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Sustainable Drainage Systems guidance

1. Introduction

Planning applications may require a site-specific Flood Risk Assessment if they meet the thresholds determined by the Environment Agency. Additionally, all planning applications require a Drainage Assessment showing that a full range of SuDS techniques has been considered and that the one proposed will, as a minimum, attenuate the surface water runoff so that both the peak discharge and the total volume are no greater than would occur from the site in its natural condition (i.e. with no development).

This requirement (where appropriate) applies also to applications for the redevelopment of previously developed (Brownfield) sites. Full details of how any SuDS elements will be maintained throughout its life should be given together with confirmation that, if adoption by a third party is assumed, that the third party has agreed to this.

Developers should consult with the Lead Local Flood Authority (LLFA) of North Lincolnshire Council (NLC) (depending on the location of the development proposal) about their SUDS proposals at an early stage (preferably at pre-planning application stage or via consultation).

1.1. What are SuDS?

SuDS are an approach to managing changes to surface water flow created by developments, SuDS systems mimic natural processes of flow rates, attenuation, water filtration and evapotranspiration. SuDS are categorised in the CIRIA SuDS manual 753 (CIRIA, 2015) into the 4 pillars of SuDS which can be found in Figure 1 below.

Diagram showing 4 pillars of Suds, Water Quantity, Water Quality, Amenity, Biodiversity

All SuDS designs should align with the principles set out in the National Planning Policy Framework (NPPF), the National Standards for SuDS, and comply with Building Regulations Part H3. The National Standards for Sustainable Drainage Systems (2025), published by Defra, provide a statutory framework for the design, construction, and long-term management of surface water drainage systems in new developments across England. These standards promote sustainable water management by encouraging the use of natural drainage methods that help reduce flood risk, improve water quality, support biodiversity, enhance amenity, and build resilience to climate change.

The standards are structured around seven key requirements, including the prioritisation of non-potable water reuse and infiltration, the management of both every day and extreme rainfall events, protection of water quality, and the incorporation of multifunctional and biodiversity-enhancing features. They are closely aligned with the NPPF, which requires that sustainable drainage systems be considered from the earliest stages of planning to ensure new development does not increase flood risk. In this way, the national standards reinforce the NPPF’s broader objective of promoting sustainable, well-integrated development.

The national standards also complement the CIRIA SuDS Manual (C753) by translating its best practice guidance into clear design and performance requirements. While the CIRIA manual offers detailed technical direction on the use and design of SuDS components, the national standards ensure these principles are applied consistently in practice. For example, they draw directly on CIRIA guidance for runoff interception, treatment trains, and long-term maintenance, requiring demonstrable compliance as part of the drainage strategy.

Integrating appropriate SuDS into development design helps to mitigate many of the adverse effects of urbanisation on the natural water cycle, such as reduced infiltration, increased runoff, and habitat loss. SuDS features manage surface water as close to its source as possible, often incorporating vegetation to enhance water quality, reduce peak flows, and support biodiversity. In addition to functional benefits, well-designed SuDS contribute positively to the character and liveability of a place by creating green spaces, improving air quality, reducing the urban heat island effect, and offering educational and recreational opportunities.

1.2. What does this handbook cover?

This Sustainable Drainage Systems Guidance Report outlines the vital role of SuDS in proposed developments across North Lincolnshire Council. It provides clear guidance on the effective consideration, design, and implementation of SuDS features within new developments. By integrating SuDS, developments can enhance biodiversity, mitigate flood risks, and improve water quality. This document aims to ensure that SuDS principles are incorporated into planning and design processes, promoting sustainable and resilient growth within the North Lincolnshire region.

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1.3. Why has this handbook been produced?

Section 14 of the NPPF and the PPG Flood and Coastal Change documents state that developments which could affect drainage on or around a site should incorporate sustainable drainage systems to control flow rates and reduce volume of runoff, which are proportionate to the nature and scale of the development. They should provide multifunctional benefits where possible through improving water quality, biodiversity as well as benefits for amenity.

