273 results on '"Backhaus, T."'
Search Results
2. Risk assessment of chemicals and their mixtures are hindered by scarcity and inconsistencies between different environmental exposure limits
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Gustavsson, M., Molander, S., Backhaus, T., and Kristiansson, E.
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- 2023
- Full Text
- View/download PDF
3. Dataset of chemicals of emerging concern detected in the marine environment in central and northern Patagonia in Chile (v1.2) [Data set]
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Inostroza, P.A., Soriano, Y., Carmona, Eric, Krauss, Martin, Brack, Werner, Backhaus, T., Quiñones, R.A., Inostroza, P.A., Soriano, Y., Carmona, Eric, Krauss, Martin, Brack, Werner, Backhaus, T., and Quiñones, R.A.
- Abstract
Synthetic organic chemicals, including pesticides, pharmaceuticals, and industrial compounds, pose a growing threat to marine ecosystems. Despite their potential impact, data on the co-occurrence of these contaminants in multiple compartments, including surface water, bottom water, porewater, and sediment in the marine environment remains limited. Such information is critical for assessing coastal chemical status, establishing environmental quality benchmarks, and conducting comprehensive environmental risk assessments. In this study, we describe a multifaceted monitoring campaign targeting pesticides, pharmaceuticals, surfactants, additives, and plasticizers among other synthetic chemicals in four sampling sites. One site was located in the small Coliumo bay affected by urban settlements and tourism in central-south and additionally, we sampled three sites, Caucahue Channel, affected by urban settlements and salmon farming in northern Patagonia in Chile. Surface water, bottom water, porewater, and adjacent sediment samples were collected for target screening analysis in LC- and GC-HRMS platforms. Our results show the detection of up to 83 chemicals in surface water, 71 in bottom water, 101 in porewater, and 244 in sediments. To enhance data utility and reuse potential, we provide valuable information on the mode of action and molecular targets of the identified chemicals. This comprehensive dataset contributes to defining pollution fingerprints in coastal areas of the Global South, including remote regions in Patagonia. It serves as a critical resource for future research including marine chemical risk assessment, policymaking, and the advancement of environmental protection in these regions.
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- 2024
4. Preliminary dataset of emerging contaminants in surface water, bottom water, porewater, and sediment: Urban and aquaculture impacts in Coliumo bay and Caucahue Channel in the central and southern coast of Chile
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Inostroza, P.A., Soriano, Y., Carmona, Eric, Krauss, Martin, Brack, Werner, Backhaus, T., Quiñones, R.A., Inostroza, P.A., Soriano, Y., Carmona, Eric, Krauss, Martin, Brack, Werner, Backhaus, T., and Quiñones, R.A.
- Abstract
Synthetic organic chemicals, including pesticides, pharmaceuticals, and industrial compounds, pose a growing threat to marine ecosystems. Despite their potential impact, data on the co-occurrence of these contaminants in multiple compartments, including surface water, bottom water, porewater, and sediment in the marine environment remains limited. Such information is critical for assessing coastal chemical status, establishing environmental quality benchmarks, and conducting comprehensive environmental risk assessments. In this study, we describe a multifaceted monitoring campaign targeting pesticides, pharmaceuticals, surfactants, additives, and plasticizers among other synthetic chemicals in four sampling sites. One site was located in the small Coliumo bay affected by urban settlements and tourism in central-south and additionally, we sampled three sites, Caucahue Channel, affected by urban settlements and salmon farming in northern Patagonia in Chile. Surface water, bottom water, porewater, and adjacent sediment samples were collected for target screening analysis in LC- and GC-HRMS platforms. Our results show the detection of up to 83 chemicals in surface water, 71 in bottom water, 101 in porewater, and 244 in sediments. To enhance data utility and reuse potential, we provide valuable information on the mode of action and molecular targets of the identified chemicals. This comprehensive dataset contributes to defining pollution fingerprints in coastal areas of the Global South, including remote regions in Patagonia. It serves as a critical resource for future research including marine chemical risk assessment, policymaking, and the advancement of environmental protection in these regions.
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- 2024
5. Co-occurrence and spatial distribution of organic micropollutants in surface waters of the River Aconcagua and Maipo basins in Central Chile
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Soriano, Y., Carmona, Eric, Renovell, J., Picó, Y., Brack, Werner, Krauss, Martin, Backhaus, T., Inostroza, P.A., Soriano, Y., Carmona, Eric, Renovell, J., Picó, Y., Brack, Werner, Krauss, Martin, Backhaus, T., and Inostroza, P.A.
- Abstract
Organic Micropollutants (OMPs) might pose significant risks to aquatic life and have potential toxic effects on humans. These chemicals typically occur as complex mixtures rather than individually. Information on their co-occurrence and their association with land use is largely lacking, even in industrialized countries. Furthermore, data on the presence of OMPs in freshwater ecosystems in South America is insufficient. Consequently, we assessed the co-occurrence and distribution of OMPs, including pharmaceuticals, pesticides, personal care products, surfactants, and other industrial OMPs, in surface waters of two river basins in central Chile. We focused on identifying and ranking quantified chemicals, classifying their mode of actions, as well as correlating their occurrence with distinct land uses. We identified and quantified 311 compounds that occurred at least once in the River Aconcagua and River Maipo basins, encompassing compounds from urban, agricultural, industrial, and pharmaceutical sectors. Pharmaceuticals were the most frequently occurring chemicals, followed by pesticides, personal care and household products. OMPs with neuroactive properties dominated surface waters in Central Chile, along with OMPs known to alter the cardiovascular and endocrine systems of humans and aquatic animals. Finally, we observed positive correlations between agricultural and urban land uses and OMPs. Our findings represent a step forward in extending current knowledge on the co-occurrence patterns of OMPs in aquatic environments, particularly in developing countries of the southern hemisphere.
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- 2024
6. A multi-scenario risk assessment strategy applied to mixtures of chemicals of emerging concern in the River Aconcagua basin in Central Chile
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Inostroza, P.A., Elgueta, S., Krauss, Martin, Brack, Werner, Backhaus, T., Inostroza, P.A., Elgueta, S., Krauss, Martin, Brack, Werner, and Backhaus, T.
- Abstract
Streams and rivers are characterised by the presence of various chemicals of emerging concern (CECs), including pesticides, pharmaceuticals, personal care products, and industrial chemicals. While these chemicals are found usually only in low (ng/L) concentrations, they might still harm aquatic life and disrupt the ecological balance of aquatic ecosystems due to their high ecotoxicological potency. Environmental risk assessments that account for the complexity of exposures are needed in order to evaluate the toxic pressure of these chemicals, which also provide suggestions for risk mitigation and management, if necessary. Currently, most studies on the co-occurrence and environmental impacts of CECs are conducted in countries of the Global North, leaving massive knowledge gaps in countries of the Global South. In this study, we implement a multi-scenario risk assessment strategy to improve the assessment of both the exposure and hazard components in the chemical risk assessment process. Our strategy incorporates a systematic consideration and weighting of CECs that were not detected, as well as an evaluation of the uncertainties associated with Quantitative Structure-Activity Relationships (QSARs) predictions for chronic ecotoxicity. Furthermore, we present a novel approach to identifying mixture risk drivers. To expand our knowledge beyond well-studied aquatic ecosystems, we applied this multi-scenario strategy to the River Aconcagua basin of Central Chile. The analysis revealed that the concentrations of CECs exceeded acceptable risk thresholds for selected organism groups and the most vulnerable taxonomic groups. Streams flowing through agricultural areas and sites near the river mouth exhibited the highest risks. Notably, the eight risk drivers among the 153 co-occurring chemicals accounted for 66-92% of the observed risks in the river basin. Six of them are pesticides and pharmaceuticals, chemical classes known for their high biological activity in spe
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- 2024
7. Defining the data gap: what do we know about environmental exposure, hazards and risks of pharmaceuticals in the European aquatic environment?
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Spilsbury, F.D., primary, Inostroza, P.A., additional, Svedberg, P., additional, Cannata, C., additional, Ragas, A.M.J., additional, and Backhaus, T., additional
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- 2023
- Full Text
- View/download PDF
8. Dataset of chemicals of emerging concern (CECs) in surface water in the Swedish west coast (Stenungsund) (v1.0) [Data set]
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Inostroza, Pedro, Carmona, Eric, Arrhenius, Å., Krauss, Martin ; orcid:0000-0002-0362-4244, Brack, Werner, Backhaus, T., Inostroza, Pedro, Carmona, Eric, Arrhenius, Å., Krauss, Martin ; orcid:0000-0002-0362-4244, Brack, Werner, and Backhaus, T.
- Abstract
The aquatic environment faces increasing threats from a variety of unregulated organic chemicals originating from human activities, collectively known as chemicals of emerging concern (CECs). These include pharmaceuticals, personal-care products, pesticides, surfactants, industrial chemicals, and their transformation products. CECs enter aquatic environments through various sources, including effluents from wastewater treatment plants, industrial facilities, runoff from agricultural and residential areas, as well as accidental spills. Data on the occurrence of CECs in the marine environment are scarce, and more information is needed to assess the chemical and ecological status of water bodies, and to prioritize toxic chemicals for further studies or risk assessment. In this study, we describe a monitoring campaign targeting CECs in surface waters at the Swedish west coast using, for the first time, an on-site large volume solid phase extraction (LVSPE) device. We detected up to 80 and 227 CECs in marine sites and the wastewater treatment plant (WWTP) effluent, respectively. The dataset will contribute to defining pollution fingerprints and assessing the chemical status of marine and freshwater systems affected by industrial hubs, agricultural areas, and the discharge of urban wastewater.
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- 2023
9. A dataset of organic pollutants identified and quantified in recycled polyethylene pellets
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Carmona, Eric, Rojo-Nieto, Elisa, Rummel, Christoph, Krauss, Martin, Syberg, K., Ramos, T.M., Brosche, S., Backhaus, T., Carney Almroth, B., Carmona, Eric, Rojo-Nieto, Elisa, Rummel, Christoph, Krauss, Martin, Syberg, K., Ramos, T.M., Brosche, S., Backhaus, T., and Carney Almroth, B.
- Abstract
Plastics are produced with a staggering array of chemical compounds, with many being known to possess hazardous properties, and others lacking comprehensive hazard data. Furthermore, non-intentionally added substances can contaminate plastics at various stages of their lifecycle, resulting in recycled materials containing an unknown number of chemical compounds at unknown concentrations. While some national and regional regulations exist for permissible concentrations of hazardous chemicals in specific plastic products, less than 1% of plastics chemicals are subject to international regulation. There are currently no policies mandating transparent reporting of chemicals throughout the plastics value chain or comprehensive monitoring of chemicals in recycled materials. The dataset presented here provides the chemical analysis of 28 samples of recycled High-Density Polyethylene (HDPE) pellets obtained from various regions of the Global South, along with a reference sample of virgin HDPE. The analysis comprises both Target and Non-Targeted Screening approaches, employing Liquid Chromatography-High-Resolution Mass Spectrometry (LC-HRMS) and Gas Chromatography-High-Resolution Mass Spectrometry (GC-HRMS). In total, 491 organic compounds were detected and quantified, with an additional 170 compounds tentatively annotated. These compounds span various classes, including pesticides, pharmaceuticals, industrial chemicals, plastic additives. The results highlight the prevalence of certain chemicals, such as N-ethyl-o-Toluesulfonamide, commonly used in HDPE processing, found in high concentrations. The paper provides a dataset advancing knowledge of the complex chemical composition associated with recycled plastics.  
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- 2023
10. A dataset of organic pollutants identified and quantified in recycled polyethylene pellets [Dataset]
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Carmona, Eric, Rojo-Nieto, Elisa, Rummel, Christoph, Krauss, Martin, Syberg, K., Ramos, T.M., Brosche, S., Backhaus, T., Carney Almroth, B., Carmona, Eric, Rojo-Nieto, Elisa, Rummel, Christoph, Krauss, Martin, Syberg, K., Ramos, T.M., Brosche, S., Backhaus, T., and Carney Almroth, B.
- Abstract
Plastics are produced with a staggering array of chemical compounds, with many being known to possess hazardous properties, and others lacking comprehensive hazard data. Furthermore, non-intentionally added substances can contaminate plastics at various stages of their lifecycle, resulting in recycled materials containing an unknown number of chemical compounds at unknown concentrations. While some national and regional regulations exist for permissible concentrations of hazardous chemicals in specific plastic products, less than 1% of plastics chemicals are subject to international regulation. There are currently no policies mandating transparent reporting of chemicals throughout the plastics value chain or comprehensive monitoring of chemicals in recycled materials. The dataset presented here provides the chemical analysis of 28 samples of recycled High-Density Polyethylene (HDPE) pellets obtained from various regions of the Global South, along with a reference sample of virgin HDPE. The analysis comprises both Target and Non-Targeted Screening approaches, employing Liquid Chromatography-High-Resolution Mass Spectrometry (LC-HRMS) and Gas Chromatography-High-Resolution Mass Spectrometry (GC-HRMS). In total, 491 organic compounds were detected and quantified, with an additional 170 compounds tentatively annotated. These compounds span various classes, including pesticides, pharmaceuticals, industrial chemicals, plastic additives. The results highlight the prevalence of certain chemicals, such as N-ethyl-o-Toluesulfonamide, commonly used in HDPE processing, found in high concentrations. The paper provides a dataset advancing knowledge of the complex chemical composition associated with recycled plastics.  
