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- 14 - Geography and Environmental Studies
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- The University of Hull
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- 14 - Geography and Environmental Studies
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- Environmental
- Is this case study continued from a case study submitted in 2014?
- No
1. Summary of the impact
Research carried out at the University of Hull (UoH) has produced a novel tool for monitoring and assessing the ecological status of lakes based on environmental DNA (eDNA) metabarcoding of fish communities. The tool has been adopted by national agencies within the Department for Environment, Food and Rural Affairs (Defra) i.e. the Environment Agency (EA); the Scottish Environmental Protection Agency (SEPA); Natural Resources Wales (NRW); Natural England (NE); and NatureScot to fulfil monitoring obligations under UK and EU law (i.e. the EU Water Framework Directive 2000/60/EC). This is the first example of eDNA metabarcoding being adopted for statutory monitoring anywhere in the world.
This non-invasive method has also been used to generate evidence of species’ distributions, informing management decisions relating to Flood Alleviation Schemes, and has been adopted by commercial companies (providing them with significant revenue).
2. Underpinning research
Biodiversity monitoring is essential for assessing human impact on the environment and is a requirement of UK and European legislation such as the Water Framework Directive (WFD). The UK is currently failing to meet national and international legislative requirements for monitoring lake fish populations because existing monitoring methods are costly, time consuming, and can cause harm to organisms and their environment. Environmental DNA (eDNA) is released by organisms into their environments and can be sampled simply by collecting water or soil. eDNA traces in water can therefore reveal the nature and extent of lake fish populations. eDNA is argued to be a ‘game-changer’ in biodiversity monitoring and is widely regarded as far more cost-effective and less invasive than conventional methods, while having minimum impact on the environment.
Since 2015, our research has pioneered the application of High Throughput Sequencing (HTS) of eDNA (i.e. ‘eDNA metabarcoding’) to provide data on entire fish communities in freshwater lakes (3.1 – 3.6). This work includes one of the first research papers to provide a practical methodology for monitoring lake fish communities with eDNA (3.1).
Our research during this impact period focussed on:
Testing, refining and validating eDNA metabarcoding for recovery of information on fish communities across a wide range of lentic environments (3.1 - 3.6).
Understanding the dynamics of dispersion and degradation of eDNA in lentic waterbodies, which is critical for accurate interpretation of the data (3.3).
Understanding the temporal and spatial distribution of eDNA in lakes, and providing recommendations for when and where to sample (3.4).
Demonstrating that data generated from eDNA metabarcoding of lake fish is informative for ecological classification (3.5) and for estimating relative abundance (3.4, 3.5, 3.6).
The key findings of our research are that:
eDNA metabarcoding consistently outperforms established monitoring methods (gill-netting) for fish species detection (e.g. detecting 12 of the 14 species recorded in Windermere, compared to only 4 by gill-net surveys (3.1, 3.4)).
eDNA metabarcoding can be considered at least semi-quantitative, as the data correlates significantly with long-term rank abundance data obtained using established methods (3.1, 3.4, 3.5) and with biomass and abundance inferred directly from drained ponds (3.6).
There is strong spatial structure in eDNA distribution (i.e. where fish species are located in a water body, and in what quantities, informs the development of an efficient sampling strategy to produce the best estimate of the total fish population). This is the case particularly in the summer, which has important implications for choosing when and where to sample, and for estimating relative abundance (using Site Occupancy Modelling approaches (3.1, 3.4)).
eDNA metabarcoding data provides accurate information on the ecological status of lakes, indicating the data is informative and appropriate for ecological assessments (3.1, 3.5, and output of 3.12).
Combined, these methodological developments and research findings demonstrate that eDNA metabarcoding provides accurate information on the composition of the fish community in lakes, which in turn can provide information on ecological status. Our research has provided the evidence base needed to produce the first eDNA metabarcoding tool for WFD and wider statutory monitoring.
3. References to the research
Hänfling, B., Lawson Handley, L.J., Read, D.S., Hahn, C., Li, J., Nichols, P., Blackman, R.C., Oliver, A., Winfield, I.J., 2016. Environmental DNA metabarcoding of lake fish communities reflects long-term data from established survey methods. Molecular Ecology, 25(13), pp.3101–3119. https://onlinelibrary.wiley.com/doi/abs/10.1111/mec.13660
Li, J., Lawson Handley, L.J., Read, D.S., Hänfling, B, 2018. The effect of filtration method on the efficiency of environmental DNA capture and quantification via metabarcoding. Molecular Ecology Resources, 18(5), pp.1102-1114. http://dx.doi.org/10.1111/1755-0998.12899
Li, J., Lawson Handley, L.J., Harper, L.R., Brys, R., Watson, H.V., Di Muri, C., Zhang, X., Hänfling, B, 2019. Limited dispersion and quick degradation of environmental DNA in fish ponds inferred by metabarcoding, Environmental DNA, 5, p.133. https://onlinelibrary.wiley.com/doi/full/10.1002/edn3.24
Lawson Handley, L.J., Read, D.S., Winfield, I.J., Kimbell, H.S., Johnson, H., Li, J., Hahn, C., Blackman, R., Wilcox, R., Donnelly, R., Szitenberg, A., Hänfling, B., 2019. Temporal and spatial variation in distribution of fish environmental DNA in England’s largest lake, Environmental DNA, 1(1), pp.26–39. https://onlinelibrary.wiley.com/doi/full/10.1002/edn3.5
Li, J., Hatton‐Ellis, T.W., Lawson Handley, L.J, Kimbell, H.S., Benucci, M., Peirson, G., Hänfling, B., 2019. Ground‐truthing of a fish‐based environmental DNA metabarcoding method for assessing the quality of lakes V. Paiva, ed. Journal of Applied Ecology, 56(5), pp.1232–1244. https://besjournals.onlinelibrary.wiley.com/doi/abs/10.1111/1365-2664.13352
Di Muri, C. **Lawson Handley, L.J., Bean, C.W., Li, J., Peirson, G., Sellers, G.S., Walsh, K., Watson, H.V., Winfield, I.J., Hänfling, B., 2020 Read counts from environmental DNA (eDNA) metabarcoding reflect fish abundance and biomass in drained ponds, Metabarcoding and Metagenomics, 4, p. e56959. https://doi.org/10.3897/mbmg.4.56959
Grants awarded (title, funder, PI, CoI (BH = Bernd Hänfling, LLH = Lori Lawson Handley), start date, end date, amount)
7. Evaluation of eDNA based metabarcoding as a monitoring tool for fish in large lakes, Environment Agency, BH, LLH, 01/01/2015 to 30/04/2015, £29,649.00
Final report https://www.gov.uk/government/publications/a-dna-based-monitoring-method-for-fish-in-lakes
8. Evaluation of eDNA based metabarcoding as a monitoring tool for fish in large lakes – Phase 2, Scottish Environmental Protection Agency, LLH, BH, 01/09/2015 to 29/01/2016, £59,657.00
9. Using eDNA surveys to evaluate the impact of River Thames Scheme Capacity Improvements and Flood Channel Project, Environment Agency, BH, LLH, 01/04/2016 to 31/01/2017, £87,618.00
10. A review of recent advances in genetic methods to identify improvements in CAMERAS partners monitoring activities, Scottish Government, BH, LLH, 15/06/2016 to 14/06/2017, £74,792.00
11. Lake fish classification delivery - Phase 3: Expansion of an eDNA sampling network in Scotland, Scottish Environmental Protection Agency, BH, LLH, 01/11/2017 to 31/10/2018, £39,267.17
12. Development of an eDNA based tool for lake fish monitoring in the UK - collection of data from reference lakes in England, Environment Agency, BH, LLH, 01/11/2018 to 31/03/2019, £57,000.00
Final results published in http://www.wfduk.org/sites/default/files/January%202020%20UK%20TAG%20Consultation%20Document.pdf pp10-18
4. Details of the impact
The key impact of the research is the development of a completely new, non-invasive way of monitoring lake fish communities and assessing the ecological status of lakes, based on environmental DNA (eDNA) metabarcoding. The method delivers comprehensive data on the distribution of fish, which in turn provides important and accurate information on the ecological status of water bodies, which is a requirement of the Water Framework Directive (WFD) (which protects and improves the water environment, and defines the legal, statutory monitoring requirements for bodies of water).
The eDNA method was adopted by Defra agencies for WFD assessment of lakes, following a consultation by the WFD UK Technical Advisory Group (UKTAG) between 6th January and 14th February 2020 (5.1).
