, affecting sedimentation across the entire delta system.
In addition to generating additional accommodation, syn-depositional compaction increases sediment resistance to resuspension. Levees act as key sediment conduits in delta systems, and the location and timing of levee breaching are commonly assessed using proxies that describe the influence of topography on hydraulic forcing acting on levee deposits. However, the role of sediment properties, particularly levee resistance to resuspension, remains poorly constrained. The modelling results show that commonly used proxies, such as superelevation and gradient advantage, are relevant in predicting when and where levee breaching is initiated, but they are insufficient to describe breach progression, which depends on the balance between flow-induced shear stress and sediment resistance to resuspension. Syn-depositional compaction modifies both bed elevation and sediment erodibility, thereby influencing whether breaches are sustained or abandoned.
Overall, this dissertation demonstrates that syn-depositional compaction is a fundamental process influencing simulated delta evolution over millennial timescales. While numerical models cannot capture all processes operating in natural deltas, they provide a controlled framework to explore process interactions that are difficult to observe directly in the field. The results show that syn-depositional compaction affects delta morphology, sediment distribution, and levee breaching, and therefore represents a critical mechanism that should be included in process-based delta modelling studies. ...
To address the above-mentioned questions, we apply and progressively refine compaction formulations within the Delft3D 4 - FLOW code. This approach focuses on mechanical compaction because it contributes to the largest sediment volume reduction compared to biological and chemical compaction. Additionally, it mainly operates within the active part of the delta top. This type of compaction occurs in two phases, primary and secondary compaction, driven by overburden weight and simulated time. Both phases lead to pore fluid expulsion, resulting in sediment volume reduction and lowering of the bed surface (subsidence). By switching compaction on and off in model simulations, the effects of syn-depositional compaction on delta development are assessed. Quantitative metrics are developed to enable comparison between simulations, including changes in delta geometry, sediment mass distribution, accommodation generation, and sediment erodibility.
Modelling results show that syn-depositional compaction generates additional accommodation during delta development, which alters delta morphology. Morphological changes are more prominent in mud-rich deltas than in sand-rich deltas, which experience larger compaction-induced volume reduction for the same compaction rate scenario. In higher compaction rate scenarios, accommodation increases at the delta top, leading to more sedimentation and more evenly distributed sediment at the delta top. This results in a less significant area increase and a wider delta top with a smoother coastline. These morphological responses emerge from feedback between compaction-induced additional accommodation, sedimentation, and channel dynamics.
Additional accommodation generated by syn-depositional compaction also affects the distribution of sediment mass across delta depositional areas. Modelling results show that increased accommodation on the delta plain promotes sedimentation in this area, thereby reducing sediment delivery to the mouth bar and beyond. Further increases in accommodation lead to enhanced lateral sediment redistribution associated with channel relocation, with sedimentation mainly occurring in the mouth bar. Changes in sedimentation within a depositional area are accompanied by compensating changes elsewhere, indicating interdependencies within the delta-wide sediment budget influenced by syn-depositional compaction. These results demonstrate that compaction-induced accommodation redistributes sediment beyond the immediate subsidence area, affecting sedimentation across the entire delta system.
In addition to generating additional accommodation, syn-depositional compaction increases sediment resistance to resuspension. Levees act as key sediment conduits in delta systems, and the location and timing of levee breaching are commonly assessed using proxies that describe the influence of topography on hydraulic forcing acting on levee deposits. However, the role of sediment properties, particularly levee resistance to resuspension, remains poorly constrained. The modelling results show that commonly used proxies, such as superelevation and gradient advantage, are relevant in predicting when and where levee breaching is initiated, but they are insufficient to describe breach progression, which depends on the balance between flow-induced shear stress and sediment resistance to resuspension. Syn-depositional compaction modifies both bed elevation and sediment erodibility, thereby influencing whether breaches are sustained or abandoned.
Overall, this dissertation demonstrates that syn-depositional compaction is a fundamental process influencing simulated delta evolution over millennial timescales. While numerical models cannot capture all processes operating in natural deltas, they provide a controlled framework to explore process interactions that are difficult to observe directly in the field. The results show that syn-depositional compaction affects delta morphology, sediment distribution, and levee breaching, and therefore represents a critical mechanism that should be included in process-based delta modelling studies.
Detection of stratigraphic heterogeneities at sub-seismic scale
Lessons from wave-dominated depositional environments
Rising waters, Resilient lives: The Can Tho region in 2075
Multidisciplinary project on the Mekong Delta
Global identification and characterization of drivers of shoreline evolution
A novel method using Satellite Derived Shorelines and spatiotemporal characteristics
Up till now, studies into coastal erosion have been conducted locally, resulting in site specific observations. However, the promising results of using satellite imagery in the field of coastal engineering allowed studies to be performed at larger spatial scales. This can lead to the identification of areas with similar characteristics, resulting in methodological standardization of approaching a specific problem. A first step toward this new approach of studying shoreline evolution was taken by Luijendijk et al. (2018) who presented a global dataset of annual shoreline positions for sandy beaches over the period 1984-2016 using satellite derived shorelines
(SDS). However, the drivers (causes) of shoreline evolution on a global scale were still unknown, making it only suitable for identifying areas of structural shoreline change, but less suitable for deriving coastal management solutions. Therefore, the research objective in this study is to identify and characterize drivers of shoreline evolution on a global scale using SDS.
This study focused on dynamic sandy beaches, or hotspots, extracted using a method developed by Kras (2019). In this method, using a 2.5-kilometer moving window, transects showing structural shoreline changes and similar characteristics both in space and time were grouped. The small size of the moving window led to locally created hotspots, 95% of which had a spatial extent of less than 10 kilometers, allowing to study shoreline drivers with small to moderate spatial scales (∼10 kilometer). Therefore, the main focus in this study lies on seasonality as a natural driver of shoreline evolution and three anthropogenic drivers: reclamations, nourishments and littoral drift barriers. As seasonality shows inter-annual variability, the temporal resolution of the SDS is increased from annual to monthly.
