HS2.3.4 | Plastic in freshwater environments
EDI
Plastic in freshwater environments
Convener: Kryss WaldschlägerECSECS | Co-conveners: Daniel González-Fernández, Marcel Liedermann, Louise SchreyersECSECS, Uwe Schneidewind
Orals
| Mon, 24 Apr, 08:30–12:20 (CEST), 14:00–15:35 (CEST)
 
Room B
Posters on site
| Attendance Mon, 24 Apr, 16:15–18:00 (CEST)
 
Hall A
Posters virtual
| Attendance Mon, 24 Apr, 16:15–18:00 (CEST)
 
vHall HS
Orals |
Mon, 08:30
Mon, 16:15
Mon, 16:15
Plastic pollution in freshwater systems is a widely recognized global problem with potential environmental risks to water and sediment quality. Furthermore, freshwater plastic pollution is also considered the dominant source of plastic input to the oceans. Despite this, research on plastic pollution has only recently expanded from the marine environment to freshwater systems. Therefore data and knowledge from field studies are still limited in regard to freshwater environments. Sources, quantities, distribution across environmental matrices and ecosystem compartments, and transport mechanisms remain mostly unknown at catchment scale. These knowledge gaps must be addressed to understand the dispersal and eventual fate of plastics in the environment, enabling a better assessment of potential risks as well as development of effective mitigation measures.
In this session, we explore the current state of knowledge and activities on macro-, micro- and nanoplastics in freshwater systems, including aspects such as:
• Plastic in rivers, lakes, urban water systems, floodplains, estuaries, freshwater biota;
• Monitoring and analysis techniques;
• Source to sink investigations, considering quantities and distribution across environmental matrices (water and sediment) and compartments (water surface layer, water column, ice, riverbed, and riverbanks);
• Transport processes of plastics at catchment and local scale;
• The role of river regulation structures, e.g. dams, navigation, flood control, etc., in plastic retention and transport
• Effects of hydrological extremes, e.g. accumulation of plastics during droughts, and short-term export during floods in the catchment;
• Degradation and fragmentation processes, e.g. from macro- to micro- and nanoplastics;
• Modelling approaches for local and/or global river output estimations;
• Legislative/regulatory efforts, such as monitoring programs and measures against plastic pollution in freshwater systems.

Orals: Mon, 24 Apr | Room B

Chairpersons: Kryss Waldschläger, Marcel Liedermann, Louise Schreyers
Small-scale transport (processes)
08:30–08:35
08:35–08:45
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EGU23-72
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HS2.3.4
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On-site presentation
Milica Velimirovic, Géraldine Dumont, Jef De Wit, Kristof Tirez, Stefan Voorspoels, and Frank Vanhaecke

Plastic is considered one of the most practical inventions of the 20th century, providing us with a range of very practical materials. However, due to mismanaged waste the plastic pollution has become persistent in aquatic environments. As the plastic products undergo environmental weathering once released in the aquatic environment, they degrade and are fragmented into a highly heterogeneous group of particles with different sizes (i.e., from centimeter over millimeter and micrometer to nanometer scale), shapes, densities, and chemical compositions. However, due to the lack of suitable analytical methodology, knowledge on degradation and/or fragmentation of plastics to nanoplastics (NPs, 1-1000nm), especially in the aquatic environments is still largely lacking.

In the framework of the MS4Plastics project, 15 different plastic materials, including a surgical face mask, different polymer pellets, rubber dust, and plastic powders as common examples of plastics expected to be present in the aquatic system were added to  Milli Q water and exposed to UV-light for 120 hours to better understand plastic degradation and/or fragmentation into NPs. Finally, for detection and size determination of NPs formed after accelerated UV-driven plastic fragmentation in water, dynamic light scattering was used. For a fraction of the samples, asymmetric flow field-flow fractionation (AF4) hyphenated to multi-angle light scattering (MALS) was used as a complementary analytical technique for characterization of NPs.

This project has received funding from the European Union’s Horizon 2020 research and innovation programme under the Marie Skłodowska-Curie grant agreement No 101023205.

 

How to cite: Velimirovic, M., Dumont, G., De Wit, J., Tirez, K., Voorspoels, S., and Vanhaecke, F.: UV-driven fragmentation of plastics in an aquatic environment: laboratory studies, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-72, https://doi.org/10.5194/egusphere-egu23-72, 2023.

08:45–08:55
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EGU23-14433
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HS2.3.4
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ECS
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On-site presentation
Nan Wu, Stuart Grieve, Andrew Manning, and Kate Spencer

Easily transportable microplastics (plastic particles < 5 mm) have become an increasingly important component of suspended particulate matter (SPM) in the aquatic environment, and their fate is significantly influenced by aggregation and flocculation. Aggregation modifies particle properties (e.g., size) controlling the hydrodynamics of SPM in the aquatic environment. Hence, understanding and quantifying aggregation is key to predicting the behaviour of both SPM and associated microplastics. However, quantifying the aggregation degree of microplastics with complex parameters in various water environments is very difficult.

Here, an extensive range of microplastics including 8 polymer types, 3 shapes, different weathering conditions and different sizes (10-300 µm for fragments and microbeads, and 10-1500 µm in length for microfibers, respectively), were used to explore the aggregation dynamics of microplastics. Over 4000 measurements of incorporated microplastics were collected, and we found microplastic size (MinFeret diameter of fragments, diameter of microfibers) is the key parameter to determining the aggregation behavior. Our results simplified the aggregation of microplastics with a wide range of properties in various water ecosystems into two parameters, the size of microplastics and the size of aggregates. A boundary curve for microplastics was fitted based on size relationships between microplastics and aggregates to divide microplastics into aggregable and un-aggregable groups. This study can aid better understanding the fate of microplastics in various aquatic environments at multiple scales.

How to cite: Wu, N., Grieve, S., Manning, A., and Spencer, K.: Aquatic Aggregates as “Vector” for Microplastics, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-14433, https://doi.org/10.5194/egusphere-egu23-14433, 2023.

08:55–09:05
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EGU23-12840
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HS2.3.4
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ECS
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Highlight
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On-site presentation
Luca Gallitelli, Maurizio Cutini, and Massimiliano Scalici

Plastics are a well-known problem that accumulates in the environment causing detrimental effects on ecosystems. Macroplastics in rivers are only recently studied, with most studies focusing on the transport of plastics to the sea. However, most plastics are retained in the fluvial system. To date, only abiotic factors have been considered in the transport process, but recently vegetation has proven to block plastics from having a pivotal role in influencing plastic riverine drift. Given that little is known on the biotic component affecting riverine plastic transport, we aimed at investigating further on (i) the three-dimensionality structure of riparian vegetation in trapping plastics along watercourses and (ii) to develop a vegetation index to describe vegetation structure and to understand the plastic entrapment service provided by plants. To do so, we sampled field data from central Italy rivers along the three riverine zones considering riparian vegetation in relation to river width. Data on plastics within vegetation has been recollected. Also, data on plant structures (i.e. the number of individuals and the number and height of branches per species) was sampled and then used to develop the 3D vegetation index (i.e. 3D Vegetation Index, 3DVI) considering the tridimensionality and diversity index. As result, plastics occurring in vegetation were significantly related to vegetation structure with the 3DVI correlated with the number of plastics (R2 = 0.36, p = 0.0086, Y = 0.007157*X + 2.562). Furthermore, the most dense and diverse community block more plastics. Considering different vegetation heights in all the rivers, there is a significant linear regression between the 3DVI in vegetation branches (0.5<r<2.0 m, and r>2.0 m, respectively R2 = 0.38, p = 0.007, Y = 0.007662*X + 2.711 and R2 = 0.45, p = 0.0023, Y = 0.2522*X + 2.696). With regards to the three riverine zones, only in the lower river zone there was a significant regression between 3DVI and plastics in vegetation (R2 = 0.94, p = 0.001, Y = 108.0*X-143.7). Biotic factors (i.e. vegetation structure) most correlate to the occurrence of plastics in vegetation driving the plastic entrapment process more than the environmental abiotic factors (i.e. hydrology). Overall, we developed for the first time a vegetation index to describe the structure and diversity of the plant community related to the plastic entrapment service. The higher the 3DVI value, the more complex the vegetation (i.e. characterised by a lot of individuals and branches). We emphasized that plant structures are important variables for understanding the entrapment efficiency of macrolitter, highlighting that the complexity of vegetation structure is key for the trapping net effect. As vegetation retain plastics efficiently in all the zones providing us the ecosystem service of trapping macrolitter, the 3DVI could be applied for future solution to plastic pollution – also detecting plastic hotspot areas for mitigation and clean-up activities.

How to cite: Gallitelli, L., Cutini, M., and Scalici, M.: Lost in the river: the plastic vegetation index for detecting plastics within vegetation, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-12840, https://doi.org/10.5194/egusphere-egu23-12840, 2023.

