2024 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, 2024
City of York Council Details |
|
Local Authority Officer |
Andrew Gillah |
Department |
Public Protection |
Address |
City of York Council, Public Protection Hazel Court Eco Depot, James Street, York, YO10 3DS |
Telephone |
(01904) 551525 |
|
|
Report Reference Number |
ASR2023 |
Date |
June 2023 |
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. Additionally, people living in less affluent areas are most exposed to dangerous levels of air pollution[2].
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. |
Through monitoring of air quality across the city, City of York Council (CYC) has previously identified some areas of the city centre, around the inner ring road, where long term annual average nitrogen dioxide (NO2) levels are above health based objective levels. These areas have been incorporated into an Air Quality Management Area (AQMA). Historically, AQMAs have also existed in Fulford (AQMA Order No.2) and on Salisbury Terrace (AQMA Order No.3). These AQMAs were revoked in 2020 and 2017 respectively due to improvements in air quality in these areas of the city. Current and historical AQMAs declared by CYC can be viewed at List of York AQMAs and are discussed in CYC’s previous Annual Status Reports.
CYC has a statutory duty to try to reduce NO2 concentrations within the remaining city centre AQMA and additional obligations in relation to the protection of public health and reduction of greenhouse gas emissions. The main air pollutants of concern in York are NO2 and particulate matter (PM). Typically, transport sources are responsible for around 50-70% of the total NO2 at any particular location in the city, although the exact amount varies according to proximity to roads and other emission sources. Road transport is also a source of PM emissions, although its contribution is less than half that of domestic burning of solid fuels in closed stoves and open fires.
The latest air pollution monitoring data for 2023, summarised in this report, indicates that NO2 concentrations in the AQMA have improved since 2022. The highest concentration of NO2 recorded at a location representative of long-term public exposure in 2023 was 43µg/m3 near the junction of Gillygate and Bootham (diffusion tube reference A1). This contrasts with 2022, where NO2 concentrations of 47µg/m3 were monitored on Gillygate.
Improvements in annual mean NO2 monitored at roadside continuous monitoring stations were observed between 2022 and 2023 at Fishergate (10% improvement), Nunnery Lane (7% improvement), Gillygate (7% improvement), Lawrence Street (8% improvement) and Heworth Green (13% improvement). Annual mean NO2 monitored at Holgate Road and Fulford Road in 2023 was broadly comparable to that monitored in 2022 (~1% change).
Annual mean background concentrations of NO2 monitored at Bootham Park Hospital (City of York Council’s urban background continuous monitoring site) also improved by 6% between 2022 and 2023.
Concentrations of NO2 monitored at the majority of locations in York throughout 2023 continue the general downward trend in NO2 concentrations monitored in the city since 2012. Ongoing air quality monitoring in all locations will be fundamental to understanding the longer-term environmental impacts of the pandemic and the magnitude of any changes due to increased levels of walking and cycling, changes in public transport use and ongoing air quality improvement initiatives.
With respect to the city centre AQMA, 5 CYC monitoring locations measured annual mean NO2 concentrations of 40µg/m3 or above in 2023. Exceedances of the health based annual mean NO2 objective of 40µg/m3 were monitored at one location on Gillygate (Diffusion Tube 7), at the junction of Gillygate and Bootham (Diffusion Tube A1) and on Rougier Street (Diffusion Tube 115[3]). Two further locations on Gillygate (Diffusion Tubes 13 and 14) measured annual mean NO2 concentrations equal to the objective of 40µg/m3.
In line with DEFRA’s LAQM guidance, before revoking an AQMA on the basis of measured pollutant concentrations, a local authority needs to be reasonably certain that any future exceedences of air quality objectives are unlikely. For this reason, it is expected that local authorities will need to consider measurements carried out over several years or more, national trends in emissions, as well as local factors that may affect the AQMA. Additionally, where NO2 monitoring is undertaken using diffusion tubes, to allow for the uncertainty associated with the monitoring method, it is recommended that revocation of an AQMA should only be considered following three consecutive years of annual mean NO2 concentrations being lower than 36µg/m3 (i.e. within 10% of the annual mean NO2 objective). CYC will keep the AQMA boundary under review, taking into account these guidelines.
Concentrations of NO2 monitored in the former Fulford Road AQMA in 2023 continue to be well below the annual mean objective of 40µg/m3. The highest recorded levels of NO2 in this area were monitored on Fulford Main Street (Diffusion Tube C58) and were 25µg/m3. This supports the decision to revoke the Fulford Road AQMA, as discussed in CYC’s previous Annual Status Reports and implemented in February 2020.
Concentrations of NO2 monitored in the former Salisbury Terrace / Leeman Road AQMA in 2023 were also all well below the annual mean objective of 40µg/m3. The highest recorded levels of NO2 in this area were monitored on Salisbury Terrace (Diffusion Tube 104) and were 27µg/m3. This confirms that the decision to revoke this AQMA in December 2017 was appropriate.
In December 2018, the boundary of the city centre AQMA was extended to include the full length of Coppergate and the buildings either side of the road, due to monitored concentrations of NO2 above the annual mean objective for this pollutant. The highest annual mean concentrations of NO2 monitored along Coppergate in 2023 was 35µg/m3 at site D56 (Three Tuns Pub, 12 Coppergate) which is below the annual mean objective for this pollutant. Whilst annual mean concentrations of NO2 were below the objective in this location in 2022 and 2023 (35-36 µg/m3), they are well above concentrations monitored in 2020 and 2021 (31-32 µg/m3). It is therefore considered appropriate to keep this area of the city under observation to establish longer term trends, prior to making any amendments to the AQMA boundary.
Revisions to the AQMA Order in 2018 also removed the reference to breaches of the short-term hourly objective along George Hudson Street / Rougier Street / Bridge Street based on monitoring results in this area. The latest 2023 monitoring results for this area of the city indicate that this short-term objective is still being met (all annual mean concentrations were less than 60µg/m3 which suggests that an exceedance of the 1-hour mean objective is unlikely).
CYC monitored particulate (PM10) at four sites in the city (Bootham, Fishergate, Holgate Road and Plantation Drive) and fine particulate (PM2.5) at three sites (Bootham, Fishergate and Gillygate) in 2023. National health-based air quality objectives for PM10 and PM2.5 are currently met in York. The highest annual mean levels of PM10 and PM2.5 monitored in York during 2023 were 16.8µg/m3 (at Holgate Road) and 8.0µg/m3 (at Fishergate) respectively. Along with many areas of the UK, these concentrations are above World Health Organisation (WHO) guidelines for these pollutants, which have recently been strengthened to 15µg/m3 (PM10) and 5µg/m3 (PM2.5). Maximum particulate concentrations monitored in 2023 are below the maximum levels of 17.9µg/m3 (PM10) and 8.8µg/m3 (PM2.5) monitored in 2022 at the same sites.
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[4] 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[5] 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[6] 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.
CYC previously produced two Air Quality Action Plans (AQAPs) in 2004 and 2006. These previous plans were primarily modal shift and congestion reduction based plans, with emphasis on reducing vehicle trips across the city.
Despite the introduction of two AQAPs, air quality in York continued to deteriorate between 2004 and 2010. In response, York adopted an overarching Low Emission Strategy (LES) in 2012 to tackle the issue. This document was the first of its kind in the UK and set out a new approach to local air quality management based on reducing emissions from all sources, including tailpipe emissions from individual vehicles and encouraging the uptake of alternative fuels and low emission vehicle technologies. The Low Emission Strategy has proved particularly effective at tackling emissions from essential service vehicles such as buses and taxis, which fall outside the scope of trip reduction based modal shift measures.
Modal shift and congestion reduction measures remain fundamental to the delivery of air quality improvement and emission reduction in York. The primary local delivery programmes for these measures are the Local Transport Plan and the iTravel York programme. Existing programmes and those such as Government Active Travel Funding encourage the uptake of walking, cycling, and public transport in the city. They are supported by planning policies that ensure that sustainable travel solutions are embedded into all new developments in York.
In February 2023, CYC published a draft Local Transport Strategy, that set out high level principles and priorities for York that will underpin future transport strategies for the city. The document examines the evidence, sets out implications and suggests the sort of interventions which could be used to overcome the challenges with York’s existing transport system. Tackling transport emissions is recognised as key policy strand within the draft strategy. CYC undertook extensive consultation on the draft strategy between November 2023 and February 2024. Initial results have shown overwhelming support for the ten policy focus areas put forward, one of which relates to ‘safeguarding our environment by cutting carbon, air pollution and noise’.
Over the same period, CYC consulted with the public and other groups to gather feedback specifically on air quality in York and on measures to improve air quality proposed in our updated Air Quality Action Plan (AQAP4). Annual Status Reports from 2025 onwards will report on progress with delivery of measures in this updated plan.
CYC continued the delivery of measures in its third Air Quality Action Plan (AQAP3) throughout 2023, progressing the following initiatives and projects:
· Bus service improvements - In August 2023, First Bus together with City of York Council ‘switched on’ a new fleet of zero emission buses for York in a transformation that will see the York bus depot become one of the first outside London to be fully electric. The buses herald new ‘York electric’ branding. Additional electric buses have since been introduced across other routes in the city.Each bus will significantly reduce NOx and particulate emissions and save up to 60 tonnes of carbon emissions a year, meaning an anticipated annual reduction of more than 3,000 tonnes of CO2 when the full fleet is in operation. As part of the overall investment, the First Bus depot has been transformed with the installation of power charging and infrastructure to handle the full zero emission fleet, totalling 86 buses. The new buses, supported by funding through DfT’s Zero Emission Bus Regional Areas (ZEBRA) scheme, complement the existing electric buses serving York’s Park and Ride sites. CYC has also been awarded additional funding to support the development of key schemes and initiatives in line with York’s Bus Service Improvement Plan (BSIP), including wider electrification of the urban bus fleet, bus priority measures, improvements to stops, shelters and passenger information. The York Enhanced Partnership for Buses will act as the principal delivery body for the BSIP funding until 2025. CYC has previously launched a Clean Air Zone (CAZ) for buses in the city centre and supported operators with bus upgrades as reported in previous Annual Status Reports.
· Anti Idling Initiatives – we continued to promote our ‘Kick the Habit’ anti-idling campaign on Clean Air Day and throughout 2023 and worked with partners including schools and businesses to reduce the incidence of vehicle idling across the city. The campaign sets out to encourage people to think about the importance of clean air and the impact that this has on them, their health and those around them. Work in 2023 reinforces action in previous years, including the erection of permanent anti-idling signage in all CYC owned car parks, at most city centre bus stops, multiple taxi ranks and at other key locations across the city. Further information about the campaign can be found on CYC’s Kick the Habit Webpage.
· Low Emission Taxi Grant – throughout 2023, we continued to rollout our DEFRA funded Low Emission Taxi Grant Scheme and welcomed further all-electric and hybrid-electric taxis to the York fleet. The scheme offers financial support for eligible CYC registered taxi drivers to upgrade to low emission vehicles and will have the direct effect of reducing emissions of NOx/NO2 and particulate matter across York. At the end of December 2023, 37% of the York fleet were using low emission petrol hybrid or zero emission electric vehicles. We have further plans to update our Taxi Licensing Policy in 2024 to further reduce taxi emissions, in consultation with the trade and other relevant parties.
· Upgrades to Electric Vehicle (EV) charging facilities – we continued to upgrade our public electric vehicle charging network, consisting of ‘fast’, ‘rapid’ and ‘ultra-rapid’ charge points, as outlined in our Public Electric Vehicle Charging Strategy. Two new ‘HyperHub’ sites (containing both 50kW rapid and 175kW ultra-rapid charge facilities) at Monks Cross and Poppleton were opened in 2022 and 2023; the use of these sites comprised over 80% of our network usage. We have plans to develop two further Hyper Hub sites. Our current charge point rollout programme is outlined on the council website. In addition to the expansion of our public electric vehicle charge point network, we finalised infrastructure upgrades at the council’s Hazel Court ECO depot site to facilitate the transition to an all-electric council fleet for vehicles under 3.5t. In February 2024, 41% of CYC’s operational fleet (<3.5t) were electric vehicles. In preparation for the new fleet of electric vehicles, we continued our programme of mandatory Alternative Fuel Vehicle (AFV) training for all staff.