Using time series decomposition methods, different parameters are extracted that can be used to link the drivers to the SDS. Besides temporal parameters, also parameters related to spatial characteristics are considered. These parameters can be split into identification parameters, used for identifying a driver, and informative parameters, providing knowledge on the behavior of the driver. These parameters were developed and tested using local case studies. Results from these local case studies showed that the identification parameters showed similar behavior along the case studies. This implies that the identification parameters correctly reflect a driver’s behavior. Next, identification of the drivers was verified on a larger scale, all transects within hotspots on West-European coastlines. Verification was done on hundreds of samples using literature or manual inspection of satellite images. Using precision scores, the fraction of true positives to the total identified cases, optimal settings were derived for identification of the drivers. These settings resulted in a pattern of driver identification and characterization along the West-European coastline that is supported by literature.
With the optimal settings for identification determined, the methods were deployed on a global scale. The global dataset consisted out of 3033 prograding and 2121 retreating hotspots containing over 58 thousand transects in total. For these hotspots, SDS were generated over the period 1984-2021 with a monthly temporal resolution. This resulted in a global dataset of more than 26 million monthly shoreline positions. Two other processes, in addition to a seasonal change in wave height, were found to be able to generate seasonal variations in coastline positions from this global dataset. At the Red Sea, even though the wave climate is low in energy (Langodan et al., 2017), the coast is characterized by seasonal behavior. However, in this basin, seasonal variations in water levels rather than the wave climate best described this pattern. In addition to varying wave height and water level, seasonal beach morphology can also be caused by a shift in wave direction. This was observed in southern and western parts of Australia. Furthermore, non-seasonal beaches were primarily seen in low-energetic wave regions where neither of these other two processes occurred, as is the case in the Mediterranean. In regions where seasonal shoreline fluctuations are caused by differences in wave energy, minimum shoreline positions were found at the start of the summer. However, the period in which minimal shoreline positions are observed may be observed at a different time of the year in regions where seasonal shoreline behavior is driven by water level variations or a shift in wave direction. The identification of reclamations pointed out that this driver was especially linked to shoreline evolution in the Middle East and East-Asia. Furthermore, while the amount of constructions of reclamations remained
constant on a global level over the period 1987-2017, in these two areas an increase was observed. Opposite behavior was found by the identification of nourishments, as this driver was identified more often in the period 2007-2017 compared to the two decades before that. Moreover, nourishments were mostly observed in Western countries, for example the USA and the Netherlands. Nevertheless, also in Non-Western countries, an increment over time in the amount of nourishments could be detected. This indicates that throughout the entire world the use of nourishments as a measure to prevent coastal erosion is increasing. Shoreline evolution linked to littoral drift barriers was mostly observed in North-America, Europe and Africa. Downdrift (erosive) hotspots were mostly observed in Africa while in North-America and Europe mostly updrift (accreting) hotspots were linked to littoral drift barriers. On a global level, a combination of an updrift and downdrift hotspots (a pair) was observed in only 2% of all hotspots.
The outcomes above can support local-scale studies by identifying the drivers of shoreline evolution, describing their characteristics and even create standardization by analyzing areas with similar behavior. Hence, it can be concluded that spatiotemporal parameters describing the behavior of a driver can be used to identify and characterize drivers on a global scale using SDS. Nevertheless, not all drivers of shoreline evolution were included in this study. Therefore, to include drivers with larger spatial scales, hotspots should be extracted by using a larger moving spatial window. Furthermore, by increasing the spatiotemporal resolution on which this extraction is based, accuracy of the spatial extent of the hotspots is expected to increase. The small proportion of pairs identified for littoral drift barriers can be partly explained by the erroneous spatial extent of some hotspots. Finally, drivers are identified independently from each other neglecting their interactions. Even though interactions might be complex, drivers should not be identified independently as this will rather
require local studies than support them. Still, even though refinement and further development of the methods is required, this research has shown that identifying the drivers of shoreline development on a global scale using SDS has great potential for sustainable coastal management in the face of future challenges
...
Up till now, studies into coastal erosion have been conducted locally, resulting in site specific observations. However, the promising results of using satellite imagery in the field of coastal engineering allowed studies to be performed at larger spatial scales. This can lead to the identification of areas with similar characteristics, resulting in methodological standardization of approaching a specific problem. A first step toward this new approach of studying shoreline evolution was taken by Luijendijk et al. (2018) who presented a global dataset of annual shoreline positions for sandy beaches over the period 1984-2016 using satellite derived shorelines
(SDS). However, the drivers (causes) of shoreline evolution on a global scale were still unknown, making it only suitable for identifying areas of structural shoreline change, but less suitable for deriving coastal management solutions. Therefore, the research objective in this study is to identify and characterize drivers of shoreline evolution on a global scale using SDS.
This study focused on dynamic sandy beaches, or hotspots, extracted using a method developed by Kras (2019). In this method, using a 2.5-kilometer moving window, transects showing structural shoreline changes and similar characteristics both in space and time were grouped. The small size of the moving window led to locally created hotspots, 95% of which had a spatial extent of less than 10 kilometers, allowing to study shoreline drivers with small to moderate spatial scales (∼10 kilometer). Therefore, the main focus in this study lies on seasonality as a natural driver of shoreline evolution and three anthropogenic drivers: reclamations, nourishments and littoral drift barriers. As seasonality shows inter-annual variability, the temporal resolution of the SDS is increased from annual to monthly.