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- 2023
11. Target screening of chemicals of emerging concern (CECs) in surface waters of the Swedish west coast
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Inostroza, Pedro, Carmona, Eric, Arrhenius, Å., Krauss, Martin, Brack, Werner, Backhaus, T., Inostroza, Pedro, Carmona, Eric, Arrhenius, Å., Krauss, Martin, Brack, Werner, and Backhaus, T.
- Abstract
The aquatic environment faces increasing threats from a variety of unregulated organic chemicals originating from human activities, collectively known as chemicals of emerging concern (CECs). These include pharmaceuticals, personal-care products, pesticides, surfactants, industrial chemicals, and their transformation products. CECs enter aquatic environments through various sources, including effluents from wastewater treatment plants, industrial facilities, runoff from agricultural and residential areas, as well as accidental spills. Data on the occurrence of CECs in the marine environment are scarce, and more information is needed to assess the chemical and ecological status of water bodies, and to prioritize toxic chemicals for further studies or risk assessment. In this study, we describe a monitoring campaign targeting CECs in surface waters at the Swedish west coast using, for the first time, an on-site large volume solid phase extraction (LVSPE) device. We detected up to 80 and 227 CECs in marine sites and the wastewater treatment plant (WWTP) effluent, respectively. The dataset will contribute to defining pollution fingerprints and assessing the chemical status of marine and freshwater systems affected by industrial hubs, agricultural areas, and the discharge of urban wastewater.
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- 2023
12. Dataset comprising pesticides, pharmaceuticals and personal care products, and industrial chemicals detected in streams and rivers of Central Chile
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Inostroza, P.A., Elgueta, S., Muz, Melis, Krauss, Martin, Brack, Werner, Backhaus, T., Inostroza, P.A., Elgueta, S., Muz, Melis, Krauss, Martin, Brack, Werner, and Backhaus, T.
- Abstract
Chemical pollution caused by synthetic organic chemicals at low concentrations in the environment poses a growing threat to the ecological status of aquatic ecosystems. These chemicals are regularly released into surface waters through both treated and untreated effluents from wastewater treatment plants (WWTPs), agricultural runoff, and industrial discharges. Consequently, they accumulate in surface waters, distribute amongst environmental compartments according to their physicochemical properties, and cause adverse effects on aquatic organisms. Unfortunately, there is a lack of data regarding the occurrence of synthetic organic chemicals, henceforth micropollutants, in South American freshwater ecosystems, especially in Chile.To address this research gap, we present a comprehensive dataset comprising concentrations of 153 emerging chemicals, including pesticides, pharmaceutical and personal care products (PPCPs), surfactants, and industrial chemicals. These chemicals were found to co-occur in surface waters within Central Chile, specifically in the River Aconcagua Basin. Our sampling strategy involved collecting surface water samples from streams and rivers with diverse land uses, such as agriculture, urban areas, and natural reserves. For sample extraction, we employed an on-site large-volume solid phase extraction (LVSPE) device. The resulting environmental extracts were then subjected to wide-scope chemical target screening using gas chromatography and liquid chromatography high-resolution mass spectrometry (GC- and LCHRMS).The dataset we present holds significant value in assessing the chemical status of water bodies. It enables comparative analysis of pollution fingerprints associated with emerging chemicals across different freshwater systems. Moreover, the data can be reused for environmental risk assessment studies. Its utilisation will contribute to a better understanding of the impact and extent of chemical pollution in aquatic ecosystems, facilitating t
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- 2023
13. Dataset of chemicals of emerging concern detected in streams and rivers of Central Chile (v1.0) [Data set]
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Inostroza, Pedro, Elgueta, S., Muz, Melis, Krauss, Martin, Brack, Werner, Backhaus, T., Inostroza, Pedro, Elgueta, S., Muz, Melis, Krauss, Martin, Brack, Werner, and Backhaus, T.
- Abstract
The aquatic environment faces increasing threats from a variety of unregulated organic chemicals originating from human activities, collectively known as chemicals of emerging concern (CECs). These include pharmaceuticals, personal-care products, pesticides, surfactants, industrial chemicals, and their transformation products. CECs enter aquatic environments through various sources, including effluents from wastewater treatment plants, industrial facilities, runoff from agricultural and residential areas, as well as accidental spills. Data on the occurrence of CECs in the marine environment are scarce, and more information is needed to assess the chemical and ecological status of water bodies, and to prioritize toxic chemicals for further studies or risk assessment. In this study, we describe a monitoring campaign targeting CECs in surface waters at the Swedish west coast using, for the first time, an on-site large volume solid phase extraction (LVSPE) device. We detected up to 80 and 227 CECs in marine sites and the wastewater treatment plant (WWTP) effluent, respectively. The dataset will contribute to defining pollution fingerprints and assessing the chemical status of marine and freshwater systems affected by industrial hubs, agricultural areas, and the discharge of urban wastewater.
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- 2023
14. SCHEER (Scientific Committee on Health, Environmental and Emerging Risks), SCHEER Position Paper on 'Draft Environmental Quality Standards for Priority Substances under the Water Framework Directive', 3 April 2023
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Scott, M., Vighi, M., Backhaus, T., Borges, T., de Voogt, P., Hoet, P., Ion, R.M., Johnson, A., and Linders, J.
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- 2023
15. SCHEER (Scientific Committee on Health, Environmental and Emerging Risks), Final Opinion on Draft Environmental Quality Standards for Priority Substances under the Water Framework Directive' - PAHs, 9 March 2023
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Scott, M, Vighi, M., Backhaus, T., Borges, T., de Voogt, P., Hoet, P., Ion, R.M., Johnson, A., and Linders, J.
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- 2023
16. An effective set of principles for practical implementation of marine cumulative effects assessment
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Judd, A.D., Backhaus, T., and Goodsir, F.
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- 2015
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17. SCHEER (Scientific Committee on Health, Environmental and Emerging Risks), Final Opinion on Draft Environmental Quality Standards for Priority Substances under the Water Framework Directive - nonylphenol, 11 November 2022
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Scott, M., Vighi, M., Backhaus, T., Borges, T., Duarte Davidson, R., Hoet, P., and de Voogt, P.
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- 2022
18. On the Ecotoxicology of Pharmaceutical Mixtures
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Backhaus, T., Sumpter, J., Blanck, H., and Kümmerer, Klaus, editor
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- 2008
- Full Text
- View/download PDF
19. SCHEER (Scientific Committee on Health, Environmental and Emerging Risks), Final Opinion on Draft Environmental Quality Standards for Priority Substances under the Water Framework Directive - diclofenac, 2 August 2022
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Scott, M., Vighi, M., Backhaus, T., Borges, T., de Voogt, P., Hoet, P., and Ion, R.M.
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- 2022
20. SCHEER (Scientific Committee on Health, Environmental and Emerging Risks), Final opinion on groundwater quality standards for proposed additional pollutants in the annexes to the Groundwater Directive (2006/118/EC). 18 July 2022
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Scott, M., Backhaus, T., Borges, T., Hoet, P., Vighi, M., de Voogt, P., Johnson, A., and Linders, J.
- Published
- 2022
21. Colloidal silica nanomaterials reduce the toxicity of pesticides to algae, depending on charge and surface area
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Book, F., Persson, M., Carmona, Eric, Backhaus, T., Lammel, T., Book, F., Persson, M., Carmona, Eric, Backhaus, T., and Lammel, T.
- Abstract
Colloidal silica nanomaterials are promising adsorbents for aquatic pollutants. The present study quantifies the toxicity reduction of differently charged pesticides (paraquat (cationic), pentachlorophenol (anionic) and diflufenican (uncharged)) by co-exposure to weakly anionic, strongly anionic and cationic silica nanomaterials in growth tests with freshwater green algae. The hypothesis was that the silica nanomaterials would preferentially adsorb the oppositely charged pesticide and reduce algal toxicity accordingly. Three different concentrations of each spherical nanomaterial (10, 20 and 50 mg L-1) were tested in mixtures with a fixed pesticide concentration (4 mu M paraquat (EC60), 0.002 mu M diflufenican (EC80) and 0.2 mu M pentachlorophenol (EC90)). In addition, we investigated the role of the specific surface area by comparing the performance of the anionic spherical silica nanomaterial with the anionic elongated silica nanomaterial (0.4-16 mg L-1). Adsorption of pesticides onto the various nanomaterials was confirmed by chemical analysis of the supernatants after removing the nanomaterial with ultracentrifugation. The results show that a concentration of 16 mg L-1 and 50 mg L-1 of the spherical and elongated strongly anionic silica, respectively, completely annulled paraquat toxicity. The cationic nanomaterial reduced pentachlorophenol toxicity by 30-50% at all test concentrations, but the effect seems to be influenced by pH and phosphate concentration of the test medium. The cationic silica also reduced the toxicity of diflufenican by 10-20%, likely due to non-electrostatic interactions. The study further indicates that the presence of algae affects the NM-pesticide equilibrium since the pesticide is taken up by the organism instead of being bound to the NM.
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- 2022
22. SCHEER (Scientific Committee on Health, Environmental and Emerging Risks), Final Opinion on Draft Environmental Quality Standards for Priority Substances under the Water Framework Directive - Chlorpyrifos, 15-16 June 2022
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Scott, M., Vighi, M., Backhaus, T., Borges, T., de Voogt, P., Hoet, P., Ion, R.M., Johnson, A., and Linders, J.
