Solutions for present and future emerging pollutants in land and water resources management
HELMHOLTZ-ZENTRUM FUR UMWELTFORSCHUNG GMBH - UFZ
€ 1 920 500
Annette Schmidt (Ms.)
Sort by EU Contribution
€ 588 509,25
ENVIRONMENTAL INSTITUTE s.r.o.
€ 818 201,08
IVL SVENSKA MILJOEINSTITUTET AB
€ 630 000
JRC -JOINT RESEARCH CENTRE- EUROPEAN COMMISSION
€ 159 172,17
KWR WATER B.V.
€ 330 500
EIDGENOESSISCHE ANSTALT FUER WASSERVERSORGUNG ABWASSERREINIGUNG UND GEWAESSERSCHUTZ
€ 350 000
NORSK INSTITUTT FOR VANNFORSKNING
€ 249 750
PROF DR ASEN ZLATAROV UNIVERSITY
€ 225 120
OEKO-INSTITUT E.V. - INSTITUT FUER ANGEWANDTE OEKOLOGIE
€ 214 839
€ 350 000
RIJKSINSTITUUT VOOR VOLKSGEZONDHEID EN MILIEU
€ 353 905,25
STICHTING WAGENINGEN RESEARCH
€ 431 202,25
AGENCIA ESTATAL CONSEJO SUPERIOR DEINVESTIGACIONES CIENTIFICAS
€ 351 840
FAUST UND BACKHAUS ENVIRONMENTAL CONSULTING GBR
€ 346 845,20
BRUNEL UNIVERSITY LONDON
€ 525 000
VLAAMSE INSTELLING VOOR TECHNOLOGISCH ONDERZOEK N.V.
€ 350 001
CARL VON OSSIETZKY UNIVERSITAET OLDENBURG
€ 175 000
€ 250 000
University of Novi Sad Faculty of Sciences
€ 150 000
MAXX MESS- UND PROBENAHMETECHNIK GMBH
€ 90 500
INSTITUT NATIONAL DE L ENVIRONNEMENT ET DES RISQUES INERIS
€ 350 000
€ 198 750
SYNCHEM LABORGEMEINSCHAFT UG & CO KG
€ 90 020
THE UNIVERSITY OF BIRMINGHAM
€ 250 652
THE UNIVERSITY OF LIVERPOOL
€ 100 000
International Commission for the Protection of the Danube River
€ 136 879
€ 95 500
€ 350 000
RHEINISCH-WESTFAELISCHE TECHNISCHE HOCHSCHULE AACHEN
€ 213 632
€ 258 600
€ 248 000
LEIBNIZ-INSTITUT FUR PFLANZENBIOCHEMIE
€ 185 001
€ 107 200
€ 233 816
€ 100 000
€ 210 000
THE UNIVERSITY OF QUEENSLAND
UNIVERSIDADE ESTADUAL DE CAMPINAS
Grant agreement ID: 603437
1 October 2013
30 September 2018
€ 16 323 009,85
€ 11 988 935,20
HELMHOLTZ-ZENTRUM FUR UMWELTFORSCHUNG GMBH - UFZ
Final Report Summary - SOLUTIONS (Solutions for present and future emerging pollutants in land and water resources management)
While current WFD monitoring and assessment of contamination of European water bodies is based on a limited number of Priority Substances complemented by River Basin Specific Pollutants, complex mixtures of thousands of chemicals can be detected in the aquatic environment and may pose a risk to ecosystems and human health. The project SOLUTIONS proposed and demonstrated innovative and efficient approaches for a more holistic and solutions-oriented assessment of these complex mixtures. To this end, SOLUTIONS provided tools and recommendations for better fulfilling the ambitions of the WFD and the European goal of achieving a non-toxic environment. This will support impact assessment and diagnosis (WFD Annex II), improved monitoring and the use of models to prioritize chemicals, identify abatement options and knowledge gaps. SOLUTIONS efforts included legacy and currently used substances as well as upcoming contamination problems.
A solutions-oriented monitoring toolbox has been developed together with extensive guidance for users. This toolbox is composed of chemical analytical tools for advanced trace analysis to improve the limits of detection for chemicals with very low effect concentrations, multi- and non-target screening to address contamination patterns and to prioritize emerging contaminants and mixtures thereof, a validated battery of effect-based methods that allow for the detection and quantification of mixtures of chemicals with common effects, sampling strategies and devices for joint effect-based and chemical monitoring and approaches to identify toxicity drivers by linking chemical and effect-based methods. The toolbox is complemented with ecological tools to diagnose impacts on communities and ecosystems and to control the success of abatement options. All these tools have been tested and demonstrated in large case studies in the river basins of Danube, Rhine and several Spanish rivers building on major monitoring, assessment and abatement activities in these rivers including the Joint Danube Survey 3, the upgrade of wastewater treatment plants (WWTPs) in Switzerland, and the assessment of pollution impacts under conditions of water scarcity in Spanish rivers. Major outcomes were a list of River Basin Specific Pollutants for the River Danube that is directly used in the River Basin Management Plan, the control and demonstration of success of abatement measures in Swiss WWTPs, as well as the prioritization of chemicals under water scarcity.
Complementary to monitoring, the SOLUTIONS model train has been developed as a closely integrated system of models involving emission modelling, fate and transport modelling and modelling of mixture risks to ecosystems and human health via drinking water and fish consumption. Due to a lack of physico-chemical property and toxicity data for many emerging pollutants major efforts have been made to provide QSAR and read across models to predict these properties as input data for all other models but also for a risk assessment and prioritization based on monitoring data. For about 5000 chemicals including REACH chemicals, pharmaceuticals and pesticides temporally and spatially explicit exposures and risks have been predicted, scenarios involving different abatement options, as well as future trends of emerging pollutants have been modeled. Chemical footprints were used for assessment and prioritization of pollution sources and abatement options.
SOLUTIONS user-friendly products include among others RiBaTox, a web-based system presenting SOLUTIONS tools and models in a systematic way along the questions of the users and an extensive knowledge base compiling monitoring and property data in an easily accessible way. All models, tools and other products have been developed in a close dialogue with a strongly participating board of stakeholders from the European Commission, national, European and international agencies, international river associations and water industry.
Project Context and Objectives:
Monitoring programs under the Water Framework Directive (WFD) have accumulated vast amounts of data on contamination and on the ecological status of surface waters in the EU . However, these data are in most cases restricted to a list of so-called Priority Substances that has been extended to 45 substances in 2013 . There has been substantial concern that this list of substances might not properly characterize the pollution status and is not sufficient for the assessment of impact as required in Annex II of the WFD . The large number of substances of emerging concern including most of the chemicals in daily use and mixtures thereof are ignored. At the same time, a wealth of chemical property and emission data from registration of chemicals (e.g. REACH ), plant protection products and biocides , pesticides  and pharmaceuticals  was becoming available. Although toxic effects on aquatic life were frequently observed, it was a great challenge to link occurrence of chemicals with the ecological status of waters, to identify major chemical stressors, and to find solutions for the abatement of pollution-related risks. Awareness was increasing that complex mixtures of priority pollutants, emerging substances, by- and transformation products, and natural compounds occur in aquatic systems. This challenged the established means of monitoring, assessment and abatement. The emerging substances were known to include a multitude of polar and ionic compounds for which many of the classical models developed for non-polar POPs such as PCBs, OCPs and PAHs do not apply. Pollution was assumed to affect a multitude of toxicity pathways in organisms, populations, and communities. However, there was a high likelihood that toxic pollution remained unrecognized due to the sheer number of potentially harmful chemicals and consequently there was a danger that adverse impacts on aquatic communities and human health from unknown or unexpected chemicals and mixtures were ignored. The problem was aggravated by analytical detection limits that were often too high for discovering certain chemicals below their predicted no-effect-levels (PNEC). There was also a lack of understanding regarding sources, transport pathways, transfer times, fate, and mixture effects, together with insufficiently developed modelling capacity.
SOLUTIONS was designed to address these challenges by mobilising the cumulative expertise from important FP6 and FP7 projects and from leading scientific groups in all relevant disciplines. SOLUTIONS involved numerous major stakeholders on a European and river basin scale as full partners, or as members of the SOLUTIONS Stakeholder Board. The partnership was forged to deliver a conceptual framework, the tools, the knowledge base, and case studies to solve major problems. Uniquely, SOLUTIONS had access to the infrastructure necessary to consider the catchment of the Danube, the EU’s largest river, with the International Commission for the Protection of the Danube River (ICPDR) as a full partner and the Joint Danube Survey 3 (JDS3), the worldwide biggest river expedition in 2013, as a resource to build on. In assessing the impact of quaternary wastewater treatments in Switzerland, SOLUTIONS had the unique opportunity to evaluate control measures and abatement options in the Rhine basin. Impact monitoring and assessment was planned to be done in joint efforts with the project EcoImpact as well as with several on-going (inter)national studies on drinking water through a network of KWR with drinking water industry and authorities (e.g. DEMEAU). SOLUTIONS approaches should also be validated under the conditions of water scarcity in the Mediterranean region through collaboration with the on-going project SCARCE. In addition, SOLUTIONS had the opportunity to benefit from an exchange of data, knowledge and experience with assessment and monitoring as well as from research projects of key players in water resources management outside Europe involving leading groups in China, Australia and Brazil and with the participation of US-EPA and Environment Canada in the Stakeholder Board.
The project decided to put a focus on contributions from SMEs and to initiate an intensive dialogue with relevant stakeholders. SOLUTIONS specifically targeted the WFD Common Implementation Strategy (CIS) expert groups, international river basin commissions and drinking water associations and supported these decision makers in developing environmental and water policies with respect to emerging pollutants and pollutant mixtures. The emphasis was on finding improved management and abatement options for the minimization of ecological and human health risks.
Our overall strategy was to build a project that is complementary to the many existing international efforts, to effectively use existing knowledge, and to bridge missing links. SOLUTIONS brought together complementary pan-European databases on current and future emerging substances including, i.a. NORMAN EMPODAT, mass spectral database MassBank and the unique SPIN database on the use of Substances in Products in the Nordic Countries. The data were linked to the assessment procedures including the Chemical Properties Estimation Software System ChemProp and latest prioritisation tools developed specifically for emerging substances (e.g. by the NORMAN Association). All of these were directly interfaced with the Integrated Platform for Chemical Monitoring (IPCheM) system developed by the European Commission (JRC) via a specific Integrated Data Portal for SOLUTIONS (IDPS), and interlinked with SOLUTIONS models and decision tools.
A full chain of next generation monitoring tools including highly sensitive target analysis for compounds with low PNECs, powerful non-target screening tools, a multitude of effect-based tools including multi-endpoint reporter gene assays and toxicogenomics tools together with effect-directed analysis (EDA) of relevant toxicants in complex contaminated environments should be advanced and applied in large scale case studies together with an extensive set of integrated models for prediction of fate, exposure, effects and risks to ecosystem and human health.
Based on thorough evaluations of existing data from previous projects and extensive own monitoring and modelling SOLUTIONS developed solution-oriented approaches to alleviate and prevent chemical pressures on Europe’s water bodies according to the WFD. These solution-oriented approaches were built through interaction processes between hazard identification efforts and problem solving options  by continuously involving stakeholders and a project-based think tank. SOLUTIONS strived for establishment of a harmonised and transparent procedure for setting up lists of River Basin Specific Pollutants (RBSPs) in support of the ecological status assessment and the review of the Water Framework Directive. This required improved procedures for the identification and prioritisation of current emerging pollutants, and the development of new criteria and predictive tools for upcoming pollutants, together with scientifically sound assessments of mixtures and options for their management. To this end, SOLUTIONS combined, integrated and mutually validated monitoring- and modelling-based approaches and evaluated potential opportunities for cooperation between the WFD and other EU water related legislation, with focus on REACH.
Unbiased approaches that address biological responses and chemicals holistically rather than through pre-selected endpoints and target compounds should be developed with the aim of defining the toxic burden of aquatic ecosystems. SOLUTIONS was designed to bring us closer to the vision of being able to estimate the overall and cumulative ecological and human health impact of all chemical substances currently used in the EU and found in European water resources addressing also the objectives of the Blueprint to Safeguard Europe's Water Resources  whose time horizon is closely related to the EU's 2020 Strategy, the European Innovation Partnerships on Water (EIP Water ) and the Joint Programming Initiative “Water challenges for a changing world” (WaterJPI ).
SOLUTIONS therefore set out with the following scientific objectives:
1) To develop a novel conceptual framework for the prioritisation of pollutants for ecological and human health risk assessment and the abatement of toxicant mixtures in European water resources. This framework should be based on the alignment and validation of unbiased field observations with exposure and mixture impact predictions for chemicals that are known to be emitted, also considering abatement options. This concept was supposed to help to identify the strengths and weaknesses of field observations and modelling approaches, and to provide guidance for optimal and cost-efficient mutual integration. This should include the evaluation of methods designed to bridge data gaps, such as thresholds of ecotoxicological concern (ecoTTC), which are intended to overcome impediments to hazard assessment due to missing NOEC data. With the same intention, pragmatic simplifications of scientific concepts, e.g. for mixture toxicity assessment, should be considered. The conceptual framework should be developed in dialogue with key stakeholders from regulation and water industry.
2) To deliver efficient tools for the identification of substances and mixtures that pose risks to the aquatic environment and human health. To achieve this goal SOLUTIONS (1) developed a new generation of monitoring approaches and tools for the early detection and identification of harmful substances. These should comprise sensitive tools for the analysis of pollutants at concentrations below their PNECs. The tools should address impacts on ecosystems and human health, include powerful targeted and novel unbiased effect-based tools (EBTs) as well as trait-based indicators of ecological impacts, and improve integrated tools to identify cause-effect relationships. (2) SOLUTIONS improved understanding and capacity for exposure, effect and risk modelling by compiling a full chain of conceptually integrated models and databases accessible via a user-friendly computer tool (RiBaTox) to support decisions in environmental and water policies. This was designed to guide the user towards the appropriate models and monitoring tools to solve specific questions involving models on sources, transport pathways, transfer times between surface waters and air, soil, sediments, groundwater and biota, chemicals fate (degradation, bioaccumulation, spatial and temporal variability of concentrations in different compartments) as well as strategies for sampling, analyzing and assessing mixtures of emerging chemicals in different compartments and their impacts and risks including possible synergistic effects. The models were designed to exploit monitoring and project data on a European scale and make use of the wealth of data from the authorisation of pesticides, biocides, pharmaceuticals, and registration of industrial chemicals under REACH.
