Supporting Citizen Science - Technical Advisory Framework
- National continuous projects
- Local studies
- Short-term monitoring activities
- Long-term monitoring programmes
- Activities requiring no previous knowledge or training
- Activities requiring specialist training and technical expertise
- Measuring environmental change
- Measuring societal change
- Mapping objects and features
- Collecting environmental observations
- Supporting scientific research and evidence gathering
- Build stronger relationships with communities and stakeholders.
- Increase understanding of local environmental issues.
- Support collaborative action.
- Provide additional environmental intelligence.
- Include appropriate quality assurance measures.
- Generate reliable information.
- Increase confidence in monitoring results.
- Provide data that can be used by the Environment Agency and other organisations to better understand the environment.
- Help inform environmental improvement actions.
- Participate in a one-off activity requiring no training or previous knowledge.
- Meet new people and become part of a community.
- Develop new skills and commit to regular participation.
- Further develop existing citizen science skills and experience.
- What information would you like to collect?
- Why is this information needed?
- Is citizen science the right approach?
- UK Environmental Observation Framework (UKEOF) Guide to Citizen Science
- UKCEH and SEPA: Choosing and Using Citizen Science
- Ten Principles of Citizen Science (European Citizen Science Association)
- Monitoring Guidance – River Restoration Centre
- UKEOF Unifying Principles for Environmental Monitoring
- Consistent monitoring
- Reliable monitoring
- Robust monitoring
- Accessible processes
- Useful outputs for volunteers and partners with different levels of experience and expertise
- Why monitoring and data collection are needed.
- Where monitoring should take place.
- When monitoring should take place.
- How monitoring should be carried out.
- How monitoring data can be used to maximise impact.
- Reduce
- Reuse
- Recycle
Connect and collaborate
Work in partnership to achieve common goals.Build on and learn from existing monitoring
Explore what, where and how others are monitoring in your local area to inform your monitoring plan.Define purpose
Clearly define the objectives and goals of your individual participation, planned citizen science initiative or monitoring programme.Develop a well-designed monitoring plan
Set an appropriate level and accuracy of monitoring design to meet project objectives.Follow quality control measures
Ensure all processes meet established standards of quality and include evidence of training, calibration and validation steps in the monitoring plan.Interpret and understand your findings
Explore the interactions between parameters measured to understand the health of your local waterbody.Communicate and share outcomes
Maximise the impact of your results by sharing outcomes in accessible, FAIR and visual ways with relevant stakeholders.Apply outputs to actions
Use the results to inform action and environmental improvement.- Connect and collaborate
- Build on and learn from existing monitoring
- Define purpose
- Develop a well-designed monitoring plan
- Follow quality control measures
- Interpret and understand your findings
- Communicate and share outcomes
- Apply outputs to actions
- Identify shared objectives.
- Work together through cooperative monitoring.
- Identify locations that would benefit most from monitoring.
- Better understand environmental pressures affecting a catchment.
- Informing site selection
- Providing reference conditions
- Providing complementary and background data
- Providing baseline information
- Continuous monitoring sondes measuring water quality
- Mud Spotter surveys during wet weather
- Sediment fingerprinting to trace sediment sources
- Testing of emerging chemicals
- Before and after restoration habitat surveys using MoRPh
- Flow monitoring
- Water vole population monitoring
- Extensive Riverfly surveys
- Breeding birds
- Butterflies
- Plants
- Volunteer flow monitoring is plugged into Environment Agency databases and directly used by hydrometry teams to fill spatial and temporal gaps.
- Geomorphology teams are advising on sediment fingerprinting and feeding results into restoration plans and fisheries work.
- Riverfly data is providing greater understanding of where populations of invertebrates occur across catchments, including invasive species.
- The skills, motivation, accessibility needs and level of commitment of volunteers and the local community.
- Recruitment, recognition and retention of volunteers.
- Realistic timescales that allow for contingency planning and account for funding restrictions.
- Short time frame, low effort
- Short time frame, high effort
- Longer time frame, low effort
- Longer time frame, high effort
- Cost
- Time
- Skills development
- Data quality
- Data quantity
- Higher costs
- More training
- Greater quality assurance
- More robust monitoring methods
- Technical programme design
- Logistical support for sample transport
- Laboratory analysis of samples
- Data interpretation
- Recruited volunteers
- Organised volunteers
- Managed citizen scientist involvement
- Locations should be safe and accessible for all citizen scientists.
- Consider the time, commitment and training needs of volunteers.
- Can existing datasets supplement your proposed monitoring?
- Can they help inform sampling locations?
- Permission must be obtained to access the site.
- Sites should be representative and appropriate to meet project objectives.
- Some initiatives, such as Riverfly, require liaison with citizen science coordinators or Environment Agency contacts to agree sampling locations and thresholds.
- The Environment Agency recommends sampling from 10 river widths downstream of a suspected pollution source to avoid the mixing zone and collect a representative sample.
- Health and safety guidance should be established and followed.
- This should include volunteer training, safe and legal access to sites and a record of compliance.
- Volunteer management and health and safety compliance should be managed by the lead organisation, which holds the duty of care for volunteers.
- Water safety training
- Provision of Personal Protective Equipment (PPE)
- Time requirements
- Commitment levels
- Training requirements
- Monitoring frequency
- Monitoring duration
- Cost of equipment
- Cost of data analysis
- River height
- Flood warnings
- Weather conditions
- Tidal cycles
- Seasonal variation
- Invertebrate diversity
- Ephemeral streams
- Intermittent streams
- Freshwater springs and sources
- Who visits these sites
- How visitor patterns vary over time
- Water quality observations
- Potential signs of pollution
- Tier 0 may include observations, photographs and anecdotal information which can provide useful additional information in locations where monitoring is not currently undertaken and requires no specific training or equipment.
- Tier 2 or Tier 3 monitoring programmes may include varying levels of quality assurance, from calibrated and quality-controlled field samples to laboratory analysed bathing water data. Depending on the level of quality control, these data may complement Environment Agency data, providing valuable information in locations and at times outside statutory monitoring programmes.
- Biological monitoring
- Water quality monitoring
- Physical monitoring
- Soil monitoring
- Severn Rivers Trust (lead partner)
- Severn Trent Water
- The Rivers Trust
- Citizen science volunteers
- Potential sources of pollution
- Method reliability
- Equipment performance
- Catchment-scale water quality patterns
- Trustworthiness
- Credibility
- Value
- Potential use of the data
- Quality
- Accuracy
- Reliability
- Repeatability
- Processes for training new volunteers.
- Refresher training for existing volunteers.
- Comparison and cross-referencing of equipment.
- Procedures for checking, maintaining and calibrating equipment.
- Procedures for checking and cleaning datasets.
- Error identification and correction processes.
- Sample replication and verification.
- Blind sampling checks.
- Random sampling checks.
- Errors in site locations.
- Incorrect grid references.
- Anomalous results.
- Unexpected trends.
- Data entry mistakes.
- Does the kit or instrument have quality certification?
- What is the principle of operation?
- Is the methodology accepted by recognised accreditation bodies in Europe or North America?
- Are reagents required?
- Are reagents safe for volunteers or children to handle?
- How frequently does the equipment require calibration?
- What maintenance requirements exist?
- What are the lower and upper limits of detection?
- What level of precision and accuracy is provided?
- What resolution is offered?
- Is the equipment robust and suitable for field conditions?
- Is the equipment cost-effective?
- Do not leave blanks. Create a consistent format to identify whether a sample was attempted but no data were collected.