This provides the UK with the first fully-operational approach anywhere in the world for lake fish monitoring and WFD assessment using eDNA metabarcoding.
Beneficiaries: The main direct beneficiaries of this work are the Defra agencies that are required to carry out fish community monitoring for regulatory and decision-making purposes, and the private companies (e.g. consultancies such as Nature Metrics) contracted to fulfil this monitoring work.
Benefits, and evidence of benefits, to Defra Agencies:
- Development of a monitoring strategy based on modern molecular eDNA methods.
Evidence: Data generated and analysed during a roll-out of the method across 101 UK lakes was included in the UKTAG consultation, which resulted in the adoption of the fish monitoring tool by Defra agencies in 2020 (5.1). In a joint statement by the Environment Agency (EA), Scottish Environment Protection Agency (SEPA) and NatureScot (5.2), the agencies described the research carried out by UoH as: “having contributed towards achieving a step change” and having “already impacted the strategic vision of the agencies and the way lake fish communities are monitored.” (5.2)
- Providing a method that enables the launch of a lake fish monitoring programme compatible with the WFD, a legal requirement which could not be previously fulfilled.
Evidence: The method has been *“approved as a WFD monitoring method, following a formal consultation process by the UK WFD Technical Advisory Group.*” (5.2)
- Providing a Standard Operating Procedure (SOP) for lake fish monitoring with eDNA, that can be followed for routine monitoring.
Evidence: “ Collectively this research has successfully delivered a standard operating procedure covering sampling and lab processes and an assessment procedure that allows the condition of lake fish communities [to be assessed].” (5.2)
- Providing evidence in ongoing monitoring programmes.
Evidence: “ The eDNA based fish monitoring tool developed by UoH is already being deployed in a number of different statutory monitoring programmes carried out by the UK-EAs.” (5.2). For example, the method was used to provide baseline data on rare and invasive species in 36 lakes of the River Thames floodplain, as part of Environmental Impact Assessments for the proposed London Flood Channel in 2016 and the Oxford Flood Alleviation Scheme in 2018 (5.3). In both cases, lake fish monitoring was required to inform mitigation strategies and develop an environmentally acceptable scheme, to enable assessment of Special Protection Areas and Sites of Special Scientific Interest, and to allow assessment against WFD objectives. Data on species detections (for example the presence of the protected bullhead, Cottus gobio) advised decisions on the mitigation of effects of the flood alleviation schemes and was included in the respective impact assessments (5.3).
- Cost implications and financial impact.
Evidence: “ The method also provides considerable cost and time savings compared to conventional methods” (5.2). For Scottish lochs, the estimated cost-saving through the eDNA approach was >£1,000 per lake (even during the proof-of-concept phase), with significant cost reduction expected after further optimisation (as substantially less labour is required, for a shorter period). SEPA will therefore make substantial savings, alongside other regulatory bodies.
Benefits, and evidence of benefits, to the private sector:
The method has been adopted by a commercial company (Nature Metrics) which is offering it as a service to ecological consultancies and other end users. This development has generated commercial and financial benefits. UoH has collaborated closely with the company to facilitate this adoption, producing a standard operating procedure covering sampling and lab processes and assessment of the condition of lake fish communities . The CEO of Nature Metrics states in her letter of support (5.4) that : “The research provided the foundation for developing a commercial service for fish eDNA metabarcoding, which we have now applied to approximately 2000 client samples from over 20 countries, primarily for purposes of conservation and environmental impact assessment (EIA). This has generated approximately £XXXX in revenue since 2017”.
Evidence of wider impact:
Throughout this research we have worked closely with Defra agencies and other stakeholders to facilitate the uptake of eDNA-based monitoring more generally. Activities that support the wider impact of our research include:
Writing a review of DNA-based methods for the Scottish Government (3.10), which “ contributed significantly to the drive towards using eDNA approaches to Site Condition Monitoring… and environmental quality assessments … *and the development of an internal NatureScot Genetics Strategy.*” (5.2)
Playing a key role in the development of the UK Earth Observation Framework DNA Working Group (5.5). UoH hosted the 2nd annual meeting in September 2014, and Lawson Handley and Hänfling are members of the steering committee and chair the Fish and Invasive Species Technical Groups (5.5). “The UoH team have played a critical role in establishing and maintaining this highly active and fast-growing group, which has brought together member organisations from Universities and end user groups.” (5.2)
Having an active role in the EU COST action ‘DNAqua-Net’: a multidisciplinary group of researchers which aims to identify gold-standard genomic tools for aquatic biodiversity monitoring including eDNA approaches, and which works with water managers, politicians and other non-academic stakeholders. Our research was key to an influential perspective paper on the implementation of DNA-based approaches for aquatic biodiversity monitoring (5.6) and led to presentations at numerous national stakeholder meetings across Europe, including to the Working Group of the European Commission’s Common Implementation Strategy, ECOSTAT, which is in charge of the implementation of the WFD. The Chair of DNAqua-Net stated that the research team at UoH “played a key role in influencing major stakeholder groups across Europe in their attitude to the feasibility of implementing DNA based methods for biodiversity monitoring. In some member countries this has already led to the initiation of implementation programmes for monitoring fish communities through the use of environmental DNA” (5.7).
These three initiatives will sustain the position of UoH at the forefront of the growing development and impact of eDNA-based monitoring, as we help to refine best practice and inform the wider professional, research and academic communities of its applications and further potential.
5. Sources to corroborate the impact
All available as pdfs on request.
UK TAG lake fish assessment standards consultation document (a) and responses (b) publicly available at http://www.wfduk.org/stakeholders/uktag-standards-consultation-january-2020
Letter of support signed by Scottish Environmental Protection Agency, Environment Agency, and NatureScot. The letter details the contribution of UoH to developing a strategic vision on DNA-based monitoring and implementing eDNA approaches for lake fish communities within the UK Environment Agencies.
Environmental Impact Assessments for the (a) River Thames and (b) Oxford Flood Alleviation Schemes.
Letter of support from the CEO of Nature Metrics ( https://www.naturemetrics.co.uk/) describing their commercial adoption of the method.
Evidence of membership of the Earth Observation Framework DNA Working Group steering committee and chairing of the fish and invasive species technical groups http://www.ukeof.org.uk/our-work/ukdna, together with programme for the annual conference, held at UoH 18th – 19th September 2014, which focussed on identifying end user needs for DNA based monitoring ( http://www.ukeof.org.uk/documents/uk-dna-wg-meeting-files/2014-dna-wg-agenda-hull).
Hering. D., Borja, A., Jones, J.I, Pont, D., Boets, P., Bouchez, A., Bruce, K., Drakare, S., Hänfling, B., Kahlert, M., Leese, F., Meissner, K., Mergen, P., Reyjol, Y., Segurado, P., Vogler, A., Kelly, M. Implementation options for DNA-based identification into ecological status assessment under the European Water Framework Directive. Water Res. 2018;138: 192–205. https://www.sciencedirect.com/science/article/abs/pii/S0043135418301830?via%3Dihub
Letter of support from Chair of the EU COST Action DNAqua-Net CA15219 ( https://dnaqua.net), stating how expertise from UoH has played a key role in influencing major stakeholder groups across Europe in terms of implementing DNA-based methods for biodiversity monitoring.
- Submitting institution
- The University of Hull
- Unit of assessment
- 14 - Geography and Environmental Studies
- Summary impact type
- Environmental
- Is this case study continued from a case study submitted in 2014?
- No
1. Summary of the impact
University of Hull (UoH) research has led to more robust implementation of the EU Marine Strategy Framework Directive and harmonisation of monitoring approaches within EU Member States. The impact is evident through the repeal of Commission Decision 2010/477/EU and its replacement with Commission Decision 2017/848/EU, which incorporated recommendations made by UoH research and which applies to all 22 marine EU Member States (a sea area of 5.72 million km2), their overseas territories, the UK and Turkey.
UoH research also contributed to the development of the DEVOTool software which in turn underpinned the development of software for assessing the ‘Good Environmental Status’. This is now in use in the HELCOM (Baltic) Region incorporating 9 EU Member States.
The project won the COLUMBUS Blue Society Knowledge Transfer Award (2018), recognising its contribution to the impactful application of knowledge by end-users implementing policy.
