HS8.2.9
New challenges and solutions to address risk assessment and remediation of groundwater from emerging contaminants

HS8.2.9

New challenges and solutions to address risk assessment and remediation of groundwater from emerging contaminants
Convener: Fritjof Fagerlund | Co-convener: Tissa Illangasekare
Presentations
| Thu, 26 May, 13:20–15:55 (CEST)
 
Room 2.17

Presentations: Thu, 26 May | Room 2.17

Chairperson: Fritjof Fagerlund
13:20–13:23
Part 1: Emerging contaminants, biofilms, MAR
13:23–13:30
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EGU22-1779
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ECS
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On-site presentation
Vera Behle, Paula Rodríguez-Escales, and Xavier Sanchez-Vila

Managed Aquifer Recharge (MAR) is a technology to deal with water stress and water scarcity worldwide. Depending on the origin and degree of prior treatment, the water inflow in MAR facilities contains measurable concentrations of Emerging Organic Compounds (EOCs). Understanding the processes that influence the fate of EOCs in the aquifer is therefore a key point for evaluating and predicting contaminant plumes and risk assessment. Such fate is clearly linked to the presence of biofilms that develop mainly in the first centimeters of the aquifer. Yet, the link between microorganisms, the development of biofilm and the fate of contaminants is not well understood. The spatial distribution into different redox states and thus the taking place of the different redox reactions, which significantly influence the degradation of pollutants as well as the sorption of these substances, is an important point. Sorption takes place in two different phases, the sediment and the biofilm. We have used the results of some conducted column experiments to create a numerical model, with which the processes taking place can be viewed in a differentiated manner and investigated further. The results show that biofilm plays an important role as a sorption phase and should therefore not be neglected when investigating and evaluating the fate of pollutants.

How to cite: Behle, V., Rodríguez-Escales, P., and Sanchez-Vila, X.: The Role of Biofilm on the Fate of Emerging Organic Compounds: Numerical Modelling of Column Experiments, EGU General Assembly 2022, Vienna, Austria, 23–27 May 2022, EGU22-1779, https://doi.org/10.5194/egusphere-egu22-1779, 2022.

13:30–13:37
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EGU22-7511
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ECS
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Virtual presentation
Sonia Jou-Claus, Paula Rodríguez-Escales, Lurdes Martínez-Landa, M. Silvia Diaz-Cruz, Jesús Carrera, Adrià Sunyer-Caldú, Gerard Quintana, and Cristina Valhondo

Ultraviolet filters (UVFs) are emerging organic contaminants that are present in personal care (sunscreens and many cosmetics) and numerous industrial products. Among UVFs, the group of benzophenone derivatives are the most used worldwide. Benzophenone-3 (PB-3, oxybenzone) is one of the most common UVF. BP-3 is considered as an endocrine disruptor with estrogenic activity, it is photo-stable, lipophilic and bioaccumulates in different organisms. The widespread use of BP-3 has led to its release into aquatic ecosystems mainly via discharge of wastewater treatment plant effluents. Common sources of water for Managed Aquifer Recharge (MAR) are affected, to some extent, by effluents of wastewater treatment plants and therefore, MAR has been proposed as a potential source of these compounds to the environment. Understanding the fate of UVFs but also of their transformation products (TPs) in MAR is relevant because some of them can be more ecotoxic than the parent compound. We evaluated the fate of selected UVFs and its TPs at different compartments (water, soil and biofilm) in two field pilot scale MAR systems; one of them operated with a permeable reactive barrier based on compost and the other with sand (without reactive barrier). We compared the temporal and spatial evolution of these UVFs before and after a slug injection of lithium acetate, as organic carbon source, in the two MAR systems. Quantification of selected UVFs and TPs showed that the two MAR systems promoted the removal of UVFs. Extended removal was enhanced by the compost reactive barrier, in which lower concentrations of all selected UVFs and TPs were measured. The fact that they were detected and quantified more often sorbed onto the biofilm and organic fraction of sediment than in the aqueous phase suggested that degradation takes place in the two solid compartments.

 

Acknowledgements

This work was financially supported by the Catalan Research Project RESTORA (ACA210/18/00040), by the Spanish Ministry of Science and Innovation through MONOPOLIOS (RTI2018-101990-B-100, MINECO/FEDER) and Project CEX2018-000794-S), as well as the EU project MARADENTRO (PCI2019-103425 and PCI2019-103603). We also thank the Consorci de la Costa Brava Girona (CCBGi) for the unlimited access to the WWTP.

How to cite: Jou-Claus, S., Rodríguez-Escales, P., Martínez-Landa, L., Diaz-Cruz, M. S., Carrera, J., Sunyer-Caldú, A., Quintana, G., and Valhondo, C.: Evaluating the fate of UV filters and transformation products during managed aquifer recharge: the role of reactive barriers, biofilms and varying redox., EGU General Assembly 2022, Vienna, Austria, 23–27 May 2022, EGU22-7511, https://doi.org/10.5194/egusphere-egu22-7511, 2022.