- For example, adding a separate tick box for "No Sample Possible" with a notes field explaining why is good practice.
- A second tick box for "Site Dry" may be useful in drought-prone areas.
- Do not use zeros to represent "no sample taken". Zeros should only be used to represent genuine results.
- Check whether your zero values are genuine measurements.
- Understanding the lower detection limits of your equipment will help determine this.
- For example, some equipment may be accurate only to ±0.04 (or 5% for higher readings), so a recorded value of zero may actually mean ≤0.04.
- Be consistent when naming sites.
- If a site location changes, use a new site name.
- If a site location name is updated with more accurate information, update all instances of that location.
- Apps often record the phone's GPS location and may create a new location record for each sample.
- Consider how your survey is configured to avoid creating multiple site references for the same monitoring site.
- Alternatively, create fixed site names and assign the same National Grid Reference to all records from that location.
- Must be unique.
- Must follow a consistent naming format.
- Should not mix formats such as A, B, C and 1, 2, 3 or 1A, 1B, 1C.
- Use 0001 to 0099 moving downstream.
- Use 0100 to 0199 for the first tributary.
- Continue this structure for additional tributaries.
- Special characters
- Punctuation
- Brackets
- Colourless phosphate and ammonia standard solutions were supplied by The Rivers Trust through a commercial partner.
- Solutions were divided into labelled tubes that identified solution type but not concentration.
- Citizen scientists from the Wensum, Lark, Cam and Waveney catchments tested these control samples using their standard monitoring procedures.
- Results were returned to a designated Quality Assurance Lead.
- A subset of samples was independently analysed by the Environment Agency laboratory for verification.
- Handheld photometers remained broadly accurate for phosphate testing.
- Ammoniacal nitrogen testing could still clearly identify potentially acutely toxic concentrations.
- Low battery levels affected photometer accuracy.
- Temperature variations during transport and storage influenced results because lower temperatures slow reaction rates.
- Equipment condition
- Monitoring procedures
- Sampling technique
- Replacing handheld photometer batteries regularly.
- Standardising monitoring techniques, particularly for ammonia testing where guidance does not clearly define reagent mixing procedures.
- Controlling temperature during transport and storage wherever possible.
- Apps may contain built-in validation checks that help reduce recording errors.
- Smartphones contain built-in GPS with an average accuracy of less than 50 metres.
- Requires access to smartphones or IT equipment.
- Phone signal or Wi-Fi may not always be available.
- Battery life can be a limitation.
- Requires a level of digital literacy and confidence.
- Your own monitoring results
- Data collected by others
- Existing environmental datasets
- Graphs
- Charts
- Maps
- Between sites
- Within sites
- Across catchments
- General Water Quality Parameter Interactions (supplementary information)
- Template for Site-Specific Water Quality Interactions (Appendix 3)
- Raw data
- Visual outputs
- Maps
- Dashboards
- Graphs
- Reports
- What data have been collected
- Where data were collected
- Trends and patterns in results
- Relationships between different datasets
- Other citizen science datasets
- Environment Agency open data
- Data from partner organisations
- How data were collected.
- Where data were collected.
- How often monitoring was carried out.
- Who collected the data.
- Methods used.
- Equipment used.
- Quality assurance processes in place (see Principle 5).
- Data
- Expertise
- Decision making
- General Data Protection Regulation (GDPR)
- Data Protection legislation
- Stored securely
- Protected appropriately
- Not made publicly available unless permitted
- Agreements with landowners
- Other restrictions on publishing data
- Concerns about publishing findings without appropriate context
- Stored
- Found
- Accessed
- Reused
- Inform your Catchment Partnership about what data you are collecting.
- Inform them where data are stored.
- Provide metadata and supporting information.
- People
- Computers
- Ensure metadata accompany your datasets.
- Follow good data governance principles.
- How to access it
- Any authentication requirements
- Any permissions needed
- Combined with other datasets
- Analysed using different software tools
- Incorporated into workflows and visualisation platforms
- Metadata should be comprehensive.
- Data should be clearly described.
- Methods should be documented.
- Others should be able to replicate or combine the work.
- Future sampling locations.
- Additional parameters to monitor.
- New monitoring methods.
- Improved understanding of environmental pressures.
- Future environmental investigations.
- The Environment Agency
- Water companies
- Catchment partnerships
- Rivers Trusts
- Local authorities
- Other environmental stakeholders
- Additional monitoring locations.
- More frequent observations.
- Greater community involvement.
- How data were collected.
- What quality assurance procedures were followed.
- What quality control measures were applied.
- The confidence that can be placed in the data.
- Hydrology
- Geology
- Biology
- Chemistry
- Physical habitat
- Lowland: < 80 metres
- Upland: > 80 metres
- High Alkalinity: > 50 mg/L CaCO₃
- Low Alkalinity: < 50 mg/L CaCO₃
- Ammonia (NH₃)
- Ammonium (NH₄⁺)
- Decomposition of organic matter
- Excretion from animals
- Raw sewage
- Agricultural run-off (fertilisers and excretion from livestock)
- Industrial processes
- Lowland: < 80 metres altitude
- Upland: > 80 metres altitude
- High Alkalinity: > 50 mg/L CaCO₃
- Low Alkalinity: < 50 mg/L CaCO₃
- pH describes how acidic or alkaline a waterbody is.
- pH > 7 is alkaline.
- pH < 7 is acidic.
- Background pH is dependent on local geology.
- Extreme pH can cause ecological problems due to encouraging the formation of toxic ammonia (see ammoniacal nitrogen).
- Photosynthesis removes dissolved CO₂ from the water and leads to an increased pH.
- Water temperature generally changes with prevailing atmospheric temperature.
- Temperature has a fundamental influence on aquatic organisms, ecological processes and the potency of pollutants.
- The ability of water to hold dissolved oxygen decreases as water temperature increases.
- Therefore, daily and seasonal patterns are observed.
- Abrupt temperature changes can indicate inputs into a waterbody.
- For example, rainfall events or effluent discharges may alter river temperature.
- Conductivity measures the total salts dissolved in water through its ability to conduct an electric current.
- Background conductivity varies depending on local geology.
- Baseline values can range from 100 to 2000 µS/cm.
- Upland streams generally have lower conductivity values.
- Lowland streams generally have higher conductivity values because rivers receive minerals from larger catchment areas.
- Rainfall
- Industrial effluent
- Sewage effluent
- Road runoff
- Winter gritting runoff
- Dissolved oxygen concentration measures the amount of oxygen dissolved in water and is expressed in mg/L.
- Dissolved oxygen is essential for aquatic life.
- Waterbodies receive oxygen through atmospheric diffusion and photosynthesis by aquatic plants.
- River turbulence increases oxygen diffusion.
- Turbulence is common in mountainous rivers and lowland rivers following rainfall events.
- Decrease as temperature increases.
- Are generally lower during summer.
- Bacteria use oxygen as they break down pollutants.
- Less oxygen becomes available for aquatic organisms.
- Dissolved oxygen saturation measures the amount of dissolved oxygen compared with the maximum amount of oxygen that could be dissolved at a particular temperature and pressure.
- Results are expressed as a percentage.
- 70% dissolved oxygen saturation is considered good.
- <20% dissolved oxygen saturation is considered poor.
- Nitrate (NO₃⁻) is an essential nutrient for aquatic organisms.
- Excessive nitrate from agricultural runoff and sewage effluent can damage river ecology.
- In the presence of sufficient dissolved oxygen, bacteria can convert ammoniacal nitrogen into nitrate.