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- 2022
23. Evidence for X(3872) in Pb-Pb Collisions and Studies of its Prompt Production at root s(NN)=5.02 TeV
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Sirunyan, A. M., Tumasyan, A., Adam, W., Ambrogi, F., Bergauer, T., Dragicevic, M., Ero, J., Del, Valle, Escalante, A., Flechl, M., Fruhwirth, R., Jeitler, M., Krammer, N., Kratschmer, I, Liko, D., Madlener, T., Mikulec, I, Rad, N., Schieck, J., Schofbeck, R., Spanring, M., Waltenberger, W., Wulz, C-E, Zarucki, M., Drugakov, V, Mossolov, V, Gonzalez, Suarez, J., Darwish, M. R., Wolf, De, E. A., Croce, Di, Janssen, D., Kello, X., Lelek, T., Pieters, A., Sfar, M., Rejeb, H., Van, Haevermaet, Van, Mechelen, Van, Putte, Van, Remortel, Blekman, N., Bols, F., Chhibra, E. S., D'Hondt, S. S., Clercq, De, Lontkovskyi, J., Lowette, D., Marchesini, S., Moortgat, I, Python, S., Tavernier, Q., Van, Doninck, Van, Mulders, Beghin, P., Bilin, D., Clerbaux, B., Lentdecker, De, Delannoy, G., Dorney, H., Favart, B., Grebenyuk, L., Kalsi, A., Moureaux, A. K., Popov, L., Postiau, A., Starling, N., Thomas, E., L. V., Velde, Er, Vanlaer, C., Vannerom, P., Cornelis, D., Dobur, T., Khvastunov, D., Niedziela, I, Roskas, M., Skovpen, C., Tytgat, K., Verbeke, M., Vermassen, W., Vit, B., Bruno, M., Caputo, G., David, C., Delaere, P., Delcourt, C., Giammanco, M., Lemaitre, A., Prisci, V, Aro, J., Saggio, A., Vischia, P., Zobec, J., Alves, G. A., Silva, Correia, G., Hensel, C., Moraes, A., Batista Das Chagas, Belchior, E., Carvalho, W., Chinellato, J., Coelho, E., Costa, Da, E. M., Silveira, Da, Damiao, G. G., De Jesus, D., Martins, De Oliveira, C., Souza, De, Fonseca, S., Malbouisson, H., Martins, J., Figueiredo, Matos, D., Jaime, Medina, M., Almeida, De, Melo, M., Herrera, Mora, C., Mundim, L., Nogima, H., Prado Da Silva, Teles, W. L., Rebello, P., Rosas, Sanchez, L. J., Santoro, A., Sznajder, A., Thiel, M., Tonelli, Manganote, E. J., Da Silva De Araujo, Torres, F., Pereira, Vilela, A., Bernardes, C. A., Calligaris, L., Fern, ez Perez Tomei, Gregores, T. R., Lemos, E. M., Mercadante, D. S., Novaes, P. G., Padula, S. F., S, Ra, S., Aleks, Rov, Antchev, A., Hadjiiska, G., Iaydjiev, R., Misheva, P., Rodozov, M., Shopova, M., Sultanov, M., Bonchev, G., Dimitrov, M., Ivanov, A., Litov, T., Pavlov, L., Petkov, B., Petrov, P., Fang, A., Gao, W., Yuan, X., Ahmad, L., Hu, M., Wang, Z., Chen, Y., Chen, G. M., Chen, H. S., Jiang, M., Leggat, C. H., Liao, D., Liu, H., Spiezia, Z., Tao, A., Yazgan, J., Zhang, E., Zhang, H., Zhao, S., Agapitos, J., Ban, A., Levin, G., Li, A., Li, J., Li, L., Mao, Q., Qian, Y., Wang, S. J., Wang, D., Xiao, Q., Avila, M., Cabrera, C., Florez, A., Gonzalez, Hern, C. F., Ez, Segura, Delgado, M. A., Mejia, Guisao, Ruiz, Alvarez, J. D., Salazar, Gonzalez, C. A., Vanegas, Arbelaez, Godinovic, N., Lelas, N., Puljak, D., Sculac, I, Antunovic, T., Kovac, Z., Brigljevic, M., Ferencek, V, Kadija, D., Mesic, K., Roguljic, B., Starodumov, M., Susa, A., Ather, T., Attikis, M. W., Erodotou, A., Ioannou, E., Kolosova, A., Konstantinou, M., Mavromanolakis, S., Mousa, G., Nicolaou, J., Ptochos, C., Razis, F., Rykaczewski, P. A., Saka, H., Tsiakkouri, H., Finger, D., Finger, M., r. M., J, Kveton, A., Tomsa, J., Ayala, E., Jarrin, Carrera, E., Mahmoud, M. A., Mohammed, Y., Bhowmik, S., Antunes De Oliveira, Carvalho, A., Dewanjee, R. K., Ehataht, K., Kadastik, M., Raidal, M., Veelken, C., Eerola, P., Forthomme, L., Kirschenmann, H., Osterberg, K., Voutilainen, M., Garcia, F., Havukainen, J., Heikkila, J. K., Karimaki, V, Kim, M. S., Kinnunen, R., Lampen, T., Lassila-Perini, K., Laurila, S., Lehti, S., Linden, T., Siikonen, H., Tuominen, E., Tuominiemi, J., Luukka, P., Tuuva, T., Besancon, M., Couderc, F., Dejardin, M., Denegri, D., Fabbro, B., Faure, J. L., Ferri, F., Ganjour, S., Givernaud, A., Gras, P., Monchenault, De, Hamel, G., Jarry, P., Leloup, C., Lenzi, B., Locci, E., Malcles, J., R, Er, Rosowsky, J., Sahin, A., Savoy-Navarro, M. O., Titov, A., Yu, M., Ahuja, G. B., Amendola, S., Beaudette, C., Bonanomi, F., Busson, M., Charlot, P., Diab, C., Falmagne, B., Cassagnac, De, Granier, R., Kucher, I, Lobanov, A., Perez, Martin, C., Nguyen, M., Och, O, Paganini, C., Rembser, P., Salerno, J., Sauvan, R., Sirois, J. B., Zabi, Y., Zghiche, A., Agram, A., J-L, Rea, Bloch, J., Bourgatte, D., Brom, G., J-M, Chabert, Collard, E. C., Conte, C., Fontaine, E., J-C, Gele, Goerlach, D., Grimault, U., Bihan, Le, A-C, Tonon, Van, Hove, Gadrat, P., Beauceron, S., Bernet, S., Boudoul, C., Camen, G., Carle, C., Chanon, A., Chierici, N., Contardo, R., Depasse, D., Mamouni, El, Fay, H., Gascon, J., Gouzevitch, S., Ille, M., Jain, B., Laktineh, Sa, Lattaud, I. B., Lesauvage, H., Lethuillier, A., Mirabito, M., Perries, L., Sordini, S., Torterotot, V, Touquet, L., G. V., Donckt, Er, Viret, M., Toriashvili, S., Tsamalaidze, T., Autermann, Z., Feld, C., Klein, L., Lipinski, K., Meuser, M., Pauls, D., Preuten, A., Rauch, M., Schulz, M. P., Teroerde, J., Erdmann, M., Fischer, M., Ghosh, B., Hebbeker, S., Hoepfner, T., Keller, K., Mastrolorenzo, H., Merschmeyer, L., Meyer, M., Millet, A., Mocellin, P., Mondal, G., Mukherjee, S., Noll, S., Novak, D., Pook, A., Pozdnyakov, T., Quast, A., Radziej, T., Rath, M., Reithler, Y., Roemer, H., Schmidt, J., Schuler, A., Sharma, S. C., Wiedenbeck, A., Zaleski, S., Flugge, S., Ahmad, G., Haj, W., Hlushchenko, O., Kress, T., Muller, T., Nowack, A., Pistone, C., Pooth, O., Roy, D., Sert, H., Stahl, A., Martin, Aldaya, M., Asmuss, P., Babounikau, I, Bakhshiansohi, H., Beernaert, K., Behnke, O., Martinez, Bermudez, A., Bin, Anuar, Borras, A. A., Botta, K., Campbell, V, Cardini, A., Connor, A., Rodriguez, P., Consuegra, S., Contreras-Campana, C., Danilov, V, Wit, De, Defranchis, A., Pardos, M. M., Diez, C., Damiani, Dominguez, D., Eckerlin, G., Eckstein, D., Eichhorn, T., Elwood, A., Eren, E., Banos, Estevez, L. I., Gallo, E., Geiser, A., Grohsjean, A., Guthoff, M., Haranko, M., Harb, A., Jafari, A., Jomhari, N. Z., Jung, H., Kasem, A., Kasemann, M., Kaveh, H., Keaveney, J., Kleinwort, C., Knolle, J., Krucker, D., Lange, W., Lenz, T., Lidrych, J., Lipka, K., Lohmann, W., Mankel, R., Melzer-Pellmann, I-A, Meyer, A. B., Missiroli, M., Mnich, J., Mussgiller, A., Myronenko, V, Adan, Perez, D., Pflitsch, S. K., Pitzl, D., Raspereza, A., Saibel, A., Savitskyi, M., Scheurer, V, Schutze, P., Schwanenberger, C., Shevchenko, R., Singh, A., Ricardo, Sosa, R. E., Tholen, H., Turkot, O., Vagnerini, A., Van De Klundert, Walsh, M., Wen, R., Wichmann, Y., Wissing, K., Zenaiev, C., Zlebcik, O., Aggleton, R., Bein, R., Benato, S., Benecke, L., Dreyer, A., Ebrahimi, T., Feindt, A., Frohlich, F., Garbers, A., Garutti, C., Gonzalez, E., Gunnellini, D., Haller, P., Hinzmann, J., Karavdina, A., Kasieczka, A., Klanner, G., Kogler, R., Kovalchuk, R., Kurz, N., Kutzner, S., Lange, V, Lange, J., Malara, T., Multhaup, A., Niemeyer, J., Reimers, C. E. N., Rieger, A., Schleper, O., Schumann, P., Schw, S., T, J., Sonneveld, J., Stadie, H., Steinbruck, G., Vormwald, B., Zoi, I, Akbiyik, M., Baselga, M., Baur, S., Berger, T., Butz, E., Caspart, R., Chwalek, T., Boer, De, Dierlamm, W., Morabit, El, Faltermann, K., Giffels, N., Gottmann, M., Hartmann, A., Heidecker, F., Husemann, C., Iqbal, U., Kudella, M. A., Maier, S., Mitra, S., Mozer, S., Muller, M. U., Muller, D., Musich, Th, Nurnberg, M., Rabbertz, G., Savoiu, K., Schafer, D., Schnepf, D., Schroder, M., Shvetsov, M., Simonis, I, Ulrich, H. J., Wassmer, R., Weber, M., Wohrmann, M., Wolf, C., Wozniewski, R., Anagnostou, S., Asenov, G., Daskalakis, P., Geralis, G., Kyriakis, T., Loukas, A., Paspalaki, D., Stakia, G., Diamantopoulou, A., Karathanasis, M., Kontaxakis, G., Manousakis-katsikakis, P., Panagiotou, A., Papavergou, A., Saoulidou, I, Theofilatos, N., Vellidis, K., Vourliotis, K., Bakas, E., Kousouris, G., Papakrivopoulos, K., Tsipolitis, I, Zacharopoulou, G., Evangelou, A., Foudas, I, Gianneios, C., Katsoulis, P., Kokkas, P., Mallios, P., Manitara, S., Manthos, K., Papadopoulos, N., Strologas, I, Triantis, J., Tsitsonis, F. A., Bartok, D., Chudasama, M., Csanad, R., Major, M., P. M., Al, K., Mehta, A., Pasztor, G., Suranyi, O., Veres, I, Bencze, G., Hajdu, G., Horvath, C., Sikler, D., Veszpremi, F., Vesztergombi, V., Beni, G., Czellar, N., Karancsi, S., Molnar, J., Szillasi, J., Raics, Z., Teyssier, P., Trocsanyi, D., Ujvari, Z. L., Csorgo, B., Metzger, T., Nemes, W. J., Novak, F., Choudhury, T., Komaragiri, S., Tiwari, J. R., Bahinipati, P. C., Kar, S., Kole, C., Mal, G., Bindhu, P., Muraleedharan Nair, V. K., Nayak, A., Sahoo, D. K., Swain, S. K., Bansal, S., Beri, S. B., Bhatnagar, V, Chauhan, S., Dhingra, N., Gupta, R., Kaur, A., Kaur, M., Kaur, S., Kumari, P., Lohan, M., Meena, M., Eep, S, Sharma, K., Singh, S., Virdi, J. B., Walia, A. K., Bhardwaj, G., Choudhary, A., Garg, B. C., Gola, R. B., Keshri, M., Kumar, S., Ashok, Naimuddin, Priyanka, M., Ranjan, P., Shah, K., Aashaq, Sharma, Bhardwaj, R., Bharti, R., Bhattacharya, M., Bhattacharya, R., Bhaw, S., Eep, U., Bhowmik, D., Dutta, S., Ghosh, S., Gomber, B., Maity, M., Mondal, K., N, An, Purohit, S., Rout, A., Saha, P. K., Sarkar, G., Sharan, S., Singh, M., Thakur, B., Behera, S., Behera, P. K., Kalbhor, S. C., Muhammad, P., Pujahari, A., Sharma, P. R., Sikdar, A., Dutta, A. K., Jha, D., Mishra, V, Netrakanti, D. K., Pant, P. K., Shukla, L. M., Aziz, P., Bhat, T., Dugad, M. A., Mohanty, S., Sur, G. B., Verma, N., Ravindra, Kumar, Banerjee, S., Bhattacharya, S., Chatterjee, S., Das, P., Guchait, M., Karmakar, S., Majumder, G., Mazumdar, K., Sahoo, N., Sawant, S., Dube, S., Kansal, B., Kapoor, A., Kothekar, K., P, Ey, Rane, S., Rastogi, A., Sharma, A., Chenarani, S., Etesami, S., Khakzad, S. M., Najafabadi, M., Mohammadi, M., Naseri, M., Hosseinabadi, Rezaei, F., Felcini, M., Grunewald, M., Abbrescia, M., Aly, R., Calabria, C., Colaleo, A., Creanza, D., Cristella, L., Filippis, De, Palma, De, Florio, Di, Elmetenawee, A., Fiore, W., Gelmi, L., Iaselli, A., Ince, G., Lezki, M., Maggi, S., Maggi, G., Merlin, M., Miniello, J. A., My, G., Nuzzo, S., Pompili, S., Pugliese, A., Radogna, G., Ranieri, R., Selvaggi, A., Silvestris, G., Simone, L., Venditti, F. M., Verwilligen, R., Abbiendi, P., Battilana, G., Bonacorsi, C., Borgonovi, D., Braibant-Giacomelli, L., Campanini, S., Capiluppi, R., Castro, P., Cavallo, A., Codispoti, F. R., Cuffiani, G., Dallavalle, M., Fabbri, G. M., Fanfani, F., Fontanesi, A., Giacomelli, E., Giommi, P., Gr, L., I, C., Guiducci, L., Iemmi, F., Meo, Lo, Marcellini, S., Masetti, S., Navarria, G., Perrotta, F. L., Primavera, A., Rossi, F., Rovelli, A. M., Siroli, T., Tosi, G. P., Albergo, N., Costa, S., Mattia, Di, Potenza, A., Tricomi, R., Tuve, A., Barbagli, C., Cassese, G., Ceccarelli, A., Ciulli, R., Civinini, V, D'Aless, C., Ro, R., Fiori, F., Focardi, E., Latino, G., Lenzi, P., Meschini, M., Paoletti, S., Sguazzoni, G., Viliani, L., Benussi, L., Bianco, S., Piccolo, D., Bozzo, M., Ferro, F., Mulargia, R., Robutti, E., Tosi, S., Benaglia, A., Beschi, A., Brivio, F., Ciriolo, V, Dinardo, M. E., Dini, P., Gennai, S., Ghezzi, A., Govoni, P., Guzzi, L., Malberti, M., Malvezzi, S., Menasce, D., Monti, F., Moroni, L., Paganoni, M., Pedrini, D., Ragazzi, S., Fatis, De, Tabarelli, T., Valsecchi, D., Zuolo, D., Buontempo, S., Cavallo, N., Iorio, De, Crescenzo, Di, Fabozzi, A., Fienga, F., Galati, F., Iorio, G., Layer, A. O. M., Lista, L., Meola, L., Paolucci, S., Rossi, P., Sciacca, B., Voevodina, C., Azzi, E., Bacchetta, P., Bisello, N., Boletti, D., Bragagnolo, A., Carlin, A., Checchia, R., Manzano, P., De