3) To assess the implications for the overall assessment of the ecological and human health risks posed by emerging substances in the (aquatic) environment. The project followed the goal to (1) demonstrate the added value of the new generation of tools in trans-European case studies in the Danube, Rhine, and rivers of the Iberian peninsula with links to existing monitoring programs (JDS) and projects (EcoImpact, DEMEAU, SCARCE). The modelling and field-based approaches should be mutually validated and applied to impact and risk assessments, the identification of RBSPs, and the evaluation of abatement options. (2) SOLUTIONS should evaluate potential opportunities and obstacles for cooperation between the WFD and other existing policies (e.g. REACH). To analyse the legal basis for an integrated approach, SOLUTIONS helped to address conflicting goals, e.g. between the overall objective of harmonization and a more targeted assessment of human health and environmental risks under specific environmental conditions.
4) To provide solutions for the prioritisation, assessment, management, and abatement of emerging pollutants and a common knowledge base for a wide range of toxicants. To meet this objective SOLUTIONS (1) synthesized the new approaches, condensed them into user-friendly guidelines, computer tools and recommendations for direct support of the WFD-CIS, EIP Water, international river basin district authorities (ICPDR), water works associations (International Association of Water Works in the Rhine Basin - IAWR and the Danube Catchment Area - IAWD), and other stakeholders. SOLUTIONS anticipated targeted dissemination to stakeholders, the scientific community, and the general public. Innovative analytical, effect-based, and modelling tools will enter the market via the strong group of SOLUTIONS SMEs. (2) The project targeted to assess abatement options and control measures for emerging pollutants in waste and drinking water treatment for effective risk reduction. SOLUTIONS planned assessments of benefits and limitations of policy options, technical and non-technical measures, and proposed innovative chemical management methods. (3) SOLUTIONS intended to deliver a common knowledge base on a wide range of toxicants, an evidence-based compilation of substances with emissions that might require regulation, and comprehensive lists of RBSPs for the case study in the Danube river basin as a result of the integrated application of the new generation of monitoring and modelling tools. Extrapolation on a European scale should be performed to support an evidence-based review of priority substances under the WFD. Based on trends and scenarios, possible pollutants of tomorrow and related risks were estimated involving a think tank of SOLUTIONS scientists together with external experts. The projections were to be combined with modelling to develop future scenarios of chemical risks, and identify upcoming demands.
To summarize, SOLUTIONS was designed to deliver a rational basis for dealing with the challenges of complex mixtures of emerging pollutants in monitoring, diagnosis and impact assessment, and to provide an effective strategy for resolving the disparities between chemical-oriented monitoring and assessments of the ecological status of surface waters that currently exists in the WFD. It should also help to align the WFD better with the philosophy of other major EU regulations such as REACH.
1. EEA State of Water report, http://www.eea.europa.eu/themes/water/publications-2012.
2. European Union, Directive 2013/39/EU of the European Parliament and the Council of 12. August 2013 amending Directives 2000/60/EC and 2008/105/EC as regards priority substances in the field of water policy. Official Journal of the European Union, 2013. L 226/1.
3. Regulation (EC) No 1907/2006 of the European Parliament and of the Council of 18 December 2006, concerning the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH), establishing a European Chemicals Agency, amending Directive 1999/45/EC and repealing Council Regulation (EEC) No 793/93 and Commission Regulation (EC) No 1488/94 as well as Council Directive 76/769/EEC and Commission Directives 91/155/EEC, 93/67/EEC, 93/105/EC and 2000/21/EC, OJ L 396/1, 30.12.2006.
4. Directive 98/8/EC of the European Parliament and of the Council concerning the placing of biocidal products on the market, OJ L123, 24.04.1998 to be replaced by Regulation (EU) No 528/2012 of the European Parliament and of the Council concerning the making available on the market and use of biocidal products, OJ L 167, 27.06.2012.
5. Directive 2009/128/EC of the European Parliament and of the Council establishing a framework for Community action to achieve the sustainable use of pesticides, OJ L309, 24.11.2009.
6. Directive 2010/84/EU of the European Parliament and of the Council amending, as regards pharmacovigilance, Directive 2001/83/EC on the Community code relating to medicinal products for human use, OJ L348, 31.12.2010; and Recital 3 of Regulation (EU) No 1235/2010 of the European Parliament and of the Council amending, as regards pharmacovigilance of medicinal products for human use, Regulation (EC) No 726/2004 laying down Community procedures for the authorization and supervision of medicinal products for human and veterinary use and establishing a European Medicines Agency, and Regulation (EC) No 1394/2007 on advanced therapy medicinal products, OJ L348, 31/12/2010.
7. National Research Council . Committee on Improving Risk Analysis Approaches Used by the, U.E. et al., Science and decisions: Advancing risk assessment. 2009: National Academy Press.
8. A Blueprint to Safeguard Europe's Water Resources, Communication from the Commission to the European Parliament, the Council, the European Economic and Social Committee and the Committee of the Regions, COM(2012) 673 final.
9. Commission Communication on the European Innovation Partnership on Water, COM(2012) 216 final, 10.05.2012.
10. See http://www.waterjpi.eu/water-jpi/.
The project SOLUTIONS has been designed in four subprojects called Concepts and Solutions (SP1), Tools (SP2), Models (SP3) and Cases (SP4), which are highly interactive and presented in Figure 1.
Figure 1: Structure of the project (see attached file)
SP1 comprises of a work package (WP1) providing the conceptual framework of SOLUTIONS together with several WPs delivering the final products based on this conceptual framework as well as on all the research that has been conducted in SPs 2, 3 and 4. The final products comprise an advanced methodology for the prioritization of contaminants, a database and guidance on abatement and innovative toxicants management, RiBaTox as a web-based tool providing SOLUTIONS tools and services in a user-friendly way to support monitoring, assessment and abatement as well as to address regulatory and societal questions on pollution, a toxicant knowledge base comprehensively compiling and providing SOLUTIONS data, trends and scenarios on future pollution and solutions to conflicts and gaps in policies.
1. SP1: Concepts and SOLUTIONS
1.1 WP1: Conceptual framework and integration of concepts and solutions
The overall objective of the project SOLUTIONS was to provide solutions for monitoring, assessment and abatement of the complex mixtures of chemicals that can be detected in European water resources and thus approaches and tools to assess the “likelihood that surface water bodies will fail to meet the environmental quality objectives” due to chemical mixtures. Although there was a specific focus on emerging substances, the conceptual framework of SOLUTIONS has been designed in a way that it is able to address the whole universe of chemicals including those that may be considered as legacy chemicals, presently used substances and even future compounds. Having in mind that current monitoring and assessment based on a small set of Priority Substances often does neither provide a clear link to the Ecological Status nor suggest and prioritize abatement options, a solutions-oriented approach was the focal point of the conceptual framework (Figure 2). In agreement with stakeholders’ questions and requirements the SOLUTIONS conceptual framework has several entry points including
(a) Environmental observations (called “environment” in the scheme) such as a not good Ecological Status or measurable toxicity in environmental compartments. This may trigger the need to identify and prioritize chemicals, mixtures and sources thereof as well as the requirement to select efficient abatement options. Both questions are intensively addressed in SOLUTIONS particularly in the SPs on tools and cases.
(b) Given chemicals and the need to predict exposure and risks from a water body up to the European scale. This requirement has been successfully addressed particularly in the SP on models and validated in close interaction with SP cases. At the same time upcoming chemicals due to societal changes have been modeled in order to predict, prioritize and minimize future risks
(c) Societal developments (called “society” in the scheme) where scenarios and trends have been analyzed by the SOLUTIONS think tank in WP6 focusing on urbanisation, food supply, health care and new technologies. Since legal and policy instruments are an important tool to implement societal needs and to decide on abatement options, legal frameworks have been investigated for synergies in WP 7.
(d) Abatement options. Prioritizing most efficient abatement options is a key question under limited available resources. SOLUTIONS contributed to this task with an extensive database on abatement options and their efficiency for emerging chemicals together with prioritization approaches involving specific subjects of protection such as drinking water abstraction and valuable ecosystems, exposure and risk modeling and chemical footprints.
The SOLUTIONS conceptual framework has been provided and discussed in Deliverable 1.1 as well as in two scientific publications [1, 2]. The conceptual framework has been directly translated to the on-line tool RiBaTox (WP 4) as one of the major SOLUTIONS products supporting the dissemination of the SOLUTIONS tools and services and supporting practitioners in selecting appropriate and efficient tools to answer their questions.
Figure 2: Conceptual Framework of SOLUTIONS (see attached file)
1.2 WP2: Advanced methodology for the prioritization of contaminants
The prioritization of contaminants and contaminant mixtures is one of the key issues of solutions-oriented monitoring and assessment of chemical contamination. The proposal for advanced prioritization of contaminants aims to tackle the major shortcomings of current prioritization procedures under the WFD. These include (a) the fact that the high demands for a conclusive risk assessment cannot be met and risks of emerging pollutants remain undetected due to the lack of monitoring data and missing knowledge on exposure and effects, and (b) the focus on individual pollutants rather than appreciating the fact that chemicals never occur in isolation but always as complex mixtures. Existing concepts and methods for prioritization have been carefully reviewed. Since none of them provides a comprehensive solution for the complex problem, a novel framework has been suggested which integrates all available lines of evidence on significant risks (Figure 3). This includes evidences from (a) modelling of co-exposure and resulting mixture risks, (b) chemical monitoring of a broad range of chemicals together with component-based approaches for mixture risk assessment and driver identification, (c) effect-based monitoring together with effect-directed analysis for the identification of causative pollutants, compound groups and mixtures and (d) ecological monitoring and indications on drivers of ecological deterioration.
Figure 3: Multiple lines of evidence approach for prioritization of chemicals and mixtures (see attached file)
The prioritization approach is the result of three workshops in Paris (2014) establishing of the state-of-the-art in prioritization, in Gothenburg (2017) focusing on the identification of priority mixtures, the identification of risk drivers and the establishment of Environmental Quality Standards for priority mixtures, and again in Gothenburg (2018) on the final design of the methodological framework.
The results of this WP are presented in detail in Deliverable D2.1.
1.3 WP3: Abatement and innovative toxicants management
Technical and non-technical abatement options as well as efficient concepts to prioritize them are keys for a solutions-oriented assessment as highlighted in the SOLUTIONS conceptual framework. As a first step the perspectives of water cycle and the chemical life cycle were connected and possible abatement options were reviewed . The requirement for and the added value of a mitigation database to assess effectiveness of interventions by coupling them to regional or global hydrological models has been explored. Modeling the impact of pollution sources such as municipal and industrial WWTPs on susceptible functions of water resources allows for a spatially smart implementation of abatement options. This has been demonstrated for the example of Dutch WWTPs impacting on drinking water abstraction and on Natura 2000 areas  (Figure 4).
A similar approach has been used to prioritize industrial WWTPs for their impact on Dutch surface water quality and drinking water production (Deliverable D3.1). The results indicated that 32% of the abstracted water for drinking water production is affected by industrial WWTPs and several of them could be prioritized for their impact.
Figure 4: Overview of all Dutch WWTPs and their relative impact on drinking water abstraction and Natura 2000 areas  (see attached file)
Based on the concept of impact boundaries from the global to the regional scale Chemical Footprints have been explored and are recommended as a large-scale indicator the priority of abatement summarizing the volume of water needed to dilute the chemical mixture of a water body to a safe level in comparison with the available water amount. The SOLUTIONS approach allows for calculating Chemical Footprints for all water bodies in a region separately and provides the opportunity to explore how chemical pollution in upstream regions influence downstream water bodies. Regional chemical footprints can be mapped support management decisions (Figure 5).
Figure 5: Chemical Footprints of Rhine catchment for biodiversity (a), for drinking water (a) and for marine environment protection (c) (see attached file)
After prioritization of regions and sources for spatially smart abatement typically effective water treatment technologies need to be selected which is hampered by a lack of a homogenous approach for testing water treatment technologies. SOLUTIONS filled this gap by developing a data evaluation framework to be used by stakeholders and by defining criteria for reliability and relevance of data together with extensive guidance for data evaluation (D3.1). In addition, a database on treatment technologies and their efficiency for major pollutants has been provided (D3.1).
1.4 WP4: RiBaTox Web-based Decision Support System
As discussed in 1.1 the SOLUTIONS Conceptual Framework has been translated in close dialogue with our stakeholders to a user-friendly tool called RiBaTox, which is designed to provide structured access to the knowledge gathered in the project to support policy makers, technical staff and water managers in selecting appropriate models and tools to address their questions. RiBaTox is freely accessible via the SOLUTIONS website or directly under https://solutions.marvin.vito.be/ and has been extensively described in D4.1. RiBaTox is designed as a systematic tree providing valuable information on a branch, twig and leave level in a comprehensive format of 94 factsheets. On the branch level users can select between monitoring, modelling, prioritization, abatement and policy strategies as well as access databases and case studies. On a twig level these categories are further broken down detailing monitoring strategies to strategies for sampling, chemical analysis, effect-based monitoring, toxicant identification and ecological assessment which then guide users to specific methodologies. All fact sheets can be accessed via this systematic tree approach as well as via the entry points and questions that are highlighted in the conceptual framework including “chemicals”, “environment”, “abatement options” and “society”. The factsheets have a consistent format, explain the objectives that can be addressed with the approach, describe the methodology, give examples of application and interpretation and provide references and contact information. They are highly interactive and provide numerous links to related factsheets. All factsheets can be also downloaded as D4.1 from the SOLUTIONS website and used as a hardcopy. RiBaTox also provides direct links to all relevant databases produced in SOLUTIONS.
