OS4.8 | Monitoring, Modeling and Risk Mapping of Marine pollution and its Environmental and Socioeconomic Footprints
EDI
Monitoring, Modeling and Risk Mapping of Marine pollution and its Environmental and Socioeconomic Footprints
Convener: Giovanni Coppini | Co-conveners: Luisa Galgani, George Zodiatis, Camille RichonECSECS, Katerina Spanoudaki
Orals
| Thu, 27 Apr, 14:00–15:45 (CEST)
 
Room 1.14
Posters on site
| Attendance Thu, 27 Apr, 10:45–12:30 (CEST)
 
Hall X5
Posters virtual
| Attendance Thu, 27 Apr, 10:45–12:30 (CEST)
 
vHall CR/OS
Orals |
Thu, 14:00
Thu, 10:45
Thu, 10:45
Oceanographic monitoring and modeling are both widely used to study the pathways and fate of marine pollutants such as anthropogenic hydrocarbons, marine litter (including plastics, microplastics, and nanoplastics), POPs, HNS, radionuclides, pharmaceutics, etc. This session focuses on monitoring frameworks, computational tools, lab experiments and emerging technologies related to tracing pollutants and their impacts on local, regional, and global scales. Coupling with met-oceanographic and biogeochemical datasets provided, for example, by the Copernicus programme will also be discussed. State-of-the-art observational techniques and protocols, ensemble and multi-model methods, risk assessment algorithms and decision support systems are solicited topics. Integration of modelling, observing systems, and lab experiments for both data assimilation and model validation are also very welcome.

We welcome studies based on in situ and lab observational, and modeling work looking at physical and biogeochemical transformation of pollutants and impacts on ocean biogeochemistry and ecosystems such as fragmentation, biofouling, ingestion but also chemical impacts such as adsorption, transport and desorption of nutrients, heavy metals, and microbes. Discussions about newly discovered phenomena, as, for example, the mucilage outbreaks, a role of Extracellular Polymeric Substances (EPS), and other ecotoxicological issues are also encouraged.

Studies that link effects to broader ecosystem stressors like environmental degradation and climate change are particularly welcome. Monitoring and modeling the pollutants’ transport under the ice conditions are also appreciated, which is related to the increase in shipping traffic in the Arctic Ocean and melting the Polar ice as a consequence of the climate changes.

Key questions of the session are identified as follows: Which factors affect the dispersion of pollutants in the marine environment? What happens to the contaminants on the ocean’s surface, in the water column, and sediments? How do marine pollutants interact with marine habitats? How do they influence marine and maritime resources? How should Integrated Coastal Zone Management (ICZM) protocols be optimized to minimize negative impacts?

Influence of other environmental stressors, including artificial light, noise, and thermal pollution, on marine ecosystems and resilience to them, is also important subjects for discussion.

Orals: Thu, 27 Apr | Room 1.14

Chairpersons: Giovanni Coppini, Katerina Spanoudaki
14:00–14:05
14:05–14:15
|
EGU23-2578
|
ECS
|
On-site presentation
Sara Cloux, Patricia Pérez, Hilda de Pablo, and Vicente Pérez-Muñuzuri

Plastic debris in the oceans is a major environmental concern that knows no borders. This material, which is the result of poor waste management on land, is spread across the ocean over long distances and over long periods of time. When macroplastics (those larger than 5 mm) break down through mechanical and chemical processes, they become microplastics. It is difficult to estimate the extent and predict the behavior of these tiny pieces of plastic, but their presence in a variety of organisms, including mollusks and humans, has raised concerns about the potential consequences, which are not yet fully understood but are believed to be significant. To address this problem at a global scale, it is important to identify and quantify the sources of plastic waste that end up in the ocean. We use a validated Lagrangian model (Cloux et al., 2022) to track floating particles coming from potential sources. We studied three types of sources along the Atlantic coast of Spain: rivers, land-based points, and maritime traffic. Over a 7-year period, we analyzed the concentrations of these plastics in the open seas. Our results showed that a significant contribution comes from these sources, both at short and medium distances from the coast. If we consider the fact that some of the simulated particles get washed up on the shore, the concentration of particles near the coast is even higher in certain locations and the concentrations at medium distances are reduced.  Considering semi-enclosed areas, the influence of seasonality was studied for the Bay of Biscay, the Gulf of Cadiz and the Alboran Sea.  The presence of particles in each zone varies between warm and cold seasons, depending on the dynamics of the zone.  The results of this study are under review processes (Cloux et al., n.d.).

 

Cloux, S., Allen-Perkins, S., de Pablo, H., Garaboa-Paz, D., Montero, P., & Pérez-Muñuzuria, V. (2022). Validation of a Lagrangian model for large-scale macroplastic tracer transport using mussel-peg in NW Spain (Ría de Arousa). Science of The Total Environment, 822, 153338. https://doi.org/10.1016/j.scitotenv.2022.153338

Cloux, S., Pérez-Pérez, P., de Pablo, H., & Pérez-Muñuzuri, V. (n.d.). A Regional Lagrangian Model to Evaluate the Dispersion of Floating Macroplastics in the North Atlantic Ocean from Different Types of Sources in the Iberian Peninsula. Available at SSRN 4306128.

How to cite: Cloux, S., Pérez, P., de Pablo, H., and Pérez-Muñuzuri, V.: A Regional Lagrangian Model for Assessing the Dispersion of Floating Macroplastics from Different Source Types over the Iberian Peninsula in the North Atlantic Ocean, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-2578, https://doi.org/10.5194/egusphere-egu23-2578, 2023.

14:15–14:25
|
EGU23-3083
|
Virtual presentation
Adolf Stips, Diego Macias, and Ove Parn

Marine plastic floating on the sea surface is a major environmental problem. The present study
investigated the potential transport patterns of floating marine litter and areas of its
accumulation in the Baltic Sea by using a hydrodynamic model coupled with a particle-tracking
model (Parcels). Mapping of marine plastic debris distribution in 2017–2018 revealed that the largest
plastic accumulation area is between latitude 59° and 61°, which includes the Northern Baltic
Proper, Archipelago Sea, and the Gulf of Finland. The floating plastic spreads from the largest
plastic pollution site River Vistula to the waters of all the countries around the Baltic Sea.

How to cite: Stips, A., Macias, D., and Parn, O.: Determining the distribution and accumulation patterns of floating litter using  modelling tools in the Baltic Sea, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-3083, https://doi.org/10.5194/egusphere-egu23-3083, 2023.