Using time series decomposition methods, different parameters are extracted that can be used to link the drivers to the SDS. Besides temporal parameters, also parameters related to spatial characteristics are considered. These parameters can be split into identification parameters, used for identifying a driver, and informative parameters, providing knowledge on the behavior of the driver. These parameters were developed and tested using local case studies. Results from these local case studies showed that the identification parameters showed similar behavior along the case studies. This implies that the identification parameters correctly reflect a driver’s behavior. Next, identification of the drivers was verified on a larger scale, all transects within hotspots on West-European coastlines. Verification was done on hundreds of samples using literature or manual inspection of satellite images. Using precision scores, the fraction of true positives to the total identified cases, optimal settings were derived for identification of the drivers. These settings resulted in a pattern of driver identification and characterization along the West-European coastline that is supported by literature.
With the optimal settings for identification determined, the methods were deployed on a global scale. The global dataset consisted out of 3033 prograding and 2121 retreating hotspots containing over 58 thousand transects in total. For these hotspots, SDS were generated over the period 1984-2021 with a monthly temporal resolution. This resulted in a global dataset of more than 26 million monthly shoreline positions. Two other processes, in addition to a seasonal change in wave height, were found to be able to generate seasonal variations in coastline positions from this global dataset. At the Red Sea, even though the wave climate is low in energy (Langodan et al., 2017), the coast is characterized by seasonal behavior. However, in this basin, seasonal variations in water levels rather than the wave climate best described this pattern. In addition to varying wave height and water level, seasonal beach morphology can also be caused by a shift in wave direction. This was observed in southern and western parts of Australia. Furthermore, non-seasonal beaches were primarily seen in low-energetic wave regions where neither of these other two processes occurred, as is the case in the Mediterranean. In regions where seasonal shoreline fluctuations are caused by differences in wave energy, minimum shoreline positions were found at the start of the summer. However, the period in which minimal shoreline positions are observed may be observed at a different time of the year in regions where seasonal shoreline behavior is driven by water level variations or a shift in wave direction. The identification of reclamations pointed out that this driver was especially linked to shoreline evolution in the Middle East and East-Asia. Furthermore, while the amount of constructions of reclamations remained
constant on a global level over the period 1987-2017, in these two areas an increase was observed. Opposite behavior was found by the identification of nourishments, as this driver was identified more often in the period 2007-2017 compared to the two decades before that. Moreover, nourishments were mostly observed in Western countries, for example the USA and the Netherlands. Nevertheless, also in Non-Western countries, an increment over time in the amount of nourishments could be detected. This indicates that throughout the entire world the use of nourishments as a measure to prevent coastal erosion is increasing. Shoreline evolution linked to littoral drift barriers was mostly observed in North-America, Europe and Africa. Downdrift (erosive) hotspots were mostly observed in Africa while in North-America and Europe mostly updrift (accreting) hotspots were linked to littoral drift barriers. On a global level, a combination of an updrift and downdrift hotspots (a pair) was observed in only 2% of all hotspots.
The outcomes above can support local-scale studies by identifying the drivers of shoreline evolution, describing their characteristics and even create standardization by analyzing areas with similar behavior. Hence, it can be concluded that spatiotemporal parameters describing the behavior of a driver can be used to identify and characterize drivers on a global scale using SDS. Nevertheless, not all drivers of shoreline evolution were included in this study. Therefore, to include drivers with larger spatial scales, hotspots should be extracted by using a larger moving spatial window. Furthermore, by increasing the spatiotemporal resolution on which this extraction is based, accuracy of the spatial extent of the hotspots is expected to increase. The small proportion of pairs identified for littoral drift barriers can be partly explained by the erroneous spatial extent of some hotspots. Finally, drivers are identified independently from each other neglecting their interactions. Even though interactions might be complex, drivers should not be identified independently as this will rather
require local studies than support them. Still, even though refinement and further development of the methods is required, this research has shown that identifying the drivers of shoreline development on a global scale using SDS has great potential for sustainable coastal management in the face of future challenges
With this study, it is shown that the Rijnstrangen realistically can contribute up to 100 Mm3/y to the drinking water production in its region. This is up to 75% of the drinking water production of the Dutch province Gelderland, in which the Rijnstrangen is located. The exact maximum extraction volume from the Rijnstrangen depends on policy choices such as the maximum accepted water level in the Rijnstrangen and the maximum accepted average extraction from the region around the Rijnstrangen.
From a water quantity point of view, the maximum extraction volume of up to 100 Mm3/y indicates that utilizing the Rijnstrangen as a retention reservoir is a promising option to contribute to drought mitigation in the eastern part of the Netherlands. Therefore, further investigation of this idea is relevant.
...
With this study, it is shown that the Rijnstrangen realistically can contribute up to 100 Mm3/y to the drinking water production in its region. This is up to 75% of the drinking water production of the Dutch province Gelderland, in which the Rijnstrangen is located. The exact maximum extraction volume from the Rijnstrangen depends on policy choices such as the maximum accepted water level in the Rijnstrangen and the maximum accepted average extraction from the region around the Rijnstrangen.
From a water quantity point of view, the maximum extraction volume of up to 100 Mm3/y indicates that utilizing the Rijnstrangen as a retention reservoir is a promising option to contribute to drought mitigation in the eastern part of the Netherlands. Therefore, further investigation of this idea is relevant.
...