- Algal blooms
- Reduced dissolved oxygen concentrations
- Ammoniacal Nitrogen is a combined measure of two dissolved nitrogen forms:
- Ammonia (NH₃)
- Ammonium (NH₄⁺)
- pH
- Temperature
- The proportion of ammonia (NH₃) increases.
- Less than 10% of total ammonia occurs as toxic NH₃ when pH is below 8.0.
- Ammoniacal nitrogen can become increasingly toxic to fish and aquatic organisms.
- Livestock waste
- Sewage
- Organic matter decomposition
- Agricultural fertilisers
- Bacteria consume dissolved oxygen to break them down.
- Less oxygen remains available for aquatic life.
- Orthophosphate, also known as dissolved phosphate, is the bioavailable form of phosphorus.
- In small concentrations it is essential for healthy freshwater ecosystems.
- Dissolved phosphate is required for plant and algal growth.
- Fertilisers
- Sewage discharges
- Eutrophication
- Excessive algal growth
- Reduced dissolved oxygen concentrations
- The Rivers Trust
- CaSTCo partners
- The Riverfly Partnership
- Earthwatch
- SmartRivers
- Citizen scientists
- Water stakeholders who provided advice and suggestions
Introduction
Supporting Citizen Science
Technical Advisory Framework
Version 1, March 2025
Introduction
The Environment Agency is working with partners to develop tools, guidance and frameworks to support a standardised and connected approach to citizen science monitoring of the water environment.
This Technical Advisory Framework has been co-produced with the citizen science community and has been designed to help individuals and groups develop new, or review existing, citizen science monitoring programmes that meet their needs.
Version 1 of the framework focuses primarily on water quality and quantity, with an emphasis on freshwater environments (rivers and lakes). Additional information relating to estuarine and coastal waters will be included in Version 2.
What is the Purpose of Citizen Science?
Citizen science involves public participation and collaboration in all aspects of scientific research. It can be adapted and applied to a wide variety of environmental situations and disciplines.
Citizen science can operate:
Across Different Scales
With Different Skills Requirements
To Achieve a Wide Range of Aims
Why is this Framework Needed?
No single organisation is responsible for collecting all the data needed to protect and manage the environment effectively.
Understanding the environment and informing action requires the combination of many sources of information and observations. Citizen science provides a valuable opportunity for the Environment Agency (EA) to engage communities in scientific research, environmental monitoring and local decision-making.
Citizen science can help:
Participation in citizen science and public interest in improving local environments continues to grow.
This increase in participation is both encouraging and inspiring. However, with limited resources, the Environment Agency cannot support every initiative or use every dataset collected by citizen scientists. Decisions therefore need to be made on a case-by-case basis.
This framework, together with the Environment Agency's advisory role, aims to support well-designed citizen science monitoring initiatives that:
How to Use This Framework
This framework is divided into eight key principles which form a structured approach to guide volunteers, coordinators and stakeholders through the process of planning, conducting and using citizen science monitoring projects. It outlines the steps needed to ensure that the data collected is consistent, high quality and meaningful.
We recommend working through the key principles in this framework with your catchment partnership, citizen science community or other local partners to benefit from their collective knowledge, experience and skills.
This framework should be used as a monitoring pathway and continuously revisited and reviewed. By following these principles, and using the linked guidance and information within, citizen science initiatives can become more meaningful and useful for both participants and stakeholders.
Given the wide range of motivations for participating in citizen science, the framework does not recommend specific equipment, methodologies or initiatives. The framework will be updated over time to reflect changes in understanding, priorities and advances in monitoring technology and methodology, with continued engagement from the citizen science community.
Where to Start: Understanding the Purpose and the Outcome
The first four principles of this framework are designed to help you plan your monitoring activity.
Before you begin, think about what you want to achieve through citizen science. For example:
If you are a volunteer coordinator, community group leader or stakeholder planning a citizen science initiative, consider:
Guidance from Other Organisations
Once you have established what you want to achieve, you can work through the framework to plan an effective approach and develop a collaborative monitoring plan.
Developing a Collaborative Monitoring Plan
The eight principles of this framework have been developed and informed by existing guidance on environmental monitoring and planning, including:
Each principle provides support and direction to help develop a well-structured collaborative monitoring plan that delivers:
Collaborative Monitoring Plans
The Catchment Systems Thinking Cooperative (CaSTCo) has produced guidance and templates to support the development of collaborative monitoring plans.
The guidance from CaSTCo and the eight principles encourage you to consider:
Before Developing Your Plan
Consider the following:
Biosecurity
Follow biosecurity measures to minimise and prevent the spread of Invasive Non-Native Species (INNS), including the Check, Clean, Dry protocol.
Sustainable Use of Equipment and Consumables
Ensure the safe use and disposal of reagents and consumables while following the waste hierarchy:
Key Principles for Citizen Science Monitoring
What are the principles and why is it important to consider them?
By following these principles, you'll ensure that your monitoring efforts are not only scientifically robust but also meaningful and impactful for your community and the broader scientific community. Each principle in this pathway helps you navigate the complexities of citizen science monitoring, from connecting with local partners to sharing findings in accessible and engaging ways.
The Eight Principles
Citizen Science Monitoring Pathway
The framework is designed as a continuous cycle:
The outputs and learning from each stage should help inform future monitoring and continuous improvement.
1. Connect and Collaborate
1. Connect and Collaborate
Work in partnership to achieve common goals.
Why is this important?
Citizen science involves collaborating with and learning from others, including local environmental groups, catchment partnerships and other citizen science projects. Identifying and connecting with local stakeholders can help you:
Citizen science initiatives should be led by the organisation best suited to deliver them. This is not always the Environment Agency. Although the Environment Agency often provides funding support and technical expertise, it aims wherever possible to work with and through partners.
How can I find out more?
Find your catchment
Get in touch with your local Catchment Partnership
Collaborate with academic institutions
Contact your local university to find out about current and future projects, research opportunities and potential areas for collaboration.
2. Build on and Learn from Existing Monitoring
2. Build on and Learn from Existing Monitoring
Explore what, where and how others are monitoring in your local area to inform your monitoring plan.
Why is this important?
Finding out where and what others monitor can help you to understand what data is already available that you can benefit from, as well as identify gaps or opportunities to complement these data and prioritise monitoring methods and locations.
How can I find out more?
We recommend getting in touch with your local catchment partnership to find out what citizen science and environmental monitoring may already be happening in your local area.
Useful Links
Home – Catchment Based Approach (CaBA)
https://catchmentbasedapproach.org/
Catchment Partnership Pages | Catchment Data Explorer
https://environment.data.gov.uk/catchment-planning/v/c3-plan/CatchmentPartnerships
Explore what and where the Environment Agency monitor
The Environment Agency’s environmental monitoring data is open to the public and accessible through the Defra data portal and signposted through the Environment Agency’s Water Hub.
Site locations and results can be visualised on the River Basin Management Plan maps.
Data within each explorer is also accessible through Application Programming Interfaces (APIs), a programming language which provides access to the raw data visualised in these applications.
Watch this video to find out more:
What is an API?
https://www.youtube.com/watch?v=Hj1M6wH7WIM
Data Access Resources
Defra Data Services Platform
https://environment.data.gov.uk/
Water Data Explorer
https://engageenvironmentagency.uk.engagementhq.com/data-publications-water
River Basin Management Plan: Maps
https://experience.arcgis.com/experience/73ed24b6d30441648f24f043e75ebed2/page/Introduction/
Environment Agency data can support your monitoring plan by:
Further information on what the Environment Agency monitors, tools to access and interpret this data, and links to useful plans and reports are outlined in Table 2.