14:25–14:35
|
EGU23-5062
|
On-site presentation
Sang Hee Hong, Yelim Moon, Gi Myung Han, Won Joon Shim, Sung Yong Ha, Il-Hoon Kim, and Hae-Rim Lee

Global production of plastics has steadily increased since 1950s. As a result, plastics are the most abundant type of marine debris on seafloor and coastal beach, and the prevalence of marine debris has detrimental impact on marine wildlife. The Convention on Biological Diversity (CBD, 2012) estimated that over 80% of adverse environmental impacts on marine life are associated with plastic debris. It is important to build up information on the amount and characteristics of plastic debris that damage marine species to devise strategies and set priorities to reduce their adverse impacts on marine life. This study investigated plastic debris ingested by sea turtles stranded, floating, or by-captured from 2012 to 2022 in the Korean coastal waters. The quantity, shape, color, size, origin, and polymer type of plastic debris (> 1 mm) ingested by sea turtles were analyzed after being sorted from gastrointestinal (GI) tract of 71 turtles: 41 loggerheads, 24 greens, 3 leatherbacks, 2 olive ridleys, and 1 hawksbill turtle. We found a very high frequency of occurrence of plastic debris in GI tract of sea turtles; 100% for greens, 83% for loggerheads, 67% for leatherbacks, 50% for olive ridleys, and 100% for hawksbill. The overall amount of plastics were in the range of 0-1.31 g/kg turtle (0-229 pieces/turtle). The ingested debris tended to be films and fibers (> 74%), light in color (white and transparent; > 60%), and light polymers (polyethylene, polypropylene, polypropylene[poly(ethylene:propylene)], expanded polystyrene; > 90%). Single-use or fishery-related plastics such as filmed packaging, plastic bags, twine, net, and rope were frequently found. Some debris were labeled with Korean (n=14), Chinese (n=10), English (n=2), and Vietnamese (n=1). The shape and origin of ingested debris varied between loggerhead and green turtles. Green turtles ingested commonly fibers (47%) such as rope, twine, and net. Conversely, loggerheads ingested frequently films (45%) such as plastic bag, and packaging. The difference in ingested plastics between greens and loggerheads may be related to feeding habit and geographical range of movement of each species. This study implies that sea turtles inhabiting around the Korean waters are severely affected by marine plastic debris, and that waste management of single-use and fishery-related plastics should be the top priority to effectively reduce the adverse impact of plastic debris on sea turtles.

How to cite: Hong, S. H., Moon, Y., Han, G. M., Shim, W. J., Ha, S. Y., Kim, I.-H., and Lee, H.-R.: Quantification and characterizations of plastic debris ingested by sea turtles in Korean waters, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-5062, https://doi.org/10.5194/egusphere-egu23-5062, 2023.

14:35–14:45
|
EGU23-5893
|
Virtual presentation
Paula Núñez, Alessandro Romano, Javier García-Alba, Margot Sánchez, Andrés P. Mendoza, Ana J. Abascal, Andrés García, Cesar Vidal, Giovanni Besio, and Raúl Medina

Plastic debris is currently a significant threat to marine and coastal ecosystems. Most previous research focused on the behavior of drifting macro and mesoplastics on global and regional ocean scales. Furthermore, a few more recent studies provide some first insights into the microplastic dispersion in coastal areas. These studies found that waves and wind, as well as the density, size, and shape of microplastics, drive their transport and dispersion in coastal areas; however, they point to the need for a more extensive characterization. This laboratory study assesses the effect of waves and wave-induced currents on the input rate from land to sea and on the cross-shore transport and dispersion of different types of plastic debris, including the macro and mesosizes, in addition to microplastics. A total of 15 types of plastic debris characterized by different sizes, shapes, and densities, including face masks, were analyzed under regular and irregular wave conditions. The results show that the input rates and transport of plastic debris in the marine environment depend on the position they acquire in the water column, which is related to the terminal velocities and the wave steepness. A higher input rate from the beach was found for plastic materials moving closer to the sea bottom and under less steep wave conditions, as these conditions allow items to escape from coastal entrapment. Furthermore, greater onshore transport was observed for plastic debris that showed greater buoyancy under steeper wave conditions. Regarding the cross-shore distribution, the heaviest plastic debris that managed to be transported accumulated in the breaking zone, while the buoyant elements showed a predominant accumulation closer to the shoreline.

How to cite: Núñez, P., Romano, A., García-Alba, J., Sánchez, M., Mendoza, A. P., Abascal, A. J., García, A., Vidal, C., Besio, G., and Medina, R.: A laboratory experiment on the effect of waves on the transport and dispersion of macro, meso, and microplastics in the surf zone, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-5893, https://doi.org/10.5194/egusphere-egu23-5893, 2023.

14:45–14:55
|
EGU23-8189
|
On-site presentation
Jens Murawski, Jun She, and Vilnis Frishfelds

The assessment of microplastic pollution in the marine environment is a requirement for the evaluation of the present situation and development of efficient combatting strategies. In combination with model based transport assessments, the monitoring of microplastics provides a tool for the assessment of the overall budget for the entire Baltic Sea and sub-basins. Furthermore, monitoring data sets can be used to evaluate the model performance in capturing spatial and seasonal pattern of marine pollution. Currently, the scope of microplastic monitoring is quite limited, which is why it is an important issue to control the quality of the available datasets and to derive useful indicators from the available data. Our study of single source data sets, with improved error statistics compared to multi source data sets, shows that the mean sampling error is still relatively high, about 40%–56%, which has been estimated using replicate samples. The lack of surface flow correction when using mantra net or trawl methods introduces and additional 12% uncertainty. When compared to model data, additional uncertainties come into play, related to the model characterization of microplastics as a set of spherical particles with a given density and diameter, which differs fundamentally from the broad range of values occurring in nature. It is therefore important to derive useful indicators from the measured and monitored data sets before attempting to validate the model. In our presentation, we will detail the assessment of sampling errors and provide an overview over the extent of microplastic monitoring assessed in the CLAIM project for the Baltic Sea. The collected data set was used to evaluate the quality of DMI’s microplastic transport model in reproducing spatial and seasonal patterns. The database of the model-observation assessment covers the 6 years period 2014-2019, with regular monitoring data sets in the eastern Baltic Sea being available since 2016. Finally, we discuss recommendations that could help to reduce sampling errors and derive indicators that are useful for a quality assessment of microplastic models. Aim is the development of operational modelling and monitoring capabilities for marine microplastic pollution.  

How to cite: Murawski, J., She, J., and Frishfelds, V.: Microplastic monitoring and data quality assessment for effective model error evaluation, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-8189, https://doi.org/10.5194/egusphere-egu23-8189, 2023.

14:55–15:05
|
EGU23-8584
|
On-site presentation
Javier Soto-Navarro and Gabriel Jordà

The main problem of characterizing the spatial distribution and variability of the marine litter (ML) in seas and oceans is the scarcity of observations. ML sampling campaigns are usually concentrated near coastal regions and are carried out during spring – summer months, when the navigation conditions are more favorable.  As a result, the spatial and temporal resolution of the observations does not allow a statistically robust description of the ML average distribution and time evolution. Considering the limited resources and the high cost of the observation campaigns, developing an optimized sampling strategy is a key step to capitalize resources and obtain a robust ML characterization.

This study analyzes the temporal and spatial requirements that a sampling should fulfill to obtain accurate estimates of ML concentration in different areas of the Mediterranean Sea. Provided that there are not enough observations to define the underlying statistics of ML concentration we use the outputs of a realistic numerical model as a synthetic reality. Then, we conduct several Monte Carlo experiments simulating different sampling strategies on the model data to obtain the mean ML concentration in a certain region. The spread of values from the ensemble of Monte Carlo members is considered as the uncertainty associated to the estimated mean. Our results suggest that for the same number of observations (i.e. the same observational effort), is better to maintain long observational records rather than to intensify the sampling (i.e. reducing the sampling interval). If the spatial distribution of ML is aimed at, the required spatial density of the sampling depends on the characteristic correlation length scale. Therefore, those regions where the ML concentration structures are larger would require less dense observational samplings.