· CYC Low Emission Planning Guidance - Throughout 2023, we continued to ensure that emissions and air quality impacts from new developments were appropriately assessed and mitigated, exposure to poor air quality was reduced via good design practices and that new private trips were minimised via the provision of sustainable transport opportunities. An overview of planning applications reviewed by Public Protection during 2023 is provided in this Annual Status Report.
· Measures around domestic solid fuel burning – we promoted the government’s national ‘Burn Better’ campaign to reduce emissions and continued compliance checks across solid fuel distribution outlets to ensure correct certification of solid fuels for domestic use. In early 2023, we were awarded further DEFRA Air Quality Grant funding to improve public awareness of domestic solid fuel burning practices, particulate emissions and associated health impacts. We undertook research via an online survey and hosted a number of focus groups with the local community to inform the creative route for the campaign, which was launched in November 2023. Details of the campaign, named ‘Fuel for Thought’, can be found at https://www.york.gov.uk/FuelForThought.
· Development of an online pollution forecasting service – In 2023 we were awarded DEFRA funding to develop an online air pollution forecasting and notification service to allow residents and visitors to York to access information that allows them to minimise their own exposure when pollution episodes are forecast. The York Air Alert service is of particular benefit to anyone who suffers from health conditions exacerbated by poor air quality. The service provides a 3-day forecast of air pollution in 8 areas of York. The service is free to subscribe to and provides notifications via email, text, voicemail and Twitter/X to users.
· Consultation on fourth Air Quality Action Plan (AQAP4) – we progressed a public consultation on our Fourth Air Quality Action Plan (AQAP4) between 22nd November 2023 and 4th February 2024. AQAP4 was developed in parallel to CYC’s draft Local Transport Strategy, which was also consulted on during the same period. AQAP4 aims to reduce levels of air pollution in the city, thereby improving the health and quality of life of residents and visitors to York. AQAP4 outlines the action the council will take to further improve air quality in York over the next 5 years. Over three quarters (79%) of respondents agreed that the council should continue to reduce air pollution, with between 67% and 87% of respondents indicated support for all AQAP4 priority areas. See https://www.york.gov.uk/AirQualityActionPlan.
· Air Quality Hub (AQ Hub) for local authorities - throughout 2023, we continued work on the development of the Air Quality (AQ) Hub alongside Bradford Metropolitan District Council and Lancaster City Council (working together as the Low Emission Partnership (LEP), with management support provided by Bureau Veritas). The AQ Hub was promoted at the national Air Quality Symposium, organised by DEFRA, in September 2023. Following a successful launch, the AQ Hub membership base has grown significantly over the last 3 years, covering local authorities across the UK. The Air Quality Hub was formally adopted by DEFRA in February 2024 to support the Local Air Quality Management regime and will now be managed by DEFRA as a national resource, with ongoing support from the Low Emission Partnership.
· Farming practices - Nationally, farming is estimated to be responsible for around 88% of ammonia emissions, which can lead to particulate formation in the atmosphere; this can cause odour impacts and can affect local and national air quality. Some farming practices (e.g. lime spreading) can also directly give rise to particulate emissions that are known to affect health. In October 2023, CYC contacted over 350 farmers to highlight resources and grant opportunities available to assist in adopting best practice with respect to reducing ammonia and particulate emissions.
Complementary air quality initiatives delivered in 2023 through CYC’s Transport and carbon reduction work programmes included:
· Local Cycling and Walking Infrastructure Plan (LCWIP) – we have progressed development of a Local Cycling and Walking Infrastructure Plan (LCWIP). The LCWIP identifies York’s key walking and cycling networks and will be used as an evidence base for future investment opportunities. The LCWIP will be a living document and will be updated as and when necessary (i.e. when schemes have been funded or delivered) to ensure a pipeline of potential schemes is always available
· York Walking Festival – our annual walking festival took place in September 2023, with a nine-day programme of ideas on how to explore the city on foot. The festival, organised by CYC’s iTravel team, aims to encourage active travel and reduce vehicle emissions produced during the school run. Activities included guided group walks, a York walking quiz and promotion of resources for exploring the city.
· Zero Emission Day - In September 2023, to coincide with Zero Emission Day, we raised awareness of the need to reduce the city’s carbon footprint by flying a flag bearing the Yorkshire climate change stripes. The climate stripes were developed to show people how the climate is changing where they live. Shades of blue indicate cooler-than-average years, while red shows years that were hotter-than-average. The Yorkshire climate stripes highlight the increase in temperature in Yorkshire over the past 150 years, shown in the stripes from left to right. In March 2019, CYC declared a climate emergency and pledged to be net zero by 2030.
· A New Energy Advice Scheme – we launched a Local Energy Advice Demonstrator (LEAD) scheme. LEAD provides York homeowners of conservation-area and listed properties detailed advice on the best ways to insulate and heat their homes; information on how to complete planning permission applications and gain listed property consent; and the best ways to save money while contributing to our Net Zero 2030 target.
· Home Upgrade Grants – we have been awarded funding to help households not using mains gas become more energy efficient through a Home Upgrade Grant. The grants can be used for a range of improvements, including wall and roof insulation, air source heat pumps, smart heating controls and solar panels.
· Business Forum Events – We launched the first York Green Business Forum event in October 2023 to support local businesses to become more sustainable, increase profitability and help York become net zero by 2030. Attendees were able to access free support, participate in workshops and network with likeminded local businesses.
· Residents invited behind the scenes on Council’s first Passivhaus site – In October 2023, we offered a first opportunity for residents to go behind the scenes to learn more about how energy-efficient and zero-carbon Passivhaus homes are being built in the city. The Passivhaus Open Day took place at CYC’s first Passivhaus development at Duncombe Square in Clifton. The Open Day was part of a national event to showcase this form of building homes. Passivhaus is a construction standard with a goal of creating energy-efficient buildings with a low carbon footprint. In order to achieve that, Passivhaus homes use a variety of features that are designed to reduce their need for heating and cooling rooms.
York already has much to celebrate in relation to reducing emissions and protecting and improving the health of its residents. However, with an increasing population and further development, preventing emission growth and improving air quality remain significant challenges for the foreseeable future.
CYC’s updated Air Quality Action Plan (AQAP4) outlines the action we will take to further improve air quality in York over the next 5 years between 2024 and 2028 to go beyond health-based National Air Quality Objectives in all areas and to work towards meeting stricter World Health Organisation (WHO) Guidelines in the longer term. AQAP4 is fully aligned to the Council Plan and reflects ambitions contained within our 10-Year Strategies covering climate, health and wellbeing and the economy.
Key findings and conclusions from this year’s Annual Status Report:
· The annual average air quality objective for NO2 (40µg/m3) was exceeded at a small number of monitoring sites within the current Air Quality Management Area on Gillygate, Bootham and Rougier Street in 2023 (Diffusion Tubes 7, 115 and A1). The highest concentration of NO2 recorded at a ‘relevant location’ was 43µg/m3 near the junction of Gillygate and Bootham (Diffusion Tube A1).
· Improvements in annual mean NO2 monitored at roadside continuous monitoring stations were observed between 2022 and 2023 at Fishergate (10% improvement), Nunnery Lane (7% improvement), Gillygate (7% improvement), Lawrence Street (8% improvement) and Heworth Green (13% improvement). Annual mean NO2 monitored at Holgate Road and Fulford Road in 2023 was broadly comparable to that monitored in 2022 (~1% change). Annual mean background concentrations of NO2 monitored at the Bootham urban background monitoring site also improved by 6% between 2022 and 2023.
· Maximum annual mean concentrations of NO2 monitored at relevant locations across the current AQMA were 43µg/m3 (Gillygate / Bootham), 37µg/m3 (George Hudson St / Rougier St), 37µg/m3 (Holgate / Blossom Street), 31µg/m3 (Lawrence St), 29µg/m3 (Fishergate / Paragon St), 26µg/m3 (Prices Lane/Nunnery Lane) and 35µg/m3 (Coppergate). Maximum concentrations of NO2 decreased in all these areas between 2022 and 2023 and ranged from 2% lower on Coppergate (in 2023) to 16% lower around Prices Lane / Nunnery Lane and Rougier Street (in 2023).
· Concentrations of NO2 monitored at the majority of locations in York throughout 2023 continue the general downward trend in NO2 concentrations monitored in the city since 2012. Concentrations of NO2 were generally lower in the years 2021 - 2023 than pre-pandemic levels in 2019.
· Maximum concentrations of NO2 monitored in the former Fulford Road and Salisbury Terrace / Leeman Road AQMAs (now revoked) in 2023 continue to be well below the annual mean objective.
· The highest annual mean concentrations of NO2 monitored along Coppergate in 2023 was 35µg/m3 at site D56 (Three Tuns Pub, 12 Coppergate) which is below the annual mean objective for this pollutant. As concentrations of NO2 have been variable at this site over the last few years and not consistently under 36µg/m3 (within 10% of the objective) it is considered appropriate to keep this area of the city under observation prior to making any amendments to the AQMA boundary.
· Monitoring of NO2 in 2023 has not indicated any potential breaches of the short-term hourly NO2 objective in the city.
· National health-based air quality objectives for PM10 and PM2.5 are currently met in York. The highest annual mean levels of PM10 and PM2.5 monitored in York during 2023 were 16.8µg/m3 and 8.0µg/m3 respectively. Trends over the last 5 years indicate that PM2.5 has generally decreased across the city, whereas there does not appear to be any clear trend in PM10 over the same period.
City of York Council’s priorities for the coming year are:
· Progress delivery of AQAP4 - CYC’s updated AQAP4 includes measures to further reduce nitrogen dioxide and particulates from all sources and will support and complement CYC’s economic strategy, Local Plan, Local Transport Plan/Strategy and Climate Change Strategy.
· Continue to progress upgrades to bus services (including further electrification of the urban fleet) - the York Enhanced Partnership (EP) for buses between CYC and York’s local bus operators acts as the principal delivery body for the £17.36 million Bus Service Improvement Plan (BSIP) funding awarded to the council by the Department of Transport (DfT) for use during the financial years 2022 to 2025. The EP also provides a platform for bus users and stakeholders to share their views on the local bus network.
· Continue to address idling emissions – CYC will continue to provide anti-idling patrols, investigate complaints of idling and raise awareness of the links between idling emissions and health in line with CYC’s existing ‘Kick the Habit’ anti-idling campaign. We propose to install additional permanent anti-idling signage in key locations requesting drivers switch off engines whilst stationary.
· Continue to reduce emissions from taxis - We will undertake further consultation with the trade in relation to updates to our Taxi Licensing Policy. Anticipated changes to the policy will see a gradual change in the operational taxi fleet, as vehicle licenses are renewed and as vehicles become too old to operate in the city. We will undertake a full evaluation of our DEFRA funded Low Emission Taxi Grant Scheme that has supported CYC licensed taxi drivers with vehicle upgrades throughout 2023. This grant funding has now all been allocated.
· Reduce emissions from new development – we will continue to work with developers to ensure development related emissions are appropriately assessed and mitigated, exposure to poor air quality is reduced via good design practices and that new private trips are minimised via provision of opportunities for sustainable transport. We will continue to encourage walking, cycling and low emission public transport use, which have co-benefits for health and wellbeing.