This sets out that the Local Planning Authorities (LPAs) as part of their function of determining planning applications should avoid flood risk to property and people, limiting the residual risk as much as possible and subsequently reducing the risk to life.
As part of this, developments are required to take account of advice of the Lead Local Flood Authority (LLFA) who act as a statutory consultee as set out in the Flood and Water Management Act 2010 and are required to be consulted in all relevant planning applications.

1.4. Who should use this guide?

The guidance set out in this document has been produced for anyone undertaking or granting and reviewing permissions to undertake construction work which has surface water drainage implications, a few examples are shown in Figure 2 below.

List of partners involved in instances of flooding

1.5. National and local standards

National legislation such as the NPPF paragraph 182 (NPPF, 2024) states that SuDS features should be incorporated into all new developments, this includes major and minor developments as well as change of use (where appropriate) with the CIRIA SuDS manual C753 (2015) providing guidance on best practice designs, maintenance as well as improving water quality and ensuring ecology and chemical status are improved.

This is in line with the Water Framework Directive (WFD), which seeks to correct and improve the water environment. This aims to ensure that water bodies achieve a good ecological and chemical status with the WFD emphasising the role of SuDS in managing surface water runoff to prevent pollution and degradation of water bodies.

In June 2025 Defra published the National Requirements for SuDS Framework to ensure consistency to the design and implementation of SuDS across the country.

North Lincolnshire Council’s Strategic Flood Risk Assessment (SFRA) covers the local authorities commitment into the design and implementation of SuDS features which should be read in conjunction with this document.

2. Flood risk

2.1. What is flood risk?

Flood risk is the potential for flooding to occur in a specific area causing damage to people, property and the environment. This can be broken down into 3 main factors:

  • Hazard – The likelihood of flooding happening due to heavy rainfall, overflowing rivers, storm surges, or other causes.
  • Exposure – The presence of people, buildings, infrastructure, and ecosystems in flood-prone areas.
  • Vulnerability – The ability (or lack thereof) of a community, buildings, or systems to withstand and recover from a flood.

Flood risk can be assessed using flood maps, hydraulic and river modelling as well as climate models to assess the risk of flooding for historic, present day and future scenarios.

The Environment Agency provide flood model data within their interactive mapping services which assess the main sources of flooding. The first mapping service is the Flood Map for Planning, which is a vital tool for developers to initially assess whether a development is at risk and will determine the initial flood mitigation and resilience measures needed if any to mitigate against flooding.

The revised flood map for planning (FMfP) which is covered above assesses current and future flooding for rivers and seas at a 2m gridded resolution, the new FMfP also takes into account surface water which is an improvement on previous versions.

The Flood Map for Planning presents flood risk data to support strategic and development planning in England. It shows:

  • Flood Zones, based on the likelihood of river or sea flooding without considering flood defences:
    • Flood Zone 1: Low probability (<0.1% annual chance).
    • Flood Zone 2: Medium probability (between 0.1% and 1% from rivers; 0.1% and 0.5% from the sea).
    • Flood Zone 3: High probability (≥1% from rivers or ≥0.5% from the sea).
    • Flood Zone 3b: Functional floodplain where water needs to flow or be stored during flooding (mapped by local authorities).
    • Flood Zone3a with Climate change: High probability (≥1% from rivers or ≥0.5% from the sea) with climate change.
  • Supporting datasets, including:
    • Present-day scenarios (both defended and undefended conditions for 0.1%, 1%, and 3.3% AEP).
    • Climate change scenarios, showing future flood risk projections based on UK Climate Projections (UKCP18) under RCP8.5 pathway.
    • Surface water flood risk maps (shown for the first time on the Flood Map for Planning).