How to cite: Soto-Navarro, J. and Jordà, G.: Observations requirements for marine litter concentration characterization in the Mediterranean Sea, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-8584, https://doi.org/10.5194/egusphere-egu23-8584, 2023.

15:05–15:15
|
EGU23-10600
|
On-site presentation
Yu Lee Jang, Jongwook Jeong, Soeun Eo, Sang Hee Hong, and Won Joon Shim

Greywater drained from showers, washbasins, laundry, and dishwashers can be discharged to the sea without further treatment unless in no discharge zone. In 2021, International Maritime Organization indicated greywater generated from ships as one of the possible sources of sea-based microplastics. However, there are only a few studies on microplastics in greywater, most of which have used the scientific literature for statistical estimation of the amount of microplastics in cruise ships. It is necessary to evaluate the amount of microplastics in real ships’ greywater for accurate calculation of emission. This study aims to measure microplastics in a ship’s greywater by its usage and to estimate the preliminary global emission of microplastics from a ship’s greywater discharge into the ocean.

Greywater was collected in three different holding tanks at 5-day intervals from a research vessel Onnuri of Korea Institute of Ocean Science and Technology (1,370 tons) before and during the cruise for 18 days (April 21–May 9, 2022) with 33 persons on board. A total of 83 m3 of greywater was generated during the cruise. The average microplastic abundance was 135,563±87,141 n/m3 (range: 60,500–322,500 n/m3) in greywater. There were no significant differences in the abundance of microplastics in greywater usage (mainly galley, laundry and shower, and cabin washbasin). The level of microplastics in greywater in this study was several orders of magnitude higher than those in effluents from terrestrial wastewater treatment plants in the literature.

The greywater generation rate during navigation was 0.15 m3/person/day, which was comparable to previous studies with various types of ships. The greywater sub-flows accounted for 51%, 17%, and 32% of tank A (drained from the galley and 5 cabins with showers), tank B (18 cabins, 2 laboratory rooms, and 4 washbasins), and tank C (laundry, shower, and washbasin), respectively. The number of microplastic from total greywater was highest in tank C (44%), followed by tank A (29%) and tank B (18%). However, there was no difference in the number and mass of microplastics. The annual microplastic load in greywater from R/V Onnuri was estimated to be 1.2ⅹ108 n/year or 91 g/year. Based on the greywater microplastic emission factor abundance in this study, it is estimated that about 28ⅹ1012 particles or 13–29 tons of microplastics could enter the global oceans from greywater of global fleets (>100 gross tonnages) in a year.

How to cite: Jang, Y. L., Jeong, J., Eo, S., Hong, S. H., and Shim, W. J.: Assessment of Microplastic Abundance and Discharge from Greywater of Ships, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-10600, https://doi.org/10.5194/egusphere-egu23-10600, 2023.

15:15–15:25
|
EGU23-11162
|
ECS
|
On-site presentation
Claudio Pierard and Erik van Sebille

During an expedition in January 2020, nanoplastics were sampled at a depth of -5170m over Cape Basin in the South Atlantic Ocean. Using photo-induced force microscopy, it was identified that these were polyethylene terephthalate (PET) particles with an approximate diameter of 50 nm at different stages of degradation. Using a state-of-the-art Lagrangian 3D simulation that includes an idealized fragmentation scheme, we backtracked virtual particles from the sampling location to establish the possible origins of the PET nanoplastics. We performed several simulations with different fragmenting timescales, for 13 years from the date of sampling, using the GLO12V3R1 hydrodynamic data from Copernicus Marine Environment Monitoring Service. We found that the nanoparticles (smaller than 1μm) could not have fragmented into nanoplastics at the surface and reached the sampling location within 13 years. The most likely scenario is that these particles started to sink from the surface as microplastics (larger than 1μm) and then fragmented in the water column far from the surface. This suggests that the fragmentation happened through processes like slow thermal oxidative degradation or hydrolysis and not photodegradation. We also found that less than 0.2% of the virtual particles came from the coast and that the fragmentation timescale prescribed to the modelled particles, affects how they drift in the ocean by controlling the time they drift at different depths. This study contributes to understanding the fate and sources of nanoplastics suspended deep in the ocean.

How to cite: Pierard, C. and van Sebille, E.: Identifying the Origins of PET Nanoplastics in the Abyssal South Atlantic Using Backtracking Lagrangian Simulations with Fragmentation, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-11162, https://doi.org/10.5194/egusphere-egu23-11162, 2023.

15:25–15:35
|
EGU23-11835
|
On-site presentation
Emmanuel Hanert, Essam Heggy, Thomas Dobbelaere, and Thomas Anselain

More than 20% of global liquefied natural gas (LNG) exports and almost all of Qatar’s drinking water production originate from three industrial sites within a few tens of kilometers on the eastern coast of Qatar’s peninsula. However, with the observed regional increase in maritime transport accidents, the vulnerability of those sites to major oil spills remains largely unquantified, let alone understood, due to complexities in forecasting and containing pollution in such shallow waters and harsh hyper-arid environments. To address this deficiency, we model the oil spill dispersal in the shallow maritime waters surrounding Qatar’s peninsula to identify which offshore areas and times of the year pose the most significant threat to both LNG export and seawater desalination facilities. By combining the outcome of our oil transport simulations with marine traffic data, we identify two high-risk areas, sizing up to ~15% of Qatar’s maritime exclusive economic zone, where the elevated oil pollution exposure is concentrated and can cause major disruptions to the above facilities. Our results suggest that the major LNG liquefaction terminal of Ras Laffan has the highest vulnerability to oil spills among all studied sites all year long. Moreover, the desalination plant to the North of Ras Laffan, producing 30% of the national water supply, has a seasonal vulnerability peaking up to an alarming level twice a year during spring and fall. The two other desalination plants located southeast of the peninsula have a lower vulnerability all year long. Furthermore, both LNG export and desalination facilities are found to be highly vulnerable to oil spills occurring outside of Qatar’s maritime borders, which could land in these vital infrastructures in less than two days. These delays are further reduced when considering the spill's arrival time near coastal waters shallower than 5 m depth, which are inaccessible to several large containment vessels. Therefore, we suggest that those two offshore high-risk areas be closely monitored with airborne and orbital SAR observations, providing early warning for oil spills that can severely disrupt the LNG exports from Ras Laffan, further aggravating the global gas crisis.

Reference:
Anselain T., E. Heggy, T. Dobbbelaere and E. Hanert (2023) Qatar Peninsula’s vulnerability to oil spills and its implications for the global gas supply, Nature Sustainability, in press, https://www.nature.com/articles/s41893-022-01037-w 

How to cite: Hanert, E., Heggy, E., Dobbelaere, T., and Anselain, T.: Qatar Peninsula's vulnerability to oil spills and its implications for the global gas supply, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-11835, https://doi.org/10.5194/egusphere-egu23-11835, 2023.

15:35–15:45
|
EGU23-16932
|
On-site presentation
Jonathan Raphael, Jason Schatz, and Ryan Avery

SkyTruth has created a fully automated system to detect anthropogenic oil pollution across the world’s oceans in near-real-time using Sentinel-1 data. This system is called Cerulean and is designed to provide environmental organizations, researchers, governments, journalists, and other users with a global monitoring and reporting system for oil pollution.