· Progress development of York’s future transport policies - Initial results from Our Big Transport Conversation, the recent consultation about transport in York, have shown overwhelming support for the ten policies put forward by Councillors. CYC will now formulate detailed plans for delivering the long-term changes residents have asked for, including a new Movement and Place Plan. A new Local Transport Plan will enable us to reduce congestion, improve air quality and help people get about the city better, as well as meeting our net zero targets.
· Expansion of strategic EV charging network - CYC will deliver additional charge points and actively monitor plug-in vehicle uptake in the city to ensure our charging network remains fit for purpose.
· Raising awareness of PM emissions and health impacts - we will fully evaluate our DEFRA funded project (2022/23 AQ Grant) to improve public awareness of the links between domestic solid fuel burning, particulate emission and health impacts.
· Improving public awareness of air pollution – we will promote our DEFRA funded air pollution forecasting and alert platform. The platform has been designed to ensure the most vulnerable residents have access to information that allows them to minimise exposure when pollution levels are high. We will seek to improve awareness of the links between all air pollution and health impacts generally to support CYC’s ongoing LAQM and public health work.
· Further controls to address fine particulate emissions – we will consider further opportunities to tackle fine particulate emissions, building on previous feasibility work. We will seek member approval for a new Enforcement Protocol for civil penalties for smoke emissions within CYC’s Smoke Control Area (SCA) and seek to expand our SCA to cover the whole of CYC’s administrative area.
· Reducing emissions associated with deliveries of light goods – we will explore further opportunities for minimising emissions from freight vehicles in the city centre in line with priorities outlined in AQAP4.
Challenges faced by City of York Council:
· The ability of current vehicle emission standards to deliver reductions in NOx emissions, particularly the on-road performance of some Euro VI diesel vehicles.
· Development related emissions through the cumulative impact of increased development in the city. CYC will endeavour to manage this through the application of local planning guidance, best practice emission mitigation measures and opportunities for sustainable transport. CYC’s Transport Strategy sets a target of 20% reduction in vehicle miles travelled by 2030, which will need to be supported by significant increases in walking, cycling and use of public transport across York.
· Addressing air pollution from domestic solid fuel burning, especially during winter months, may present challenges as people turn to solid fuels to heat their homes in response to the energy and cost of living crisis. This may be further exacerbated in certain areas where fuel poverty may be a factor in the burning of non-certified wood products / waste wood or other materials. CYC has aimed to tackle this issue in 2023 and early 2024 through it’s ‘Fuel for Thought’ campaign.
· Uncertainties with respect to future travel behaviour and challenges in achieving required modal shift targets to sustainable modes.
· Continued unnecessary vehicle idling in the city, particularly amongst heavy diesel vehicles.
Despite longer term improvements seen in air quality across CYC’s area in recent years, the above factors are anticipated to remain challenges for CYC in the future.
Further information about air quality and previous consultations can be obtained from the air quality pages of CYC’s main website.
Residents, businesses and other interested parties are encouraged to participate in future consultations relating to air quality. These are advertised online at: City of York Council Consultations.
This ASR was prepared by Public Protection at City of York Council. Updates on Air Quality Action Plan measures have been obtained from various teams across the council including Transport Planning, Highways, Parking Services, Carbon Reduction and Fleet Services.
This ASR has been approved by Cllr Jenny Kent and Cllr Kate Ravilious (Executive Members for Environment and Climate Change) and signed off by Peter Roderick, Director of Public Health and James Gilchrist, Director of Transport, Environment and Planning. <<SUBJECT TO APPROVAL>>
If you have any comments on this ASR please send them to Public Protection at:
Email: public.protection@york.gov.uk
Phone: 01904 551525
Write to: City of York Council, Public Protection (Air Quality), Hazel Court Eco Depot, James Street, York, YO10 3DS
Table of Contents
Executive Summary: Air Quality in Our Area
Actions to Improve Air Quality
Local Engagement and How to get Involved
Local Responsibilities and Commitment
1 Local Air Quality Management
2 Actions to Improve Air Quality
2.1 Air Quality Management Areas
2.2 Progress and Impact of Measures to address Air Quality in York
2.3 PM2.5 – Local Authority Approach to Reducing Emissions and/or Concentrations
3 Air Quality Monitoring Data and Comparison with Air Quality Objectives and National Compliance
3.1 Summary of Monitoring Undertaken
3.1.1 Automatic Monitoring Sites
3.1.2 Non-Automatic Monitoring Sites
3.2.2 Particulate Matter (PM10)
3.2.3 Particulate Matter (PM2.5)
3.3.1 Council Plan Air Quality Indicators
3.3.2 Local Transport Plan Air Quality Indicator
Appendix A: Monitoring Results
Appendix B: Full Monthly Diffusion Tube Results for 2023
Appendix C: Supporting Technical Information / Air Quality Monitoring Data QA/QC
New or Changed Sources Identified Within York During 2023
Additional Air Quality Works Undertaken by City of York Council During 2023
QA/QC of Diffusion Tube Monitoring
Diffusion Tube Bias Adjustment Factors
NO2 Fall-off with Distance from the Road
PM10 and PM2.5 Monitoring Adjustment
Automatic Monitoring Annualisation
NO2 Fall-off with Distance from the Road
Appendix D: Map(s) of Monitoring Locations and AQMAs
Figures
Figure A.1 – Trends in Annual Mean NO2 Concentrations
Figure A.2 – Trends in Number of NO2 1-Hour Means > 200µg/m3
Figure A.3 – Trends in Annual Mean PM10 Concentrations
Figure A.4 – Trends in Number of 24-Hour Mean PM10 Results > 50µg/m3
Figure A.5 – Trends in Annual Mean PM2.5 Concentrations
Figure D.1 – Map of Non-Automatic Monitoring Site
Figure D.2 - Map of Automatic Monitoring Sites in relation to AQMA
Tables
Table 2.1 – Declared Air Quality Management Areas
Table 2.2 – Progress on Measures to Improve Air Quality
Table A.1 – Details of Automatic Monitoring Sites
Table A.2 – Details of Non-Automatic Monitoring Sites
Table A.3 – Annual Mean NO2 Monitoring Results: Automatic Monitoring (µg/m3)
Table A.4 – Annual Mean NO2 Monitoring Results: Non-Automatic Monitoring (µg/m3)
Table A.5 – 1-Hour Mean NO2 Monitoring Results, Number of 1-Hour Means > 200µg/m3
Table A.6 – Annual Mean PM10 Monitoring Results (µg/m3)
Table A.7 – 24-Hour Mean PM10Monitoring Results, Number of PM10 24-Hour Means > 50µg/m3
Table A.8 – Annual Mean PM2.5 Monitoring Results (µg/m3)
Table B.1 – NO2 2023 Diffusion Tube Results (µg/m3)
Table C.1 – Annualisation Summary (concentrations presented in µg/m3)
Table C.2 – Bias Adjustment Factor
This report provides an overview of air quality in York during 2023. 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 City of York Council (CYC) 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.
2.1 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 CYC can be found in Table 2.1. The table presents a description of the AQMA that is currently designated within York. Appendix D: Map(s) of Monitoring Locations and 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 are as follows:
· NO2 annual mean
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 |
City Centre AQMA (AQMA Order No.5) |
December 2018 (supercedes AQMA Order No. 4 declared Sept 2012) |
NO2 Annual Mean |
Inner ring road and properties included within multiple areas of technical breach |
NO |
62 |
43 |
1 (compliance demonstrated in 2020) |
AQAP3 published September 2015
(Updated AQAP4 due June 2024) |
☒ City of York Council
confirm the information on UK-Air regarding their AQMA(s) is up
to date.
☒ City of York Council confirm that all current AQAPs have been submitted to DEFRA
2.2 Progress and Impact of Measures to address Air Quality in York
DEFRA’s appraisal of last year’s ASR supported the outlined measures to improve air quality across the city and accepted the conclusions reached for all sources and pollutants.
The only comments made by DEFRA with respect to how CYC could improve the Annual Status Report for 2024 was to increase the resolution of maps showing monitoring locations (to ensure labels are clearer when zooming in) and to ensure that no blank cells are presented in Table 2.2 which provides an update on AQAP measures. These issues have been addressed in this year’s report.
CYC has taken forward a number of direct measures during the current reporting year of 2023 in pursuit of improving local air quality. Details of all measures completed, in progress or planned are set out in Table 2.2. Twenty six measures are included within Table 2.2, with the type of measure and the progress CYC have made during the reporting year of 2023 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.
Key completed measures are:
· Bus service improvements - In August 2023, First Bus together with CYC ‘switched on’ a new fleet of zero emission buses for York in a transformation that will see the York bus depot become one of the first outside London to be fully electric. Each bus will significantly reduce NOx and particulate emissions and save up to 60 tonnes of carbon emissions a year, meaning an anticipated annual reduction of more than 3,000 tonnes of CO2 when the full fleet is in operation. The new buses, supported by funding through DfT’s Zero Emission Bus Regional Areas (ZEBRA) scheme, complement the existing electric buses serving York’s Park and Ride sites.
· Anti-idling initiatives - we continued to promote our ‘Kick the Habit’ anti-idling campaign on Clean Air Day and throughout 2023 and worked with partners including schools and businesses to reduce the incidence of vehicle idling across the city. Further information about the campaign can be found on CYC’s Kick the Habit Webpage.
· Low Emission Taxi Grant – we continued to rollout our DEFRA funded Low Emission Taxi Grant Scheme so that by the end of December 2023, 37% of the York fleet were using low emission petrol hybrid or zero tailpipe emission electric vehicles.
· Upgrades to Electric Vehicle (EV) charging facilities – we continued to upgrade our public electric vehicle charging network throughout 2023, consisting of ‘fast’, ‘rapid’ and ‘ultra-rapid’ charge points, as outlined in our Public Electric Vehicle Charging Strategy. We also finalised infrastructure upgrades at the council’s Hazel Court ECO depot site to facilitate the transition to an all-electric council fleet for vehicles under 3.5t. In February 2024, 41% of CYC’s operational fleet (<3.5t) were electric vehicles.
· Low Emission Planning Guidance - Throughout 2023, we continued to ensure that emissions and air quality impacts from new developments were appropriately assessed and mitigated, exposure to poor air quality was reduced via good design practices and that new private trips were minimised via the provision of sustainable transport opportunities in line with our Low Emission Planning Guidance.
· Measures around domestic solid fuel burning – we promoted the government’s national ‘Burn Better’ campaign to reduce emissions and continued compliance checks across solid fuel distribution outlets to ensure correct certification of solid fuels for domestic use. We progressed a DEFRA Air Quality Grant funded campaign to improve public awareness of domestic solid fuel burning practices, particulate emissions and associated health impacts. CYC’s ‘Fuel for Thought’ campaign was launched in November 2023.
· Air pollution forecasting and alert service – In 2023, we progressed a DEFRA Air Quality Grant funded air pollution forecasting and alert service to allow residents and visitors to York to access information that allows them to minimise their own exposure when pollution episodes are forecast. The York Air Alert service is of particular benefit to anyone who suffers from health conditions exacerbated by poor air quality. The service provides a 3-day forecast of air pollution with 8 zones of York. The service is free to subscribe to and provides notifications via email, text, voicemail and Twitter/X to users.
· Consultation on fourth Air Quality Action Plan (AQAP4) – we held a public consultation on our Fourth Air Quality Action Plan (AQAP4) between 22 November 2023 and 4 February 2024. AQAP4 was developed in parallel to CYC’s draft Local Transport Strategy, which was consulted on during the same period. AQAP4 aims to reduce levels of air pollution in the city, thereby improving the health and quality of life of residents and visitors to York. AQAP4 outlines the action the council will take to further improve air quality in York over the next 5 years. Over three quarters (79%) of respondents agreed that the council should continue to reduce air pollution, with between 67% and 87% of respondents indicated support for all AQAP4 priority areas.
