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Water environment, resilience and adaptation to change

Work Package 1.2 - Water resources and flood risk management

Research Deliverable 
1.2.3 Water environment resilience and adaption to change
Leading Ideas 
Climate and the Environment


The role of resilience is particularly crucial in managing the impacts of environmental changes (i.e. climate change, land use change) for example to prioritise mitigation measures to tackle greatest risks first. Aquatic ecosystems can experience multiple and interacting pressures and respond suddenly to environmental change, sometimes flipping to a new equilibrium. However, our understanding of resilience to environmental change is limited due to the difficulty in detecting ecological stability across pressure gradients at various spatio-temporal scales. Lack of knowledge on how key ecosystem functions relate to multiple stressors and drivers of change (notably climate & land use) therefore constrains effective resilience-based responses. This has implications for meeting current policy targets and prioritisation of adaptation actions to avoid future loss of function and service. Furthermore, regulatory measures have often been implemented in isolation rather than maximising potential synergies for maintaining resilient functioning ecosystems.

The need to evaluate resilience at national-level thus defines a high-level requirement to assess present and future risk and adaptive capacity for catchments across Scotland.

Aim of Research

To evaluate the capacity of water resources to adapt to changing environmental and socio-economic conditions, in order to maintain key functions, goods and services (resilience) 

This RD addresses one of the fundamental research questions of the programme: How resilient are Scotland’s natural assets to climate change and other risks (invasive non-native species (INNS), pollution, etc.), and what are the key interventions to make them more resilient or to protect them from further harm? To do this, RD 1.2.3 considers components of natural and managed water systems (and their interactions), their responses to multiple stressors, aspects of risk vs resilience and control measures. Using case studies, we explore (a) the concept of multiple stressors acting on a water body now and under future scenarios; (b) the provision of goods and services through the water environment; (c) natural resilience of the water environment that we can characterise and utilise in managing change. This natural resilience may be utilised as an alternative or complement to conventional management approaches. We may also need to manage this resilience with engineering (e.g. flood defence; water treatment) and accompany it with actions to enhance community resilience.

The research in RD 1.2.3 focusses on:

  1. Catchment typologies of risk and resilience to enable better understanding of grouped behaviours in waterbody sensitivities and responses to multiple stressors and how we may combine catchment spatial data in meaningful ways related to functions.
  2. Wastewater effluents in terms of ecosystem resilience to effluents, sustainable treatments for trace contaminants, and novel circular systems for wastewater treatment.
  3. Drinking waters, for example tracing presence and sources of key pathogen risks to drinking waters.
  4. River temperature and its impacts for aquatic ecology.


2019 / 2020
2019 / 2020

Work continued to evaluate approaches to help inform the mitigation and assessment of physical (river temperature), chemical (nutrients, emerging contaminants) and biological (parasites) water quality issues in the face of changing environmental conditions. The research has led to developments in representing catchment pollution sources (geese, septic tanks and farmyards), now being shared with SEPA and informing developing applied work (via CREW) and collaborations with international water management scientists (Nordic Centre of Excellence BIOWATER (link is external). The Tarland long-term monitoring data and mechanistic studies, both RESAS-funded, continue to provide a strong basis for developing international collaborations with other researchers on the phenomena of rising background P concentrations in headwater catchments.

Work on assessing novel approaches to treating wastewater continued through two strands.  Firstly, the constructed wetland (CW) under two flow regimes was assessed. The focus was to refine the model based on existing data from Yr3 to help evaluate the performance of the CW. The work suggested that the current sampling regime requires further refinement for reliable estimation of bed efficiency.  Secondly, experiments continued with the application of sustainable biosorbent column for emerging contaminant removal from waters.  The results showed the column can potentially remove a single compound as well as a mixture.