Castro, P., Dorigo, T., Dosselli, U., Gasparini, F., Gasparini, U., Gozzelino, A., Hoh, S. Y., Margoni, M., Meneguzzo, A. T., Pazzini, J., Presilla, M., Ronchese, P., Rossin, R., Simonetto, F., Tiko, A., Tosi, M., Zanetti, M., Zotto, P., Zucchetta, A., Zumerle, G., Braghieri, A., Fiorina, D., Montagna, P., Ratti, S. P., Re, V, Ressegotti, M., Riccardi, C., Salvini, P., Vai, I, Vitulo, P., Biasini, M., Bilei, G. M., Ciangottini, D., Fano, L., Lariccia, P., Leonardi, R., Manoni, E., Mantovani, G., Mariani, V, Menichelli, M., Rossi, A., Santocchia, A., Spiga, D., Rosov, K., Azzurri, P., Bagliesi, G., Bertacchi, V, Bianchini, L., Boccali, T., Castaldi, R., Ciocci, M. A., Dell'Orso, R., Donato, S., Giannini, L., Giassi, A., Grippo, M. T., Ligabue, F., Manca, E., Orli, M, Messineo, G., Palla, A., Rizzi, F., Rol, A., I, G., Chowdhury, Roy, S., Scribano, A., Spagnolo, P., Tenchini, R., Tonelli, G., Turini, N., Venturi, A., Verdini, P. G., Cavallari, F., Cipriani, M., Del, Re, Marco, Di, Diemoz, E., Longo, M., Meridiani, E., Organtini, P., G. P., Olfi, F., Paramatti, R., Quaranta, C., Rahatlou, S., Rovelli, C., Santanastasio, F., Soffi, L., Tramontano, R., Amapane, N., Arcidiacono, R., Argiro, S., Arneodo, M., Bartosik, N., Bellan, R., Bellora, A., Biino, C., Cappati, A., Cartiglia, N., Cometti, S., Costa, M., Covarelli, R., Demaria, N., Fern, Ez, Gonzalez, J. R., Kiani, B., Legger, F., Mariotti, C., Maselli, S., Migliore, E., Monaco, V, Monteil, E., Monteno, M., Obertino, M. M., Ortona, G., Pacher, L., Pastrone, N., Pelliccioni, M., Angioni, Pinna, G. L., Romero, A., Ruspa, M., Salvatico, R., Sola, V, Solano, A., Soldi, D., Staiano, A., Trocino, D., Belforte, S., Elise, C, Casarsa, V, Cossutti, M., Rold, Da, Della, Ricca, Vazzoler, G., Zanetti, F., Kim, A., Kim, B., Kim, D. H., Lee, G. N., Lee, J., Moon, S. W., C. S., Oh, Pak, Y. D., I, S., Sekmen, S., Son, D. C., Yang, Y. C., Kim, H., Moon, D. H., Francois, B., Kim, T. J., Park, J., Cho, S., Choi, S., Go, Y., Ha, S., Hong, B., Lee, K., Lee, K. S., Lim, J., Park, S. K., Roh, Y., Yoo, J., Goh, J., Kim, H. S., Almond, J., Bhyun, J. H., Choi, J., Jeon, S., Kim, J., Kim, J. S., Lee, H., Lee, S., Nam, K., Oh, M., S. B., Oh, Radburn-Smith, B. C., Yang, U. K., Yoo, H. D., Yoon, I, Jeon, D., Kim, J. H., Lee, J. S. H., Park, I. C., Watson, I. J., Choi, Y., Hwang, C., Jeong, Y., Lee, Y., Yu, I, Veckalns, V., Dudenas, V, Juodagalvis, A., Rinkevicius, A., Tamulaitis, G., Vaitkus, J., Idris, Mohamad, F., Abdullah, Wan, W. A. T., Yusli, M. N., Zolkapli, Z., Benitez, J. F., Hern, Ez, Castaneda, A., Quijada, Murillo, J. A., Palomo, Valencia, L., Castilla-Valdez, H., De La Cruz-Burelo, Heredia-De La Cruz, Lopez-Fern, I, Ez, R., Sanchez-Hern, Ez, Moreno, A., Carrillo, S., Oropeza, Barrera, Ramirez-Garcia, C., Vazquez, Valencia, Eysermans, F., Pedraza, J., I, Salazar, Ibarguen, H. A., Uribe, Estrada, Pineda, C., Morelos, A., Mijuskovic, J., Raicevic, N., Krofcheck, D., Bheesette, S., Butler, P. H., Lujan, P., Ahmad, A., Ahmad, M., Awan, M. I. M., Hassan, Q., Hoorani, H. R., Khan, W. A., Shah, M. A., Shoaib, M., Waqas, M., Avati, V, Grzanka, L., Malawski, M., Bialkowska, H., Bluj, M., Boimska, B., Gorski, M., Kazana, M., Szleper, M., Zalewski, P., Bunkowski, K., Byszuk, A., Doroba, K., Kalinowski, A., Konecki, M., Krolikowski, J., Olszewski, M., Walczak, M., Araujo, M., Bargassa, P., Bastos, D., Francesco, Di, Faccioli, A., Galinhas, P., Gallinaro, B., Hollar, M., Leonardo, J., Niknejad, N., Seixas, T., Shchelina, J., Strong, K., Toldaiev, G., Varela, O., Afanasiev, J., Bunin, S., Ershov, P., Golutvin, Y., Gorbunov, I, Kamenev, I, Karjavine, A., Korenkov, V, Lanev, V, Malakhov, A., Matveev, A., Mitsyn, V, Moisenz, V. V., Palichik, P., Perelygin, V, Shmatov, V, Skatchkov, S., Yuldashev, N., Zarubin, B. S., Zhiltsov, A., Chtchipounov, V, Golovtcov, L., Ivanov, V, Kim, Y., Kuznetsova, V, Levchenko, E., Murzin, P., Oreshkin, V, Smirnov, V, Sosnov, I, Sulimov, D., Uvarov, V, Vorobyev, L., Reev, A., Dermenev, Yu, Gninenko, A., Golubev, S., Karneyeu, N., Kirsanov, A., Krasnikov, M., Pashenkov, N., Tlisov, A., Toropin, D., Epshteyn, A., Gavrilov, V, Lychkovskaya, V, Nikitenko, N., Popov, A., Pozdnyakov, V, Safronov, I, Spiridonov, G., Stepennov, A., Toms, A., Vlasov, M., Zhokin, E., Aushev, A., Bychkova, T., Chistov, O., Danilov, R., Polikarpov, M., Tarkovskii, S., Reev, E., Azarkin, V, Dremin, M., Kirakosyan, I, Terkulov, M., Belyaev, A., Boos, A., Demiyanov, E., Ershov, A., Gribushin, A., Kodolova, A., Korotkikh, O., Lokhtin, V, Obraztsov, I, Petrushanko, S., Savrin, S., Snigirev, V, Vardanyan, A., Barnyakov, I, Blinov, A., Dimova, V, Kardapoltsev, T., Skovpen, L., Azhgirey, Y., Bayshev, I, Bitioukov, I, Kachanov, S., Konstantinov, V, D. M., Rik, P., Petrov, V, Ryutin, R., Slabospitskii, S., Sobol, A., Troshin, S., Tyurin, N., Uzunian, A., Volkov, A., Babaev, A., Iuzhakov, A., Okhotnikov, V, Borchsh, V, Ivanchenko, V, Tcherniaev, E., Adzic, P., Cirkovic, P., Dordevic, M., Milenovic, P., Milosevic, J., Stojanovic, M., Aguilar-Benitez, M., Alcaraz, Maestre, Alvarez, Fern, Ez, A., Bachiller, I, Barrio, Luna, Bedoya, M., Cristina, F., Brochero, Cifuentes, J. A., Carrillo, Montoya, Cepeda, C. A., Cerrada, M., Colino, M., De la Cruz, Delgado, Peris, Fern, A., Ramos, Ez, Flix, J. P., Fouz, J., M. C., Gonzalez, Lopez, Goy, Lopez, Hern, S., J. M., Ez, Josa, I, Moran, M., Navarro, Tobar, Perez-Calero, Yzquierdo, Puerta, Pelayo, Redondo, J., Romero, I, Sanchez, Navas, Soares, S., Triossi, M. S., Willmott, A., Albajar, C., Troconiz, De, Reyes-Almanza, J. F., Alvarez, Gonzalez, Cuevas, B., Erice, J., Fern, C., Menendez, Ez, Folgueras, J., Gonzalez, Caballero, Palencia, Cortezon, Ramon, Alvarez, Rodriguez, Bouza, V, Sanchez, Cruz, Cabrillo, S., Calderon, I. J., Chazin, Quero, Duarte, Campderros, Fern, J., Ez, M., Manteca, Ez, P. J., Garcia, Alonso, Gomez, A., Martinez, Rivero, Martinez Ruiz del Arbol, Matorras, P., Piedra, Gomez, Prieels, J., Ricci-Tam, C., Rodrigo, F., Ruiz-Jimeno, T., Russo, A., Scodellaro, L., Vila, L., Vizan, Garcia, Sonnadara, J. M., Dharmaratna, D. U. J., Wickramage, W. G. D., Aarrestad, N., Abbaneo, T. K., Akgun, D., Auffray, B., Auzinger, E., Baechler, G., Baillon, J., Ball, P., Barney, A. H., Bendavid, D., Bianco, J., Bocci, M., Bortignon, A., Bossini, P., Brondolin, E., Camporesi, E., Caratelli, T., Cerminara, A., Chapon, G., Cucciati, E., D'Enterria, G., Dabrowski, D., Daci, A., Daponte, N., David, V, Davignon, A., Roeck, De, Deile, A., Maria, Di, Dobson, R., Dunser, M., Dupont, M., Elliott-Peisert, N., Emriskova, A., Fallavollita, N., Fasanella, F., Fiorendi, D., Franzoni, S., Fulcher, G., Funk, J., Giani, W., Gigi, S., Gill, D., Glege, K., Gouskos, F., Gruchala, L., Guilbaud, M., Gulhan, M., Hegeman, D., Heidegger, J., Iiyama, C., Innocente, Y., James, V, Janot, T., Karacheban, P., Kaspar, O., Kieseler, J., Krammer, J., Kratochwil, M., Lange, N., Lecoq, C., Long, P., Lourenco, K., Malgeri, C., Mannelli, L., Massironi, M., Meijers, A., Mersi, F., Meschi, S., Moortgat, E., Mulders, F., Ngadiuba, M., Niedziela, J., Nourbakhsh, J., Orfanelli, S., Orsini, S., Pantaleo, L., Pape, F., Perez, L., Peruzzi, E., Petrilli, M., Petrucciani, A., Pfeiffer, G., Pierini, A., Pitters, M., Rabady, F. M., Racz, D., Rovere, M., Sakulin, M., Salfeld-Nebgen, H., Scarfi, J., Schafer, S., Schwick, C., Selvaggi, C., Sharma, M., Silva, A., Snoeys, P., Sphicas, W., Steggemann, P., Summers, J., Tavolaro, S., Treille, V. R., Tsirou, D., Van, Onsem, Vartak, G. P., Verzetti, A., Wozniak, M., Zeuner, K. A., Caminada, W. D., Deiters, L., Erdmann, K., Horisberger, W., Ingram, R., Kaestli, Q., Kotlinski, H. C., Langenegger, D., Rohe, U., Backhaus, T., Berger, M., Cal, P., Ri, A., Chernyavskaya, N., Dissertori, G., Dittmar, M., Donega, M., Dorfer, C., Espinosa, Gomez, T. A., Grab, C., Hits, D., Lustermann, W., Manzoni, R. A., Meinhard, M. T., Micheli, F., Musella, P., Nessi-Tedaldi, F., Pauss, F., Perovic, V, Perrin, G., Perrozzi, L., Pigazzini, S., Ratti, M. G., Reichmann, M., Reissel, C., Reitenspiess, T., Ristic, B., Ruini, D., Becerra, Sanz, D. A., Schonenberger, M., Shchutska, L., Olsson, Vesterbacka, M. L., Wallny, R., Zhu, D. H., Amsler, C., Botta, C., Brzhechko, D., Canelli, M. F., Cosa, De, Del, Burgo, Kilminster, R., Leontsinis, B., Mikuni, S., Neutelings, V. M., Rauco, I, Robmann, G., Schweiger, P., Takahashi, K., Wertz, Y., Kuo, S., Lin, C. M., Roy, W., Sarkar, A., Yu, T., Chang, S. S., Chao, P., Chen, K. F., Hou, P. H., W-S, Li, Y. Y., Lu, R-S, Paganis, Psallidas, E., Steen, A., Asavapibhop, A., Asawatangtrakuldee, B., Srimanobhas, C., Suwonj, N., Ee