Thanet District Council 2025 Annual Status Report June 2025
Document Control Sheet
Identification | |
Client | Thanet District Council |
Document Title | 2025 Annual Status Report |
Bureau Veritas Ref No. | AIR26231721 |
Contact Details | ||
Company Name | Bureau Veritas UK Limited | Thanet District Council |
Contact Name | Alicia Dale | Amanda Berry |
Position | Senior Consultant | Senior Environmental Health Practitioner |
Address | 2nd Floor Atlantic House, Atlas Business Park, Manchester, M22 5PR | Thanet District Council Offices Cecil Street Margate Kent CT9 1XZ |
alicia.dale@bureauveritas.com | amanda.berry@thanet.gov.uk |
Version Control | ||||
Version | Date | Author | Reason for Issue/Summary of Changes | Status |
1.0 | 11/06/2025 | L Thomas | Draft for Comment | Draft |
2.0 | 16/06/2025 | L Thomas | Client Comments addressed | Final |
Name | Job Title | Signature | |
Prepared By | Louis Thomas | Junior Air Quality Consultant | L Thomas |
Approved By | A Dale | Senior Consultant |
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In fulfilment of Part IV of the Environment Act 1995 Local Air Quality Management, as amended by the Environment Act 2021
Date: June, 2025
Information | Thanet District Council’s Details |
Local Authority Officer | Amanda Berry |
Department | Senior Environmental Health Practitioner |
Address | Cecil Street Margate, CT9 1XZ |
Telephone | 01843 577 422 |
amanda.berry@thanet.gov.uk | |
Report Reference Number | AIR26231721 |
Date | 11/06/2025 |
Local Responsibilities and Commitment
This ASR was prepared by Bureau Veritas on behalf of Thanet District Council with the support and agreement of the following officers and departments:
Amanda Berry – Senior Environmental Health Practitioner
This ASR has been approved by: Mike Humber Director of Environment
This ASR has been signed off by a Director of Public Health, Dr Anjan Ghosh
If you have any comments on this ASR please send them to Amanda Berry at:
Cecil Street Margate,
CT9 1XZ
01843 577 422
Amanda.berry@thanet.gov.uk
Breathing in polluted air affects our health and costs the NHS and our society billions of pounds each year. Air pollution is recognised as a contributing factor in the onset of heart disease and cancer and can cause a range of health impacts, including effects on lung function, exacerbation of asthma, increases in hospital admissions and mortality. In the UK, it is estimated that the reduction in healthy life expectancy caused by air pollution is equivalent to 29,000 to 43,000 deaths a year[1].
Air pollution particularly affects the most vulnerable in society, children, the elderly, and those with existing heart and lung conditions. Low-income communities are also disproportionately impacted by poor air quality, exacerbating health and social inequalities.
Table ES 1 provides a brief explanation of the key pollutants relevant to Local Air Quality Management and the kind of activities they might arise from.
Table ES 1 - Description of Key Pollutants
Pollutant | Description |
Nitrogen Dioxide (NO2) | Nitrogen dioxide is a gas which is generally emitted from high-temperature combustion processes such as road transport or energy generation. |
Sulphur Dioxide (SO2) | Sulphur dioxide (SO2) is a corrosive gas which is predominantly produced from the combustion of coal or crude oil. |
Particulate Matter (PM10 and PM2.5) | Particulate matter is everything in the air that is not a gas. Particles can come from natural sources such as pollen, as well as human made sources such as smoke from fires, emissions from industry and dust from tyres and brakes. PM10 refers to particles under 10 micrometres. Fine particulate matter or PM2.5 are particles under 2.5 micrometres. |
Annual mean NO2 concentrations at all but six monitoring sites across Thanet District Council have shown a decrease in 2024 compared to 2023. All monitoring locations continued to record annual mean NO2 concentrations below the annual mean NO2 air quality objective in 2024. This continues a trend of six years of compliance with the annual mean NO2 air quality objective across Thanet District Council. In September 2024 Thanet District council revoked Ramsgate AQMA, which was initially declared in June 2023 in place of the wider Thanet Urban AQMA following modelled exceedances of the annual mean NO2 air quality objective. With additional monitoring showing NO2 well below the annual mean NO2 air quality objective, an Air Quality Strategy has now been drafted and due to be published this autumn.
With regard to the 1-hour mean NO2 AQS objective, whereby there should be no more than 18 hours where concentrations exceed 200µg/m3, both automatic monitoring locations continue to report no hourly concentrations greater than 200µg/m3.
For PM10, the reported annual mean concentration continues to be below the annual mean PM10 AQS objective of 40µg/m3 at both automatic monitoring stations (ZH4 at Boundary Road, Ramsgate and ZH5 at The Square, Birchington). Concentrations of PM10 have shown a decreasing trend at ZH5 Birchington from 2020-2023 with a very slight increase in observed annual mean concentration in 2024. Concentrations of PM10 at ZH4 Ramsgate have fluctuated in the past five years with concentrations in 2024 now lower than levels in 2023. With regards to the 24-hour mean PM10 AQS objective, whereby there should be no more than 35 24-hour periods where concentrations exceed 50µg/m3, the maximum number of 24-hour period means greater than 50µg/m3 was four and zero, reported at ZH4 at Boundary Road and ZH5 at The Square, respectively.
In 2025 Thanet District Council updated its Air Quality Technical Planning guidance[2]. This was produced in conjunction with Kent and Medway Air Quality Partnership and sets out the approach for considering air quality that should be adopted from pre-application stage through to submitting details as part of the planning application.
Whilst air quality has improved significantly in recent decades, there are some areas where local action is needed to protect people and the environment from the effects of air pollution.
The Environmental Improvement Plan[3] sets out actions that will drive continued improvements to air quality and to meet the new national interim and long-term targets for fine particulate matter (PM2.5), the pollutant of most harmful to human health. The Air Quality Strategy[4] provides more information on local authorities' responsibilities to work towards these new targets and reduce fine particulate matter in their areas.
The Road to Zero[5] details the Government’s approach to reduce exhaust emissions from road transport through a number of mechanisms, in balance with the needs of the local community. This is extremely important given that cars are the most popular mode of personal travel, and the majority of Air Quality Management Areas (AQMAs) are designated due to elevated concentrations heavily influenced by transport emissions.
Thanet District Council has successfully progressed and implemented the following measures:
The Electric Vehicle Guidance for Developers[6], in accordance with the local plan policy, building regulations and Thanet’s Air Quality and Planning Technical Guidance, sets the requirements for EV charging points to be installed in new residential and commercial developments. Given the rapid pace of technological advancements in electric vehicle (EV) charging infrastructure, developers must stay up-to-date on the latest available information and consult with the relevant Local Planning Authority. Beyond just providing this basic EV infrastructure, developers will also be expected to incorporate additional low-emission measures. This may include facilitating active travel options, such as pedestrian and cycling facilities, as well as supporting sustainable public transportation.
Thanet District Council continues to uphold and work alongside the existing partnership with Kent County Council to engage in a joint approach to tackle air quality issues and the implementation of the Thanet Transport Strategy[7], and as part of the Kent and Medway Air Quality Partnership.
Road transport is the dominant source of pollution within Thanet and reducing road traffic emissions across Thanet therefore continues to remain the key air quality priority. This will also contribute to reducing PM10 and PM2.5 concentrations across the district.
Considering no exceedances of the annual mean NO2 AQS objective in 2018, Thanet District Council revoked the Thanet Urban AQMA as recommended by Defra in the 2021 appraisal letter. The concentrations continued to be below the annual mean NO2 AQS objective since 2018 and there is a decreasing trend in the concentrations.
Following a detailed assessment, the Ramsgate AQMA was declared on 25th June 2023. This AQMA was declared in place of the revoked Thanet Urban AQMA as a precautionary action. However, considering there are no exceedances of the annual mean NO2 AQS objective for the last 6 years within the Ramsgate AQMA, Thanet has revoked the Ramsgate AQMA. A Thanet wide Air Quality Strategy 2025 is currently being developed.
As the main source of air pollution within Thanet are road transport emissions, a way for the public to get involved with helping improve air quality in the District is to find alternatives to travelling by private vehicle. The following are suggested alternatives to private travel that would contribute to improving air quality within the District:
Thanet District Council are part of Kent Air which provides a website of educational material with the aim of educating the local population on air pollution and displaying the current air pollutions in Kent, called Care for KentAir[8].