13:37–13:44
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EGU22-7832
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Presentation form not yet defined
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Paula Rodriguez-Escales, Arnau Canelles, and Xavier Sanchez-Vila

Understanding the fate of Emerging Organic Compounds (EOCs) is quite complex. It depends on several direct processes (e.g. sorption or biodegradation) but also on indirect ones (e.g. reduction oxidation processes, soil-water interaction). For that, modeling is a useful tool to evaluate it. Nevertheless, most of the models in literature are quite simple. Most of them are completely disconnected from the geochemical conditions of the environmental systems and it has been widely proved that both sorption and degradation of EOCs depends on that, specially, on pH and reduction oxidation dynamics. For that, in this work we have evaluated different conceptual models of EOC’s fate in the context of Managed Aquifer Recharge. The tested models were from the simplest one (fully disconnected from the geochemistry) to the more complex one (coupling both EOC’s sorption and biodegradation to the geochemistry). The models were validated with a column experiment, which reproduced the fate five EOC’s (paracetamol, diuron, benzophenone-3, carbamazepine and sulfamethoxazole)  in an infiltration pond with a reactive barriers made up of compost (3 types of columns, 0% of compost, 10% and 50%) (Modrzyński et al., 2021). The EOC’s models were also coupled with a previous geochemical model focused in carbon and nitrogen cycle and validated with the same experiments (Canelles et al., 2021). Our results demonstrate that a better reproduction is achieved when both sorption and biodegradation are coupled with a geochemical reactive transport, specially for systems with a higher presence of organic carbon.   

This work was financially supported by the Catalan Research Project RESTORA (ACA210/18/00040), by the Spanish Ministry of Science and Innovation through MONOPOLIOS (RTI2018-101990-B-100, MINECO/FEDER), as well as the EU project MARADENTRO (PCI2019-103425). 

How to cite: Rodriguez-Escales, P., Canelles, A., and Sanchez-Vila, X.: Coupling sorption and biodegradation of Emerging Organic Compounds with geochemical modeling, EGU General Assembly 2022, Vienna, Austria, 23–27 May 2022, EGU22-7832, https://doi.org/10.5194/egusphere-egu22-7832, 2022.

13:44–13:51
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EGU22-8720
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ECS
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On-site presentation
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Edinsson Muñoz-Vega, Lucas Spada, Stephan Schulz, and Christoph Schüth

Over the last two decades there has been a growing interest in the occurrence and fate of emerging organic contaminants (EOCs) in groundwater globally. Managed aquifer recharge (MAR) has been recognized as one of the possible causes of pollution, because of the use of insufficiently or partially treated waters as infiltration source.

Biofilms are one of the most widely distributed modes of life on Earth, and they drive biogeochemical cycling processes of most elements in water, soil, sediment and subsurface environments. Biofilms are aggregates of microorganisms in which cells are frequently embedded in a self-produced matrix of extracellular polymeric substances (EPS). Biofilms partially cover the underlying material, changing the sorption behavior of the soil surface and giving a proper environment to microorganisms for the degradation of EOCs.

To understand the role of biofilms in the transport processes of EOCs, we performed batches studies and a set of three saturated column experiments where biofilms were established. Two of the columns were filled with a soil having a high organic content (0.6% organic carbon) and the third one contained the same soil but muffled, to characterize the role of organic matter in the growth of biofilms. The feed water consisted of ten-fold diluted synthetic wastewater (SWW) without EOCs, and in the case of one of the organic columns, sodium azide was spiked to have an abiotic control. The columns were equipped with automated sensors (high resolution oxidation-reduction potential, water pressure and soil pH) to link these variables to biofilm development. Several tracer experiments were run during the duration of the experiments and analysis of major ions, organic carbon and trace elements were performed as well. After hydrogeochemical equilibrium was reached in each column, inflow SWW was spiked with a cocktail of five EOCs in environmental concentrations (µg/L), covering different hydrophobicity, speciation and biodegradability parameters: Carbamazepine, Metoprolol, BP3, Ibuprofen and Diclofenac.  Breakthrough curves of the EOCs were measured, and double porosity models were fitted to compare retardation factors and rates of degradation of each system. Post experiments analysis allowed the determination of the biofilms on each column by means of EPS extraction and quantification. Differences in the transport behavior of most of the compounds were observed between the columns, concluding that biofilms and biological structures can be an important factor in the transport of EOCs in soils.

How to cite: Muñoz-Vega, E., Spada, L., Schulz, S., and Schüth, C.: Role of soil biofilms in the transport processes of emerging organic contaminants: A laboratory experimental study, EGU General Assembly 2022, Vienna, Austria, 23–27 May 2022, EGU22-8720, https://doi.org/10.5194/egusphere-egu22-8720, 2022.

13:51–13:58
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EGU22-12751
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ECS
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On-site presentation
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Marcel Horovitz, Edinsson Muñoz-Vega, Teresa Leitão, Christoph Schüth, and Stephan Schulz

Managed aquifer recharge (MAR) via infiltration basins to replenish aquifers is an important part of the integrated water resource management (IWRM) toolbox. Soil aquifer treatment managed aquifer recharge (SAT-MAR) basins are used to improve water quality during infiltration. However, SAT-MAR can also pose the risk of contaminating the aquifer, by infiltrating treated wastewater effluent, which may still contain high concentrations of e.g., nutrients (N and P) and emerging organic compounds (EOCs), e.g., pharmaceuticals. In order to assess these potential risks and to be able to take measures, it is important to understand the SAT-MAR system. In this context, it is necessary to study the degradation and sorption capacity of natural conditions as well as modified regimes, e.g., by incorporating reactive layers. While laboratory column experiments are widely used and provide detailed process understanding under controlled conditions, transferring the results to field size and conditions remains challenging. On the other end, in-situ field experiments give great insights into real systems while they often study only one SAT-MAR site under distinct environmental settings which hinders to transfer knowledge to other sites. One way to bridge this gap between the two scales is through large tank experiments. However, there are few such large tank experiments in research on MAR that seek to combine the representativeness of in-situ experiments with the controlled characteristics of laboratory column studies.