, N., Bat, A., Boran, F., Celik, A., Damarseckin, S., Demiroglu, Z. S., Dolek, F., Dozen, C., Dumanoglu, I, Gokbulut, G., Guler, Emine, Gurpinar, Guler, Y., Hos, I, Isik, C., Kangal, E. E., Kara, O., Topaksu, Kayis, A., Kiminsu, U., Onengut, G., Ozdemir, K., Simsek, A. E., Tok, U. G., Turkcapar, S., Zorbakir, I. S., Zorbilmez, C., Isildak, B., Karapinar, G., Yalvac, M., Atakisi, I. O., Gulmez, E., Kaya, M., Kaya, O., Tekten, S., Yetkin, E. A., Cakir, A., Cankocak, K., Komurcu, Y., Sen, S., Cerci, S., Kaynak, B., Ozkorucuklu, S., Cerci, Sunar, D., Grynyov, B., Levchuk, L., Bhal, E., Bologna, S., Brooke, J. J., Burns, D., Clement, E., Cussans, D., Flacher, H., Goldstein, J., Heath, G. P., Heath, H. F., Kreczko, L., Krikler, B., Paramesvaran, S., Sakuma, T., Nasr-Storey, El, Seif, S., Smith, V. J., Taylor, J., Titterton, A., Bell, K. W., Brew, C., Brown, R. M., Cockerill, D. J. A., Coughlan, J. A., Harder, K., Harper, S., Linacre, J., Manolopoulos, K., Newbold, D. M., Olaiya, E., Petyt, D., Reis, T., Schuh, T., Shepherd-Themistocleous, C. H., Thea, A., Tomalin, I. R., Williams, T., Bainbridge, R., Bloch, P., Bonomally, S., Borg, J., Breeze, S., Buchmuller, O., Bundock, A., Chahal, Gurpreet, Singh, Colling, D., Dauncey, P., Davies, G., Della, Negra, Everaerts, M., Hall, P., Iles, G., Komm, G., Langford, M., Lyons, J., Magnan, L., A-M, Malik, Martelli, S., Milosevic, A., Morton, V, Nash, A., Palladino, J., Pesaresi, V, Raymond, M., Richards, D. M., Rose, A., Scott, A., Seez, E., Shtipliyski, C., Stoye, A., Strebler, M., Tapper, T., Uchida, A., Virdee, K., Wardle, T., Webb, N., Winterbottom, S. N., Zecchinelli, D., Zenz, A. G., Cole, S. C., Hobson, J. E., Khan, P. R., Kyberd, A., Mackay, P., Reid, C. K., Teodorescu, I. D., Zahid, L., Brinkerhoff, S., Call, A., Caraway, K., Dittmann, B., Hatakeyama, J., Madrid, K., Mcmaster, C., Pastika, B., Smith, N., Bartek, C., Dominguez, R., Uniyal, A., Hern, R., Vargas, A. M., Buccilli, A., Cooper, I, Gleyzer, S., V, S., Henderson, C., Rumerio, P., West, C., Albert, A., Arcaro, D., Demiragli, Z., Gastler, D., Richardson, C., Rohlf, J., Sperka, D., Spitzbart, D., Suarez, I, Sulak, L., Zou, D., Benelli, G., Burkle, B., Coubez, X., Cutts, D., Duh, Y. T., Hadley, M., Heintz, U., Hogan, J. M., Kwok, K. H. M., Laird, E., Sberg, L, Lau, G., Lee, K. T., Narain, J., Sagir, M., Syarif, S., Usai, R., Wong, E., W. Y., Yu, Zhang, D., W. B., Brainerd, R., Breedon, C., Sanchez, R., Calderon De La Barca, M., Chertok, M., Conway, J., Conway, R., Cox, P. T., Erbacher, R., Flores, C., Funk, G., Jensen, F., Ko, W., Kukral, O., L, Er, Mulhearn, R., Pellett, M., Pilot, D., Shi, J., Taylor, M., Tos, D., Tripathi, K., Wang, M., Zhang, Z., Bachtis, F., Bravo, M., Cousins, C., Dasgupta, R., Florent, A., Hauser, A., Ignatenko, J., Mccoll, M., Nash, N., Regnard, W. A., Saltzberg, S., Schnaible, D., Stone, C., Valuev, B., Burt, V., Chen, K., Clare, Y., Gary, R., Shirazi, J. W., Ghiasi, S. M. A., Hanson, G., Karapostoli, G., Long, O. R., Manganelli, N., Negrete, Olmedo, M., Paneva, I, Si, M., Wimpenny, W., Yates, S., Zhang, B. R., Branson, Y., Chang, J. G., Cittolin, P., Cooperstein, S., Deelen, S., Derdzinski, N., Duarte, M., Gerosa, J., Gilbert, R., Hashemi, D., Klein, B., Krutelyov, D., Letts, V, Masciovecchio, J., May, M., Padhi, S., Pieri, S., Tadel, V, Wurthwein, M., Yagil, F., Della, Porta, Zevi, G., Amin, N., Ari, Bh, Campagnari, R., Citron, C., Dutta, M., Inc, V, Ela, J., Marsh, B., Mei, H., Ovcharova, A., Qu, H., Richman, J., Sarica, U., Stuart, D., Wang, S., Erson, D., Bornheim, A., Cerri, O., Dutta, I, Lawhorn, J. M., Lu, N., Mao, J., Newman, H. B., Nguyen, T. Q., Pata, J., Spiropulu, M., Vlimant, J. R., Xie, S., Zhu, R. Y., Alison, J., Rews, M. B., Ferguson, T., Mudholkar, T., Paulini, M., Sun, M., Vorobiev, I, Weinberg, M., Cumalat, J. P., Ford, W. T., Macdonald, E., Mulholl, T., Patel, R., Perloff, A., Stenson, K., Ulmer, K. A., Wagner, S. R., Alex, Er, Cheng, J., Chu, Y., Datta, J., Frankenthal, A., Mcdermott, A., Patterson, K., Quach, J. R., Ryd, D., Tan, A., Tao, S. M., Thom, Z., Wittich, J., Zientek, P., Abdullin, M., Albrow, S., Alyari, M., Apollinari, M., Apresyan, G., Apyan, A., Banerjee, A., Bauerdick, S., Beretvas, L. A. T., Berry, A., Berryhill, D., Bhat, J., Burkett, P. C., Butler, K., Canepa, J. N., Cerati, A., Cheung, G. B., Chlebana, H. W. K., Cremonesi, F., Elvira, M., Freeman, V. D., Gecse, J., Gottschalk, Z., Gray, E., Green, L., Grunendahl, D., Gutsche, S., Hanlon, O., Harris, J., Hasegawa, R. M., Heller, S., Hirschauer, R., Jayatilaka, J., Jindariani, B., Johnson, S., Joshi, M., Klijnsma, U., Klima, T., Kortelainen, B., Kreis, M. J., Lammel, B., Lewis, S., Lincoln, J., Lipton, D., Liu, R., Liu, M., Lykken, T., Maeshima, J., Marraffino, K., Mason, J. M., Mcbride, D., Merkel, P., Mrenna, P., Nahn, S., O'Dell, S., Papadimitriou, V, Pedro, V, Pena, K., Ravera, C., Hall, F., Reinsvold, A., Ristori, L., Schneider, B., Sexton-Kennedy, E., Soha, A., Spalding, W. J., Spiegel, L., Stoynev, S., Strait, J., Taylor, L., Tkaczyk, S., Tran, V, Uplegger, N., Va, L., Ering, E. W., Vidal, R., Weber, H. A., Woodard, A., Acosta, D., Avery, P., Bourilkov, D., Cadamuro, L., Cherepanov, V, Errico, F., Field, R. D., Guerrero, D., Joshi, B. M., Kim, M., Konigsberg, J., Korytov, A., K. H., Lo, Matchev, K., Menendez, N., Mitselmakher, G., Rosenzweig, D., Shi, K., Wang, J., Zuo, X., Joshi, Y. R., Adams, T., Askew, A., Hagopian, S., Hagopian, V, Johnson, K. F., Khurana, R., Kolberg, T., Martinez, G., Perry, T., Prosper, H., Schiber, C., Yohay, R., Zhang, J., Baarm, M. M., Hohlmann, M., Noonan, D., Rahmani, M., Saunders, M., Yumiceva, F., Adams, M. R., Apanasevich, L., Betts, R. R., Cavanaugh, R., Chen, X., Dittmer, S., Evdokimov, O., Gerber, C. E., Hangal, D. A., Hofman, D. J., Kumar, V, Mills, C., Oh, G., Roy, T., Tonjes, M. B., Varelas, N., Viinikainen, J., Wang, H., Wang, X., Wu, Z., Alhusseini, M., Bilki, B., Dilsiz, K., Durgut, S., Rajula, G, Haytmyradov, R. P., Khristenko, M., Koseyan, V, Merlo, O. K., J-P, Mestvirishvili, Moeller, A., Nachtman, A., Ogul, J., Onel, H., Ozok, Y., Penzo, F., Snyder, A., Tiras, C., Wetzel, E., Yi, J., Blumenfeld, K., Cocoros, B., Eminizer, A., Gritsan, N., V, A., Hung, W. T., Kyriacou, S., Maksimovic, P., Mantilla, C., Roskes, J., Swartz, M., Vami, T. A., Barrera, Baldenegro, C., Baringer, P., Bean, A., Boren, S., Bylinkin, A., Isidori, T., Khalil, S., King, J., Krintiras, G., Kropivnitskaya, A., Lindsey, C., Majumder, D., Mcbrayer, W., Minafra, N., Murray, M., Rogan, C., Royon, C., Ers, S, Schmitz, S., Takaki, E., Tapia, J. D., Wang, Q., Williams, J., Wilson, G., Duric, S., Kaadze, K., Kim, D., Maravin, Y., Mendis, D. R., Mitchell, T., Modak, A., Mohammadi, A., Rebassoo, F., Wright, D., Baden, A., Baron, O., Belloni, A., Eno, S. C., Feng, Y., Hadley, N. J., Jabeen, S., Jeng, G. Y., Kellogg, R. G., Mignerey, A. C., Nabili, S., Seidel, M., Skuja, A., Tonwar, S. C., Wang, L., Wong, K., Abercrombie, D., Allen, B., Bi, R., Br, T, Busza, S., Cali, W., D'Alfonso, I. A., Ceballos, M., Gomez, G., Goncharov, M., Harris, P., Hsu, D., Klute, M., Kovalskyi, D., Lee, Y-J, Luckey, P. D., Maier, B., Marini, A. C., Mcginn, C., Mironov, C., Narayanan, S., Niu, X., Paus, C., Rankin, D., Rol, Rol, C., Shi, G., Stephans, Z., Sumorok, G. S. F., Tatar, K., Velicanu, K., Wyslouch, T. W., Chatterjee, B., Evans, R. M., Guts, A., Hansen, S., Hiltbr, P., Jain, J., Kubota, Sh, Lesko, Y., Mans, Z., Revering, J., Rusack, M., Saradhy, R., Schroeder, R., Strobbe, N., Wadud, N., Acosta, M. A., Oliveros, J. G., Bloom, S., Chauhan, K., Claes, S., Fangmeier, D. R., Finco, C., Golf, L., Kamalieddin, F., Kravchenko, R., Siado, I, Snow, J. E., Stieger, G. R., Tabb, B., Agarwal, W., Harrington, G., Iashvili, C., Kharchilava, I., Mclean, A., Nguyen, C., Parker, D., Pekkanen, A., Rappoccio, J., Roozbahani, S., Alverson, B., Barberis, G., Freer, E., Haddad, C., Hortiangtham, Y., Madigan, A., Marzocchi, G., Morse, B., Nguyen, D. M., Orimoto, V, Skinnari, T., Tishelman-Charny, L., Wamorkar, A., Wang, T., Wisecarver, B., Wood, A., Bhattacharya, D., Bueghly, S., Fedi, J., Gilbert, G., Gunter, A., Hahn, T., Odell, K. A., Schmitt, N., Sung, M. H., Velasco, K., Bucci, M., Dev, R., Goldouzian, N., Hildreth, R., Anampa, M., Hurtado, K., Jessop, C., Karmgard, D. J., Lannon, K., Li, W., Loukas, N., Marinelli, N., Mcalister, I, Meng, F., Musienko, Y., Ruchti, R., Siddireddy, P., Smith, G., Taroni, S., Wayne, M., Wightman, A., Wolf, M., Alimena, J., Bylsma, B., Cardwell, B., Durkin, L. S., Francis, B., Hill, C., Ji, W., Lefeld, A., Ling, T. Y., Winer, B. L., Dezoort, G., Elmer, P., Hardenbrook, J., Haubrich, N., Higginbotham, S., Kalogeropoulos, A., Kwan, S., Lange, D., Lucchini, M. T., Luo, J., Marlow, D., Mei, K., Ojalvo, I, Olsen, J., Palmer, C., Piroue, P., Stickl, D., Tully, C., Malik, S., Norberg, S., Barker, A., Barnes, V. E., Chawla, R., Das, S., Gutay, L., Jones, M., Jung, A. W., Mahakud, B., Miller, D. H., Negro, G., Neumeister, N., Peng, C. C., Piperov, S., Qiu, H., Schulte, J. F., Trevisani, N., Wang, F., Xiao, R., Xie, W., Cheng, T., Dolen, J., Parashar, N., Baty, A., Behrens, U., Dildick, S., Ecklund, K. M., Freed, S., Geurts, F. J. M., Kilpatrick, M., Kumar, Arun, Padley, B. P., Redjimi, R., Roberts, J., Rorie, J., Shi, W., Leiton, Stahl, A. G., Tu, Z., Zhang, A., Bodek, A., Barbaro, De, Demina, P., Dulemba, R., Fallon, J. L., Ferbel, C., Galanti, T., Garcia-Bellido, M., Hindrichs, A., Khukhunaishvili, O., Ranken, A., Taus, E., Chiarito, R., Chou, B., J. P. G., Rakota, A., Gershtein, Y., Halkiadakis, E., Hart, A., Heindl, M., Hughes, E., Kaplan, S., Laflotte, I, Lath, A., Montalvo, R., Nash, K., Osherson, M., Salur, S., Schnetzer, S., Somalwar, S., Stone, R., Thomas, S., Acharya, H., Delannoy, A. G., Spanier, S., Bouhali, O., Dalchenko, M., Mattia, De, Delgado, M., Eusebi, A., Gilmore, R., Huang, J., Kamon, T., Kim, T., Luo, H., Malhotra, S., Marley, S., Mueller, D., Overton, R., Pernie, D., Rathjens, L., Safonov, D., Akchurin, A., Damgov, N., Guio, De, Hegde, F., Kunori, V, Lamichhane, S., Mengke, S. W., Muthumuni, T., Peltola, S., Undleeb, T., Volobouev, S., Wang, I, Whitbeck, Z., Greene, A., Gurrola, S., Janjam, A., Johns, R., Maguire, W., Melo, C., Ni, A., Padeken, H., Romeo, K., Sheldon, F., Tuo, P., Velkovska, S., Verweij, J., Arenton, M., Barria, M. W., Cox, P., Cummings, B., Hakala, G., Hirosky, J., Joyce, R., Ledovskoy, M., Neu, A., Tannenwald, C., Wang, B., Wolfe, Y., Xia, E., Harr, F., Karchin, R., Poudyal, P. E., Sturdy, N., Thapa, J., Black, P., Bose, K., Buchanan, T., Caillol, J., Carlsmith, C., Dasu, D., Bruyn, De, Dodd, I, Galloni, L., He, C., Herndon, H., Herve, M., Hussain, A., Lanaro, U., Loeliger, A., Loveless, A., Sreekala, R., Madhusudanan, J., Mallampalli, A., Pinna, D., Ruggles, T., Savin, A., Sharma, V, Smith, W. H., Teague, D., Trembath-reichert, S., and Cms, Collaboration