09:05–09:15
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EGU23-12960
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HS2.3.4
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ECS
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On-site presentation
Marziye Molazadeh, Guilherme Calabro, Fan Liu, Rachid Dris, Cedric Chaumont, Lorenzo Rovelli, Andreas Lorke, Bruno J. Lemaire, Johnny Gasperi, Bruno Tassin, and Jes Vollersten

The widespread use of plastic has made it a widely dispersed product with a high impact on the environment. Through fragmentation of larger pieces or direct discharge, microplastic particles (MP) are present in almost every aquatic ecosystem. MPs based on polymers of lower density than water (ρ < 1.0 g cm−3), such as polyethylene (PE), are among the MPs most commonly found in the sediments of freshwater systems which is counterintuitive. Different mechanisms and theories may explain the dynamics of buoyant positive MP motion and their deposition in water systems. Thus, examining the behavior of MP particles carried in suspension is particularly relevant to assess this contaminant fate. The experimental approach is an important way to help to fill the knowledge gap exist on the transport of these particles in natural flows. In this study, Particle Image Velocimetry (PIV) has been deployed to investigate how turbulent water regime contribute affect the dynamics of buoyant particles and if it drives them towards the bed . Different sets of experiments with different flow velocities and non-cohesive bed types were conducted in a 200 cm long, 30 cm wide, 22 cm deep, rectangular, re-circulating, tilting flume. The PIV measurements were done in the centerline of the flume. A camera framed and recorded images in the laser sheet at 15 Hz to follow fast turbulence fluctuations. Pristine PE particles of around 47µm were used. A particle tracking technique was used to record, to follow the trajectory and to calculate de velocity of the particles. The analyzed images clearly show that turbulence homogenizes the particles in the water column. Also, a substantial quantities of PE particles were subject to downward vertical transport which in its turn increase the chance of particles coming in contact with the bed. Turbulent energy is an important driver in the dynamics of buoyant positive particles, and under more realistic environmental conditions, as biofilm presence on the sediment, would enlighten the trapping of these particles by the sediment.

How to cite: Molazadeh, M., Calabro, G., Liu, F., Dris, R., Chaumont, C., Rovelli, L., Lorke, A., Lemaire, B. J., Gasperi, J., Tassin, B., and Vollersten, J.: Visualization of Buoyant MP motion in response to different flow velocities and bed types, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-12960, https://doi.org/10.5194/egusphere-egu23-12960, 2023.

09:15–09:25
09:25–09:35
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EGU23-15187
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HS2.3.4
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ECS
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Virtual presentation
Khoa Thi, Tim van Emmerik, Ton Hoitink, Bart Vermeulen, and Nhan Pham Quy

The transport of plastic in rivers is affected by a wide variety of factors, such as river discharge, wind drag, and tides. These dynamic processes include the travelling time or distance, retention time or location, and remobilization rate of plastic items, which can be quantified by using GPS-based trackers. However, these properties are still unknown in some specific locations, including river bifurcations where the changes in river discharge, flow velocity, and river morphology are significant. Here, we demonstrate the behaviour of plastic transport in a river bifurcation area not influenced by tides during flood season in the Red River system of Vietnam. While all trackers retained somewhere in the river after hours or days, we found that after 10.5 kilometers downstream of the bifurcation, 9 out of 10 trackers followed the main channel retained in the same approximately 6-kilometer-long river segment. Meanwhile, 50% of the 6 trackers that left the main channel to enter the tributary also retained in the same 2.5-kilometer-long river segment 9 kilometers downstream of the bifurcation. These findings are linked to the concept of rivers as plastic reservoirs, as none of the trackers that stranded on the riverbanks for several days was remobilized. Furthermore, the retention of trackers in the same area after leaving the bifurcation clearly indicates shared driving factors on plastic transport, which are likely the river discharge, wind direction or velocity, and river morphology. Our results underscore the need for future research on delineating exact accumulation zones of the plastics in riverbanks considering the effects of wind, river discharge, and river morphology.

How to cite: Thi, K., van Emmerik, T., Hoitink, T., Vermeulen, B., and Pham Quy, N.: Plastic transport and retention around river bifurcations, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-15187, https://doi.org/10.5194/egusphere-egu23-15187, 2023.

09:35–09:45
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EGU23-14971
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HS2.3.4
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Virtual presentation
John C. Wells

Kimitsuki et al (SIL 2022; EGU 2023, this session) have reported near-surface microplastic particle concentrations from 26 quasi-monthly sampling dates over three years in Lake Biwa, Japan.  The concentrations show a high degree of intermittency, both in the shallow South Basin and the deep North Basin.  Kimitsuki et al have suggested that the dates of high particle concentrations followed relatively strong wind events, which are hypothesized to stir up bottom sediments together with deposited microplastic particles. In the South Basin, which has an average depth of 4 m, this hypothesis seems very natural.  However the sampling point in the North Basin was located in waters well exceeding 60 m depth.  If the sampled microplastic particles there originated from wind-induced resuspension events, it seems likely that the resuspension occurred at shallower bottom depths close to shore.

Through well-resolved hydrodynamic simulations, combined with particle tracking, the current work considers how resuspension at shallow depths, followed by advection during the days preceding sampling, might explain the two highest spikes in Kimitsuki et al’s sampled concentrations in the North Basin.  These spikes occurred on June 20, 2021 and July 4, 2021, when measured particle concentrations were respectively 54 and 46 particles/m3, as may be compared to the median value over the three-year campaign of 6.5 particles/m3.  Preceding both dates, both forward and time-reversed particle tracking suggest that the sampled microplastic particles could have been resuspended from the lakebed at depths of around 10 meters, near to the shore about 5 km northwest of the sampling point. At this location and depth, internal waves, associated with vertical undulations of the thermocline, were predicted to induce strong water currents near the lake bottom.  The simulated near-surface currents were then predicted to transport such resuspended particles offshore toward the sampling location.

How to cite: Wells, J. C.: On the hypothesis of microplastics resuspension by internal waves in a deep stratified lake., EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-14971, https://doi.org/10.5194/egusphere-egu23-14971, 2023.

09:45–09:55
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EGU23-16732
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HS2.3.4
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ECS
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On-site presentation
Daniele la Cecilia, Christian Moeck, Ralf Kägi, Matthias Philipp, and Mario Schirmer

Managed Aquifer Recharge (MAR) belong to the nature-based engineering approaches poised to play an increasingly positive role in climate change adaptation. In fact, the increased groundwater availability thank to MAR can buffer future temporal water shortages driven by forecast longer droughts. However, one concern of MAR regards the quality of the infiltrating water as it affects groundwater quality.

There is growing concern about groundwater contamination by microplastics (MP) delivered by the infiltrated surface water. Indeed, MPs have been found in rivers globally. Groundwater contamination by MPs could then have direct detrimental consequences on groundwater management and availability for human uses.

In this study, we measured MPs larger than 20 µm in the different important stages of a major MAR-water supply system in Switzerland. The MAR system has been diverting an average of 95,000 m3/day of Rhine water through channels and ponds since 1958. Samples of filtered water were taken in triplicates from the Rhine River near Basel, the treatment stages before the managed infiltration outlets, the pumped groundwater, before and after the activated carbon filters. The methodology involved the analysis of the filters by means of micro-Fourier Transform InfraRed (FTIR) spectroscopy and MPs identification by means of the machine-learning model developed by the Purency company. The possible contamination by MPs smaller than 20 µm could not be assessed due to practical challenges for water filtration in the field and quantification (reliable micro-FTIR measurements down to 20 µm). Before analyses, we added surrogate particles of polyethylene with an average size of 60 µm for quality assurance and quality control.

The measurements revealed satisfactory MPs reduction along the MAR system. While the number of MPs in the raw Rhine River had to be quantified still, MPs average concentration decreased from about 9.75 particles/l in the treatment stage to about 1.3 particle/l after the activated carbon filter. MPs average concentration increased to 7 particles/l between the pumped groundwater and the activated carbon filters. The increase was driven by a high count of polypropilene MPs in one of the triplicates. Our study could not exclude a possible MPs contamination by construction materials used in the facility. The measured concentrations referred to a randomised scan of about 50% of the area of the filters encompassing the centre and the edges of the filters. Most of the surrogate particles accumulated along the edges. Yet, we only considered particles with a value of the Relevance and Similarity metrics greater than 0.3.

Acknowledgements: We thank our colleague Reto Britt who supported with the sampling campaign and laboratory measurements and the drinking water supplier for allowing us to carry out the study within their premises.

How to cite: la Cecilia, D., Moeck, C., Kägi, R., Philipp, M., and Schirmer, M.: Microplastics transport during Managed Aquifer Recharge – A potential cause of groundwater contamination?, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-16732, https://doi.org/10.5194/egusphere-egu23-16732, 2023.

09:55–10:05
Coffee break
Chairpersons: Louise Schreyers, Uwe Schneidewind, Daniel González-Fernández
Large-scale transport (processes)
10:45–10:50
10:50–11:00
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EGU23-10261
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HS2.3.4
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Highlight
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On-site presentation
John O'Sullivan, Michael Bruen, Linda Heerey, Annemarie Mahon, Heather Lally, Sinead Murphy, James O'Connor, Ian O'Connor, and Roisin Nash

The increasing recognition that significant amounts of plastic are disposed of and accumulating in agricultural soils has highlighted the need for increased research in the study area.  Once on soils, MP may be transported through vertical migration and/ or overland surface runoff, with processes governing the overland runoff pathway to freshwater systems being poorly understand.   Here we present a study of MP transport from soils through overland flow processes.  The research utilised a medium-scale, laboratory based, rainfall simulator that facilitated experimental testing of multiple variables that influence MP mobilisation and export from field settings under controlled conditions.  A total of 15 experiments were conducted across four separate test series in which differences in MP characteristics (including particle shape, size and density), rainfall regime (including intensity and duration), catchment topography (slope), time lag between MP seeding in the soil surface and rainfall event, together with the catchment condition in the progression of a growing cycle (bare soil to grassland), were tested to capture an extensive and realistic set of MP and environmental test conditions.