2. Underpinning research
The Marine Strategy Framework Directive (MSFD, Directive 2008/56/EC) aims to achieve Good Environmental Status (GES) of EU seas by 2020 and to protect the natural system in supporting marine-related economic and social activities. GES is defined as where the marine waters provide ecologically diverse and dynamic oceans and seas which are clean, healthy and productive. The Directive is implemented by all 22 EU Member States with marine waters, covering 5.72 million km2 of sea and 68,000 km of coastline, and affects an estimated 41% of the European population. Additionally, the Directive is implemented in overseas territories of EU Member States and by Turkey. It continues to be implemented in the UK after it exited the EU.
The original Directive came into force in 2008, and was implemented in a stepwise manner in order to achieve GES by 2020. Part of this implementation was through the Commission Decision 2010/477/EU which detailed criteria and methodological standards for achieving GES. Since that time, UoH has contributed to research (see references 1- 4) on the definition and interpretation of GES and on the development and evaluation of indicators for the assessment of GES, thereby supporting MSFD implementation. The details of this research and the UoH contribution are outlined in points i) and ii):
i) Evaluation of the Commission Decision 2010/477/EU: Elliott’s research (1, 2) highlighted inconsistencies in the definition of GES (in terms of criteria, setting of targets, scale of assessment and practical application of the concept), together with weaknesses in the approach to implementing the MSFD. Elliott’s role in these publications was in (1) as second author, contributing substantially to the conception of the study and to the writing and (2) as initiator of the study. At the request of the European Commission (EC), Elliott and Mazik jointly coordinated (with the EC Joint Research Centre) research (3) (co-authored by Boyes and Burdon), to identify the specific limitations of the MSFD using a critical analysis of EC legal texts to identify and clarify specific scientific and technical issues of the Directive.
In particular, the research identified that Tables 1 and 2 of the MSFD Annex 3 required clarification in terms of the categorisation of habitats, the inclusion of all European marine habitats, and in its methodological approaches to collecting geospatial data. Further, the list of anthropogenic pressures acting upon the marine environment was considered incomplete and the terminology used was inconsistent. Furthermore, the EUNIS (European Nature Information System) habitat classification required updating to facilitate implementation of the MSFD, and overall clarification of terminology and consistency of its use was needed to achieve sustainability.
Marine management requires an understanding of the human pressures on the marine environment (3), together with integration of the various human uses of the sea, in order to achieve sustainability. The EU and UK Marine Strategies rely on the MSFD (for environmental quality and status) being implemented jointly with the recent Maritime Spatial Planning Directive (MSPD). Accordingly, Elliott developed a ‘Best Expert Judgement’-based (BEJ) approach to maximise the assimilative capacity of a marine area and minimise the environmental degradation due to new activities (4). The research showed BEJ as central to cost-effective marine adaptive management, especially in data-poor areas.
ii) Evaluation of GES assessment tools: Mazik jointly conceived and coordinated research on the collation and interrogation of European marine biodiversity indicators (5) and monitoring programmes, leading to the development of a framework to enable the transparent and standardised evaluation and selection of indicators for MSFD implementation (5). This was linked to the development of DEVOTool (a software tool to select appropriate indicators for the MSFD, providing an integrated and comparative means of biodiversity assessment) which in turn underpinned the development of NEAT (the Nested Environmental Status Assessment Tool). The research highlighted that standardized approaches such as this are necessary to ensure coherence of MSFD implementation and knowledge-sharing between Member States.
3. References to the research
Borja, A., Elliott, M., Andersen, J.H., Cardoso, A.C., Carstensen, J., Ferreira, J.G., Heiskanen, A-S., Marques, J.C., Neto, J., Teixeira, H., Uusitalo, L., Uyarra, M.C., Zampoukas, N. 2013. Good Environmental Status of marine ecosystems: What is it and how do we know when we have attained it? Marine Pollution Bulletin 76, 16-27. http://dx.doi.org/10.1016/j.marpolbul.2013.08.042
Saul, R., Barnes, R., Elliott, M. 2016. Is climate change an unforeseen, irresistible and external factor – a force majeure in marine environmental law? Marine Pollution Bulletin 113 (1-2), 25-35. https://doi.org/10.1016/j.marpolbul.2016.06.074
Patricio, J., Texeira, H., Borja, A., Elliott, M., Berg, T., Papadopoulou, N., Smith, C., Tiziana Luisetti (Cefas), Uusitalo, L., Wilson, C., Mazik, K., Niquil, N., Cochrane, S., Andersen, J.H., Boyes, S., Burdon, D., Carugati, L., Danovaro, R., Hoepffner, N. 2014. DEVOTES recommendations for the implementation of the Marine Strategy Framework Directive. DEVOTES Deliverable D 1.5 ( http://www.devotes-project.eu/wp-content/uploads/2014/10/DEVOTES_Deliverable-1-5.pdf)
Elliott, M., Boyes, S.J., Barnard, S., Borja, A. 2018. Using best expert judgement to harmonise marine environmental status assessment and maritime spatial planning. Marine Pollution Bulletin 133, 367-377. https://doi.org/10.1016/j.marpolbul.2018.05.029
Queiros, A.M., Strong, J.A., Mazik, K., Carstensen, J., Bruun, J., Somerfield, P., Bruhn, A., Ciavatta, S., Chuševė, R., Nygård, H., Flo, E., Bizsel, N., Ozaydinli, M., Muxika, I., Papadopoulou, N., Pantazi, M. & Krause-Jensen, D. 2016. An objective framework to test the quality of candidate indicators of good environmental status . Front. Mar. Sci. 3:73 https://doi.org/10.3389/fmars.2016.00073
Grant: EU FP7 programme ‘DEVOTES project’ (DEVelopment Of innovative Tools for understanding marine biodiversity and assessing Good Environmental Status) 2012-2016. UoH PI: Prof. Mike Elliott. £281,628.8 awarded to UoH.
Awards: DEVOTES was runner up in the Frontiers (Open Access Journals) Spotlight Award (2017) for the scientific impact of the project ( https://blog.frontiersin.org/2017/05/08/ocean-sustainability-plastic-policy-supported-by-science-to-protect-our-oceans/).
It also received the COLUMBUS Blue Society Knowledge Transfer Award (2018) for impactful research and knowledge exchange, recognising its contribution to the impactful application of knowledge by end-users implementing policy. The award specifically acknowledged the ‘user-friendly tool’ (NEAT) developed in the project ( http://www.columbusproject.eu/columbus-news/news/1852-bs-awards).
4. Details of the impact
Research by UoH generated two major forms of impact:
Highlighting inadequacies in the MSFD which, together with simultaneous reports by others across Europe, led to a technical review of the Directive. This review in turn led to a major policy update which acted upon recommendations made by UoH and collaborators. This represented a key change to the strategy for MSFD implementation in all European Seas.
Evaluation and testing of indicators of GES led to the development of the NEAT tool (based on DEVOTool) which has provided a validated tool for the integrated, consistent and comparative assessment of biodiversity status and GES across European regional seas. This has also been taken up for use in the HELCOM (Helsinki Commission) region (the Baltic).