Synthetic Aperture Radar (SAR) data is commonly used to remotely sense the presence of oil on the surface of the ocean. However, SAR based oil slick detection is prone to false positives caused by wind shadows, sea ice, organic surfactants on the water surface, and other phenomena that cause look-alike dark patches in SAR data. We have taken a three tiered approach to reducing false positive detections from our oil slick detection model: (1) Providing a significant number of false-positive look-alikes in our training dataset, (2) Experimenting with different classes of deep learning model architectures, including a U-Net semantic segmentation model and a Mask R-CNN object segmentation model, (3) Leveraging various post-processing techniques to help distinguish true positives from false positives, including morphological characteristics of slicks, proximity to shipping lanes and offshore infrastructure, and weather data. Results of these analyses and promising avenues for improving oil slick discrimination with SAR data will be described in detail.

How to cite: Raphael, J., Schatz, J., and Avery, R.: Improving the accuracy of SAR-based oil slick detection, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-16932, https://doi.org/10.5194/egusphere-egu23-16932, 2023.

Posters on site: Thu, 27 Apr, 10:45–12:30 | Hall X5

Chairpersons: Giovanni Coppini, Katerina Spanoudaki
X5.307
|
EGU23-11561
Katerina Spanoudaki, George Kozyrakis, Vassiliki Metheniti, Antonios Parasyris, and Nikos Kampanis

The world’s oceans have been studied and monitored for many decades to enhance our understanding. In today’s world, with the explosion of new data provided by many different Earth observation sources and the availability of advanced computing infrastructures (cloud computing, HPC, IoT, Big Data), creating a digital representation of the ocean is becoming a reality. The EC recently funded the H2020 ILIAD project, which aims at establishing an interoperable, data-intensive Digital Twin of the Ocean (DTO). The ILIAD DTO will integrate real-time sensing of ocean variables, state-of-the-art high-resolution models, modern data analytics and digital infrastructures to create virtual representations of physical processes and understand their behaviour, anticipating and predicting their response to simulated events and future changes. ILIAD will enable an ecosystem of interoperable DTOs, integrating the plethora of existing EU Earth Observing and Modelling Digital Infrastructures. It will fuse a large volume of diverse data and will enhance ocean data infrastructures with additional observation technologies and citizen science.  ILIAD will provide a virtual environment representing the ocean, capable of running predictive management scenarios and will utilize Big Data analytics for forecasting of spatiotemporal events and pattern recognition. Several DT pilots will be undertaken in several key thematic areas such as offshore wind energy, wave and tidal energy, biodiversity assessments, marine pollution and more. 

The current work presents ongoing activities for a coastal, high-resolution Digital Twin pilot for Cretan Sea, to be demonstrated in the frame of ILIAD project. The pilot focuses on oil spill pollution monitoring and forecasting. The DT environment combines high-resolution forecasting services based on numerical weather (WRF), hydrodynamic (NEMO), sea state (WAVEWATCH III) and particle tracking models (MEDSLIK-II), enhanced by the integration of  Sentinel data and real-time observations from novel, low cost current and waves meters, drifting trackers, as well as citizen science. WRF model is applied for forecasting of meteorological variables at  ̴ 3 km resolution by dynamic downscaling of coarser resolution climatic modelling forecast data (NOAA’s GFS). This way, higher computational accuracy is achieved over Cretan Sea, thus revealing finer wind scales phenomena. The downscaled weather forecasting data are used to force NEMO and WAVEWATCH III, to obtain high-resolution forecasts of important marine parameters, such as sea currents, temperature, salinity and waves over a fine grid of   ̴ 1 km for the coastal area of Crete. For oil spills, the DT of Cretan Sea will integrate operational analysis of Sentine-1 images, triggering MEDSLIK-II oil spill model once an oil spill event or anomaly is identified. Adjusting forecasts to observations by reinitialising the model with updated observational patterns will contribute to the forecast error growth being implicitly accounted for and minimized. The pilot DT virtual environment will allow on-demand simulations of predictive scenarios of oil spill events and response strategies.  

The aim of the Digital Twin is to aid the immediate response in case of accidental oil releases, minimize the damage and reduce the time for environmental recovery.

Acknowledgement: This research has received funding from the European Union’s H2020 RIA programme under GA No 101037643.

How to cite: Spanoudaki, K., Kozyrakis, G., Metheniti, V., Parasyris, A., and Kampanis, N.: The Cretan Sea oil spill Digital Twin pilot for the ILIAD Digital Twin of the Ocean, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-11561, https://doi.org/10.5194/egusphere-egu23-11561, 2023.

X5.308
|
EGU23-1573
|
ECS
Panagiota Keramea, Nikolaos Kokkos, George Zodiatis, Georgios Sylaios, Giovanni Coppini, Juan Peña, Pablo Benjumeda Herreros, Antonio Augusto Sepp-Neves, Robin Lardner, Svitlana Liubartseva, Dmitry Soloviev, Matteo Scuro, Andreas Nicolaidis, and Fabio Viola

Oil spills in the marine field can have serious consequences for ecosystems, the environment, public health, the economy, and communities. Thus, following the spillage of 12,000 tons of crude oil from the fuel tanks of the Baniyas power plant in summer 2021, daily operational oil spill predictions were carried out  to predict the spill transport and fate in the Levantine basin, Eastern Mediterranean, supporting the Regional Marine Pollution Emergency Response Centre for the Mediterranean  (REMPEC) and national response agencies. High frequency met-ocean forecasting data from the Copernicus Marine Monitoring Service (CMEMS), the European Centre for Medium-Range Weather Forecasts (ECMWF), and regional models (SKIRON, CYCOFOS) were used, along with satellite-derived SAR data from EMSA-CSN and optical images from ESA to initiate the oil spill models and to determine the evolution, the extent and coverage of the spillages. Two up-to-date and advanced Lagrangian particle-tracking models, OpenDrift and MEDSLIK were used to assess and evaluate the oil spill predictions, generated by the aforementioned models, under a variety of met-ocean forcings and configurations, indicating the significant role of the high-resolution met-ocean data in the evolution of the oil spill trajectory. A number of quantitative metrics were used to evaluate the ability to adequately reproduce the oil spill spreading, by comparing the SAR observed oil spillages against the models results, in more detail.

How to cite: Keramea, P., Kokkos, N., Zodiatis, G., Sylaios, G., Coppini, G., Peña, J., Benjumeda Herreros, P., Sepp-Neves, A. A., Lardner, R., Liubartseva, S., Soloviev, D., Scuro, M., Nicolaidis, A., and Viola, F.: Oil spill modeling assessment of the 2021 Syrian oil spill using SAR imagery and multi-forcing forecasts, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-1573, https://doi.org/10.5194/egusphere-egu23-1573, 2023.

X5.309
|
EGU23-2235
Svitlana Liubartseva, Giovanni Coppini, Giuseppe Verdiani, Teresa Mungari, Francesco Ronco, Mariantonietta Pinto, Giusi Pastore, and Rita Lecci

In the present work, we focus on chronic oil pollution from ships since even small amount of toxic oil compounds has immediate adverse biological effects. Moreover, routinely released hydrocarbons tend to cumulatively exceed volumes of the largest historical oil spills.