· Air Quality Hub (AQ Hub) - throughout 2023, we continued work on the development of the Air Quality Hub alongside Bradford Metropolitan District Council and Lancaster City Council (working together as the Low Emission Partnership (LEP), with management support provided by Bureau Veritas). The Air Quality Hub was formally adopted by DEFRA in February 2024 to support the Local Air Quality Management regime and will now be managed by DEFRA as a national resource, with ongoing support from the Low Emission Partnership.
· Emissions from farming practices - In October 2023, CYC contacted over 350 farmers within York to highlight resources and grant opportunities available to assist them to adopt best practice with respect to reducing ammonia and particulate emissions.
Complementary air quality initiatives delivered in 2023 through CYC’s Transport and carbon reduction work programmes included:
· Local Cycling and Walking Infrastructure Plan (LCWIP) – we progressed development of a Local Cycling and Walking Infrastructure Plan (LCWIP).
· York Walking Festival – our annual walking festival took place in September 2023, with a nine-day programme of ideas on how to explore the city on foot. The festival, organised by CYC’s iTravel team, aims to encourage active travel and reduce vehicle emissions produced during the school run.
· Zero Emission Day - In September 2023, to coincide with Zero Emission Day, we raised awareness of the need to reduce the city’s carbon footprint by flying a flag bearing the Yorkshire climate change stripes. The climate stripes were developed to show people how the climate is changing where they live.
· A New Energy Advice Scheme – we launched a Local Energy Advice Demonstrator (LEAD) scheme. LEAD provides York homeowners of conservation-area and listed properties detailed advice on the best ways to insulate and heat their homes; information on how to complete planning permission applications and gain listed property consent; and the best ways to save money while contributing to our Net Zero 2030 target.
· Home Upgrade Grants – we were awarded funding to help households not using mains gas become more energy efficient through a Home Upgrade Grant. The grants can be used for a range of improvements, including wall and roof insulation, air source heat pumps, smart heating controls and solar panels.
· Business Forum Events – We launched the first York Green Business Forum event in October 2023 to support local businesses to become more sustainable, increase profitability and help York become net zero by 2030. Attendees were able to access free support, participate in workshops and network with likeminded local businesses.
· Residents invited behind the scenes on Council’s first Passivhaus site – In October 2023, we offered a first opportunity for residents to go behind the scenes to learn more about how energy-efficient and zero-carbon Passivhaus homes are being built in the city. The Passivhaus Open Day took place at CYC’s first Passivhaus development at Duncombe Square in Clifton.
City of York Council expects the following measures to be completed over the course of the next reporting year:
· City of York Council’s Fourth Air Quality Action Plan (AQAP4) updates and replaces the existing Action Plan (AQAP3) which ran from September 2015 and was the principal delivery mechanism for York’s Low Emission Strategy (LES) produced in October 2012. As part of AQAP4’s preparation, a comprehensive review of previously adopted air quality improvement measures has been undertaken. Where still relevant to York’s air quality issues and principal emission sources, measures and targets have been updated to ensure they strive to achieve continual improvement in air quality across the city over the next 5-year period to improve public health outcomes. Additional measures are included in AQAP4 to reflect:
o the growing evidence base around air quality and health impacts of fine particulate matter, together with new targets introduced through the Environment Act 2021 and obligations for local authorities outlined in DEFRA’s Air Quality Strategy;
o updated emissions source apportionment work for CYC’s area;
o the current air quality position across the city with respect to health-based Air Quality Objectives, and
o additional work undertaken in relation to freight movements since publication of the last AQAP in 2015.
CYC’s future Annual Status Reports will report on progress with measures in the updated AQAP4, due for publication in June 2024. Priorities from 2024 are as follows:
City of York Council’s priorities for the coming year are:
· Progress delivery of AQAP4 - CYC’s updated AQAP4 includes measures to further reduce nitrogen dioxide and particulates from all sources and will support and complement CYC’s economic strategy, Local Plan, Local Transport Plan/Strategy and Climate Change Strategy.
· Progress upgrades to bus services - the York Enhanced Partnership (EP) for buses between CYC and York’s local bus operators acts as the principal delivery body for the £17.36 million Bus Service Improvement Plan (BSIP) funding awarded to the council by the Department of Transport (DfT) for use during the financial years 2022 to 2025. The EP also provides a platform for bus users and stakeholders to share their views on the local bus network.
· Continue to address idling emissions – CYC will continue to investigate complaints of idling and raise awareness of the links between idling emissions and health in line with CYC’s existing ‘Kick the Habit’ anti-idling campaign. We propose to install additional anti-idling signage in key locations requesting drivers switch off engines whilst stationary.
· Continue to reduce emissions from taxis - We will undertake further consultation with the trade in relation to updates to our Taxi Licensing Policy. Anticipated changes to the policy will see a gradual change in the operational taxi fleet, as vehicle licenses are renewed and as vehicles become too old to operate in the city. We will undertake a full evaluation of our DEFRA funded Low Emission Taxi Grant Scheme that has supported CYC licensed taxi drivers with vehicle upgrades throughout 2023.
· Reduce emissions from new development – we will continue to work with developers to ensure development related emissions are appropriately assessed and mitigated, exposure to poor air quality is reduced via good design practices and that new private trips are minimised via provision of opportunities for sustainable transport.
· Progress development of York’s future transport policies - Initial results from Our Big Transport Conversation, the recent consultation about transport in York, have shown overwhelming support for the ten policies put forward by councillors. CYC will now fully analyse the results and come back to residents with detailed plans on how to deliver the long-term changes they’ve asked for, including a new Movement and Place Plan. A new Local Transport Plan will enable us to reduce congestion, improve air quality and help people get about the city better, as well as meeting our net zero targets.
· Expansion of strategic EV charging network - CYC will deliver additional charge points and actively monitor plug-in vehicle uptake in the city to ensure our charging network remains fit for purpose.
· Raising awareness of PM emissions and health impacts - we will full evaluate our DEFRA funded project (2022/23 AQ Grant) to improve public awareness of the links between domestic solid fuel burning, particulate emission and health impacts.
· Improving public awareness of air pollution – we will promote our DEFRA funded air pollution forecasting and alert platform. The platform has been designed to ensure the most vulnerable residents have access to information that allows them to minimise exposure when pollution levels are high. We will seek to improve awareness of the links between all air pollution and health impacts generally to support CYC’s ongoing LAQM and public health work.
· Further controls to address fine particulate emissions – we will consider further opportunities to tackle fine particulate emissions, building on previous feasibility work. We will seek member approval for a new Enforcement Protocol for civil penalties for smoke emissions within CYC’s Smoke Control Area (SCA) and seek to expand our SCA to cover the whole of CYC’s administrative area.
· Reducing emissions associated with deliveries of light goods – We will explore further opportunities for minimising emissions from freight vehicles in the city centre in line with priorities outlined in AQAP4.
City of York Council worked to implement these measures in partnership with the following stakeholders during 2023:
· Residents of York
· Local schools
· York Railway Station
· York and Scarborough Teaching Hospitals NHS Foundation Trust
· York Bus operators
· York Taxi Driver / Associations (and vehicle dealerships for taxi grants)
· Freight operators and local retailers
The principal challenges and barriers to implementation that City of York Council anticipates facing are:
· The ability of current vehicle emission standards to deliver reductions in NOx emissions, particularly the on-road performance of some Euro VI / Euro VI retrofitted diesel vehicles.
· Development related emissions through the cumulative impact of increased development in the city. CYC will endeavour to manage this through the application of local planning guidance, best practice emission mitigation measures and opportunities for sustainable transport. CYC’s Transport Strategy sets a target of 20% reduction in vehicle miles travelled by 2030, which will need to be supported by significant increases in walking, cycling and use of public transport across York.
· Addressing air pollution from domestic solid fuel burning, especially during winter months, may present challenges as people turn to solid fuels to heat their homes in response to the energy and cost of living crisis. This may be further exacerbated in certain areas where fuel poverty may be a factor in the burning of non-certified wood products / waste wood or other materials. CYC has aimed to tackle this issue in 2023 and early 2024 through it’s ‘Fuel for Thought’ campaign.
· Uncertainties with respect to future travel behaviour and challenges in achieving required modal shift targets to sustainable modes
· Continued unnecessary vehicle idling in the city, particularly amongst heavy diesel vehicles.
Despite longer term improvements seen in air quality across CYC’s area in recent years, the above factors are anticipated to remain challenges for CYC in the future.
Progress on the following measures has been slower than expected:
· Pilot micro-consolidation centre – this project was delayed in 2023 due to withdrawal of the primary delivery partner at an advanced stage of the project. We aim to progress this pilot in 2024, subject to a new delivery partner being found. The pilot delivery hub will aim to maximise the efficiency of city centre deliveries, using e-cargo cycles and EVs, thereby minimising the need for large vehicles to enter the city centre.
Whilst the measures stated above and in Table 2.2 will help to contribute towards compliance, CYC anticipates that further additional measures, as outlined in our Fourth Air Quality Action Plan (AQAP4), will be required in subsequent years to achieve compliance and enable the revocation of the city centre AQMA (Order No.5).
Table 2.2 – Progress on Measures to Improve Air Quality
The estimated efficacy of measures in terms of ‘overall emission impact’ is colour coded from red (least impact) - amber - green (most impact). Rows shaded in yellow will be published on UK-AIR.