Therefore, we designed and conducted a large-scale tank experiment consisting of three tank replicates for the purpose of analyzing SAT infiltration basins using treated wastewater effluent under controlled conditions. The three tanks are packed with fine sand and comprise a vadose zone as well as a saturated zone. The vadose zone of two tanks incorporates a mixed layer of biochar/fine sand as reactive layer, while the third tank consists solely of fine sand and acts as reference. The tanks are equipped with various sensors (high resolution oxidation-reduction potential, water pressure, soil moisture content, electrical conductivity, water pressure, and temperature). To be able to measure the concentration of solutes along the flow path, several suction cups and small-diameter wells allow sampling in the vadose zone and saturated zone, respectively. The infiltrating water in this study is treated wastewater while the groundwater flowing continuously in the lower part of the tank consists of local groundwater. A set of six EOCs (carbamazepine, diclofenac, ibuprofen, naproxen, gemfibrozil, and triclosan) act as model substances as they cover a wide range of physicochemical parameters and degradation potentials.

Preliminary results are presented on the influence of operational regimes and reactive barriers on the attenuation of EOCs, as well as on nutrients, dissolved organic carbon, and major ions in both the vadose zone and groundwater.

Acknowledgement: This work is presented within the framework of the project MARSoluT (www.marsolut-itn.eu), a four-year Marie Skłodowska-Curie Actions (MSCA) Innovative Training Network (ITN) funded by the European Commission (Grant Agreement 814066).

How to cite: Horovitz, M., Muñoz-Vega, E., Leitão, T., Schüth, C., and Schulz, S.: Large-scale tank experiments simulating soil aquifer treatment – Assessing the attenuation potential of emerging organic compounds and nutrients during managed aquifer recharge, EGU General Assembly 2022, Vienna, Austria, 23–27 May 2022, EGU22-12751, https://doi.org/10.5194/egusphere-egu22-12751, 2022.

13:58–14:05
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EGU22-11191
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ECS
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On-site presentation
Karolina Solymos, Badam Ariya, Izabella Babcsányi, Andrea Farsang, and Zsolt Pap

Titanium dioxide nanoparticles (TiO2 NPs) are increasingly used as photocatalysts, or as additives in personal care products, paints or food packaging, owing to their specific and individual properties. TiO2 NPs can enter the environment through corrosion and degradation of end-of-life products and surfaces bearing these entities. Additionally, the agricultural application of sewage sludge, presumed to be the primary sink for engineered TiO2 through the treatment of wastewater, has become a widespread fertilizing practice. The primary environmental medium receiving unwanted TiO2NPs as pollutants is the soil environment. Hence, studying the behavior and interactions of such NPs with the soil and the soil solution is a prerequisite for apprehending the ecological risk related to such emerging pollutants. The interactions of TiO2 NPs with the soil solution and solid phases -adsorption, aggregation, dissolution and sedimentation- are governed by the physicochemical characteristics of the nanoparticles (size, shape, surface properties, crystal structures) as well as the properties of the soil (pH, salt and organic matter contents).

            Our study focuses on performing laboratory experiments in soil extracts, as model soil solutions, of a neutral phaeozem, an acidic regosol and a solonetz (pH>9) with engineered TiO2 NPs: 89% anatase (20-25 nm) and 11% rutile (50 nm), pure rutile and pure anatase. The goal is twofold i) investigating the changes of the photocatalytic activity of TiO2 NPsfollowing their interactions with the different soil solutions, and ii) studying the degradation of the dissolved natural organic material in the soil solution due to the addition of TiO2 catalysts. Three different types of soils have been selected for the experiments displaying variable pH and salt contents (acidic and neutral soils with low salt contents, and alkaline soils with high salt contents) to examine the effect of the pH, ionic strength and salt concentrations in the soil extracts on the outcome of the experiments. The reacted NPs will be characterized by SEM for potential changes in the particle morphology, XRD for analyzing the changes induced in its crystal structure, and IR spectroscopy for examining the changes occurred on the surface of the NPs (adsorption of organic molecules from the soil solution, changes in hydrophylicity) and DRS (changes in their optical properties). The photocatalytic activity following NP interactions with the soil solutions will be evaluated by monitoring phenol degradation in a reactor. The impact of the TiO2 NPs on the degradation of natural organic matter will be assessed by total organic carbon measurements. Our preliminary results show that depending on the crystal structure of the applied TiO2 NP, the pH of the soil solution may significantly change and there are visible changes of the NPs' properties. These results will promote our understanding of potential environmental risks related to engineered nanoparticles released into soils and groundwater.

How to cite: Solymos, K., Ariya, B., Babcsányi, I., Farsang, A., and Pap, Z.: Investigating the behavior and catalytic activity of TiO2 nanomaterials in soil extracts, EGU General Assembly 2022, Vienna, Austria, 23–27 May 2022, EGU22-11191, https://doi.org/10.5194/egusphere-egu22-11191, 2022.