- Subjects
MODEL ,Physics and Astronomy ,High Energy Physics::Experiment ,QUARK-GLUON PLASMA ,Nuclear Experiment - Abstract
The first evidence for X(3872) production in relativistic heavy ion collisions is reported. The X(3872) production is studied in lead-lead (Pb-Pb) collisions at a center-of-mass energy of root s(NN) = 5.02 TeV per nucleon pair, using the decay chain X(3872) -> J/psi pi(+)pi(-) -> mu(+) mu(-) pi(+)pi(-). The data were recorded with the CMS detector in 2018 and correspond to an integrated luminosity of 1.7 nb(-1). The measurement is performed in the rapidity and transverse momentum ranges vertical bar y vertical bar < 1.6 and 15 < p(T) < 50 GeV/c. The significance of the inclusive X(3872) signal is 4.2 standard deviations. The prompt X(3872) to psi 2S yield ratio is found to be rho(Pb-Pb) = 1.08 +/- 0.49(stat) +/- 0.52(syst), to be compared with typical values of 0.1 for pp collisions. This result provides a unique experimental input to theoretical models of the X(3872) production mechanism, and of the nature of this exotic state.
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- 2022
24. Estimating the release of chemical substances from consumer products, textiles and pharmaceuticals to wastewater
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Gustavsson, M., primary, Molander, S., additional, Backhaus, T., additional, and Kristiansson, E., additional
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- 2022
- Full Text
- View/download PDF
25. We need a global science-policy body on chemicals and waste: Major gaps in current efforts limit policy responses
- Author
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Wang, Z., Altenburger, Rolf, Backhaus, T., Covaci, A., Diamond, M.L., Grimalt, J.O., Lohmann, R., Schäffer, A., Scheringer, M., Selin, H., Soehl, A., Suzuki, N., Wang, Z., Altenburger, Rolf, Backhaus, T., Covaci, A., Diamond, M.L., Grimalt, J.O., Lohmann, R., Schäffer, A., Scheringer, M., Selin, H., Soehl, A., and Suzuki, N.
- Abstract
Many countries and regional political unions have regulatory and policy frameworks for managing chemicals and waste associated with human activities to minimize harms to human health and the environment. These frameworks are complemented and expanded by joint international action, particularly related to pollutants that undergo long-range transport via air, water, and biota; move across national borders through international trade of resources, products, and waste; or are present in many countries (1). Some progress has been made, but the Global Chemicals Outlook (GCO-II) from the United Nations Environment Programme (UNEP) (1) has called for “strengthen[ing] the science-policy interface and the use of science in monitoring progress, priority-setting, and policy-making throughout the life cycle of chemicals and waste.” With the UN Environment Assembly (UNEA) soon meeting to discuss how to strengthen the science-policy interface on chemicals and waste (2), we analyze the landscape and outline recommendations for establishing an overarching body on chemicals and waste.
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- 2021
26. Demonstration of an aggregated biomarker response approach to assess the impact of point and diffuse contaminant sources in feral fish in a small river case study
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Schmitz, M., Deutschmann, B., Markert, N., Backhaus, T., Brack, Werner, Brauns, Mario, Brinkmann, M., Seiler, T.-B., Fink, Patrick, Tang, S., Beitel, S., Doering, J.A., Hecker, M., Shao, Y., Schulze, Tobias, Weitere, Markus, Wild, Romy, Velki, M., Hollert, H., Schmitz, M., Deutschmann, B., Markert, N., Backhaus, T., Brack, Werner, Brauns, Mario, Brinkmann, M., Seiler, T.-B., Fink, Patrick, Tang, S., Beitel, S., Doering, J.A., Hecker, M., Shao, Y., Schulze, Tobias, Weitere, Markus, Wild, Romy, Velki, M., and Hollert, H.
- Abstract
The assessment of the exposure of aquatic wildlife to complex environmental mixtures of chemicals originating from both point and diffuse sources and evaluating the potential impact thereof constitutes a significant step towards mitigating toxic pressure and the improvement of ecological status. In the current proof-of-concept study, we demonstrate the potential of a novel Aggregated Biomarker Response approach involving a comprehensive set of biomarkers to identify complex exposure and impacts on wild brown trout (Salmo trutta fario). Our scenario used a small lowland river in Germany (Holtemme river in the Elbe river catchment) impacted by two wastewater treatment plants (WWTP) and diffuse agricultural runoff as a case study. The trout were collected along a pollution gradient (characterised in a parallel study) in the river. Compared to fish from the reference site upstream of the first WWTP, the trout collected downstream of the WWTPs showed a significant increase in micronucleus formation, phase I and II enzyme activities, and oxidative stress parameters in agreement with increasing exposure to various chemicals. By integrating single biomarker responses into an Aggregated Biomarker Response (ABR) approach, the two WWTPs' contribution to the observed toxicity could be clearly differentiated. The ABR results were supported by chemical analyses and whole transcriptome data, which revealed alterations of steroid biosynthesis and associated pathways, including an anti-androgenic effect, as some of the key drivers of the observed toxicity. Overall, this combined approach of in situ biomarker responses complemented with molecular pathway analysis allowed for a comprehensive ecotoxicological assessment of fish along the river. This study provides evidence for specific hazard potentials caused by mixtures of agricultural and WWTP derived chemicals at sublethal concentrations. Using aggregated biomarker responses combined with chemical analyses enabled an evidence-based
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- 2021
27. Assessing the ecological impact of chemical pollution on aquatic ecosystems requires the systematic exploration and evaluation of four lines of evidence
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Backhaus, T, Brack, W, van den Brink, PJ, Deutschmann, B, Hollert, H, and Posthuma, L
- Published
- 2020
28. Risks of floating microplastic in the global ocean
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Everaert, G., De Rijcke, M., Lonneville, B., Janssen, C. R., Backhaus, T., Mees, J., van Sebille, E., Koelmans, A. A., Catarino, A. I., Vandegehuchte, M. B., Sub Palaeoecology begr. 01-01-12, Sub Physical Oceanography, Marine and Atmospheric Research, Sub Palaeoecology begr. 01-01-12, Sub Physical Oceanography, and Marine and Atmospheric Research
- Subjects
Pollution ,Aquatic Ecology and Water Quality Management ,010504 meteorology & atmospheric sciences ,media_common.quotation_subject ,Health, Toxicology and Mutagenesis ,Microplastics ,010501 environmental sciences ,Spatial distribution ,Toxicology ,01 natural sciences ,Sensitivity distribution ,Mediterranean sea ,Mediterranean Sea ,Marine ecosystem ,Toxicology and Mutagenesis ,14. Life underwater ,Ecosystem ,0105 earth and related environmental sciences ,media_common ,Environmental risk assessment ,WIMEK ,Microplastic ,Multidecadal ,General Medicine ,Aquatische Ecologie en Waterkwaliteitsbeheer ,Oceanography ,13. Climate action ,Health ,Earth and Environmental Sciences ,Environmental science ,Plastics ,Water Pollutants, Chemical ,Marine ecosystems ,Environmental Monitoring - Abstract
Despite the ubiquitous and persistent presence of microplastic (MP) in marine ecosystems, knowledge of its potential harmful ecological effects is low. In this work, we assessed the risk of floating MP (1 μm–5 mm) to marine ecosystems by comparing ambient concentrations in the global ocean with available ecotoxicity data. The integration of twenty-three species-specific effect threshold concentration data in a species sensitivity distribution yielded a median unacceptable level of 1.21 ∗ 105 MP m−³ (95% CI: 7.99 ∗ 103–1.49 ∗ 106 MP m−³). We found that in 2010 for 0.17% of the surface layer (0–5 m) of the global ocean a threatening risk would occur. By 2050 and 2100, this fraction increases to 0.52% and 1.62%, respectively, according to the worst-case predicted future plastic discharge into the ocean. Our results reveal a spatial and multidecadal variability of MP-related risk at the global ocean surface. For example, we have identified the Mediterranean Sea and the Yellow Sea as hotspots of marine microplastic risks already now and even more pronounced in future decades.
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- 2020
29. Risks of floating microplastic in the global ocean
- Author
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Sub Palaeoecology begr. 01-01-12, Sub Physical Oceanography, Marine and Atmospheric Research, Everaert, G., De Rijcke, M., Lonneville, B., Janssen, C. R., Backhaus, T., Mees, J., van Sebille, E., Koelmans, A. A., Catarino, A. I., Vandegehuchte, M. B., Sub Palaeoecology begr. 01-01-12, Sub Physical Oceanography, Marine and Atmospheric Research, Everaert, G., De Rijcke, M., Lonneville, B., Janssen, C. R., Backhaus, T., Mees, J., van Sebille, E., Koelmans, A. A., Catarino, A. I., and Vandegehuchte, M. B.