1.5 WP5: Toxicant knowledge base
The SOLUTIONS toxicant knowledge base provides compound- and structure-associated as well as site- and receptor-specific data and metadata of SOLUTIONS. It consists of different databases that are accessible via IDPS, the Integrated Data Portal for SOLUTIONS that includes five different modules including environmental modules, ecotoxicology, structure and properties, legislation and emission and abatement. One of the big advantages is the opportunity to search for different information on a specific chemical accessing all the modules at the same time. Searching a chemical by CAS, name, INChIKey or substructure, IDPS provides you with monitoring and ecotoxicity data for the compound of interest, structural information and physico-chemical properties, but also legislation, emission data and abatement information. Filtering options can be applied in order to restrict the search for example to a specific country, specific media or to distinct species. IDPS is linked to the European Information Platform for Chemical monitoring IPChem as well as to RiBaTox and accessible via the SOLUTIONS website.
1.6 WP6: Trends and scenarios
SOLUTIONS had the ambition to consider not only existing chemicals but also to provide first ideas of chemical pollution of tomorrow in order to provide options to act on future risks. The analysis of future perspectives on pollution trends was based on three major columns. The first column was the in-depth analysis of 34 publicly available studies on development in society by UNEP, EEA, McKinseys 2030 Water Resources Group, UNESCO, BMBF, OECD, EU Watch and many others including (a) scenarios for mid- and long-term developments in society, (b) developments in water use and water cycles, (c) developments in use and impact of chemicals, (d) climate change, (e) demographic change, (f) technological and economical changes, (g) development in food production, (h) nutrient scenarios and (i) further aspects such as precautionary principle, green economy, megatrends and scientific developments. The results are presented in D6.1. The second column was four workshops bringing together the SOLUTIONS think tank with external experts and addressing the topics public health 2030, food 2030, cities 2030 and technologies 2030. The third column was related to modelling of future risks combining scenarios and the application of the SOLUTIONS model train (D14.2). This approach considered 2 different scenarios in relation to reference situation in 2018 including no specific action and responsible action on upcoming problems.
The approach resulted in 21 recommendations on how to include future emerging pollutants into the management of river basins, which are detailed in D6.1. A key message might be that future increase in pressure and changes in pollution patterns are expected that need to be addressed with more efforts than end-of-pipe technologies only but should rely on the design and production of more sustainable chemicals and products.
1.7 WP7: Solutions to conflicts and gaps in policies
Regulatory frameworks can be one of the key drivers towards a non-toxic environment as proposed by the European Commission. Thus, SOLUTIONS investigated 19 existing regulatory frameworks for chemicals including EU regulations on industrial chemicals (REACH), plat protection products (PPP), biocidal products (BPR), Cosmetics and medicinal products, EU directives on water (WFD), groundwater (GWD), marine environments (MSFD), dringking water (DWD), sewage sludge (SSD), industrial emission (IED), mining waste, hazardous substances in electric and electronic equipment (RoHS) and toy safety, and multilateral agreements such as the Stockholm Convention, the Convention on Long-Range Transboundary Pollution, the Protocol on Pollutant Release and Transfer and the Rotterdam Convention. As discussed in D7.1 the overview revealed a quite fragmented situation with the regulatory frameworks designed for specific groups of chemicals and for protecting different endpoints. Despite the existence of a large number of regulations, many chemicals are not regulated but represent a potential risk and are denoted as Chemicals of Emerging Concerns (CECs).
The studied regulatory frameworks all regulate chemicals, but with different objectives. They address different endpoints including human health, human health an the environment or only the environment. Many of the frameworks only regulate emissions and/or occurrence in one receiving media but also consider only specific stages in the life cycle of a product as has been summarized in Figure 6.
From in-depth analysis of regulatory frameworks SOLUTIONS identified regulatory gaps and derived a number of recommendations to improve the situation (D7.1). In brief, we suggest (a) to harmonize objectives in a way that regulations consider both human health and environment and (b) to closer link emission and receiving-media oriented regulations such as REACH and WFD. REACH could clearly benefit from considering monitoring data collected under WFD. (c) The regulation of only selected and different stages in life cycles may introduce the risk of inefficient implementation and control. Systematic gaps are observed in trade and product use stages. (d) A key requirement for a better harmonized regulation is cooperation and exchange of information. Many chemicals are listed in different regulations. Common objectives, exchange of information and the use of harmonized terminology would substantially improve regulation. Information on use and emissions, physicochemical and toxicological properties, monitoring data and information on efficiencies, costs and applicability of abatement options should be made transparent and shared in common platforms. (e) Additional substances as well as mixtures need to be considered and (f) the international perspective should be strengthened. Despite the regulations on European market authorization of chemicals many other chemicals enter the EU via imported products.
Figure 6: Life cycle stages covered by the regulatory frameworks (see attached file)
2. SP2: Tools
In SP2 novel approaches and tools for chemical and biological monitoring have been developed and integrated to consistent workflows accompanied by user-friendly guidance for practitioners supposed to use the methods.
2.1 WP9: Integration of chemical, effect-based and ecological tools
The development of chemical, effect-based and ecological tools for a solutions-oriented monitoring and assessment of the presence and effects of complex mixtures of contaminants including the many non-regulated CECs was one of the major tasks of SOLUTIONS. It has been defined in detail in an early stage of the project  focusing on the development and adaptation of tools to deal with mixtures of pollutants in water resources management. This included, in addition to innovative research and development of tools, the integration in a comprehensive toolbox including a user-friendly guidance document and decision tree for the use of these tools in the identification of River Basin Specific Pollutants (RBSPs), impact assessment, and establishment of cause-effect relationships. The results of these efforts are provided in deliverable D9.1 that has been also submitted as a scientific publication. In addition, the information has been included in a condensed and structured way into RiBaTox (WP4). The toolbox developed in SOLUTIONS included several water sampling technologies, multi-residue target analysis and non-target screening, bioanalytical methods for complementary use in an effect-based water monitoring, effect-directed analysis as a tool to identify drivers of risks and to establish cause-effect relationships and finally ecology-directed analysis as a lines-of-evidence approach combining the afore-mentioned approaches with in situ-tests and field-based monitoring studies as it is schematically presented in Figure 7.
Figure 7: Aggregating information of different lines of evidence in a weight-of-evidence matrix (see attached file)
2.2 WP10: Chemical analytical tools
Major challenges of chemical monitoring of organic micro-pollutants are (a) the detection and quantification of target analytes at very low concentrations including particularly those that have very low predicted non-effect concentrations (PNECs), (b) the screening for the whole mixture including unexpected and unknown chemicals using non-target screening (NTS) and (c) the identification of the chemicals detected with NTS.
A major achievement of SOLUTIONS was the development, advancement and testing of tools for time-integrated sampling and enrichment of water samples for chemical analysis and the application of effect-based methods in order to achieve very low limits of detection and to collect sufficient material for more volume consuming methods such as some of the effect-based tools. In SOLUTIONS, two powerful approaches have been advanced and evaluated for this purpose, namely passive sampling and large volume solid phase extraction (LVSPE). Several partition- and adsorption-based passive samplers have been applied and a detailed guidance for their application has been provided in D10.1. They are powerful screening tools particularly for hydrophobic chemicals with low costs involved. LVSPE has been developed as a mobile tool to extract large volumes of water (50 to 1000L) in the field in order to strongly facilitate logistics related with handling, transportation and storage of large water volumes . Well-reflecting the original mixture in the water sample and excellent recoveries of analytes with a broad range of physico-chemical properties as well as of measured effects  suggest LVSPE particularly as a tool for lowly to moderately hydrophobic water contaminant mixtures, while very hydrophilic and very hydrophobic chemicals are outside the domain of this tool. Guidance is given in D10.1. In addition, the feasibility of using high-performance counter-current chromatography has been demonstrated as an alternative to SPE. For cases, where trace contaminants need to be quantified in water samples without the need of biotesting on-line solid phase extraction coupled to liquid chromatography mass spectrometry (SPE-LC-MS) has been explored and recommended (D10.1).
Sensitive and innovative tools in target analysis of emerging pollutants have been reviewed  and successfully demonstrated for the analysis of difficult trace components in the context of evaluation of treatment technologies including pharmaceuticals and iodinated contrast media in hospital wastewater , drugs of abuse [10, 11] and cytostatic drugs .
A large set of standard operational procedures for target analysis of emerging contaminants has been provided in D10.1.
Since target analysis is necessarily restricted to an (increasing) number of selected analytes, while SOLUTIONS has the ambition to address chemical contamination as a whole, suspect and non-target screening (NTS) got a strong focus in SOLUTIONS. A powerful NTS workflow has been established with a particular emphasis on its application in SOLUTIONS case studies (D10.1). This included methodological developments  as well as a collaborative trial . A complete evaluation and the identification of all underlying chemicals are not feasible. Thus, approaches to extract valuable information out of these huge datasets have been developed. These include three complementary approaches: (a) Prioritization of individual peaks or groups of peaks for in-depth analysis according to the specific objectives. This may include the selection of high intensity, high frequency, site-specific peaks, peaks with increasing trends or peak occurrence in time series, peaks occurring after specific sources etc. A powerful example is the application of NTS for monitoring of the River Rhine and the identification of peak emissions including unknown chemicals . (b) Suspect screening by searching NTS data for a large number of exact masses representing suspect chemicals lacking available standards. A typical example is the prediction of and screening for transformation products of known environmental pollutants [16, 17]. (c) The evaluation of whole NTS patterns using multivariate analysis. Several publications are in progress.
Compound identification and structure elucidation are typical follow-up steps on NTS. A highly efficient workflow based on the software MetFrag has been developed (10.1) involving novel computational approaches to use exact masses for the derivation of molecular formula and to identify structures. Candidate structures are retrieved by searching compound databases such as PubChem and ChemSpider or by predicting possible structures with MOLGEN. Subsequently, scoring and filtering criteria are used to select most probably structures. These criteria are based on mass spectrometric information including fragmentation and ionization, chromatographic retention time predictions, hydrogen/deuterium exchangeability but also other criteria such as the number of references in the database assuming that a frequently mentioned chemical is more likely to be found than a compound mentioned only few times. Several publications have summarized the new developments [18-21]. Diagnostic derivatization has been developed as a tool to detect specific groups of chemicals such as aromatic amines .
2.3 WP11: Effect-directed analysis
Effect-directed analysis (EDA) is designed to identify drivers of toxic effects in complex mixtures such as water, sediment and biota extracts. A consistent conceptual framework for EDA (Figure 8) has been developed in SOLUTIONS and supported by a comprehensive compilation and critical evaluation of available tools , (D11.1). Driver identification is considered as a stepwise approach most efficiently exploiting existing information and large scale chemical and effect-based monitoring linked by mass balance approaches and multivariate analysis. Higher tier EDA as a combination of biotesting, fractionation and in-depth chemical analysis is used as a site-specific approach for those cases where neither mass balances nor statistics are able to unravel cause-effect relationships.
Figure 8: Conceptual framework for EDA as a stepwise approach (see attached file)
Novel method applications and several successful field studies have been performed to demonstrate the power of EDA approaches. This includes mass balance approaches identifying drivers of endocrine disruption and other effects in water of the River Danube impacted by untreated wastewater from the city of Novi Sad  but also in small streams in the Rhine catchment . Virtual EDA has been demonstrated as a powerful tool in the identification of diaminophenazines as drivers of mutagenicity in industrial wastewater on the basis of a time series of samples [26, 27]. Several successful higher tier EDA studies have been performed in order to unravel site-specific toxic contamination. In a small German stream strong anti-androgenic effects have been detected and could be linked to coumarin 47, a frequently used fluorescent dye that has never been detected in monitoring so far and that was, thus, unknown as an environmental contaminant . Endocrine disruptors could be identified and quantitatively confirmed in the River Danube . EDA has been also demonstrated as a powerful tool to get insight into mutagenicity in the River Rhine. The effects have been shown to be mixture effects rather than driven by individual chemicals . Mixtures of industrial aromatic amines and natural carboline alkaloids detectable in the river water have been demonstrated to exhibit strong synergistic effects.
2.4 WP12: Effect-based tools
SOLUTIONS strongly recommends effect-based tools and methods (EBM) to complement chemical monitoring in order to determine the likelihood that “surface water bodies will fail to meet environmental quality objectives” (WFD) and to reduce the risk to overlook toxic chemicals not necessarily covered with chemical monitoring. Intensive research has been performed in order to develop improved bioassay solutions (D12.1) and to assess the feasibility of these solutions integrating for environmental monitoring (D12.2). A first important step has been the evaluation of frequently found surface water contaminants for their mode of action (MoA) in order to design a diagnostic test battery that covers all relevant MoAs . Since only for few MoAs specific in vitro assays are available SOLUTIONS suggests the use of a combination of apical tests involving fish embryos, daphnids and algae, also representing WFD BQEs, relevant for the Ecological Status, with MoA-specific in vitro assays on endocrine disruption, mutagenicity and dioxin-like effects. For specific purposes a set of additional tests on adaptive stress responses and changes in metabolism is available and covers links in relevant adverse outcome pathways (AOP) (Figure 9) .
Figure 9: AOP conceptual framework and the bioassays used within SOLUTIONS (see attached file)
The effects of 34 water pollutants with different MoAs were fingerprinted in a test battery of 20 bioassays. We could demonstrate that the tested battery was able to detect these specific effects individually and in mixtures.
Interlaboratory investigations further enhanced the degree of confidence into the application of EBMs in monitoring of complex mixtures [33, 34]. A specific focus was given on the detectability of mixture responses of active compounds against a background of other inactive compounds. The majority of in vitro and in vivo tests produced mixture responses in agreement with additivity expectation of concentration addition . Our findings support the application and further development of effect-based methods for water quality assessment, safeguarding specific water uses and diagnosis of complex contamination. This was also recommended in a policy brief released by SOLUTIONS and suggesting the test battery shown in Figure 10.