In addition to this the Environment Agency include additional mapping services which assess flooding from fluvial, pluvial flooding containing flood depth data and additional climate change models. Also, the additional mapping service includes flood modelling data for reservoir breaches which can be useful for assessing a larger area and provide an additional view of flooding for an area.

NLC have also conducted additional modelling to assist with assessing flood risk and set out their requirements within the North and Northeast Lincolnshire Strategic Flood Risk Assessment (SFRA).

NLC also offer an interactive mapping system which includes additional modelling from within the SFRA for the modelled breach scenarios under the 0.5% AEP event (2121), this mapping is a vital resource for assessing flooding within the region as North Lincolnshire has a varied and complicated topography making individual site assessment incredibly important.

The aforementioned mapping services are a valuable tool to understanding flood risk within an area, they alone should not be used as a sole resource to determine site specific flooding as each site will have its own variations in topography, land drainage issues, standing water, groundwater or artificial bodies that can influence flooding on a more localised scale. As such it is required that all forms of flooding are considered when conducting flood risk assessments of the site and the relevant flood mitigation and resilience measures are implemented on this basis.

Additionally, within a flood risk assessment there should be reference to the NPPF, NLC local flood risk policies and documents such as the SFRA with other factors such as safe haven, access/ egress and flood evacuation plans considered within.

Typically a flood risk assessment is needed whenever a site falls within Flood Zone 2 or 3 or is shown to be at risk within the future, however this is not always the case and sites that are over 1ha in size are also subject to a site specific flood risk assessment. Additionally, an area which is known to the LPA that is at risk of critical flooding or is known to have groundwater or other risks associated with flooding may be required to undergo flood risk assessment.

The Environment Agency cover when a flood risk assessment is needed. Further details are available on the government website.

3. SuDS requirements

3.1 Design principles

SuDS features should be in line with NPPF, the National Standards for SuDS seven standards and CIRIA SuDS requirements and should follow the four pillars of sustainable systems as outlined in Figure 1. SuDS should follow the drainage hierarchy as set out in the NPPF, National Standards for SuDS and Building Regulations part H3 which states that surface water discharge from developments should follow the below hierarchy which can be seen below and follow the 5 priorities outlines in standard 1 of the National Standards for SuDS (Figure 3):

Collected for non-potable use – Rainwater harvesting is a priority and should be applied in all developments. This ensures that there is a source control procedure in place which follows the SuDS train, allows for a reduction on flows leaving the site and provides an amenity for water reuse which can be utilised for gardens, agriculture and businesses.

Infiltration – The next most sustainable and preferred option is to discharge surface water via infiltration, to determine if the ground is suitable for infiltration, testing should be conducted using an appropriate methodology such BRE Digest 365. NLC has guidance on the requirements for this which can be found here. This guidance follows the BRE Digest 365 which sets out the standard for infiltration testing. Assuming the water drains away at a rate as a minimum of 1×10-6m/s then the test can be considered successful, and infiltration can be used as a viable method for discharge.

Other points to note for infiltration is if there is sufficient space within a development (a minimum of 5m from building foundations and adjacent highways is required and a minimum of 2.5m for boundary lines), location within a source protection zone and groundwater must also be considered when considering soakaways with a minimum of 1m below the base of the soakaway being a necessity for infiltration to be feasible. Hydraulic modelling should be conducted to determine storage capacities required for discharge via infiltration and require a factor of safety input within the calculations. An appropriate factor of safety should be input within any hydraulic modelling for infiltration features, this is usually set at 2, however if the infiltration feature is designed to discharge a large surface area. If this is the case, then the factor of safety may change (factors of safety should align with Tables 25.2 in Section 25 of the CIRIA SuDS Manual 2015). A justification for a factor of safety different to the standard should be include within the drainage strategy/ report.

Where infiltration rates are lower than 1×10-6m/s a hybrid solution may be possible by way of designing small infiltration basins within the development for small storm events and a piped outfall into attenuation which allows for added storage capacity for larger events and would bring half drain times down to allowable amounts.