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 |
AQAP3 (1) |
Clean Air Zone (CAZ) |
Promoting Low Emission Transport |
Low Emission Zone |
2015 |
2021 |
CYC |
CYC and DEFRA Grant |
YES |
Funded |
£1 million - £10 million |
Completed |
Every electric bus introduced into the CAZ will remove local emissions of NO2 and PM10 and reduce CO2 emissions by approximately 35 tonnes |
Number of CAZ compliant low emission buses (electric and Euro 6) operating within York
|
York’s CAZ for buses was fully operational from January 2021 and applied to all high frequency services entering the CAZ area more than 5 times a day. In August 2023, First Bus together with CYC ‘switched on’ a new fleet of zero emission buses for York in a transformation that will see the York bus depot become one of the first outside London to be fully electric. The full zero emission fleet will total 86 buses. The new buses have been supported by funding through DfT’s Zero Emission Bus Regional Areas (ZEBRA) scheme and complement the existing electric buses serving York’s Park and Ride sites. CYC has also been awarded additional funding to support the development of key schemes and initiatives in line with York’s Bus Service Improvement Plan (BSIP), including wider electrification of the urban bus fleet, bus priority measures, improvements to stops, shelters and passenger information. |
Measures to reduce emissions from buses were a critical part of AQAP3. CYC made funding available to support bus upgrades on essential services affected by CAZ implementation. CYC will continue to improve emissions from lower frequency services and strive to maximise the number of services operating fully electric buses to further reduce exhaust emissions. It remains CYC's ambition to pursue an all-electric bus fleet within the city. Further measures to tackle emissions from buses are included in AQAP4 |
AQAP3 (6) |
Development and implementation of Low Emission Planning guidance |
Policy guidance and development control |
Air quality planning and policy guidance |
2015 |
2024 |
CYC |
CYC |
NO |
Funded |
£10k - 50k |
Implementation |
Aims to minimise additional emission impact of development across the entire York area. Emission savings generally calculated and reported per development. |
Number of publicly accessible EV parking bays available in York (some deliverable via the planning process) |
Low Emission Planning Guidance has been developed to accompany policy ENV1 ‘Air Quality’ of the Local Plan. The guidance outlines CYC's design and mitigation expectations for all new developments in the city, including EV charging. The guidance note was last updated in June 2022 to reflect changes to Building Regulations as outlined in 'Approved Document S: Infrastructure for the charging of electric vehicles'. Further updates to this guidance note are proposed in AQAP4. |
In line with CYC guidance, developers are required to demonstrate how they are mitigating site emission 'damage costs' via the implementation of suitable mitigation measures. Idling Management Plans now required for some sites, such as drive through food retail establishments, where there is the potential for customers to sit in parked vehicles with engines running. |
AQAP3 (7a) |
Reducing emissions from taxis (financial incentives for low emission taxi purchase) |
Promoting low emission transport |
Taxi emission incentives |
2015 |
2024 |
CYC |
CYC and DEFRA Grant |
YES |
Funded |
£100k - £500k |
Implementation |
A hybrid taxi produces approximately 8t per annum of CO2 less than a diesel equivalent and has considerably lower emissions of NOx and PM. Electric taxis eliminate tailpipe emissions of NOx and PM |
Number of low emission taxis purchased / supported through the local grant scheme |
CYC's first incentive scheme was launched in 2015/16 and provided financial assistance to CYC licensed taxi drivers to purchase low emission taxis. CYC was awarded additional DEFRA AQ Grant funding in March 2020 to continue the incentive scheme in 2020/21. The new scheme was formally launched on 10th November 2020. At the end of 2023, CYC had supported 34 taxi drivers with vehicle upgrades and operational costs. Details of the scheme can be viewed at Low Emission Taxi Grant Scheme. |
Further measures to tackle emissions from taxis are included in AQAP4. Current grant funding has now run out. |
AQAP3 (2) |
Anti-idling measures |
Traffic Management |
Anti-idling enforcement |
2015 |
2024 |
CYC |
CYC and DEFRA Grant |
YES |
Funded |
£10k - 50k |
Implementation |
From feasibility report done by TTR Ltd - at 5 busiest service bus locations, estimated savings per annum of 1,526kg NOx, 36kg PM10, 46,555kg CO2,and 17,949 litres of fuel. |
Estimate of idling time saved |
CYC continued to promote its 'Kick the Habit' anti-idling campaign throughout 2023 and worked with partners including schools and businesses to reduce the incidence of vehicle idling across the city. Further promotion of the campaign was also undertaken for Clean Air Day 2023. Work in 2023 reinforces action in previous years, including the erection of permanent signage in all council owned car parks across the city, at most city centre bus stops, multiple taxi ranks and at other key locations across the city. Information about the campaign can be found on CYC’s Kick the Habit Webpage Public Protection Support Officers (PPSOs) assisted with ongoing awareness raising and idling patrols throughout 2023. |
To date CYC has not had to serve any Fixed Penalty Notices (FPNs) specifically for idling. A Fixed Penalty Notice will only be issued if a vehicle has been observed idling on the public highway for more than two minutes (without reasonable cause) and the driver refuses to switch their engine off when asked. The legislation only applies to the public highway and not to private land, such as car parks. It is also not applicable to vehicles waiting in a queue of traffic, unless there’s an obvious source of prolonged delay, such as a level crossing or an incident that’s blocking the highway. Drivers’ are also allowed a reasonable period in which to defrost their vehicles to a safe level during periods of cold weather. With respect to buses, condition 2 of the CAZ Traffic Regulation Condition (see AQAP measure 1) prohibits buses from idling their engines anywhere within the affected CAZ area for more than 2 minutes. This condition applies to all local bus services operating within the affected streets irrespective of service frequency or engine type. Further measures to tackle emissions from idling vehicles are included in AQAP4. |
AQAP3 (3) |
Further development of ECO-Stars Fleet Recognition Scheme |
Vehicle Fleet Efficiency |
Fleet efficiency and recognition schemes |
2015 |
2018 |
CYC |
DEFRA Grant |
YES |
Funded |
£10k - 50k |
Completed |
A typical van operator could see its annual output of carbon dioxide fall by six tonnes per year (see http://www.ecostars-uk.com/about-eco-stars/why-join/) |
Number of operators signed up to the scheme |
ECO-Stars scheme launched March 2013. CYC is not currently actively recruiting new members to the York scheme as funding expired in November 2018, but throughout the project CYC recruited 106 members to the scheme. |
CYC will explore further opportunities for promoting operational best practice with operators / businesses as part of ongoing work to address emissions associated with freight movements and deliveries in York. Further measures to tackle these emissions are included in AQAP4. |
AQAP3 (4) |
Planning and delivery of CNG refuelling infrastructure |
Promoting Low Emission Transport |
Procuring alternative refuelling infrastructure to promote Low Emission Vehicles, EV charging, Gas fuel recharging |
2015 |
2021 |
CYC and third party investment (to be identified) |
Subject to third party investment |
YES |
Partially Funded |
£10k - 50k |
Aborted |
Detailed emission savings were to be determined at planning application stage, but this measure is no longer being progressed |
- |
CNG feasibility study completed in 2013. Potential site identified based on location of high-pressure gas mains to the south west of the city. However, this location is designated greenbelt and line with local air quality and carbon reduction aspirations, promotion of hydrocarbon based fuels is no longer considered appropriate for subsequent AQAPs. This action will not be progressed. Recent research has shown that vehicles fuelled by CNG may emit especially large numbers of ultra-fine particles, with the highest particle number emissions measured during urban driving (i.e. low speeds, cold-starts) which has implications for York’s city centre environment and fine particulate exposure reduction targets (Environment Act 2021). |
Note that estimated cost of £10-£50k was for the feasibility study and not the implementation of a CNG refuelling facility |
AQAP3 (5) |
Freight delivery and service plan for key city centre retailers and streets. |
Freight and delivery management |
Delivery and service plans |
2015 |
2024 |
CYC |
CYC and DEFRA Grant |
YES |
Partially Funded |
£100k - £500k |
Planning |
To be determined |
To be determined |
CYC was awarded additional DEFRA funding in March 2021 to carry out a feasibility study and subsequent pilot scheme to reduce emissions relating to freight deliveries travelling in to and out of York (see update for measure 5a). |
Depends on external investment and planning process. Estimated cost includes feasibility and pilot study only. Further measures to tackle emissions from freight / delivery vehicles are included in AQAP4. |
AQAP3 (5a) |
Freight consolidation Centre |
Freight and delivery management |
Freight consolidation centre |
2015 |
2024 |
CYC and third-party investment (to be identified) |
CYC and DEFRA Grant |
YES |
Partially Funded |
£1 million - £10 million |
Planning |
To be determined |
Number of city centre businesses using consolidation centre. |
CYC was awarded DEFRA funding in March 2021 to carry out a feasibility study and subsequent pilot scheme to reduce emissions relating to freight deliveries travelling in to and out of York. The initial feasibility work aimed to more precisely quantify the emission / air quality impact of freight deliveries in the city and identify suitable sustainable alternatives, which may include a delivery ‘hub’ allowing the last or first mile of the journey to be made by low emission modes, including e-cargo bikes. As part of this work, CYC has engaged with businesses, including delivery companies, on the initial feasibility work and proposed pilot scheme. The initial feasibility study was completed December 2021 although the pilot project has been delayed due to CYC's primary delivery partner withdrawing from the project. CYC has identified a base for the hub pilot, which is expected to progress in 2024 subject to a suitable delivery partner being found. |
The delivery of a permanent freight consolidation centre is subject to third party investment / participation and a suitable site. CYC's ambition is that a sustainable model can be found to allow the operation to continue post pilot. Further measures to tackle emissions from freight / delivery vehicles are included in AQAP4. |
AQAP3 (7b) |
Reducing emissions from taxis (taxi licensing emissions controls) |
Promoting low emission transport |
Taxi licensing conditions |
2015 |
2024 |
CYC |
CYC |
NO |
Funded |
< £10k |
Implementation |
Not yet quantified |
% of ultra-low emission Licensed Taxis operating in York (Electric and Hybrid) At Dec 2023 this was 36.9% |
In October 2022, CYC Licensing and Regulatory Committee approved the issuing of ten new hackney carriage vehicle licences to wheelchair accessible vehicles, which are also fully electric or plug in electric hybrid (e.g. LEVC TX). Updates to CYC's Taxi Licensing Policy currently in progress. Updates to this policy will specify the types of vehicles that CYC will license as taxis in the future. Changes to Licensing Policy will be progressed in full consultation with the trade, including representatives of each registered Hackney Carriage and Private Hire Association. |
Operators may experience some increased vehicle replacement costs as only modern vehicles meeting the required standards are proposed to be licensed as taxis in York. However, national / local government grants can be used to offset the purchase price of replacement vehicles. A DEFRA Air Quality grant allocation was awarded to CYC in 2020 to assist with further taxi upgrades (see update for AQAP3 Measure 7a) Further measures to tackle emissions from taxis are included in AQAP4. |
AQAP3 (8) |
Planning and delivery of strategic EV charging network |
Promoting Low Emission Transport |
Procuring alternative refuelling infrastructure to promote Low Emission Vehicles, EV charging, Gas fuel recharging |
2015 |
2024 |
CYC |
CYC |
NO |
Funded |
£1 million - £10 million |
Implementation |
- |
The number of CYC electric vehicle recharging points in York (at Dec 2023 this was 103) |
EV charging previously provided at 12 hotels in conjunction with Zero Carbon World who provided grants for the installations. CYC Public EV Charging Strategy approved March 2020. CYC intends to deliver an updated Public EV Charging Strategy by 2025, to ensure we continue to provide a robust and fit for purpose future EV charging network across York. Implementation of an extensive ‘pay as you go’ fast charge public electric vehicle recharging network. Upgrades to charging facilities were progressed in 2023. The number of charging episodes reported in the city for 2023 was 36,219 Two HyperHub EV charging sites are now operational (Poppleton Park and Monks Cross). |
Lack of off-street parking is a significant barrier to the uptake of EVs, as the prevailing model for domestic charging involves parking off-street (on a driveway or in a garage) and charging vehicles overnight on a domestic trickle charge. This is a particular issue in York due to high proportions of terraced housing with no off-street parking. In addition, new flatted developments present additional challenges for EV charging due to power management issues and potentially costly supply upgrades. The ultra-rapid HyperHub facilities are aimed at improving recharging facilities for owners of electric vehicles. especially those without off-street parking. CYC is committed to exploring future options for on-street charging. The CYC charging network is complemented by several commercial providers. Residents and visitors can use ZapMap to find the charging options available to them. |
AQAP3 (9a) |
Reducing CYC ‘grey fleet’ trips |
Alternatives to private vehicle use |
Car clubs |
2015 |
2024 |
CYC |
CYC |
NO |
Funded |
£50k - £100k |
Implementation |
- |
Reduction in annual business mileage |
CYC, working in partnership with Enterprise Car Club, provide a range of pool vehicles at various locations near West Offices (Main CYC HQ), Hazel Court and across the city which can be booked online and accessed via a smart membership card. The vehicles available come in a range of sizes and transmission variations so there is something to suit every type of driver. A number of existing diesel pool cars have been replaced with low emission Yaris Petrol Hybrid vehicles as part of the car club initiative. |
CYC membership of car club has significantly reduced the number of people using their own private vehicles on CYC business. Further measures to maximise CYC journey efficiency (and minimise emissions) through use of telematics, training and sustainable travel options for staff are included in AQAP4. |
AQAP3 (9b) |
Introduction of low emission vehicles into CYC fleet |
Promoting Low Emission Transport |
Company vehicle procurement – prioritising uptake of low emission vehicles |
2015 |
2025 |
CYC |
CYC |
NO |
Partially Funded |
£1 million - £10 million |
Implementation |
CYC aims to replace 153 vehicles from its current fleet, reducing CO2 emissions by a third. The entire fleet emits a total of 1,763 tonnes of CO2 each year. |
% of ultra-low emission vehicles in CYC Fleet, operating in York At Jan 2024, the % of fully electric cars / LGVs (<3.5T) in the CYC Fleet was 42%. |
Progressing the transition to an electric fleet for all vehicles under 3.5 tonnes as part of a four-year programme. Major infrastructure upgrades were progressed at CYC’s Hazel Court ECO Depot site throughout 2022 and 2023 to facilitate the introduction of EV charging facilities for operational fleet vehicles. Officers are also exploring options for vehicles over 3.5 tonnes to move away from diesel as a fuel. All depot staff undertaken mandatory Alternative Fuel Vehicle (AFV) training which included information on local air quality and health impacts to raise awareness of air quality issues across the CYC workforce. With respect to waste collection, twelve new refuse trucks, including two fully electric vehicles, have been bought by CYC. The new vehicles will reduce fuel costs and pollution output by approximately 16%. |