14:05–14:10
Part 2: PFAS
14:10–14:17
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EGU22-3831
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ECS
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On-site presentation
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Eva Weidemann, René Lämmer, Thorsten Stahl, Bernd Göckener, Mark Bücking, Jörn Breuer, Janine Kowalczyk, Hildegard Just, Runa S. Boeddinghaus, and Matthias Gassmann

Per- and polyfluoroalkyl substances (PFAS) are anthropogenic substances, which moved to the scientific focus due to their ubiquity in the environment. Several thousands of individual PFAS are known, which differ in chemical structure as well as in their chemical and physical properties. Due to the huge number of substances, the assessment of their environmental behaviour is challenging. Still, more information about these substances, which are partly already declared PBT (persistent, bioaccumulative and toxic), is needed for risk assessments and remediation.

The overall aim of this study was to describe the environmental behaviour in soil during leaching of ten different PFAAs (perfluoroalkyl acids), a group of persistent PFAS, and two diPAPs (polyfluoroalkyl phosphate diesters) with physical equations and parameters to gain knowledge about substance-related characteristics. For this purpose, we simulated the leaching of all surveyed PFAAs and of the biodegradable precursors 6:2 diPAP and 8:2 diPAP, which can transform into PFAAs. Soil and percolation data received from two experimental studies, a laboratory soil column study and a field lysimeter study, were used to evaluate the leaching and transformation behaviour using the MACRO model. In both studies the behaviour of diPAPs were simulated, which enables a comparison between natural and unnatural conditions. Modelling results from the laboratory study, in which climate impacts are limited, were used as input for the field study with natural climatic conditions. Parameters used for calibration were substance-related such as the adsorption distribution coefficient (KD). The amount of non-recovered PFAS, which is potentially related to the formation of non-extractable residues (NERs), was described using a first-order degradation equation. The evaluation of simulations was done using the goodness-of-fit function KGE (Kling-Gupta Efficiency) and a fitting score comparing simulated and observed soil and percolation data. Optimisation was done using the caRamel evolutionary algorithm with multi-objectives within the GNU R environment and up to 15,000 runs per substance, which resulted in a pareto front. Results of parameter values were then used to describe their leaching behaviour as transformation products (PFAAs) of diPAPs in two steps: (1) optimisation of leaching and transformation of diPAPs with soil data, (2) simulation of leaching of transformation products using results of PFAA simulations. The preliminary modeling results are promising for simulating the behavior of PFAAs as well as their precursors with MACRO.

How to cite: Weidemann, E., Lämmer, R., Stahl, T., Göckener, B., Bücking, M., Breuer, J., Kowalczyk, J., Just, H., Boeddinghaus, R. S., and Gassmann, M.: Is it possible to describe the behaviour of per- and polyfluoroalkyl substances (PFAS) and biodegradable precursors using the MACRO model? – Approach and preliminary results., EGU General Assembly 2022, Vienna, Austria, 23–27 May 2022, EGU22-3831, https://doi.org/10.5194/egusphere-egu22-3831, 2022.

14:17–14:24
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EGU22-7877
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ECS
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Presentation form not yet defined
Georgios Niarchos, Anna Merle Liebenehm-Axmann, Dan Berggren Kleja, Lutz Ahrens, and Fritjof Fagerlund

Remediation of sites contaminated with per- and polyfluoroalkyl substances (PFASs) is a significant step towards protecting drinking water sources and limiting human exposure. PFAS production and use is increasingly being restricted worldwide with a reduction of point sources; however, legacy plumes are still posing a threat due to the persistence of these chemicals against degradation. One of the most widely applied soil remediation techniques for PFASs is stabilisation, aiming to long-term entrapment of the contaminants with the addition of fixation agents in the subsurface, which prevent their leaching from soil to groundwater. In relation to this, the aim of this study was to identify the leaching behaviour of various PFASs in a treatment scenario using colloidal activated carbon (CAC). The effect of dissolved organic carbon (DOC), one of the major groundwater constituents in Sweden, on sorption was evaluated. Silt loam soil sampled from central Sweden was used, as well as a mixture of the soil with CAC at 0.1% w/w. Spiked artificial groundwater was prepared with a mixture of 21 PFASs, at a total concentration of 1.4 μg mL-1. The sorption of PFASs to the solid phase was investigated using 15 cm long column experiments under saturated conditions, with and without DOC at 10 mg L-1. Non-reactive tracer tests with NaCl were used to evaluate hydrological parameters. The desorption behaviour after treatment was also investigated, by switching the inflow from contaminated to clean water after steady state was achieved. Analysis of the compounds was conducted using ultra performance liquid chromatography coupled with tandem mass spectrometry (UPLC-MS/MS). Preliminary results showed retardation of PFASs with the addition of CAC, primarily for long-chain PFASs, exhibiting a correlation between sorption strength capacity and perfluorocarbon chain length. Some short-chain compounds, like perfluorobutanoate (PFBA) and perfluoropentanoate (PFPeA), exhibited immediate breakthrough. Slightly higher retardation of long-chain PFASs was noticed in the presence of DOC, for both treated and reference soil, indicating a potential increase of adsorption sites. Conversely, short-chain PFASs appeared to be outcompeted by DOC and showed faster breakthrough in its presence. These results indicate that humus content can have variable effect on PFAS sorption to soil and CAC, depending on perfluorocarbon chain length. Further experiments aim to the quantification of the sorption capacity.