Suitable watercourse – Where infiltration is not suitable or has failed due to low permeability then discharge of surface water into a watercourse should be the next preferred option (if appropriate). Assessment into the site should be conducted to determine if there are any suitable watercourses within the vicinity that could be suitable for discharge via this method.

North Lincolnshire Council promote that all developments regardless of greenfield or brownfield should attempt to achieve the greenfield runoff rate or the lowest practical discharge rate possible. If this is not achievable then justification will need to be provided to the LLFA within a drainage impact assessment/ surface water management plan.

Watercourses fall under various authorities within North Lincolnshire, and this should be determined with permissions gained before any discharge can be allowed. Within North Lincolnshire all open watercourses which could be suitable for discharge of surface water fall into different categories of ownership or management. It is the developer/ consultant’s responsibility to contact the relevant owner/ manager for permissions. Watercourses either fall into main rivers which are managed by the Environment Agency and may require an environmental permit. Riparian watercourses come under the jurisdiction of the Land Drainage Authority. This can be either Local Authority – North Lincolnshire Council or one of the five the Internal Drainage Boards (IDBs) which operate in the county if they cover the area. These are:

There is a requirement to complete an ordinary watercourse consent form under the provision of section 23 of the Land drainage Act 1991 and it should be returned to LLFAdrainageteam@northlincs.gov.uk. Completion of this form is only required if the watercourse falls outside of an IDB area. The IDB will need to be contacted directly for a copy of an ordinary watercourse consent form.

Surface water sewer – If there are no suitable watercourses present then discharge into a surface water sewer is the next preferred option, surface water sewers are predominantly managed by a Water Company, however some may be managed by private owners, a limited company or the Highway Authority if it only drains the highway. As such it is important to determine the ownership of the surface water sewer of the proposed discharge point.

North Lincolnshire has two Water Companies within its boundaries, and a pre-planning enquiry should be made to the relevant company in the first instance to determine feasibility of the discharge point.

Combined sewer – If there is no other possibility then it may be applicable to discharge into a combined sewer system although this should be sought after all other options have been considered and dismissed.

As with the surface water sewer system, combined sewers are managed by Water Companies and permissions should be granted from them before discharge into their network.

Diagram showing the preferred methods for drainage hierarchy. Starting with preferred option at the top, 'collected for reuse' Infiltration into the ground, Discharge to a watercourse, Discharge to a surface water sewer, down to Discharge to a combined sewer

In all of these cases the requirement for SuDS is to ensure that:

  • Water quantity is managed by controlling surface water runoff to minimise flood risks, to limit peak flows to an acceptable and preferable predevelopment state and ensure adequate attenuation is provided to prevent flooding elsewhere.
  • Water Quality is improved via filtration, sedimentation and biological processes, provide appropriate treatment stages to meet environmental standards and to prevent contamination of groundwater and other water bodies.
  • Biodiversity and Amenity can be achieved by providing a biodiversity net gain within the development and often within the SuDS system itself, create habitats that can support wildlife, and the integration of SuDS features into public spaces for aesthetic and recreational purposes.

Within the design principles there is a requirement for SuDS features to be resilient to climate change which includes increased extreme weather events, sea level rise and increased temperatures to ensure there is long-term functionality of the systems.

In addition to the above, SuDS systems should be designed with practicality in mind and be of a design as to limit the amount of maintenance required for its lifespan and within development plans or reports should contain a SuDS maintenance plan.

3.2 Groundwater

The design of Sustainable Drainage Systems must consider both soil permeability and the depth of the groundwater table beneath a development site. North Lincolnshire site-specific ground investigations are required to assess infiltration capacity and identify the likely groundwater table level. In areas with high groundwater levels, SuDS features should be designed to be surface-based or shallow to prevent inundation. The use of liners may be necessary to control infiltration and manage groundwater movement effectively. Seasonal variations in groundwater levels should also be considered during the design process to ensure the long-term effectiveness and resilience of the SuDS design.