We perform stochastic simulations of virtual oil spills from ships in the Adriatic 2017–2020 applying the EMODnet vessel densities as a proxy for starting locations. MEDSLIK-II oil spill model is run using the high resolution (1/24 degree) currents and sea surface temperature provided by the Copernicus Marine Service and the ECMWF winds with a horizontal resolution of 1/8 degree.

Chronic exposure to operational oil spills is reported in terms of hazard indices for 5 vessel groups: (1) the pleasure and passenger ships that comprise ~47.2% of the total number of ships in the model domain; (2) cargo and service vessels with a contribution of ~24.2%; (3) fishing fleet with ~21.5%; (4) tankers with ~5.9%; and (5) remaining ships with ~1.2%.

The highest hazard indices from all ships are found in the northernmost part of the basin and along the coastlines of Italy, Croatia, and Slovenia. Near several major ports (Trieste, Koper, Venice, Split, Rijeka, Pescara, Brindisi, Durres, Zadar, Šibenik, and Dubrovnik), they are also elevated at the sea surface and on the coastlines. Conversely, the southern Adriatic exhibited the lowest values of hazard indices.

Comparative analysis of the integrals over the territorial waters of Italy and Croatia shows that the Croatian coastal waters are more chronically polluted than the Italian ones, despite their host less ships than the coastal waters of Italy. The reason for such an inconsistency is probably related to the differences in efficiency of circulation when the pollution from ships quickly dissipates along the Italia coast and tends to stagnate near the Croatian coast. Cargo and service ships are identified to be the main polluters in the Italian coastal waters. While in the Croatian coastal waters, most of the oil is received from the pleasure and passenger ships, particularly, from coastwise shipping. Offshore waters are found to be significantly less polluted than the coastal ones, with the main contribution from fishing, cargo and service vessels.

The results obtained can be considered representative of future events since the vessel density distribution and the amount of oil operationally spilled are assumed to be typical of the present state and not to change dramatically in the future. The historical meteo-oceanographic datasets 2017–2020 used are supposed to correspond to a realistic sample of possible weather and sea state conditions. The hazard indices computed can be used to improve the strategy of satellite and aerial surveillance, in-situ sampling, and ecotoxicological research in the Adriatic.

The presentation summarizes the results obtained in the framework of the FIRESPILL Project (Fostering Improved Reaction of cross-border Emergency Services and Prevention Increasing safety LeveL) funded under the Interreg V-A Italy-Croatia CBC 2014–2020 Programme (AP2–Security and Resilience).

How to cite: Liubartseva, S., Coppini, G., Verdiani, G., Mungari, T., Ronco, F., Pinto, M., Pastore, G., and Lecci, R.: Modeling the operational oil spills from shipping in the Adriatic Sea, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-2235, https://doi.org/10.5194/egusphere-egu23-2235, 2023.

X5.310
|
EGU23-5089
|
ECS
|
Anastasia Angela Biancardi, Enrico Zambianchi, Giovanni Coppini, and Svitlana Liubartseva

Starting our work on model-based coupling microplastic (MP) and the low-trophic level marine biota, we present a contemporary overview of existing models, both the Lagrangian and Eulerian ones.

MP biofouling has been modeled by Kooi et al. (2017), who develop a 1D Lagrangian model to describe size- and density specific vertical motion of MP. They have found that

  • Denser particles settle sooner than the less dense particles when they have the same size.
  • The settling velocity decreases with decreasing particle size.
  • MP particle can oscillate due its buoyancy controlled by biofouling. MP density is balanced by the source-and-sink terms in a biofouling equation for algae attached to the MP surface.
  • Oscillation periods increase with decreasing particle size.

 

Lobelle et al. (2021) improve the Kooi et al. (2017) model developing a 3D Lagrangian model with horizontal and vertical advection. They consider a global distribution of MP of different size and density and note that the timescale is largely size-dependent as opposed to density dependent.

Finally, Fischer et al. (2022) modify the physics part of the model by Lobelle et al. (2021), focusing on the vertical movement, both vertical advection and vertical turbulence diffusion. Additionally, they add two loss terms in the biofouling equation. They conclude that the vertical movement of particles is mainly affected by wind induced mixing within the upper mixed layer and by biofilm dynamics in the deep ocean.

Biofouling as a possible mechanism of the MP removal from the surface has been incorporated into a 3D Lagrangian model for 6 size classes of MP (Tsiaras et al., 2021). In the water column, a sub-surface maximum in MP abundance is obtained, with increasing contribution of smaller particles in deep layers.

MP has been embedded in a biogeochemical 3D Euler model by Kvale et al. (2020), who consider the processes of MP aggregation in sinking marine snow and faecal pellets in the global ocean. In the subsequent work (Kvale, 2022), a two-way coupling developed in the model allows finding a way of the MP influence on global marine carbon cycling and climate.

Biofouling, the MP transport by marine snow and fecal pellets have been simulated by Berezina et al. (2021), who incorporate MP into a biogeochemical 2D Euler model with translational symmetry. They reveal that the so-called “biological pump” (or vertical transport of MP by marine snow and fecal pellets) can be one of the important drivers controlling the distribution of MP in the water column and bottom sediments in the Oslo Fjord.

A new Lagrangian model that we plan to implement in the future will help to advance our understanding of biota-mediated processes in MP transport and fate in the Mediterranean Sea.

How to cite: Biancardi, A. A., Zambianchi, E., Coppini, G., and Liubartseva, S.: State-of-the-art modeling the interaction between microplastic and the low-trophic level marine biota, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-5089, https://doi.org/10.5194/egusphere-egu23-5089, 2023.

X5.311
|
EGU23-13780
Thierry Huck, Raphaël Bajon, Nicolas Grima, Christophe Maes, Bruno Blanke, Camille Richon, and Xavier Couvelard

The world's oceans are confronted with plastic pollution, 80% of which is of terrestrial origin, flowing mainly from the mismanaged waste of coastal populations and to a less extent, from river discharge. To study the fate of this pollution, we follow the trajectories of neutral plastic particles released continuously in numerical ocean simulations with two realistic source scenarios defined according to poorly managed waste from coastal populations and river discharge. The trajectories are three-dimensional and calculated for a period of 24 years by the Ariane Lagrangian tool from ocean currents simulated by a ¼° global ocean general circulation model (NEMO). The important particularity of the present model is that it is coupled with the WaveWatch III (WW3) wave model and consequently represents the Stokes drift in a consistent manner. The results are compared to trajectories calculated with an uncoupled NEMO simulation in which the Stokes drift is simply not considered. The results show that microplastics (as neutral particles) accumulate at the surface in the subtropical convergence zones of the Ekman transport before penetrating to depth and being strongly dispersed around 200 to 300 m depth over 40 degrees of latitude. At the end of the simulation, about 5.3% of the microplastics remains at the surface in these convergence zones and near the emission regions for the wave-coupled model, whereas only 2% remains for the uncoupled model. Our results indicate that waves may increase the retention of neutral plastic particles at the surface by a factor of two to three because of the upward vertical velocities induced by the divergence of Stokes transport in the surface layers. Plastic surface concentrations are maximal in the North Pacific and Indian Ocean basins. This result is due to the large discharge fluxes surrounding these basins of the northern hemisphere. The Mediterranean Sea exhibits also highly concentrations in microplastics due to high coastal population densities. This work shows the strong influence of waves (and Stokes drift) on the transport of plastic particles in the oceans, both on the retention of particles at the surface, the importance and location of convergence zones, and on the dispersion of neutral plastics at depth.