Explore data from others which may be useful
Box 1. Case Study: Smarter Waters – River Chess (Tier 2)
The River Chess Smarter Water Catchment project has used a series of complementary monitoring techniques to understand the issues and monitor actions to restore this chalk stream catchment.
The project has involved partners from statutory agencies, non-governmental organisations, water companies and academic institutions, with an emphasis on working with communities and citizen science throughout.
Monitoring has included:
Using a combination of techniques from both citizen scientists and science professionals has enabled a greater depth of understanding both spatially and over time, increasing confidence in where investment is needed to improve river condition.
This work has been run alongside the Tracking the Impact project which focuses on terrestrial species within the catchment, including:
Recognising the importance of the surrounding landscape as part of the whole catchment ecosystem.
How are we using this information?
The discovery of the winterbourne stonefly by Riverfly volunteers at the top of the River Chess helped drive the Environment Agency’s intermittent stream monitoring programme across chalk catchments.
Further Information
Citizen Science | River Chess Catchment | Smarter Water Catchment
https://chesssmarterwatercatchment.org/citizen-science/
Chiltern Chalk Stream Project | The Ripple Effect
https://www.youtube.com/watch?v=YDbWg2DulXk
Mud Spotter
https://modularriversurvey.org/mud-spotter/
Tracking the Impact Project
https://www.chilterns.org.uk/flagship-projects/tracking-the-impact/
Table 1: Examples of Freshwater and Coastal Citizen Science Monitoring Programmes and National Monitoring Blitzes in England
| Monitoring Initiative | Lead Organisation | Water Type | Duration of Monitoring | Link |
|---|---|---|---|---|
| Riverfly Monitoring Initiative (RMI) | Riverfly Partnership | Freshwater | Regular monitoring (weekly/monthly) | https://riverflydata.org/ |
| SmartRivers | WildFish | Freshwater | Spring and Autumn | https://wildfish.org/project/smart-rivers/ |
| FreshWater Watch | Earthwatch | Freshwater | Regular monitoring (weekly/monthly) | https://www.freshwaterwatch.org/pages/explore-our-data |
| Angling Trust Water Quality Monitoring Network | Angling Trust | Freshwater | Regular monitoring (weekly/monthly) | https://five.epicollect.net/project/water-quality-monitoring-network/data |
| MoRPh Rivers | Modular River Survey | Freshwater Habitat | Occasional | https://modularriversurvey.org/morph-rivers/ |
| Surfers Against Sewage Recreational Water Quality | Surfers Against Sewage | Recreational Waters (Coastal and Inland) | Regular monitoring (weekly/monthly) | https://datahq.sas.org.uk/citizen-science-data-hq/citizen-science-results/ |
| Big Seaweed Search | Natural History Museum | Marine/Coastal | Occasional | https://www.nhm.ac.uk/take-part/monitor-and-encourage-nature/big-seaweed-search.html |
| Shoresearch | The Wildlife Trusts | Marine/Coastal | Occasional | https://www.wildlifetrusts.org/shoresearch |
| The Big River Watch | The Rivers Trust | Freshwater | Spring and Autumn WaterBlitz over a weekend | https://theriverstrust.org/big-river-watch-data-dashboard |
| Great UK WaterBlitz | Earthwatch | Freshwater | Spring and Autumn WaterBlitz over a weekend | https://www.freshwaterwatch.org/pages/great-uk-waterblitz-results |
Table 2: Examples of Open Access Environment Agency Monitoring Data, Reports and Plans
| Type of Data | What it Covers | How it can be Viewed | Where to Access this Information | Parameters / Indices Measured or Category of Data Available | Further Information |
|---|---|---|---|---|---|
| Macroinverte | Datasets of benthic macroinvertebrates, macrophytes (aquatic plants), and fish from surveys for river and tidal freshwaters. Includes species lists, abundances, biotic indices and site data. | Viewed online and/or bulk downloaded | Ecology & Fish Data Explorer | ASPT, BMWP, WHPT, RMNI, individual taxa records Rivers (uktag): Invertebrates, macrophytes, fish Lakes (uktag): Macrophytes | The different types of fish monitoring – Creating a better place Find out what we discovered on one of our freshwater plant surveys A day in the life – plant surveying on the River Mimram – Creating a better place How to use data explorer |
| Hydrometric Data | River levels and flow, rainfall, groundwater and continuous water quality measurements (sondes). | Viewed online and/or bulk downloaded | Hydrology Data Explorer | River level, groundwater level, daily mean river flow, daily rainfall, dissolved oxygen (% saturation), temperature, long-term flow records | Making river, rainfall and groundwater data available |
| River Habitat | River Habitat Survey data on the physical character and quality of river habitats. | Download required to view data | Channel form, bankside vegetation, weirs, sluices, culverts, outfalls, dams, abstractions, HQA, HMS | ||
| Water Quality | Water quality measurements (physico-chemical and specific pollutants) analysed in laboratories from sampling points across the country. | Viewed online and/or bulk downloaded | Explore sites Download data | Ammonia, ammonium, dissolved oxygen saturation, conductivity, orthophosphate, pH, temperature, turbidity, metals, inorganic and organic chemicals | What is a chemistry sample and why does the Environment Agency do them? – Creating a better place |
| Marine Plans | Marine planning information for England including licences, designations and regional marine plans. | Viewed online | Explore Marine Plans | Marine licences, species data, protected areas, aquaculture, fish habitat, ports, harbours, shipping and recreation | Marine Plans guidance video. |
| Bathing Waters | Designated bathing water site information and monitoring results. Water quality assessed by the Environment Agency from May to September. | Viewed online and/or bulk downloaded | Find a bathing water Bathing data | Escherichia coli (E. coli), Intestinal Enterococci (IE) | How the Environment Agency monitors and tests bathing water quality – Creating a better place How does the Environment Agency check bathing water quality? Bathing water quality glossary Bathing Water Quality |
| Geographic Information | Interactive mapping of environmental information across Great Britain covering rural, urban, coastal and marine environments. | Viewed online and downloadable | MAGIC Map Application | Protected sites, designations, landscape classification, habitat classification, geology, soils, administrative boundaries, access information and mapping layers | MAGIC Help |
| Agricultural Land Environmental Risk and Opportunity Tool (ALERT) | Online Earth Observation mapping system developed by the Environment Agency and Catchment Sensitive Farming to support targeting interventions which reduce agricultural pollution. | Viewed online | ALERT Map | Hydrology layers, land use and soils, slope thresholds, LiDAR topography, satellite imagery, urban and road layers | ALERT support resources |
| Catchment Data Explorer | Information used in River Basin Management Plans including Water Framework Directive classifications, objectives and measures. | Viewed online and/or bulk downloaded | Catchment Data Explorer | River Basin Management Plans, classifications, surface water chemical classifications, objectives, predicted outcomes, challenges, protected areas and chemical status | Water body data update August 2023 – Creating a better place |
| Shoreline Management Plans | Plans identifying the most sustainable approach for managing coastal flooding and erosion over short, medium and long timescales. | Reports and plans downloadable | Shoreline management plans | Shoreline change evidence, flooding and erosion risks, impacts on people, heritage and the natural environment | The coast is clear: strengthening shoreline management planning – Creating a better place |
3. Define Purpose
3. Define Purpose
Clearly define the objectives and goals of your individual participation, planned citizen science initiative or monitoring programme.
Why is this important?
To maximise the impact of your monitoring, you should be outcome-driven. Setting clear and realistic project objectives, agreed by all those involved, will help direct your monitoring plan and ensure the data collected is relevant and impactful.