- Published
- 2020
30. Toxicity of Sulfonylurea Herbicides to the Green Alga Scenedesmus vacuolatus: Predictability of Combination Effects
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Junghans, M., Backhaus, T., Faust, M., Scholze, M., and Grimme, L. H.
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- 2003
- Full Text
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31. Evaluation of a Novel 7-Joint Ultrasound Score in Daily Rheumatologic Practice: A Pilot Project
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BACKHAUS, M., OHRNDORF, S., KELLNER, H., STRUNK, J., BACKHAUS, T. M., HARTUNG, W., SATTLER, H., ALBRECHT, K., KAUFMANN, J., BECKER, K., SÖRENSEN, H., MEIER, L., BURMESTER, G. R., and SCHMIDT, W. A.
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- 2009
- Full Text
- View/download PDF
32. Prioritisation of water pollutants: the EU Project SOLUTIONS proposes a methodological framework for the integration of mixture risk assessments into prioritisation procedures under the European Water Framework Directive
- Author
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Faust, M, Backhaus, T, Altenburger, R, Dulio, V, van Gils, J, Ginebreda, A, Kortenkamp, A, Munthe, J, Posthuma, L, and et. al.
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- 2019
33. Effect-based methods are key. The European Collaborative Project SOLUTIONS recommends integrating effect-based methods for diagnosis and monitoring of water quality
- Author
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Brack, W, Aissa, SA, Backhaus, T, Dulio, V, and Posthuma, L
- Published
- 2019
34. SAPEA, Science Advice for Policy by European Academies (2019). A Scientific Perspective on Microplastics in Nature and Society
- Author
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Koelmans, B., Pahl, S., Backhaus, T., Bessa, F., van Calster, G., Contzen, N., Cronin, R., Galloway, T., Hart, A., Henderson, L., Kalčíková, G., Kelly, F., Kolodziejczyk, B., Marku, E., Poortinga, W., Rillig, M., van Sebille, E., Steg, L., Steinhorst, J., Steidl, J., Syberg, K., Thompson, R., Wagner, M., van Wezel, A., Wyles, K., and Wright, S.
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- 2019
35. A Scientific Perspective on Microplastics in Nature and Society
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Koelmans, B., Pahl, S., Backhaus, T., Bessa, F., van Calster, G., Contzen, N., Cronin, R., Galloway, T., Hart, A., Henderson, L., Kalcikova, G., Kelly, F., Kolodziejczyk, B., Marku, E., Poortinga, W., Rillig, M., van Sebille, E., Steg, L., Steinhorst, J., Steidl, J., Syberg, K., Thompson, R., Wagner, M., van Wezel, A., Wyles, K., Wright, S., Koelmans, B., Pahl, S., Backhaus, T., Bessa, F., van Calster, G., Contzen, N., Cronin, R., Galloway, T., Hart, A., Henderson, L., Kalcikova, G., Kelly, F., Kolodziejczyk, B., Marku, E., Poortinga, W., Rillig, M., van Sebille, E., Steg, L., Steinhorst, J., Steidl, J., Syberg, K., Thompson, R., Wagner, M., van Wezel, A., Wyles, K., and Wright, S.
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- 2019
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36. Exploring the ‘solution space’ is key: SOLUTIONS recommends an early‑stage assessment of options to protect and restore water quality against chemical pollution
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Posthuma, L., Backhaus, T., Hollender, J., Bunke, D., Brack, Werner, Müller, Christin, van Gils, J., Hollert, H., Munthe, J., van Wezel, A., Posthuma, L., Backhaus, T., Hollender, J., Bunke, D., Brack, Werner, Müller, Christin, van Gils, J., Hollert, H., Munthe, J., and van Wezel, A.
- Abstract
Present evaluations of chemical pollution in European surface and groundwater bodies focus on problem description and chemical classification of water quality. Surprisingly, relatively low attention has been paid to solutions of chemical pollution problems when those are encountered. Based on evaluations of current practices and available approaches, we suggest that water quality protection, monitoring, assessment and management of chemical pollution can be improved by implementing an early-stage exploration of the ‘solution space’. This follows from the innovative paradigm of solution-focused risk assessment, which was developed to improve the utility of risk assessments. The ‘solution space’ is defined as the set of potential activities that can be considered to protect or restore the water quality against hazards posed by chemical pollution. When using the paradigm, upfront exploration of solution options and selecting options that would be feasible given the local pollution context would result in comparative risk assessment outcomes. The comparative outcomes are useful for selecting optimal measures against chemical pollution for management prioritization and planning. It is recommended to apply the solution-focused risk assessment paradigm to improve the chemical pollution information for river basin management planning. To operationalize this, the present paper describes a still-growing database and strategy to find and select technical abatement and/or non-technical solution options for chemical pollution of surface waters. The solutions database and strategy can be applied to help prevent and reduce water quality problems. Various case studies show that implementing these can be effective, and how solution scenarios can be evaluated for their efficacy by comparative exposure and effect assessment.
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- 2019
37. Statement on advancing the assessment of chemical mixtures and their risks for human health and the environment
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Drakvik, E., Altenburger, Rolf, Aoki, Y., Backhaus, T., Bahadori, T., Barouki, R., Brack, Werner, Cronin, M.T.D., Demeneix, B., Hougaard Bennekou, S., van Klaveren, J., Kneuer, C., Kolossa-Gehring, M., Lebret, E., Posthuma, L., Reiber, L., Rider, C., Rüegg, J., Testa, G., van der Burg, B., van der Voet, H., Warhurst, A.M., van de Water, B., Yamazaki, K., Öberg, M., Bergman, Å., Drakvik, E., Altenburger, Rolf, Aoki, Y., Backhaus, T., Bahadori, T., Barouki, R., Brack, Werner, Cronin, M.T.D., Demeneix, B., Hougaard Bennekou, S., van Klaveren, J., Kneuer, C., Kolossa-Gehring, M., Lebret, E., Posthuma, L., Reiber, L., Rider, C., Rüegg, J., Testa, G., van der Burg, B., van der Voet, H., Warhurst, A.M., van de Water, B., Yamazaki, K., Öberg, M., and Bergman, Å.
- Abstract
The number of anthropogenic chemicals, manufactured, by-products, metabolites and abiotically formed transformation products, counts to hundreds of thousands, at present. Thus, humans and wildlife are exposed to complex mixtures, never one chemical at a time and rarely with only one dominating effect. Hence there is an urgent need to develop strategies on how exposure to multiple hazardous chemicals and the combination of their effects can be assessed. A workshop, “Advancing the Assessment of Chemical Mixtures and their Risks for Human Health and the Environment” was organized in May 2018 together with Joint Research Center in Ispra, EU-funded research projects and Commission Services and relevant EU agencies. This forum for researchers and policy-makers was created to discuss and identify gaps in risk assessment and governance of chemical mixtures as well as to discuss state of the art science and future research needs. Based on the presentations and discussions at this workshop we want to bring forward the following Key Messages:•We are at a turning point: multiple exposures and their combined effects require better management to protect public health and the environment from hazardous chemical mixtures.•Regulatory initiatives should be launched to investigate the opportunities for all relevant regulatory frameworks to include prospective mixture risk assessment and consider combined exposures to (real-life) chemical mixtures to humans and wildlife, across sectors.•Precautionary approaches and intermediate measures (e.g. Mixture Assessment Factor) can already be applied, although, definitive mixture risk assessments cannot be routinely conducted due to significant knowledge and data gaps.•A European strategy needs to be set, through stakeholder engagement, for the governance of combined exposure to multiple chemicals and mixtures. The strategy would include research aimed at scientific advancement in mechanistic understanding and modelling techniques, as well as r
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- 2019
38. Mixture risks threaten water quality: the European Collaborative Project SOLUTIONS recommends changes to the WFD and better coordination across all pieces of European chemicals legislation to improve protection from exposure of the aquatic environment to multiple pollutants
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Kortenkamp, A., Faust, M., Backhaus, T., Altenburger, Rolf, Scholze, M., Müller, Christin, Ermler, S., Posthuma, L., Brack, Werner, Kortenkamp, A., Faust, M., Backhaus, T., Altenburger, Rolf, Scholze, M., Müller, Christin, Ermler, S., Posthuma, L., and Brack, Werner
- Abstract
Evidence is mounting that chemicals can produce joint toxicity even when combined at levels that singly do not pose risks. Environmental Quality Standards (EQS) defined for single pollutants under the Water Framework Directive (WFD) do not protect from mixture risks, nor do they enable prioritization of management options. Despite some provisions for mixtures of specific groups of chemicals, the WFD is not fit for purpose for protecting against or managing the effects of coincidental mixtures of water-borne pollutants. The conceptual tools for conducting mixture risk assessment are available and ready for use in regulatory and risk assessment practice. Extension towards impact assessment using cumulative toxic unit and mixture toxic pressure analysis based on chemical monitoring data or modelling has been suggested by the SOLUTIONS project. Problems exist in the availability of the data necessary for mixture risk assessments. Mixture risk assessments cannot be conducted without essential input data about exposures to chemicals and their toxicity. If data are missing, mixture risk assessments will be biassed towards underestimating risks. The WFD itself is not intended to provide toxicity data. Data gaps can only be closed if proper feedback links between the WFD and other EU regulations for industrial chemicals (REACH), pesticides (PPPR), biocides (BPR) and pharmaceuticals are implemented. Changes of the WFD alone cannot meet these requirements. Effect-based monitoring programmes developed by SOLUTIONS should be implemented as they can capture the toxicity of complex mixtures and provide leads for new candidate chemicals that require attention in mixture risk assessment. Efforts of modelling pollutant levels and their anticipated mixture effects in surface water can also generate such leads. New pollutant prioritization schemes conceived by SOLUTIONS, applied in the context of site prioritization, will help to focus mixture risk assessments on those chemicals and si
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- 2019
39. Strengthen the European collaborative environmental research to meet European policy goals for achieving a sustainable, non‑toxic environment
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Brack, Werner, Ait‑Aissa, S., Backhaus, T., Birk, S., Barceló, D., Burgess, R., Cousins, I., Dulio, V., Escher, Beate, Focks, A., van Gils, J., Ginebreda, A., Hering, D., Hewitt, L.M., Hilscherová, K., Hollender, J., Hollert, H., Köck, M., Kortenkamp, A., López de Alda, M., Müller, Christin, Posthuma, L., Schüürmann, Gerrit, Schymanski, E., Segner, H., Sleeuwaert, F., Slobodnik, J., Teodorovic, I., Umbuzeiro, G., Voulvoulis, N., van Wezel, A., Altenburger, Rolf, Brack, Werner, Ait‑Aissa, S., Backhaus, T., Birk, S., Barceló, D., Burgess, R., Cousins, I., Dulio, V., Escher, Beate, Focks, A., van Gils, J., Ginebreda, A., Hering, D., Hewitt, L.M., Hilscherová, K., Hollender, J., Hollert, H., Köck, M., Kortenkamp, A., López de Alda, M., Müller, Christin, Posthuma, L., Schüürmann, Gerrit, Schymanski, E., Segner, H., Sleeuwaert, F., Slobodnik, J., Teodorovic, I., Umbuzeiro, G., Voulvoulis, N., van Wezel, A., and Altenburger, Rolf
- Abstract
To meet the United Nations (UN) sustainable development goals and the European Union (EU) strategy for a non-toxic environment, water resources and ecosystems management require cost-efficient solutions for prevailing complex contamination and multiple stressor exposures. For the protection of water resources under global change conditions, specific research needs for prediction, monitoring, assessment and abatement of multiple stressors emerge with respect to maintaining human needs, biodiversity, and ecosystem services. Collaborative European research seems an ideal instrument to mobilize the required transdisciplinary scientific support and tackle the large-scale dimension and develop options required for implementation of European policies. Calls for research on minimizing society’s chemical footprints in the water–food–energy–security nexus are required. European research should be complemented with targeted national scientific funding to address specific transformation pathways and support the evaluation, demonstration and implementation of novel approaches on regional scales. The foreseeable pressure developments due to demographic, economic and climate changes require solution-oriented thinking, focusing on the assessment of sustainable abatement options and transformation pathways rather than on status evaluation. Stakeholder involvement is a key success factor in collaborative projects as it allows capturing added value, to address other levels of complexity, and find smarter solutions by synthesizing scientific evidence, integrating governance issues, and addressing transition pathways. This increases the chances of closing the value chain by implementing novel solutions. For the water quality topic, the interacting European collaborative projects SOLUTIONS, MARS and GLOBAQUA and the NORMAN network provide best practice examples for successful applied collaborative research including multi-stakeholder involvement. They provided innovative conceptual, mode
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- 2019
40. Improved component‑based methods for mixture risk assessment are key to characterize complex chemical pollution in surface waters
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Posthuma, L., Altenburger, Rolf, Backhaus, T., Kortenkamp, A., Müller, Christin, Focks, A., de Zwart, D., Brack, Werner, Posthuma, L., Altenburger, Rolf, Backhaus, T., Kortenkamp, A., Müller, Christin, Focks, A., de Zwart, D., and Brack, Werner
- Abstract
The present monitoring and assessment of water quality problems fails to characterize the likelihood that complex mixtures of chemicals affect water quality. The European collaborative project SOLUTIONS suggests that this likelihood can be estimated, amongst other methods, with improved component-based methods (CBMs). The use of CBMs is a well-established practice in the WFD, as one of the lines of evidence to evaluate chemical pollution on a per-chemical basis. However, this is currently limited to a pre-selection of 45 and approximately 300 monitored substances (priority substances and river basin-specific pollutants, respectively), of which only a few actually co-occur in relevant concentrations in real-world mixtures. Advanced CBM practices are therefore needed that consider a broader, realistic spectrum of chemicals and thereby improve the assessment of mixture impacts, diagnose the causes of observed impacts and provide more useful water management information. Various CBMs are described and illustrated, often representing improvements of well-established methods. Given the goals of the WFD and expanding on current guidance for risk assessment, these improved CBMs can be applied to predicted or monitored concentrations of chemical pollutants to provide information for management planning. As shown in various examples, the outcomes of the improved CBMs allow for the evaluation of the current likelihood of impacts, of alternative abatement scenarios as well as the expected consequences of future pollution scenarios. The outputs of the improved CBMs are useful to underpin programmes of measures to protect and improve water quality. The combination of CBMs with effect-based methods (EBMs) might be especially powerful to identify as yet underinvestigated emerging pollutants and their importance in a mixture toxicity context. The present paper has been designed as one in a series of policy briefs to support decisions on water quality protection, monitoring, assessme
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- 2019
41. Assessing the ecological impact of chemical pollution on aquatic ecosystems requires the systematic exploration and evaluation of four lines of evidence
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Backhaus, T., Brack, Werner, van den Brink, P.J., Deutschmann, B., Hollert, H., Posthuma, L., Segner, H., Seiler, T.-B., Teodorovic, I., Focks, A., Backhaus, T., Brack, Werner, van den Brink, P.J., Deutschmann, B., Hollert, H., Posthuma, L., Segner, H., Seiler, T.-B., Teodorovic, I., and Focks, A.