Impact 1. Change to EU policy
Elliott’s research (1, 2) and co-authorship of 3 with Mazik, Boyes and Burdon, together with documents produced by other Institutions, Member States and EU Departments, unanimously concluded the requirement for review and clarification of the Commission Decision 2010/477/EU. The review was a three-Phase process; UoH research contributed significantly to Phase 1 through leadership of the Work Package (Elliott and Mazik) under which the research was carried out, joint coordination and authorship of the research, and joint coordination of a workshop during which the final recommendations were agreed (A, B):
Phase 1 (end 2013 – mid 2015): technical and scientific review
Experts from the respective MSFD CIS (MSFD Common Implementation Strategy) or RSC (Regional Seas Conventions) groups under the coordination of the JRC (European Commission Joint Research Centre) and ICES (International Council for the Exploration of the Sea) prepared technical and scientific reviews for each of the 11 descriptors of GES. These formed the basis of a series of descriptor-specific workshops, led by the JRC, which led to recommendations for revision of the Commission Decision 2010/477/EU. UoH research (1, 3) and research later published as 2 and 4 was submitted (at the request of the EC, as confirmed by B) to feed into this process, and is cited throughout JRC workshop reports C and D. These reports clearly acknowledge the recommendations made by UoH work (e.g. “recent scientific literature and R&D projects have provided a huge amount of guidance on this topic (e.g. Patricio et al., 2014)”) (3), as cited in D. These recommendations agreed with those made by other organisations within the EU and individual Member States and were taken forward to Phase 2. The UoH’s contribution is clearly evidenced in two testimonials:
The Policy Officer at the European Commission’s Directorate-General for Environment (DG ENV) confirms (A) that, for Phase 1 of the process, *“Ongoing research projects, including the FP7 DEVOTES project in which the University of Hull was a partner, were a valuable source of information used in the advice. DEVOTES was particularly useful in that it was specifically focused on MSFD implementation and produced a considerable volume of relevant scientific studies in support of MSFD implementation, including…Patricio et al., 2014 [ **(3)*]…This study represents an example of the importance of sound scientific research which is dedicated to support implementation of EU marine policy, and of the continued interaction between the research and policy implementation communities.” (A)
A testimonial from the Policy Officer at the European Commission’s Directorate-General for Research and Innovation (DG RTD), in the Unit where the DEVOTES FP7 project was managed (B) confirms “ the University of Hull’s significant contribution to informing the technical review of Commission Decision 2010/477/EU (undertaken between 2013 and 2015) regarding the Marine Strategy Framework Directive (MSFD)… as indicated by extensive citations to the work in ICES and JRC (European Commission Joint Research Centre) workshop reports that formed the outputs of this first phase… The workshop reports drew directly on the findings of the DEVOTES project, specifically recommendations from the research undertaken by the University of Hull’s Mike Elliott and his colleagues.” (B)
Furthermore, DEVOTool and NEAT and the underpinning indicator catalogue (see Impact 2 above) fed into the 2015 ICES technical review of the Commission Decision 2010/477/EU in relation to seafloor integrity (Descriptor 6) (E).
Phase 2 (mid 2015 - end 2015): consultation and discussion
The MSCG (Marine Strategy Coordination Group, chaired by the EC Directorate-General for Environment) coordinated a formal consultation of the results of the technical review, allowing the MSFD Common Implementation Strategy (CIS) to provide a consolidated opinion.
Phase 3 (end 2015 – mid 2016): decision-making
During this phase, the European Commission took on board the outcome of phase 1 and 2 and made a final decision on the clarifications required to address the inadequacies of the MSFD. On 17th May 2017, as a direct result of this technical review to which UoH outputs contributed (A, B), the European Commission adopted Commission Decision 2017/848/EU (F), which repeals the Decision 2010/477/EU and redefines the criteria and methodological standards on GES, and the specifications and standardised methods for marine monitoring and assessment. This represented a major change to the strategy for MSFD implementation in all EU Member States and other European seas (F). The recommendations made by the UoH research are carried through into the new policy document (A, B).
Testimony from the Joint Head of the Marine Ecosystems Team at the UK’s Joint Nature Conservation Committee (JNCC) (G) confirms the adoption of the new Commission Decision 2017/848/EU “ as beneficial in terms of our ability to deliver under MSFD, and acknowledges that the revised Commission Decision constitutes an important guidance to support the UK Marine Strategy and assessments under OSPAR (representing the North East Atlantic region)”. (G)
Impact 2. Provision of tools for delivering GES
Mazik played a key role in the collation, evaluation and testing of indicators for assessment of GES. This led to the development of the DEVOTool catalogue and software which facilitates selection of appropriate indicators for assessing GES under the MSFD. DEVOTool underpinned and was directly incorporated into the Nested Environmental status Assessment Tool (NEAT) (H) which has now been further developed and implemented across the Helsinki Commission (HELCOM) region (the Baltic) (I).
Beneficiaries
Direct beneficiaries include the EU, and thus its 22 maritime Member States; other states and overseas territories adopting EU practices; the UK Government, Devolved Administrations and their relevant executive bodies (e.g. Defra, Marine Scotland, DAERA (Dept. of Agriculture, Environment and Rural Affairs, NI), Natural Resources Wales); and the Regional Seas Conventions - OSPAR (NE Atlantic), HELCOM (Baltic), Barcelona Convention (Mediterranean), and Black Sea Commission (under the Bucharest Convention).
Dates of impact
Review of EU Directive and policy update: 18th May, 2017- present. Ongoing until next policy revision (F).
Development of NEAT: February 2016 – present. Ongoing (H, I).
5. Sources to corroborate the impact
All available as pdfs on request.
A. Letter of support from Marine Environment Policy Officer at the European Commission’s Directorate-General for Research and Innovation (DG RTD)), explaining the role of UoH in the review and repeal of Commission Decision 2010/477/EU.
B. Letter of support from Policy Officer at the European Commission’s Directorate-General for Research and Innovation (DG RTD), (formerly at Joint Research Centre, Ispra, Italy) explaining the role of UoH in the review and repeal of Commission Decision 2010/477/EU.
C. Palialexis, A. (ed.) 2015. Review of the Commission Decision 2010/477/EU concerning MSFD criteria for assessing Good Environmental Status. https://mcc.jrc.ec.europa.eu/documents/201604040717.pdf
D. Palialexis A. & Cardoso, A.C. (eds), Report of the JRC’s Descriptor 1 workshop to support the review of the Commission Decision 2010/477/EU concerning MSFD criteria for assessing Good Environmental Status; EUR 27715. https://mcc.jrc.ec.europa.eu/documents/201604040555.pdf
E. ICES. 2015. Report of the workshop on guidance for the review of MSFD decision descriptor 6 – seafloor integrity II (WKGMSFDD6-II), 16-19 February 2015, ICES Head-quarters, Denmark. ICES CM 2015\ACOM:50.
F. European Commission - Environment. Our Oceans, Seas and Coasts. Legislation: The Marine Strategy Framework Directive. https://ec.europa.eu/environment/marine/eu-coast-and-marine-policy/marine-strategy-framework-directive/index_en.htm and https://eur-lex.europa.eu/legal-content/EN/TXT/PDF/?uri=CELEX:32017D0848&from=EN
G. Letter of support from Joint Head of Marine Ecosystems Team, Joint Nature Conservation Committee, explaining the impact of the policy change on MSFD implementation in the UK.
H. Berg,T., Murray, C., Carstensen, J., Andersen, J.H. 2016. NEAT – Nested Environmental status Assessment Tool v1.3.
http://devotes-project.eu/wp-content/uploads/2017/06/NEAT-manual-v1.3.pdf, providing details of the incorporation of DEVOTool into NEAT (see pages 4, 7, 17, 31, 37).
I. Outcome of the HELCOM BalticBOOST workshop on the HOLAS II biodiversity assessment tool.
- Submitting institution
- The University of Hull
- Unit of assessment
- 14 - Geography and Environmental Studies
- Summary impact type
- Environmental
- Is this case study continued from a case study submitted in 2014?
- No
1. Summary of the impact
Research undertaken at Hull International Fisheries Institute (HIFI), University of Hull has shaped key UK policies aimed at the conservation of fish species and the protection of fish populations impacted by water-resource management. This case study details specific areas of HIFI’s research that contributed directly to the:
formation of the Joint Nature Conservation Committee (JNCC) Common Standards Monitoring (CSM) guidance, which is used by all five UK regulatory authorities, all five conservation agencies, and all researchers and contractors in the UK and Ireland when establishing the conservation status of designated freshwater fish species, and;
UK government complying with, and implementing, key requirements of the European Union (EU) Habitats and Water Framework Directives.
2. Underpinning research
Effective conservation, restoration and enhancement of inland fisheries in the UK requires accurate assessment of the status of fish populations, and precise understanding of relevant, key environmental drivers such as river flow. Research conducted by Harvey, Cowx, Noble, Nunn and Bolland developed and tested protocols to establish the status of ‘conservation fish’ species and habitats [1-3, 7-11] and to develop robust scientific understanding of the flow requirements of UK fish species for migration, spawning and natural behaviour [4-6, 12-13]. The underpinning research that developed UK protocols for assessing the conservation status of fish and the impacts of flow on their sustainability is as follows:
1) The EU Conservation of Natural Habitats and of Wild Fauna and Flora Directive (known as the EU Habitats Directive) requires member states to: maintain or restore natural habitats and wild species to a favourable conservation status to promote the maintenance of biodiversity; provide robust protection for habitats and species of European conservation importance; undertake surveillance of habitats and species every six years; and ensure the long-term survival of Europe’s most valuable and threatened species and habitats. Seven UK fish species (Atlantic salmon; allis and twaite shad; brook, river and sea lamprey; and bullhead) are of European conservation importance. Effective protection of these ‘conservation fish’ species requires accurate estimates of their populations. However, there was no standard UK methodology or approach for establishing these estimates that met the EU Directive’s requirements. The underpinning research [1-3, 7-11] developed new, robust and rigorous standard monitoring methods and sampling strategies to establish the ‘conservation fish’ populations. Data derived via these methods therefore underpinned the UK Government’s compliance with the EU Habitats Directive, and allowed individual UK country-level Article 17 (of the Directive) assessments and associated evidence (which regulate species conservation across the EU) to be successfully aggregated, submitted to and accepted by the EU.