For initial assessments, information on groundwater levels suitable for an outline application can be obtained from the British Geological Survey.

In addition to this the Environment Agency offer an interactive mapping system which contains groundwater levels at various stations within England and can be used as a tool to assess trends and help determine groundwater levels within the area. This tool shouldn’t be used as a site-specific assessment and only to aid in the investigation process.

3.3 Hydraulics

All drainage systems should be designed to accommodate the 1% (1 in 100-year return period) design storm with no above ground flooding occurring within the site for any event up to and including the 3.3% (1 in 30-year return period).

The following parameters are set out below and include the minimum requirements for hydraulic modelling NLC would expect to see in their designs:

  • Volumetric runoff Coefficient (Cv) – 1 as per HR Wallingford procedure who have addressed the use of lower Cv values on their website with them saying ‘’ This approach was justified in a paper in the 1990s based on the original runoff model in the Wallingford Procedure which was issued in 1983. This justification is a misuse of the correlation equation which had been developed and has since which been rendered obsolete based on the fact that the original equation was shown to under-predict runoff for large rainfall events.”
  • Rainfall – FEH data should be used as this is more statistically accurate and uses more modern methods to determine rainfall and should be used for all storm lengths of 60 minutes or more with the most up to date data used i.e. FEH22 or FEH13 if this is unavailable. FSR data should be used for storms under 60 minutes as it provides sub hourly rainfall data
  • M5-60 (mm) and Ratio-R – If the software uses exact mapping coordinates, then these should be used, where manual location values are entered then this should be supported with appropriate evidence supplied
  • Design Return Period – Set to 1 as default
  • Time of entry (mins) – Should be set to 5 minutes
  • Additional Flows – An additional allowance for urban creep should be factored in which is set at 10% for all developments as covered in standard 3 of the National SuDS Standards.
  • MADD Factor – The MADD factor should be set to zero, this is because the MADD factor accounts for a hypothetical value of 20m3 of storage to be kept within the rainwater pipes before entering the drainage system.
  • Storage Volume in Pipe network (m3) – This should be set to 0. If pipes have been oversized to provide storage this will be considered within the modelling, and this value should still be set to 0.
  • Addition flow/ Climate Change – This is where an additional allowance for urban creep should be input (10%), this can be done by increasing the impermeable areas and accounting that way, but it should be clear. This should not be used for climate change values.
  • Climate change – An additional allowance based on current Environment Agency peak rainfall allowances and NLC guidance should be incorporated into all modelling.
    • The upper end allowances should be used for the 1 in 30 and 1 in 100 yr rainfall events (in NL they are 35% and 40% respectively).
  • Storm durations – Results for all critical storms both summer and winter, ranging from 15 minutes up to 10080 minutes should be included within designs.

The following outputs should be made available within the modelling results to allow for accurate assessment of the model. These should be provided as a PDF with the electronic outputs available if requested.

These are the minimum requirements and failure to provide this data or in sufficient detail will result in further questions and requests for further information subsequently holding up the planning process.

  • The following should be included within the results as a minimum:
  • Design criteria and input variables
  • Drainage network details
  • Manhole schedule
  • Area summaries
  • Outfall details
  • Modelled storm details and simulation criteria
  • Online flow control structure details
  • Offline controls structure details (if these exist within the design)
  • Summary of results for critical storms. Results should be provided for the 1yr, 2yr, 5yr, 30yr plus climate change and 100yr plus climate change storms.
  • Greenfield runoff rate calculations
  • Storage calculations
  • Storage feature details
  • Half drain times (which should fall within 24 hours, justification is required if this is not possible)
  • A pdf drawing should be provided at an appropriate scale showing the layout of the drainage system/s with the pipe and manhole numbers clearly labelled to allow cross-referencing and showing cover levels, invert levels, gradients and diameters of all structures where necessary. The locations of all storage and attenuation features must also be clearly shown.