Local Responsibilities and Commitment i
Executive Summary: Air Quality in Our Area ii
Air Quality in Thanet District Council ii
Actions to Improve Air Quality iv
1 Local Air Quality Management 1
2 Actions to Improve Air Quality 2
2.1 Air Quality Management Areas 2
2.2 Progress and Impact of Measures to address Air Quality in Thanet District Council 4
2.3 PM2.5 – Local Authority Approach to Reducing Emissions and/or Concentrations 12
3 Air Quality Monitoring Data and Comparison with Air Quality Objectives and National Compliance 14
3.1 Summary of Monitoring Undertaken 14
3.1.1 Automatic Monitoring Sites 14
3.1.2 Non-Automatic Monitoring Sites 14
3.2.1 Nitrogen Dioxide (NO2) 15
3.2.2 Particulate Matter (PM10) 16
3.2.3 Particulate Matter (PM2.5) 16
Appendix A: Monitoring Results 18
Appendix B: Full Monthly Diffusion Tube Results for 2024 37
Appendix C: Supporting Technical Information / Air Quality Monitoring Data QA/QC 40
New or Changed Sources Identified Within Thanet District Council During 2024 40
Additional Air Quality Works Undertaken by Thanet District Council During 2025 41
QA/QC of Diffusion Tube Monitoring 41
Diffusion Tube Annualisation 43
Diffusion Tube Bias Adjustment Factors 43
NO2 Fall-off with Distance from the Road 44
QA/QC of Automatic Monitoring 45
PM10 and PM2.5 Monitoring Adjustment 45
Automatic Monitoring Annualisation 45
NO2 Fall-off with Distance from the Road 45
Appendix D: Map(s) of Monitoring Locations and AQMAs 46
Appendix E: Summary of Air Quality Objectives in England 55
Figures
Figure A.1 – Trends in Annual Mean NO2 Concentrations within the Ramsgate AQMA 28
Figure A.2 – Trends in Annual Mean NO2 Concentrations outside the AQMA in the North of the District 29
Figure A.3 – Trends in Annual Mean NO2 Concentrations outside the AQMA in the centre of the District 30
Figure A.4 – Trends in Annual Mean NO2 Concentrations outside the AQMA in the South of the District 31
Figure A.5 – Trends in Annual Mean PM10 Concentrations 34
Figure A.6 – Trends in Number of 24-Hour Mean PM10 Results > 50µg/m3 36
Figure C.1 – Bias Adjustment Factor Database 42
Figure D.1 – Detailed Map of Ramsgate AQMA 46
Figure D.2 – Map of Automatic Monitoring Sites 47
Figure D.3 – Map of Non-Automatic Monitoring Sites 48
Figure D.4 – Map of Monitoring Locations in Birchington 49
Figure D.5 – Map of Monitoring Locations in Minster 50
Figure D.6 – Map of Monitoring Locations in Cliffsend, Ramsgate 51
Figure D.7 – Map of Monitoring Locations in Westwood 52
Figure D.8 – Map of Monitoring Locations in Margate and Westgate-on-Sea 53
Figure D.9 – Map of Monitoring Locations in Ramsgate AQMA 54
Tables
Table 2.1 – Declared Air Quality Management Areas 3
Table 2.2 – Progress on Measures to Improve Air Quality 8
Table A.1 – Details of Automatic Monitoring Sites 18
Table A.2 – Details of Non-Automatic Monitoring Sites 19
Table A.3 – Annual Mean NO2 Monitoring Results: Automatic Monitoring (µg/m3) 23
Table A.4 – Annual Mean NO2 Monitoring Results: Non-Automatic Monitoring (µg/m3) 24
Table A.5 – 1-Hour Mean NO2 Monitoring Results, Number of 1-Hour Means > 200µg/m3 32
Table A.6 – Annual Mean PM10 Monitoring Results (µg/m3) 33
Table A.7 – 24-Hour Mean PM10 Monitoring Results, Number of PM10 24-Hour Means > 50µg/m3 35
Table B.1 – NO2 2024 Diffusion Tube Results (µg/m3) 37
Table C.1 – Planning Applications with Air Quality Conditions in 2024 40
Table C.2 – Annualisation Summary (concentrations presented in µg/m3) 43
Table C.3 – Bias Adjustment Factor 44
Table C.4 – Local Bias Adjustment Calculation 44
Table E.1 – Air Quality Objectives in England 55
This report provides an overview of air quality in Thanet District Council during 2024. It fulfils the requirements of Local Air Quality Management (LAQM) as set out in Part IV of the Environment Act (1995), as amended by the Environment Act (2021), and the relevant Policy and Technical Guidance documents.
The LAQM process places an obligation on all local authorities to regularly review and assess air quality in their areas, and to determine whether or not the air quality objectives are likely to be achieved. Where an exceedance is considered likely the local authority must declare an Air Quality Management Area (AQMA) and prepare an Air Quality Action Plan (AQAP) setting out the measures it intends to put in place in order to achieve and maintain the objectives and the dates by which each measure will be carried out. This Annual Status Report (ASR) is an annual requirement showing the strategies employed by Thanet District Council to improve air quality and any progress that has been made.
The statutory air quality objectives applicable to LAQM in England are presented in Table E.1.
Air Quality Management Areas (AQMAs) are declared when there is an exceedance or likely exceedance of an air quality objective. After declaration, the authority should prepare an Air Quality Action Plan (AQAP) within 18 months. The AQAP should specify how air quality targets will be achieved and maintained, and provide dates by which measures will be carried out.
A summary of AQMAs declared by Thanet District Council can be found in Table 2.1. Ramsgate AQMA was revoked in September 2024 after 6 years of consecutive compliance with the annual mean NO2 air quality objective, however, details are still shown in Table 2.1 due to the relevance of the AQMA to monitoring in 2024. Appendix D: Map(s) of Monitoring Locations and now revoked AQMAs provides maps of AQMA and also the air quality monitoring locations in relation to the AQMA. The air quality objectives pertinent to the current AQMA designation is the NO2 annual mean.
Ramsgate AQMA has now been revoked (see monitoring section) and a Thanet wide Air Quality Strategy 2025 has now been drafted to prevent and reduce polluting activities.
Table 2.1 – Declared Air Quality Management Areas
AQMA Name | Date of Declaration | Pollutants and Air Quality Objectives | One Line Description | Is air quality in the AQMA influenced by roads controlled by Highways England? | Level of Exceedance: Declaration | Level of Exceedance: Current Year | Number of Years Compliant with Air Quality Objective | Name and Date of AQAP Publication | Web Link to AQAP |
Ramsgate AQMA | 25/6/2023 | NO2 Annual Mean | An area encompassing 600 properties between High Street St Lawrence and Shah Place | No | 35.2µg.m3 | 27.9µg.m3 | 6* | January 2025 | https://www.thanet.gov.uk/wp-content/uploads/2018/03/Thanet-Detailed-Assessment-v1.0.pdf |
Ramsgate AQMA was revoked in September 2024 after 6 years of consecutive compliance with the annual mean NO2 air quality objective. An Air Quality Strategy 2025 for Thanet District council is currently being drafted.
☒ Thanet District Council confirm the information on UK-Air regarding their AQMA(s) is up to date
☒ Thanet District Council confirm that all current AQAPs have been submitted to Defra.
* Except for one diffusion tube monitoring site recorded annual mean NO2 concentration within 10% below the annual mean NO2 concentration in 2019, all monitoring site recorded concentrations within the Ramsgate AQMA achieved compliance with the AQS.
Defra’s appraisal of last year’s ASR concluded:
This will be continued in this year’s ASR.
All formatting issues have been amended in Thanet District Council’s 2025 ASR.
This will be continued in the 2025 ASR.
The 2025 ASR continues to present robust and detailed QA/QC procedures of diffusion tube monitoring.
The ASR Excel Spreadsheets submitted in previous years is no longer a requirement with the submission of the 2025 ASR.
PMcoarse values will correspond to the correct automatic monitoring station for the 2025 ASR.
This will be continued in this year’s ASR.
The 2025 ASR includes the bias adjustment factor in the relevant column heading .
The Council will aim to provide this approval in the 2025 ASR.
The Public Health Outcomes Framework and human health indicator D01 have been included in the 2025 ASR.
Thanet District Council has taken forward a number of direct measures during the current reporting year of 2025 in pursuit of improving local air quality. Details of all measures completed, in progress or planned are set out in Table 2.2. 20 measures are included within Table 2.2, with the type of measure and the progress Thanet District Council have made during the reporting year of 2024 presented. Where there have been, or continue to be, barriers restricting the implementation of the measure, these are also presented within Table 2.2.
More detail on these measures can be found in their respective Action Plans (in progress and will be transformed to Air Quality Strategy). Key completed measures are:
Thanet District council expects the following measures to be completed over the course of the next reporting year:
Thanet District Council’s priorities for the coming year are to produce a Thanet wide AQ strategy to ensure better air quality for public health. Thanet’s 2025 AQS is in the final draft stages and is looking to be published this autumn.
Thanet District Council worked to implement these measures in partnership with the following stakeholders during 2024:
Table 2.2 – Progress on Measures to Improve Air Quality
Measure No. | Measure Title | Category | Classification | Year Measure Introduced in AQAP | Estimated / Actual Completion Date | Organisations Involved | Funding Source | Defra AQ Grant Funding | Funding Status | Estimated Cost of Measure | Measure Status | Reduction in Pollutant / Emission from Measure | Key Performance Indicator | Progress to Date | Comments / Barriers to Implementation |
1 | Parking Strategy | Traffic Management | Emission based parking or permit charges | 2025 | Local Authority Parking Dept | - | No | Not Funded | - | Planning | - | - | Ongoing | Thanet Council adopted its first Parking Strategy in Dec 2024. A key theme within the strategy is promoting active and sustainable transport and prioritising measures that deliver cleaner air. Subject to financial constraints: lack of funding, competing budgets and cost of associated infrastructure upgrades. | |
2 | Digital Training Resource for Health Care Professionals | Public Information | Via other mechanisms | 2022 | 2024 | Kent & Medway Air Quality Monitoring Network | Defra and LA contributions | YES | Partially Funded | £50k - £100k | Completed | - | - | Implementation on-going | A new Healthcare Professionals Training Platform has been launched across Thanet and Kent. Defra funding has supported the development of the Kent & Medway Air Quality Partnership digital platform for the Clean Air Academy, this includes Patient and Public resources. cleanairacademy.org.uk/ |
3 | Updated Thanet Air Quality Technical Planning Guidance | Policy Guidance and Development Control | Air Quality Planning and Policy Guidance | 2024 | 2025 | Local Authority Environmental Health, Local Authority Planning Dept.. | N/A | NO | Not Funded | Completed | - | - | Completed | All major development in Thanet shall be accompanied by an AQ assessment and Emission Mitigation Assessment as part of the planning application validation process. www.thanet.gov.uk/info-pages/air-quality/ Challenges include limited in-house expertise i.e. transport modelling and air quality dispersion modelling. | |
4 | Adoption of Anti Idling Powers | Traffic Management | Anti-idling enforcement | 2024 | 2024 | Local Authority Environmental Health, | N/A | NO | Not Funded | Completed | - | - | Implementation on-going | Thanet has adopted anti idling powers to enable effective campaigning and enforcement in areas of poor air quality. The campaign will be supported by a new handheld emissions monitor which can measure PM10/PM2.5 and NO2 for awareness / behavioural change opportunities. Barriers: conflicting priorities between parking and environmental health departments. | |
5 | Clean Air Schools Campaign | Public Information | Via other mechanisms | 2024 | 2025 | Local Authority Environmental Health, | N/A | Not Funded | - | Planning | - | - | Implementation On-going | Scheduled for 10 primary schools June 2025 | |
6 | Promotion of air quality issues, working with stakeholders | Public Information | Via the Internet | 2025 | Local Authority | - | No | Not Funded | - | - | - | Social media engagement | On-going | Kent & Medway Air Quality Partnership Communications Sub Group to work on Social Media Campaigns across the county. | |