How to cite: Niarchos, G., Liebenehm-Axmann, A. M., Berggren Kleja, D., Ahrens, L., and Fagerlund, F.: Evaluating the effect of DOC on PFAS sorption to soil and colloidal activated carbon using column tests, EGU General Assembly 2022, Vienna, Austria, 23–27 May 2022, EGU22-7877, https://doi.org/10.5194/egusphere-egu22-7877, 2022.

14:24–14:31
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EGU22-8076
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Presentation form not yet defined
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Fritjof Fagerlund, Georgios Niarchos, Lutz Ahrens, Dan Berggren Kleja, Jonny Bergman, Anna Larsson, Gareth Leonard, Jim Forde, Matilda Schütz, and Henning Persson

Due to their extreme persistence, often combined with high aqueous mobility, per- and polyfluoroalkyl substances (PFAS) are challenging to remediate and remove from the environment. Stabilisation by activated carbon is a method that can potentially stop or at least reduce the migration of PFAS and limit further spreading to the environment from contaminated hot spots. In the StopPFAS project, the use of sorbents to limit PFAS migration in groundwater has been investigated, including in a field trial of colloidal activated carbon (CAC) injection at a PFAS contaminated site in Arboga, Sweden. After CAC injection at the field site, there was an initial reduction in PFAS concentrations by approximately 72% for a sum of 11 PFAS. This indicates significant reduction, but that there were still flow paths where the PFAS transport was not intercepted by CAC. Later however, the PFAS concentrations rebounded to levels equal or higher than before CAC injection. After the rebound concentrations again declined to lower than before CAC injection. The reduction in PFAS concentrations by sorption is related to the amount of CAC that the PFAS come in contact with. A sorptive barrier application is likely to be less effective if the CAC emplacement is uncertain or does not reach all flow paths, if the contaminant transport is dominated by a few preferential flow channels or if the barrier is bypassed due to changes in flow directions. Furthermore, our laboratory experiments indicate that competition with natural organic matter (NOM) does not have a large net effect on the PFAS sorption to CAC on the site. The most reasonable explanation to the post-CAC-injection changes in downstream PFAS concentrations was deemed to be changes in the groundwater flow direction causing bypass or partial bypass of the injected CAC. It was concluded that the distribution of CAC in the subsurface and the extent to which CAC intercepts the PFAS-transporting groundwater are critical to the reduction in PFAS concentrations leaving the contaminated site. The soil characteristics including texture, heterogeneity and existence of preferential flow channels are important factors for the resulting CAC distribution. In a treatment with CAC to limit PFAS migration the goal is to catch as much as possible of the contaminant transport with the injected CAC. Our results show that complex hydrogeological conditions pose a challenge to this goal. For optimal design and placement of a sorptive CAC barrier, it is essential to have a detailed characterization and understanding of soil conditions, groundwater flow directions, including seasonal variations, and flux-zone locations on the local scale of flow through and around the CAC barrier.

How to cite: Fagerlund, F., Niarchos, G., Ahrens, L., Berggren Kleja, D., Bergman, J., Larsson, A., Leonard, G., Forde, J., Schütz, M., and Persson, H.: Lessons learnt from a field trial of colloidal activated carbon injection to reduce PFAS migration from a contaminated site, EGU General Assembly 2022, Vienna, Austria, 23–27 May 2022, EGU22-8076, https://doi.org/10.5194/egusphere-egu22-8076, 2022.

14:31–14:36
Part 3: Field-scale contamination problems
14:36–14:43
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EGU22-11391
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ECS
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On-site presentation
Leonardo Costa and Paolo Salandin

Evidence of pesticides leaching due to intense rainfall events was found in two wellhead protection areas (WHPAs) located in the wine-growing areas of the Veneto piedmont area, in Italy. In this territory, the extensive agricultural activities related to the Prosecco production are developed often using pesticides-based vine protection practices. In the same area, numerous wells extract from the phreatic aquifers the drinking water needs of most of the province of Treviso, rising concern on the possibility of groundwater contamination from pesticides and risks for human health. Further experimental surveys – infiltration tests and soil samplings – were developed in the same WHPAs to study the spatial variability of the chemical-physical properties of the soil governing the pesticides leaching. The experimental data collected on areas of 2 hectares comprising both vineyards and non-agricultural areas, highlighted a larger variability of the soil properties inside the vineyards. Moreover, soil infiltration capacity, assumed in our case as the main property governing the pesticide leaching capacity, showed values up to one order of magnitude higher within the areas destined to wine-growing activities than the non-agricultural ones. This information, obtained at the local and at the field scale, were included in a geospatial analysis related to the distribution of vine-specific pesticides at the scale of the Treviso province, to obtain a vulnerability map for all the wells located in area. The geospatial analysis, developed in a geographical information system (GIS), is based on the sale data of pesticides for agricultural activities - also referred to as plant protection products (PPPs) – registered in the province in the period 2012-2019. The units of PPPs (kilograms or liters) collected at the municipal scale (the province of Treviso counts 94 municipalities) were analyzed by: i) identification of the vine-specific products based on the local guidelines for the vine-protection practices, ii) hazard classification of the vine-specific PPPs based on the CLP pictograms and statements (Classification, Labelling and Packaging Regulation, EC/1272/2008). This information, combined with the extension of the wine-growing areas from land use geographical data (Corine Land Cover 2018), allowed to outline, by assuming the use of the PPP in the municipality of sale, a map showing the hazard level of the wine-growing areas. The geospatial analysis based on the level of superimposition obtained between the extension of the wellhead protection areas and the wine-growing areas, led to a vulnerability map for wells. The map, resulting from the definition in different scenarios of the WHPAs extensions based on a geometrical criterion and the PPPs-based hazard of the vineyards, gives a clear picture of the wells that require PPPs-specific actions to minimize the risk for the quality of the water supplied for human consumption. 

