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Business waste data
Publication
Reporting year
When published
Business waste data 2021
2021
June 2023
Business waste data 2018
2018
July 2020
Business waste data 2017
Methodology 2017
2017
May 2019
Business waste data 2016 Methodology 2016
2016
July 2018
Business waste data 2015 Methodology 2015
2015
Sept 2017
Business waste data 2014Methodology 2014
2014
Business waste data 2013Methodolog
Who is involved with RBMP
Information regarding the different organisations involved in the RBMP process.
Information regarding the different organisations involved in the RBMP process.
River basin management planning requires co-ordination and integration, only achievable by working in partnership. A broad range of stakeholders help to provide a steer on the development, coordination and implementation of projects to improve Scotland’s water environment. The challenge of meeting the targets set in the river basin plans has to be a shared effort for Scottish Government, SEPA, res
Terms & conditions
Information regarding the different organisations involved in the RBMP process.
Information regarding the different organisations involved in the RBMP process.
SEPA Flood maps: Acceptance of Terms and Conditions
By selecting ACCEPT you, as a member of the public or as an internal business user, agree that you have read, understood and will be bound by the Terms and Conditions provided below.
If you find any of these Terms and Conditions unacceptable, you must not use the flood maps in any way and should select DECLINE.
Terms and Conditions
Ownership:All
Household waste data
Publication
When reported
When published
Household waste summary data and text, pre-release access list and quality report
2024
28th October 2025
Household waste summary data and text, pre-release access list and quality report
2023
29th October 2024
Household waste summary data and textHousehold waste summary data
2022
17th October
Pre-release access list
2022
17th October
Hou
Aquatic Classification
There are a number of significant environmental problems caused by a number of pressures, including diffuse and point source pollution, alterations to beds, banks and shores, alterations to water levels and flows and the presence of invasive non-native species. In order to measure these pressures and their potential effects, we use an aquatic classification system which covers rivers, lochs, estuaries, coastal and groundwater bodies. These are split into management units called water bodies, with a classification produced for each body (the number of water bodies between years varies slightly, as some water body boundaries are reviewed to ensure that they can be managed appropriately).
There are a number of significant environmental problems caused by a number of pressures, including diffuse and point source pollution, alterations to beds, banks and shores, alterations to water levels and flows and the presence of invasive non-native species.
In order to measure these pressures and their potential effects, we use an aquatic classification system which covers rivers, lochs, estuaries, coastal and groundwater bodies. These are split into management units called water bodies, with a classification produced for each body (the number of water bodies between years varies slightly, as some water body boundaries are reviewed to ensure that they can be managed appropriately).
We produce an annual Water Framework Directive (WFD) Classification for all the water bodies in Scotland.
Classification results for 2007 to the current year can be found on the Water Classification Hub.
Read the State of Scotland's Water Environment 2024 summary report (MS Word, 1.17 MB).
Most of our water environment is already in a good condition and subject to fewer pressures than most other E
Protected areas
Information regarding water bodies designated as protected areas.
Information regarding water bodies designated as protected areas.
A significant number of the water bodies in Scotland are designated as protected areas.
This is because of their importance for special purposes such as wildlife conservation, drinking water supply, shellfish harvesting or bathing.
These designated areas are vital to ensure that the diverse ecosystems and cultural and economic benefits contained within them are safeguarded. Protected areas are als
Sea lice regulatory framework implementation
Frequently asked questions
Why is a sea lice framework needed?
Populations of wild Atlantic salmon have been in serious decline in recent decades and are now at crisis point. The pattern of decline is repeated across the salmon’s North Atlantic range and is likely caused, at least in part, by the effect of climate change on the survival of salmon during their time at sea.
To build resilience of Sc
Position Statement: Elevated buildings in areas of flood risk
What is an elevated building?
A building where structures such as pillars or stilts are used to raise it above the expected flood water level. The ground below the building remains at risk of flooding and allows for the free flow of water.
Context for this position statement
This position statement constitutes part of ‘relevant SEPA advice’ as referred to in criterion a) iv of the National Plannin
Developing our flooding knowledge
We are continually working to develop and improve our knowledge on flood risk and flooding impacts and to identify new technologies to better support our flooding work.
We are continually working to develop and improve our knowledge on flood risk and flooding impacts and to identify new technologies to better support our flooding work.
As the strategic flood risk management authority in Scotland we are continually working to develop and improve our knowledge of the sources and impacts of flooding. We have developed a knowledge base of methods, guidance and summaries that may be useful to responsible authorities, academic projects and consultants delivering flood risk management projects, which can be accessed below.
National Flo
Modelling
Marine aquaculture modelling
Computer modelling is used as a guide to determining licensed discharge quantities of anti-parasitic chemicals and organic waste arising from marine fish-farm operations.
The modelling tools promoted by SEPA provide robust predictions in most cases, requiring relatively little site-specific information. Nevertheless, the quality of the model outputs is dependent upon g