7 | Kent and Medway Integrated Care Strategy | Policy Guidance | Other policy | 2022 | 2024 | Kent County Council | - | No | Not Funded | - | Implementation | - | - | Implementation On-going | Kent and Medway Integrated Care Partnership was formed in 2022 and combines the NHS and Kent and Medway County Councils to produce the Integrated Care Strategy. The strategy aspires to tackle the full range of health determinants to improve health and address inequalities including environmental factors such as improving air quality. www.kmhealthandcare.uk/about-us/vision-and-priorities/kent-and-medway-integrated-care-strategy |
8 | Kent and Medway Energy and Low Emissions Strategy | Policy Guidance and Development Control | Low Emissions Strategy | 2020 | 2023 | Kent County Council | - | No | Not Funded | - | Implementation | - | - | Implementation on-going | Kent and Medway Energy and Low Emission Strategy adopted and KCC travel plan monitoring officer appointed. |
9 | Thanet District Council Local Plan Adopted July 2020 | Policy Guidance and Development Control | Other policy | 2020 | 2031 | Local Authority Planning Department | Developer Contributions | No | Not Funded | - | Implementation | - | - | Implementation on-going | The LP contains many policies relevant to air quality improvements: SE05 specifically addresses air quality. |
10 | Thanet Transport Strategy 2015 -2031 | Policy Guidance and Development Control | Other policy | 2020 | - | Kent County Council Highways and Local Authority Strategic Planning Dept | - | No | Not Funded | - | Implementation | - | Inner Circuit Road, Thanet Parkway station | Implementation on-going | Although not yet formally adopted, KCC and TDC use to support adopted Local Plan. |
11 | Taxi Licensing Policy | Promoting Low Emission Transport | Taxi emission incentives | 2020 | 2025 | Local Authority Licensing Dept | - | - | - | - | Implementation | - | - | Underway | Promoting Euro 6 and incentivising ULEVs. Challenges: delays in policy adoption |
12 | ULEV funding application EV charging points for taxis | Promoting Low Emission Transport | Taxi emission incentives | 2019 | 2022 | Kent County Council and LA Environmental Health Dept | DfT | No | Funded | £10k - £50k | Completed | - | Number of chargers installed | Completed March 2021 | 2 x 2 rapid chargers in Market Street and Albion Road car parks |
13 | EV Points are maintained and available for the public | Promoting Low Emission Transport | Other | 2013 | - | Local Authority Parking Dept | - | - | - | - | - | - | Number of charges | Ongoing | Maintenance of EV point and back office. Challenges with applying for and obtaining funding. |
14 | Kent Realising Electric Van Scheme | Vehicle Fleet Efficiency | Promoting Low Emission Public Transport | 2021 | - | Kent County Council | DfT | - | - | £1 million - £10 million | Implementation | - | - | Ongoing | Electric van trials for business |
15 | Climate Emergency - Strategic Action Plan - Sustainable Council Housing | Policy Guidance and Development Control | Other policy | 2020 | 2025 | Local Authority Strategic Housing | LA, Homes England & Brownfield Release Fund - | - | - | - | - | - | - | Awaiting formal adoption | Improved energy efficiency of Council Housing Stock. 49 new EPC A-rated homes that will be completed by the spring of 2026 |
16 | Tenant and Leaseholder Services: Our Journey to Net Zero | Other | Other | 2020 | 2030 | Local Authority Strategic Housing | SHDF2.1 WH:SHF 3.0 / Homes England, LA | - | - | - | - | - | - | Ongoing | Improved energy efficiency of rental sector |
17 | Kent air website development | Public Information | Via the Internet | 2021 | 2022 | Kent & Medway Air Quality Monitoring Network | LAs, KCC & Medway UKHSA | No | - | £10k - £50k | Completed | - | - | Completed | Improvements to kentair.org.uk/ website |
18 | Pollution Patrol School Resource | Public Information | Via other mechanisms | 2022 | - | Local Authority Environmental Health, & K&MAQP | Defra and LA contributions | YES | Partially Funded | <£10k | On-going | - | - | Implementation On-going | Further school engagement planned over coming year to promote Pollution Patrol resources in schools within ne AQMA |
19 | TDC Net Zero Action Plan 2024 and Strategy | Policy Guidance and Development Control | Low Emissions Strategy | 2022 | Local Authority Climate Change | No | Not Funded | - | Completed | - | - | Implementation On-going | The council is seeking formal adoption of the Council’s Net Zero Strategy and associated energy efficient Housing Strategies. | ||
20 | Cycling and Walking audit to identify areas for improvement | Alternatives to private vehicle use | Promotion of cycling | 2023 | 2023 | Local Authority | DfT | No | Funded | £10k - £50k | Planning | - | Number of cyclists/walkers | Planning | Working with Sustrans to support development plans to connect rural areas. The Council will be consulting on the draft Thanet Cycling & Walking Infrastructure Plan (TCWIP) to bid for further project funding to deliver route schemes. |
As detailed in Policy Guidance LAQM.PG22 (Chapter 8) and the Air Quality Strategy[9], local authorities are expected to work towards reducing emissions and/or concentrations of fine particulate matter (PM2.5)). There is clear evidence that PM2.5 (particulate matter smaller 2.5 micrometres) has a significant impact on human health, including premature mortality, allergic reactions, and cardiovascular diseases.
No monitoring of PM2.5 is currently conducted within Thanet, however the two automatic monitoring sites located at Ramsgate and Birchington monitor PM10 concentrations. As per LAQM.TG(22) guidance, PM2.5 concentrations can be estimated from monitored PM10 concentrations. It is possible to estimate PM2.5 concentrations by using a local or national factor. In this case the most conservative approach was used and so the national factor was selected to estimate PM2.5 values at both Ramsgate ad Birchington automatic monitoring stations.
The 2024 national PMcoarse value for roadside sites as found on the LAQM website[10], is 6.0. Applied to the 2024 PM10 annual mean concentrations of 23.8µg/m3 and 18.8µg/m3 at Ramsgate and Birchington respectively, this gives an estimated PM2.5 annual mean of 17.8µg/m3 and 12.8µg/m3 respectively. The estimated annual mean concentration at both monitoring stations is below the indicative stage II annual mean limit value for PM2.5 (20µg/m3).
The Department of Health’s Public Health Outcomes Framework[11] has a number of public health indicators that are used for public health actions, to identify areas of health inequality and concern, and monitor the differences in health impacts across regions in the UK. This framework includes an indicator “D01- Fraction of Mortality Attributable to Particulate Air Pollution” which is calculated using background annual average PM2.5 concentrations, modelled at a 1km2 resolution based on measured concentrations from the AURN. Thanet has a 4.9% fraction of mortality calculated for 2023, which is lower than the average for England overall (5.2%), and lower than the South East Region (5.1%). The 2023 data is presented as the 2024 dataset has not been made available at the time of writing.
Many of the measures employed by Thanet District Council aim to reduce vehicular travel frequency and time, such as the encouragement of active travel. NOx and PM2.5 emissions arise from vehicular sources, and therefore although the measures pursued by Thanet District Council focus on reducing NO2 concentrations many of these will also likely have a positive impact on reducing PM2.5 concentrations.
Thanet District Council has been working with members of KMAQP and KCC on the production of a Kent and Medway Energy and Low Emissions Strategy. The implementation plan 2020-2023 was adopted in October 2020 and updated in May 2021.
The planning regime is also important for reducing PM2.5 concentrations. With the formal adoption of the Thanet Local Plan in 2020, the updated Air Quality Policy SE05 focuses on ensuring that all future developments produce an Air Quality and/or Emissions Mitigation Assessment to prevent the users and local area are not adversely impacted by air quality. This also promotes developments to encourage the use of sustainable and low emissions transport. The Thanet Transport Strategy is also included within the Local Plan and sets out improvements which will also benefit the reduction of PM2.5 concentrations.
Thanet District Council does not have any smoke control areas; however it does provide guidance on “Smoke and Bonfires”[12] in order to reduce air pollution arising from these. This includes guidelines for burning waste as part of a bonfire, the use of wood burners and stoves, information on the ban on the sale of wet wood and coal but also sets out how to make a nuisance complaint if required.
This section sets out the monitoring undertaken within 2024 by Thanet District Council and how it compares with the relevant air quality objectives. In addition, monitoring results are presented for a five-year period between 2020 and 2024 to allow monitoring trends to be identified and discussed.
Thanet District Council undertook automatic (continuous) monitoring at two sites during 2024. Table A.1 in Appendix A shows the details of the automatic monitoring sites. The Kent Air Data page presents automatic monitoring results for Thanet District Council, with automatic monitoring results also available through the UK-Air website .
Maps showing the location of the monitoring sites are provided in Appendix D. Further details on how the monitors are calibrated and how the data has been adjusted are included in Appendix C.
Thanet District Council undertook non- automatic (i.e. passive) monitoring of NO2 at 43 sites, including three triplicate sites bringing the total to 49 sites, during 2024. Table A.2 in Appendix A presents the details of the non-automatic sites.
Maps showing the location of the monitoring sites are provided in Appendix D Further details on Quality Assurance/Quality Control (QA/QC) for the diffusion tubes, including bias adjustments and any other adjustments applied (e.g. annualisation and/or distance correction), are included in Appendix C.
The air quality monitoring results presented in this section are, where relevant, adjusted for bias, annualisation (where the annual mean data capture is below 75% and greater than 25%), and distance correction. Further details on adjustments are provided in Appendix C.
Table A.3 and Table A.4 in Appendix A compare the ratified and adjusted monitored NO2 annual mean concentrations for the past five years with the air quality objective of 40µg/m3. Note that the concentration data presented represents the concentration at the location of the monitoring site, following the application of bias adjustment and annualisation, as required (i.e. the values are exclusive of any consideration to fall-off with distance adjustment).
In 2024, monitored NO2 concentrations across Thanet District Council decreased at all but six existing monitoring locations compared to 2023. The six diffusion tube locations where annual NO2 concentrations increased were at TH16, TH26, TH31, TH89, TH95 and TH98. A general continuous decreasing trend is seen in annual mean NO2 concentrations overall since 2019, if 2020 and 2021 are discounted due to COVID-19. All monitoring locations recorded annual mean NO2 concentrations below the annual mean NO2 air quality objective in 2024. The highest monitored NO2 concentration in 2024 is 27.9µg/m3 at triplicate site TH70, TH71, TH72.The average reduction of NO2 concentration from 2023 to 2024 is 1.2µg/m3.
For diffusion tubes, the full 2024 dataset of monthly mean values is provided in Appendix B. Note that the concentration data presented in Table B.1 includes distance corrected values, only where relevant.
Table A.5 in Appendix A compares the ratified continuous monitored NO2 hourly mean concentrations for the past five years with the air quality objective of 200µg/m3, not to be exceeded more than 18 times per year.