Further measures relating to improvements to CYC fleet vehicles are included in AQAP4. |
AQAP3 (9c) |
CYC Eco-driver training and vehicle emission controls |
Vehicle Fleet Efficiency |
Driver training and Eco aids |
2015 |
2021 |
CYC |
CYC |
NO |
Funded |
£10k - 50k |
Completed |
- |
Number of CYC staff obtaining ECO driver training |
Lightfoot trial completed, Fuel additive trial completed, Programme of mandatory HGV driver training completed (including eco-driving element). In mid-2021, CYC implemented a Masternaut telematics system for fleet vehicles to improve safety, reduce emissions and improve vehicle and driver efficiency. |
Ongoing programme of driver training, including mandatory ‘Alternatively Fuelled Vehicles’ training for all staff. |
AQAP3 (10) |
Marketing and Communication Strategy |
Public Information |
Via the Internet |
2015 |
2024 |
CYC |
CYC and DEFRA Grant |
YES |
Funded |
£10k - 50k |
Implementation |
Difficult to quantify exact emission savings as measures aimed at preventing idling / air quality awareness / education |
Number of visitors to website per annum / Idling time saved |
Ad-hoc public communication work ongoing, including ongoing updates to CYC's air quality web pages. ‘Kick the Habit’ anti-idling awareness raising campaign was launched in mid-2019. Campaign posters have been put up in doctors’ surgeries and petrol stations in York. Permanent signage has also been erected in all CYC owned car parks, at most city centre bus stops, multiple taxi ranks and at other key locations across the city where vehicles have been observed idling. Promotion undertaken for Clean Air Day in June 2023 In early 2023, CYC was awarded further DEFRA Air Quality Grant funding to improve public awareness of domestic solid fuel burning practices, particulate emissions and associated health impacts. 'Fuel for Thought' launched in November 2023. Compliance checks across key solid fuel distribution outlets continued in 2023 to ensure that all solid fuels being sold were certified as ‘Ready to Burn’ in line with the Air Quality (Domestic Solid Fuels Standards) (England) Regulations 2020. In October 2023, CYC contacted over 350 farmers to highlight resources and grant opportunities available to assist in adopting best practice with respect to reducing ammonia and particulate emissions. |
Anti-idling awareness / enforcement patrols are undertaken by staff in Public Protection in response to persistent complaints of idling in specific areas. Further measures around improved public information and awareness are included in AQAP4 |
AQAP3 (11a) |
Local incentives for low emission vehicles and alternative fuel use – EV chargers and business demonstrators |
Promoting Low Emission Transport |
Company Vehicle Procurement – Prioritising the uptake of low emission vehicles |
2015 |
2019 |
CYC |
CYC and DEFRA Grant |
YES |
Funded |
£10k - 50k |
Completed |
- |
Number of businesses that have installed EV charging |
CYC has provided advice to other local authorities regarding the operation of electric vehicles and the installation of charging infrastructure within their areas, including Selby District Council and Oxfordshire County Council. CYC has previously facilitated the installation of EV charging infrastructure in a number of business premises. CYC is also supporting the uptake of low emission taxis through the local Low Emission Taxi Grant scheme (see measure AQAP3 7a) |
CYC provides ongoing advice on EV charging to local businesses and other local authorities. Further measures around local incentives for low emission vehicles / modes are included in AQAP4 |
AQAP3 (11b) |
Local incentives for low emission vehicles and alternative fuel use – Priority parking / reduced parking fees for low emission vehicles |
Promoting Low Emission Transport |
Priority parking for LEVs |
2015 |
2024 |
CYC |
CYC |
NO |
Funded |
£10k - 50k |
Implementation |
- |
Number of low emission permits issued |
CYC continued to issue Low Emission Permits (including Household Low Emission Permits) throughout 2023. See https://www.york.gov.uk/LowEmissionParking |
CYC will periodically review the local definition of ‘low emission vehicle’ in the context of local parking discounts, to ensure that incentives remain appropriate and deliver continuous improvement in air quality. Further measures around local incentives for low emission vehicles / modes are included in AQAP4 |
AQAP3 (12) |
Attracting Low Emission industries, businesses and jobs to York |
Policy guidance and development control |
Other policy |
2015 |
2024 |
CYC |
CYC |
NO |
Funded |
£10k - 50k |
Implementation |
Not quantifiable |
Advice provided |
Provided advice to business on low emission technologies/solutions as required. |
Will support wider air quality improvement measures across the city |
AQAP3 (13a) |
Modal shift and network improvement measures (i-Travel York campaign) |
Promoting Travel Alternatives |
Intensive active travel campaign & infrastructure |
2015 |
2024 |
CYC |
DfT / Local Sustainable Transport Fund |
NO |
Funded |
£1 million - £10 million |
Implementation |
Hard to precisely quantify but target to increase modal shift away from conventional car |
% mode split or walking/cycling/bus vs conventional car drivers and car passengers % trips into city centre |
Ongoing delivery of i-Travel York sustainable travel programme - see https://www.itravelyork.info/news for further details and current updates. The iTravel Team work to bring about travel behaviour change in York, through increased sustainable travel. BetterPoints is an app that people in York can download to be rewarded with points for their walk/wheeling, cycle and bus journeys, which can be redeemed with vouchers for shopping, drinks and even charity donations. Events promote sustainable travel, such as the York Walking Festival (Sept 2023), Walk to School Week and journey advice at community/employment sites. Resources, such as cycle videos, cycle map and walk leaflets enable people to travel sustainably. The Active Travel Ambassador programme, run by Modeshift, encourages secondary school children to find ways to make the school run sustainable. The cycle training provided by the Road Safety Team is an important offer that iTravel raise awareness of. The iTravel Team also support travel plans in the city – documents, often done through the planning process, that set out how an organisation will increase the sustainable travel it makes and reduce car journeys. Residential travel plans are a big part of this and the iTravel Team have recently set up a scheme to provide cycle vouchers, bus passes and car club offers at new residential estates, using section 106 funding. |
The i-Travel York programme was established following a successful bid for funding from the DfT's Local Sustainable Transport Fund. The programme has been delivering an integrated programme of personal, business and school travel planning, combined with targeted infrastructure enhancements to increase people's travel choices since 2012. I-Travel York aims to inspire people in York to help look after our city - to keep it moving and keep the air clean - by considering travel options before making a journey. |
AQAP3 (13b) |
Modal shift and network improvement measures (Bus Improvements) |
Transport planning and infrastructure |
Public transport improvements interchanges, stations and services |
2015 |
2025 |
CYC |
CYC/DfT |
NO |
Funded |
> £10 million |
Implementation |
Aim to increase uptake of public transport |
National Annual Passenger satisfaction survey |
CYC and bus operators have worked together to improve York’s bus network in previous years through the York Quality Bus Partnership. Innovations in York have included improvements to bus information, including new on-street timetables and more real time displays; two new park and ride sites at Askham Bar and Poppleton Bar; fare reductions and new tickets; improvements to well used bus stops in the city centre including Museum Street and Exhibition Square; new electric buses on park and ride services; introduction of refurbished electric open-top buses on the City Sightseeing tour service ; new vehicles and higher frequencies on some existing services; introduction of a multi-operator “All York” ticket and a smartcard ticket; the introduction of two “Bus Wardens” and the bus enquiry desk at the Railway Station to help passengers. CYC published its Bus Service Improvement Plan (BSIP) in October 2021. The plan, a document required by the government’s Department for Transport (DfT) National Bus Strategy published in March 2021, reflects the key priorities for improving bus services across the city. A statutory Enhanced Partnership between CYC and local bus operators was made by officers on 27th September 2022; this is a prerequisite to secure the confirmed £17.36 million in BSIP funding from DfT. This award is in addition to £8.4m ZEBRA (Zero Emission Bus Regional Area) funding allocated to the council. BSIP funding will be used to implement a range of improvements to the city's bus network and associated infrastructure between 2022 and 2025 |
See York Bus Service Improvement Plan (BSIP) York Enhanced Partnership for Buses formally came into effect on 27th Sept 2022. This will act as the principal delivery body for the £17.36m BSIP funding. Delivery of the BSIP forms a measure in AQAP4 |
AQAP3 (13c) |
Modal shift and network improvement measures (Other LTP measures) |
Transport planning and infrastructure |
Other |
2015 |
2024 |
CYC |
CYC / West Yorkshire Plus Transport Fund / DfT |
NO |
Funded |
£500k - £1 million |
Implementation |
- |
Concentration reduction target in LTP3 and AQAP3 |
Measures in LTP3 (published 2011) can be viewed online at Local Transport Plan (Also see updates against measure 13b). Funding obtained to deliver major schemes for York Central, increasing the capacity of the A1237 (between the A19N and Hopgrove roundabout junctions) and improve the area in front of York Station. LTP4 currently in development. In February 2023, CYC developed a draft Local Transport Strategy, that set out high level principles and priorities for York that will underpin future transport strategies. See 'Our Big Transport Conversation'
|
The York Outer Ring Road (YORR) project has been underway since 2017 when CYC were allocated approximately £38m for improvements to the A1237 using funds from the West Yorkshire Plus Transport Fund. This funding was for upgrades of 7 roundabouts from Wetherby Road to Monks Cross. In early 2019 the upgrade of the A1237/B1224 Wetherby Road roundabout was completed. In October 2019 the Department for Transport awarded CYC £26m from its Major Road Network fund to dual the Outer Ring Road from A19 Rawcliffe (Shipton Road) roundabout to A1036 Little Hopgrove (Malton Road) roundabout. |
AQAP3 (14) |
Other air quality improvement measures (non-transport sources) |
Environmental Permits |
Introduction/Increase of Environment charges through permit systems and economic instruments |
2015 |
2024 |
CYC |
CYC |
NO |
Funded |
£10k - 50k |
Implementation |
- |
Number of scheduled inspections completed per annum |
Enforcement of relevant air quality legislation is currently undertaken by the Environmental Protection team. Estimated cost of measure is staffing resource but this will be offset by permit costs. |
Additional measures to tackle non-transport sources are included in AQAP4 |
AQAP3 (15) |
Provide more green infrastructure |
Policy Guidance and Development Control |
Other policy |
2015 |
2024 |
CYC |
CYC |
NO |
Partially Funded |
£100k - £500k |
Implementation |
- |
Trees planted |
Protecting and enhancing York’s natural environment is a key influence and delivery mechanism in the Council’s 10 year strategies and York 2032:10 year plan. York’s natural environment is a key component for meeting the city’s requirements for climate change, particularly relating to our Climate Emergency which set an ambition for York to be a net-zero carbon city by 2030. CYC has a dedicated ‘Green Streets’ project team working to increase the tree canopy cover across York. The council has set a target to increase York's tree canopy to 13% by 2050 and is working with schools and communities to deliver this ambition. |
For further details see: |
16 |
Further conversion of diesel double decker tour buses to electric |
Vehicle Fleet Efficiency |
Vehicle Retrofitting programmes |
2014 |
2019 |
CYC |
DfT Clean Bus Technology Fund |
NO |
Funded |
£100k - £500k |
Completed |
The 4 electric buses used in York reduced tailpipe emissions in the city |
Number of buses converted to electric |
CYC made a bid to DfT’s Clean Bus Technology Fund (CBTF) in 2013 for funds to convert six open-top buses used on York’s City Sightseeing tour service from diesel engines to fully electric. Four buses were converted and entered service under this programme. The remaining 2 buses were not converted due to the performance of the retro-fitted electric buses on the ground not meeting an acceptable threshold of reliability, causing operational issues for the service. CYC's experience was not unique in this respect, with a project at another historic UK city suffering problems with the supply of retro-fitted electric buses, similar to those in York. Although the York trial was not successful in meeting its primary objective, it has been successful in delivering against other objectives. It allowed a five year trial of retro-fitted buses, which has yielded much useful data in the development of subsequent electric bus projects. Use of the electric buses in York has both led to investment in the P&R fully electric bus fleet and Transdev’s electric bus fleet in Harrogate. York and Harrogate now have some of the most intensively used electric buses in the UK and use of the new, as opposed to retrofitted, electric buses has been entirely successful. |
York's Clean Air Zone means that it is not now possible to use the previous fleet of older diesel buses on the City Sightseeing Tour service. After 31/01/2021 this service needed to be Euro VI diesel or better to achieve compliance with the CAZ. |
17 |
Retrofitting of school buses |
Vehicle Fleet Efficiency |
Vehicle Retrofitting programmes |
2016 |
2022 |
CYC |
DfT Clean Bus Technology Fund |
NO |
Funded |
£100k - £500k |
Completed |
- |
Number of retrofitted school buses |
Following the withdrawal of the Clean Vehicle Retrofit Accreditation Scheme (CVRAS) certification for the primary vehicle retrofit manufacturer, no further vehicles were retrofitted although York Pullman invested £1.2m in new vehicles in the previous reporting year of 2021. CYC will continue to drive improvements in emission standards through contractual arrangements for school buses (and taxis). |
Clean Bus Technology Funding of £308K previously obtained to support this measure |
18 |
Solar panels at electric P&R sites |
Promoting Low Emission Transport |
Procuring alternative Refuelling infrastructure to promote Low Emission Vehicles, EV recharging, Gas fuel recharging |
2017 |
2021 |
CYC |
European Regional Development Fund (ERDF) |
NO |
Funded |
£1 million - £10 million |
Completed |
- |
Amount of energy generated by solar panels |
CYC secured European funding (ERDF) to allow the delivery of a full solar canopy/battery storage solution in addition to the proposed charging points at Monks Cross and Poppleton Bar. Planning applications for the new ultra rapid charge units and solar canopies were approved in November 2019. The solar canopies have a generation capacity of up to 400kW powering a mix of charge points. |
- |
19 |
Hyper Hubs |
Promoting Low Emission Transport |
Procuring alternative Refuelling infrastructure to promote Low Emission Vehicles, EV recharging, Gas fuel recharging |
2016 |
2023 |
CYC |
CYC and OLEV |
NO |
Funded |
£1 million - £10 million |
Completed |
- |
Number of charging episodes at hyper hubs |
Two Hyper Hub sites now fully operational at Poppleton and Monks Cross. Both Hyper Hub sites contain 4 ultra-rapid (175kW) and 4 Rapid (50kW) vehicle chargers, helping to support the uptake of modern electric vehicles that have larger battery capacities and are capable of ultra-rapid charging. HyperHubs have been part funded by Office for Low Emission Vehicles and the European Regional Development Fund. CYC is currently working on a third city centre site. See https://www.york.gov.uk/hyperhubs |
The CYC operated network is complemented by several commercial providers. Details of all charge points in the city can be viewed using ZapMap |
2.3 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[7], 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.