Perforated and Fractured Territories
Socio-territorial identity building as response to growing interest in metalogenic mining in Finnmark, Northern Norway
Morphological Response of the Dutch Sandy Coast to Accelerated Sea Level Rise
A process-based modelling approach using Delft3D, applied to the Delfland coast
Determination of REV and Effective Properties of Fluvial Depositional Systems
A feasibility study using 3D FLUMY models
To illustrate this problem on a local scale, a project side in the northeast of Florida is selected, Duval County. At this site numerous beach and shoreface nourishments have been applied with an average nourishment cycle of approximately 5 years. However, taking the effect of climate change and sea-level rise into account, the required nourishment volumes will increase in the future. This means that other solutions need to be investigated. In the Netherlands, the pilot experiment Sand Engine is carried out, involving a large-scale feeder nourishment. It is expected that this type of nourishment will be more beneficial as it reduces the nourishment frequency and contains a concentrated displacement area. The nourishment will spread along the adjacent coastlines in a natural fashion, reducing the impact on ecology. Lastly, large-scale nourishment can temporary lead to additional recreational and environmental area, with a potential of creating new ecological habitats. This leads to the following research question:
'How can a large-scale feeder nourishment be beneficial for highly erosive coastlines along the Atlantic coast of the US, and how can the effects of such nourishments be quantified on different timescales?'
In order to evaluate the effect of large-scale feeder nourishments on the coast of Duval County, an evaluation framework has been developed. This framework is based on ecosystem services, which describe the way humans are linked to and depend on nature. Three main ecosystem services have been identified, which have been divided into several sub-services indicated by quantifiable parameters. The first ecosystem service is coastal protection, which is evaluated in terms of flood protection and maintenance of the coastline position. The time-dependent indicators for these sub-services are the foreshore volume and the distance between the Coastal Construction Control Line and the Momentary Coast Line. Secondly, recreation is evaluated by the sub-services of beach leisure, swimming, kitesurfing and strolling. Beach leisure is indicated by the dry beach width, swimming by the offshore directed flow velocities around the nourishment, kitesurfing by the additional sheltered area, and strolling by the walkable beach length along the shoreline. Lastly, the ecosystem service of habitat provision is split into three sub-services, namely nursery area, turtle nesting and dune growth potential. The nursery area is quantified by mapping the existing ecotopes, turtle nesting is evaluated by the beach slope and the beach width and finally the dune growth potential is indicated by the intertidal beach width.
The researched nourishment alternatives differ from geometric shape and in nourishment frequency. Two shapes are connected to the beach and have a width to height ratio of (1:1) and (1:3), while one is detached from the beach in the form of an island. The first two shapes have been applied with a frequency of 1, 3, 5 and 10 years, and the island only for 5 and 10 years. The morphological development of the alternatives is predicted with the numerical model of Delft3D over a period of 10 years.
All nourishment alternatives have been evaluated for all the selected indicators. For coastal protection the most suitable nourishment alternative is an attached and elongated nourishment with a frequency of 10 years (the (1:3) nourishment alternative). For recreation it differs largely per sub-service, but considering all sub-services have an equal weighting, the (1:3) alternative in combination with a 1 year frequency and the offshore island alternative with a 10 year frequency perform the best. The (1:3) nourishment alternative with a 1 year frequency creates the most benefit for beach leisure and swimming, while the offshore island with a 10 year frequency does this for kitesurfing and strolling. Finally for the ecosystem service of habitat provision, the offshore island in combination with a 10 year frequency has the most potential. The most suitable nourishment alternative cannot be selected for Duval County as a whole since the weighting between the different ecosystem services is unknown, as it depends on the stakeholders involved.
Based on the analysis of the different nourishment strategies, the following conclusions have been drawn for the application of large-scale feeder nourishments:
•Large-scale nourishments can decrease the required coastline maintenance on the long-term as long as they are placed within the dynamic wave zone. However, shore connected shapes can cause initial downdrift erosion because of their protrusion into the ocean, which requires extra nourishments at these locations. The application involves a trade-off between applying a low nourishment frequency with a large volume, and being able to place all the sediment within the dynamic zone.
•The largest temporal additional recreational and environmental area is created by emerged alternatives. Shore connected nourishments provide the largest accessible beach area, while detached nourishments provide the largest sheltered area. In this study, the increase in sheltered area was up to 5 times as large compared to the original situation.
•Nourishment alternatives that are elongated and streamlined along the coastline have a larger region of influence after the simulation period. Here, the region of influence was 10-20\% larger compared to the other shapes.
•Large-scale feeder nourishments have the potential to transport sediment over the entire project area under sufficient tidal and wave forcing. It leads to a more gradual spread of sediment than small-scale nourishments, as they tend to pile up within the placement area.
•As the disturbance of large-scale feeder nourishments is less frequent and concentrated, the adjacent coastlines are fed in a natural fashion, reducing the stress on ecology.
In conclusion, large-scale feeder nourishment can be evaluated by the approach of ecosystem services. They can certainly be beneficial for highly erosive coastlines, but its optimal dimensions depend on the required wishes for the considered coastline. ...
To illustrate this problem on a local scale, a project side in the northeast of Florida is selected, Duval County. At this site numerous beach and shoreface nourishments have been applied with an average nourishment cycle of approximately 5 years. However, taking the effect of climate change and sea-level rise into account, the required nourishment volumes will increase in the future. This means that other solutions need to be investigated. In the Netherlands, the pilot experiment Sand Engine is carried out, involving a large-scale feeder nourishment. It is expected that this type of nourishment will be more beneficial as it reduces the nourishment frequency and contains a concentrated displacement area. The nourishment will spread along the adjacent coastlines in a natural fashion, reducing the impact on ecology. Lastly, large-scale nourishment can temporary lead to additional recreational and environmental area, with a potential of creating new ecological habitats. This leads to the following research question:
'How can a large-scale feeder nourishment be beneficial for highly erosive coastlines along the Atlantic coast of the US, and how can the effects of such nourishments be quantified on different timescales?'