During 2024 there were no exceedances of the NO2 hourly objective of 200μg/m3, with the maximum hourly concentration recorded at the two automatic monitoring stations being 122.3μg/m3 (ZH5 Birchington Road) and 76.1μg/m3 (ZH4 Ramsgate). In addition, no single diffusion tube recorded an annual mean concentration greater than 60μg/m3, indicating that it is unlikely that the 1-hour objective was exceeded at any diffusion tube monitoring site in 2024.
In summary, relative to the previous reporting year, the NO2 annual mean concentrations have decreased at all but six existing diffusion tube sites and all reported concentrations were below the NO2 annual mean AQS objective (40μg/m3) in 2024. The NO2 annual mean concentration recorded at the two automatic monitoring sites were lower than concentrations recorded in 2023 and well below the AQS objective. Annual NO2 concentrations of 14.5μg/m3 (ZH4 Ramsgate) and 21.7μg/m3 (ZH5 Birchington) were recorded in 2024. Therefore, both the annual mean and hourly objective of NO2 was not breached during 2024.
Monitored PM10 concentrations were well below the annual mean PM10 air quality objective 40µg/m3 at both automatic monitoring locations in 2024. Concentrations of PM10 have shown a decreasing trend at ZH5 Birchington from 2020-2023 with a very slight increase in observed annual mean concentration in 2024. Concentrations of PM10 at ZH4 Ramsgate have fluctuated in the past five years with concentrations in 2024 lower than levels in 2023. This is likely in part due to the major development occurring in Boundary Rd gas work site remediation for development to a new large retail unit and residential site. Overall, concentrations of PM10 are well below the annual mean PM10 air quality objective of 40µg/m3.
Table A.6 in Appendix A: Monitoring Results compares the ratified and adjusted monitored PM10 annual mean concentrations for the past five years with the air quality objective of 40µg/m3.
Table A.7 in Appendix A compares the ratified continuous monitored PM10 daily mean concentrations for the past five years with the air quality objective of 50µg/m3, not to be exceeded more than 35 times per year.
Thanet Council does not currently undertake monitoring of PM2.5, however the two automatic monitoring sites located at Ramsgate and Birchington monitor PM10 concentrations. As per LAQM.TG(22) guidance, PM2.5 concentrations can be estimated from monitored PM10 concentrations. It is possible to estimate PM2.5 concentrations by using a local or national factor. In this case the most conservative approach was used and so the national factor was selected to estimate PM2.5 values at both Ramsgate and Birchington automatic monitoring station.
The methodology detailed within Box 7.7 of LAQM.TG(22) has been followed to calculate a national derived PMcoarse value of 6.0. Applied to the 2024 PM10 annual mean concentrations of 23.8µg/m3 and 18.8µg/m3 at Ramsgate and Birchington respectively, this gives an estimated PM2.5 annual mean of 17.8µg/m3 and 12.8µg/m3 respectively. The estimated annual mean concentration at both monitoring stations is below to the indicative stage II annual mean limit value for PM2.5 (20µg/m3).
Table A.1 – Details of Automatic Monitoring Sites
Site ID | Site Name | Site Type | X OS Grid Ref (Easting) | Y OS Grid Ref (Northing) | Pollutants Monitored | In AQMA? Which AQMA? | Monitoring Technique | Distance to Relevant Exposure (m) (1) | Distance to kerb of nearest road (m) (2) | Inlet Height (m) |
Thanet Ramsgate (ZH4) | Boundary Road, Ramsgate | Roadside | 638483 | 165430 | NO2, PM10 | Yes – Thanet Urban AQMA | Chemiluminescent; beta attenuation | 16 | 4 | 2 |
Thanet Birchington (ZH5) | The Square, Birchington | Roadside | 630284 | 169052 | NO2, PM10 | Yes – Thanet Urban AQMA | Chemiluminescent; beta attenuation | 4 | 3 | 2 |
Notes:
(1) N/A if not applicable
(2) 0m if the monitoring site is at a location of exposure (e.g. installed on the façade of a residential property).
Table A.2 – Details of Non-Automatic Monitoring Sites
Diffusion Tube ID | Site Name | Site Type | X OS Grid Ref (Easting) | Y OS Grid Ref (Northing) | Pollutants Monitored | In AQMA? Which AQMA? | Distance to Relevant Exposure (m) (1) | Distance to kerb of nearest road (m) (2) | Tube Co-located with a Continuous Analyser? | Tube Height (m) |
TH05 | THE BROADWAY BROADSTAIRS | Kerbside | 639019 | 167982 | NO2 | No | N/A | 2.5 | No | 2.5 |
TH10 | COLLEGE ROAD MARGATE | Kerbside | 635539 | 169839 | NO2 | No | 0.0 | 2.0 | No | 2.5 |
TH13, TH46, TH47 | BIRCHINGTON SQUARE 3 | Kerbside | 630254 | 169037 | NO2 | No | 2.0 | 1.0 | No | 2.5 |
TH16 | EARLSMEDE CRESCENT CLIFFSEND | Urban Background | 634444 | 164416 | NO2 | No | 3.0 | N/A | No | 2.5 |
TH26 | KING STREET RAMSGATE | Kerbside | 638492 | 165409 | NO2 | No | 0.0 | 3.0 | No | 2.5 |
TH27 | AVEBURY AVENUE RAMSGATE | Urban Background | 639097 | 165970 | NO2 | No | 7.0 | N/A | No | 2.5 |
TH31 | HIGH STREET MANSTON | Urban Background | 634662 | 166026 | NO2 | No | 9.0 | N/A | No | 2.5 |
TH32 | BELL-DAVIES DRIVE MANSTON | Urban Background | 632994 | 166428 | NO2 | No | 10.0 | N/A | No | 2.5 |
TH33 | HILL HOUSE DRIVE MINSTER | Urban Background | 631160 | 165486 | NO2 | No | 9.0 | N/A | No | 2.5 |
TH34 | WESTWOOD RD, BROADSTAIRS (Pizza Hut) | Roadside | 636570 | 167894 | NO2 | No | N/A | 14.0 | No | 2.5 |
TH36 | STAR LANE, RAMSGATE RD, MARGATE | Kerbside | 636404 | 168227 | NO2 | No | 0.0 | 2.0 | No | 2.5 |
TH37 | KENTMERE AVE RAMSGATE | Suburban | 635932 | 165333 | NO2 | No | 10.0 | N/A | No | 2.5 |
TH48 | CANTERBURY RD, BIRCH (A28) (Yew Tree) | Kerbside | 630438 | 169111 | NO2 | No | 1.0 | 0.5 | No | 2.0 |
TH49 | CANTERBURY RD, BIRCH (A28) (Kent Gdns) | Roadside | 630186 | 168983 | NO2 | No | 3.0 | 3.5 | No | 2.5 |
TH51, TH52, TH53 | BOUNDARY RD, RAMSGATE 3 | Roadside | 638472 | 165432 | NO2 | No | 16.0 | 4.1 | Yes | 2.5 |
TH54 | 3 HIGH STREET, ST LAWRENCE | Roadside | 637135 | 165354 | NO2 | Ramsgate AQMA* | 7.0 | 1.0 | No | 2.5 |
TH55 | COXES LANE (M'GATE RD) RAMSGATE | Roadside | 636814 | 167297 | NO2 | No | 3.0 | 10.0 | No | 2.0 |
TH59 | CHURCH STREET, ST PETERS | Kerbside | 638220 | 168614 | NO2 | No | 3.0 | 2.0 | No | 2.5 |
TH66 | HIGH STREET, ST LAWRENCE - FAÇADE | Roadside | 637112 | 165331 | NO2 | Ramsgate AQMA* | 0.0 | 3.0 | No | 2.5 |
TH70, TH71, TH72 | 9 HIGH STREET, ST LAWRENCE 3 | Roadside | 637092 | 165340 | NO2 | Ramsgate AQMA* | 0.0 | 1.0 | No | 2.5 |
TH76 | BUENOS AYRES MARGATE | Roadside | 634752 | 170679 | NO2 | No | 9.5 | 12.0 | No | 2.0 |
TH77 | HIGH STREET, MINSTER | Kerbside | 630972 | 164708 | NO2 | No | 2.5 | 1.0 | No | 1.5 |
TH78 | MANSTON WAY WALK WWX | Roadside | 636014 | 167851 | NO2 | No | 8.0 | 2.5 | No | 2.0 |
TH80 | 58 NEWINGTON RD, RAMSGATE | Roadside | 636909 | 165780 | NO2 | Ramsgate AQMA* | 0.0 | 1.0 | No | 2.5 |
TH81 | MARGATE RD, RAMSGATE (Winifred) | Roadside | 637097 | 166799 | NO2 | No | 0.0 | 7.8 | No | 2.5 |
TH82 | WESTWOOD RD, BROADSTAIRS (St Georges) | Roadside | 637271 | 167873 | NO2 | No | 7.0 | 7.9 | No | 2.5 |
TH83 | RAMSGATE RD, MARGATE | Roadside | 635907 | 169266 | NO2 | No | 0.0 | 9.5 | No | 2.5 |
TH84 | NORTHDOWN RD, MARGATE | Kerbside | 635997 | 171095 | NO2 | No | 0.0 | 6.0 | No | 3.0 |
TH85 | 143 BOUNDARY RD, RAMSGATE | Roadside | 638026 | 165442 | NO2 | Ramsgate AQMA* | 0.0 | 0.0 | No | 3.0 |
TH87 | MARLOWE WAY | Roadside | 636198 | 166771 | NO2 | No | 2.0 | 1.0 | No | 2.5 |
TH89 | TOTHILL MINSTER | Kerbside | 631057 | 165478 | NO2 | No | 10.0 | 1.0 | No | 2.5 |
TH90 | MERIDIAN CL, RAMSGATE | Roadside | 636109 | 165766 | NO2 | No | 3.0 | 2.0 | No | 2.5 |
TH91 | SHOTTENDANE RD, MARGATE | Roadside | 635029 | 169494 | NO2 | No | 5.0 | 1.0 | No | 2.5 |
TH92 | CANTERBURY RD WESTGATE (Victoria Ave) | Roadside | 632695 | 169877 | NO2 | No | 5.0 | 2.0 | No | 2.5 |
TH93 | MINSTER RD, WESTGATE | Roadside | 632563 | 169291 | NO2 | No | 4.0 | 1.0 | No | 2.5 |
TH95 | PORT RAMSGATE | Urban Background | 637791 | 164087 | NO2 | No | 250.0 | 4.0 | No | 2.5 |
TH96 | 31A CHATHAM STREET, RAMSGATE | Kerbside | 637964 | 165426 | NO2 | Ramsgate AQMA* | 1.0 | 1.0 | No | 2.5 |
TH97 | 98 BOUNDARY RD | Kerbside | 637946 | 165460 | NO2 | Ramsgate AQMA* | 1.0 | 1.0 | No | 2.5 |
TH98 | 5 SHAR PLACE, RAMSGATE | Kerbside | 637927 | 165477 | NO2 | Ramsgate AQMA* | 3.0 | 1.0 | No | 2.5 |
TH99 | 37 PARK ROAD, RAMGATE | Roadside | 637598 | 165439 | NO2 | Ramsgate AQMA* | 3.0 | 1.0 | No | 2.5 |
TH100 | 13 NEWINGTON RD, RAMSGATE | Roadside | 637058 | 165400 | NO2 | Ramsgate AQMA* | 3.0 | 2.0 | No | 2.5 |
TH101 | ASHBURNHAM RD, RAMSGATE | Roadside | 636961 | 165140 | NO2 | Ramsgate AQMA* | 5.0 | 2.0 | No | 2.5 |
TH102 | CECIL STREET MARGATE | Roadside | 635455 | 170791 | NO2 | No | 0.0 | 2.0 | No | 2.5 |
Notes:
(1) 0m if the monitoring site is at a location of exposure (e.g. installed on the façade of a residential property).