The Public Health Outcomes Framework includes an indicator relating to the fraction of mortality attributable to particulate pollution. This indicator enables Directors of Public Health to prioritise action on air quality in their local area to help reduce the health burden from air pollution. Indicator D01 ‘Fraction of mortality attributable to particulate air pollution’ is defined as the fraction of annual all-cause adult mortality attributable to particulate air pollution (measured as fine particulate matter, PM2.5), expressed as the percentage of annual deaths from all causes in those aged 30+.
It is estimated that long-term exposure to air pollution (specifically, PM2.5) was a contributory factor to the cause of death in 4.6% of deaths in York in 2022 (latest data available at the time of writing). This figure is less than the figure reported for the wider Yorkshire and Humber region in 2022 (5.1%) and less than the average figure reported for England in 2022 (5.8%).
It is widely accepted that fine particulate matter has a significant impact on both morbidity and mortality and diesel emissions have been classified as carcinogenic by the International Agency for Research on Cancer (part of the World Health Organisation). There is particular concern about the ‘black carbon’ fraction of particulate matter due to its health impacts, and its strong ability to absorb light energy and increase global warming. Black carbon emissions in urban environments arise predominantly from diesel transport, but are also a product of biomass combustion, used increasingly for energy production and space heating.
Emissions of oxides of nitrogen (NOx) and man-made particulate must be reduced to meet the health based national air quality objectives in York and improve public health.
To date CYC has produced two trip reduction / modal shift based Air Quality Action Plans (AQAPs) and in 2015 adopted a third Action Plan (AQAP3) focussing on reducing vehicle tailpipe emissions from the remaining vehicle fleet through the use of low emission technologies. In 2023/24 CYC consulted on an updated Action Plan (AQAP4) that outlines the action CYC will take to further improve air quality in York over the next 5 years to go beyond health-based National Air Quality Objectives in all areas and work towards meeting World Health Organisation (WHO) Air Quality Guidelines. AQAP4 aims to reduce concentrations of air pollutants and exposure to air pollution, thereby improving the health and quality of life of residents and visitors to York. AQAP4 recognises that there are no ‘safe’ limits for particulate emissions, particularly PM2.5. The maximum concentration of PM2.5 monitored in York in 2023 was 8.0µg/m3 at the Fishergate site.
CYC is demonstrating a commitment to addressing PM2.5 through measures in its Air Quality Action Plan and wider associated strategies. Some specific items related directly to reducing fine particulate emissions (and indeed related to reducing exposure to such emissions) are described below:
· Exposure Reduction through the Planning Process [Measure AQAP3(6)] - Air quality staff routinely comment on planning applications to ensure that new developments are designed in a way which minimises exposure to air pollution and further emission growth. The most recent approach requires developers to calculate the damage costs of the additional emissions that their developments will cause and to mitigate this using a range of sustainable transport and low emission vehicle measures. Such measures must be considered reasonable and proportionate, relative to the damage costs associated with the development. Pre-planning advice is often provided on locations for key exposure sites (e.g. housing, schools, sports facilities, medical facilities etc.) and the use of biomass heating systems is generally discouraged in urban areas and near sensitive receptors.
· Policy Led Exposure Reduction [Links to various AQAP3 measures] – CYC’s Public Protection team work alongside other council departments with joint inputs into key council policies that can impact on air quality and exposure reduction. Examples of previous joint policies include the Local Transport Plan / Strategy, Local Plan, Climate Change Strategy, Air Quality Action Plan and Low Emission Strategy. Work continues to strengthen links between air quality and the Health and Wellbeing Strategy. In 2019, CYC announced a Climate Emergency and have since set an ambition for CYC to reduce its carbon emissions to net zero by 2030. CYC recognise the threat of climate change at both a global and local scale, and are committed to delivering bold, local climate action to deliver economic and social benefits, such as new green jobs, economic savings, market opportunities and much improved well-being for York residents. Air quality improvement strategies in York complement the wider climate change/carbon reduction agenda and are well aligned to recognise synergies and prevent conflict.
· Information Led Exposure Reduction [Measure AQAP3(10)] - at the present time there is no single marketing and communications strategy at a national level to deal with dissemination of public information on the links between health, air quality and transport. Acting as part of the Low Emission Partnership (alongside Bradford Metropolitan District Council and Lancaster City Council), CYC obtained DEFRA AQ Grant funding to develop a new Air Quality Knowledge Hub. Focused on information exchange between local authority professionals, the Hub features a range of content areas related to air quality improvement measures that local authorities can adopt, as well as more specific practitioner advice notes that focus on various aspects of local air quality management, planning, monitoring and enforcement. The Hub also includes a growing library of relevant case studies and a forum to facilitate discussion and information exchange. It was also updated in 2023 to include a dedicated resource area for hosting communication materials arising from DEFRA funded Air Quality Grant Projects. CYC has also undertaken promotional work in relation to anti-idling as part of Clean Air Day and raised awareness of the links between idling emissions, air quality and health impacts.
In early 2023, CYC was awarded further DEFRA Air Quality Grant funding to improve public awareness of domestic solid fuel burning practices, particulate emissions and associated health impacts. We undertook research via a online survey and hosted a number of focus groups with the local community to inform the creative route for the campaign, which was launched in November 2023. Details of the ‘Fuel for Thought’ campaign can be found online.
Additionally in 2023, CYC was awarded DEFRA funding to develop an online air pollution forecasting and notification service to allow residents and visitors to York to access information that allows them to minimise their own exposure when pollution episodes are forecast. The York Air Alert service is of particular benefit to anyone who suffers from health conditions exacerbated by poor air quality. The service provides a 3-day forecast of air pollution with 8 zones of York. The service is free to subscribe to and provides notifications via email, text and voicemail to users.
· Low Emission Vehicle Upgrades [AQAP3 Measures 16 & 17] – In August 2023, First Bus together with CYC ‘switched on’ a new fleet of zero emission buses for York in a transformation that will see the York bus depot become one of the first outside London to be fully electric. With these additional vehicles, the First York bus fleet will become fully electric by the end of 2024, significantly reducing carbon, NOx and particulate emissions across the city. The new buses, supported by funding through DfT’s Zero Emission Bus Regional Areas (ZEBRA) scheme, complement the existing electric buses serving York’s Park and Ride sites. CYC has also been awarded additional funding to support the development of key schemes and initiatives in line with York’s Bus Service Improvement Plan (BSIP), including wider electrification of the urban bus fleet, bus priority measures, improvements to stops, shelters and passenger information. The York Enhanced Partnership for Buses will act as the principal delivery body for the BSIP funding until 2025.
· Clean Air Zone [Measure AQAP3(1)] – The Clean Air Zone (CAZ) for buses in the city centre was launched on 31st January 2020. Buses making 5 or more entrances to the CAZ per day are now required to be low emission (Euro VI diesel or electric). A total of £1,654,000 was allocated by CYC to 5 bus operators to help replace/retrofit 93 buses that pass through the city centre Air Quality Management Area (AQMA). Low / zero emission buses will reduce the amount of fine particulate (as well as NOx) emitted in the city.
· Low Emission Taxis [Measure AQAP3(7)] – York has previously pioneered a taxi grant scheme aimed at encouraging taxi drivers to move away from diesel/petrol to petrol hybrid and electric taxis. Further funding was awarded to York under DEFRA’s 2019/20 Air Quality Grant Scheme to accelerate the transition to electric and other ultra-low emission taxis. Through the taxi incentive scheme and changes to Taxi Licensing Policy, the number of low emission (fully electric or electric hybrid) taxis in the York fleet has been increased to approximately 37% (figure correct as of end December 2023). Traditional petrol hybrid, plug-in hybrid and electric cars produce significantly lower tailpipe emissions than diesel equivalents.
· Low Emission Vehicle Events – In previous years, CYC has held various Low Emission Vehicle events for the public to showcase a variety of electric cars and bikes.