Figure 10: Recommended test battery bridging Chemical and Ecological Status (see attached file)
2.5 WP13: Ecological assessment tools
SOLUTIONS developed weight-of-evidence (WoE) approach that may be used for impact description, identification and quantification and for stressor identification and the establishment of cause-effect relationships. Four line of evidence (LoE) are considered including (a) chemical monitoring profiles and predictive mixture modelling, (b) effect-based monitoring and fingerprinting, (c) in situ approaches for the identification of chemical exposure or effects (e.g. biomarkers), (d) community indices based on field surveys of community composition. Available tools as well as the integrated concept are described in depth in D13.1.
This approach has been fully or in relevant parts applied and demonstrated in the large SOLUTIONS case studies Danube and Rhine as well as in an additional field study in the River Holtemme in Germany.
The WoE study in the case study Danube has been performed as a joint activity of WPs 13 and 19 and is based on data collected during Joint Danube Survey (JDS) 3 by ICPDR and SOLUTIONS. This demonstration study involved all four LoEs suggested above including chemical analysis and toxicity modelling based on toxic units (TU), in vitro bioassays, a battery of in situ biomarkers in sentinel fish and taxonomy- and trait-based analysis of fish and macroinvertebrate community. LoE1 based on chemical analysis indicated a considerable risk for macroinvertebrates. LoE2 representing effect-based fingerprinting used large-volume solid phase extracts for testing fish embryo toxicity, effects on algal growth and photosynthesis inhibition as well as nine receptor-based in vitro assays, including endocrine disruption, mutagenicity, neurotoxicity and adaptive stress responses. Along the River Danube significant effects at many sites have been detected for different endpoints without strong differentiation. Some tributaries inhibited stronger effects. LoE3 involved a substantial battery of biomarkers in wild fish including DNA damage, enzyme activities indicating changes in phase I and II biotransformation, oxidative stress and neurotoxicity, gene expression analysis in liver samples as well as histopathology. As for LoE3 similar biomarker responses have been detected along the Danube however with some significant peaks of neurotoxicity and genotoxicity . Taxonomy- and trait-based assessment of aquatic communities focused on macroinvertebrate and fish community structure using indices based on species richness, heterogeneity of the community, and other taxonomic and functional indicators for fish and three characteristic indices for macroinvertebrates including the Average Score Per Taxon (ASPT), the well-known saprobic index and the trait-based indicator SPEARpesticide reflecting the effect of toxic pollution. Most sites exhibited a moderate status with some significant exceptions with poor to bad status downstream of big cities such as Belgrade. The LoEs were integrated using quality classes for each of them: no effect, moderate effect, clear effect. In agreement with expectations for a large river with high dilution potential on the one hand but a lot of significant input of pollution from many sources, the WoE evaluation indicated clear anthropogenic impact and toxic pressure as a potential cause of degradation but also a ‘flat’ profile with not very pronounced differences and no real reference sites.
The WoE in the case study Rhine was performed as a joint activity with WP20 and focused on two LoEs, namely chemical analysis and TU distributions and in situ experiments with complex algal communities based on structure and pollution-induced community tolerance (PICT) . The study focused on the impact of wastewater treatment plants (WWTP) on river ecosystems and was designed as an upstream-downstream gradient study but as well as a Before-and-After-Impact study integrating the evaluation of the upgrade of one of the WWTPs. The study clearly indicated the strong impact of the WWTPs on the TU distributions with clear increase downstream based on pesticides and antibiotics. After WWTP upgrade with a fourth treatment step using powder-activated carbon filtration there was no more significant difference between upstream and downstream. This result was confirmed by the investigation of bacterial and algal structure. Principal component analysis (PCA) indicated clearly different communities upstream and downstream for non-upgraded WWTPs while the communities were very similar in structure after upgrade. PICT, indicating increased tolerance by the disappearance of sensitive species provided a further LoE confirming the occurrence of tolerant communities downstream the WWTPs without upgrade, while the upgraded WWTP had no impact on tolerance (Figure 11).
Figure 11: Tolerance of algal and bacterial production upstream and downstream of an upgraded and a non-upgraded WWTP (see attached file)
The WoE in the Holtemme River combined the analysis of toxic unit distribution for algae, daphnids and fish  with in situ biomarker responses in fish and genetic structure and body burdens of Gammarus pulex . All LoEs indicated significant risks and the strong and different impact of the two WWTPs along the river. The TU evaluation indicated significant risks to invertebrates, algae and fish with seasonal and random peaks of pesticides predominating acute toxicity while chronic and sublethal effects to fish were driven by constantly emitted pharmaceuticals . Water contamination was well reflected by internal concentrations in Gammarus pulex  as well as in genetic diversity in Gammarus populations . Detectable mutagenicity downstream of one of the WWTPs was reflected in Gammarus as the occurrence of private alleles.
3. SP3: Models
3.1 WP14: Integrated Models
SOLUTIONS provided the approaches and tools for a more holistic and solutions-oriented monitoring that covers a large set of chemicals, measurable effects in laboratory test systems and in situ, and community alterations. However, there will be always gaps in compounds covered, in time, in space and in matrix under consideration. Thus, SOLUTIONS developed an integrated system of models called the SOLUTIONS model train that helps identify gaps of specific concern and thus provide indications on monitoring needs with high priority and tentatively fill these gaps, and identify chemicals, regions and times with low or no risk that do not require major monitoring efforts. The SOLUTIONS model train comprises four highly integrated modules including emission modelling (WP15), transport and fate modelling (WP16), substance metabolism and properties modelling (WP17) and human and ecological risk modelling of pollutant mixtures (WP18). A scheme of the integrated model train and external data used is compiled in Figure 12. The model train operates on the scale of Europe as a whole or for one or more individual river basins. The spatial schematization as well as hydrology, soil type, land use and crop cover are derived from the Europe-wide hydrology model E-hype developed by SMHI. The SOLUTIONS model train is designed to provide temporarily and spatially explicit predictions of exposure and risks. The whole modelling framework is described in more detail in D14.1.
Figure 12: Scheme of the SOLUTIONS modelling system and its modules (see attached file)
3.2 WP15: Emission modelling
Emission modelling has been derived from the Dutch Pollutant Release and Transfer Register (PRTR) as a basis of the European Pollutant Release and Transfer Register (E-PRTR, http://prtr.ec.europa.eu/#/home). The emission modelling separates three groups of substances (pesticides, pharmaceuticals and chemicals registered under REACH) and provides temporally and spatially resolved emissions to surface waters and soils (D14.1).
The losses of pharmaceuticals are estimated based on per-capita sales in different countries. Human excretion is assumed to be 12% of the amount sold on average and all losses are assumed to reach the wastewater. The losses of pesticides to air, surface water and soil have been estimated using the harvested-area approach combining crop- and substance-specific application rates with known agricultural land uses. The losses of REACH registered organic chemicals have been estimated based on registered amounts produced, imported and exported submitted to the European Chemicals Agency as a part of REACH registration dossiers. This information is confidential, but SOLUTIONS was allowed to use the numbers for the purpose of EU wide analysis of impacts. Emissions are assumed to reach air (8.5%), water (12%) and soil (3.0%), calculated from loss factors for various use categories. Due to a lack of compound-specific information the general assumptions given above had to be done, however being well aware that this is a source of uncertainty that can be reduced only with more transparency in compound related data.
The losses to the environment are spatially distributed on the basis of so-called locator values. For REACH-registered chemicals and pharmaceuticals SOLUTIONS assumed that a higher standard of living implies (gross domestic product based on purchasing-power-parity, GDP-PPP taken from the World Bank) a higher use of chemicals. At the same time, increased standard of living is also related to higher environmental awareness quantifiable as the share of wastewater collected and treated (Figure 13).
Figure 13: Country-by-country indicators for wastewater management (a) and GDP dependent population weight factor used in spatial distribution of emissions (see attached file)
Based on simulations with the model Simple Treat developed at RIVM, the fate of individual chemicals in wastewater treatment is calculated.
For pesticides, the losses to water, soil and air are spatially distributed according to the agricultural land use considering distribution in time by taking into account spring crops, autumn and perennial crops.
In total emissions have been modeled for 621 pharmaceuticals, 408 plant protection products and 4159 REACH registered chemicals for the entire European Union plus few other countries spanning a period of 5 years (2009 to 2013). As an example, spatial distribution of emissions of the pharmaceutical flukonazol to surface water is given in Figure 14.
Figure 14: Simulated spatial distribution of emissions of fukonazole to surface water (see attached file)
3.3 WP16: Fate and transport modelling
For fate and transport modelling, a dynamic mass balance model called STREAM-EU has been developed. Its description and several relevant applications with a specific focus on the perfluorinated surfactants PFOS and PFOA in the SOLUTIONS case studies have been published [40-42]. STREAM-EU was implemented in the Delft3D-WAQ open source modelling framework was used to calculate contaminant concentrations in a spatially and temporally resolved way in all relevant environmental compartments including surface water, groundwater, snow, soil and sediment. The compartments are considered as well mixed and contain different phases. Partitioning between the phases is modelled using the fugacity concept. Precipitation, dissolution and ionization as well as biodegradation have been implemented in the model. Within the compartment with an atmosphere interface volatilization is included. In order to properly cover particle-bound contamination, the fate and transport model needs information about erosion and sedimentation fluxes which is derived from a separate dynamic mass balance simulation driven by E-Hype schematization and hydrology.
With a focus on the fish consumption pathway for human health risk assessment the fate and transport model was expanded with a module to quantify expected bioaccumulation in fish combining the estimation of rate constants with food-web modelling. Bioaccumulation was modelled for several fish species at different trophic levels. Internal equilibrium concentrations modeling involved also the uptake and elimination rates for ionogenic organic chemicals using the innovative BIONIC model .
In addition to the European scale, mean concentrations of pesticides, pharmaceuticals and REACH chemicals were modeled for the big SOLUTIONS case study Rivers Danube and Rhine, Spanish rivers and Vegea River in Sweden in order to evaluate modeling data with monitoring data that were provided by SOLUTIONS in WPs 19 to 21 or available from external sources. To summarize the results for pesticides, although correlations between predicted and observed concentrations of different compounds were quite dependent on the investigated basin, the overall bias was less than one order of magnitude in 72% of cases and less than two orders of magnitude in 94% of cases (Figure 15).
Figure 15: Histogram of bias for individual pesticides (left) and pharmaceuticals (right) for all investigated cases (see attached file)
For data sets with good temporal coverage a very good fit could be achieved as exemplified for the River Vegea in Figure 16.
Figure 16: Simulated vs. observed concentrations of pesticides for River Vegea (see attached file)
The deviations between simulated and measured concentrations for pharmaceuticals were low for Spanish rivers and River Rhine but higher for the Danube (no data for River Vegea were available). Altogether the bias is less than one order of magnitude in 61% of all cases and less than two orders of magnitude in 88% (Figure 15). All simulations were based on available pharmaceutical sales in Sweden and Great Britain, which obviously only poorly reflected pharmaceutical consumption in the Danube countries. Better data availability will probably improve predictions.
For REACH registered chemicals again the bias is dependent on the river basin under consideration. Deviations occurred particularly for volatile chemicals despite the fact that volatilization from soils and surface waters in included in the model.
3.4 WP17: Substance metabolism and properties modelling
Data gaps with respect to chemical fate and effects of emerging compounds are one of the major obstacles for the evaluation of monitoring data as well as for simulating emissions and fate and transport with models. Thus, SOLUTIONS put major efforts on closing these data gaps using QSAR models (D17.2). For prediction of sorption and bioaccumulation of emerging contaminants novel experimentally-based LSER models were developed (D17.1).
For the large set of chemicals used in modelling as well as for the chemicals detected in the aquatic environment in SOLUTIONS case studies physico-chemical properties including water solubility, partition coefficients and other pure compound molecular properties have been calculated using the model suite developed for and compiled in ChemProp at UFZ have been estimated. Where needed this approach was complemented with the commercial software package ACD/Percepta and EPI Suite models.
The CATALOGIC software suite, developed by LMC, is a platform for models and databases to predict the environmental fate of chemicals including abiotic and biotic degradation, bioaccumulation but also acute ecotoxicity to algae, daphnid and fish for narcotic chemicals. These models were complemented by a set of TIMES models developed by LMC for the prediction of an extensive set of sublethal endpoints relevant for human health as well as partially for effects on aquatic organisms including genotoxicity such as Ames mutagenicity, chromosomal aberrations (both including S) activation), in vivo Comet genotoxicity, in vivo liver clastogenicity, in vivo liver transgenic rodent mutagenicity, in vivo bone marrow micronucleus test, other types of reactive toxicity such as skin and eye irritation and skin sensitization, phototoxicity, aromatase inhibition and three nuclear receptor based endpoints involving AhR, AR and ER. In total 11 large sets of chemicals for different purposes have been modelled feeding the results into many different SOLUTIONS work packages.
3.5 WP18: Human and ecological risk modelling of pollutant mixtures
Estimating ecosystem and human health risks from predicted and measured exposure is an important building block for an integrated modelling framework, which can be used for the prioritization of emerging pollutants and for the assessment of abatement options. In SOLUTIONS we developed a common tiered framework for human and ecological mixture risk assessment (MRA), which has been further extended with the specific aim of increasing the predictive modelling capacity with respect to the ecological effects of emerging compounds, both described in detail in D18.1.