How to cite: Costa, L. and Salandin, P.: Vulnerability of wells supplying drinking water and use of pesticides in wine-growing areas: the Treviso province case study, EGU General Assembly 2022, Vienna, Austria, 23–27 May 2022, EGU22-11391, https://doi.org/10.5194/egusphere-egu22-11391, 2022.

14:43–14:50
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EGU22-1581
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ECS
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On-site presentation
Changmin Kim, Juyeon Lee, Subin Kim, and Minjune Yang

Nitrate (NO3) is the final product of the microbial nitrification process in the subsurface environment and can play a significant factor in potential contamination, causing seasonal hypoxia or eutrophication in the aquatic ecosystem. Excessive nitrogen (N) input by anthropogenic activities is well known as one of the major nitrogen sources such as dissolution of organic or synthetic (NH4+, NO3) fertilizer, leakage of the municipal and industrial landfill, and manure or septic wastewater. This study implemented dual nitrate isotopes approach to investigate the spatial distribution of nitrate contamination and its relative contribution of multiple nitrate sources in Daejeong region, Jeju island, South Korea. A total of 26 groundwater samples were collected from Sangmo, Hamo, and Dongil areas in Daejeong region and their nitrate concentrations were measured. The isotope ratios of N (δ15 NNO3) and O (δ18 ONO3) were analyzed using a denitrifier which converts the dissolved nitrate in the groundwater sample into gaseous nitrous oxide (N2O). The NO3-N concentration above the DWS (drinking water standard, 10 mg/L) was found in 11 out of 19 wells only in Sangmo, while the average NO3-N concentrations of Hamo and Dongil were 2.95 and 2.58 mg/L, respectively. More than 80% of land use in Daejeong region was reported as agricultural farming, and massive synthetic fertilizer usage was expected. However, the δ15 NNO3 ranged from 8.3‰ to 10.2‰, with an average of 9.22‰ and δ18 ONO3 ranged from 3.2 to 6.9‰ with an average of 5.58‰, which are similar values of manure and septic wastewater. Thus, further investigation on land use changes, historical fertilizer consumption and its isotopic shifting in Daejeong region need to be considered for the relative contribution of nitrate sources.

How to cite: Kim, C., Lee, J., Kim, S., and Yang, M.: Dual isotopes evaluation of nitrate contamination and their relative contribution of multiple sources in Daejeong, Jeju island, South Korea, EGU General Assembly 2022, Vienna, Austria, 23–27 May 2022, EGU22-1581, https://doi.org/10.5194/egusphere-egu22-1581, 2022.

Coffee break
Chairperson: Fritjof Fagerlund
15:10–15:17
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EGU22-2659
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ECS
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On-site presentation
Mary Kisaka, Ines Tomašek, George Bennett, Ceven Shemshanga, Jean-Luc Devidald, Karen Fontijn, Wilson Mahene, Kristine Walraevens, Pierre Delmelle, and Matthieu Kervyn

A water quality problem exists in populated areas along the flanks of Mt. Meru in northern Tanzania, with excessively high fluoride (F-) concentrations exceeding the WHO drinking water standards (1.5 mg/L). Little is known about the potential sources of F-among the various rocks types forming the Meru aquifers. Nineteen samples (Debris avalanche deposits (DAD n=4), lava flows n=6, brecciated lava n=4, pumice n=2, scoria n=1, ash n=1, carbonitic n=1) representative of the materials covering the slopes of Mt. Meru were characterized for their mineralogical, chemical, and total and water-soluble F- compositions. Mt. Meru is mainly composed of alkaline volcanic rocks of basaltic to phonolitic composition. The total F- analysis indicated that F-occurs in all rock types with a mean value varying per rock type from 0.6 to 3.2 g/kg. The DAD in the east and northwest of Mt.Meru contained the highest amount of F- (mean 3.1±0.17 g/kg), whilst the lava flow samples had the lowest mean value (0.6±0.25 g/kg). Water rock-interaction experiments further revealed the highest release of F- in the analyzed DAD samples, possibly associated with their weathering status that progressively converted the primary minerals into secondary clay-bearing minerals assemblage, and favoring F- release into the interacting water. Unlike DAD, pumice and ash have a moderately high level of total F- (1.76±0.04 g/kg) yet; release a minimal amount of it through leaching. Petrographic observations showed that the analyzed volcanic rocks consist of volcanic glass and rare F--bearing accessory minerals (amphibole, titanite, biotite, and apatite), among others. Using electron microprobe analysis, the F- concentrations were found to be as high as 3- 6.5 g/kg in the glassy groundmass and up to 4 g/kg, 5 g/kg, and 45 g/kg in accessory phases of titanite, amphibole, and fluorapatite, respectively. Comparing the abundance and the composition of the glassy groundmass with the mineral phases, the former harbors most of the total F-content. The findings of leaching experiments are congruent with past water quality which show that, low F- is found in water from lava and tephra-dominated areas at higher altitudes and Mt. Meru west, respectively. This new information could guide future explorations for safer locations to place wells for water consumption. Itcould also be of interest for other East African Rift sectors and similar volcanic settings.