(2) N/A if not applicable.
*Ramsgate AQMA was revoked in September 2024.
Table A.3 – Annual Mean NO2 Monitoring Results: Automatic Monitoring (µg/m3)
Site ID | X OS Grid Ref (Easting) | Y OS Grid Ref (Northing) | Site Type | Valid Data Capture for Monitoring Period (%) ⁽¹⁾ | Valid Data Capture for 2024 (%) ⁽²⁾ | 2020 | 2021 | 2022 | 2023 | 2024 |
Thanet Ramsgate (ZH4) | 638483 | 165430 | Roadside | 94.0 | 94.0 | 17.1 | 15.9 | 17.4 | 14.9 | 14.5 |
Thanet Birchington (ZH5) | 630284 | 169052 | Roadside | 94.3 | 94.3 | 29.3 | 24.3 | 24.6 | 22.0 | 21.7 |
☒ Annualisation has been conducted where data capture is <75% and >25% in line with LAQM.TG22
☒ Reported concentrations are those at the location of the monitoring site (annualised, as required), i.e. prior to any fall-off with distance correction
☒ Where exceedances of the NO2 annual mean objective occur at locations not representative of relevant exposure, the fall-off with distance concentration has been calculated and reported concentration provided in brackets for 2024
Notes:
The annual mean concentrations are presented as µg/m3.
Exceedances of the NO2 annual mean objective of 40µg/m3 are shown in bold.
All means have been “annualised” as per LAQM.TG22 if valid data capture for the full calendar year is less than 75%. See Appendix C for details.
Concentrations are those at the location of monitoring and not those following any fall-off with distance adjustment.
(1) Data capture for the monitoring period, in cases where monitoring was only carried out for part of the year.
(2) Data capture for the full calendar year (e.g. if monitoring was carried out for 6 months, the maximum data capture for the full calendar year is 50%).
Table A.4 – Annual Mean NO2 Monitoring Results: Non-Automatic Monitoring (µg/m3)
Diffusion Tube ID | X OS Grid Ref (Easting) | Y OS Grid Ref (Northing) | Site Type | Valid Data Capture for Monitoring Period (%) (1) | Valid Data Capture 2023 (%) (2) | 2020 | 2021 | 2022 | 2023 | 2024 |
TH05 | 639019 | 167982 | Kerbside | 92.5 | 92.5 | 25.1 | 23.3 | 25.9 | 22.4 | 19.6 |
TH10 | 635539 | 169839 | Kerbside | 90.6 | 90.6 | 28.2 | 24.5 | 28.8 | 23.3 | 22.3 |
TH13, TH46, TH47 | 630254 | 169037 | Kerbside | 100.0 | 100.0 | 31.7 | 30.3 | 32.3 | 27.7 | 23.3 |
TH16 | 634444 | 164416 | Urban Background | 100.0 | 100.0 | 13.9 | 12.8 | 13.5 | 10.2 | 12.9 |
TH26 | 638492 | 165409 | Kerbside | 100.0 | 100.0 | 25.3 | 25.6 | 26.6 | 21.7 | 22.0 |
TH27 | 639097 | 165970 | Urban Background | 90.6 | 90.6 | 13.8 | 12.0 | 13.0 | 11.2 | 10.1 |
TH31 | 634662 | 166026 | Urban Background | 100.0 | 100.0 | 11.3 | 11.6 | 12.3 | 9.2 | 9.3 |
TH32 | 632994 | 166428 | Urban Background | 83.0 | 83.0 | 13.0 | 12.2 | 13.4 | 10.6 | 10.3 |
TH33 | 631160 | 165486 | Urban Background | 100.0 | 100.0 | 12.5 | 12.6 | 14.1 | 12.3 | 10.3 |
TH34 | 636570 | 167894 | Roadside | 100.0 | 100.0 | 19.6 | 21.4 | 20.2 | 15.5 | 13.2 |
TH36 | 636404 | 168227 | Kerbside | 66.0 | 66.0 | 21.9 | 23.3 | 25.0 | 18.6 | 17.4 |
TH37 | 635932 | 165333 | Suburban | 100.0 | 100.0 | 14.5 | 12.3 | 14.2 | 11.6 | 10.7 |
TH48 | 630438 | 169111 | Kerbside | 100.0 | 100.0 | 23.4 | 21.5 | 24.9 | 20.9 | 17.4 |
TH49 | 630186 | 168983 | Roadside | 100.0 | 100.0 | 16.6 | 15.5 | 20.8 | 16.0 | 15.3 |
TH51, TH52, TH53 | 638472 | 165432 | Roadside | 100.0 | 100.0 | 17.0 | 16.3 | 18.5 | 14.5 | 14.1 |
TH54 | 637135 | 165354 | Roadside | 100.0 | 100.0 | 28.9 | 27.8 | 31.7 | 23.5 | 23.4 |
TH55 | 636814 | 167297 | Roadside | 92.5 | 92.5 | 21.1 | 21.3 | 19.9 | 18.1 | 16.9 |
TH59 | 638220 | 168614 | Kerbside | 83.0 | 83.0 | 25.3 | 22.8 | 28.9 | 23.6 | 21.5 |
TH66 | 637112 | 165331 | Roadside | 100.0 | 100.0 | 21.3 | 19.6 | 23.0 | 18.7 | 16.7 |
TH70, TH71, TH72 | 637092 | 165340 | Roadside | 100.0 | 100.0 | 30.7 | 30.8 | 35.2 | 28.3 | 27.9 |
TH76 | 634752 | 170679 | Roadside | 100.0 | 100.0 | 20.3 | 17.7 | 18.8 | 16.2 | 13.4 |
TH77 | 630972 | 164708 | Kerbside | 100.0 | 100.0 | 18.7 | 17.8 | 19.5 | 15.2 | 14.6 |
TH78 | 636014 | 167851 | Roadside | 90.6 | 90.6 | 16.0 | 19.3 | 17.5 | 12.4 | 10.8 |
TH80 | 636909 | 165780 | Roadside | 100.0 | 100.0 | 17.3 | - | - | 14.0 | 13.8 |
TH81 | 637097 | 166799 | Roadside | 100.0 | 100.0 | 17.9 | 17.0 | 18.9 | 15.3 | 13.7 |
TH82 | 637271 | 167873 | Roadside | 90.6 | 90.6 | 21.7 | 22.5 | 28.4 | 20.9 | 19.8 |
TH83 | 635907 | 169266 | Roadside | 75.0 | 75.0 | 15.7 | 15.0 | 17.7 | 13.0 | 12.4 |
TH84 | 635997 | 171095 | Kerbside | 90.6 | 90.6 | 20.7 | 17.6 | 20.0 | 15.9 | 13.5 |
TH85 | 638026 | 165442 | Roadside | 100.0 | 100.0 | 25.4 | 23.6 | 25.3 | 20.3 | 19.9 |
TH87 | 636198 | 166771 | Roadside | 100.0 | 100.0 | - | 13.9 | 13.9 | 11.3 | 10.6 |
TH89 | 631057 | 165478 | Kerbside | 90.6 | 90.6 | - | 19.3 | 20.3 | 16.1 | 16.3 |
TH90 | 636109 | 165766 | Roadside | 92.5 | 92.5 | - | 13.9 | 18.6 | 15.4 | 13.7 |
TH91 | 635029 | 169494 | Roadside | 83.0 | 83.0 | - | 13.7 | 13.9 | 11.9 | 10.4 |
TH92 | 632695 | 169877 | Roadside | 90.6 | 90.6 | - | 14.5 | 15.9 | 13.3 | 11.8 |
TH93 | 632563 | 169291 | Roadside | 100.0 | 100.0 | - | 14.5 | 14.2 | 13.0 | 11.4 |
TH95 | 637791 | 164087 | Urban Background | 83.0 | 83.0 | - | - | 20.8 | 11.7 | 11.9 |
TH96 | 637964 | 165426 | Roadside | 90.6 | 90.6 | - | - | - | 22.6 | 20.3 |
TH97 | 637946 | 165460 | Roadside | 92.5 | 92.5 | - | - | - | 25.5 | 24.2 |
TH98 | 637927 | 165477 | Roadside | 64.2 | 64.2 | - | - | - | 21.8 | 22.5 |
TH99 | 637598 | 165439 | Kerbside | 83.0 | 83.0 | - | - | - | 15.4 | 14.0 |
TH100 | 637058 | 165400 | Kerbside | 81.1 | 81.1 | - | - | - | 22.5 | 21.7 |
TH101 | 636961 | 165140 | Kerbside | 100.0 | 100.0 | - | - | - | 16.7 | 14.8 |
TH102 | 635455 | 170791 | Kerbside | 75.0 | 75.0 | - | - | - | 17.2 | 15.1 |
☒ Annualisation has been conducted where data capture is <75% and >25% in line with LAQM.TG22
☒ Diffusion tube data has been bias adjusted
☒ Reported concentrations are those at the location of the monitoring site (bias adjusted and annualised, as required), i.e. prior to any fall-off with distance correction
Notes:
The annual mean concentrations are presented as µg/m3.