NLC expect that the runoff rates discussed within the National Standards for SuDS are followed, this requires a developer to use an appropriate statistical method such as the IH124, FEH, HR Wallingford to calculate the QBAR or QMED runoff rates.

Alternatively, a rate of 1.4l/s/ha can be used. The National SuDS standards states that a minimum rate of 3l/s should be used when runoff rates are too low and a minimum of 50mm applied to an orifice plate, this is to help prevent risk of blockages to systems and flow control devices.

For Brownfield sites a relaxation factor can be applied to the greenfield calculations, but it must be robustly justified and evidenced. The relaxation factor can be up to 5x the calculated greenfield rate but must be agreed with all relevant risk management authorities.

If the greenfield rate is assumed too low to be practical due to risk of blockages, inability for self-cleaning then clear justification needs to be provided within drainage drawings and drainage reports to allow the LLFA to assess the feasibility of the design.

In addition to the above, it is imperative that impermeable areas are included and allocated to the correct pipes/ SuDS feature, this should include all impermeable areas of a site and any areas in which flows are likely to enter the relevant system. This will ensure systems are designs appropriately and allow for correct volumes in turn managing surface water correctly.

A good method of ensuring this is to create impermeable areas drawings which should include urban creep and detailing which area has been allocated to which SuDS features.

3.4 Exceedance flows

Surface water exceedance flows occur when the volume or rate of surface water runoff surpasses the capacity of a drainage system, leading to the potential of overland flooding. This situation can arise due to intense rainfall events, blockages, or when the drainage infrastructure is overwhelmed.

To effectively manage exceedance flows, drainage systems must be designed to accommodate extreme events and potential blockages by incorporating safe overland flow routes that direct excess water away from vulnerable areas and properties.

Approved Document H of the Building Regulations emphasises the importance of sustainable drainage solutions, such as infiltration systems, to prevent surface water from overwhelming drainage networks or mixing with foul water drains. Proper exceedance flow routing ensures that, during intense rainfall, water is managed safely, minimising flood risks. Protecting property, infrastructure and people.

3.5 SuDS Management train

Management train is a fundamental principle within SuDS design. It creates a series of stages within a journey which starts when the rain falls over a surface and subsequently flows to its destination which could be a soakaway, wetland, stream or river. SuDS features intend to mimic these natural processes to reduce pollution, flow rates and volume of water entering the final outfall (Figure 4).

An image showing a series of stages within a journey which starts when the rain falls over a surface and subsequently flows to its destination which could be a soakaway, wetland, stream or river.

The first step of the management train starts with prevention, the aim of this is to prevent runoff from impermeable areas being unrestricted and controlling them by reducing impermeable areas and reducing pollutants.

The next stage is source control, this looks at managing surface water flows at the source via measures such as permeable paving, individual soakaways, localised swales and re-use of water.

The next step is site control, the premise of this step is to manage surface water flows at site level and can incorporate SuDS features such as swales, ponds, basins which all help to reduce and attenuate surface water which aids evapotranspiration processes and absorption.

The final step is, regional controls, these controls are predominantly used on larger sites and provide one last level of water quality improvement and volume reduction after site controls have been deemed inadequate.

All these control measures do not need to be used in tandem and should be assessed on a site-by-site basis, however it is always best to treat runoff as close to source as possible to reduce impact on watercourses and drainage systems downstream.

A site-specific assessment is required to determine the types of SuDS features. For example, run-off from a roof would require less treatment than runoff from a highway and runoff from an industrial area used for steel would require multiple levels of SuDS features to remediate all of the possible pollutants within the runoff.