Each test followed an identical procedure to ensure consistency across all test series. For each test, a soil sample (particle size distribution of 21.1%, 40.9% and 37.8% clays, silts and sands, respectively) was prepared in a free draining test box (measuring 3.3 x 1.2 x 0.1 m (length x width x depth)) and compacted to achieve a soil bulk density of 1.36 ± 0.2 g/cm3, a value typical for soils in standard agricultural settings.  MP were then seeded in the soil surface with the soil sample being exposed to the test rainfall regime. MP in runoff samples, collected every ten-minutes from a single point drainage system mounted on the test box, were filtered and dried, microscopically and manually separated into their three polymer groups (PP, HDPE and PVC). Mean size for each polymer was recorded as was the overall MP mass in each sample.

Among all parameters examined in this study, rainfall intensity was observed to be one of the most influential in exporting MP from the test catchments.  However, a statically significant difference was not observed when comparing MP export and the timing of a rainfall event following MP seeding.  Increasing catchment slope was also shown to be driver of MP transport in overland runoff with values being higher for bare (simulating recently tilled conditions) soils as opposed to soils with grass swards. Smaller MP particles were shown to be more mobile across all experiments, with larger particles only increasing in mobility with an increase in rainfall intensity. Average MP size in collected samples for low intensity rainfall events (8.4 mm/h) was 0.89 mm, 0.63 mm and 1.67 mm for PP, HDPE, and PVC respectively, increasing to 1.15 mm, 0.89 mm and 1.74 mm for the same polymers during the high intensity event (18 mm/h). Increases in MP mobility were shown to be shape specific, with the strongest correlations noted for PP and HDPE, while no significant correlation was found for PVC particles.

How to cite: O'Sullivan, J., Bruen, M., Heerey, L., Mahon, A., Lally, H., Murphy, S., O'Connor, J., O'Connor, I., and Nash, R.: Understanding the overland transport of microplastics from agricultural soils to freshwater systems, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-10261, https://doi.org/10.5194/egusphere-egu23-10261, 2023.

11:00–11:10
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EGU23-673
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HS2.3.4
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ECS
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On-site presentation
Steve Utecht and Tobias Schuetz

To date, we know little about depth-resolved distributional patterns of microplastic particles (<630 µm) of streambed sediments. Reports in literature about the abundance of considerable amounts of microplastic particles in fluvial sediments indicate that the transport follows naturally occurring flow vectors into streambed sediments. We hypothesize, that locally occurring hydraulic conditions at the water-sediment interface which are characteristic for various naturally occurring riverbed morphological structures might influence the evolution of microplastic depth profiles.

As a first step of identifying morphologic feature specific microplastic depth profiles, we have carried out a series of six freeze core sampling campaigns at the centre of the longitudinal axis of two riffles located in a fourth order gravelbed river (Ruwer) contributing to the Moselle River in Trier, West Germany. The setup allows for sampling a 50 cm long undisturbed sediment freeze-core. Using dry ice as coolant and a diamond saw blade we obtained ten undisturbed sediment cube samples (125 ccm) cut from the vertical axis up to 50 cm depth from each freeze-core. Over the range from 5000 – 25 μm five size fractions were analysed with regard to mineralic sediment and microplastic particle distribution. In all sediment cube samples microplastic particles and fibres could be detected without showing distinct distributional patterns related to its depth. Although the samples represent only a small surface area (25 sq. cm), we could qualify and quantify 81 microplastic items plus 606 suspected items mainly composed of transparent fibres using Raman microspectroscopy. Furthermore, we observe an exponentially increase in microplastic abundance with decreasing size fraction by three orders of magnitude. Dominant plastic types are polypropylene, polyethylene, nitrile and polyether terephthalate representing 85% of our findings. Our first results imply that in riffle heads downward directed transport within the sediment layer affects rather the shape and size of the plastic than the absolute abundance. As a next step, typical depth patterns of microplastic at the upstream and downstream end of streambed riffles have to be identified.

How to cite: Utecht, S. and Schuetz, T.: A depth-resolved snapshot of microplastic abundances in riffle heads in a gravelbed river, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-673, https://doi.org/10.5194/egusphere-egu23-673, 2023.

11:10–11:20
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EGU23-7893
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HS2.3.4
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On-site presentation
Paul Vriend, Margriet Schoor, Mandy Rus, Stephanie B. Oswald, and Frank P. L. Collas

Riverine macroplastic pollution (>0.5 cm) negatively impacts ecosystems and human livelihoods. Monitoring data are crucial for understanding this issue and designing effective interventions. Macroplastic pollution floating on the river surface and plastic deposited on riverbanks are studied relatively often. Data on riverine plastics in the water column remain scarce. In this study we utilize trawl nets at different depths to sample plastic pollution in the water column at the entry point of the river Rhine to the Netherlands. We show that plastic concentrations in the water column increased during higher discharge. The combination of higher macroplastic concentrations and higher discharge leads to considerably higher plastic transport during high discharge events. Moreover, the results indicate that the vertical distribution of macroplastic pollution changes during different flow conditions. Significantly higher concentrations of macroplastic can be seen near the riverbed during low discharge conditions, while no significant differences in concentration are observed between the bottom, middle and surface samples during high discharge conditions. These findings provide first insights into the key role of hydrology in explaining macroplastic transport in the water column. These insights can be used to improve future monitoring and intervention strategies. 

How to cite: Vriend, P., Schoor, M., Rus, M., Oswald, S. B., and Collas, F. P. L.: Macroplastic concentrations in the water column of rivers increase with higher discharge, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-7893, https://doi.org/10.5194/egusphere-egu23-7893, 2023.

11:20–11:30
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EGU23-16958
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HS2.3.4
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On-site presentation
Andrew Gray, Win Cowger, Samiksha Singh, and Clare Murphy-Hagan

Globally, fluxes of microplastics to marine environments are thought to be dominated by stormflow from urban environments, which may be moderated by storage in estuaries. Fluvial transport of microplastics is primarily a supply-limited phenomenon, but flow field and particle characteristics can result in a wide range of transport modes, from surface load to bedload, with potential ramifications for estuarine transport and fate. Here we report preliminary findings from microplastic monitoring campaigns conducted in a number of streams draining urban watersheds in Southern California, and estuarine wetland and benthic sediment deposits. These studies will serve as the basis for microplastic flux, accretion, and composition evaluation, and inform the optimization of microplastic monitoring in urban systems.

How to cite: Gray, A., Cowger, W., Singh, S., and Murphy-Hagan, C.: Microplastics in Urban Watersheds, Southern California, USA, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-16958, https://doi.org/10.5194/egusphere-egu23-16958, 2023.

11:30–11:40
11:40–11:50
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EGU23-14632
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HS2.3.4
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On-site presentation
Renata Correia, Thaine Assumpção, Luke Buchanan, Darren Fletcher, and Ava Maxam

Mismanaged plastic waste continually accumulates in the marine environment. A large amount of its emission to the ocean originates on land and is transported by rivers, streams and artificial drains. However, monitoring efforts and knowledge building on the dynamics and quantification of these emissions based on field research is scarce and subject to local catchment scale.

Here, we present an experimental study of plastic waste transport and retention dynamics in artificial drains (gullies) subject to flash floodings in short drainage areas of Kingston, Jamaica. We developed a novel plastic waste piles survey using UAV and field measurements. The offered investigation has the potential for estimation of plastic waste piles (i) volumes and composition, (ii) transport-retention-remobilization cycles and (iii) correlation with local hydro-meteorology, especially during peak events, where most of the plastic waste is transported.

Until now, monitoring efforts were carried out on the lower stretch (1km) of three gullies flowing to Kingston Harbour and the Caribbean Sea during 90 days in the hurricane season of 2021 on a bi-weekly basis. The current dataset includes 24 orthorectified images of the gullies and plastic waste piles. Direct samples of the plastic waste piles are being collected for ground-truth validation. We observe that plastic waste piles are more prominent when large objects (such as refrigerators, tree branches or tyres) are present, forming a base for greater accumulation and affecting remobilization cycles.

These results are essential for understanding macroplastic transport processes and the development of innovative technological solutions preventing plastics inflow into the ocean. It has the potential to provide insights into the operational performance before and after the implementation of interception solutions or mitigation measures. Furthermore, it serves as baseline data to strengthen local policy-making on initiatives assessing harmful effects in surrounding ecosystems.

How to cite: Correia, R., Assumpção, T., Buchanan, L., Fletcher, D., and Maxam, A.: Understanding plastic waste dynamics, correlations with hydrological extremes and its contributions to the development of innovative interception and mitigation solutions within Kingston Harbour, Jamaica, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-14632, https://doi.org/10.5194/egusphere-egu23-14632, 2023.