The common and advanced framework for human and ecological mixture risk assessment uses a component-based tiered approach based on the model of concentration addition (CA) as a lower tier approach, complemented with the model of independent action (IA) in higher tier. In Tier 1, regulatory values such as ADI, TDI and EQS (or their equivalents such as PNECs) are used together with modelled or measured data on exposures in order to calculate a Hazard Index (HI), a Point of departure Index (PODI) or related quotients. These indices are conservative approaches that consider and mix all toxicological endpoints and use assessment factors (from 10 to 10,000) to consider uncertainty. In Tier 2 the influence of assessment factors of differing magnitude is removed and taxa-specific PODs are used coming up with risk quotients (RQ). In Tier 3, subgroups of mixture components that affect a common endpoint through a similar mode of action are compiled and hybrid approach using CA for similarly acting compounds within a group and IA as tool for aggregation of the groups. A detailed guidance is given providing the assessment rules main and sub-tiers. All tiers are detailed with workflow schemes based on the same principle for human health and ecosystems.
Figure 17: The principle of driver identification based on their contribution to mixture effects compared to PODIs as thresholds of acceptable exposures. (see attached file)
For driver identification in mixtures existing approaches have been discussed in D18.1 and complemented by an approach sorting the chemicals under consideration in ascending order according to the size of their RQ. PODIs of concern need to be established as the limit of acceptable exposures (typically 0.01 or 0.1). The components of the mixture with cumulative HQs exceeding the PODI are considered as drivers of toxicity (Figure 17).
Human health risk assessment was based on the exposure pathways drinking water and consumption of freshwater fish. In order to answer the question “Is the fish caught from a given freshwater site safe for human consumption water concentrations were converted into expectable concentrations in fish tissues using bioaccumulation modelling based on trophic levels and lipid contents. The approach was demonstrated for the assessment of chronic mixture risks to fish and humans in the River Danube on the basis of JDS3 data. In total four chemicals have been identified as drivers of mixture risks for human fish consumption including three pharmaceuticals and one insecticide.
On the basis of modelled concentrations of 1800 compounds MRA was performed for all case studies (Rivers Danube, Rhine and the Iberian river basins) and the endpoints algal reproduction, immobilization of Daphnia and toxicity to fish deriving endpoint-specific lists of toxicity drivers including 40, 19 and 7 compounds, respectively. Statistical and trait-based approaches together with the alignment of modeled risks with the ecological status have been performed. It was shown that mixture exposure is a significant factor that limits reaching or maintaining good or high ecological status with higher mixture toxic pressure (msPAF) implying higher limitations (Figure 18).
Figure 18: Empirical relationship between mixture toxic pressure (msPAF) and Ecological Status (see attached file)
4. SP4: Cases
SP Cases has been designed to evaluate, demonstrate and mutually validate monitoring tools and models in the large case studies on the Rivers Danube and Rhine as well as on several Spanish rivers. In addition, smaller cases for specific purposes such as the Rivers Holtemme (Germany) and Vegea (Sweden) have been involved. Many of these tasks have been already reported above in SPs 2 and 3 in order to demonstrate the power of the tools and models developed in these sub-projects. Thus, the major focus of the reporting in WP19 to 21 will be on activities that have not been reported elsewhere.
4.1 WP19: Danube river basin case study
A major basis and anchoring point of the Danube river basin case study was the Joint Danube Survey 3 (JDS3) two months before the official start of SOLUTIONS. Several members of the SOLUTIONS consortium participated in JDS3 safeguarding that samples were collected in a way that they could be analyzed and evaluated by SOLUTIONS to support the specific objectives of this project.
In addition to large scale method testing, demonstration and evaluation, the identification of River Basin Specific Pollutants (RBSP) for the Danube was a key objective of the case study. This included the development of a methodology together with the guidance for application as well as the RBSP list itself for introduction into Danube River Basin Management Plans by ICPDR as a stakeholder directly involved into the SOLUTIONS consortium. The methodology and guidance is based on the NORMAN prioritization framework (Figure 19) involving the approaches and tools developed in the SPs on tools and models. Chemical monitoring data measured by SOLUTIONS and additional laboratories in JDS3 samples are the basis of the prioritization complemented by the screening and evaluation of a 12 WWTPs in the Danube river basin as a source related dataset. The prioritization framework is explained in detail in D19.4.
Figure 19: Decision tree for the categorization and prioritization of chemicals (see attached file)
The categorization of measured chemicals according to the decision tree in Figure 19 and a prioritization of those chemicals that have been sufficiently monitored using the extent of exceedance of the lowest PNEC and the spatial frequency of exceedance of the lowest PNEC as criteria to calculate the final ranking scores, SOLUTIONS came up with an interims list of 20 substances that have been presented in the 2015 update of the Danube River Basin Management Plan. Extensive curation of monitoring data has been carried out to exclude outliers. This resulted for example in an exclusion of PAHs from the RBSP list. An updated version of a list of 20 RBSP may be found in D19.4 and has been submitted to ICPDR. This list includes PFOS, isoproturon and some metals as WFD Priority Substances together several pesticides, pharmaceuticals and some industrial chemicals such as bisphenol A.
SOLUTIONS came to the conclusion that there is a need to involve modelling, effect-based monitoring and ecological monitoring into a multiple LoE approach on prioritization (see WP2). Thus, these methods were tested in the case study Danube investigating them for their potential to provide additional candidates for RBSPs that may be considered in upcoming JDS4 and other monitoring activities in the River Danube. This included an in-depth study of the River Danube downstream of the city of Novi Sad as a potential pollution source due to the emission of untreated wastewater into the Danube as well as an emission-based modelling exercise for the whole River Danube using the SOLUTIONS model train as detailed in the report on SP3.
Integrated effect-based and chemical monitoring in the River Danube downstream of Novi Sad with a focus on endocrine disruption and other specific in vitro assays together with a mass balance approach involving default mixture toxicity modelling and an EDA study revealed a list of 14 chemicals driving ER- and AR-mediated effects [24, 29]. These chemicals include natural steroids, phytoestrogens and synthetic steroids used for medication. Due to their very low PNECs the limits of detection of chemical screening are too high to detect them in river water. Thus, using the chemical monitoring-based approach alone, they are overlooked and ignored in RBSP lists. This finding highlights the importance of involving effect-based methods into monitoring, assessment and prioritization.
A prioritization exercise modelling exposure and risks for 1835 chemicals known to be emitted in the Danube basin together with the extent of exceedance/frequency of exceedance scoring revealed a top hundred list of potential candidates (D19.4). This list may be seen as complementary and will be considered when designing the list of compounds for monitoring in JDS4.
4.2 WP20: Assessment of abatement options in the River Rhine catchment
The case study in the River Rhine catchment was designed as a test field for abatement options, the application of new effect-based and chemical methods for evaluation of abatement efficiency and the derivation of emission limit values (ELVs) and provisional drinking water guideline values.
Building on the toolbox provided in WP9, a targeted toolbox for abatement assessment has been established (D20.1). This includes sampling strategies that allow for the calculation of elimination efficiencies and the impact of wastewater to river water quality. Grab sampling typically used in monitoring is compared to time-integrated sampling techniques. Enrichment and sample preparation techniques have been investigated suggesting SPE with multi-layer cartridges as a tool to enrich a broad spectrum of compounds with in situ LVSPE as a major advancement. Care needs to be taken to avoid toxic blanks. To observe the performance of certain abatements chemical analysis and effect-based methods are recommended. Guidance is given on the selection of marker compounds for specific purposes. Polar and ionic chemicals are suggested to be targeted for testing breakthrough in activated carbon filtration, chemicals with low reactivity should be in the focus of efficiency of reactive abatement processes such as ozonation, while bank filtration needs to be tested with persistent and mobile organic compounds (PMOC) with poor removal. Also different sources can be addressed with marker compounds for agricultural runoff and urban wastewater. Effect-based methods representing endpoints with human health concern such as genotoxicity and endocrine disruption as a part of the modular test battery suggested in WP11 should be in the focus of drinking-water-quality related assessments. In upstream-downstream studies at WWTPs in Switzerland integrated effect-based and chemical monitoring has been demonstrated to assess the impact of wastewaters on river water quality [25, 44]. Ecological assessment tools (discussed in WP13) further supported the development of cause-effect relationships using PICT of microbial communities and the SPEcies At Risk (SPEARpesticide) index for the assessment of macroinvertebrate communities. A significant correlation between SPEARpesticides and toxic contamination characterized by msPAF has been detected.
Since WWTPs emitting complex mixtures of chemicals are one of the major sources of deterioration of surface water qualities Emission Limit Values (ELVs) are required and have been provided by SOLUTIONS for a large number of chemicals based on EQS for Priority Substances and RBSPs considering the dilution of the discharged water in the receiving river during dry weather flow conditions.
While ELVs target the regulation of emissions, provisional drinking water guideline values (pGLVs) are required to protect drinking water and thus human health as a major receptor from contamination and adverse effects. While the concept of the Threshold of Toxicological Concern (TTC) is a pragmatic approach using information on chemical structure to sort chemicals in three so-called Cramer classes with a uniform threshold value, SOLUTIONS derived compound-specific pGLVs based on available toxicological information for 142 chemicals . The latter were derived from a set of 686 chemicals detected in water resources in general by selecting those 76 that have been detected in produced drinking water together with 87 substances in raw drinking water or direct sources. For most chemicals SOLUTIONS did not find appreciable human health risk, while for several compounds including vinylchloride, trichlorothene, bromosichloromethane, aniline, phenol, 2-chlorobenzamine, mevinphos, 1,4-dioxane and nitrilotriacetic acid human health risks could not be excluded.
Riverbank filtration (RBF) is considered as a cost-efficient approach to produce high-quality drinking water making use of natural processes. SOLUTIONS investigated this process involving filtration, biodegradation and sorption for improvement of water quality at 10 RBF sites along the River Rhine and its tributaries. For one RBF system with detailed long-term hydrological, hydrogeological and chemical observation data a detailed reactive transport modelling study was varied out to assess the long-term/long-distance behavior of organic compounds. A major uncertainty in estimating degradation is the calculation of degradation rate constants. In SOLUTIONS, these rate constants were calculated with QSAR technology using the CATALOGIC platform described in WP17. For a total of 82 substances concentrations in raw drinking water after RBF could be estimated from river water concentrations suggesting that at the in-depth investigation site of Rodenhuis (The Netherlands) 1,4-dioxane, iopamidol and tolyltriazole may exceed 100 ng/L regularly, diclofenac and dyglyme at least occasionally. Investigations at the Lek River (The Netherlands) indicated that there were 10 compounds that were fully persistent during RBF even after 3.6 years of transit time, five others were only partially removed. Reversed osmosis (RO) is considered as a tool for further purification of riverbank filtrates. SOLUTIONS used effect-based methods to test water quality at a Dutch drinking water treatment plant after RO detecting no positive response up to a relative enrichment of 2000.
In the Swiss part of the Rhine catchment five times lower residence times in RBF are legally required (10 days) compared to EU. Based on 526 targeted compounds no health risk of drinking water was indicated under normal conditions. However, the short residence times result in vulnerability to contamination peaks in case of heavy rain events, during pesticide application periods, accidents etc..
4.3 WP21: Iberian river basins
The Iberian case study involved four river basins including Ebro, Llobregat, Júcar and Guadalquivir was performed in collaboration with the Spanish national project SCARCE and had a specific focus on prioritization of chemicals under water scarcity, which is considered as a major bundle of non-chemical stressors, and thus on the relationship between chemical and non-chemical stressors.
On the basis of about 200 compounds detected, prioritization of chemicals was performed based on TUs for the green algae, Daphnia magna and fish using a ranking according to the frequency of occurrence (sites) of a chemical in rank classes defined as ranges of log TU (D21.1). Highest risks were concluded for six insecticides (chlorfenvinphos, chlorpyriphos, dichlofenthion, ethion, diazinon and carbofuran), the fungicide prochloraz and the herbicide diuron, as well nonylphenol and octylphenol. Sediment assessment at the same river basins involving the equilibrium partitioning approach to estimate corresponding water concentrations prioritized a similar selection however including the insecticide malathion and the antibiotic ciprofloxacin. In fish tissues 135 compounds were analysed with highest frequency of detection and highest concentration for several perfluorinated compounds, some pesticides and polychlorinated flame retardants.
The study on the relationship between chemical and non-chemical stressors used biofilms and invertebrate communities as representative receptors and used TUs as an indicator for toxic stress. Using an assessment approach published at the beginning of SOLUTIONS , dependent of the basis under consideration up top 74 % of the sites were under acute toxic risk driven mainly by pesticides and metals, while for chronic risks pharmaceuticals such as the antidepressant sertraline played an important role. Toxic stress could be confirmed by the correlation of the disappearance of sensitive macroinvertebrate species (SPEAR) with TUs. However, the results were suffering from a limited gradient since reference conditions with low concentrations and well established macro invertebrate communities were lacking in all investigated river basins.
In close interaction with SP3 (WP16), the SOLUTIONS model train was applied to more than 200 organic pollutants monitored in the Iberian river basins. Grouping the chemicals according to pesticides, pharmaceuticals and REACH compounds similar to other basins most substance average concentrations could be predicted within one or two orders of magnitude.
1. Brack, W., et al., The SOLUTIONS project: Challenges and responses for present and future emerging pollutants in land and water resources management. Science of The Total Environment, 2015. 503–504(0): p. 22-31.
2. Munthe, J., et al., An expanded conceptual framework for solution-focused management of chemical pollution in European waters. Environmental Sciences Europe, 2017. 29(1): p. 13.
3. van Wezel, A.P. et al., Mitigation options for chemicals of emerging concern in surface waters; operationalising solutions-focused risk assessment. Environmental Science: Water Research & Technology, 2017. 3(3): p. 403-414.
4. Coppens, L.J.C. et al., Towards spatially smart abatement of human pharmaceuticals in surface waters: Defining impact of sewage treatment plants on susceptible functions. Water Research, 2015. 81: p. 356-365.
5. Altenburger, R., et al., Future water quality monitoring - Adapting tools to deal with mixtures of pollutants in water resource management. Science of the Total Environment, 2015. 512: p. 540-551.