In order to evaluate the effect of large-scale feeder nourishments on the coast of Duval County, an evaluation framework has been developed. This framework is based on ecosystem services, which describe the way humans are linked to and depend on nature. Three main ecosystem services have been identified, which have been divided into several sub-services indicated by quantifiable parameters. The first ecosystem service is coastal protection, which is evaluated in terms of flood protection and maintenance of the coastline position. The time-dependent indicators for these sub-services are the foreshore volume and the distance between the Coastal Construction Control Line and the Momentary Coast Line. Secondly, recreation is evaluated by the sub-services of beach leisure, swimming, kitesurfing and strolling. Beach leisure is indicated by the dry beach width, swimming by the offshore directed flow velocities around the nourishment, kitesurfing by the additional sheltered area, and strolling by the walkable beach length along the shoreline. Lastly, the ecosystem service of habitat provision is split into three sub-services, namely nursery area, turtle nesting and dune growth potential. The nursery area is quantified by mapping the existing ecotopes, turtle nesting is evaluated by the beach slope and the beach width and finally the dune growth potential is indicated by the intertidal beach width.
The researched nourishment alternatives differ from geometric shape and in nourishment frequency. Two shapes are connected to the beach and have a width to height ratio of (1:1) and (1:3), while one is detached from the beach in the form of an island. The first two shapes have been applied with a frequency of 1, 3, 5 and 10 years, and the island only for 5 and 10 years. The morphological development of the alternatives is predicted with the numerical model of Delft3D over a period of 10 years.
All nourishment alternatives have been evaluated for all the selected indicators. For coastal protection the most suitable nourishment alternative is an attached and elongated nourishment with a frequency of 10 years (the (1:3) nourishment alternative). For recreation it differs largely per sub-service, but considering all sub-services have an equal weighting, the (1:3) alternative in combination with a 1 year frequency and the offshore island alternative with a 10 year frequency perform the best. The (1:3) nourishment alternative with a 1 year frequency creates the most benefit for beach leisure and swimming, while the offshore island with a 10 year frequency does this for kitesurfing and strolling. Finally for the ecosystem service of habitat provision, the offshore island in combination with a 10 year frequency has the most potential. The most suitable nourishment alternative cannot be selected for Duval County as a whole since the weighting between the different ecosystem services is unknown, as it depends on the stakeholders involved.
Based on the analysis of the different nourishment strategies, the following conclusions have been drawn for the application of large-scale feeder nourishments:
•Large-scale nourishments can decrease the required coastline maintenance on the long-term as long as they are placed within the dynamic wave zone. However, shore connected shapes can cause initial downdrift erosion because of their protrusion into the ocean, which requires extra nourishments at these locations. The application involves a trade-off between applying a low nourishment frequency with a large volume, and being able to place all the sediment within the dynamic zone.
•The largest temporal additional recreational and environmental area is created by emerged alternatives. Shore connected nourishments provide the largest accessible beach area, while detached nourishments provide the largest sheltered area. In this study, the increase in sheltered area was up to 5 times as large compared to the original situation.
•Nourishment alternatives that are elongated and streamlined along the coastline have a larger region of influence after the simulation period. Here, the region of influence was 10-20\% larger compared to the other shapes.
•Large-scale feeder nourishments have the potential to transport sediment over the entire project area under sufficient tidal and wave forcing. It leads to a more gradual spread of sediment than small-scale nourishments, as they tend to pile up within the placement area.
•As the disturbance of large-scale feeder nourishments is less frequent and concentrated, the adjacent coastlines are fed in a natural fashion, reducing the stress on ecology.
In conclusion, large-scale feeder nourishment can be evaluated by the approach of ecosystem services. They can certainly be beneficial for highly erosive coastlines, but its optimal dimensions depend on the required wishes for the considered coastline.
This study concentrates on the Eridanos Delta and identifies the properties of the delta in terms of its progadation distance and sedimentation rate and compare different time models to the ones provided by Overeem (2001) and Kuhlmann (2008). Furthermore, studies the reservoir rocks in terms of their petrophysical properties and facies distribution. Moreover investigates the reasoning behind the shallow sediments gas accumulations and factors behind the concentration of all the discoveries around the A and B blocks. Lastly, constructs a 3D model of the reservoirs distribution in the study area and their properties by integrating the study results of geological, geophysical, petrophysical and reservoir engineering data.
Such results were achieved by interpreting a high resolution 3D seismic survey and 2D lines in combination with wells’ wireline logs and core data. Seismically, a total of 12 units were mapped to categories the successions (3.6 – 1.8Ma) that deposited post the Mid Miocene Unconformity. In addition, more than 20 wells were used to understand the reservoir properties in which seven wells have cores. Sedimentological aspects were assessed by studying the descriptions of cores and thin sections and the measurements of the core plugs. Gas accumulations were studied by evaluating the production data for gas and linking the gas to its source.
...
This study concentrates on the Eridanos Delta and identifies the properties of the delta in terms of its progadation distance and sedimentation rate and compare different time models to the ones provided by Overeem (2001) and Kuhlmann (2008). Furthermore, studies the reservoir rocks in terms of their petrophysical properties and facies distribution. Moreover investigates the reasoning behind the shallow sediments gas accumulations and factors behind the concentration of all the discoveries around the A and B blocks. Lastly, constructs a 3D model of the reservoirs distribution in the study area and their properties by integrating the study results of geological, geophysical, petrophysical and reservoir engineering data.
Such results were achieved by interpreting a high resolution 3D seismic survey and 2D lines in combination with wells’ wireline logs and core data. Seismically, a total of 12 units were mapped to categories the successions (3.6 – 1.8Ma) that deposited post the Mid Miocene Unconformity. In addition, more than 20 wells were used to understand the reservoir properties in which seven wells have cores. Sedimentological aspects were assessed by studying the descriptions of cores and thin sections and the measurements of the core plugs. Gas accumulations were studied by evaluating the production data for gas and linking the gas to its source.