How to cite: Huck, T., Bajon, R., Grima, N., Maes, C., Blanke, B., Richon, C., and Couvelard, X.: Influence of waves on the three-dimensional distribution of plastic in the ocean, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-13780, https://doi.org/10.5194/egusphere-egu23-13780, 2023.

X5.312
|
EGU23-10694
|
ECS
Jongwook Jeong, Yu Lee Jang, Soeun Eo, Sang Hee Hong, and Won Joon Shim

Marine microplastics are a global environmental issue. However, there are still large data and knowledge gaps in microplastics from sea-based sources. One of the concerned sea-based microplastic sources is ships' greywater discharge. Greywater generated from galley, laundries, showers, and washbasins in a ship can be discharged directly to the sea without treatment. In this study, we present the sampling approach of greywater and information about the abundance and characteristics of microplastics. To our knowledge, it is the first attempt to determine microplastic abundance and characteristics in ships' greywater according to its use categories (galley, laundry and shower, and cabin washbasin). Greywater samples were collected from three different holding tanks (tanks A, B, and C) at R/V Onnuri of Korea Institute of Ocean Science and Technology (KIOST). To enable the sample collection, the discharge system was converted to manual discharge and an additional pump and valve were installed on the pipeline connected to each tank. Greywater was sampled when the vessel was at anchor (1st sample) and during the research cruise (2nd sample). For the 1st sample, a grab sampling was conducted and for the 2nd sample, samples were collected at 5-day intervals. Semi-automated FTIR analysis was conducted for microplastic identification. During the analysis, fiber bundles composed of polyester (PES) and polypropylene (PP) were detected. Bundles were counted as one individual particle or composing particles were counted individually, if possible. The highest microplastic abundance was found in tank C from the laundry and shower room in which a large number of microfibers such as PES fibers were detected. The average microplastic abundances were 149,660±77,574 n/m3 (62,000–209,600 n/m3) in 1st sample and 135,563±87,141 n/m3 (75,000–177,667 n/m3) in 2nd sample. The microplastic abundances were similar and this can be attributed to the fact that people use the ship's facilities where greywater can be generated even while at anchor. In addition, not only the generation of microplastics but also greywater could be large during navigation. Though the microplastic abundances were similar in 1st and 2nd samples, a greater variety of polymers were detected in 2nd sample (25 types) than in 1st sample (15 types). Polymers used in paint were also highly detected in the 2nd sample (8%) than in the 1st sample (2%). This might be due to more diverse activities took place on the deck and inside the ship during the research activity than when at anchor. Fibers were more dominant in 2nd sample (66%) than in 1st sample (25%). This may be because more people use washing machines while sailing than at anchor. In addition, since many cabins are occupied during the research cruise than when at anchor, washing in cabins and fibers detached from fabrics from people’s activity during navigation might have contributed to relatively higher PES fiber composition in 2nd sample. The results of this study would be useful in understanding the sea-based microplastic pollution through ship’s greywater, and for estimation of the microplastic emission from ships to the marine environment.

How to cite: Jeong, J., Jang, Y. L., Eo, S., Hong, S. H., and Shim, W. J.: Occurrence and Characteristics of Microplastics in in a Ship’s Greywater According to Usage Patterns, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-10694, https://doi.org/10.5194/egusphere-egu23-10694, 2023.

X5.313
|
EGU23-13936
|
ECS
Bradley Reed, Peter Robins, Jonathan Demmer, and Simon Neill

Marine plastic pollution is one of the most visible environmental problems in and around the coastal regions of South East Asia. To fully address the marine plastic pollution problem, there must be a source-to-sink approach, reducing litter at each stage of its pathway to the open ocean. Mangroves are an important and widespread ecosystem in South East Asia on the interface between terrestrial and marine environments, and a key habitat and nursery for a number of species. Mangroves have also been reported to trap plastic litter, potentially acting as secondary sources to coastal marine environments. The Philippines are particularly vulnerable to compound hydrological events due to the seasonal monsoon and typhoons which regularly cross the region. South East Asia is a complex region oceanographically and hydrologically with high loads of plastic litter being exported into the regional seas. To correctly estimate local plastic pollution budgets and understand the transboundary movement of plastic from land to sea, modelling studies must account for the different environmental drivers and strong seasonality of the region. 

Here, we present preliminary results of a modelling study investigating the impact of Typhoon Rai on the retention and contribution of plastic litter by mangrove ecosystems of Cebu Island, the Philippines. The results of a three-dimensional, hydrodynamic model (ROMS) with wind, tidal and wave forcing will be presented. Future plans to apply a Lagrangian particle tracking model informed by in-situ measurements to investigate the behaviour of plastic litter within this typhoon weather system will also be outlined. 

This will help to understand how plastic litter is retained or exported during extreme events around Cebu Island and assess the likelihood of mangroves to act like a temporary sink or secondary source during extreme and mean events. Understanding the role of mangroves under different environmental conditions could clarify another step in the source-pathway-sink model of plastic litter in the region. 

How to cite: Reed, B., Robins, P., Demmer, J., and Neill, S.: Do mangroves act as a secondary source of plastic during extreme events?, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-13936, https://doi.org/10.5194/egusphere-egu23-13936, 2023.

X5.314
|
EGU23-2333
|
ECS
|
Noam Vogt-Vincent, April Burt, David Kaplan, Satoshi Mitarai, Lindsay Turnbull, and Helen Johnson

Vast quantities of debris are beaching at remote islands in the western Indian Ocean, despite minimal or zero local sources of pollution. We carry out marine dispersal simulations, informed by observations, incorporating currents, waves, winds, beaching, and sinking, for both terrestrial and marine sources of debris, to predict where this debris comes from. Our results show that most terrestrial debris beaching at these remote western Indian Ocean islands drifts from Indonesia, India, and Sri Lanka, although we also find evidence that a large fraction of bottles polluting these islands may have been discarded from fishing vessels and ships transiting the Indian Ocean. Abandoned, lost or otherwise discarded fishing gear (ALDFG) associated with purse-seine fisheries likely originates from within the western Indian Ocean, but ALDFG from longline fisheries may be sourced from further afield. Debris accumulation rates at Seychelles are likely seasonal, peaking during February-April. This pattern is driven by monsoonal winds and may be amplified during positive Indian Ocean Dipole and El-Nino events. We make suggestions for future beach clean-up operations, and also recommend that observational campaigns intending to identify sources of debris accumulating at remote islands should either target beaches that are not subject to regular clean-ups, or monitor accumulation over multiple years. Our results underline the vulnerability of small island states to marine plastic pollution, and are a crucial step towards improved management of the issue. The trajectories used in this study are available for download, and our analyses can be rerun under different parameter choices.