When considering the intended outcomes for your project, consider:
Figure 1: Balance Between Investment in Time and Effort
Projects can vary significantly in the balance between effort and duration:
For example, a WaterBlitz event may involve a short timeframe and relatively low investment, whereas a comprehensive monitoring programme such as the River Chess case study requires substantial investment in equipment, training and long-term commitment.
A Four-Tier Approach to Citizen Science Monitoring
In collaboration with CaSTCo and environmental non-government organisations (eNGOs), a four-tier approach has been developed to help categorise monitoring activities and identify the methods and initiatives most suitable for different project objectives.
This approach encourages groups to consider:
Deciding on an appropriate tier at the start of project planning can help inform the monitoring plan and provide clarity when working through the rest of the framework.
Data and information from all tiers are valuable and contribute to a wider understanding of environmental health and catchment management.
Tier Structure
| Tier | Description |
|---|---|
| Tier 0 | Mass participation, observational monitoring |
| Tier 1 | High-density, indicative methods |
| Tier 2 | Targeted advanced monitoring |
| Tier 3 | High precision monitoring |
Increasing tiers generally involve:
Participation levels and spatial/temporal coverage tend to decrease as monitoring becomes more specialised.
How Can I Find Out More?
Setting Your Primary Purpose
Guidance: Defining Your Primary Monitoring Purpose (CaSTCo)
https://castco.org/knowledge-base/monitoring-purpose/
Defining Objectives and Environmental Questions
Defining Your Purpose (CaSTCo)
https://castco.org/knowledge-base/defining-your-purpose/
Setting Biodiversity Monitoring Objectives (JNCC Resource Hub)
https://hub.jncc.gov.uk/assets/f592f2bc-ab02-4acd-a615-90d5fe9c9069
Measuring Project Impact
Measuring Impact of Citizen Science – Indicators
https://about.mics.tools/indicators
Making a Difference (CaSTCo)
https://castco.org/knowledge-base/making-a-difference/
Designing a WaterBlitz
If your project involves running a WaterBlitz event such as The Big River Watch:
The Big River Watch
https://theriverstrust.org/take-action/the-big-river-watch
Guidance: Designing a WaterBlitz (CaSTCo)
https://castco.org/knowledge-base/river-blitz/
RiverBlitz Review – Ribble Rivers Trust
https://www.youtube.com/watch?v=UcwF09NQFhs
Table 3: Description and Examples of Tiers of Citizen Science Monitoring
The activities within this table are generally characterised against the different monitoring tiers, although future activities may not fit neatly within a single tier.
| Tier | Description | Purpose | Bathing Water Investigations examples | Water Quality / Nutrient Testing examples | Biodiversity Monitoring examples | Water Quantity examples |
|---|---|---|---|---|---|---|
| 0 | High-density, low-resolution data, limited or no training, previous experience or equipment required, flexible location and timing. Basic data quality control measures in place. | Broad-scale water surveillance, capturing seasonal snapshots of water quality through mass sampling. Includes anecdotal records and monitoring in response to weather events. Useful for engagement and education. | Observation of bather numbers and weather conditions. Observations of signs of pollution. Example: Hello Lamp Post | Observation of water colour, signs of run-off, surface drainage, outfall pipes discharging sediment into the water. Example: The Big River Watch | Incidental or anecdotal records of wildlife on, in or around the water. Angling match-catch records, or records of invasive non-native species. Example: Invasive Non Native Species Mapper | Observations of barriers to river flow. Basic reporting of river flow as part of wider engagement initiatives such as The Big River Watch. Example: River Obstacles |
| 1 | Planned and delivered through a lead environmental Non-Government Organisation or academic partner, including volunteer recruitment and management. Basic monitoring equipment used with spatial or temporal focus. Training provided in person or online. | Short-term, high spatial scale or long-term regular catchment monitoring of pollution indicators and environmental pressures. Collects high-density, moderate-resolution data to provide catchment intelligence and complement statutory monitoring. | Monitoring indicators of pollution such as algae and nutrient levels (phosphate, ammonia, nitrates) using test strips or handheld colourimeters. Monitoring of outfall discharges and indicators of misconnections in dry weather. Example: Severn Citizen Science Bacteria Testing - CaSTCo | Monitoring indicators of pollution such as colour, turbidity and pH. Nutrient testing using test strips or handheld colourimeters with quality assurance and quality control in place. Example: FreshWater Watch | Invertebrate monitoring as part of a wider national initiative with volunteer training, quality assurance and quality control. Can provide early warning signs of pollution and support preventative action. Example: The Riverfly Partnership | Flood wardens acting as additional eyes on the ground to provide intelligence on flood risk and water levels. Reporting flow using reviewed apps with standardised flow categories. Example: CrowdWater |
| 2 | Monitoring plan is co-designed with multiple partners to meet monitoring standards, including methodology, sample location and frequency. Training and equipment provided and approved by lead organisation, academic institution, stakeholder or statutory body, with high levels of quality assurance and quality control in place, including appropriate limits of detection. | To collect low volumes of high-resolution data with significant investment in training, quality control and assurance. Uses high-quality equipment for direct monitoring of pollutants, environmental pressures or pollution indicators. Data complements statutory monitoring. | This could include laboratory analysis of physio-chemical parameters as indicators of sewage treatment works discharges. Example: iWharfe Report | Direct monitoring of nutrient levels using high-specification equipment or equipment calibrated to statutory monitoring equipment. Data could be used as supporting evidence for Reasons for Not Achieving Good Status or contribute to a Weight of Evidence approach for decision making. Example: River Wensum - CaSTCo | Monitoring using a statutory monitoring methodology and following agreed moderation and quality control procedures, such as diatom assemblage or macroalgal intertidal monitoring. Data could contribute to a Weight of Evidence approach for decision making. Example: Community Science for Healthy Coasts | Flow monitoring using regulation-standard kit (Environment Agency equivalent), with appropriate training, quality assurance and quality control in place and following Environment Agency direction on site location and sampling frequency. Example: Flow Monitoring | Smarter Water Catchment |
| 3 | Data collected and analysed to professional standards and meets data and monitoring quality control standards with a resilient and robust management system behind it, enabling long-term continuity of monitoring services. | Supplement statutory monitoring to complete spatial and temporal data and evidence gaps. | Direct bacterial load monitored using in situ monitoring equipment or samples collected and laboratory analysed by an accredited laboratory using appropriate thresholds. Examples: Working Towards a Cleaner Wharfe The Big Windermere Survey | Real-time continuous monitoring with service level agreements for calibration and maintenance and a traceable quality assurance process. Example: Water Quality Sensors | Smarter Water Catchment | Biodiversity citizen science monitoring data uploaded to and quality assured by the National Biodiversity Network is used by the Environment Agency when considering the impacts of planning applications and permits on wildlife. Example: Nature Conservation Screening in the Environment Agency | Rainfall monitoring through long-term regular rainfall recording used by the Met Office. Example: Rainfall Observer Network |
Table 3. Description and examples of tiers of citizen science monitoring. Activities within this table would generally be characterised against the different tiers as follows, although there may be legitimate reasons why future activities would not fit neatly within a particular tier.
4. Develop a Well-Designed Monitoring Plan
Principle 4: Develop a Well-Designed Monitoring Plan
Set appropriate level and accuracy of monitoring design to meet project objectives.
Why is this important?
Once you have agreed on the purpose and objectives of your project, it is essential that you work collectively with your citizen science and monitoring community to set a clear plan of where, when and how you carry out your monitoring to achieve these objectives.