Macro-scale performance of a mega-feeder nourishment
Describing and predicting the long-term feeding performance
Today, engineers and policy makers rely on expert judgement when assessing alternative nourishment strategies, or the need for additional nourishments. Currently no tool exists that enables quantification of the performance of a mega-feeder nourishment. Existing models that describe and predict developments of nearshore coastal areas have been applied before to assess the developments of a mega-feeder nourishment, but have not been validated specifically to describe the performance in terms of alongshore feeding. The research question is therefore: "How to describe and predict macro-scale mega-feeder nourishment performance with behaviour-based coastal indicators?"
A tool is proposed that enables the quantification of the performance of a mega-feeder nourishment, as well as the validation of models that describe and predict the performance of a mega-feeder nourishment, The tool is specifically aimed at quantifying the performance in terms of the alongshore feeding. The tool comprises of indicators that representatively quantify the contribution of sediment, the region of feeding, and the time it does so.
The tool is applied to the Sand Engine, used as a case study to examine the applicability. This Sand Engine, constructed during the spring of 2011, has a nourishment volume of 21.5Mm3, initially spanned a width of 2.4km and extended 1km into the sea. Application of the indicators to the Sand Engine confirmed the performance developed with continuous trends, suggesting the performance can be predicted.
From the validation of the model approaches, it is concluded that the analytical model can be used to predict the initial performance of a mega-feeder nourishment, if the longshore spreading is derived from the LST equation by Kamphuis. Second, if the bathymetry is regularly monitored (e.g. semi-annually), the input of the analytical model can be calibrated, enabling long-term predictions of the performance. If more detailed descriptions of the developments of a mega-feeder nourishment are needed, a bruteforce process-based numerical modelling approach can serve as a method to describe and predict the feeding performance of a mega-feeder nourishment.
The performance of the Sand Engine is predicted with the validated models up until 2030. The volumetric growth will stagnate on the south, while on the north it is expected to grow up to 4Mm3. The width will increase to approximately 7km. From this, it is concluded that it is unlikely the Sand Engine will meet its original objective of contributing to coastal safety along the Westland coast (17.2km). Further, the half-life of the Sand Engine will be reached near 2030, indicating the actual lifetime is significantly longer than the design lifetime (20 years).
...
Today, engineers and policy makers rely on expert judgement when assessing alternative nourishment strategies, or the need for additional nourishments. Currently no tool exists that enables quantification of the performance of a mega-feeder nourishment. Existing models that describe and predict developments of nearshore coastal areas have been applied before to assess the developments of a mega-feeder nourishment, but have not been validated specifically to describe the performance in terms of alongshore feeding. The research question is therefore: "How to describe and predict macro-scale mega-feeder nourishment performance with behaviour-based coastal indicators?"
A tool is proposed that enables the quantification of the performance of a mega-feeder nourishment, as well as the validation of models that describe and predict the performance of a mega-feeder nourishment, The tool is specifically aimed at quantifying the performance in terms of the alongshore feeding. The tool comprises of indicators that representatively quantify the contribution of sediment, the region of feeding, and the time it does so.
The tool is applied to the Sand Engine, used as a case study to examine the applicability. This Sand Engine, constructed during the spring of 2011, has a nourishment volume of 21.5Mm3, initially spanned a width of 2.4km and extended 1km into the sea. Application of the indicators to the Sand Engine confirmed the performance developed with continuous trends, suggesting the performance can be predicted.
From the validation of the model approaches, it is concluded that the analytical model can be used to predict the initial performance of a mega-feeder nourishment, if the longshore spreading is derived from the LST equation by Kamphuis. Second, if the bathymetry is regularly monitored (e.g. semi-annually), the input of the analytical model can be calibrated, enabling long-term predictions of the performance. If more detailed descriptions of the developments of a mega-feeder nourishment are needed, a bruteforce process-based numerical modelling approach can serve as a method to describe and predict the feeding performance of a mega-feeder nourishment.
The performance of the Sand Engine is predicted with the validated models up until 2030. The volumetric growth will stagnate on the south, while on the north it is expected to grow up to 4Mm3. The width will increase to approximately 7km. From this, it is concluded that it is unlikely the Sand Engine will meet its original objective of contributing to coastal safety along the Westland coast (17.2km). Further, the half-life of the Sand Engine will be reached near 2030, indicating the actual lifetime is significantly longer than the design lifetime (20 years).
Over the past decade, most research in MPS has emphasized on new algorithms for improving efficiency of MPS (Mariethoz and Caers, 2014; Mariethoz and Lefebvre, 2014), but there are still issues remain for the workflow to be widely used in geosciences. Furthermore, using nonstationary TI such as process-based simulation model in MPS are still an issue because the workflow is always different for specific cases. Until recently, little published works are available in applicating nonstationary TI in MPS.
The principal objective of this project was to determine an optimised methodology that allows the use of nonstationary process-based simulation model for TI input with MPS simulation in the fluvial-dominated delta. The process-based simulation model used in the study is a post-processed data from numerical model done in process-based modelling software Delft3D (Lesser et al., 2004) which is the PhD work of van der Vegt in 2018. There were two different cases utilised in this study that represents the whole delta development: Case A with high repetition in the patterns and Case B with low repetition in the patterns.
In order to achieve the desired outcome, this study links process-based simulation model with MPS using unconditional and conditional 2D MPS simulation with two different approaches: zonation approach and control map approach. The realisations from the unconditional simulation have to be validated until successful unconditional MPS simulation. The conditional MPS simulation were carried out when the unconditional realisations have been acknowledged as the approved results in mimicking the patterns of the Delft3D model. Lastly, the results were evaluated with four methods: connectivity function, E-type models, conditional variance models, and analysis of distance (ANODI).