Another aspect of this RD is assessing and modelling river temperature dynamics.  Models simulating daily river temperature from weather and river flow have been implemented for 41 catchments across Scotland to quantify past changes in river temperature and identify their drivers. For one catchment (River Gairn) where the James Hutton Institute monitors high-resolution data, deep learning models of hourly river temperature using weather covariates have been developed.


  • Two talks based on Scottish case studies were given to the Land Use and Water Quality conference (link is external) (Aarhus, June 2019) exploring (i) long-term changes in water quality variables and their relationship with changing river flow and (ii) reasons for differing response groups by combining spatial data into a model of phosphorus loading.
  • Demonstration of issues of internal phosphorus loading from river sediments interacting with management are pooling insights from long-term water quality monitoring, channel dynamics and condition, chemical P release processes. At the 9th International Phosphorus workshop (link is external) (Zurich, July 2019) research into sediment P release (internal P loading, a cause of rising river phosphorus concentrations which lead to water quality deterioration in a Scottish research catchment) was presented.
  • Collaboration strengthened with applied research in Ireland. SEFARI researchers presented multiple aspects of RESAS-funded research at the Catchment Science 2019 conference (link is external) (Wexford, November 2019), including modelling of phosphorus sources and mitigation; the F-MAPT tool to enable placement of Flooding Measures, riparian management and water payment for ecosystem services and soil erosion work. Researchers are working closely with the Teagasc Institute (link is external) and the Irish EPA (link is external) in riparian and Natural Flood Management (NFM) allied research projects with mutual benefit for land and water outcomes.
2018 / 2019
2018 / 2019

Catchment typologies of risk and resilience, which will help to quantify, group and predict different responses were investigated further, including the development and application of novel methods ranging from laboratory experiments to modelling approaches. We also continued monitoring of environmental variables at different field sites allowing robust analysis of the water environment, its resilience and adaptation to change (e.g. biomass growth and nutrient concentration in the constructed wetland at Dinnet and river temperature in the Gairn catchment).

The research conducted this year has resulted in a range of important findings in the individual projects. For example, risk factors to chemical and ecological responses in waterbodies have been identified (e.g. in terms of septic tank risk profiles in river catchments and by DNA extraction of protozoan parasites). Laboratory experiments have been conducted to quantify the removal of contaminants (such as pharmaceuticals and heavy metals) by biosorbents. In addition, analysis of monitoring data has been combined with water balance modelling to enhance process-understanding in the constructed wetland at Dinnet. Further, process-based and statistical modelling has been combined with trend analysis to explore long-term changes in river temperature and its drivers using a 105-year citizen science river temperature record of the river Spey. A model has also been developed to investigate the temporal pattern of high-resolution river temperature data at the outlet of the river Gairn.


2017 / 2018
2017 / 2018

Collectively, work in the RD has progressed ways of looking at risk vs resilience in the translation of pressures on the environment through risk factors to chemical and ecological responses in waterbodies. This has involved some conceptual strengthening via our cases studies, namely: river ecosystem susceptibility to diffuse and point source pollution; management of effluents in closed loop wastewater systems; temperature related stress to stream ecology; the factor of riparian condition in alleviating or adding to risk of impaired water quality. Two further case studies are in earlier development stages: improving pesticide and pharmaceutical data for rivers for risk evaluation; improving drinking water safety planning for the water industry to manage risk.


  • Evidence dissemination: A talk was given at the Rank Prize Funds meeting at Grasmere in Cumbria in the Symposium on “Soil Organisms and Pollutants and their Consequences for Human Health”, The talk addressed how to assess the human health risks associated with the use of reclaimed water for irrigation of amenity land and food crops.
  • Catchment typologies approaches underpin developing SRP and CREW work and international collaborations: Research between RD1.2.2, 1.2.3 and CEH conceptualises how landscape structure, soils etc. underpin how waters respond to environmental pressures. This framework is being used in the CREW project Eco-P 2 project, SRP phosphorus modelling, a recent paper on alleviating eutrophication, international links with BIOWATER project and a session at the EGU conference, Vienna. A report was delivered to stakeholders (SEPA, SNH, Forest Research, Scottish Water, Marine Scotland, SG), following a workshop in spring 2017, establishing the needs and development pathway of these concepts and applications.
  • Records from the past century show that Scottish rivers are warming: Research in RD1.2.3 combined citizen science, through archived long-term records of water temperature taken by fisheries and estates, with high resolution scientific data and developed statistical methods to provide evidence that Scottish rivers are warming. A factsheet outlines river temperature changes and recommendations to make rivers more resilient to potential future warming.
2016 / 2017
2016 / 2017