How to cite: Vogt-Vincent, N., Burt, A., Kaplan, D., Mitarai, S., Turnbull, L., and Johnson, H.: Sources of marine debris for Seychelles and other remote islands in the western Indian Ocean, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-2333, https://doi.org/10.5194/egusphere-egu23-2333, 2023.

X5.315
|
EGU23-2815
Tran Vu La, Ramona-Maria Pelich, Marco Chini, Yu Li, and Patrick Matgen

Over the last ten years, satellite imagery has become one of the most effective means to observe offshore oil spills, especially over a large area, thanks to their high spatial resolution and wide swath coverage. In particular, the use of images acquired by multi-sensors, including Synthetic Aperture Radar (SAR), optical, and visible/near-infrared, allows not only to early and quickly detect oil spills but also to monitor oil drift in short-terms (several hours) and long-terms (one or two days). Such approach has not been assessed in-depth in previous studies probably due to the lack of satellite data. A case study was presented in [1] to observe the movement of oil slicks through the combination of data acquired by SAR satellites, SAR airborne system, optical instrument, and in-situ observations. However, it is very complicated to implement such method for the other cases of oil spills since it requires many different platforms and sensors that are not systematically available. Therefore, this paper focuses uniquely on the collocation of sequential images acquired by various satellite sensors (SAR and optical) for oil drift monitoring in short-terms (several hours) and long-terms (up to 24–36 hours).

For instance, to observe oil spills caused by a wrecked ship offshore Corsica (France) in Oct. 2018, we combine the images acquired by Sentinel-1 SAR (Oct. 8, 2018, 05:27:57 UTC, 17:21:45 UTC; Oct. 9, 2018, 17:14:27 UTC), Sentinel-2 optical sensor (Oct. 9, 2018, 10:20:21 UTC), and Radarsat-2 SAR (Oct. 9, 2018, 04:04:15 UTC). The techniques of oil spill detection from SAR and optical images are different. They are based on an advanced image processing procedure that will be presented at the conference. Due to the time lags between these images, we can estimate the movement of the detected oil slicks in terms of distance, velocity, and direction for 6, 12, 24, 36 hours of observation. Finally, we compare the oil drift results with the hourly data of met-ocean variables (surface wind and current) to assess the impact of the latter on oil drift. Surface wind fields (0.25° × 0.25° grid) and current vectors (0.083° × 0.083° grid) are extracted from the ERA-5 [2] and CMEMS [3] reanalysis data, respectively.

[1] C. Brekke, M. M. Espeseth, K.-F. Dagestad, J. Röhrs, L. R. Hole, and A. Reigber, “Integrated analysis of multisensor datasets and oil drift simulations—a free-floating oil experiment in the open ocean,” J. of Geophysical Research: Oceans, vol. 126, e2020JC016499, 2021, doi: 10.1029/2020JC016499.

[2] H. Hersbach et al., “ERA5 hourly data on single levels from 1959 to present,” Copernicus Climate Change Service (C3S) Climate Data Store (CDS). (Accessed on <05-12-2022>), 10.24381/cds.adbb2d47, 2018.

[3] Global Ocean 1/12° Physics Analysis and Forecast updated Daily (Accessed on <05-12-2022>), doi: 10.48670/moi-00016.

How to cite: La, T. V., Pelich, R.-M., Chini, M., Li, Y., and Matgen, P.: Making use of multi-sensor satellite imagery for oil spill observation and oil drift monitoring, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-2815, https://doi.org/10.5194/egusphere-egu23-2815, 2023.

X5.316
|
EGU23-7580
|
ECS
|
Nia Jones, Peter Robins, and Simon Neill

Oceanic and coastal fronts are well-documented as accumulators of microplastic debris; however the impact of estuarine fronts and their associated secondary flows on microplastic concentrations are less well-known. An investigation into the dynamics of microplastic behaviour within estuarine systems will allow for a greater understanding of plastic retention and exportation to coastal and offshore environments. This study combines high resolution modelling of estuarine processes with realistically parameterized microplastic particles to determine local exposure levels, residence times and temporal variability. 

We present a validated, three-dimensional, D-Flow Flexible mesh (D-Flow FM) model of a well-mixed estuary (Conwy Estuary, Wales, UK), demonstrating the regular development of an axial convergent front following high tide. A Lagrangian particle tracking model has been applied to simulate the behaviour of microplastic in these frontal systems and analyse how this behaviour may change as a response to various river discharge levels and tidal phases. The results of the ocean model and Lagrangian particle tracking model will be presented. 

Understanding how estuarine fronts impact microplastic concentration and dispersal within estuaries will increase the accuracy of modelling and in-situ estuarine microplastic studies alike, helping to quantify the contribution of well-mixed estuaries to regional and global microplastic budgets, and bridging the gap between terrestrial and marine environments.

How to cite: Jones, N., Robins, P., and Neill, S.: Simulating the impact of estuarine fronts on microplastic concentrations in well-mixed estuaries, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-7580, https://doi.org/10.5194/egusphere-egu23-7580, 2023.

X5.317
|
EGU23-9817
|
ECS
Modeling the influence of biogeochemical processes on the transport of microplastics in the Arctic Ocean
(withdrawn)
Anfisa Berezina, Evgeniy Yakushev, Philip Wallhead, and André Staalstrøm
X5.318
|
EGU23-15119
Guttorm Alendal, Jerry Blackford, Stefan Carpentier, Dorothy J. Dankel, Marius Dewar, Sufyan El Droubi, Bjarte Fagerås, Sarah E. Gasda, Anna Olyenik, Abdirahman Omar, Rajesh Pawar, Katherine Romanak, Darren Snee, Sigrid E. Schütz, and Parisa Torabi

Formulating appropriate monitoring programs for offshore geological CO2 storage projects, from either a regulatory or operator viewpoint, is difficult to achieve without a properly quantified cost-benefit analysis of what that monitoring could and should achieve. In addition, communicating risks and uncertainties is a challenge for offshore storage projects, and tools assisting in dialogue with stakeholders, governments and public at large will be of value.   

The monitoring programs will have a role in communicating risks and benefits for storage projects and assure against unjustified accusations for having adverse environmental effects but cannot be seen in isolation from the multi-leveled CCUS (Carbon Capture, Usage and Storage) management systems. 

Evaluations of CO2 storage monitoring techniques usually aim to determine the suitability to user‐defined project scenario (e.g., IEAGHG monitoring selection tool, https://ieaghg.org/ccs-resources/monitoring-selection-tool) or to assess the availability of sensors that can measure variables that are likely to fluctuate under a seepage scenario, or processes that are sensitive to CO2-related stress. Less focus has been on how they perform relative to regulatory requirements, cost efficiency, and user friendliness.  

We can use observations and models to characterise the natural variability of the marine system, or the noise from which an anomalous signal must be detected. We can use models to simulate hypothetical leak events thereby defining the monitoring target(s). We have algorithms that assess the cost-benefit of a range of anomaly criteria – i.e., a signal that would provoke a more concerted monitoring campaign and finally algorithms that can derive the optimal deployment strategy – i.e., where to monitor and when. The challenge is to collate these abilities into a coherent whole, which then allows the presentation of an evaluated monitoring system that can be judged against regulatory and societal expectations. 