In all of the MPS simulation results, the use of control map approach with unilateral simulation path proved to deliver better realisations for unconditional and conditional MPS simulations. Also, this study has presented an optimised workflow of 2D MPS simulation on using process-based simulation model in fluvial-dominated delta environment as TI based on different conditions of patterns’ repetition and hard data distribution. ...
Over the past decade, most research in MPS has emphasized on new algorithms for improving efficiency of MPS (Mariethoz and Caers, 2014; Mariethoz and Lefebvre, 2014), but there are still issues remain for the workflow to be widely used in geosciences. Furthermore, using nonstationary TI such as process-based simulation model in MPS are still an issue because the workflow is always different for specific cases. Until recently, little published works are available in applicating nonstationary TI in MPS.
The principal objective of this project was to determine an optimised methodology that allows the use of nonstationary process-based simulation model for TI input with MPS simulation in the fluvial-dominated delta. The process-based simulation model used in the study is a post-processed data from numerical model done in process-based modelling software Delft3D (Lesser et al., 2004) which is the PhD work of van der Vegt in 2018. There were two different cases utilised in this study that represents the whole delta development: Case A with high repetition in the patterns and Case B with low repetition in the patterns.
In order to achieve the desired outcome, this study links process-based simulation model with MPS using unconditional and conditional 2D MPS simulation with two different approaches: zonation approach and control map approach. The realisations from the unconditional simulation have to be validated until successful unconditional MPS simulation. The conditional MPS simulation were carried out when the unconditional realisations have been acknowledged as the approved results in mimicking the patterns of the Delft3D model. Lastly, the results were evaluated with four methods: connectivity function, E-type models, conditional variance models, and analysis of distance (ANODI).
In all of the MPS simulation results, the use of control map approach with unilateral simulation path proved to deliver better realisations for unconditional and conditional MPS simulations. Also, this study has presented an optimised workflow of 2D MPS simulation on using process-based simulation model in fluvial-dominated delta environment as TI based on different conditions of patterns’ repetition and hard data distribution.
Our understanding of the Earth’s interior is limited by the access we have of its deep layers, while the knowledge we have of Earth’s evolution is restricted to harvested information from the present state of our planet. We therefore use proxies, physical and numerical models, and observations made on and from the surface of the Earth. The landscape results from a combination of processes operating at the surface and in the subsurface. Thus, if one knows how to read the landscape, one may unfold its geological evolution.
In the past decade, numerous studies have documented km-scale upward and downward vertical movements in the continental rifted margins of the Atlantic Ocean and in their hinterlands.These movements, described as exhumation (upward) and subsidence (downward), have been labelled as “unpredicted” and/or “unexpected”. ‘Unpredicted’ because conceptual, physical, and numerical models that we dispose of for the evolution of continental margins do not generally account for these relatively recent observations. ‘Unexpected’ because the km-scale vertical movements occurred when our record of the geological history is insufficient to support them. As yet, the mechanisms responsible for the km-scale vertical movements remain enigmatic.
One of the common techniques used by geoscientists to investigate the past kinematics of the continental crust is to couple ‘low-temperature thermochronology’ and ‘time-temperature modelling’. In Morocco alone, over twenty studies were conducted following this approach. The reason behind this abundance of studies and the related enthusiasm of researchers towards Moroccan geology is due to its puzzling landscapes and complex history. In this Thesis, we investigate unconstrained aspects of the km-scale vertical movements that occurred in Morocco and its surroundings (Canary Islands, Algeria, Mali, and Mauritania). ...
Our understanding of the Earth’s interior is limited by the access we have of its deep layers, while the knowledge we have of Earth’s evolution is restricted to harvested information from the present state of our planet. We therefore use proxies, physical and numerical models, and observations made on and from the surface of the Earth. The landscape results from a combination of processes operating at the surface and in the subsurface. Thus, if one knows how to read the landscape, one may unfold its geological evolution.
In the past decade, numerous studies have documented km-scale upward and downward vertical movements in the continental rifted margins of the Atlantic Ocean and in their hinterlands.These movements, described as exhumation (upward) and subsidence (downward), have been labelled as “unpredicted” and/or “unexpected”. ‘Unpredicted’ because conceptual, physical, and numerical models that we dispose of for the evolution of continental margins do not generally account for these relatively recent observations. ‘Unexpected’ because the km-scale vertical movements occurred when our record of the geological history is insufficient to support them. As yet, the mechanisms responsible for the km-scale vertical movements remain enigmatic.
One of the common techniques used by geoscientists to investigate the past kinematics of the continental crust is to couple ‘low-temperature thermochronology’ and ‘time-temperature modelling’. In Morocco alone, over twenty studies were conducted following this approach. The reason behind this abundance of studies and the related enthusiasm of researchers towards Moroccan geology is due to its puzzling landscapes and complex history. In this Thesis, we investigate unconstrained aspects of the km-scale vertical movements that occurred in Morocco and its surroundings (Canary Islands, Algeria, Mali, and Mauritania).
From fluvial supply to delta deposits
Simulating sediment delivery, transport and deposition
Sequence stratigraphic analysis of Eridanos deltaic shallow gas-bearing deposits in North Sea
An insight into the shallow Dutch subsurface
been deposited by Eridanos fluvio-deltaic system, draining the Fennoscandian and Baltic shield through the present Baltic Sea. Three successful producing fields - A12-FA (2007), F02a-B-Pliocene (2009) and B13-FA (2011)- and
five under development have triggered the conduction of several studies in the offshore area. However the deltaic environment has been characterized as highly complex owing to its influence by the onset of Northern Hemisphere
Glaciation and thus the processes that governed the system have not become entirely understood. Enhanced cooling followed by the waxing and waning of the glaciers during warmer periods had an immediate impact on sediment
supply, accommodation space and mineralogical input. Although the sediments have been studied in terms of chrono-biostratigraphy, no systematic investigation with respect to the three main aforementioned factors as well
as the regional sequence stratigraphy and its link to the reservoir deposits has been made up to date. Therefore, this study employed sequence stratigraphy as a method to examine Eridanos conditions of deposition, investigate the
interplay between accommodation space and sediment supply and explore the nature of the gas-bearing reservoir sediments. The adopted methodology is comprised of two basic pillars, observation and interpretation. The first
records as clearly as possible the observations arise from the sequence analysis while the second extracts the meaningful information and interprets it in terms of temporal and spatial concepts. Using 2D seismic and well log data the basic observations were the stratal terminations, stacking patterns, seismic facies and the shoreline trajectory.