6. Schulze, T., et al., Assessment of a novel device for onsite integrative large-volume solid phase extraction of water samples to enable a comprehensive chemical and effect-based analysis. Science of the Total Environment, 2017. 581: p. 350-358.
7. Neale, P.A. et al., Solid-phase extraction as sample preparation of water samples for cell-based and other in vitro bioassays. Environmental Science: Processes & Impacts, 2018.
8. Čelić, M., et al., Chapter 15 - Environmental analysis: Emerging pollutants, in Liquid Chromatography (Second Edition), S. Fanali, et al., Editors. 2017, Elsevier. p. 451-477.
9. Mendoza, A., et al., Pharmaceuticals and iodinated contrast media in a hospital wastewater: A case study to analyse their presence and characterise their environmental risk and hazard. Environmental Research, 2015. 140: p. 225-241.
10. Catalá, M., et al., Elimination of drugs of abuse and their toxicity from natural waters by photo-Fenton treatment. Science of The Total Environment, 2015. 520: p. 198-205.
11. Mendoza, A., et al., Drugs of abuse and benzodiazepines in the Madrid Region (Central Spain): Seasonal variation in river waters, occurrence in tap water and potential environmental and human risk. Environment International, 2014. 70: p. 76-87.
12. Negreira, N., M.L. de Alda, and D. Barceló, Cytostatic drugs and metabolites in municipal and hospital wastewaters in Spain: Filtration, occurrence, and environmental risk. Science of The Total Environment, 2014. 497–498: p. 68-77.
13. Hu, M., et al., Optimization of LC-Orbitrap-HRMS acquisition and MZmine 2 data processing for nontarget screening of environmental samples using design of experiments. Analytical and Bioanalytical Chemistry, 2016. 408(28): p. 7905-7915.
14. Schymanski, E., et al., Non-target screening with high resolution mass spectrometry: Critical review using a collaborative trial on water analysis. Anal Bioanal Chem., 2015. in review.
15. Hollender, J., et al., Nontarget Screening with High Resolution Mass Spectrometry in the Environment: Ready to Go? Environmental Science & Technology, 2017. 51(20): p. 11505-11512.
16. Schollée, J.E. et al., Prioritizing Unknown Transformation Products from Biologically-Treated Wastewater Using High-Resolution Mass Spectrometry, Multivariate Statistics, and Metabolic Logic. Analytical Chemistry, 2015. 87(24): p. 12121-12129.
17. Schollee, J.E. et al., Similarity of High-Resolution Tandem Mass Spectrometry Spectra of Structurally Related Micropollutants and Transformation Products. Journal of the American Society for Mass Spectrometry, 2017. 28(12): p. 2692-2704.
18. Hu, M., et al., Performance of combined fragmentation and retention prediction for the identification of organic micropollutants by LC-HRMS. Analytical and Bioanalytical Chemistry, 2018.
19. Ruttkies, C., et al., MetFrag relaunched: incorporating strategies beyond in silico fragmentation. Journal of Cheminformatics, 2016. 8.
20. Schymanski, E.L. et al., Critical Assessment of Small Molecule Identification 2016: automated methods. Journal of Cheminformatics, 2017. 9(1): p. 22.
21. Schymanski, E.L. et al., Identifying Small Molecules via High Resolution Mass Spectrometry: Communicating Confidence. Environmental Science & Technology, 2014. 48(4): p. 2097-2098.
22. Muz, M., et al., Nontargeted detection and identification of (aromatic) amines in environmental samples based on diagnostic derivatization and LC-high resolution mass spectrometry. Chemosphere, 2017. 166: p. 300-310.
23. Brack, W., et al., Effect-directed analysis supporting monitoring of aquatic environments - An in-depth overview. Science of the Total Environment, 2016. 544: p. 1073-1118.
24. König, M., et al., Impact of untreated wastewater on a major European river evaluated with a combination of in vitro bioassays and chemical analysis. Environmental Pollution, 2017. 220, Part B: p. 1220-1230.
25. Neale, P.A. et al., Integrating chemical analysis and bioanalysis to evaluate the contribution of wastewater effluent on the micropollutant burden in small streams. Science of the Total Environment, 2017. 576: p. 785-795.
26. Hug, C., et al., Linking mutagenic activity to micropollutant concentrations in wastewater samples by partial least square regression and subsequent identification of variables. Chemosphere, 2015. 138: p. 176-182.
27. Muz, M., et al., Identification of Mutagenic Aromatic Amines in River Samples with Industrial Wastewater Impact. Environmental Science & Technology, 2017. 51(8): p. 4681-4688.
28. Muschket, M., et al., Identification of Unknown Antiandrogenic Compounds in Surface Waters by Effect-Directed Analysis (EDA) Using a Parallel Fractionation Approach. Environmental Science & Technology, 2018. 52(1): p. 288-297.
29. Hashmi, M.A.K. et al., Effect-directed analysis (EDA) of Danube River water sample receiving untreated municipal wastewater from Novi Sad, Serbia. Science of The Total Environment, 2018. 624: p. 1072-1081.
30. Muz, M., et al., Mutagenicity in Surface Waters: Synergistic Effects of Carboline Alkaloids and Aromatic Amines. Environmental Science & Technology, 2017. 51(3): p. 1830-1839.
31. Busch, W., et al., Micropollutants in European rivers: A mode of action survey to support the development of effect-based tools for water monitoring. Environ. Toxicol. Chem., 2016. DOI:10.1002/etc.3460.
32. Neale, P.A. et al., Development of a bioanalytical test battery for water quality monitoring: Fingerprinting identified micropollutants and their Contribution to effects in surface water. Water Research, 2017. 123: p. 734-750.
33. Di Paolo, C., et al., Bioassay battery interlaboratory investigation of emerging contaminants in spiked water extracts – Towards the implementation of bioanalytical monitoring tools in water quality assessment and monitoring. Water Research, 2016. 104: p. 473-484.
34. Altenburger, R., et al., Mixture effects in samples of multiple contaminants – An inter-laboratory study with manifold bioassays. Environment International, 2018. 114: p. 95-106.
35. Deutschmann, B., et al., Longitudinal profile of the genotoxic potential of the River Danube on erythrocytes of wild common bleak (Alburnus alburnus) assessed using the comet and micronucleus assay. Science of The Total Environment, 2016. dx.doi.org/1016/j.scitotenv.2016.07.175.
36. Tlili, A., et al., Micropollutant-induced tolerance of in situ periphyton: Establishing causality in wastewater-impacted streams. Water Research, 2017. 111: p. 185-194.
37. Beckers, L.-M. et al., Characterization and risk assessment of seasonal and weather dynamics in organic pollutant mixtures from discharge of a separate sewer system. Water Research, 2018.
38. Inostroza, P.A. et al., Anthropogenic stressors shape genetic structure: Insights from a model freshwater population along a land use gradient. Environmental Science & Technology, 2016. DOI:10.1021/acs.est.6b04629.
39. Inostroza, P.A. et al., Chemical activity and distribution of emerging pollutants: Insights from a multi-compartment analysis of a freshwater system. Environmental Pollution, 2017. 231: p. 339-347.
40. Lindim, C., I.T. Cousins, and J. vanGils, Estimating emissions of PFOS and PFOA to the Danube River catchment and evaluating them using a catchment-scale chemical transport and fate model. Environmental Pollution, 2015. 207: p. 97-106.
41. Lindim, C., J. van Gils, and I.T. Cousins, A large-scale model for simulating the fate and transport of organic contaminants in river basins. Chemosphere, 2016. 144: p. 803-810.
42. Lindim, C., J. van Gils, and I.T. Cousins, Europe-wide estuarine export and surface water concentrations of PFOS and PFOA. Water Research, 2016. 103: p. 124-132.
43. Chen, Y., et al., Which Molecular Features Affect the Intrinsic Hepatic Clearance Rate of Ionizable Organic Chemicals in Fish? Environmental Science & Technology, 2016. 50(23): p. 12722-12731.
44. Munz, N.A. et al., Pesticides drive risk of micropollutants in wastewater-impacted streams during low flow conditions. Water Research, 2017. 110: p. 366-377.
45. Baken, K.A. et al., Toxicological risk assessment and prioritization of drinking water relevant contaminants of emerging concern. Environment International, 2018. 118: p. 293-303.
46. Malaj, E., et al., Organic chemicals jeopardise freshwater ecosystems health on the continental scale. Proceedings of the National Academy of Science, 2014. 111(26): p. 9549-9554.
List of official Deliverables public available via the SOLUTIONS website (from February 2019)
Del. No. Title
D1.1 Conceptual framework as basis for implementation in RiBaTox and the toxicant knowledge base on the basis of specified stakeholder problems and requirements
D1.2 Integrated publications on novel solutions for risks of mixture of emerging pollutants in water resources
D2.1 Advanced methodological framework for the identification and prioritisation of contaminants and contaminant mixtures
D3.1 Technical and non-technical abatement options implemented in RiBaTox including rules for placement of abatement options, removal efficiencies and prioritisation
D3.2 Example cases for the application of the Chemical Footprint and the (Planetary) Boundaries concept to abatement strategies
D4.1 RiBaTox fully documented on-line ‘final’ version
D5.1 Integrated Data Portal for SOLUTIONS (IDPS)
D5.2 Web-based knowledge base integrated with IPCheM and RiBaTox
D6.1 Recommendations: Pollution of tomorrow: options to act on future risk and final report
D8.1 Functional interactive SOLUTIONS web-side, stakeholder communication platform and intranet
D8.2 Final products (RiBaTox, models, knowledge base and guidelines) accessible via the SOLUTIONS web-site
D8.3 Final Report on Communication, dissemination and training
D9.1 Guidance document and decision tree for use of chemical, bioanalytical and ecological tools in RBSP identification, impact assessment and establishment of cause-effect relationships
D10.1 Guidelines for target and non-target analysis of emerging contaminants in water and biota
D11.1 SOP for mutually validated virtual and higher tier EDA of surface waters and fish tissue ready for translation into guidelines
D12.1 Improved bioassay solutions for environmental monitoring based on adverse outcome pathways
D12.2 Feasibility assessment of extract-bioassay approaches for environmental monitoring
D13.1 Diagnostic toolbox for ecological effects of pollutant mixtures, including bio-tests, trait-based database and detection tool and WoE studies at hot-spot sites
D14.1 Modelling framework and model-based assessment for substance screening
D14.2 Europe wide modelling and simulations of emerging pollutants risk including think tank scenarios
D15.1 Peer reviewed paper on the entire process of estimating emissions of chemical substances
D16.1 Evaluation of the basin-wide river catchment and soil-to-groundwater-to-surface water transport model including sensitivity and uncertainty analyses
D17.1 Novel experimentally-based LSER models for sorption and bioaccumulation of emerging pollutants
D17.2 Predictions of transformation products, physico-chemical properties, fate and toxicity of candidate compounds from chemical screening, EDA and emission modelling
D18.1 Common assessment framework for HRA and ERA higher tier assessments including fish and drinking water and multi-species ERA via SSD, population-level ERA via IBM and food web vulnerability ERA
D19.4 Guidance for identification of RBSPs and list of Danube RBSP including quantification of their ecological impact and modeling-based exposure and risk predictions validated with case-study data
D20.1 Targeted tool-box for the assessment of abatement options, derivation of ELVs and pGLVs for drinking water and assessment of natural attenuation during river bank filtration
D21.1 Guidance for identification of RBSPs in Mediterranean river basins and list of RBSP including quantification of their ecological impact and modeling-based exposure and risk predictions validated
D23.1 Risk Management Contingency Plan
“Water is not a commercial product like any other but, rather, a heritage which must be protected, defended and treated as such”. Based on this strong opinion of the European Commission, the Water Framework Directive (WFD) was developed and implemented in the European Union striving for a good water quality in rivers and lakes on a continental scale. This is a unique and ambitious goal and the project SOLUTIONS has been developed to support the achievement of this goal and to provide solutions for one of the major obstacles in the implementation of an effective WFDComplex mixtures of emerging pollutants are known to occur in European water bodies, and they may cause harm to ecosystems and human health, but they are not addressed accordingly under WFD monitoring, assessment, prioritization, and management. Thus, in line with the FP7 call ENV.2013.6.2-2 on “toxicants, environmental pollutants and land and water resources management”, with the EU strategy for a non-toxic environment, the OECD Council Recommendation on Water and the Sustainable Development Goals of the UN, SOLUTIONS developed a comprehensive, consistent, integrated, solution-oriented and enduser-friendly system of tools, models and a knowledge base in order to support decision-makers and practitioners in achieving the goals of European water quality management. This has been done in a close and intensive dialogue with the SOLUTIONS Stakeholder Board (SB) covering over five years of project duration with at least two very well attended meetings per year in order to make sure that all scientific results and developments can directly impact on discussions and decisions on European, river basin and national levels by the competent authorities and bodies. The SOLUTIONS SB involved among others the European Commission (DG Environment), the European Environment Agency (EEA), national and regional environmental, water and chemical agencies (e.g. the Catalan Water Agency, the German UBA and the Swedish KEMI), the international commissions for the protection of the Rivers Rhine and Danube (ICPR and ICPDR), the water industry represented by Veolia and EUREAU, the European Federation of National Associations of Water Services, the NORMAN network as a major science-policy interface in the field of emerging contaminants. For the exchange of concepts and approaches beyond Europe US-EPA and Environment Canada were involved. Other relevant stakeholders such as the European Chemical Agency ECHA, the European Food Safety Authority (EFSA), chemical industry and environmental NGOs were involved in SOLUTIONS workshops and conferences.