Keywords: Northern Tanzania, East African Rift, Meru volcano, fluoride contamination, volcanic rocks, leaching

 

How to cite: Kisaka, M., Tomašek, I., Bennett, G., Shemshanga, C., Devidald, J.-L., Fontijn, K., Mahene, W., Walraevens, K., Delmelle, P., and Kervyn, M.: Characterization of volcanic deposits along the slopes of Mount Meru, Northern Tanzania: insights into the potential sources and release of fluoride, EGU General Assembly 2022, Vienna, Austria, 23–27 May 2022, EGU22-2659, https://doi.org/10.5194/egusphere-egu22-2659, 2022.

15:17–15:22
Part 4: Inorganic contaminants and their remediation
15:22–15:29
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EGU22-3693
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ECS
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On-site presentation
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Yikai Liu, Simone Molinari, Maria Chiara Dalconi, Maurizio Pietro Bellotto, Luca Valentini, Giorgio Ferrari, Roberto Pellay, Gabriella Salviulo, and Gilberto Artioli

Solidification/stabilization (S/S) is a versatile process used in contaminated soil remediation. The development of green binders and the associated immobilization mechanisms is imperative to the remediation research due to the aggravated carbon/energy footprints of the widely employed ordinary Portland cement (OPC). In this work, a pyrite ash disposal site, where the soil has high lead and sulfates contents, was selected for lab-scale tests and the following in-situ field trials. Traditional binders (OPC and cement III/B) and alternative binders (calcium aluminate cement, mayenite-blast furnace mix, and alkaline-activated blast furnace slag) were preliminarily applied using the high-performance S/S pelletization treatment (HPSS©). Systematic mineralogical and microstructural characterization and pH-dependent leaching tests were applied to investigate the S/S effectiveness of different scenarios. Subsequently, simulations were developed to identify the minerals controlling the leaching behavior of stabilized pellets. Overall, the proposed methodology is a pertinent tool for extrapolating the contaminated soil HPSS© to realistic conditions.

How to cite: Liu, Y., Molinari, S., Dalconi, M. C., Bellotto, M. P., Valentini, L., Ferrari, G., Pellay, R., Salviulo, G., and Artioli, G.: Mechanisms of in-situ remediation of soil with lead and sulfate contaminants using multiple binder strategies: experimental and numerical studies, EGU General Assembly 2022, Vienna, Austria, 23–27 May 2022, EGU22-3693, https://doi.org/10.5194/egusphere-egu22-3693, 2022.

15:29–15:36
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EGU22-4348
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ECS
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On-site presentation
Lidia Fernandez-Rojo, Miquel Rovira, Irene Jubany, and Vicens Martí

Ferrosorp® Plus (FSP) is a commercial adsorbent obtained from the sludges of drinking water treatment plants, composed of mainly amorphous ferric oxy(hydroxides) and calcite among others impurities. This product is indicated to remove arsenic along with phosphates in water treatments[1]. A novel application can be the in-situ remediation of arsenic polluted aquifers through injection of modified product of a smaller size, allowing higher reactivity and mobility through porous media, as already observed for phosphates[2]. To this end, the original granular product (G-FSP) was sonicated (S-FSP), reducing the size from 0.5-2 mm to 0.001-0.1 mm, and increasing the surface area from 218 m2/g to 233 m2/g, respectively. The only crystalline phase detected with x-ray diffraction (XRD) was calcite, which accounted for 8.3%, as determined by thermogravimetric analysis (TGA).  

Batch kinetics studies of arsenite and arsenate adsorption on these two materials were evaluated at initial pH 4 and pH 9, the two extremes of pH range application according to the manufacturer. Adsorption equilibrium was reached after ~48 h and the experimental results fitted to a pseudo-second order kinetics model.

Adsorption isotherms were determined in batch studies at the equilibrium pH (around 9.5) and fitted to a Freundlich model. It was observed that, despite the slight increase on the surface area in the sonicated by-product, the amount of arsenic adsorbed on both material sizes were similar;   the Freundlich constant for granular and sonicated FSP were, respectively, 10.0 and 12.8 mg(1‑1/n)·L(1/n)/g for As(III), and 5.1 and 5.3 mg(1-1/n)·L(1/n)/g for As(V). The adsorbed arsenic concentrations at equilibrium were simulated using the PHREEQC software and the Dzombak and Morel (1992) surface complexation model. Simulations were fitted to reproduce the experimental results and to elucidate the role of calcite and of the released bicarbonate anions on arsenic adsorption onto FSP[3].  

These experiments provide evidence about the role of the material size and of the calcite on arsenic adsorption, which can be extended to other applications, like aquifers polluted by acid drainage. In this case, the presence of calcite is advantageous as it counteracts acidity while adsorbing arsenic. 

 

Acknowledgements

This work received the financial support of the Torres Quevedo (2019) grant number PTQ2019-010503.


