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2025 Air Quality Annual Status Report (ASR)
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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

Email

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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Company Number: 01758622

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 Thanet District council's logo

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2025 Air Quality Annual Status Report (ASR)

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

E-mail

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

Executive Summary: Air Quality in Our Area

Air Quality in Thanet District Council

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.

Actions to Improve Air Quality

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.

Conclusions and Priorities

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.

How to get Involved

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].

Table of Contents

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

Conclusions and Priorities        v

How to get Involved        vi

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        Individual Pollutants        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

Glossary of Terms        56

References        57

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

Local Air Quality Management

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.

Actions to Improve Air Quality

Air Quality Management Areas

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.

Progress and Impact of Measures to address Air Quality in Thanet District Council

Defra’s appraisal of last year’s ASR concluded:

  1. TDC has included and addressed the previous year’s appraisal report comments, which is commended.

This will be continued in this year’s ASR.

  1. There are a few formatting issues in the report, including Table 2.2 which is cut off as it doesn’t fit on the page. This should be amended before resubmission for completeness.

All formatting issues have been amended in Thanet District Council’s 2025 ASR.

  1. The Council has included the DTDES spreadsheet which is commended.

This will be continued in the 2025 ASR.

  1. QA/QC procedures of diffusion tube monitoring is robust and detailed. This is commended and the Council should continue this for future reports.

The 2025 ASR continues to present robust and detailed QA/QC procedures of diffusion tube monitoring.

  1. Table 2.1 in the ASR table excel spreadsheet hasn’t been filled in with the Ramsgate AQMA details, so it doesn’t not match that in the ASR report. This needs to be amended before resubmission.

The ASR Excel Spreadsheets submitted in previous years is no longer a requirement with the submission of the 2025 ASR.

  1. In section 2.3 of the report, the locally derived PMcoarse values for Birchington and Ramsgate have been mixed up. TDC should check this and amend if applicable.  

PMcoarse values will correspond to the correct automatic monitoring station for the 2025 ASR.

  1. All graphs are well-presented, and colours schemes allow for both monitoring sites and years to be easily distinguished, and maps illustrating the AQMA and monitoring sites.

This will be continued in this year’s ASR.

  1. Table B.1 is missing the bias adjustment factor from the column heading ‘Annual Mean: Annualised and Bias Adjusted <(x.x)>’. This should be amended before resubmission.

The 2025 ASR includes the bias adjustment factor in the relevant column heading .

  1. Although not sign off is not a requirement, Defra recommends that Directors of Public Health approve draft ASRs. This is recommended for the next annual reporting process too.

The Council will aim to provide this approval in the 2025 ASR.

  1. The Public Health Outcomes Framework and human health indicator D01 have been included in the 2024 ASR. This is welcome and TDC should continue to do this in future ASRs.

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.

PM2.5 – Local Authority Approach to Reducing Emissions and/or Concentrations

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.

Air Quality Monitoring Data and Comparison with Air Quality Objectives and National Compliance

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.

Summary of Monitoring Undertaken

Automatic Monitoring Sites

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.

Non-Automatic Monitoring Sites

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.

Individual Pollutants

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.

Nitrogen Dioxide (NO2)

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.

Particulate Matter (PM10)

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.

Particulate Matter (PM2.5)

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).

Appendix A: Monitoring Results

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

A graph showing 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

A graph showing 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

A graph showing 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

A graph showing 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

A graph showing 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

A graph showing Trends in Number of 24-Hour Mean PM10 Results > 50µg/m3


Appendix B: Full Monthly Diffusion Tube Results for 2024

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.

Appendix C: Supporting Technical Information / Air Quality Monitoring Data QA/QC

New or Changed Sources Identified Within Thanet District Council During 2024

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

Additional Air Quality Works Undertaken by Thanet District Council During 2025

Thanet District Council has not completed any additional works within the reporting year of 2024.

QA/QC of Diffusion Tube Monitoring

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 A screenshot of the national diffusion tube bias adjustment factor spreadsheet

Diffusion Tube Annualisation

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

Diffusion Tube Bias Adjustment Factors

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.

NO2 Fall-off with Distance from the Road

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 Automatic Monitoring

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.

PM10 and PM2.5 Monitoring Adjustment

The type of PM10 monitor utilised within Thanet District Council do not require the application of a correction factor.

Automatic Monitoring Annualisation

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.

NO2 Fall-off with Distance from the Road

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.

Appendix D: Map(s) of Monitoring Locations and now revoked AQMAs

Figure D.2 – Detailed Map of Ramsgate AQMA

A Detailed Map of Ramsgate AQMA

Figure D.3 – Map of Automatic Monitoring Sites

A Map of Automatic Monitoring Sites

Figure D.4 – Map of Non-Automatic Monitoring Sites

A Map of Non-Automatic Monitoring Sites

Figure D.5 – Map of Monitoring Locations in Birchington

Map of Monitoring Locations in Birchington

Figure D.6 – Map of Monitoring Locations in Minster

Map of Monitoring Locations in Minster

Figure D.7 – Map of Monitoring Locations in Cliffsend, Ramsgate

Map of Monitoring Locations in Cliffsend, Ramsgate

Figure D.8 – Map of Monitoring Locations in Westwood

Map of Monitoring Locations in Westwood

Figure D.9 – Map of Monitoring Locations in Margate and Westgate-on-Sea

Map of Monitoring Locations in Margate and Westgate-on-Sea

Figure D.10 – Map of Monitoring Locations at the now revoked Ramsgate AQMA

Map of Monitoring Locations at the now revoked Ramsgate AQMA

Appendix E: Summary of Air Quality Objectives in England

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

Glossary of Terms

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

References

Bureau Veritas Group | C2.1 - Internal


[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).