Seismic and well log interpretation showed that the delta experienced multiple events of sea level fall which forced the shoreline to regress basinward and caused sediment erosion or non-deposition. These events are bounded
by nine time-significant surfaces of subaerial unconformities which constitute the depositional sequences. Normal regression comprised the dominant depositional trend, combined with aggrading-prograding patterns, leading to
characteristic alternations of highstand and lowstand system tracts. Three main depositional environments which correspond to open marine turbidites (submarine lobes), delta front and delta top were identified from well logs,
core descriptions and the seismic facies analysis. The study suggests that the shallow gas is located in the alternations of silty-sandstones and claystones of the delta plain which comprise the vertical stacking of parasequence
topsets within the highstand- lowstand system tracts. Reconstruction of the relative sea level changes and sedimentation rates was made based on a technique introduced by this study. It uses the average thickness of each seismic
unit in order to interpolate time between the three known absolute ages obtained by the literature. The graphs showed that the accommodation space was generated by a low rate of sea level rise while sedimentation rates were
increasing over time. However the scarcity of time constrains in combination with the uncertainty in the estimation of seismic volumes resulted in a low resolution outcome. A comparison between the findings of this study and
those of the existing literature was made. The overall depositional trends and conditions seem to be in accordance with the other surveys. Nonetheless the proposed interplay between accommodation and supply can be assigned as
local since the examined area is limited compare to areas studied in literature. Limitations are traced in the quality of the 2D seismic data hampering the observation regarding the relation between the reflectors and the surfaces.
Consequently, the study offers an insight into the conditions under which the gas-bearing deltaic sediments were deposited and tries to place them in the established sequence stratigraphic framework. Also it provides information
regarding the distribution of the deltaic environments and identification of the reservoir rocks within each setting. The resulting interpretation can be used for prediction of the reservoir formations since the genetically-related
packages where they were identified are distributed in a predictable manner within a sedimentary basin. ...
been deposited by Eridanos fluvio-deltaic system, draining the Fennoscandian and Baltic shield through the present Baltic Sea. Three successful producing fields - A12-FA (2007), F02a-B-Pliocene (2009) and B13-FA (2011)- and
five under development have triggered the conduction of several studies in the offshore area. However the deltaic environment has been characterized as highly complex owing to its influence by the onset of Northern Hemisphere
Glaciation and thus the processes that governed the system have not become entirely understood. Enhanced cooling followed by the waxing and waning of the glaciers during warmer periods had an immediate impact on sediment
supply, accommodation space and mineralogical input. Although the sediments have been studied in terms of chrono-biostratigraphy, no systematic investigation with respect to the three main aforementioned factors as well
as the regional sequence stratigraphy and its link to the reservoir deposits has been made up to date. Therefore, this study employed sequence stratigraphy as a method to examine Eridanos conditions of deposition, investigate the
interplay between accommodation space and sediment supply and explore the nature of the gas-bearing reservoir sediments. The adopted methodology is comprised of two basic pillars, observation and interpretation. The first
records as clearly as possible the observations arise from the sequence analysis while the second extracts the meaningful information and interprets it in terms of temporal and spatial concepts. Using 2D seismic and well log data the basic observations were the stratal terminations, stacking patterns, seismic facies and the shoreline trajectory.
Seismic and well log interpretation showed that the delta experienced multiple events of sea level fall which forced the shoreline to regress basinward and caused sediment erosion or non-deposition. These events are bounded
by nine time-significant surfaces of subaerial unconformities which constitute the depositional sequences. Normal regression comprised the dominant depositional trend, combined with aggrading-prograding patterns, leading to
characteristic alternations of highstand and lowstand system tracts. Three main depositional environments which correspond to open marine turbidites (submarine lobes), delta front and delta top were identified from well logs,
core descriptions and the seismic facies analysis. The study suggests that the shallow gas is located in the alternations of silty-sandstones and claystones of the delta plain which comprise the vertical stacking of parasequence
topsets within the highstand- lowstand system tracts. Reconstruction of the relative sea level changes and sedimentation rates was made based on a technique introduced by this study. It uses the average thickness of each seismic
unit in order to interpolate time between the three known absolute ages obtained by the literature. The graphs showed that the accommodation space was generated by a low rate of sea level rise while sedimentation rates were
increasing over time. However the scarcity of time constrains in combination with the uncertainty in the estimation of seismic volumes resulted in a low resolution outcome. A comparison between the findings of this study and
those of the existing literature was made. The overall depositional trends and conditions seem to be in accordance with the other surveys. Nonetheless the proposed interplay between accommodation and supply can be assigned as
local since the examined area is limited compare to areas studied in literature. Limitations are traced in the quality of the 2D seismic data hampering the observation regarding the relation between the reflectors and the surfaces.
Consequently, the study offers an insight into the conditions under which the gas-bearing deltaic sediments were deposited and tries to place them in the established sequence stratigraphic framework. Also it provides information
regarding the distribution of the deltaic environments and identification of the reservoir rocks within each setting. The resulting interpretation can be used for prediction of the reservoir formations since the genetically-related
packages where they were identified are distributed in a predictable manner within a sedimentary basin.