SOLUTIONS was designed to have a strategic impact by addressing major challenges of WFD as follows:
• Evidence based development of environmental and water policies
In a comprehensive assessment of the WFD in concert with six other environmental occurrence-based regulatory frameworks covering air, water and land as well as thirteen emission-based frameworks on chemical pollution compiled in D7.1 SOLUTIONS provided policy recommendations for realising synergies between these frameworks. The latter have been reviewed for their coverage of regulated chemicals and their life cycle stages from production via trade, use, and to their end of the live cycle. Regulatory mechanisms have been analysed and regulatory gaps identified. On this basis, recommendations have been developed and intensively discussed with SOLUTIONS stakeholders in the SB and beyond. Harmonisation of objectives among regulatory frameworks, ensuring to coherently cover all life stages and environmental media, the exchange of information, considering mixtures and the need for an international perspective with regard to the global market have been particularly highlighted. The recommendations are compiled in a Policy Brief targeted to relevant authorities but also disseminated to a broader group of stakeholders and even the general public.
For the review process of the WFD, a well perceived and intensively discussed contribution has been published as a peer-reviewed paper. It provides ten recommendations on improving the success of WFD implementation, involving advancements in monitoring and strengthening of comprehensive prioritization, fostering consistent assessment and supporting solution-oriented assessment and management . The recommendations have been developed and disseminated after broad discussion with the SOLUTIONS stakeholders and within the NORMAN network with more than 70 members including scientific institutions, industry and agencies from 20 countries in order to maximize the impact . A central recommendation concerning the integration of effect-based methods to diagnose and monitor water quality, has been directly taken up by WG Chemicals under the WFD Common Implementation Strategy (CIS) process establishing a working group on effect-based methods (EBMs) for the development of guidance for the new tool. SOLUTIONS is directly involved in this group. The development and integration of EBMs into WFD monitoring has been appreciated by the European Water Directors, thus direct impact on WFD review and further advancement may be expected.
• Improved knowledge and tools to assess emerging pollutants and pollutant mixtures
Knowledge and data gaps but also data scattering over a myriad of scientific publications and a lack of data accessibility are major obstacles for the assessment of emerging pollutants and pollutant mixtures. At the same time, monitoring and assessment tools, predictive models and other relevant services are hardly available in a structure and format that is useful for consideration and application by decision makers and practitioners. Thus, SOLUTIONS put a major focus on and created impact through the development of an interlinked, well-structured and open access web-based structure providing data, knowledge and guidance developed and compiled by SOLUTIONS in a user-friendly web-based format. Major elements of this system include (1) the Integrated Data Portal for SOLUTIONS (IDPS) as a door to the full universe of SOLUTIONS data and with a direct link to IPCheM operated by the European Commission, (2) the online web-based service RiBaTox, (3) a database on abatement options, (4) the SOLUTIONS model train for predictive modelling of chemicals and risks from emissions and (5) a comprehensive guidance on the use of solution-oriented monitoring tools.
IDPS is a modular system on chemicals including modules on environmental monitoring data, (eco)toxicity, structures and properties, legislation and emission and abatement options with user-friendly search and mapping functions that allows rapid retrieval of existing knowledge on a large range of environmental contaminants. RiBaTox is based on the SOLUTIONS conceptual framework that represents a reduced DPSIR approach providing the user with four entry points including societal developments as drivers (D), chemicals as the pressure (P) considered in SOLUTIONS, environmental observations combining state (S) and impact (I), and abatement options as a response. RiBaTox may be seen as the web-based operationalization of this framework providing a condensed and digested compilation of SOLUTIONS approaches, models and tools in a well-structured way fit for purpose of directing endusers with their questions to informative fact sheets that help them select appropriate methods to find solutions to their problems. In order to optimize the tool with respect to applicability and user-friendliness and thus to maximize its potential impact, RiBaTox has been developed under the continuous evaluation by stakeholders. IDPS, RiBaTox but also the database on abatement options, the model train and the guidance on tools are freely accessible via the SOLUTIONS website but also directly linked with each other.
• New knowledge enabling the design of control measures and abatement options, and the assessment of their effectiveness in meeting the environmental objectives of the WFD
Solutions-oriented approaches dealing with complex mixtures of environmental contaminants in order to actually inspire River Basin Management Plans were the key in SOLUTIONS. Thus, abatement options are considered already at early stages of assessment involving monitoring and modeling tools. In this context the SOLUTIONS abatement database is a milestone in the selection and implementation of most efficient abatement considering the regulation of chemicals as well as their whole life cycle from production via usage down to end-of-pipe technical solutions such as the upgrade of WWTPs. The combination of the abatement database with modelling and the consideration of specific protection goals such as protecting drinking water production or the integrity of Natura 2000 areas were demonstrated to be a powerful tool for prioritization of abatement measures to be used by water managers.
Derived from the concept of planetary boundaries chemical footprints were elaborated in SOLUTIONS as a tool to quantify and prioritize the impact of a specific pollution source, a region, and also management measures. Chemical footprints are based on an easily understandable principle as they characterize and prioritize pollution by the ratio of the amount of water that is required vs. available to dilute this pollution to a level at which there are no (unacceptable) effects. This, may be seen as a local boundary. In collaboration with SOLUTIONS stakeholders this approach based on emission, fate and transport modelling has been demonstrated in the River Rhine basin. The basic principles will be digested for stakeholders in a specific policy brief.
• Identification of new substances with emissions which might require regulation because of the risk posed to or via the aquatic environment
Awareness is increasing that current prioritization procedures have a significant bias towards well-known data-rich chemicals that are regularly monitored in EU Member States, while there is a big chance that less-investigated and –monitored or even unknown potentially hazardous compounds as well as mixture risks are overlooked. Prioritization and assessment within the WFD are often hampered by substantial data gaps on exposure as well as effects that cause a failure of these compounds to meet the criteria for prioritization while no procedures are required and established to prioritize and fill the relevant data gaps. This situation leads to rewarding uncertainty with the assessment of low risks, which is in strong contradiction to the approach used for chemical risk assessment. Here uncertainty is penalised with enlarged assessment factors providing incentives to fill the data gaps. To this end, SOLUTIONS suggested to advance prioritization on the basis of the NORMAN prioritization scheme categorizing chemicals according to the required action and including addressing of specific data gaps. SOLUTIONS exposure and risk modelling has been shown to be a very helpful approach to tentatively fill data gaps in WFD-realted assessment and prioritization by providing conservative estimates, thus generating incentives to validate or replace these values by more realistic measured ones. At the same time, SOLUTIONS modelling helps to prioritize data gaps on compound/site -related risks, and it also helps to identify those chemicals which are very unlikely to pose a risk even if uncertainty is considered in a conservative way.
SOLUTIONS put major efforts in improving current prioritization of chemicals involving a four-lines-of-evidence approach considering (1) chemical monitoring and component-based risk assessment, (2) exposure and risk modelling of compounds produced and used in Europe, (3) effect-based monitoring findings and the compounds identified as drivers of effects and finally (4) ecological monitoring outcomes and relating deviations in structure and function of ecosystems from the reference status to drivers of these deviations. These approaches have been discussed with a broad panel of stakeholders in three well attended workshops and are compiled and digested in a Policy Brief use by policy makers and technical experts in the European Commission, environmental, water and chemical agencies, international river basin commissions but also industry and NGOs. SOLUTIONS prioritization of chemicals in the River Danube based on JDS3 data provided a list of RBSPs, which were directly adopted into the according River Basin Management Plan by ICPDR.
• Evidence-based review of the list of priority substances under the WFD
In all SOLUTIONS case studies there was strong evidence that compounds others than the WFD Priority Substances (PS) play a major role for ecosystems and human health risks. These chemicals may be used at a large scale or be more specific for a river stretch or catchment. Although in SOLUTIONS case studies a substantial set of non-priority substances with the potential to cause harm to aquatic organisms and humans at existing concentrations has been identified, a simple extension of the list of seems to be no sustainable solution due to the variability of pollution as well as to the tendency to replace Priority Substances on the market with (often several and similarly problematic) chemicals without a mechanism to avoid regrettable substitution. In exemplary cases, SOLUTIONS could show that even if the predominating chemicals may be quite variable in space  and time , the distribution of toxicity profiles may be more robust and independent of substituted chemicals. Based on this experience we strongly argue to include effect-based monitoring and corresponding trigger values into prioritization. These suggestions have been discussed with our stakeholders on several workshops and provided as policy briefs and scientific papers  as basis for decision making.
• The development of innovative identification and detection tools
A more comprehensive monitoring and assessment of chemical mixtures that might pose a risk to ecosystems and human health but also for success control of management measures strongly relies on the availability of appropriate chemical and effect-based monitoring tools as well as a consistent concept for their application. SOLUTIONS put major efforts on the development of such tools ranging from innovative but routine-application oriented sampling procedures via more sensitive target analysis of chemicals with insufficient limit of detection for the monitoring of chemicals with very low effect concentrations, target, suspect and non-target screening for detecting a much larger fraction of contaminants and effect-based methods for monitoring of groups of chemicals with similar effects up to community-based tools such as pollution induced community tolerance. All these tools are embedded in a conclusive strategy that has been intensively discussed with stakeholders and with guidance that is available in different formats in order to provide different stakeholders with tailor-made pathways to perceive this information and utilize the novel tools. These pathways include (1) the compilation in RiBaTox in informative but concise factsheets organized in a tree structure and accessible following stakeholder questions, (2) extensive guidance to use the toolbox in a publicly available deliverable, (3) several scientific publications explaining the scientific background of concepts and tools, and demonstrating the application of the tools in case studies, (4) in policy briefs digesting the toolbox to recommendations for application, (5) in brief overview together with a comprehensive listing of scientific papers on the website, (6) in many stakeholder oriented workshops and scientific conferences and (7) in demonstration studies together with the stakeholders showing them the advantages of the new tools to solve their problems, such as assessing the impact of WWTP upgrades on water quality or for preparing monitoring schemes for River Basin Management Plans.
The impact of the SOLUTIONS monitoring strategy and tools may be already seen in many follow up studies on different scales where they are involved and further developed for specific requirements. Examples include a pilot project for the establishment of regulatory monitoring of small streams in Germany under the National Action Plan for Sustainable Use of Pesticides, and the Joint Danube Survey 4 which will take place in 2019. Both initiatives involve SOLUTIONS sampling technology, effect-based and chemical monitoring together with experts and experience provided from the SOLUTIONS consortium.
• Increase of European competitiveness and market opportunities by innovative SMEs
SOLUTIONS involved nine innovative SMEs and one big enterprise and was very successful in developing market opportunities for their innovative approaches and tools. The SME EI played a key role in SOLUTIONS as head of the SP cases and as organizer of JDS3 as an important pillar of SOLUTIONS. EI could demonstrate their excellent skills in scientific and logistic organization and evaluation of large sampling campaigns and related databases to the full range of Danube countries and was nominated also for the follow up survey JDS4, which will take place in 2019. The SME MAXX developed several versions of a large-volume solid phase extraction (LVSPE) device for in situ application. This device has been applied in different case studies (rivers Danube and Rhine) as well as additional field studies to be a very robust fit-for-purpose device for collecting extracts of sufficient quantity and with sufficient quality (free of toxicity blanks, excellent recovery of chemicals and effects) avoiding logistic challenges of transporting large volumes of water to the lab. The device is now available in different versions for 100 or 1000 L water enrichment, for event-based sampling, sampling with high temporal resolution and as a very mobile backpack version. The new devices have been demonstrated among others for European scale WWTP effluent sampling and sampling campaigns in China and Kenya. Recently, MAXX served a 500.000 Euro order by the German Environment Agency on 60 event-based LVSPE sampling devices that have been installed all over Germany to monitor small streams. The device will be also used in JDS4 and there is a good chance that this instrument will develop towards a standard sampling procedure for integrated effect-based and chemical monitoring in Europe and beyond. The SME Dynex developed in SOLUTIONS a High Performance Counter Current Chromatography (HPCCC) processor as a high performance separation device for the enrichment of organic micro-pollutants from river water and for analytical purposes. These developments led to a new patent while the new device will be offered as an innovative, commercially available processor specifically for pharmaceutical companies to clean up their production process waters. The SME WatchFrog developed and applied highly innovative in vivo effect-based methods and faces a great enhancement of market opportunities for the measurement of biological activities particularly for industrial chemicals. They presented their tools at multiple conferences and trade shows opening new markets for the tools developed and successfully demonstrated in SOLUTIONS. Also the SME Synchem synthesizing new chemical standards for environmental monitoring strongly enhanced their product portfolio with chemicals that were shown to be of environmental and toxicological relevance but have not been commercially available so far. The SME KOCMOC designed the excellent SOLUTIONS website (inter- and intranet) and thus provided an outstanding example of presenting a large scientific project to a diverse audience and structuring internal as well as stakeholder communication. This opens new market opportunities in the field of web-based science communication. In a similar way this holds also for the SME HAM that facilitated stakeholder communication in SOLUTIONS in a focused manner unfamiliar to science-stakeholder interactions.
Main dissemination activities
SOLUTIONS not only pursued a very strong focus on dissemination of project results but involved a large number of stakeholders into the development of these results from the very beginning in order to safeguard that the products are useful and will be actually applied by the anticipated users. In addition a large number of targeted media have been used to disseminate SOLUTIONS to the scientific community as well as the broad public. Overall, dissemination has been based on three main pillars:
1) Structured dialogue with a broad range of stakeholders
2) An attractive website as well as user-friendly products accessible via this website
3) Targeted dissemination of results to stakeholders, scientific community and the broad public
In the following, these activities will be explained in more detail.
1) Structured dialogue with a broad range of stakeholders
SOLUTIONS aimed to deliver an advanced conceptual framework for environmental and water policies that obviously could not be achieved by scientific work alone. Rather, science needed to be complemented by the experience and expectations of stakeholders who will later on make use of the projects results.