Exceedances of the NO2 annual mean objective of 40µg/m3 are shown in bold.
NO2 annual means exceeding 60µg/m3, indicating a potential exceedance of the NO2 1-hour mean objective are shown in bold and underlined.
Means for diffusion tubes have been corrected for bias. All means have been “annualised” as per LAQM.TG22 if valid data capture for the full calendar year is less than 75%. See Appendix C for details.
Concentrations are those at the location of monitoring and not those following any fall-off with distance adjustment.
(1) Data capture for the monitoring period, in cases where monitoring was only carried out for part of the year.
(2) Data capture for the full calendar year (e.g. if monitoring was carried out for 6 months, the maximum data capture for the full calendar year is 50%).
Figure A.1 – Trends in Annual Mean NO2 Concentrations within the Ramsgate AQMA
Figure A.2 – Trends in Annual Mean NO2 Concentrations outside the AQMA in the North of the District
Figure A.3 – Trends in Annual Mean NO2 Concentrations outside the AQMA in the centre of the District
Figure A.4 – Trends in Annual Mean NO2 Concentrations outside the AQMA in the South of the District
Table A.5 – 1-Hour Mean NO2 Monitoring Results, Number of 1-Hour Means > 200µg/m3
Site ID | X OS Grid Ref (Easting) | Y OS Grid Ref (Northing) | Site Type | Valid Data Capture for Monitoring Period (%) (1) | Valid Data Capture 2024 (%) (2) | 2020 | 2021 | 2022 | 2023 | 2024 |
Thanet Ramsgate (ZH4) | 638483 | 165430 | Roadside | 94.0 | 94.0 | 0 | 0 | 0 | 0 | 0 |
Thanet Birchington (ZH5) | 630284 | 169052 | Roadside | 94.3 | 94.3 | 0 | 0 | 0 | 0 | 0 |
Notes:
Results are presented as the number of 1-hour periods where concentrations greater than 200µg/m3 have been recorded.
Exceedances of the NO2 1-hour mean objective (200µg/m3 not to be exceeded more than 18 times/year) are shown in bold.
If the period of valid data is less than 85%, the 99.8th percentile of 1-hour means is provided in brackets.
(1) Data capture for the monitoring period, in cases where monitoring was only carried out for part of the year.
(2) Data capture for the full calendar year (e.g. if monitoring was carried out for 6 months, the maximum data capture for the full calendar year is 50%).
Table A.6 – Annual Mean PM10 Monitoring Results (µg/m3)
Site ID | X OS Grid Ref (Easting) | Y OS Grid Ref (Northing) | Site Type | Valid Data Capture for Monitoring Period (%) (1) | Valid Data Capture 2024 (%) (2) | 2020 | 2021 | 2022 | 2023 | 2024 |
Thanet Ramsgate (ZH4) | 638483 | 165430 | Roadside | 95.6 | 95.6 | 22.6 | 24.5 | 22.3 | 25.6 | 23.8 |
Thanet Birchington (ZH5) | 630284 | 169052 | Roadside | 94.5 | 94.5 | 23.9 | 23.0 | 21.1 | 18.4 | 18.8 |
☒ Annualisation has been conducted where data capture is <75% and >25% in line with LAQM.TG22.
Notes:
The annual mean concentrations are presented as µg/m3.
Exceedances of the PM10 annual mean objective of 40µg/m3 are shown in bold.
All means have been “annualised” as per LAQM.TG22 if valid data capture for the full calendar year is less than 75%. See Appendix C for details.
(1) Data capture for the monitoring period, in cases where monitoring was only carried out for part of the year.
(2) Data capture for the full calendar year (e.g. if monitoring was carried out for 6 months, the maximum data capture for the full calendar year is 50%).
Figure A.5 – Trends in Annual Mean PM10 Concentrations
Table A.7 – 24-Hour Mean PM10 Monitoring Results, Number of PM10 24-Hour Means > 50µg/m3
Site ID | X OS Grid Ref (Easting) | Y OS Grid Ref (Northing) | Site Type | Valid Data Capture for Monitoring Period (%) (1) | Valid Data Capture 2024 (%) (2) | 2020 | 2021 | 2022 | 2023 | 2024 |
Thanet Ramsgate (ZH4) | 638483 | 165430 | Roadside | 95.6 | 95.6 | 13 | 0 | 7 | 6 | 4 |
Thanet Birchington (ZH5) | 630284 | 169052 | Roadside | 94.5 | 94.5 | 10 | 1 | 2 | 1 | 0 |
Notes:
Results are presented as the number of 24-hour periods where daily mean concentrations greater than 50µg/m3 have been recorded.
Exceedances of the PM10 24-hour mean objective (50µg/m3 not to be exceeded more than 35 times/year) are shown in bold.
If the period of valid data is less than 85%, the 90.4th percentile of 24-hour means is provided in brackets.
(1) Data capture for the monitoring period, in cases where monitoring was only carried out for part of the year.
(2) Data capture for the full calendar year (e.g. if monitoring was carried out for 6 months, the maximum data capture for the full calendar year is 50%).
Figure A.6 – Trends in Number of 24-Hour Mean PM10 Results > 50µg/m3
Table B.1 – NO2 2024 Diffusion Tube Results (µg/m3)
DT ID | X OS Grid Ref (Easting) | Y OS Grid Ref (Northing) | Jan | Feb | Mar | Apr | May | Jun | Jul | Aug | Sep | Oct | Nov | Dec | Annual Mean: Raw Data | Annual Mean: Annualised and Bias Adjusted (0.78) | Annual Mean: Distance Corrected to Nearest Exposure | Comment |
TH05 | 639019 | 167982 | 24.8 | 25.3 | 29.7 | 22.7 | 29.8 | 22.4 | 25.6 | 26.6 |
| 26.9 | 22.8 | 22.2 | 25.3 | 19.6 | - |
|
TH10 | 635539 | 169839 | 31.1 | 32.7 | 34.5 | 18.5 | 33.1 | 25.2 | 28.6 | 28.9 | 24.6 | 29.5 | 29.1 |
| 28.7 | 22.3 |
|
|
TH13, | 630254 | 169037 | 29.7 | 21.4 | 32.0 | 25.4 | 31.9 | 29.7 | 32.4 | 35.0 | 19.8 | 38.2 | 19.5 | 28.5 | - | - |
| Triplicate Site with TH13,TH46 and TH47 - Annual data provided for TH47 only |
TH46 | 630254 | 169037 | 31.7 | 22.0 | 34.2 | 24.4 | 32.0 | 31.8 | 30.4 | 36.4 | 31.7 | 33.6 | 29.0 | 29.7 | - | - |
| Triplicate Site with TH13, TH46 and TH47 - Annual data provided for TH47 only |
TH47 | 630254 | 169037 | 32.0 | 21.6 | 35.2 | 19.7 | 35.4 | 33.6 | 32.6 | 32.9 | 27.0 | 36.8 | 33.5 | 33.2 | 30.1 | 23.3 |
| Triplicate Site with TH13, TH46 and TH47 - Annual data provided for TH47 only |
TH16 | 634444 | 164416 | 17.2 | 15.9 | 11.5 | 12.6 | 13.1 | 11.5 | 49.2 | 13.7 | 10.3 | 14.1 | 17.5 | 13.8 | 16.7 | 12.9 |
|
|
TH26 | 638492 | 165409 | 29.5 | 32.4 | 29.5 | 28.1 | 30.7 | 27.8 | 27.6 | 26.8 | 23.8 | 28.8 | 28.5 | 27.0 | 28.4 | 22.0 |
|
|
TH27 | 639097 | 165970 | 14.8 |
| 15.6 | 10.4 | 16.0 | 10.5 | 12.8 | 11.6 | 10.1 | 12.7 | 15.8 | 12.7 | 13.0 | 10.1 |
|
|
TH31 | 634662 | 166026 | 13.5 | 14.8 | 14.4 | 9.3 | 14.1 | 8.6 | 13.7 | 10.2 | 8.7 | 12.5 | 13.6 | 11.2 | 12.1 | 9.3 |
|
|
TH32 | 632994 | 166428 | 13.4 |
| 12.3 | 11.4 | 16.3 |
| 12.9 | 12.5 | 11.9 | 15.0 | 14.2 | 13.2 | 13.3 | 10.3 |
|
|
TH33 | 631160 | 165486 | 14.3 | 15.8 | 15.7 | 10.2 | 15.4 | 10.2 | 11.9 | 12.2 | 11.8 | 15.3 | 12.5 | 13.8 | 13.3 | 10.3 |
|
|
TH34 | 636570 | 167894 | 14.7 | 20.8 | 20.2 | 13.8 | 19.6 | 13.9 | 16.4 | 16.9 | 15.9 | 20.1 | 14.4 | 17.4 | 17.0 | 13.2 |
|
|
TH36 | 636404 | 168227 | 22.1 | 25.3 |
| 19.0 | 24.3 | 18.5 |
| 23.0 | 22.0 |
| 25.0 |
| 22.4 | 17.4 |
|
|
TH37 | 635932 | 165333 | 12.1 | 17.7 | 16.3 | 12.1 | 15.8 | 9.6 | 13.9 | 12.4 | 10.3 | 15.4 | 14.4 | 15.1 | 13.8 | 10.7 |
|
|
TH48 | 630438 | 169111 | 23.3 | 27.3 | 21.7 | 17.0 | 25.4 | 19.7 | 21.0 | 21.7 | 20.8 | 24.7 | 22.0 | 24.7 | 22.4 | 17.4 |
|
|
TH49 | 630186 | 168983 | 19.5 | 30.5 | 21.9 | 12.0 | 17.5 | 15.7 | 20.5 | 19.5 | 17.4 | 21.0 | 21.9 | 19.5 | 19.7 | 15.3 |
|
|
TH51 | 638472 | 165432 | 20.5 | 23.2 | 22.7 | 16.5 | 21.6 | 16.0 | 18.5 | 16.4 | 15.2 | 19.3 | 20.2 | 17.1 | - | - |
| Triplicate Site with TH51, TH52 and TH53 - Annual data provided for TH53 only |
TH52 | 638472 | 165432 | 16.4 | 20.8 | 22.5 | 16.6 | 20.6 | 15.3 | 15.7 | 17.4 | 14.2 | 17.3 | 21.7 | 17.2 | - | - |
| Triplicate Site with TH51, TH52 and TH53 - Annual data provided for TH53 only |