2) Water companies in England and Wales, and the regulator (the Environment Agency (EA)), have historically lacked reliable information on the impact of water abstraction (for industrial, domestic or agricultural use) on fish populations and communities. Similarly, they lack knowledge of how different flow regimes affect the sustainability of fisheries and habitats. HIFI’s research evaluated the potential impact of differing flow and water levels on coarse fish, on conservation species and on other fish populations in UK rivers [4-6, 12-13]. The flow requirements of different species were applied to various river reach examples in the UK, and then adjusted for the generic seasonal flows and water level regimes required for the key life stages of freshwater fish species. This research contributed significantly to the development of a standard policy for managing flows and water resources in UK rivers. All English and Welsh water companies and the EA use the standard policy (and HIFI also assessed Yorkshire Water’s programme to design ecologically-suitable flows in rivers impacted by reservoirs). This research, and the resultant standards ensures the compliance of water companies with the regulator (EA) and with the EU Water Framework Directive, while meeting societal needs for water abstraction.
3. References to the research
1. Cowx I.G. and Fraser D. (2003). Monitoring the Atlantic Salmon, Salmo salar. Conserving Natura 2000 Rivers Monitoring Series No. 7, English Nature, Peterborough. http://publications.naturalengland.org.uk/publication/113031
2. Cowx I.G. and Harvey J.P. (2003). Monitoring the Bullhead, Cottus gobio. Conserving Natura 2000 Rivers Monitoring Series No. 4, English Nature, Peterborough. http://publications.naturalengland.org.uk/publication/80012
3. Harvey J. and Cowx I. (2003). Monitoring the River, Brook and Sea Lamprey, Lampetra fluviatilis, L. planeri and Petromyzon marinus. Conserving Natura 2000 Rivers Monitoring Series No. 5, English Nature, Peterborough. http://publications.naturalengland.org.uk/publication/69040
4. Cowx I.G., Noble R.A., Nunn A. D., Harvey J. P., Welcomme R. L. and Halls A. (2004) Flow and level criteria for coarse fish and conservation species. Environment Agency Science Report, https://assets.publishing.service.gov.uk/government/uploads/system/uploads/attachment_data/file/291545/scho1204bilg-e-e.pdf
5. Cowx I.G., Noble R.A., Nunn A.D., Bolland J., Walton S., Peirson G. and Harvey J.P. (2012) Flow requirements of non-salmonids. Fisheries Management and Ecology 19, 548-556. https://doi.org/10.1111/fme.12017
6. Baker N.J., Taylor M.J., Cowx I.G., Harvey J.P., Nunn A.D., Angelopoulos N.V., Smith M.A., Noble R.A., Tinsdeall M., Baxter J. and Bolland J.D. (2020). The response of river‐resident fish to reservoir freshet releases of varying profiles intended to facilitate a spawning migration. Water resources research. https://doi.org/10.1029/2018WR024196
Relevant grants & contracts:
7. A standardised survey and monitoring protocol for the assessment of Atlantic salmon, Salmo salar, populations in SAC rivers in the UK, English Nature, £7,000 (2002-2003) (Cowx)
8. A standardised survey and monitoring protocol for the assessment of Lampreys, Bullhead and Shad populations in SAC rivers in the UK, English Nature £37,300 (2002-2003) (Harvey, Cowx, Noble, Nunn)
9. Determine the conservation status of larval river, sea and brook lamprey (ammocoetes and transformers) in the Yorkshire Ouse and Derwent SACs. Environment Agency, £15,200 (2004-2005) (Harvey, Nunn, Cowx, Noble and Bolland)
10. Determine the conservation status of river, sea and brook lamprey, bullhead and shad in the Rivers Wye and Usk SACS £63,370 (2005-2007) Countryside Council of Wales (Harvey, Noble, Cowx, Nunn and Bolland)
11. Determine the exploitation rate of the commercial fisheries and the run size of river lamprey in the Ouse system to support assessment of condition status in the Humber SAC. Environment Agency, £19,180 (2012-2013) (Bolland, Noble, Cowx)
12. Flow and level criteria for coarse fish and conservation species. Environment Agency, £36,017 (2003-2004) (Cowx, Noble, Nunn, Harvey)
13. Yorkshire Water Adaptive Management flow and drought research. Yorkshire Water £1,036,292 (2013-2020) (Harvey, Bolland, Nunn, Noble, Cowx)
4. Details of the impact
1) The Joint Nature Conservation Committee (JNCC) advises the UK Government on UK and international nature conservation. The JNCC “Common Standards Monitoring Guidance for Freshwater Fauna Monitoring Protocols (2015)” [A] is used by conservation and regulatory agencies to determine the status of ‘conservation fish’ species and whether their populations meet UK and EU regulatory requirements. HIFI’s research established survey and testing methodologies to produce standard protocols for seven fish species of conservation concern, five of which are highlighted in the references to the research [1-3, 7-11]. HIFI research contributed significantly to the standard survey and monitoring protocols in the JNCC policy. Cowx, Harvey and Nunn also served on an August 2014 panel of fisheries experts from UK conservation and regulatory agencies that reviewed the lamprey population assessment methodologies which shaped the JNCC protocols for lamprey analysis and monitoring. The key HIFI contributions to the JNCC process were recognised extensively in the JNCC Common Standards Monitoring (CSM) document [A], which directly cites HIFI’s contributions as follows:
Protocol 5 – For Atlantic salmon: “ The general approach in this protocol is broadly similar to Cowx and Fraser (2003)” (p.44); “ Cowx and Fraser (2003) list the range of environmental variables and catch data that should be recorded at each sampling site, regardless of the survey method employed” (p.45).
Protocol 7 – For Brook, river and sea lamprey: “ This protocol is based on a report produced as part of the LIFE in UK Rivers Project (Harvey and Cowx 2003)” (p.56); Harvey and Cowx (2003) is also quoted (p.67); and Cowx, Harvey and Nunn are credited with providing additional advice on the 2014 expert panel: “The UK conservation agencies are indebted to these people for their advice” (p.65).
Protocol 8 – For Bullhead: “Section 2 outlines how to undertake monitoring surveys where bullhead is the target species (based on Cowx and Harvey 2003)” (p.77); “The survey area may be smaller depending on the level of historical densities in the tributary. See Cowx and Harvey (2003) for further guidance” (p.77); “A statistical method for selecting a suitable number of sites is detailed in Cowx and Harvey (2003)” (p.78), with Cowx and Harvey (2003) also quoted (p.78).
HIFI’s research therefore shaped key areas of the JNCC CSM policy document: providing UK and Ireland government agencies with scientifically robust protocols to assess the status of ‘conservation fish’ species. These standards also met UK and EU statutory reporting requirements. As a result, UK conservation agencies possessed sufficient, legally-recognised monitoring evidence to inform and implement policies to ensure sustainable fish populations.
Examples of HIFI research impacting upon additional conservation agencies include:
Inland Fisheries Ireland (IFI) is the statutory agency responsible for inland fisheries in Ireland (within the Department of Communications, Climate Action and Environment (DCCAE)). HIFI’s research on lampreys was credited by IFI in the National Programme: Habitats Directive and Red Data Book Fish Species (2019) report [B] which functions to “fulfil legal obligations of our Fisheries Minister in regard to undertaking monitoring and surveillance of the fish species listed in Annex II of the Habitats Directive”. The report states:
“A semi-quantitative sample was taken at each site by electrofishing for 2 minutes in a defined area (1 m2) of suitable nursery habitat comprising silty deposits (after Harvey & Cowx 2003).” and “Of particular interest is the process of status assessment for larval lamprey. An important guidance document was provided by Harvey and Cowx (2003) covering this area and it has provided a basis for reporting for the Habitats team” (p.7 and p.67).
IFI’s Senior Research Officer further states [C]:
“In excess of 2,400 individual sites have been sampled for larval lamprey via Harvey and Cowx (2003)… I would suggest that HIFI has done all of us in the lamprey world a great service in generating the protocols as described in Harvey and Cowx (2003) and I envisage us continuing to use the procedure within IFI into the future”.