11:50–12:00
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EGU23-8819
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HS2.3.4
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ECS
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On-site presentation
Sophie Defontaine and Isabel Jalon-Rojas

Standardized sampling methods and protocols are essential to facilitate the comparison of studies on plastic pollution and to advance knowledge of this environmental issue. Several protocols for sampling microplastics in oceanic and coastal waters have been developed, compared and even harmonized for this purpose. However, these protocols may be not adapted for the study of estuarine environments, characterized by strong vertical, horizontal and temporal gradients.  In this work, microplastic sampling methods and strategies are discussed in relation to estuarine hydrodynamic processes. The analogies between the dynamical behaviour of microplastics and sediments make it possible to draw out recommendations for sampling microplastics based on several decades of research in estuarine hydro-sedimentary dynamics. In particular, we will discuss when, where, and how to sample microplastics in order to capture the most representative picture of microplastic pollution in these highly dynamic systems subject to strong anthropogenic pressures.  

How to cite: Defontaine, S. and Jalon-Rojas, I.: Sampling microplastics in estuarine environments: lessons learned from suspended sediment dynamics and perspectives., EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-8819, https://doi.org/10.5194/egusphere-egu23-8819, 2023.

12:00–12:10
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EGU23-1182
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HS2.3.4
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ECS
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Highlight
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On-site presentation
David Mennekes, Yvette Mellink, Tim van Emmerik, and Bernd Nowack

Over the last years macroplastic has been increasingly monitored not only in oceans but also in freshwaters. Despite the ongoing discussion of linking plastic masses in rivers with masses in oceans, multiple studies showed a highly complex transport of plastic debris from in land-based sources towards the oceans. However, current modeling and monitoring studies mostly focused on specific processes in single rivers or used highly simplified approaches. While such studies may be helpful to identify the fate mechanisms, they are less suitable to predict macroplastic flows in a large river network on country-scale. The aim of our work was therefore to develop a macroplastic fate model for a whole country which was parameterized based on measurements in specific rivers. For the macroplastic modelling we considered four different states: (1) in suspension, (2) temporally stored (3) long term burial or accumulated and (4) removal / cleaning from in suspension or temporally stored masses. The model considers a high spatial resolution with river sections of few meters to kilometers in length which are connected to the overall river network. As input data we used macroplastic emissions predicted by a material flow analysis model on the same spatial resolution. The model was applied before to predict macroplastic masses on a river level.

Using our model we found that the considered transport and fate processes for macroplastics must clearly differ from processes considered for microplastics. As possible influencing fate and transport factors we compared the influence of parameters such as sinuosity of rivers, the land use in close river distance, the discharge or impact of weirs with macroplastic removals. Each parameter was identified by other studies as potential factor for macroplastic retention. Here, we explore their influence on the output on a country-scale. We conclude that based on our modelling a high retention of macroplastics must occur within the system to match monitoring data with predicted macroplastic releases. While we assume that high amounts of macroplastics will be temporally stored until the next flooding event, it remains challenging to predict the long term in-situ accumulation. As a first step, we simulated different parameter settings to mimic "normal" discharge conditions in comparison with flooding events.

Overall our results bring existing concepts and understanding in a wider context by coupling emission modelling with fate modeling and monitoring results from literature. Moreover, we are able to predict macroplastic masses in rivers and temporally stored in river banks and compare predicted values with first available measurements. Especially, predicting microplastic masses is of high importance for policy makers to manage plastic pollutions along riversides.

How to cite: Mennekes, D., Mellink, Y., van Emmerik, T., and Nowack, B.: Exploring Macroplastic Transport and Retention Dynamics in Country-Wide River Networks, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-1182, https://doi.org/10.5194/egusphere-egu23-1182, 2023.

12:10–12:20
Lunch break
Chairpersons: Daniel González-Fernández, Marcel Liedermann, Uwe Schneidewind
Methods for monitoring and detection
14:00–14:05
14:05–14:15
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EGU23-13885
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HS2.3.4
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ECS
|
On-site presentation
Anouk Boon, Tim van Emmerik, and Bart Vermeulen

Suspended plastic transport is one of the big unknowns in present plastic research. It is either neglected or measured using expensive and labour-intensive underwater net-measurements. In search for additional measurement methods, the Acoustic Doppler Current Profiler (ADCP) has recently been explored as a tool for detecting plastic debris. ADCPs emit a high-frequency acoustic signal, which is scattered back to the transducer by particles in the water column. The frequency shift and the strength of the returned signal (backscatter) are used for respectively flow velocity and suspended sediment concentration estimates. Large objects like fish and organic material can be recognised in the acoustic signal by a strong local increase in backscatter. It has been shown that ADCPs can also detect plastic debris during controlled tests. The characteristics of the acoustic signal of plastics in an uncontrolled setup under varying conditions is still understudied.

To develop knowledge on in situ plastic detection, we first deployed an ADCP in a small flowing system into which we introduced plastic litter varying in size, composition and shape. Secondly, a test was undertaken with a simultaneous ADCP and net measurement in a large Dutch river. The uncontrolled plastic transport of the river is estimated based on ADCP data, and calibrated and validated using the net measurement. The tests gave novel insight into the signature of flowing plastics in the backscatter signal, and the present possibilities and challenges of in situ plastic detection using ADCPs. Overall, plastic detection using ADCPs has the potential to provide valuable information about the spatial and temporal variability of suspended macroplastic transport in rivers, aiding efforts to mitigate the negative impacts of plastic pollution. More research is needed to create a complete overview of backscatter characteristics of litter and to develop effective automated algorithms and methods for accurately distinguishing plastic.

How to cite: Boon, A., van Emmerik, T., and Vermeulen, B.: Detection of suspended macroplastics in the field using acoustic backscatter, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-13885, https://doi.org/10.5194/egusphere-egu23-13885, 2023.

14:15–14:25
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EGU23-12092
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HS2.3.4
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ECS
|
On-site presentation
André Vallendar, Tianlong Jia, Rinze de Vries, Zoran Kapelan, and Riccardo Taormina

Plastic pollution of water bodies is a major environmental issue, as it can have harmful effects on marine life, riverine ecosystems and society as a whole. To mitigate the impacts of plastic pollution, accurate detection and quantification of macroplastic litter (plastic items > 5 mm) is of particular importance. In recent years, researchers and engineers have developed Deep Learning methods showing promising performances for detecting riverine macroplastic litter. However, there are several outstanding issues hindering the advancement of the field, including the lack of available data sources for training such models.

Here, we present a new open source dataset for the detection of floating macroplastic litter. We generated the dataset from controlled experiments carried out in a small drainage canal on the TU Delft campus. The dataset features 626 different litter items including plastic bottles, bags and other plastic objects, as well as metal tins and paper litter. These items include household waste as well as litter recovered from canals in the Netherlands. We captured images with a resolution of 1080p and a linear field of view using two different action cameras and a phone, mounted on a bridge. The dataset consists of 10000 images, taken from two different heights (2.7 and 4.0 meters), two different inclinations (0 and 45 degrees from the horizontal), and two different weather conditions (sunny and cloudy sky).

In this presentation, we provide information on the dataset and the experiments carried out to generate it. We also discuss the results of benchmark Deep Learning models for multi-class classification trained on the dataset, and their out-of-sample generalization ability to other case studies. While labels are currently available only for image classification, we aim to release annotations for object detection and image segmentation tasks in the future.

How to cite: Vallendar, A., Jia, T., de Vries, R., Kapelan, Z., and Taormina, R.: An open source dataset for Deep Learning-based visual detection of floating macroplastic litter, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-12092, https://doi.org/10.5194/egusphere-egu23-12092, 2023.

14:25–14:35
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EGU23-14841
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HS2.3.4
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ECS
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On-site presentation
Rocío Quintana Sepúlveda, Daniel González-Fernández, Andrés Cózar, Sandra Manzano-Medina, Lucía Pérez-López, and Carmen Morales-Caselles

Rivers and estuaries are a key transport pathway for plastics from inland to the sea. These systems are subject to fluctuations depending on sources of plastics and local environmental factors, causing variation in the plastic concentration up to several orders of magnitude within limited time ranges. Due to this large variability, in freshwater systems, it is challenging to obtain representative monitoring data. This study presents a new methodological approach to determine the number of plastic particles needed to obtain representative data for plastic pollution characterization in estuarine waters. The method used monthly in situ observations during a period of two years in the Guadalquivir River estuary (SW Spain). The data allowed the characterization of plastic concentrations across all size categories (micro-, meso- and macroplastics). The items were categorized into different size classes (<5 mm, 5-25 mm, 2.5-5 cm, 5-10 cm and >10 cm) and a resampling simulation was applied to generate 95% confidence intervals for plastic concentration variability. Our results suggest that, when using a limited number of samples, there is an underestimation of all size classes, e.g., up to three quarters of the samples could underestimate the average number of particles. Differences up to 3 orders of magnitude can be established between the lower (<5 mm) and the higher (>10 cm) size class in terms of number of particles sampled. This approach will help to optimize time and define sample size for specific particle size classes to improve plastic monitoring in freshwater environments.

How to cite: Quintana Sepúlveda, R., González-Fernández, D., Cózar, A., Manzano-Medina, S., Pérez-López, L., and Morales-Caselles, C.: A new methodological approach for the assessment of plastic pollution in estuarine waters: Guadalquivir River (SW Spain), EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-14841, https://doi.org/10.5194/egusphere-egu23-14841, 2023.