Therefore, a highly competent SOLUTIONS Stakeholder Board was set up at the coordination level of the project. It involved central authorities and main users of results at European and at river basin level, experts from international technical authorities, thus assembling a group of highly competent external stakeholders representing a broad range of relevant experience. On the working level, SOLUTIONS Work Packages and Case Studies included a number of elaborate formats for stakeholder interactions as described below. Regardless of the specific format, stakeholder interactions were designed to follow basic principles, in particular
➢ representation of all important issues
➢ comprehensive information
➢ frank discussions
➢ responsiveness by SOLUTIONS to stakeholder contributions and questions
SOLUTIONS Stakeholder Board consisted of three member groups
A – external stakeholders (external)
B – partners of SOLUTIONS who concurrently represented external stakeholders (double-role)
C – members of SOLUTIONS Coordination Committee and leaders of strategic work packages (SOL)
The double role of group B was due to the high ambitions and broad conception of SOLUTIONS. Since the project aimed for integration of all relevant knowledge regarding innovative tools, models and methods to support environmental and water quality, it had to include important institutions regarding technical and political aspects as partners in SOLUTIONS work process. At the same time those partners represented important societal stakes with respect to the projects issues.
Even though the role of these board members cannot be viewed as pure stakeholders, they clearly and frequently expressed stakeholder interests in the Boards discussions.
The following organizations participated with regular representatives in group A external stakeholders (in alphabetic order): Catalan Water Agency (ACA); Environment Canada; European Commission, DG Environment; European Environment Agency (EEA); European Federation of National Association of Water and Waste Water Services (EUREAU); German Environment Agency (UBA); International Commission for the Protection of the Rhine (ICPR); Italian National Institute for Environmental Protection and Research – ISPRA; Oekotoxzentrum, Swiss Centre for Applied Ecotoxicology; Swedish Chemical Agency (KEMI); US-Environment Protection Agency (EPA); Veolia Environment.
In group B – external stakeholders and at the same time partners of SOLUTIONS, the following organizations were represented: International Commission for the Protection of the River Danube (ICPDR); Network of Reference Laboratories for Monitoring of Emerging Environmental Pollutants (NORMAN); European Commission, Joint Research Centre (JRC).
Several more stakeholders contributed to single meetings resp. special issues of the Stakeholder Board (alphabetical order): Arctic Monitoring and Assessment Program (AMAP); Association of Water Companies in Slovakia; International Associations of Water Works in the Danube Catchment Area (IAWD); Ministry of the Environment, Japan.
SOLUTIONS requested also European Chemical Industry Council (CEFIC), European Food Safety Agency EFSA and European Chemicals Agency (ECHA) as member of Stakeholder Board without positive response. However, EFSA and ECHA participated in SOLUTIONS workshops on prioritization of chemicals in European waters. Environmental NGOs such as ChemTrust and Greenpeace as well as chemical industry became involved into the discussions in the later stage of the project.
The Stakeholder Board followed a set of basic procedures:
Gathering stakeholders expectations: Already at SOLUTIONS Kick Off in October 2013, main stakeholders took part and presented their expectations to the project. Then, concurrent with the buildup of SOLUTIONS work process in the first project months, in December 2013 a questionnaire was circulated to the external members of the Stakeholder Board (SB) to specify stakeholders problems and requirements. Resulting issues were discussed at the first regular Board meeting and the members agreed on proceedings how to integrate them in the project.
Periodic facilitated meetings with timely announcements: Board meetings took place twice a year, one during the General Assemblies in late autumn, and a second one subsequent to SETAC conferences in spring. All SB meetings and continuous stakeholder communications were facilitated by SOLUTIONS partner Hammerbacher (HAM) who brought in comprehensive experience in stakeholder interactions. In addition to the discussion of the projects work progress and results as presented by SOLUTIONS, external stakeholders presented and discussed matters of their own interest.
Online platform for stakeholders for archive and selected information: A password protected online platform for external stakeholders supported the Board members. It served as always accessible archive for basic documents, minutes and presentations of the Board and also for documents provided by external Board members. The platform compiled selected scientific publications on SOLUTIONS results with special relevance for external stakeholders. It also gave them privileged access to project deliverables - official deliverables as well as selected internal deliverables. Furthermore, the Stakeholder Forum allowed for online discussions.
SOLUTIONS designed General Assemblies open for stakeholders: Therefore, the Board meetings in combination with General Assemblies turned out to be especially attractive for stakeholders because of the more comprehensive information and contact opportunities. SP external stakeholder members took active roles in SOLUTIONS Kick-Off, in General Assemblies and in the concluding discussions of the final conference. According to their individual interests, they participated in a number of discussion rounds and workshops during the General Assemblies.
Stakeholder participation in outcome discussions: The intensity of interactions between SOLUTIONS and its stakeholders are also highlighted by several cases of early stakeholder inclusion in the drafting of main documents. This included the Paper 'Potential synergies between distinctive regulatory frameworks' (Resulting in a report on chemical policies and regulations), the paper "Towards the review of the European Union Water Framework management of chemical contamination in European surface water resources" together with NORMAN, and the Guidance Document for Tools (D9.1).
Moreover, SOLUTIONS Work Packages performed specific stakeholder formats, related to their scientific tasks. WP 1 organised (1) online discussion on the draft paper 'Potential synergies between distinctive regulatory frameworks', (2) several informal meetings for discussion of interim results regarding WP1 research on policies and tools, (3) presentations and discussions of potential applications and of future harmonisation of chemicals legislations, with representatives of the Swedish National Agencies for Environment, for Water, for Chemicals of the Swedish Ministry of Environment, (3) presentation and discussion of potential contributions to global science-policy dialogue, with representatives of SAICM secretariat, in 2017. WP2 organised three workshops on prioritisation methodologies with broad stakeholder involvement. WP4 organized eleven WP meetings on RiBaTox with stakeholder interaction at GAs, three RiBaTox-surveys and a workshop with water managers, co-hosted together with SB-member Veolia, June 2018. WP6 organised a think tank 'Pollution of tomorrow and options to act' and three workshops on future pollutants and received valuable advice and comments regarding the use of patent database and the use of the SPIN database. WP9 organised a specific online stakeholder discussion on the draft paper 'Guidance Document for Tools'. WP14 organised intensive presentations and discussions with various Dutch stakeholders on integrated models and contributed to the meeting of EU WG Chemicals – December 2016, related to Data Request from research project SOLUTIONS and participated in three ICPDR WG meetings on Pressures and Measures. WP19 demonstrated SOLUTIONS results in nine regional events with local, regional and state officials, NGOs, research institutions and the public at locations in Germany, Austria, Slovakia, Hungary, Croatia, Serbia, Bulgaria, Ukraine and Romania. Each event included a press conference. A specific website www.danubesurvey.org and numerous leaflets and fact sheets in different languages with information about the JDS3 survey were released.
2) Attractive website as well as user-friendly products accessible via this website
The SOLUTIONS website https://www.solutions-project.eu/ has been designed as a major entrance portal to the project, its results and the partners involved for the scientific community, for stakeholders and for the general public. The website has been designed in a highly attractive and well-structured way in close collaboration of the SME KOCMOC with the UFZ coordination team. Already on the front page, a lot of background information is available together with recent videos explaining the outcome and informing on the final conference. Via self-explanatory links with few klicks the user can gain extensive information on the project, the consortium, results and products and important collaborations. Under “Results & Products” the outcome of the project is available in the format of easily understandable short texts on results, summaries of the major products with direct links to the respective models and databases, a full set of publications and the deliverables. The major products such as RiBaTox (D4.1) and the Knowledge Base (D5.1) are directly interlinked and accessible via the website. Both tools can be regarded in themselves as key tools for dissemination. RiBaTox guides users through systematic decision trees in a self-explanatory way along the questions of the users towards the concepts, tools and other information developed and compiled by SOLUTIONS and required to solve the problem. The knowledge base provides access and allows easy search for environmental monitoring, toxicity and compound property data on a large set of chemicals but also the results of prioritization exercises. The website also provides direct links to six important partner projects, relevant networks such as NORMAN and EIONET as well as other related and helpful websites.
3) Dissemination of results to stakeholders, scientific community and the broad public
Large efforts have been undertaken and have been very successful in creating visibility and awareness of SOLUTIONS and its results in the scientific community, among decision makers and practitioners in the field of water and chemical monitoring and management as well as in the general public using targeted dissemination tools for each group.
The scientific community was addressed with more than 100 highly ranked publications in peer-reviewed scientific journals that have been published so far together with about 30 more that are submitted or in preparation. Of particular importance were a series of integrated papers with a specific focus on policy-related issues such as the recommendations for the revision of the WFD [1, 5] and more specifically on the implementation of effect-based tools [6, 7]. These dissemination activities are complemented by the organization of conferences, workshops and special sessions on regular scientific conferences. In many cases, these activities involved not only the scientific community but also had a strong focus on stakeholder involvement. Some outstanding examples include (1) the combined SOLUTIONS – EDA Emerge – MARS – GlobAqua – NORMAN – MOTREM student conference in 2015 that also demonstrates the close interaction with other projects, (2) three excellent workshops on prioritization of chemicals receiving a lot of attention from stakeholders from most relevant institutions, (3) a Special Session on SOLUTIONS at SETAC Europe 2018 with 18 presentations only in this session and many more distributed over other sessions, (4) the SOLUTIONS Final Conference in 2018 in Leipzig, (5) the SETAC-UNEP-LCI Workshop on environmental footprinting and (6) the Conference Water Science for Impact in Wageningen. Several workshops were dedicated exclusively to specific stakeholder groups such as officers from DGs Research, Environment and Agriculture of the European Commission in 2017 in Brussels and the RiBaTox Workshop in Brussels. Since SOLUTIONS demonstrated the added value of effect-based methods for monitoring as a key tool for addressing complex mixtures and provided extensive guidance for their implementation, SOLUTIONS principle investigators strongly contributed to the WG on effect-based methods under the WG Chemicals of WFD CIS attending and presenting the SOLUTIONS concept at their workshops. Further highlights included a workshop on the development of mitigation and abatement options for a Dutch SOLUTIONS stakeholder group, the presentation of major SOLUTIONS findings on the EUREAU Workshop on micropollutants in Stockholm (Sweden), and at the Conference on pharmaceuticals and micropollutants in surface waters by the Ministry for the Environment in North Rhine-Westphalia (Düsseldorf, Germany), both in 2018.
A series of 10 policy briefs will inform decision and policy makers on the European, national and regional level on key findings and recommendations of SOLUTIONS and are distributed individually, as a brochure and in the scientific journal Environmental Sciences Europe. The first policy brief on effect-based methods has been finalized, distributed and submitted for publication. The others are in preparation.
While SOLUTIONS results have been presented in numerous oral presentations in many conferences, a number of invited keynotes on SOLUTIONS given worldwide shall be particularly highlighted here since they illustrate the global interest in SOLUTIONS. Invited keynotes have been given on the International Conference on Emerging Contaminants in Kaohsiung (Taiwan, 2015), on the International Symposium on Chemical Risk Prediction and Management in Wuxi (China, 2016), on the Symposium on Environmental Chemistry in Niigata (Japan, 2016), on the Conference on Innovation in Environmental Monitoring in York (Great Britain, 2016) and on ISTA Conference in Limeiras (Brasil, 2017). A particular focus was given on the interaction with the FP7 projects on multiple stress MARS and GlobAqua with SOLUTIONS keynotes on their final conferences and several of their symposia. By discussing SOLUTIONS on all Annual General Assemblies of the European network NORMAN during the run-time of the project, we used this outstanding science-policy interface for dissemination and discussing SOLUTIONS results with scientists and stakeholders. The close interaction with NORMAN is also reflected by common workshops (e.g. the first workshop on prioritization of chemicals in Paris, 2015) as well as the common recommendation paper on WFD revision .
The general public has been addressed using different media including TV clips in several partner countries, several videos that were disseminated via the worldwide web, a series of freshwater blogs highlighting important news from the project, several articles published in the popular press of different partner countries, media briefings and press releases. In addition, discussion with the local public has been organized in different formats such as the “Leipziger Umweltstammtisch” in 2016.
1. Brack, W., et al., Towards the review of the European Union Water Framework Directive: Recommendations for more efficient assessment and management of chemical contamination in European surface water resources. Science of The Total Environment, 2017. 576: p. 720-737.
2. Dulio, V., et al., Emerging pollutants in the EU: 10 years of NORMAN in support of environmental policies and regulations. Environmental Sciences Europe, 2018. 30(1): p. 5.
3. Massei, R., et al., Screening of Pesticide and Biocide Patterns As Risk Drivers in Sediments of Major European River Mouths: Ubiquitous or River Basin-Specific Contamination? Environmental Science & Technology, 2018. 52(4): p. 2251-2260.
4. Beckers, L.-M. et al., Characterization and risk assessment of seasonal and weather dynamics in organic pollutant mixtures from discharge of a separate sewer system. Water Research, 2018.
5. Brack, W., et al., Towards a holistic and solution-oriented monitoring of chemical status of European water bodies: how to support the EU strategy for a non-toxic environment? Environmental Sciences Europe, 2018. DOI: 10.1186/s12302-018-0161-1.
6. Altenburger, R., et al., Future water quality monitoring - Adapting tools to deal with mixtures of pollutants in water resource management. Science of the Total Environment, 2015. 512: p. 540-551.
7. Neale, P.A. et al., Development of a bioanalytical test battery for water quality monitoring: Fingerprinting identified micropollutants and their Contribution to effects in surface water. Water Research, 2017. 123: p. 734-750.
List of Websites:
SOLUTIONS web site: www.solutions-project.eu
contact person: Dr. Werner Brack, email: firstname.lastname@example.org
Grant agreement ID: 603437
1 October 2013
30 September 2018
€ 16 323 009,85
€ 11 988 935,20
HELMHOLTZ-ZENTRUM FUR UMWELTFORSCHUNG GMBH - UFZ
Deliverables not available
Grant agreement ID: 603437
1 October 2013
30 September 2018
€ 16 323 009,85
€ 11 988 935,20
HELMHOLTZ-ZENTRUM FUR UMWELTFORSCHUNG GMBH - UFZ
Grant agreement ID: 603437
1 October 2013
30 September 2018
€ 16 323 009,85
€ 11 988 935,20
HELMHOLTZ-ZENTRUM FUR UMWELTFORSCHUNG GMBH - UFZ