Your monitoring plan should also include information on how you plan to share your findings to maximise impact and use (see Principle 7: Communicate and Share Outcomes).
This will form the basis of your collaborative monitoring plan.
Box 2. Case Study: iWharfe and EA Bathing Water Investigation – Tier 3
The River Wharfe in Yorkshire has an active and engaged citizen science community which works collaboratively with the Environment Agency, catchment partners and academic institutes and operates under the iWharfe project banner, largely coordinated by Professor Rick Batterbee and Yorkshire Dales Rivers Trust (YDRT) under the Dales to Vales River Network Catchment Partnership.
Ilkley was designated a bathing water site in December 2020 and was the first river site in England to be designated.
Collaborative monitoring was carried out by the Environment Agency and iWharfe citizen scientists to characterise the waterbody from source to confluence and better understand the bacterial loading from various tributaries in the catchment.
The Environment Agency provided:
Yorkshire Dales Rivers Trust:
Yorkshire Water funded Yorkshire Dales Rivers Trust staff time to support volunteer recruitment and management.
This involved intensive surveying across one day to collect samples throughout the catchment. This level of sampling effort could not have been achieved using Environment Agency resources alone.
How have we used this data?
Samples were sent to laboratories for analysis and the results helped direct efforts further upstream.
This case study demonstrates how working collaboratively with different catchment partners can produce highly spatially intensive datasets.
Further information
Working Towards a Cleaner Wharfe – A Closer Look at Water Quality Testing at Ilkley's Bathing Water
https://environmentagency.blog.gov.uk/2024/04/04/working-towards-a-cleaner-wharfe-a-closer-look-at-water-quality-testing-at-ilkleys-bathing-water/
The iWharfe Project, a Case Study – A CaSTCo Webinar (21 November 2023)
https://www.youtube.com/watch?v=soRr5k6_ei4
Where to Sample
When deciding on the number and location of sampling sites for your monitoring strategy, consider the following.
Volunteer Needs
Existing Monitoring
(See Principle 2: Build on and Learn from Existing Monitoring.)
Sample Location
Further Guidance
CaSTCo – Where Will You Collect Data?
https://castco.org/knowledge-base/collecting-data/#3-where-will-you-collect-data
Health and Safety
Further Guidance
CaSTCo Health and Safety Guidance
https://castco.org/knowledge-base/health-and-safety-guidance/
On the exceptional occasions where volunteer citizen scientists are recruited and managed directly by the Environment Agency, volunteers will be required to follow Environment Agency guidance on working with volunteers. This may include:
Volunteers being trained to carry out a water vole survey.
When to Sample
When setting the timing and frequency of monitoring, consider the following.
Volunteer Needs
Project Budget
Balance:
Environmental Conditions
Consider:
Variation in environmental conditions can influence the physical, chemical and biological characteristics of a waterbody and determine when it is safe to sample.
Examples include:
Seasonal Sensitive Areas
Be aware of potential disturbance to wildlife, including fish, where impacts may vary throughout the year.
Further Information
Respecting the Coarse Fish Close Season and Why We Enforce It
https://environmentagency.blog.gov.uk/2023/03/15/respecting-the-coarse-fish-close-season-and-why-we-enforce-it/
A User's Guide to Being River and Lake Friendly
https://scrt.co.uk/wp-content/uploads/river-environment-work-shop-angling.pdf
Bathing Waters
If your monitoring plan involves bathing water sampling, the following resources may be useful:
How the Environment Agency Monitors and Tests Bathing Water Quality
https://environmentagency.blog.gov.uk/2024/05/15/how-the-environment-agency-monitors-and-tests-bathing-water-quality/
How Does the Environment Agency Check Bathing Water Quality?
https://www.youtube.com/watch?v=mY3dxWEPErw
Bathing Water Quality Profiles
https://environment.data.gov.uk/bwq/profiles/
Further Guidance
CaSTCo – When Will You Collect Data?
https://castco.org/knowledge-base/collecting-data/#4-when-will-you-collect-data
Box 3. Case Study: Hello Lamp Post – Tier 0
Hello Lamp Post invites local residents and visitors at selected sites across the country to chat to their local beach, river or lake using the Hello Lamp Post artificial intelligence platform.
Participants can contribute to citizen science by sharing their own observations from these sites.
Information gathered from these conversations has helped the Environment Agency understand:
Further Information
Supporting Citizen Science – Hello Lamp Post Pilot
How to Sample
When considering which methods to use, these should be appropriate for the purpose of your monitoring. You should also consider the tiers of methods outlined in Table 3 and the associated quality assurance expectations linked to different tiers.
For example:
This can be invaluable for understanding variation in water quality over space and time but generally requires a greater investment in equipment, training and quality control to meet the standards expected within Tier 2 and Tier 3 monitoring programmes.
We recommend:
Use existing methodologies where possible
Where appropriate, use established methodologies and existing monitoring initiatives (see Table 1), which will already have quality control measures in place.
Follow a method audit process
Method audits can be used to compare different methods for:
CaSTCo has developed a framework and supporting guidance to support method auditing.
Further Information
Overview: Method Audit Process - CaSTCo
https://castco.org/knowledge-base/overview-of-method-audit-process/
Understanding Monitoring Parameters
Further information on commonly monitored parameters may be useful when deciding how to monitor.
Phosphorus
Overview: Phosphorus - CaSTCo
https://castco.org/knowledge-base/overview-phosphorus/
Ammoniacal Nitrogen
Ammoniacal Nitrogen Fact Sheet
(See Appendix 2)
Monitoring Methods
Methods List and Categories - CaSTCo
https://castco.org/knowledge-base/methods-list/
Box 4. Case Study: Bacteria and Chemistry Water Blitz - Tier 2
In the West Midlands, the Environment Agency is working with:
to monitor bathing water quality and river health across the Teme catchment as part of the Catchment Systems Thinking Cooperative (CaSTCo).
With a newly designated bathing water at Ludlow, partners are testing different methodologies to monitor bacteria and water quality throughout the catchment. This work is providing valuable information about:
Further Information
Severn: Citizen Science Bacteria Testing - CaSTCo
https://castco.org/case-study/severn-bacteria/
CaSTCo Water Blitz Comparing Bacteria and Chemistry Methods in the Severn
https://www.youtube.com/watch?v=fPcSJO_8f-c&t=5s
CaSTCo Teme Data Visualisation Tool
https://experience.arcgis.com/experience/c00987a329bd4aba8b131f08506786d6
5. Follow Quality Control Measures
Principle 5: Follow Quality Control Measures
Ensure all processes meet established standards of quality and include evidence of training, calibration and validation steps in the monitoring plan.
Why is this important?
Putting measures in place to ensure that monitoring methods, data entry processes and data analysis procedures meet agreed standards will improve the quality of your data and provide greater confidence in your findings.
Demonstrating to others that your data has followed a quality assurance process will also improve:
The level of quality assurance applied within a monitoring plan can be cross-referenced to the tiered monitoring approach described under Principle 3 and Table 3.
This helps the Environment Agency and other organisations assess where data and information collected under different tiers can be used to maximise impact while ensuring that the right data is used for the right purpose.
Quality Assurance
Quality assurance is the process used to assess the:
of monitoring methods and the data they produce.
This increases confidence in the data and can increase the weight given to that information within a wider evidence base.
A quality assurance process should include:
Quality Control
Steps to Check Sample Accuracy
Collecting good-quality data is the foundation of any monitoring programme. Quality considerations should be built into a project from the outset.