14:35–14:45
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EGU23-2987
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HS2.3.4
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ECS
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On-site presentation
|
Youna Cho, Won Joon Shim, Sung Yong Ha, Gi Myung Han, Mi Jang, and Sang Hee Hong

Stormwater runoff is considered a major pathway for land-based microplastic transportation to aquatic environments. By applying time-weighted stormwater sampling at stormwater outlets from industrial and residential catchments, we investigated the emission characteristics and loads (number- and mass-based) of microplastics to aquatic environments through urban stormwater runoff during rainfall events. Microplastics were detected in stormwater runoff from industrial and residential catchments in the concentration range of 68-568 n/L and 54-639 n/L, respectively. Polypropylene and polyethylene were found as major polymers accounting for around 60% of total microplastics. The fragment was the dominant shape of microplastics, and the most common size class were 20-100 μm or 100-200 μm. The microplastic load emitted from industrial and residential catchments were estimated to be 1.54 - 46.1 x 108 and 0.63 - 28.5 x 108 particles, respectively. The discharge characteristics of microplastics inter– and intra–event were affected by the land-use pattern and rainfall characteristics. The concentration of microplastics did not significantly differ between industrial and residential catchments, but the composition of polymer types reflected the land-use pattern. The microplastics in stormwater were more concentrated when the number of antecedent dry days (ADDs) was higher; the concentration of microplastics was generally peaked in the early stage of runoff and varied according to rainfall intensity during a rainfall event. The contamination level and load of microplastics were heavily affected by the total rainfall depth. Most microplastics were transported in the early stage of runoff (19–37% of total runoff time), but the proportion of larger and heavier particles increased in the later period of runoff. The microplastic emission via stormwater runoff was significantly higher than that through the discharge of wastewater treatment plant effluent in the same area, implying that stormwater runoff is the dominant pathway for transporting microplastics to aquatic environments.

 

 

How to cite: Cho, Y., Shim, W. J., Ha, S. Y., Han, G. M., Jang, M., and Hong, S. H.: Microplastic emission characteristics of stormwater runoff in an urban area: Intra-event variability and influencing factors, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-2987, https://doi.org/10.5194/egusphere-egu23-2987, 2023.

14:45–14:55
14:55–15:05
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EGU23-6634
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HS2.3.4
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ECS
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On-site presentation
Rahel Hauk, Tim H.M. van Emmerik, Martine van der Ploeg, Marijke Boonstra, Winnie de Winter, and Adriaan J. Teuling

Rivers transport, and store a large share of the global plastic pollution. Riverbanks are one of the river compartments where macroplastic litter is deposited and retained. Different factors influence macroplastic deposition on riverbanks. Retention related factors such as riverbank features, and supply related factors, such as hydrometeorology or land-use. Riverbank macrolitter along the Dutch Meuse has been quantified, characterized, and removed biannually since 2017. At each monitored riverbank, macroplastic and other litter items were collected along a 100 m section and classified in over 100 specific litter categories. We assume that after each monitoring round all litter is removed, and that the litter sampled in the following round has accumulated in the time between rounds. This monitoring dataset is analyzed to identify riverbanks with plastic accumulation rates continuously below or above average, and the specific characteristics of these identified riverbanks. Furthermore, correlations are investigated between macroplastic deposition and individual riverbank features and river morphology, such as types of riparian vegetation, or curvature of the river. These correlations are tested for the total amount of plastic litter, but also categories grouped by plastic characteristics such as potential source, density, size, or flexibility. This is done based on the hypothesis that plastic litter items with different characteristics are associated to different processes of plastic emission and deposition. For example, items with low or high density, or different levels of flexibility. Items with low and high densities are transported differently, because their density is lower or higher than the density of water. Items with a high level of flexibility, such as soft plastic foils, have a higher potential for entanglement in vegetation, and a lower potential for remobilization, compared to items with a low level of flexibility. The aim of this study is to identify riverbank characteristics that explain high plastic accumulation rates.

How to cite: Hauk, R., van Emmerik, T. H. M., van der Ploeg, M., Boonstra, M., de Winter, W., and Teuling, A. J.: Linking macroplastic deposition to riverbank characteristics, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-6634, https://doi.org/10.5194/egusphere-egu23-6634, 2023.

15:05–15:15
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EGU23-15526
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HS2.3.4
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ECS
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On-site presentation
Using secondary currents induced by air curtains to improve trapping of plastic particles
(withdrawn)
Rui Lage Ferreira, Steven Restrepo, and Ana Ricardo
15:15–15:25
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EGU23-13804
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HS2.3.4
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Highlight
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On-site presentation
Alena Bartosova, Fanny Jeppsson Stahl, Conrad Brendel, Johan Temnerud, Jan Havelka, and Berit Arheimer

Plastic pollution is one of the major global water quality issues. Yet the lack of consistent data and standardized monitoring and assessment methods leads to a wide range of uncertainties in estimating the plastic load that is being delivered to marine environments. At the same time, continental and global dynamic hydrological models are becoming more available for large-scale estimation of time-dynamic water fluxes into sea basins. One such tool is a dynamic process-based rainfall-runoff and water quality model Hydrological Predictions for Environment (HYPE) and its global application, World-Wide HYPE (WWH, Arheimer et al., 2020).

Here, we present the first results from simulating global riverine plastic pollution using WWH. The model development is based on the results of the global literature review of sources of microplastics through the lens of a hydrological modeler. Traditional model calibration techniques may not be appropriate in this case due to insufficient number of data points, large variability in plastic characteristics and sampling techniques applied in the collected monitoring studies, as well as large uncertainty and a lack of current knowledge of transport and transformation processes in water bodies. Thus, an ensemble of WWH model setups was developed where the model structure and hydrology is the same and the model parameters that affect generation, transformation, and transport of plastic from various land uses, sanitation categories, and in rivers are varied to explore the defined parameter space. Collected data together with other global estimates were then used to evaluate the ensemble with a weight of evidence approach, highlighting sources and processes of major significance and focusing the ensemble towards a realistic set. Further model error analyses indicate which sources and processes play an important role in transport of riverine plastics as well as how different monitoring approaches can affect the results.

References:

Arheimer, B., Pimentel, R., Isberg, K., Crochemore, L., Andersson, J. C. M., Hasan, A., and Pineda, L., 2020. Global catchment modelling using World-Wide HYPE (WWH), open data and stepwise parameter estimation, Hydrol. Earth Syst. Sci. 24, 535–559, https://doi.org/10.5194/hess-24-535-2020

How to cite: Bartosova, A., Jeppsson Stahl, F., Brendel, C., Temnerud, J., Havelka, J., and Arheimer, B.: What can global hydrological models tell us about sources and flows of riverine plastics?, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-13804, https://doi.org/10.5194/egusphere-egu23-13804, 2023.

15:25–15:35

Posters on site: Mon, 24 Apr, 16:15–18:00 | Hall A

Chairpersons: Kryss Waldschläger, Uwe Schneidewind, Marcel Liedermann
A.48
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EGU23-1300
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HS2.3.4
Xin Tian, Patrick Bäuerlein, and Frederic Beén

Monitoring and identifying environmental microplastics is of great importance for the scientific world, environmental agencies, and water authorities, to estimate the environmental impact and increase efforts to decrease emissions. As one of the infrared spectroscopy techniques, Laser Directed Infrared (LDIR) imaging can observe various microplastics, in terms of spectroscopical signals. Such signals are useful for follow-up analyses, particularly, identification by machine learning (ML) algorithms. Based on medium or large-sized datasets, past studies applied a variety of ML models to detect microplastics from their LDIR spectra. To tackle it, we first propose a practical data augmentation technique to generate synthetic samples when only a few samples are available. Then a comprehensive comparison of multiple models, including both machine learning and deep learning models, is presented. Our results show that the ensemble ML model, compared to neural network models, can take the least training time to achieve the best performance, i.e., a classification accuracy of 99.5%, even with a small dataset (210 samples collected from aquatic systems). This study provides a generic framework for monitoring and detecting microplastics by combining LDIR and ML.

How to cite: Tian, X., Bäuerlein, P., and Beén, F.: Classifying polymers with mid-IR spectra and machine learning: From monitoring to detection, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-1300, https://doi.org/10.5194/egusphere-egu23-1300, 2023.

A.49
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EGU23-530
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HS2.3.4
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ECS
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Highlight
Paolo Tasseron, Finn Begemann, Nonna Joosse, Martine van der Ploeg, Joppe van Driel, and Tim van Emmerik

Accumulation of plastic in aquatic environments negatively impacts ecosystems and human livelihood. Urban areas are assumed to the main source of plastic pollution in these environments, because of high anthropogenic activity. Yet, the drivers of plastic emissions, abundance and retention within these systems and subsequent transport to river systems is poorly understood. In this study, we demonstrate that urban water systems function as major contributors to river plastic pollution, and explore the potential driving factors contributing to the transport dynamics. Monthly visual counting of floating litter at six outlets of the Amsterdam water system results in an estimated 2.7 million items to enter the closely connected IJ river annually, ranking it among the most polluting systems measured in the Netherlands and Europe. Subsequent analyses of environmental drivers (including rainfall, sunlight, wind speed and tidal regimes) and litter flux showed no strong correlations (r = -0.19 - 0.16), implying additional investigation of potential drivers is required. High frequency observations at various locations within the urban water system and advanced monitoring using novel technologies could be explored to harmonize and automate monitoring. Once litter type and abundance are well-defined with a clear origin, communication of the results with local communities and stakeholders could help co-develop solutions and stimulate behavioural change geared to reduce plastic pollution in urban environments.