3.6 Types of SuDS

SuDS features for developments come in many different variations with some much simpler and easier to manage and maintain than others. Some features that could be implemented would include:

  • Infiltration based SuDS – Soakaways, infiltration basins, permeable paving, filter trenches, underground geocellular storage, deep bore soakaways.
  • Conveyance SuDS – Swales, filter drains/ strips, rainwater channels.
  • Storage and attenuation – Both above and underground storage basins, retention ponds, geocellular storage and tanks.
  • Vegetated SuDS – Green roofs, raingardens, wetlands and reed bed systems.
  • Urban SuDS – Water Butts, tree pits and rainwater planters, blue green infrastructure such as bioswales, green corridors and urban wetlands.

Whilst this list is not exhaustive and there are many more SuDS features that can and should be considered this list gives a good understanding of the types of SuDS features that could be implemented within a site.

3.7 Design details

The design details for SuDS should be included within a relevant report such as a drainage impact assessment or surface water management plan and include all design details with consideration taken to the type of development being proposed and the likely remediation from a water quality perspective that should be implemented.

This should incorporate a drainage maintenance plan for the lifetime of the development, covering who is responsible for manging the drainage systems, with details outlining what maintenance requirements and how often they will be maintained.

3.8 Landscape design

Another consideration for SuDS is the aesthetic and biodiversity gains from the design, this is covered in detail within the National Standards for SuDS and is expected to be addressed within an application in relation to SuDS. The wider ecology and biodiversity is outside of the remit for the LLFA but is still a functional part of the principles of SuDS and should be incorporated into drainage designs. This will be assessed by the NLC planning teams and environmental departments.

3.9 Water quality and water framework directive (WFD)

3.9.1 Water framework directive (WFD)

The Water Framework Directive (WFD), established in 2000, sets out a framework for the protection and enhancement of all water bodies, including rivers, lakes, groundwater, estuaries, and coastal waters. In England, the implementation of the WFD is facilitated through River Basin Management Plans (RBMPs), which are reviewed and updated on a six-year cycle to assess and improve the ecological and chemical status of water bodies.

The main environmental objectives of the WFD are to ensure water quality is kept to or returned to the highest possible standard which will allow biodiversity to flourish and achieve ‘good’ ecological status which is determined by looking at the abundance of aquatic flora and fauna, the availability of nutrients, salinity, temperature, the impact of pollution and morphological features such as water flow, depth and river bed structures.

The WFD classification scheme for surface water ecological status includes five categories which can be categorised as:

  • High Ecological Status – Represents near-natural conditions with no or minimal human influence. The water body is in excellent condition, with natural biodiversity and functioning ecosystems.
  • Good Ecological Status – Slight deviation from natural conditions, but the water body still supports a healthy and functioning ecosystem. This is the target for most water bodies under the WFD.
  • Moderate Ecological Status – Some degradation in ecological quality, but the water body still maintains some biological health. Measures are required to improve it to good status.
  • Poor Ecological Status – Significant degradation, with the water body failing to support a healthy ecosystem. Immediate measures are necessary to reduce the pressure on the water body.
  • Bad Ecological Status – Severe degradation, with significant damage to ecosystems. Immediate and substantial intervention is required to restore ecological health.

3.9.2 River basin management plans (RBMP’S)

The Humber River Basin Management Plan (RBMP) provides a strategic framework for improving and protecting the water environment within the Humber River Basin District. It aims to achieve good ecological and chemical status for all water bodies by 2027, in compliance with the Water Framework Directive (WFD). The plan assesses the current state of rivers, lakes, estuaries, and coastal waters, identifying key pressures such as pollution, habitat degradation, and invasive species. A series of measures and actions are proposed to address these issues, including pollution reduction, habitat restoration, water resource management, and invasive species control.

The plan is overseen by the Environment Agency and involves collaboration with regional local authorities, including NLC as well as other stakeholders. As the LLFA it is our responsibility to coordinate and encourage the implementation of SuDS within the area to maintain and improve water quality whilst mitigating against the risk of flooding.

3.9.3 SuDS

As such using SuDS to manage surface water plays an important role in preventing the pollution of water bodies from surface water runoff. The implementation of the SuDS approach for the drainage for new developments will ensure that these sites cannot contribute to the degradation in the quality of surface or ground water.