Additional Guidance
Quality Assurance Handbook and Toolkit for Participatory Science Projects (US EPA)
https://www.epa.gov/participatory-science/quality-assurance-handbook-and-toolkit-participatory-science-projects
Marine Biological Association (DASSH) Best Practice - Verification and Quality Control Schemes
https://www.dassh.ac.uk/citizen-science/best-practice/transcript#plan-verification_and_quality_control_qc_schemes
Visualising Data
Basic visualisation of data using graphs or maps can help identify:
Visual checks can often identify issues that might otherwise go unnoticed.
Selecting Monitoring Equipment
Choosing appropriate equipment is essential for generating quality-assured data.
Consider the following:
For example, some phosphorus monitoring kits may not detect concentrations at the lower limits required for environmental assessment.
Consistency in Recording Your Data
Data Input
Site Locations
If using apps to record data:
Site Naming Guidance
Site names:
If site names contain location information, build capacity into the naming system. For example:
Site names should not include:
These can create issues when uploading or managing data.
Box 5. Case Study: Ongoing Quality Assurance for Citizen Science in East Anglia (Tier 2)
The accuracy of data generated by trained citizen scientists using digital photometers on the Rivers Lark and Wensum was investigated as part of the CaSTCo demonstration catchment programme.
A pilot quality assurance process was developed to assess consistency in volunteer-generated data.
As part of the process:
Findings
The results showed that:
Volunteers whose results fell outside expected ranges were contacted to review:
Lessons Learned
The work highlighted the importance of:
Recording Your Data Digitally
Where possible, record monitoring data digitally.
If paper forms are used, ensure that data are transferred to digital systems and checked for errors.
Benefits of Recording Data Digitally
Disadvantages of Recording Data Digitally
6. Interpret and Understand Your Findings
Principle 6: Interpret and Understand Your Findings
Explore the interactions between parameters measured to understand the health of your local waterbody.
Why is this important?
Rivers, estuaries and coastal waters vary naturally across both space and time. Parameters monitored within and around a waterbody do not act independently but interact with one another.
Collating and analysing:
can help identify patterns and trends and provide a broader understanding of waterbody health.
Visual summaries such as:
can help demonstrate how parameters vary and interact.
Looking for patterns over time and across locations allows comparison:
and can help identify spatial changes.
However, each waterbody responds differently according to its physical, ecological and chemical characteristics. Care should therefore be taken when comparing data between locations.
How Can I Find Out More?
Freshwater: Rivers and Lakes
Further guidance to help understand river types and interpret Environment Agency data:
River Typology Locations
River Basin Management Plan Maps
https://experience.arcgis.com/experience/73ed24b6d30441648f24f043e75ebed2/page/Location/
River Type for Water Framework Directive (WFD) Classification
Water Quality Interpretation
Lakes
Long-Term Lakes Monitoring
https://www.ceh.ac.uk/our-science/projects/long-term-lakes-monitoring
Ecological Classification of UK Lakes Using Aquatic Macrophytes
Marine and Coastal Waters
Further coastal monitoring guidance will be included in future versions of the framework.
Current Water Framework Directive UKTAG guidance includes:
Transitional and Coastal Waters – Saltmarsh
https://www.wfduk.org/resources/transitional-and-coastal-waters-saltmarsh
Coastal Waters – Rocky Shore Macroalgae
https://www.wfduk.org/resources/coastal-waters-rocky-shore-macroalgae
7.Communicate and Share Outcomes
Principle 7: Communicate and Share Outcomes
Maximise the impact of your results by sharing outcomes in accessible, FAIR and visual ways with stakeholders.
Why is this important?
To maximise the impact of your data, once you have collected it, you should aim to share it.
We recommend following an Open by Default approach and considering options to share your data both as:
This helps stakeholders access your information, gain insights and maximise its value.
Open by Default
Follow an Open by Default approach to data sharing wherever possible.
Making data accessible maximises the likelihood that it can be used by others and increases opportunities for environmental improvements by enabling a wider range of stakeholders to draw insights from it.
The Environment Agency follows an Open by Default approach and publishes much of its data under the Open Government Licence.
Further Information
Open Government Licence
https://www.nationalarchives.gov.uk/doc/open-government-licence/version/3/
Environment Agency Data Licensing – Simpler, Easier, Faster
https://defradigital.blog.gov.uk/2016/02/11/environment-agency-data-licensing-simpler-easier-faster/
Consider Advice from Others
Principles of Good Data Governance
https://castco.org/knowledge-base/principles-of-good-data-governance/
Open Data in the Water Industry
https://www.ofwat.gov.uk/regulated-companies/open-data-in-the-water-industry/#H2Open
What is Open Data and Why Should We Care?
https://theodi.org/insights/explainers/what-is-open-data-and-why-should-we-care/
Visualising Yours and Others' Data
Visualising data can help others understand:
Combining your data with:
can provide a more complete understanding of environmental conditions.
Transparency
It is good practice to communicate the following information alongside your data.
This information is known as metadata and provides important context.
Include:
Box 6. Case Study: WyeViz Data Visualisation Tool
Various citizen science groups across the River Wye catchment have formed the Wye Alliance.
The Wye Alliance is a collection of organisations that follow aligned methodologies when collecting data throughout the catchment.
This collaborative approach helps groups combine:
Data are uploaded into a shared EpiCollect database as a single dataset rather than separate individual datasets.
This consistent approach helps improve accuracy and provides the Environment Agency with a better understanding of the complexity of the catchment.
Further Information
Citizen Science in the Wye | Engage Environment Agency
https://engageenvironmentagency.uk.engagementhq.com/citizen-science
Introduction to WyeViz (The Wye Alliance Citizen Science Dashboard)
https://www.youtube.com/watch?v=JEyTPuq22kA
Sensitive Data
Personal information is subject to legal protection, including:
Personal information should be:
It is the responsibility of those collecting and managing data to ensure they comply with applicable legislation.
You may also have:
Where restrictions are necessary, systems should allow data access to be controlled whilst remaining Open by Default and FAIR wherever possible.
FAIR Data Principles
Once collected, consideration should be given to how data will be:
If you are collecting data as part of a national monitoring initiative, much of this work may already be done through their data portal.
Consider storing data on a platform with an API.
What is an API?
An Application Programming Interface (API) allows systems and users to access data directly and can significantly improve the FAIRness of datasets.
We Recommend
Ensure data are findable by all organisations involved in management and decision making.
For example:
Useful Links
Catchment Based Approach (CaBA)
https://catchmentbasedapproach.org/
Catchment Partnership Pages | Catchment Data Explorer
https://environment.data.gov.uk/catchment-planning/v/c3-plan/CatchmentPartnerships
F - Findable
The first step in reusing data is being able to find it.
Metadata and data should be easy to find for both:
Recommendations:
Principles of Good Data Governance
https://castco.org/knowledge-base/principles-of-good-data-governance/
A - Accessible
Once users find the data, they need to understand:
Consider whether restricting access is necessary and whether doing so limits the usefulness of the dataset.
I - Interoperable
Data should be structured so they can be:
R - Reusable
The ultimate goal of FAIR is to optimise reuse.
To support reuse:
If information is shared only as a graph or map without access to the underlying dataset, it is not fully reusable.
8. Apply Outputs to Actions
Principle 8: Apply Outputs to Actions
Use the results to inform action and environmental improvement.
Why is this important?
As part of your monitoring, it is essential to consider what you will do with your data and how your findings can be used to inform action.