We outline the approach chosen in the ACTOM project (https://actom.w.uib.no) to develop procedures for design and execution of appropriate, rigorous, and cost-effective monitoring of offshore carbon storage, aligning industrial, societal, and regulative expectations with technological capabilities and limitations. 

The ACTOM toolbox is capable of simulating “what if” seep scenarios, as well as monitoring deployments, that can be used to deliver environmental impact assessments as required under the CCS (Carbon Capture and Storage) and EIA directives. As a result, recommended monitoring strategies could be delivered autonomously and be dependent on established generic operational marine simulation models, both factors reducing costs.  

We will demonstrate use of the toolbox on three sites in the Gulf of Mexico, in southern North Sea and off the coast of Norway, each with distinctive features and availability of data.  

How to cite: Alendal, G., Blackford, J., Carpentier, S., Dankel, D. J., Dewar, M., El Droubi, S., Fagerås, B., Gasda, S. E., Olyenik, A., Omar, A., Pawar, R., Romanak, K., Snee, D., Schütz, S. E., and Torabi, P.: Assurance offshore CO2 monitoring, a cross-disciplinary approach., EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-15119, https://doi.org/10.5194/egusphere-egu23-15119, 2023.

X5.319
|
EGU23-15139
|
ECS
Enriko Siht, Arun Mishra, Germo Väli, Natalja Buhhalko, Taavi Liblik, and Urmas Lips

In this study, we conduct numerical simulations to investigate the transport and accumulation of microplastics (MPs) in the Gulf of Finland (eastern Baltic Sea). The transport of MPs is simulated using a Lagrangian particle tracking model, developed by the authors, which accounts for the physical transport and transformational processes specific to MPs, such as diffusion, beaching, resuspension, and biofouling.

Positively and negatively buoyant particles were included to represent different types of MPs. High-resolution (250 m) 3D hydrodynamic and biogeochemical model data are used as input to the MPs model. Major rivers and wastewater treatment plants around the Gulf of Finland are the sources of MPs in the model.

The main objectives of the study are 1) to perform a sensitivity analysis of four processes (beaching, mixing, resuspension, and biofouling) to investigate the importance of each process on the distribution of MPs in the Gulf of Finland; and 2) to execute a multi-year simulation using realistic MPs input to locate the main accumulation areas in sediments and beaches around the Gulf of Finland.

Results of the initial sensitivity analysis indicate that the changes in the parametrization of beaching have a stronger effect on the horizontal distribution of MPs in off-shore sediments than the changes in the parametrization of resuspension. The maximum MPs concentration is observed near the sea surface; however, MPs have also spread into the water column.

How to cite: Siht, E., Mishra, A., Väli, G., Buhhalko, N., Liblik, T., and Lips, U.: Modeling the transport and accumulation of microplastics in the Gulf of Finland, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-15139, https://doi.org/10.5194/egusphere-egu23-15139, 2023.

X5.320
|
EGU23-16357
An exploratory approach to establish baselines and threshold levels for the assessment of floating marine litter in the Black Sea region
(withdrawn)
Daniel González-Fernández, Josué Viejo Marín, Rocío Quintana Sepúlveda, Lucía Pérez-López, and Sandra Manzano-Medina
X5.321
|
EGU23-5971
|
ECS
|
Daniel R Wilson, Katy L Sheen, James R Clark, Sally E Thorpe, and Emma F Young

Microplastic pollution is a ubiquitous marine environmental contaminant that is found in all the world’s oceans. The Southern Ocean is not exempt from microplastic pollution, with numerous studies reporting microplastics to be present in the region, including south of the Antarctic Circumpolar Current (ACC). However, the challenges involved in collecting data on microplastic pollution in the Southern Ocean mean there are large areas of the Southern Ocean where microplastic pollution levels are largely unknown. In addition, the processes and resulting transport pathways that move microplastic pollution across the ACC into the highly sensitive Antarctic marine ecosystem are not yet well understood.

To tackle these knowledge gaps, we use a modelling approach to simulate the transport pathways of microplastic in the Southern Ocean, with a specific focus on cross-ACC transport. Specifically, we use the Lagrangian particle tracking framework OceanParcels, forced with ocean velocity fields from a Southern Ocean configuration of NEMO-LIM3 with 1/12॰ horizontal resolution. This model set up, which includes the effect of Stokes drift and sub-grid scale diffusion alongside underlying ocean currents, has allowed us to identify key regions where surface microplastic pollution may cross the ACC and potential hotspots of microplastic accumulation along the Antarctic coastline. We describe seasonal and inter-annual variability in microplastic transport through analysis of 22 years of model output, and suggest potential drivers of this variability. The results of our study will inform future field research into microplastic pollution in the Southern Ocean.

How to cite: Wilson, D. R., Sheen, K. L., Clark, J. R., Thorpe, S. E., and Young, E. F.: Modelling the transport of microplastic pollution across the Antarctic Circumpolar Current, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-5971, https://doi.org/10.5194/egusphere-egu23-5971, 2023.

Posters virtual: Thu, 27 Apr, 10:45–12:30 | vHall CR/OS

Chairperson: Katerina Spanoudaki
vCO.8
|
EGU23-16273
Svetlana Pakhomova, Igor Zhdanov, Anfisa Berezina, and Evgeny Yakushev

Plastic is recognized as a threat to marine ecosystems and estimating the level of plastic and microplastics (MP) pollution of the World Ocean is nowadays the goal of many studies. However, the use of different methods for sampling and analysis of MPs leads to the problem of comparing the results obtained. Studies on surface MP pollution of the surface sea water are based on the application of the manta or neuston nets that collect water from the upper 10-20 cm layer (the “surface” MP) or submersible pumping systems, that collect water from the water layer 3-5 m below the sea surface (the “subsurface” MP). These two techniques allow to collect particles of different size fraction, i.e. >300 µm for the surface MP and >100 µm for subsurface MP. The aim of this work was to study the distribution of surface and subsurface MPs and to reveal an influence of oceanographic conditions on their spatial distribution as an example of the open ocean waters of the Central Atlantic and coastal water in Norwegian fjords. It was shown that microplastics found in the surface and subsurface layers differ not only in the size of the items found, but also in morphology, types of polymers, abundance, weight concentration and their spatial distribution. Different hydrodynamic processes affect the fate of plastic occurring exactly at the sea surface and several meters deeper. MPs inhabiting the subsurface waters (about 3-5 m depth) have buoyancy close to neutral and appear to be suspended in the surface mixed layer and are readily transported from the sources to the distant regions by ocean currents. Subsurface turbulence is probably the main process that maintains the MPs in the near-surface part of the water column. In contrast, the surface MPs (which are captured by sampling with surface nets) have positive buoyancy and its spatial distribution is significantly influenced by water dynamics, wind and waves, which led to a more scattered distribution on the ocean surface. It was shown that surface and subsurface microplastics differ significantly in a number of properties and, apparently, they should be considered as two independent groups that may have different sources, and their distribution is driven by different hydrophysical processes. Thus, MPs data collected using both methods simultaneously could provide additional information about MPs fate in the ocean.

How to cite: Pakhomova, S., Zhdanov, I., Berezina, A., and Yakushev, E.: Difference in the fate of surface and subsurface microplastics: an example for open and coastal waters, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-16273, https://doi.org/10.5194/egusphere-egu23-16273, 2023.