Chapter 26 of the CIRIA SuDS manual offers a range of different SuDS features and their treatment values which can be assessed through its ‘Simple Index Approach’. The LLFA expects SuDS components to be installed within developments which will allow for Standard 4 of the National standards for SuDS to be met and follow the SuDS train to reduce pollutants entering waterways and groundwater.

The aforementioned Simple Index approach highlights a wide range of features that can be used to manage water quality within a development.

It may be appropriate to include proprietary treatment devices such as oil interceptors, reed beds or isolation valves within designs in order to manage water quality and ensure positive impacts to systems, this would be dependent on the specific development proposals.

3.10 Riparian responsibilities

A riparian owner is the person or persons with a watercourses or culvert on or adjacent to their property. Under common law there are certain responsibilities riparian owners have for maintenance of these assets.

In most cases riparian responsibilities lie with the landowner. However, it is advised that you seek clarification on whether these responsibilities have been included in any tenancy agreement. Where a watercourse forms a boundary, the riparian responsibilities are shared equally between the adjacent landowners on each side.

The only time this would be different is if the property deeds or land registry show or detail other arrangements or ownership.

The responsibility of riparian owners is as follows:

  • You have the responsibility to pass on flow without obstruction, pollution or diversion affecting the rights of others. Others also have the right to receive water in its natural quantity and quality.
  • You must accept flood flows through your land, even if caused by inadequate capacity upstream or downstream. There is no duty in common law for a landowner to improve the drainage capacity of a watercourse.
  • You must maintain the bed and banks of the watercourse, and also the trees and shrubs growing on the banks. You must also clear any debris, even if it did not originate from your land. This debris may be natural or man-made and includes litter and animal carcasses.
  • You must not cause any obstructions – either temporary or permanent – that would prevent the free passage of fish.
  • You must keep the bed and banks clear of any matter that could cause an obstruction, either on your land or downstream if it is washed away. Please help us to protect water quality – do not use riverbanks for the disposal of any form of garden or other waste where there is any danger that it will be washed into the river. This includes grass clippings, which are highly polluting.
  • You must keep any structures that you own clear of debris. These structures include culverts, trash screens, weirs and mill gates.
  • Any invasive species such as Japanese Knotweed should be managed, reported and dealt with in an appropriate manner.

North Lincolnshire Council has published its own Guide to Watercourses and Riparian Ownership . The Environment Agency has also published a useful guide which sets outs the rights and responsibilities of Riparian owners.

Under the Land Drainage Act 1991 consent must be sought before any works are carried out on ordinary watercourses, which includes changes to dams, weirs and any other structures, this also includes culverting or installing a pipe in the watercourse. Routine maintenance doesn’t require a consent.

If there is damage to the banks or bed of the watercourse then the relevant authority should be contacted, this is dependent on the location of the watercourse but would likely be the LLFA, Internal Drainage Board or the Environment Agency. If it is an emergency, then the Environment Agencies Emergency Flood line should be contacted on 0800 80 70 60.

3.11 Maintenance requirements

The Construction and Design Management (CDM) Regulations 2015 requires all designers to identify, eliminate or control risks that could arise during the lifetime of a scheme. Therefore, any SuDS designs should incorporate a management plan for how it is proposed to be maintained.

SuDS components should have shallow side slopes no steeper than 1:3 for attenuation, swales or open basin features with ponds having shallows shelving towards the edges.

Pipe connections should be of short enough length and capable of being maintained. Inlets and outlets should be designed to be able to be safely cleaned, maintained and kept free from debris.

Chapter 36 of the CIRIA SuDS manual C736 provides guidance on managing the safety risks associated with SuDS features, the SUSDrain website also provides useful guidance on SuDS features and best practices to maintain and manage them appropriately.

The link to SUSDrain can be found here.

4. Useful resources