Your results and findings may be important in shaping future monitoring plans and may feed directly back into the monitoring pathway. Outcomes may influence:
Others may also be interested in your data, including:
Your data, combined with information from others, contributes to a collective evidence base and a more comprehensive picture of environmental health, helping to inform and prioritise environmental action and decision-making.
Refer to Principle 1: Connect and Collaborate.
Further Guidance
Making a Difference - CaSTCo
https://castco.org/knowledge-base/making-a-difference/
The Environment Agency Currently Uses Citizen Science Data To Help
Improve Certainty in Decision-Making
For example, citizen science data can contribute to the Environment Agency's Weight of Evidence approaches.
Further information:
Environment Agency Eutrophication Weight of Evidence Approach
https://www.youtube.com/watch?v=LvguG0EvdSc
Working Towards a Cleaner Wharfe – A Closer Look at Water Quality Testing at Ilkley's Bathing Water
https://environmentagency.blog.gov.uk/2024/04/04/working-towards-a-cleaner-wharfe-a-closer-look-at-water-quality-testing-at-ilkleys-bathing-water/
Provide Additional Catchment Intelligence
Citizen science can provide information across wider spatial and temporal scales than statutory monitoring alone.
For example:
See the iWharfe example in Box 2.
Support Investigations
Citizen science can provide information that helps identify, investigate and resolve environmental issues.
For example:
Citizen Science Helps Resolve Pollution Issue – River Tat Case Study (CaSTCo)
https://castco.org/case-study/river-tat/
Using the Tiered Approach
The tiered approach enables the Environment Agency and other organisations to understand:
This helps determine where data from each tier can be used most effectively and ensures that the right data are used for the right purpose.
Further examples of collaborative citizen science activities and how the Environment Agency is using citizen science data are available through:
Participate in Citizen Science – Environment Agency
https://engageenvironmentagency.uk.engagementhq.com/citizen-science-participate
Appendix 1: River Type for Water Framework Directive (WFD) Classification
Appendix 1: River Type for Water Framework Directive (WFD) Classification
Understanding River Types
Rivers vary naturally across England according to their:
These characteristics combine to create different river types with different ecological communities.
For example, a mountainous stream in Cumbria can be expected to support a different invertebrate community than a lowland chalk stream in Hampshire.
When collecting and interpreting data, it is important to consider river type so that data are interpreted within the correct environmental context.
WFD Standards for Ammoniacal Nitrogen (mg/L)
| River Type | High | Good | Moderate | Poor |
|---|---|---|---|---|
| Upland and Low Alkalinity | 0.2 | 0.3 | 0.75 | 1.1 |
| Lowland and High Alkalinity | 0.3 | 0.6 | 1.1 | 2.5 |
River Categories
WFD Standards for Dissolved Oxygen Saturation (%)
| River Type | High | Good | Moderate | Poor |
|---|---|---|---|---|
| Upland and Low Alkalinity and High Alkalinity Salmonid River | 80 | 75 | 64 | 50 |
| Lowland and High Alkalinity | 70 | 60 | 54 | 45 |
WFD Standards for Annual Mean Soluble Reactive Phosphorus (mg/L)
| Altitude (m) | Annual Mean Alkalinity CaCO₃ (mg/L) | Type | High | Good | Moderate | Poor |
|---|---|---|---|---|---|---|
| < 80 | < 50 | Type 1 | 0.03 | 0.05 | 0.15 | 0.50 |
| > 80 | < 50 | Type 2 | 0.02 | 0.04 | 0.15 | 0.50 |
| < 80 | > 50 | Type 3 | 0.05 | 0.12 | 0.25 | 1.00 |
| > 80 | > 50 | Type 4 | 0.05 | 0.12 | 0.25 | 1.00 |
River Type Classification
| Site Altitude | <10 mg/L | 10-50 mg/L | 50-100 mg/L | 100-200 mg/L | >200 mg/L |
|---|---|---|---|---|---|
| <80 metres | Type 1 | Type 2 | Type 3 | Type 5 | Type 7 |
| >80 metres | Type 4 | Type 6 | Type 6 | Type 6 | Type 6 |
Appendix 2: Ammoniacal Nitrogen Fact Sheet
Appendix 2: Ammoniacal Nitrogen Fact Sheet
What is Ammoniacal Nitrogen?
Ammoniacal Nitrogen is the combined measure of two states of inorganic nitrogen:
Natural Sources of Ammoniacal Nitrogen in Rivers Include
Anthropogenic (Human) Sources of Ammoniacal Nitrogen Include
Terminology
| Chemical Name | Also Known As |
|---|---|
| Ammoniacal Nitrogen (NH₄-N) | Total Ammonia; Ammonia Nitrogen |
| Ammonia (NH₃) | Unionised ammonia, free ammonia, toxic ammonia |
| Ammonium (NH₄⁺) | Ionised ammonia, less toxic ammonia |
Water Framework Directive Thresholds for Ammoniacal Nitrogen in Rivers
WFD Standards for Ammoniacal Nitrogen (mg/L)
| River Type | High | Good | Moderate | Poor |
|---|---|---|---|---|
| Upland and Low Alkalinity | 0.2 | 0.3 | 0.75 | 1.1 |
| Lowland and High Alkalinity | 0.3 | 0.6 | 1.1 | 2.5 |
River Categories
Appendix 3: Template for Site-Specific Water Quality Interactions
Appendix 3: Template for Site-Specific Water Quality Interactions
Understanding Water Quality Data and What it Means for River Health
Use the following template to collect, record or incorporate information from other sources that can help you interpret the health of your river.
Use this template alongside the supplementary information: General Water Quality Parameter Interactions.
Site Monitoring Template
| Parameter | Metric |
|---|---|
| pH | pH |
| Temperature | °C |
| Conductivity at 25°C | µS/cm |
| Dissolved Oxygen Concentration | mg/L |
| Dissolved Oxygen Saturation | % |
| Ammoniacal Nitrogen as N | mg/L |
| Nitrate as N | mg/L |
| Orthophosphate Reactive as P | mg/L |
Additional Information to Record
| Monitoring Information | Details |
|---|---|
| Date and Time of Water Sample | Add volunteer data |
| Site Location | Add site location |
pH (Power of Hydrogen)
Temperature
Conductivity
Changes in conductivity can indicate inputs such as:
Rainfall often has a diluting effect, reducing conductivity. However, agricultural or road runoff following heavy rainfall may increase conductivity as pollutants enter the waterbody.
Dissolved Oxygen Concentration
Dissolved oxygen concentrations:
When pollutants enter a river:
Therefore, during warmer periods with lower rainfall, pollution can have a greater impact on river ecology.
Dissolved Oxygen Saturation
General guidance:
Nitrate as N
Excessive nitrate may contribute to:
Ammoniacal Nitrogen
The balance between ammonia and ammonium is influenced by:
As pH or temperature increases:
In general:
As temperature and alkalinity increase:
Sources of ammonium include:
Although it is an essential nutrient for plant and algal growth, excessive concentrations can cause eutrophication and algal blooms.
When algae die:
Orthophosphate (Reactive as P)
Excessive amounts from:
can lead to:
Reporting Pollution
Reporting Pollution
If During Your Monitoring You Identify Evidence of Pollution
You must contact the Environment Agency Incident Hotline:
0800 80 70 60
The following resources may help determine whether observations are the result of a natural process or a pollution incident:
What's the Foam You Sometimes See Along Britain's Coastlines?
Telling the Difference Between an Algal Bloom and Sewage
Acknowledgements
Acknowledgements
This framework was developed through collaboration, with thanks to:
Feedback
Feedback
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