We have been developing approaches for typologies of catchments as a way of grouping behaviours with respect to ways that waterbody sensitivity factors translate catchment risks (pollution pressures etc.) into impacts. This has been widely validated with stakeholders. The pressures and responses have been selected to serve the wider work and comprise: eutrophication impacts, temperature impacts on aquatic ecology and drinking water quality. As part of this, key datasets have been attained working alongside SEPA, for point sources, livestock number and sensitivity factors like riparian structure. New evidence provision has involved a package of work on effluents, septic tanks and larger wastewater sources, environmental tracing of effluents and novel control measures for effluents (working with Scottish Water) and river temperature effects.


  • New experiments started at the the constructed wetland at Dinnet. For this purpose, the existing vegetation has been harvested and locally available gravel has been chosen as standard material in the beds. It was decided to trial novel "add on" media in additional modules discrete from the main beds.
  • Structures to represent risk vs resilience in catchment systems are being developed within RD1.2.3 with links to developing risk modelling (for phosphorus) in RD1.2.2 and using expertise from CEH supporting waterbody ecological impacts. A Catchment Typologies of Risk and Resilience report has been delivered to stakeholders (SEPA, SNH, Forest Research, Scottish water, Marine Scotland, SG) who supported a workshop in spring 2017, establishing the needs and pathway of development.
  • WP staff met with representatives of the drinking water industry and regulators (Scottish Water, the Drinking Water Quality Regulator for Scotland, and SEPA) and agreed a pathway to integrate research on understanding, communicating and tackling risks to drinking water supply.

Future Activities

Experimental data of in-stream impacts associated with point source effluents against the very heterogeneous nature of background pollution sources in rural streams and rivers is being written up. Changes in phosphorus concentrations and explanatory mechanisms are also being written up using data from the Tarland research catchment. This involves data from spatial analysis of the river network denoting zones of channel sediment deposition and erosion, in-stream sediment release experiments and statistical evaluation of long-term water quality monitoring data.

Combining social science and biophysical expertise, we are examining the factors that have contributed to practical outcomes and scientific evidence for buffer strips. We are looking at how the combination of multiple stakeholders (regulatory, estate management, farm advisors and fisheries as practitioners, local communities and academics) has shaped outcomes on the ground.  

The development of novel treatment systems for effluents using combined column-leaching and plant-growth systems will be accelerated offering the opportunity to continue to test different flow regimes, bed media and plant combinations. The evaluation of the mass balance model using recent monitoring data from Dinnet (link is external) will continue. The model will also be applied to inform optimal system design.  To develop advances in treatments to remove emerging contaminants from wastewaters and increase resilience in receiving waters, further experiments will be run on the fixed column, particularly on further different mixtures, solution pH and organic matter which reflect the real effluent background.

Sources of zoonotic parasites from livestock and wildlife species will be identified by detection, speciation and genotyping of parasites in a second catchment. The results of this analysis and the risk from zoonotic parasites will be discussed with relevant stakeholders. 

River temperature research will continue in terms of application of the models at daily and hourly intervals. Daily river temperature under climate change scenarios will be modelled and potential changes in ecologically relevant river temperature thresholds will be assessed. The hourly river temperature model will be tested as a predictive tool in the Gairn and the Spey catchments.  

Selected Outputs