[1] HeGo BIOTEC GmbH, 2015, accessed 09/01/2022, <https://www.ferrosorp.de/english/produkte/ferrosorpplus/index.html>

[2] Martí, V., Jubany, I., Ribas, D., Benito, J. A., & Ferrer, B. (2021). Improvement of Phosphate Adsorption Kinetics onto Ferric Hydroxide by Size Reduction. Water, 13(11), 1558

[3] Appelo, C. A. J., Van der Weiden, M. J. J., Tournassat, C., & Charlet, L. (2002). Surface complexation of ferrous iron and carbonate on ferrihydrite and the mobilization of arsenic. Environmental Science & Technology36(14), 3096-3103.

How to cite: Fernandez-Rojo, L., Rovira, M., Jubany, I., and Martí, V.: Effect of size reduction and calcite impurities on the adsorption of arsenic onto a ferric (hydr)oxide-calcite by-product, EGU General Assembly 2022, Vienna, Austria, 23–27 May 2022, EGU22-4348, https://doi.org/10.5194/egusphere-egu22-4348, 2022.

15:36–15:43
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EGU22-11168
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Virtual presentation
Mustapha Chabane, Khaled Rahoui, Chikh Melkaoui, Benamar Dahmani, and Nacer Ferrah

Waste water treatment using chemicals reagents are effective but pose serious environmental and health problems.Public demand for renewable and biodegradable products grows with awareness of environmental protection, materials of biological origin appear to offer solutions. In our present work, we have synthetized matrix membranes based on different compositions of granulated actived carbonne (GAC),kaolin,Zinc Oxide (ZnO) and Iron Oxyde (Fe2O3). The membrane samples  were characterized by different analytical methods such as FTIR spectroscopy and XRD .The matrix membranes were tested for the removal of toxic metals such as chromium from aqueous solutions  The experimental test were caried on filtration unit .After each filtration test ,the concentraton of the heavy metals were be determined by analytical method . The rejection rate ratio was calculatad refering to the values of the copper and chromium concentration on Feed and permeate .solutions .The results shows the important contribution of natural inorganic matter on the copper and chromium ions from water.

How to cite: Chabane, M., Rahoui, K., Melkaoui, C., Dahmani, B., and Ferrah, N.: Removal of copper and chromnium from water by mixed matrix membranes loaded with natural inorganic fillers, EGU General Assembly 2022, Vienna, Austria, 23–27 May 2022, EGU22-11168, https://doi.org/10.5194/egusphere-egu22-11168, 2022.

15:43–15:50
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EGU22-12154
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ECS
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Virtual presentation
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Claudia Ursino, Sergio Santoro, Ibtissem Ounifi, Amor Hafiane, and Alberto Figoli

Water contamination by traces of heavy metals is a global issue causing serious environmental and health concerns and, as a consequence, an increasing of demand for water remediation technologies. Nowadays, membranes, defined as a selective barrier that permit the separation of molecules or ions in a liquid by a combination of sieving and diffusion mechanisms, have more attention due to their several advantages. In particular, ultrafiltration (UF) is a well-established membrane technology for purification of contaminated water bodies enabling an efficient and cost-saving low-pressure filtration. However, UF membranes possesses a pore size ranging from 20 nm to 0.1 µm, ineffective in rejecting small molecules and ions, such as heavy metals. In this work, a new generation of antifouling UF membranes able to heavy metals remediation has been developed [1]. Specifically, poly (acrylic acid) (PAA) as ideal complexing agent for heavy metals, was blended with cellulose acetate (CA), polymer extensively studied in UF membranes preparation. The novel membranes were prepared via non solvent-induced phase separation (NIPS). These new membranes combine the use of carboxyl group of the PAA that allowing one to efficiently adsorb or chelate heavy metal ions with the processability/biocompatibility/hydrophilicity of the CA. The membranes were produced varying the PAA concentration from 0 to 15wt. %. The homogeneity of the blend was evaluated via differential scanning calorimetry (DSC) and Fourier Transform Infrared Spectroscopy (FTIR). Mitigation of the fouling phenomena and the improvement of the efficiency of the CA membrane on heavy metal rejection was studied and evaluated. The experiments results revealed the important advantages of the blend, since CA/PAA membranes showed superior performance with respect to the neat CA membrane, in terms of: (i) water permeability (20% higher than the neat CA membrane); (ii) Cd rejection (83% at pH 6.5); and (iii) antifouling resistance to humic acid (HA) (R% of 99.9 and 95.3% of flux recovery ratio FRR).

 

[1] I. Ounifi, Y. Guesmi, C. Ursino, S. Santoro, S. Mahfoudhi, A. Figoli, E. Ferjanie, A. Hafiane, Antifouling Membranes Based on Cellulose Acetate (CA) Blended with Poly(acrylic acid) for Heavy Metal Remediation, Appl. Sci. 2021, 11, 4354. https://doi.org/10.3390/app11104354

How to cite: Ursino, C., Santoro, S., Ounifi, I., Hafiane, A., and Figoli, A.: A Novel Cellulose Acetate Fouling-Resistant Ultrafiltration Membranes for Heavy Metal Remediation, EGU General Assembly 2022, Vienna, Austria, 23–27 May 2022, EGU22-12154, https://doi.org/10.5194/egusphere-egu22-12154, 2022.

15:50–15:55