- Abstract
The aim of the European Water Framework Directive is to ensure good ecological status for all European surface waters. However, although current monitoring strategies aim to identify the presence and magnitude of ecological impacts, they provide little information on the causes of an ecosystem impairment. In fact, approaches to establish causal links between chemical pollution and impacts on the ecological status of exposed aquatic systems are largely lacking or poorly described and established. This is, however, crucial for developing and implementing appropriately targeted water management strategies. In order to identify the role of chemical pollution on the ecological status of an aquatic ecosystem, we suggest to systematically combine four lines of evidence (LOEs) that provide complementary evidence on the presence and potential ecological impact of complex chemical pollution: (1) component-based methods that allow a predictive mixture risk modeling; (2) effect-based methods; (3) in situ tests; (4) field-derived species inventories. These LOEs differ systematically in their specificity for chemical pollution, data demands, resources required and ecological relevance. They complement each other and, in their combination, allow to assess the contribution of chemical pollution pressure to impacts on ecological structure and function. Data from all LOEs are not always available and the information they provide is not necessarily consistent. We therefore propose a systematic, robust and transparent approach to combine the information available for a given study, in order to ensure that consensual conclusions are drawn from a given dataset. This allows to identify critical data gaps and needs for future testing and/or options for targeted and efficient water management.
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- 2019
42. Prioritisation of water pollutants: the EU Project SOLUTIONS proposes a methodological framework for the integration of mixture risk assessments into prioritisation procedures under the European Water Framework Directive
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Faust, M., Backhaus, T., Altenburger, Rolf, Dulio, V., van Gils, J., Ginebreda, A., Kortenkamp, A., Munthe, J., Posthuma, L., Slobodnik, J., Tollefsen, K.E., van Wezel, A., Brack, Werner, Faust, M., Backhaus, T., Altenburger, Rolf, Dulio, V., van Gils, J., Ginebreda, A., Kortenkamp, A., Munthe, J., Posthuma, L., Slobodnik, J., Tollefsen, K.E., van Wezel, A., and Brack, Werner
- Abstract
Current prioritisation procedures under the EU Water Framework Directive (WFD) do not account for risks from chemical mixtures. SOLUTIONS proposes a multiple-lines-of-evidence approach to tackle the problem effectively. The approach merges all available evidence from co-exposure modelling, chemical monitoring, effect-based monitoring, and ecological monitoring. Full implementation of the proposed methodology requires changes in the legal text in adaptation to scientific progress.
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- 2019
43. Future water quality monitoring: improving the balance between exposure and toxicity assessments of real-world pollutant mixtures
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Altenburger, Rolf, Brack, Werner, Burgess, R.M., Busch, Wibke, Escher, Beate, Focks, A., Hewitt, L.M., Jacobsen, B.N., López de Alda, M., Ait-Aissa, S., Backhaus, T., Ginebreda, A., Hilscherová, K., Hollender, J., Hollert, H., Neale, P.A., Schulze, Tobias, Schymanski, E.L., Teodorovic, I., Tindall, A.J., De Aragão Umbuzeiro, G., Vrana, B., Zonja, B., Krauss, Martin, Altenburger, Rolf, Brack, Werner, Burgess, R.M., Busch, Wibke, Escher, Beate, Focks, A., Hewitt, L.M., Jacobsen, B.N., López de Alda, M., Ait-Aissa, S., Backhaus, T., Ginebreda, A., Hilscherová, K., Hollender, J., Hollert, H., Neale, P.A., Schulze, Tobias, Schymanski, E.L., Teodorovic, I., Tindall, A.J., De Aragão Umbuzeiro, G., Vrana, B., Zonja, B., and Krauss, Martin
- Abstract
Environmental water quality monitoring aims to provide the data required for safeguarding the environment against adverse biological effects from multiple chemical contamination arising from anthropogenic diffuse emissions and point sources. Here, we integrate the experience of the international EU-funded project SOLUTIONS to shift the focus of water monitoring from a few legacy chemicals to complex chemical mixtures, and to identify relevant drivers of toxic effects. Monitoring serves a range of purposes, from control of chemical and ecological status compliance to safeguarding specific water uses, such as drinking water abstraction. Various water sampling techniques, chemical target, suspect and non-target analyses as well as an array of in vitro, in vivo and in situ bioanalytical methods were advanced to improve monitoring of water contamination. Major improvements for broader applicability include tailored sampling techniques, screening and identification techniques for a broader and more diverse set of chemicals, higher detection sensitivity, standardized protocols for chemical, toxicological, and ecological assessments combined with systematic evidence evaluation techniques. No single method or combination of methods is able to meet all divergent monitoring purposes. Current monitoring approaches tend to emphasize either targeted exposure or effect detection. Here, we argue that, irrespective of the specific purpose, assessment of monitoring results would benefit substantially from obtaining and linking information on the occurrence of both chemicals and potentially adverse biological effects. In this paper, we specify the information required to: (1) identify relevant contaminants, (2) assess the impact of contamination in aquatic ecosystems, or (3) quantify cause–effect relationships between contaminants and adverse effects. Specific strategies to link chemical and bioanalytical information are outlined for each of these distinct goals. These strategies have
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- 2019
44. Effect‑based methods are key. The European Collaborative Project SOLUTIONS recommends integrating effect‑based methods for diagnosis and monitoring of water quality
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Brack, Werner, Ait-Aissa, S., Backhaus, T., Dulio, V., Escher, Beate, Faust, M., Hilscherova, K., Hollender, J., Hollert, H., Müller, Christin, Munthe, J., Posthuma, L., Seiler, T.-B., Slobodnik, J., Teodorovic, I., Tindall, A.J., De Aragão Umbuzeiro, G., Zhang, X., Altenburger, Rolf, Brack, Werner, Ait-Aissa, S., Backhaus, T., Dulio, V., Escher, Beate, Faust, M., Hilscherova, K., Hollender, J., Hollert, H., Müller, Christin, Munthe, J., Posthuma, L., Seiler, T.-B., Slobodnik, J., Teodorovic, I., Tindall, A.J., De Aragão Umbuzeiro, G., Zhang, X., and Altenburger, Rolf
- Abstract
The present monitoring and assessment of the chemical status of water bodies fail to characterize the likelihood that complex mixtures of chemicals affect water quality. The European Collaborative Project SOLUTIONS suggests that this likelihood can be estimated with effect-based methods (EBMs) complemented by chemical screening and/or impact modeling. These methods should be used to identify the causes of impacted water quality and to develop programs of measures to improve water quality. Along this line of reasoning, effect-based methods are recommended for Water Framework Directive (WFD) monitoring to cover the major modes of action in the universe of environmentally relevant chemicals so as to evaluate improvements of water quality upon implementing the measures. To this end, a minimum battery of bioassays has been recommended including short-term toxicity to algae, Daphnia and fish embryos complemented with in vitro and short-term in vivo tests on mode-of-action specific effects as proxies for long-term toxicity. The likelihood of adverse impacts can be established with effect-based trigger values, which differentiate good from poor water quality in close alignment with Environmental Quality Standards for individual chemicals, while taking into account mixture toxicity. The use of EBMs is suggested in the WFD as one avenue to establish the likelihood of adverse effects due to chemical pollution in European water systems. The present paper has been written as one component of a series of policy briefs to support decisions on water quality monitoring and management under the WFD.
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- 2019
45. Chemicals in plastic packaging: Prioritization of hazardous substances
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Groh, K, Backhaus, T., Carney Almroth, Bethany, Geueke, B, Lennquist, A, Leslie, H.A., Muncke, J, E&H: Environmental Chemistry and Toxicology, and AIMMS
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- 2018
46. Harmonised risk assessment for human health, animal health and ecological risk assessment of combined exposure to multiple chemicals:a food and feed safety perspective
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Dorne, J. -L. C. M., Benford, D., Ragas, A., Posthuma, L., Kass, G. E., Manini, P., Dujardin, B., Benfenati, E., Hardy, A., Testai, E., Castle, L., Svendsen, C., Bennekou, S., Laskowski, R., Solecki, R., Leblanc, J. C., Kortenkamp, A., Kille, P., Price, P., Backhaus, T., Cedergreen, N., Hogstrand, C., Dorne, J. -L. C. M., Benford, D., Ragas, A., Posthuma, L., Kass, G. E., Manini, P., Dujardin, B., Benfenati, E., Hardy, A., Testai, E., Castle, L., Svendsen, C., Bennekou, S., Laskowski, R., Solecki, R., Leblanc, J. C., Kortenkamp, A., Kille, P., Price, P., Backhaus, T., Cedergreen, N., and Hogstrand, C.
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- 2018
47. Harmonised risk assessment for human health, animal health and ecological risk assessment of combined exposure to multiple chemicals: a food and feed safety perspective
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Dorne, J.-L.C.M., primary, Benford, D., additional, Ragas, A., additional, Posthuma, L., additional, Kass, G.E., additional, Manini, P., additional, Dujardin, B., additional, Benfenati, E., additional, Hardy, A., additional, Testai, E., additional, Castle, L., additional, Svendsen, C., additional, Bennekou, S., additional, Laskowski, R., additional, Solecki, R., additional, Leblanc, J.C., additional, Kortenkamp, A., additional, Kille, P., additional, Price, P., additional, Backhaus, T., additional, Cedergreen, N., additional, and Hogstrand, C., additional
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- 2018
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48. 5217Long-term effects of iron deficiency in patients with heart failure with or without anemia - the RAID-HF follow-up study
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Wienbergen, H, primary, Pfister, O, additional, Hochadel, M, additional, Fach, A, additional, Backhaus, T, additional, Bruder, O, additional, Remppis, B A, additional, Maeder, M T, additional, Von Scheidt, W, additional, Pauschinger, M, additional, Senges, J, additional, and Hambrecht, R, additional
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- 2018
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49. P3679Trends in mortality and MACCE-rates between 2006 and 2016 in patients with ST-elevation myocardial infarctions and a low overall risk
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Schmucker, J, primary, Wienbergen, H, additional, Fach, A, additional, Backhaus, T, additional, Garstka, D, additional, Osteresch, R, additional, Fiehn, E, additional, and Hambrecht, R, additional
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- 2018
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50. P1228Which role plays the school degree in effectiveness of prevention after myocardial infarction?
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Backhaus, T, primary, Michel, S, additional, Meyer, S, additional, Fach, A, additional, Schmucker, J, additional, Osteresch, R, additional, Stehmeier, J, additional, Wettwer, T, additional, Haase, H, additional, Elsaesser, A, additional, Hambrecht, R, additional, and Wienbergen, H, additional
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- 2018
- Full Text
- View/download PDF
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