Site Condition Monitoring is a Scottish Natural Heritage (SNH, now named NatureScot) rolling programme to monitor the special features of protected areas, including their condition, their management, and any wider environmental factors which contribute to their condition. HIFI’s underpinning research on lampreys was recognised as the standard methodology used by SNH to provide site condition lamprey monitoring across all Scottish Special Areas of Conservation (SAC), including Endrick Water Site of Special Scientific Interest (SSSI) [D]. HIFI’s research thus ensured SNH could undertake site condition monitoring to the required standard for reporting to the EU [D]. The SNH report [D] credits HIFI’s research:
“The survey consisted of electrofishing optimal or sub-optimal habitat within 100 m long stretches of river (Harvey and Cowx, 2003). Quantitative samples were collected by depletion fishing within net frames (quadrats) as described by Harvey and Cowx (2003).” (p.2 and p.3).
In addition, NatureScot’s Freshwater Adviser (Geodiversity Group) states [E]:
“Credible population data are the backbone of meaningful site condition assessments. These data can be derived only by the application of well researched, robust, and repeatable methods; the work undertaken by the University [of Hull] has been instrumental in the successful evaluation of sites designated for one or more species of lamprey in Scotland, and has indirectly informed remedial management measures.”
Natural England (NE) provides advice to the UK government on natural environments and resources and has a wide remit of other roles and responsibilities [F]. NE is required by EU legislation to report on species conservation status in freshwaters, and to deliver this role it uses the JNCC CSM (2015) guidance [A]. Therefore, HIFI research allows NE to fulfil its legal requirement to report to UK and EU governments. NE’s Freshwater Fish and Fisheries Specialist states [F]:
“The provision of evidence for the suitability of the various monitoring protocols provided by HIFI has enabled Natural England to fulfill both their statutory and advisory roles when reporting to, and informing, the UK Government.”
The Scottish Fisheries Co-ordination Centre (SFCC) is an association of 23 Fisheries Trusts, the Scottish Government, Scottish Environment Protection Agency (SEPA) and Scottish Natural Heritage (SNH). It provides evidenced-based management of freshwater fisheries in Scotland. To standardise the collection of fisheries data by its members, the SFCC adopted a range of monitoring protocols including the ‘key underpinning research’ of Harvey and Cowx (2003) for lamprey monitoring [G]. The SFCC’s Manager and Senior Biologist (Forth Rivers Trust) / Chair states [H]:
“SFCC members follow these protocols adhering to UK standardized approaches to fisheries monitoring and assessment at the highest possible level for reporting under European Union (EU) Habitats Directive and Water Framework Directive (WFD). One such protocol adopted by SFCC, and its members, is the EU LIFE lamprey monitoring protocol (Harvey & Cowx, 2003) which was key underpinning research on lamprey for the Joint Nature Conservation Council (2015) Common Standards Monitoring Guidance for Freshwater Fauna… The protocol has been useful in Scotland in delivering compliance with the EU Habitats Directive and provides benefit to our members who are often required to quantify larval lamprey communities to ensure their protection during developments involving in-channel works. To our knowledge, it is the only widely accepted standard method available and we have found it very useful.”
In summary HIFI’s research on fish conservation species contributed significantly to the development of the JNCC CSM (2015) guidance and its subsequent successful application in the UK and Ireland by government conservation agencies. This application of HIFI’s research ensures the UK and Ireland use a robust, rigorous and standardised survey approach to meet reporting requirements for ‘conservation species’ for UK and EU governments.
2) The second strand of our impact arises from HIFI’s research for the UK Environment Agency, which developed a clear understanding of the water flow and level requirements needed for rivers to sustain coarse fish and ‘conservation fish’ species [4-5, 12]. The UK Technical Advisory Group (UKTAG) on the Water Framework Directive (WFD) makes recommendations to the UK and Republic of Ireland Governments on implementing the WFD. The UKTAG (December 2013) policy outlines a consistent method for designing appropriate flow regimes across the UK (and for flow regimes that also comply with the EU WFD). HIFI’s work was integral to the UKTAG (2013) policy: River Flow for Good Ecological Potential. This document [I] outlined recommendations “to help UKTAG’s member agencies design appropriate mitigation flow regimes for good ecological potential in heavily modified rivers”. The document [I] states:
“In developing guidance on the different flow building blocks, we have considered current scientific knowledge of the flows required: by fish species, including coarse fish, salmonids and lamprey” [the report cites: “Cowx et al. 2004, Noble et al., 2004, Cowx et al. 2012]. HIFI work is noted as providing “current scientific knowledge of the flows required by fish species” [I] (page 6, footnote 14).
The UKTAG (2013) report impacts upon organisations subject to the regulatory requirements of the EU WFD, namely UK and Republic of Ireland governments, water companies and water abstractors. An appropriate example is Yorkshire Water (YW), a major water company in England, that utilises the UKTAG (2013) policy to manage its water resources. YW also contract HIFI to help them to address their UK/EU regulatory and environmental targets better.
YW funded HIFI research to identify how flows and habitats associated with reservoirs can be managed more comprehensively to enhance fisheries and ensure the resilience of fish populations (despite increasing pressure for water resources) [6, 13]. HIFI’s research ensured that YW met regulatory requirements by improving 9.39 km of rivers for fish populations, thus avoiding statutory financial penalties to YW of over £1 million. The research also improved brown trout populations and habitat in these rivers. The impact also led to water savings of 57 million litres per annum, ensuring the increased resilience of water supply and savings to YW, and potential financial savings to YW customers [J]. Evidence of HIFI’s impact for YW is provided by their Environmental Assessment Manager who states [J]:
“In summary, HIFI’s research for YW has provided considerable impact by helping YW meet regulatory requirements while protecting the environment and providing water resources for the people and businesses of the Yorkshire region”.
5. Sources to corroborate the impact
A. Common Standards Monitoring Guidance for Freshwater Fauna (2015). Joint Nature Conservation Committee. http://data.jncc.gov.uk/data/9b80b827\-b44b\-4965\-be8e\-ff3b6cb39c8e/CSM\-FreshwaterFauna\-2015.pdf
B. Gallagher T., O’Gorman N.M., Rooney S.M., Coghlan B., and King J.J. (2019) National Programme: Habitats Directive and Red Data Book Species Summary Report 2017. Inland Fisheries Ireland. https://www.fisheriesireland.ie/extranet/fisheries-research-1/habitats/1581-habitats-directive-and-red-data-book-fish-species-summary-report-2017/file.html
C. Letter from Senior Research Officer at Inland Fisheries Ireland
D. Bull C., Perfect C. & Watt J. (2016) Site condition monitoring of lamprey in the Endrick Water SSSI and SAC 2012. Scottish Natural Heritage Commissioned Report No 911
E. Letter from Freshwater Adviser (Geodiversity Group) at NatureScot
F. Letter from Freshwater Fish and Fisheries Specialist at Natural England
G. Scottish Fisheries Co-ordination Centre (SFCC) Adopted Protocols (2019). https://www.sfcc.co.uk/resources/more-protocols.html and EU LIFE lamprey monitoring protocol” file://adir.hull.ac.uk/home/351/351036/Downloads/lamprey_monitoring[1].pdf
H. Joint letter from Manager and Chair/Senior Biologist (Forth Rivers Trust) at SFCC
I. UKTAG (2013) River flow for good ecological potential. Final recommendations. http://www.wfduk.org/sites/default/files/Media/Assessing%20the%20status%20of%20the%20water%20environment/UKTAG%20River%20Flow%20for%20GEP%20Final%2004122013.pdf
J. Letter from Environmental Assessment Manager at Yorkshire Water
- Submitting institution
- The University of Hull
- Unit of assessment
- 14 - Geography and Environmental Studies
- Summary impact type
- Environmental
- Is this case study continued from a case study submitted in 2014?
- No
1. Summary of the impact
The University of Hull’s flood hazard and risk research has informed UK national flood policy and has guided an investment of £2.6 billion of government funding between 2015 and 2020, resulting in improved flood protection for more than 300,000 homes nationwide.
The underpinning research has delivered an ongoing and deepening impact on UK flood policy through legislation in terms of the Water Act (2014), the Surface Water Management Action Plan (2018), the 25-year Environment Plan (2018) and the development of the Environment Agency’s new Flood and Coastal Erosion Risk Management Strategy (2020).