TH53 | 638472 | 165432 | 21.0 | 19.7 | 15.4 | 15.0 | 20.7 | 16.4 | 17.9 | 17.0 | 14.8 | 17.5 | 19.6 | 17.3 | 18.2 | 14.1 |
| Triplicate Site with TH51, TH52 and TH53 - Annual data provided for TH53 only |
TH54 | 637135 | 165354 | 36.6 | 36.6 | 33.7 | 29.1 | 31.7 | 28.7 | 26.9 | 27.1 | 27.6 | 27.8 | 24.7 | 32.0 | 30.2 | 23.4 |
|
|
TH55 | 636814 | 167297 | 23.8 | 26.7 | 24.2 |
| 24.8 | 17.0 | 21.2 | 17.9 | 15.7 | 24.7 | 24.0 | 20.2 | 21.8 | 16.9 |
|
|
TH59 | 638220 | 168614 | 30.0 |
| 31.1 | 27.5 | 26.0 | 24.0 | 26.9 | 27.1 |
| 27.2 | 28.6 | 29.2 | 27.8 | 21.5 |
|
|
TH66 | 637112 | 165331 | 20.1 | 27.2 | 22.3 | 20.0 | 22.6 | 19.4 | 23.8 | 21.7 | 19.8 | 27.0 | 13.9 | 20.3 | 21.5 | 16.7 |
|
|
TH70 | 637092 | 165340 | 39.8 | 39.4 | 36.4 | 35.7 | 42.0 | 37.1 | 31.4 | 36.2 | 37.4 | 30.9 | 41.3 | 32.4 | - | - |
| Triplicate Site with TH70, TH71 and TH72 - Annual data provided for TH72 only |
TH71 | 637092 | 165340 | 35.5 | 38.8 | 34.1 | 37.1 | 41.0 | 36.8 | 32.0 | 33.4 | 35.2 | 35.5 | 34.7 | 31.9 | - | - |
| Triplicate Site with TH70, TH71 and TH72 - Annual data provided for TH72 only |
TH72 | 637092 | 165340 | 40.4 | 38.7 | 35.8 | 36.8 | 42.3 | 38.0 | 35.4 | 34.2 | 39.3 | 40.4 | 31.7 | 17.7 | 36.0 | 27.9 |
| Triplicate Site with TH70, TH71 and TH72 - Annual data provided for TH72 only |
TH76 | 634752 | 170679 | 12.7 | 23.2 | 10.6 | 15.3 | 25.0 | 14.8 | 18.0 | 18.5 | 16.5 | 22.6 | 9.6 | 20.0 | 17.2 | 13.4 |
|
|
TH77 | 630972 | 164708 | 22.4 | 22.4 | 19.0 | 14.9 | 20.0 | 16.5 | 16.0 | 17.3 | 15.9 | 17.6 | 24.2 | 19.9 | 18.8 | 14.6 |
|
|
TH78 | 636014 | 167851 | 16.9 | 19.3 | 18.3 | 13.1 | 18.7 | 6.6 | 14.1 | 13.4 | 14.0 |
| 4.4 | 13.9 | 13.9 | 10.8 |
|
|
TH80 | 636909 | 165780 | 21.1 | 19.8 | 19.4 | 15.2 | 21.7 | 15.7 | 15.6 | 16.3 | 17.7 | 20.0 | 14.5 | 16.3 | 17.8 | 13.8 |
|
|
TH81 | 637097 | 166799 | 19.7 | 22.4 | 22.4 | 15.4 | 21.1 | 15.6 | 17.1 | 19.1 | 11.8 | 20.0 | 10.3 | 17.9 | 17.7 | 13.7 |
|
|
TH82 | 637271 | 167873 | 28.0 | 28.1 | 28.5 | 20.3 | 30.2 | 22.7 | 24.0 | 25.6 | 25.6 | 29.6 | 19.0 |
| 25.6 | 19.8 |
|
|
TH83 | 635907 | 169266 | 19.0 | 18.9 |
| 14.3 | 20.9 | 13.5 | 14.8 | 15.0 | 14.5 | 12.7 |
|
| 16.0 | 12.4 |
|
|
TH84 | 635997 | 171095 | 21.9 | 25.4 | 21.2 | 9.3 | 19.4 | 14.8 | 16.7 | 18.2 | 16.1 |
| 7.6 | 20.4 | 17.4 | 13.5 |
|
|
TH85 | 638026 | 165442 | 28.8 | 31.5 | 29.1 | 20.9 | 26.5 | 22.1 | 28.8 | 23.6 | 21.6 | 25.5 | 26.2 | 22.9 | 25.6 | 19.9 |
|
|
TH87 | 636198 | 166771 | 16.7 | 17.4 | 15.4 | 12.9 | 17.2 | 10.8 | 12.0 | 12.8 | 11.3 | 16.2 | 6.9 | 14.5 | 13.7 | 10.6 |
|
|
TH89 | 631057 | 165478 | 21.6 | 21.0 | 23.1 | 19.4 | 26.2 | 18.8 | 15.6 |
| 25.0 | 24.6 | 16.6 | 18.8 | 21.0 | 16.3 |
|
|
TH90 | 636109 | 165766 |
| 22.1 | 19.0 | 14.6 | 22.1 | 13.1 | 16.9 | 17.6 | 14.7 | 22.2 | 13.5 | 18.4 | 17.7 | 13.7 |
|
|
TH91 | 635029 | 169494 | 14.3 | 17.1 | 17.0 | 11.1 | 15.9 |
| 12.9 | 12.7 | 11.0 | 14.1 | 7.6 |
| 13.4 | 10.4 |
|
|
TH92 | 632695 | 169877 | 18.3 | 18.5 | 17.5 | 10.7 | 18.2 | 12.5 | 11.7 |
| 14.3 | 18.8 | 9.6 | 17.6 | 15.2 | 11.8 |
|
|
TH93 | 632563 | 169291 | 18.4 | 16.3 | 20.2 | 12.5 | 16.6 | 10.5 | 11.8 | 13.6 | 12.9 | 17.3 | 10.0 | 15.8 | 14.7 | 11.4 |
|
|
TH95 | 637791 | 164087 |
| 15.8 | 16.5 | 12.1 | 21.1 | 13.2 | 15.2 | 16.2 | 11.8 | 15.4 | 16.4 |
| 15.4 | 11.9 |
|
|
TH96 | 637964 | 165426 | 28.7 | 28.5 | 29.7 | 24.1 | 36.4 | 27.1 | 25.6 | 24.1 | 21.2 |
| 22.3 | 20.9 | 26.2 | 20.3 |
|
|
TH97 | 637946 | 165460 |
| 34.8 | 31.2 | 29.6 | 42.8 | 33.1 | 30.0 | 29.7 | 32.1 | 27.9 | 31.0 | 20.7 | 31.2 | 24.2 |
|
|
TH98 | 637927 | 165477 |
|
| 27.8 | 26.1 | 32.5 | 24.5 | 23.7 | 24.3 | 22.4 |
| 30.3 |
| 26.5 | 22.5 |
|
|
TH99 | 637598 | 165439 |
| 20.2 | 21.0 | 15.2 | 20.4 | 14.0 | 18.6 | 17.6 | 15.1 | 20.5 | 17.9 |
| 18.1 | 14.0 |
|
|
TH100 | 637058 | 165400 | 34.8 | 32.9 | 30.5 | 27.8 |
| 26.2 | 26.4 | 27.4 | 24.7 | 24.0 | 25.5 |
| 28.0 | 21.7 |
|
|
TH101 | 636961 | 165140 | 20.4 | 20.2 | 21.7 | 17.1 | 21.3 | 15.8 | 18.4 | 17.0 | 22.4 | 16.1 | 19.8 | 18.6 | 19.1 | 14.8 |
|
|
TH102 | 635455 | 170791 | 10.9 | 27.7 | 23.2 | 11.8 | 22.3 | 20.4 | 19.5 | 20.8 |
|
|
| 18.6 | 19.5 | 15.1 |
|
|
☒ All erroneous data has been removed from the NO2 diffusion tube dataset presented in Table B.1.
☒ Annualisation has been conducted where data capture is <75% and >25% in line with LAQM.TG22.
☒ Local bias adjustment factor used.
☐ National bias adjustment factor used.
☒ Where applicable, data has been distance corrected for relevant exposure in the final column.
☒ Thanet District Council confirm that all 2024 diffusion tube data has been uploaded to the Diffusion Tube Data Entry System.
Notes:
Exceedances of the NO2 annual mean objective of 40µg/m3 are shown in bold.
NO2 annual means exceeding 60µg/m3, indicating a potential exceedance of the NO2 1-hour mean objective are shown in bold and underlined.
See Appendix C for details on bias adjustment and annualisation.
In 2025 Thanet District council updated its Air Quality Technical Planning guidance[13]. This was produced in conjunction with Kent and Medway Air Quality Partnership and sets out the approach for considering air quality that should be adopted from pre-application stage through to submitting details as part of the planning application. The process determines whether a development does not require any assessment and/or mitigation or if the development requires an air quality assessment and/or emissions mitigation assessment.
The following planning applications within the Thanet District Council area were granted permission in 2024 and identified to have the potential to impact on air quality in the district. All developments within the Thanet AQMA with more than 10 residential units with car parking provision are required to have EV charging points. Table C.1 details a list of planning applications which were commented on by the Environmental Health Department in terms of air quality. If it is a major development, then Thanet District Council are requesting that an Emissions Mitigation Assessment (EMA) is completed, and in some cases an Air Quality Assessment (AQA).
Table C.1 – Planning Applications with Air Quality Conditions in 2024
Reference | Location | Details | Status | Comments |
F/TH/23/1209 | Land East and West of Hengrove Farm Shottendane Road, Margate, Kent, CT9 4NH | Solar farm | 28 August 2024 | Negligible AQ impacts |
OL/TH/23/1606 | Land To The East Of New Haine Road RAMSGATE Kent | 9,253 sqm, Primary medical care facility, 70no. self contained flats, a 80no. bed care home, and a childrens nursery | Approved 24th September 2024 | AQ Assessment undertaken |
F/TH/23/1475 | Land On The West Side Of Tothill Street RAMSGATE Kent | Erection of 36no. dwellings | Approved 4th October 2024 | AQ Assessment submitted |
F/TH/23/1352 | Land At Staner Court Manston Road RAMSGATE Kent | 9 No 3-bed and 2 No 4-bed two story dwellings | 31st January 2024 | AQ Assessment submitted |
F/TH/23/1343 | Garage Blocks At Tomlin Drive MARGATE Kent | 3-bed semi detached dwellings and 4No three storey 4-bed terraced dwellings | 31st Jan 2024 | AQ Assessment submitted |
F/TH/21/0671 | Land To The North Of Fairlawn Road And The West Of Northwood Road Broadstairs Kent | 4no. 1-bed flats, 4no. 2-bed dwellings, 8no 3-bed dwellings, and 17no 4-bed dwellings (single to 3-storey in height), and erection of part 2-storey, part 3-storey detached building accommodating 4no. 2-bed flats and 1no. 3-bed flat, | 25th July 2024 | Emissions Mitigation Assessment £22k damage costs |
Thanet District Council has not completed any additional works within the reporting year of 2024.