How to cite: Tasseron, P., Begemann, F., Joosse, N., van der Ploeg, M., van Driel, J., and van Emmerik, T.: Urban water systems as entry points for river plastic pollution, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-530, https://doi.org/10.5194/egusphere-egu23-530, 2023.

A.50
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EGU23-13061
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HS2.3.4
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ECS
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Highlight
Louise Schreyers, Tim van Emmerik, Khiet Bui, Khoa Van Le Thi, Bart Vermeulen, Hong-Q. Nguyen, and Martine van der Ploeg

The processes controlling the transport in tidal rivers and estuaries, the interface between fluvial and marine systems, remain largely unresolved. For this reason, current estimates of riverine plastic pollution and export into the ocean remain highly uncertain. Hydrodynamics in tidal rivers and estuaries are influenced by tides and freshwater discharge. As a consequence, flow velocity direction and magnitude can change diurnally. In turn, this impacts the transport dynamics of solutes and pollutants, including plastics. 

Plastic transport dynamics in tidal rivers and estuaries remain understudied, yet the few available observations suggest that plastics can be retained here for long time periods, especially during periods of low net discharge. Additional factors such as riparian vegetation and riverbank characteristics, in combination with bidirectional flows and varying water levels, can lead to even higher likelihood of long-term retention.

Here, we provide a first observation-based estimation of net plastic transport on daily time scales in tidal rivers. For this purpose, we developed a simple Eulerian approach using sub-hourly observations of floating plastic transport and discharge during full tidal cycles. We applied our method to the Saigon river, Vietnam, throughout six full tidal cycles in May 2022.

We show that the net plastic transport is about 27-32% of the total plastic transport. We found that plastic transport and river discharge are positively and significantly correlated (Pearson's r = 0.87, R2= 0.75). The net plastic transport is higher than the net discharge (27-32% and 18%, respectively), suggesting that plastic transport is governed by other factors than water flow. Such factors include wind, plastic concentrations in the water, and entrapment of plastics downstream of the measurement site. The net plastic transport rates per tidal cycle alternate between positive (seaward) net transport and negative (landward) net transport, as a result of the diurnal inequality in the tidal cycles. We found that soft and neutrally buoyant items had considerably lower net transport rates than rigid and highly buoyant items (11-17% vs 31-39%), suggesting the retention time strongly depends on item characteristics.

Our results demonstrate the crucial role of tidal dynamics and bidirectional flows in net plastic transport. We emphasize the importance of understanding fundamental transport dynamics in tidal rivers and estuaries to ultimately reduce the uncertainties of plastic emission estimates into the ocean.

How to cite: Schreyers, L., van Emmerik, T., Bui, K., Van Le Thi, K., Vermeulen, B., Nguyen, H.-Q., and van der Ploeg, M.: Tidal plastic recycling: net river plastic transport limited by tidal dynamics, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-13061, https://doi.org/10.5194/egusphere-egu23-13061, 2023.

A.51
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EGU23-6918
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HS2.3.4
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ECS
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Highlight
Yvette Mellink, Simone van Langen, Paul Vriend, Nadieh Kamp, Anne de Weme, and Tim van Emmerik

Macroplastics have been found in many compartments of freshwater systems amongst which floating at the water surface. To quantify the floating macroplastic flux in rivers, the visual counting method was developed. This method is based on visual observations from bridges, and has already been applied in various river systems across the world, including the Rhine-Meuse delta. A two-year dataset of monthly field measurements on ten bridges across the Rhine, Meuse, and IJssel rivers has been collected. This dataset revealed the high variability of the floating macroplastic flux in both time and space. Except for extreme flooding events, the fluctuations are not always simply related to the discharge or season. This finding raises the questions of how to assure representative field observations. Representative field observations are important, as they are typically inter- and extrapolated in time and space. If the timing or location of the measurement is not representative of the ‘normal’ condition, then the extrapolation of that measurement will be associated with a large uncertainty range, resulting in over- or underestimations of the total floating macroplastic flux in the river. As field observations play a major role in calibrating and validating river plastic transport and emission models, it is essential to minimize the uncertainty of field-based floating plastic transport estimates. To optimize the visual counting method and explore its limits, we executed three experiments. The first experiment demonstrated that the temporal variability at bridge level is high, but can be attenuated by repeated measurements. The second experiment showed how many observation points on the bridge are sufficient to account for the spatial variability of the macroplastic flux across the river cross profile. The third experiment determined that the size limit of the visible macroplastics is 1 cm2 on bridges that are up to 5 meter above water level and 4 cm2 for bridges up to 15 meter above water level. The findings of these experiments endorse the effectiveness of the visual counting method and allow for a substantiated implementation of this method in floating macroplastic monitoring campaigns across river networks worldwide.

How to cite: Mellink, Y., van Langen, S., Vriend, P., Kamp, N., de Weme, A., and van Emmerik, T.: Reducing uncertainty of floating plastic transport estimates in rivers using the visual counting method, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-6918, https://doi.org/10.5194/egusphere-egu23-6918, 2023.

A.52
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EGU23-12701
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HS2.3.4
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Highlight
Uwe Schneidewind, Sophie Comer-Warner, Lee Haverson, Anna Kukkola, Holly Nel, and Stefan Krause

Mangrove forests provide important ecosystem services with regards to carbon storage and nutrient removal in coastal areas. They have also been found to retain emerging contaminants such as microplastics. However, in many parts of the world, mangrove forests are severely affected by deforestation and transformation into areas of intense agriculture/aquaculture. To restore their original ecosystem functions, mangrove forests are increasingly being targeted in small-scale conservation and restoration efforts, which often results in the coexistence of a variety of mangrove forest types with respect to tree age and vegetation density. This might have a severe impact on their retention capacity of fine particulate matter including microplastics (MP).

Here, we study Mangrove sediment samples from Xuan Thuy National Park, Vietnam located in the Red River Delta with respect to microplastics. Sediment samples were taken from four types of landcover, i.e., (i) completely deforested area, (ii) 5–7-year-old naturally regenerated forest, (iii) eight-year-old replanted forest, and (iv) 15 year-old naturally regenerated forest. Surface samples and 50 cm-long cores were collected using mini augers and dried at 50°C. Subsamples were used to extract microplastics by means of density separation with ZnCl2 and digestion with Fenton reagent. Extracted MP were stained with Nile Red for florescence microscopy to determine MP concentration and shape. Additionally, microFTIR was used to identify the respective polymer type.

Microplastics concentrations (>64 µm) range from 64 to 2141 particles/kg dry weight (n=568) with the vast majority being fragments. Higher concentrations were found in the naturally regrown forests (ii and iv) than in deforested or reforested areas. Although no depth-dependent trends were visible, high concentration spikes in 30 cm depth at sites (ii) and (iii) have been identified. Future analyses will relate particle concentration to sediment grain size distribution and carbon/nutrient data from the same locations.

How to cite: Schneidewind, U., Comer-Warner, S., Haverson, L., Kukkola, A., Nel, H., and Krause, S.: Microplastics retention in different types of Mangrove forest in Xuan Thuy National Park, Vietnam, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-12701, https://doi.org/10.5194/egusphere-egu23-12701, 2023.

A.53
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EGU23-14876
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HS2.3.4
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Highlight
Marcel Liedermann, Sebastian Pessenlehner, Philipp Gmeiner, Johannes Mayerhofer, Ionut Procop, and Helmut Habersack

Microplastics are already part of our environment - even in the most inaccessible and remote places we find plastic particles that also remain there due to their longevity. The finer the scale at which we analyse samples, the more particles we find. It also became clear in the recent years, that rivers transport microplastics and that they also represent a principal pathway for plastic transport from land to the sea.

Initial measurements with benthic nets on the Austrian Danube have shown that the plastic particles are not only found on the surface, but are distributed unevenly with maximum concentrations partly near the bottom, partly on the surface and partly concentrated on one side of the river. Given the spatial and temporal distribution, a multipoint method seems inevitable and was chosen for further measurements, in which three measuring points each are distributed over the depths of several measuring verticals along a cross-section. Furthermore, it was found that the microplastic concentration also strongly depends on the discharge conditions and that by far the largest quantities of microplastics are mobilized and then transported during flood events.

After the first comprehensive measurements on the Austrian Danube between 2014 and 2015, further samplings were carried out in Hungary, Serbia and at 3 locations in Romania over the recent years. Despite the limitations of the data set, regarding the longitudinal, cross-sectional and hydrological representation of the micro plastic transport in the Danube River, an attempt is made to describe its characteristics on a basin wide scale. The measurements, reaching from impounded sections in the Upper Danube all the way down to the Danube delta, have shown, that the concentrations fluctuate strongly longitudinally according also to the discharge level. Therefore, at least at certain times, the Danube – and river systems with their inundation areas in general – are not only pathways, but can also be regarded as a microplastic sink. However, to increases process understanding and derive reliable statements, more data are needed.