An international dimension has broadened the reach of the impact, with Kingston-upon-Hull being one of five cities selected as global exemplars of multi-agency adaptive approaches to living with water as part of the Rockefeller Foundation’s Resilient Cities programme. The underpinning research directly led to Hull being selected and has in turn shaped the development of the City Water Resilience Approach (CWRA), which is now being adopted and deployed by city administrations globally as the new international standard for city-level water resilience.
2. Underpinning research
This case study builds ongoing impact from a case study presented in REF2014 and describes extensive further, and new, impact on flood legislation and policy within the REF2021 period. The impact from the research has seen a combination of: our policy influence - which underpinned our REF2014 submission - being fully realised and implemented within the REF2021 period; a deepening of reach and significance through further impact on new policy and new legislative influence over the last six years within the UK; and, an extension of the reach and significance of the impact into the global context through the development of the City Water Resilience Approach (CWRA).
The underpinning research presented multi-factorial analysis of how the devastating 2007 summer floods across the UK developed so quickly and why the physical, institutional and regulatory structures designed to prevent flooding failed comprehensively. The research combined the insights of physical and human geographers (Thomas Coulthard, Lynne Frostick, Graham Haughton) to establish what went wrong in Hull in 2007, and how water management strategies and governance structures could be strengthened for future flooding events.
The research was designed to be policy-relevant and impact-driven, with key partnership working at its core. Following an approach by Hull City Council in July 2007, an Independent Review Body (IRB) was established by the Council to investigate the cause and effects of the June 2007 floods in Hull and the Humber. The IRB was led by University of Hull staff and chaired by Coulthard. It also included representatives from local authorities, water companies, community organisations and industrial and commercial organisations. The collaborative research involved 30+ interviews, panel meetings, reviews of literature and reports, and field and site visits. The interim findings (August 2007) and the final report (November 2007) were edited and led by Coulthard [3a, 3b, 3c]. Three key findings from these reports are directly cited within the Pitt Review [5b (NB: Section 5 below provides detailed page and paragraph references for the content that evidences the route to impact) ]. In turn, the Pitt Review has guided and directly informed UK flood policy for the past decade through the Flood and Water Management Act 2010, the Water Act 2014, and the 25-year Environment Plan 2018.
The summer 2007 floods had significant environmental and societal impacts across the UK. In addition to reviewing the physical impacts of the flooding and the response of flood infrastructure, the IRB reports also addressed the social and psychological impacts of flooding too. In Hull alone over 8600 houses and 1300 businesses flooded, with 90% of the city’s schools closed and many events cancelled. The reports concluded that, at the regional scale, the flooding was mainly caused by problems conveying rapid surface water through the drainage networks, along with the poor performance of three key pumping stations. The research detailed how the city drainage system functioned sub-optimally, causing much of the flood damage [3a, 3c]. The research was highly influential in terms of the technical outcomes it described. It was also impactful because it revealed a series of weaknesses in the governance and policy systems for managing drainage and flood response regionally but also, and crucially, at the national scale.
In summary, the research demonstrated that:
1) the UK had no robust warning system for localised pluvial flooding following heavy rain. The Environment Agency (EA) had established a warning system for fluvial flooding (due to increasing river flow) in 2000, but pluvial flooding was not addressed before 2007. The research exposed this oversight and proposed a suitable warning system for pluvial flooding, based on modelling rainfall patterns.
2) the ‘1 in 30-year event’ average usually used in UK urban flood planning is not appropriate in all regions, and especially not in low-lying regions with little natural drainage. In such regions, like Hull and the Humber, additional measures are required.
3) the structure of UK water governance (with local authorities, the EA and privatised water utility companies controlling separate parts of the system) left no single agency with overall responsibility for managing flooding. This dispersed management was also found to hinder the development of better flood-event responses [3c, 3d].
3. References to the research
a) Coulthard, T. and Frostick L. (2010) The Hull floods of 2007: implications for the governance and management of urban drainage systems, Journal of Flood Risk Management, 3, 223-231: https://doi.org/10.1111/j.1753-318X.2010.01072.x .
b) Coulthard, T., Frostick, L., Hardcastle, H., Jones, K., Rogers, D., Scott, M. and Bankoff, G. (2007) The 2007 floods in Hull. Final report by the Independent Review Body, 21 November 2007. Hull City Council, 68pp. https://zenodo.org/record/4454437#.YEqnwLYYBnJ
c) Coulthard, T., Frostick, L., Hardcastle, H., Jones, K., Rogers, D. and Scott, M. (2007) The 2007 floods in Hull. Interim report by the Independent Review Body, 24th August 2007. Hull City Council, 36pp. https://zenodo.org/record/4454422#.YEqno7YYBnJ.
d) Haughton, G., Bankoff, G., and Coulthard, T. (2015). In search of ‘lost’ knowledge and outsourced expertise in flood risk management. Transactions Institute of British Geographers, 40(3), 375-386: https://doi.org/10.1111/tran.12082
Underpinning research - grants awarded:
Coulthard, T. Haughton, G., and Bankoff, G. Rethinking the spaces and institutions for the governance of flood management. Funder: ESRC, Partner: Hull City Council (2008-11).
Haughton, G., Coulthard, T. and Bankoff, G. Flood Risk and Economic Development. Funder: ESRC, Partner: Environment Agency (2008-11).
Haughton, G., Coulthard, T. and Bankoff, G. Sub-Contracting Risk: Neoliberal Policy Agendas and the Changing Nature of Flood Risk Management. Funder: ESRC, Partner: Hull City Council (2008-11).
4. Details of the impact
Note: Section 5 (below) provides detailed and specific citation and page and paragraph locations for the relevant content and context within the supporting evidence.
The route to impact:
Research [3b] and [3c] and the three insights (highlighted at the end of Section 2) directly informed the findings of:
the House of Commons Select Committee on Environment, Food and Rural Affairs on the Summer 2007 floods (published 7 May 2008) [5a];
the highly influential 2008 Pitt Review (a Government Independent Review into the 2007 floods led by Sir Michael Pitt) and its Final Report [5b].
These reviews, and their recommendations, provided the route to impact from our 2007 research into the Hull floods. The policy impact was realised when our research findings were implemented in the Flood and Water Management Act 2010 and this policy impact underpinned our REF2014 case study. However, impact is only realised when policy shapes legislation and is implemented and the REF2021 period has seen this legislation embedded into the national approaches to flood management, in turn guiding ~£2.6bn in UK flood management funding between 2015 and 2020 [5c]. The REF2021 period has additionally seen impact delivered through new policy frameworks and the shaping of new national legislation including the Water Act 2014, the related Surface Water Management Action Plan 2018 [5d], and the 25-year Environment Plan 2018 [5c]. These documents contain significant policy drivers founded on our underpinning research and they have significantly improved flood prevention and mitigation measures across the country (~300,000 homes better protected **[5c]**). Further, beyond their impact on legislation, these documents also highlight the importance of physical and social resilience. The underpinning research changed the tone of UK debates about flood planning: it embedded cooperation and communication between communities, industry, civic agencies and government throughout the legislation cited. It helped flood planning to progress beyond technical analysis to also encompass wider aspects of the societies at risk [5c, 5d, 5e].
Impact in the REF2021 period:
During the REF2021 period, the research impact has enjoyed increasing reach and significance both nationally and internationally. The underpinning research has shaped policies and strategies for flood prevention and response, evidencing the full impact translation pathway of research into policy and subsequent implementation.
At the national scale, the Flood and Water Management Act 2010 gave the Environment Agency (EA) overall responsibility for all flooding, including surface water flooding. Part of this core recommendation from the underpinning research went into policy in the REF2014 period, but has been implemented fully in the REF2021 period. Local authorities now retain responsibility for the control of regional surface water drainage, but do so under the auspices of the EA [5c, 5d, 5f]. This change responded to the third recommendation of the underpinning research: that one lead agency should oversee flood events with multi-agency partnerships working together and collaborating on broader flood governance.