The diffusion tubes for the year 2024 were supplied and analysed by SOCOTEC Didcot, the tubes were prepared using the 50% TEA in acetone preparation method.
SOCOTEC is a UKAS accredited laboratory and participates in the AIR-PT Scheme for NO2 tube analysis and the Annual Field Inter-Comparison Exercise. These provide strict performance criteria for participating laboratories to meet, thereby ensuring NO2 concentrations reported are of a high calibre. The latest available AIR-PT results in 2024 are AIR-PT AR055 (January – February 2024), AIR-PT AR056 (April– June 2024), AIR-PT AR058 (July – August 2024) and AIR-PT AR059 (September – October 2024), in which SOCOTEC all scored 100%. The percentage score reflects the results deemed to be satisfactory based upon the z-score of < ± 2. Data from November 2024 onwards was not available at the time of writing.
The precision of the current 33 local authority co-location studies in 2024 detailed within the national bias adjustment factor spreadsheet (version 04/25) was rated as ‘good’ (tubes are considered to have "good" precision where the coefficient of variation of duplicate or triplicate diffusion tubes for eight or more periods during the year is less than 20%). Further information on the precision summary results can be found on the LAQM website.
Monitoring in 2024 had been completed in adherence with the 2024 Diffusion Tube Monitoring Calendar, whereby all changeovers were completed within ±2 days of the specified date.
The 2024 national bias adjustment factor for SOCOTEC 50% TEA in acetone preparation method is 0.78.
Figure C.1 – Bias Adjustment Factor Database
As per LAQM.TG(22), annualisation is required for any site which has a data capture of less than 75%, but greater than 25%. Annualisation was therefore required to be completed for three diffusion tube monitoring sites. The two closest continuous monitoring background locations which were selected to annualise the data were:
These sites have a data capture of >85% and therefore could be used for annualisation.
Table C.2 presents the annualisation summary and is taken directly from the Diffusion Tube Data Processing Tool.
Table C.2 – Annualisation Summary (concentrations presented in µg/m3)
Site ID | Annualisation Factor Thurrock | Annualisation Factor Southend-on-Sea | Average Annualisation Factor | Raw Data Annual Mean | Annualised Annual Mean |
TH36 | 0.9954 | 1.0106 | 1.0030 | 22.4 | 22.5 |
TH98 | 1.0757 | 1.1167 | 1.0962 | 26.5 | 29.0 |
The diffusion tube data presented within the 2024 ASR have been corrected for bias using an adjustment factor. Bias represents the overall tendency of the diffusion tubes to under or over-read relative to the reference chemiluminescence analyser. LAQM.TG22 provides guidance with regard to the application of a bias adjustment factor to correct diffusion tube monitoring. Triplicate co-location studies can be used to determine a local bias factor based on the comparison of diffusion tube results with data taken from NOx/NO2 continuous analysers. Alternatively, the national database of diffusion tube co-location surveys provides bias factors for the relevant laboratory and preparation method.
Thanet District Council have applied a local bias adjustment factor of 0.78 to the 2024 monitoring data. A summary of bias adjustment factors used by Thanet District Council over the past five years is presented in Table C.3. The 2024 national bias adjustment factor for SOCOTEC 50% TEA in acetone preparation method has the same value of 0.78 the local bias adjustment factor. The co-located diffusion tubes show a good overall precision and the co-located continuous monitor has a data capture of 92%. Therefore, the local bias adjustment is considered to be representative.
Table C.3 – Bias Adjustment Factor
Monitoring Year | Local or National | If National, Version of National Spreadsheet | Adjustment Factor |
2024 | Local | - | 0.78 |
2023 | Local | - | 0.78 |
2022 | Local | - | 0.82 |
2021 | National | 03/22 | 0.78 |
2020 | Local | - | 0.82 |
Table C.4 – Local Bias Adjustment Calculation
Local Bias Adjustment Input 1 | |
Periods used to calculate bias | 10 |
Bias Factor A | 0.78 (0.74 – 0.81) |
Bias Factor B | 29% (23% -25%) |
Diffusion Tube Mean (µg/m3) | 18.3 |
Mean CV (Precision) | 5.7% |
Automatic Mean (µg/m3) | 14.2 |
Data Capture | 92% |
Adjusted Tube Mean (µg/m3) | 14 (14 - 15) |
Notes:
A single local bias adjustment factor has been used to bias adjust the 2024 diffusion tube results.
Wherever possible, monitoring locations are representative of exposure. However, where this is not possible, the NO2 concentration at the nearest location relevant for exposure has been estimated using the Diffusion Tube Data Processing Tool/NO2 fall-off with distance calculator available on the LAQM Support website. Where appropriate, non-automatic annual mean NO2 concentrations corrected for distance are presented in Table B.1.
Distance correction was not required at any NO2 diffusion tube monitoring locations within Thanet during 2024.
QA/QC of the two automatic monitoring stations within the Thanet district are undertaken by Ricardo AEA on an annual basis. QA/QC programmes include an established schedule of regular site calibrations, site service and audits, verification and ratification of all measured data and documentation of all procedures. Calibrations are undertaken in accordance with Kentair and Ricardo AEA procedures. Daily data checks are undertaken and data downloads twice a day. Data Ratification is a detailed manual check of the data set carried out on a quarterly basis for the KMAQN and AURN sites covered by the full QA/QC process. The data for 2024 is fully ratified for both sites.
The type of PM10 monitor utilised within Thanet District Council do not require the application of a correction factor.
All automatic monitoring locations within Thanet District Council recorded data capture of
greater than 75% therefore it was not required to annualise any monitoring data. In
addition, any sites with a data capture below 25% do not require annualisation.
Wherever possible, monitoring locations are representative of exposure. However, where this is not possible, the NO2 concentration at the nearest location relevant for exposure has been estimated using the NO2 fall-off with distance calculator available on the LAQM Support website. Where appropriate, automatic annual mean NO2 concentrations corrected for distance are presented in Table A.3.
Distance correction was not required at any NO2 automatic monitoring locations within Thanet during 2024.
Figure D.2 – Detailed Map of Ramsgate AQMA
Figure D.3 – Map of Automatic Monitoring Sites
Figure D.4 – Map of Non-Automatic Monitoring Sites
Figure D.5 – Map of Monitoring Locations in Birchington
Figure D.6 – Map of Monitoring Locations in Minster
Figure D.7 – Map of Monitoring Locations in Cliffsend, Ramsgate
Figure D.8 – Map of Monitoring Locations in Westwood
Figure D.9 – Map of Monitoring Locations in Margate and Westgate-on-Sea
Figure D.10 – Map of Monitoring Locations at the now revoked Ramsgate AQMA
Table E.1 – Air Quality Objectives in England[14]
Pollutant | Air Quality Objective: Concentration | Air Quality Objective: Measured as |
Nitrogen Dioxide (NO2) | 200µg/m3 not to be exceeded more than 18 times a year | 1-hour mean |
Nitrogen Dioxide (NO2) | 40µg/m3 | Annual mean |
Particulate Matter (PM10) | 50µg/m3, not to be exceeded more than 35 times a year | 24-hour mean |
Particulate Matter (PM10) | 40µg/m3 | Annual mean |
Sulphur Dioxide (SO2) | 350µg/m3, not to be exceeded more than 24 times a year | 1-hour mean |
Sulphur Dioxide (SO2) | 125µg/m3, not to be exceeded more than 3 times a year | 24-hour mean |
Sulphur Dioxide (SO2) | 266µg/m3, not to be exceeded more than 35 times a year | 15-minute mean |
Abbreviation | Description |
AQAP | Air Quality Action Plan - A detailed description of measures, outcomes, achievement dates and implementation methods, showing how the local authority intends to achieve air quality limit values’ |
AQMA | Air Quality Management Area – An area where air pollutant concentrations exceed / are likely to exceed the relevant air quality objectives. AQMAs are declared for specific pollutants and objectives |
ASR | Annual Status Report |
Defra | Department for Environment, Food and Rural Affairs |
DMRB | Design Manual for Roads and Bridges – Air quality screening tool produced by National Highways |
LAQM | Local Air Quality Management |
NO2 | Nitrogen Dioxide |
NOx | Nitrogen Oxides |
PM10 | Airborne particulate matter with an aerodynamic diameter of 10µm or less |
PM2.5 | Airborne particulate matter with an aerodynamic diameter of 2.5µm or less |
QA/QC | Quality Assurance and Quality Control |
SO2 | Sulphur Dioxide |
[1] UK Health Security Agency. Chemical Hazards and Poisons Report, Issue 28, 2022.
[2] Available at: https://www.thanet.gov.uk/info-pages/air-quality/
[3] Defra. Environmental Improvement Plan 2023, January 2023
[4] Defra. Air Quality Strategy – Framework for Local Authority Delivery, August 2023
[5] DfT. The Road to Zero: Next steps towards cleaner road transport and delivering our Industrial Strategy, July 2018
[6] Electric Vehicle Guidance for Developers. Available at: https://www.thanet.gov.uk/info-pages/air-quality/
[7] Thanet District Council. Thanet Local Plan – 6 – Transport Strategy, July 2020.
[8] Care for KentAir available at [https://care-for-air.kentair.org.uk/]
[9] Defra. Air Quality Strategy – Framework for Local Authority Delivery, August 2023
[10] Defra. Estimating PM2.5 from PM10 Measurements
[11] Public Health Outcomes Framework: D01- Fraction of Mortality Attributable to Particulate Air Pollution
[12] Thanet District Council. Smoke and Bonfires webpage, available at: https://www.thanet.gov.uk/info-pages/smoke-and-bonfires/
[13] Thanet District Council. Air Quality Technical Planning Guidance – January 2025
[14] The units are in microgrammes of pollutant per cubic metre of air (µg/m3).