How to cite: Liedermann, M., Pessenlehner, S., Gmeiner, P., Mayerhofer, J., Procop, I., and Habersack, H.: Microplasic measurements at the Danube river using a multi-level approach, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-14876, https://doi.org/10.5194/egusphere-egu23-14876, 2023.

A.54
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EGU23-6474
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HS2.3.4
Thomas Mani, Tadiwanashe Gutsa, Cristina Trois, Robin de Vries, Asanda Qadi, and Muthukrishnavelaisamy Kumarasamy

Rivers are major contributors of plastic waste entering the oceans. The Umgeni River in Kwazulu-Natal, South Africa, runs through the densely populated city of Durban, with 3.5 million inhabitants and is estimated to emit 400 tons of plastic waste annually into the Indian Ocean. The banks of the Umgeni River are lined with plastic waste accumulations, derived from accidental, intentional, and natural accumulation. This study uses high-resolution aerial imagery and several hydrometeorological measuring sensors in the catchment to (1) locate, monitor, and quantify macroplastic waste hotspots along the Umgeni River; and (2) investigate the influence of hydrometeorological factors driving the spatio-temporal evolution of the hotspots. This novel attempt to map and monitor plastic waste sources along the Umgeni River could assist waste managers and communities with a framework for developing targeted waste removal practices and mitigation measures.

How to cite: Mani, T., Gutsa, T., Trois, C., de Vries, R., Qadi, A., and Kumarasamy, M.: Monitoring macroplastic waste sources along the Umgeni River using unmanned aerial vehicles, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-6474, https://doi.org/10.5194/egusphere-egu23-6474, 2023.

A.55
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EGU23-15273
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HS2.3.4
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ECS
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Faith Tumwet, Rebecca Serbe, and Traugott Scheytt

Since microplastics are an obstinate pollutant in terrestrial environments, posing a risk to the subsurface soil matrix and entering inland waters via erosion pathways, it is necessary to understand their transport behaviours. The morphological descriptors used to characterize microplastic particles are usually highly subjective. This study explores the transport and retention behaviour of 125 – 200 μm Polyvinyl chloride (PVC) plastic fragments in saturated quartz sand (1.6 – 2.0 mm) columns. Retention profiles at different ultrapure water flow rates (2.0 – 3.5 ml/min) were compared and analysed. At the beginning and end of each column test, the microplastic particles were scrutinized, identified, and quantified by light microscopy. Each particle was characterized by dimensionless 3D morphological descriptors that can describe any particle shape. The results showed that the transport distance of microplastic particles increased with decreasing diameter of the microplastic particles. PVC microplastic particles, whose morphology was more 1-dimensional, were more susceptible to degradation and fragmentation within the column, promoting migration. Microplastic degradation into fragments appeared to play an important role in improving the movement of particles. This study offers initial indications of infiltration depths and morphology-dependent fragmentation of secondary microplastics in coarse sand, outlining the limitations of 2D projected images conventionally used to study the transport of microplastics.

How to cite: Tumwet, F., Serbe, R., and Scheytt, T.: Morphology-dependent degradation and fragmentation of PVC microplastic particles influence their transport in saturated quartz sand columns, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-15273, https://doi.org/10.5194/egusphere-egu23-15273, 2023.

A.56
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EGU23-6498
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HS2.3.4
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ECS
|
Francesca Uguagliati, Massimiliano Ghinassi, and Massimiliano Zattin

Rivers are the primary pathways for microplastic (MP) particles from terrestrial sources to the sea, but they can also be temporary reservoirs of MPs, that can be easily stored in alluvial sediments. Knowing the MPs content in sediments is critical for i) understanding where and how they accumulate over time, ii) assessing their toxic effects, and iii) developing mass balance models based on their fate and fluxes. Given the rapid growth of the research field and the lack of standardized methods, extraction strategies for MP particles from sediments have become inconsistent, and new techniques are constantly being developed. Several studies highlight that density separation using high-density concentrated saline solutions is one of the most reliable and efficient separation methods. In this study, we tested the efficiency of sodium polytungstate (ρ = 3.1 g · cm-3), diluted with distilled water to a density of 1.6 g · cm-3, as a density separation agent. Sodium polytungstate has an intermediate density between that of sediments and plastic and has also been used successfully for the gravity separation of minerals and rocks. Furthermore, it is non-toxic, it is stable in the pH range of 2-14 and can be easily recovered and reused. In this study, artificial sediment samples were created by adding 50 MP items into 25 grams of plastic-free sand. MPs-free sediments were sampled from Pleistocene alluvial deposits of the Upper Valdarno Basin (Italy) after removing the surficial layer to avoid contamination. Sediments were divided into three different particle size ranges (i.e., 250-63 μm, <63 μm, <250 μm). Different shapes of MPs were used in the experiments: i) fibres obtained by cutting 500 μm long segments of a nylon drawstring, ii) fragments created by cutting PVC pipes, and iii) PET glitters used as films. A total of 45 experiments were performed. Before applying the procedure for density separation, samples were prepared using Wet Peroxide Oxidation (WPO) to remove the organic matter. Successively, a sodium polytungstate saline solution was used for the extraction technique and the suspended solids were collected and transferred to filters. The MP particles were counted using a stereomicroscope. Results highlight the very high efficiency of the system, although some variance is present and related to the different shapes of MPs and the sediment particle size.

How to cite: Uguagliati, F., Ghinassi, M., and Zattin, M.: Testing the use of sodium polytungstate for an efficient extraction of microplastic particles from river sediments, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-6498, https://doi.org/10.5194/egusphere-egu23-6498, 2023.

A.57
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EGU23-14892
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HS2.3.4
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ECS
Jagoda Worek, Ewa Gawlak, Kamil Kawoń, Joanna Chwiej, Wioleta Bolesta, and Katarzyna Styszko

Microplastics found in sewage are mainly microparticles from cosmetics (peelings, toothpaste) and fibres from fabrics (which get into the sewage during washing). Microplastics removed from wastewater accumulate primarily in raw sludge, which it ends up in the sludge processing sector. Due to their low susceptibility to biodegradation, microplastics together with stabilised sewage sludge end up in the soil or are otherwise processed together with the sludge.

The purpose of the research was to analyze the content of microplastics in stabilised sewage sludge, of which up to 90% is used to produce fertilizers. The analysis was based first on the oxidation of the matrix with peroxide and then density separation with a saturated solution of zinc chloride (ZnCl2). The second stage consisted of the analysis of separated microplastic fractions. For this purpose, the ATR FTIR and FTIR microscope were used. A complementary apparatus was also used, which was a confocal Raman microscope. Stabilised sewage sludge was analyzed depending on the day of its collection. The highest amount of microplastics was found in the samples from Monday, Friday and Saturday. This was due to the increased release of hygiene products containing plastic microbeads. Qualitative analysis, which showed the highest amount of LDPE microplastic fraction. The highest amount of microplastics per 100 grammes of dry weight was 1,084 fragments and 1,128 fibres, for a total of 2,212 microplastic particles. If 90% of the stabilised sewage sludge was used for the production of fertiliser, the emission would be about 1990 particles per 100 grammes. The study showed that the use of sewage sludge to create fertilisers will contribute to the emission of a significant amount of microplastics into the environment.

 

 

 

 

 

 

 

 

 

Acknowledgments: A Research project financed by program “Initiative for Excellence – Research
University” for the AGH University of Science and Technology. The research was supported by
Research Subsidy AGH 16.16.210.476.

How to cite: Worek, J., Gawlak, E., Kawoń, K., Chwiej, J., Bolesta, W., and Styszko, K.: Risk of re-release of microplastics from sewage fertilisers into the environment, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-14892, https://doi.org/10.5194/egusphere-egu23-14892, 2023.

A.58
|
EGU23-8216
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HS2.3.4
Rose Boahemaa Pinto, Linda Bogerd, Tim van Emmerik, Martine van der Ploeg, Kwame Anhwere Duah, and Remko Uijlenhoet

River catchments are important to consider when investigating the fate of plastics once introduced into the environment. However, plastic transport at the river catchment scale is rarely quantified. In this study, we present a catchment-scale field assessment of macroplastic litter in the Odaw (270 km2). The catchment was sub-divided into non-urban riverine, urban riverine and urban tidal zones based on the urbanisation level and riverine transport across the catchment. The riverine (river and riverbank) and terrestrial environments at ten locations along the catchment were monitored on three days in December, 2021. Floating litter items in the river were monitored by visual counting. At the riverbank and terrestrial environments, litter items were sampled in a designated area (5 x 2 m2) and categorised according to the River-OSPAR list (Schone-Rivieren, 2018). Results showed a high plastic flux (1125 items/h) in the urban riverine zone, which was higher by a factor of 16 and 2 to the plastic flux at the non-urban riverine and urban tidal zones, respectively. Terrestrial and riverbank plastic density was highest closest to the river mouth (urban tidal). The factor increase between the most upstream (non-urban riverine) and downstream (urban tidal) was larger for terrestrial than for riverbank. This shows the influence of urbanisation on the generation of mismanaged plastics in the catchment. Top three plastic polymer types observed in the catchment were PO soft, EPS and Multilayer. However, at each zone, the top three plastic polymer types varied with PO Soft as the most dominant at each zone. The highest abundance of PO soft, EPS and multilayer was found at the urban riverine (56%), urban tidal (31%) and non-urban riverine (24%) zones respectively. Our findings provide information on the spatial variation of plastic transport in the Odaw catchment and therefore can help create better strategies to manage the plastic pollution problem in this catchment. Future work will further explore the potential sources and temporal sink zones in the catchment.