Second, the regional Surface Water Management Plans (SWMPs), which are now fully codified in the REF2021 period through the Water Act 2014, the related Surface Water Management Action Plan (2018) [5d], along with the 25-year Environment Plan (2018) [5c], have also been shaped by the call for connected governance and planning advocated by the University’s 2007 research and the subsequent Pitt Review. Hull was one of five areas to trial SWMPs, and Coulthard sat on the Steering Committee from 2014 to 2017. The SWMPs mandate planners, investors and developers to incorporate flood risk into their planning. This tranche of legislation prepares society for future flood events to a degree that was never required previously. The University’s research also recommended creating ‘Aqua Green’ sites in open public spaces, that would retain surplus surface water temporarily during flood events. Hull City Council has adopted these recommendations within the work of the Living with Water Partnership (see below). The use of natural flood management strategies like these are now also firmly embedded in the new EA National Flood and Coastal Erosion Risk Management Strategy (2020) [5f, 5g] and the 25-year Environment Plan (2018) [5c] :
“…Lead Local Flood Authorities (LLFAs) are now required to maintain a register of flood defence structures, including details of ownership and condition. The 2018 Surface Water Management Action Plan, which also has foundation in the University’s research, requires the Environment Agency to work with LLFAs and other expert bodies to develop best practice for local flood defence management.” Director of Flood and Coastal Risk Management (FCRM), EA [5g].
The University’s research recommendations have additionally shaped new UK flood policies and strategies in the REF2021 period through their incorporation into the development of the Environment Agency’s new National Flood and Coastal Erosion Risk Management Strategy for England (2020) [5f, 5g]. The EA Director of FCRM further states:
“…the University of Hull research has significantly impacted governance and inter-agency partnership working, as well leading to the adoption of a more integrated approach to flood risk management.” [5g].
In this review period, the research has also impacted international flood and resilience strategies through the development, and subsequent global deployment, of the City Water Resilience Approach (CWRA). This is part of the Resilient Cities Programme pioneered by the Rockefeller Foundation, with support from Arup, Resilience Shift, and the OECD [5e]. Launched in 2018, the CWRA [5e, 5h] is now the global standard for city-level water resilience. It promotes a methodology and framework that enables cities to diagnose their challenges related to water and deploy that knowledge to inform planning and investment decisions to better-prepare for, and respond to, shocks and stresses to their water systems. The University’s underpinning research was vital to Hull being chosen as one of only five founding cities for the programme (along with Amman, Cape Town, Mexico City and Greater Miami) [5h]:
“The University of Hull’s research into the 2007 Hull floods and the partnership working enabled by the research, created the governance and inter-agency working that lay the foundations that helped to support the case for why the city was selected as one of the Wave 1 cities for the development of the CWRA in 2015.”…
“Kingston-Upon-Hull’s specific water challenges… have been adopted into the establishment of qualitative and quantitative indicators to measure city water resilience embedded within the CWRA, for use in any city, anywhere.” Global Water Director, Arup [5h].
Hull’s participation in the CWRA project was facilitated by the creation of the Living with Water Partnership (LWW) [5i] between the Environment Agency, Yorkshire Water, Hull City Council and the East Riding of Yorkshire Council, with Professor Dan Parsons (Director of the Energy and Environment Institute) representing Hull University on the Partnership’s Executive Board. As part of this partnership, the University’s Energy and Environment Institute undertook a baseline city-wide investigation of flood risk, surveying >450 households to understand the impacts –physical, economic, or linked to health and wellbeing– of Hull’s 2007 and 2013 floods. It also explored concerns about future flood risk and how people hoped to protect themselves and their homes [5j]. This survey contributed to the development of the CWRA approach and has informed its global adoption [5i]. Without the multi-agency approach advocated by the University’s underpinning research, the CWRA would lack a robust, evidence-based framework for approaching water resilience on a multi-factorial, catchment-focussed basis:
“Hull was specifically selected as a Wave 1 City for the CWRA due the way in which research undertaken by the University into the 2007 floods had resulted in strong partnership working across the city.”
“The global rollout of the CWRA now underway through the Rockefeller Foundation, Arup and the OECD, and is seeing the learning from Hull’s experience of flooding, the implementation of aspects of Living with Water concerning flood resiliency now being adopted around the world.” Head of Resilience, Yorkshire Water, and Living with Water Programme Director [5i].*
The impact generated by the University’s flood research is considerable. Policy influence in REF2014 has translated into full implementation in the REF2021 period. New UK policy impacts have also resulted from the research and they have been adopted into legislation and have been implemented on the ground. The reach and significance of the impact has expanded and is now world-wide through its influence on the development of the Rockefeller CWRA and its ongoing deployment in cities across the globe such as Thessaloniki (Greece), Addis Ababa (Ethiopia), and Kigali (Rwanda).
5. Sources to corroborate the impact
(All available as pdfs on request.)
a) House of Commons EFRA Select Committee report (2008) Flooding : http://www.publications.parliament.uk/pa/cm200708/cmselect/cmenvfru/49/49.pdf
p11, p14-15: Lack of single agency with overall responsibility for managing flooding
p36: Underpinning research was taken into account in proceedings
p50: Coulthard cited as a witness.
b) Pitt, M. (2008) The Pitt Review: Lessons learned from the 2007 floods: Final Report
p33: p47-51, Recom. 5 p51, p168, p328: Lack of a robust pluvial flood warning system
p33: Recom. 2 p34: Lack of single agency with overall responsibility for flooding
p94: Lack of integrated flood plans, management systems and data sharing
p97, p101: Inappropriateness of ‘1 in 30-year’ standard of urban flood protection and need for risk-based approach
p97: Lack of adequate planning and the IRB’s role in exposing Yorkshire Water’s role
p111, p168, p129: Conceptual frames adopted by the Pitt Review from the IRB about ‘hard’ and ‘soft’ infrastructure, and ‘essential services’
p407-408: Importance of local scrutiny committees and the utility of the Hull IRB report by the Pitt Review
p408: IRB’s role in exposing the inadequate design, maintenance and operation of Hull’s flood-water pumping system
p408: Acknowledgements: the role of the underpinning research in shaping Pitt’s understanding of the 2007 floods.
c) A Green Future: Our 25 Year Plan to Improve the Environment, DEFRA (2018) https://assets.publishing.service.gov.uk/government/uploads/system/uploads/attachment_data/file/693158/25-year-environment-plan.pdf
p51: Statutory planning consultations
p52: Storage of water on open lands
p54: Lead Local Flood Authorities, water and sewerage companies, highways authorities and other risk management authorities work together.
d) Surface water management action plan, Defra (2018), with linkage to Water Act 2014 https://www.gov.uk/government/publications/surface-water-management-action-plan
p7, pp21-22 Box 6: Importance of multi-agency approach with clarity about responsibilities
p7, p.5; 1.17 p7: Coordinated action by all those with responsibilities for managing flooding
p8, pp26-30: Coordinated planning and action specifically in relation to surface water, to include water industry
p14: Improvements to surface water mapping and forecasting
p18: Need for resilience in infrastructures
p19 Box 4: Inappropriateness of ‘1 in 30-year’ standard of urban flood protection and need for risk-based approach
p19: Need for regulatory control to establish performance standards for water industry in relation to surface water and drainage
e) The City Water Resilience Approach (Arup) https://www.arup.com/-/media/arup/files/publications/c/cwra_city_water_resilience_approach.pdf
p57, p102, p110: Importance of multi-agency approach with clarity about responsibilities
p59: Need to incorporate resilience into water sources, networks and assets
p61: Promotion of diverse infrastructure for flood protection (i.e. hard and soft defences (e.g. aqua greens)).
f) Environment Agency (2020) National Flood and Coastal Erosion Risk Management Strategy for England https://assets.publishing.service.gov.uk/government/uploads/system/uploads/attachment_data/file/920944/023_15482_Environment_agency_digitalAW_Strategy.pdf
p74, Measure 2.1.5: Extending risk management planning to encompass more adaptive responses to increasingly extreme climate-change driven events
p87, Measures 2.7.1 and 2.7.2: Cooperation between flood agencies and water industry for long-term adaptive planning and surface water flood management
p105, Measures 3.3.1 and 3.3.3: Multi-agency approach to surface water flood resilience.
g) Impact evidence letter from Director, Flood and Coastal Risk Management, Environment Agency, highlighting how Hull University’s underpinning research has continued to shape flood risk policy in the UK, including natural flood management.
h) Impact evidence letter from Global Water Lead, Arup, highlighting how the underpinning research led to Hull being selected as one of five global cities in the CWRA programme.
i) Impact evidence letter from Director of Resilience, Yorkshire Water, highlighting how the underpinning research led to Hull being selected as one of five global cities in the CWRA and the role of the Living with Water Partnership.
j) Hull Household Flooding Survey (2018) Results, showing the data that informed elements of the CWRA: https://www.hull.ac.uk/editor-assets/docs/hull-household-flooding-survey.pdf