Reference

Schone-Rivieren (2018). Handleiding voor monitoring, pp. 1–3.

How to cite: Pinto, R. B., Bogerd, L., van Emmerik, T., van der Ploeg, M., Anhwere Duah, K., and Uijlenhoet, R.: Plastic routing through the Odaw catchment, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-8216, https://doi.org/10.5194/egusphere-egu23-8216, 2023.

A.59
|
EGU23-10819
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HS2.3.4
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ECS
Anuja Joseph and Sudha Goel

Microbeads in personal care and cosmetic products (PCCPs) such as facial scrubs and face washes are added to provide mechanical exfoliation while washing one’s face. Such abrasive scrub cleansers have gained global acceptance from consumers, some of these microbeads are made up of plastics. Plastic beads are used because of their round and smooth surfaces, which impart painless exfoliation. These microbeads in turn act as a primary source of microplastics (MP) in wastewater systems. Ten facewashes containing MP beads that are popularly available in the Indian market were analysed to detect the presence of microplastics. MP beads were found in 4 out of 10 facial scrubs and ranged in size from 220 to 600 µm. Based on the Fourier Transformed Infrared spectrophotometer (FTIR) analysis, the MP beads were made of cellophane, polyethylene (PE), or polypropylene (PP). India generates approximately 72,368 MLD of sewage of which about 60% is untreated. In India, it was estimated that 4.7 x 1010 microbeads are released into the environment through untreated sewage every year, which amounts to 3.8 tonnes of microbeads being released into the environment annually. The study indicates that massive annual release of MPs in the form of microbeads into the water bodies through facial scrubs and other similar personal care products is inevitable. These microplastic beads are small and can easily escape wastewater treatment systems. Hence, their presence in aquatic ecosystems can lead to the adsorption of contaminants and pollutants like heavy metals, synthetic organic compounds, and other pathogens. The microbeads along with the contaminants can potentially bio-accumulate and bio-magnify within different trophic levels, thus increasing the toxicity at each level.

How to cite: Joseph, A. and Goel, S.: Microbead nuisance: Estimation of microplastic release into water bodies through personal care and cosmetic products, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-10819, https://doi.org/10.5194/egusphere-egu23-10819, 2023.

A.60
|
EGU23-11175
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HS2.3.4
Maciej Liro, Paweł Mikuś, Zielonka Anna, and Mateusz Kieniewicz

Information on the transport and deposition of riverine macroplastic is crucial for selecting proper locations for river cleaning actions and for trapping infrastructure installation. Obtaining such information for mountain rivers is of particular importance because their specific characteristics make them particularly prone to illegal dumping, plastic litter input from slope to the river channel, and an increased rate of secondary microplastic production in the river channel (1).

To shed some light on the patterns of macroplastic transport and deposition along mountain rivers we have performed a field experiment utilizing tracked plastic (PET) bottles injected to the channel of the mountainous Skawa River in the Polish Carpathians. After 50-57 days of low-flow conditions, we documented transport distances (n=64) which were non-normally distributed and reached from 0.37 km to 16.27 km (median=1.73 km, quartile range=5.29 km). Most of the tracked bottles were deposited on woody debris (71.9%, n=46) (Photo 1) at elevations ranging from 0 to 1.2 m (median=0.4 m, quartile range=0.45 m) above the low-flow water level. Surprisingly, the straight and narrow channelized reach of the studied river trapped 15.3 % of the plastic bottles transported through it, while the highly sinuous, wide unregulated one only 8.7 %, which is probably related to the more frequent contact of woody debris (present in both reaches) with the flowing water, occurring during low-flow conditions within the narrower, channelized reach.

Our initial results suggest that places of woody debris deposition along rivers can be a good location for river cleaning actions. 

Photo 1. The deposition of plastic bottles on wood jam
(the Skawa River, S Poland) (photo by M. Liro)

 

References

(1) Liro, M., van Emmerik, T.H., Zielonka, A., Gallitelli, L., Mihai, F.C., 2023. The unknown fate of macroplastic in mountain river. Sci. Total Environ. 865, 161224.

How to cite: Liro, M., Mikuś, P., Anna, Z., and Kieniewicz, M.: Field experiment on transport and deposition of plastic bottles along mountain river, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-11175, https://doi.org/10.5194/egusphere-egu23-11175, 2023.

A.61
|
EGU23-10476
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HS2.3.4
|
ECS
Maiyatat Nunkhaw and Hitoshi Miyamoto

In recent years, plastic pollution in the ocean has become a global environmental problem, deeply affecting the ecosystem as well. In fact, 80 percent of ocean plastic was reported to come from terrestrial river basins, therefore it would be extremely important to recognize how much plastic waste runoff from rivers around the world was. In response to this global environmental problem, an image analysis method for monitoring river waste transport has recently been started to propose. However, this image analysis indicated a difficulty to fully detect plastic waste in various types of waters because it needed to use a color difference in each water to classify the type of waste.

This paper tried to develop an automated detection system based on a modified convolutional neural network (CNN) for detecting and counting floating river waste. The CNN used in this research was You Only Look Once (YOLO) architecture with a fine-tuning for adjusting it to the waste detection. The proposed model has further been improved its accuracy through the enlarged image processing. As for the waste counting, an object tracking method, e.g., deep SORT, could be used with the proposed model in video frames of flowing water.  

The results showed that the proposed YOLO model with enlarged image processing achieved the evaluation values of mean average precision mAP (%) of can, carton, plastic bottle, foam, glass, paper, and plastic were 95, 89, 94, 97, 92, 71, and 81, respectively. Moreover, the proposed mode with deep SORT has achieved the F1-score (%) of 80, 80, 75, 85, 100, 100, and 50, in each waste type. Consequently, the proposed model could be feasible for identifying and counting flowing river waste accurately. The future research work should improve the counting accuracy and further develop an automated model implementation method.

How to cite: Nunkhaw, M. and Miyamoto, H.: A Deep Learning Method for Detecting Floating Garbage in Urban Rivers, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-10476, https://doi.org/10.5194/egusphere-egu23-10476, 2023.

Posters virtual: Mon, 24 Apr, 16:15–18:00 | vHall HS

Chairpersons: Louise Schreyers, Daniel González-Fernández
vHS.14
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EGU23-15136
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HS2.3.4
|
ECS
Mayu Kimitsuki

Considerable amounts of plastic waste that flow into rivers and the ocean have become a major environmental problem. This is especially true for microplastics (MPs: Plastic particles less then 5mm in size) and different organizations are investigating their impact on the environment. While a lot of related research has focused on oceans and coastal seas, investigations of MPs in lakes and rivers remain sparse. Lake Biwa, the largest and the oldest lake in Japan is no exception. In order to better understand the situation, we conducted quasi-monthly sampling on Lake Biwa (26 times total from March 2019 to July 2022) by filtering one cubic meter of water from the lake surface at a specified location in the North Basin (average depth <d>= 43m) and a second location in the South Basin (<d>= 4m). FT-IR and Nile Red staining were used to evaluate the quantity and quality of MPs in the two locations.

We found that the particle concentrations were highly intermittent in both basins. Median particle concentrations were low: 2.5 particles/m3 in the South Basin, and 6.6 particles/m3 in the North Basin. But a few “spikes” in concentration were observed. Notably, more than 100 Small MPs (plastic particles sized less than 1mm, per m3) were observed on Nov. 29th and Dec. 27th, 2020, and on June 20th, 2022, in the South Basin. We suggest that it is related to the weather that occurred in Lake Biwa. Within the 3 days preceding these sampling days, strong winds of more than 10m/s were observed. Because the South Basin is much shallower, it is more likely that the sediment on the bottom was lifted up by wind-driven waves, and deposited MPs were resuspended into the water column.

Overall, the median number of MPs was clearly higher in the North Basin. We suggest that it happened because of the gyre that exist during the stratified season in North Basin. There are 3 gyres in the North Basin which create a non-uniform distribution in plastic particles. In addition, we have to note that the residence time in the North and the South Basin are quite different. The residence time in the North Basin is 5.5 years, whereas in the South Basin, it is only about 15 days. Due to the presence of the gyre, the residence time in the North Basin will be longer (19 years to be precise). Therefore, we can presume that many MPs stayed in the North Basin.

Concerning the composition of MPs in Lake Biwa, Polyethylene (PE) and Polypropylene (PP) were dominant, together accounting for 90%. Since PE and PP are low-cost, light, easy to process, etc., they are the most commonly used type of plastics. Similar results for the composition of MPs have been obtained by other research groups as well.

How to cite: Kimitsuki, M.: The abundance and composition of Micro Plastics in the North and South Basins of Lake Biwa, Japan, EGU General Assembly 2023, Vienna, Austria, 23–28 Apr 2023, EGU23-15136, https://doi.org/10.5194/egusphere-egu23-15136, 2023.