· Clean Air Act / Smoke Control Areas – Under the requirements of the Clean Air Act, certain areas of York have been designated Smoke Control Areas (SCAs), where emissions of smoke from chimneys of domestic properties are prohibited. CYC continue to enforce existing smoke control areas to reduce particulate emissions and nuisance. In 2023, we developed a new Enforcement Protocol for civil penalties for smoke emissions within Smoke Control Areas (under the Clean Air Act 1993, as amended by the Environment Act 2021). This protocol is subject to member decision in 2024. CYC also undertakes seasonal promotion of the rules around SCAs and issued advice and guidance to residents on the use of appropriate fuels and maintenance of appliances in line with the Government’s national ‘Burn Better’ campaign. This promotional work accompanies compliance checks across retailers within CYC’s area to ensure that all solid fuels being sold are certified as ‘Ready to Burn’ in line with the Air Quality (Domestic Solid Fuels Standards) (England) Regulations 2020. As mentioned above, CYC has also launched a DEFRA funded campaign specifically aimed at improving public awareness of domestic solid fuel burning practices, particulate emissions and associated health impacts.
· First/last mile delivery options - City of York Council was awarded £297,237 by DEFRA in March 2021 to carry out a feasibility study and subsequent pilot scheme to reduce emissions relating to deliveries travelling in to and out of York. The project will focus on how to reduce the number of deliveries made to the city centre and around York by LGVs and HGVs. This will directly reduce particulate and other emissions. Unfortunately, this project has been significantly delayed to staff shortages and withdrawal of CYC’s primary delivery partner for the pilot. It is hoped to progress this project in 2024.
Throughout 2023, CYC’s Director of Public Health and colleagues in the Public Health team have been involved in in the development of AQAP4 and delivery of air quality improvement measures. CYC maintain good contacts within the sustainability team at the York and Scarborough NHS Trust and have delivered a number of joint Clean Air Day awareness raising events in partnership with them.
This section sets out the monitoring undertaken within 2023 by City of York Council (CYC) and how it compares with the relevant air quality objectives. In addition, monitoring results are presented for a five-year period between 2019 and 2023 to allow monitoring trends to be identified and discussed.
3.1 Summary of Monitoring Undertaken
CYC undertook automatic (continuous) monitoring at 9 sites during 2023. Table A.1 in Appendix A shows the details of the automatic monitoring sites. NB. Local authorities do not have to report annually on the following pollutants: 1,3 butadiene, benzene, carbon monoxide and lead, unless local circumstances indicate there is a problem. The Air Quality England page presents automatic monitoring results for CYC’s area, 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.
Whilst there have been no significant changes to CYC’s overall automatic monitoring strategy (in terms of monitoring locations) in the last 12 months, the following upgrades have occurred to ensure compliance with LAQM requirements. Note that the pollutants monitored are the same, with the exception of Holgate Road which now monitors PM2.5 instead of PM10.
· Gillygate - upgrade to NOx analyser (Thermo 42i NOx) and PM2.5 monitor (Thermo 1405F PM2.5)
· Lawrence Street – upgrade to enclosure, A/C and NOx analyser (Thermo 42i NOx)
· Holgate Road – upgrade to enclosure, A/C, NOx analyser (Thermo 42i NOx) and PM2.5 monitor (Thermo 1405F PM2.5)
CYC undertook non- automatic (i.e. passive) monitoring of NO2 at 233 sites (including blank) during 2023. Table A.2 in Appendix A presents the details of the non-automatic sites.
Maps showing the location of the monitoring sites are provided on City of York Council’s website. 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).
For diffusion tubes, the full 2023 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.
The highest annual mean concentration of NO2 recorded at a location representative of long-term public exposure in 2023 was 43µg/m3 near the junction of Gilllygate and Bootham (Diffusion tube reference A1).
Improvements in annual mean NO2 monitored at roadside continuous monitoring stations were observed between 2022 and 2023 at Fishergate (10% improvement), Nunnery Lane (7% improvement), Gillygate (7% improvement), Lawrence Street (8% improvement) and Heworth Green (13% improvement). Annual mean NO2 monitored at Holgate Road and Fulford Road in 2023 was broadly comparable to that monitored in 2022 (~1% change).
Annual mean background concentrations of NO2 monitored at Bootham Park Hospital (CYC’s urban background continuous monitoring site) also improved by 6% between 2022 and 2023.
Concentrations of NO2 monitored at the majority of locations in York throughout 2023 continue the general downward trend in NO2 concentrations monitored in the city since 2012. Ongoing air quality monitoring in all locations will be fundamental to understanding the longer-term environmental impacts of the pandemic and the magnitude of any changes due to increased sustained levels of walking and cycling, changes in public transport use and ongoing air quality improvement initiatives.
With respect to the city centre AQMA, 5 CYC monitoring locations measured annual mean NO2 concentrations of 40µg/m3 or above in 2023. Exceedances of the health based annual mean NO2 objective of 40µg/m3 were monitored at one location on Gillygate (Diffusion Tubes 7), at the junction of Gillygate and Bootham (Diffusion Tubes A1) and on Rougier Street (Diffusion Tube 115[8]). Two further locations on Gillygate (Diffusion Tubes 13 and 14) measured annual mean NO2 concentrations equal to the objective of 40µg/m3.
Maximum annual mean concentrations of NO2 monitored at relevant locations across the current AQMA were 43µg/m3 (Gillygate / Bootham), 37µg/m3 (George Hudson St / Rougier St), 37µg/m3 (Holgate / Blossom Street), 31µg/m3 (Lawrence St), 29µg/m3 (Fishergate / Paragon St), 26µg/m3 (Prices Lane/Nunnery Lane) and 35µg/m3 (Coppergate). Maximum concentrations of NO2 decreased in all these areas between 2022 and 2023 and ranged from 2% lower on Coppergate (in 2023) to 16% lower around Prices Lane / Nunnery Lane and Rougier Street (in 2023).
In line with DEFRA’s LAQM guidance, before revoking an AQMA on the basis of measured pollutant concentrations, a local authority needs to be reasonably certain that any future exceedences of air quality objectives are unlikely. For this reason, it is expected that local authorities will need to consider measurements carried out over several years or more, national trends in emissions, as well as local factors that may affect the AQMA. Additionally, where NO2 monitoring is undertaken using diffusion tubes, to allow for the uncertainty associated with the monitoring method, it is recommended that revocation of an AQMA should only be considered following three consecutive years of annual mean NO2 concentrations being lower than 36µg/m3 (i.e. within 10% of the annual mean NO2 objective). CYC will keep the AQMA boundary under review taking into account these guidelines.
Concentrations of NO2 monitored in the former Fulford Road AQMA in 2023 continue to be well below the annual mean objective of 40µg/m3. The highest recorded levels of NO2 in this area were monitored on Fulford Main Street (Diffusion Tube C58) and were 25µg/m3. This supports the decision to revoke the Fulford Road AQMA, as discussed in CYC’s previous Annual Status Reports and implemented in February 2020.
Concentrations of NO2 monitored in the former Salisbury Terrace / Leeman Road AQMA in 2023 were also all well below the annual mean objective of 40µg/m3. The highest recorded levels of NO2 in this area were monitored on Salisbury Terrace (Diffusion Tube 104) and were 27µg/m3. This confirms that the decision to revoke this AQMA in December 2017 was appropriate.
In December 2018, the boundary of the city centre AQMA was extended to include the full length of Coppergate and the buildings either side of the road, due to monitored concentrations of NO2 above the annual mean objective for this pollutant. The highest annual mean concentrations of NO2 monitored along Coppergate in 2023 was 35µg/m3 at site D56 (Three Tuns Pub, 12 Coppergate) which is below the annual mean objective for this pollutant. Whilst annual mean concentrations of NO2 were below the objective in this location in 2022 and 2023 (35-36 µg/m3), they are well above concentrations monitored in 2020 and 2021 (31-32 µg/m3). It is therefore considered appropriate to keep this area of the city under observation to establish longer term trends, prior to making any amendments to the AQMA boundary.
Revisions to the AQMA Order in 2018 also removed the reference to breaches of the short-term hourly objective along George Hudson Street / Rougier Street / Bridge Street based on monitoring results in this area. The latest 2023 monitoring results for this area of the city indicate that this short-term objective is still being met (all annual mean concentrations were less than 60µg/m3 which suggests that an exceedance of the 1-hour mean objective is unlikely).
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.
CYC monitored particulate (PM10) at 4 sites in the city in 2023 (Bootham, Fishergate, Holgate Road and Plantation Drive). National air quality objectives for PM10 are currently met in York; this has been the case since monitoring of PM10 was established in the city. The highest annual mean concentration of PM10 monitored in York during 2023 was 16.8µg/m3 at the Holgate Road continuous monitor. Along with many areas of the UK, this concentration is above the World Health Organisation (WHO) guideline for this pollutant, which has recently been strengthened to 15µg/m3. Annual mean concentrations of PM10 monitored in 2023 were below levels monitored in 2022 at all 4 CYC sites.
At roadside locations between 2022 and 2023, annual mean PM10 decreased at Plantation Drive, Holgate Road and Fishergate by 5%, 6% and 19% respectively. Annual mean concentrations of PM10 monitored at the Bootham background site also decreased by 23% between 2022 and 2023. Based on PM10 monitoring data over the last 5 years, there does not appear to be any clear trend in PM10 concentrations.
Table A.8 in Appendix A presents the ratified and adjusted monitored PM2.5 annual mean concentrations for the past five years.
Although not explicitly required under the Local Air Quality Management regime, where Local Authorities undertake PM2.5 monitoring they are encouraged to report it as part of the Annual Status Report. Micro-particulate, or PM2.5, is the pollutant which has the biggest impact on public health and on which the Public Health Outcomes framework (PHOF) indicator is based.
CYC monitored PM2.5 at four locations in the city in 2023, namely Bootham (urban background site), Fishergate, Gillygate and Holgate (roadside sites). Monitoring of PM2.5 at Fishergate and Bootham is carried out as part of DEFRA’s Automatic and Rural Monitoring Network (AURN). Monitoring at Gillygate and Holgate was established by CYC as a result of the growing concerns over the health impacts of PM2.5.
National air quality objectives for PM2.5 are currently met in York. The highest annual mean level of PM2.5 monitored in York during 2023 was 8.0µg/m3 at the Fishergate monitor. This compares with a maximum level of 8.8µg/m3 monitored in 2022, also at Fishergate. All monitored concentrations in 2023 are well within the current annual mean objective of 10µg/m3. As with most areas of the UK, monitored concentrations of PM2.5 in York are above the WHO Guideline value of 5µg/m3 for this pollutant.
Between 2022 and 2023, annual mean concentrations of PM2.5 decreased at Bootham and Fishergate (10% and 8% respectively) and remained the same at Gillygate at 7.2µg/m3. Trends over the last 5 years reveal that concentrations of PM2.5 have generally decreased across the city.
Three air quality indicators have been developed to look at trends in air quality across AQMAs/technical breach areas and are as follows:
Indicator CAN027 – Average Annual Mean Nitrogen Dioxide Concentration in each area of technical breach. This indicator provides an average nitrogen dioxide concentration within areas of the AQMA where properties are included in the boundary and breaches of the annual mean objective have previously been monitored (historical areas of technical breach, such as Salisbury Terrace, are also shown for information). Monitoring results include bias corrected diffusion tube data and data from continuous monitors (if applicable). Trends for CAN027 between 2019 and 2023 are shown below:
Average concentrations of NO2 monitored in 2023 were equal to (within 0.3µg/m3) or lower than 2022 in all areas. Indicator CAN027 continues to suggest a steady downward trend in NO2 concentrations over the last 10+ years. It should be noted that NO2 concentrations in 2020 were atypical / depressed due to the Covid-19 pandemic, as shown on the graph above.
Indicator CAN028 - Maximum Nitrogen Dioxide Concentration (at relevant location) in each area of Technical Breach. This indicator provides a maximum recorded annual mean nitrogen dioxide concentration within areas of the AQMA where properties are included in the boundary and breaches of the annual mean objective have previously been monitored (historical areas of technical breach, such as Salisbury Terrace and Fulford Road, are also shown for information). This only considers monitoring at relevant locations and is therefore useful to look at the validity of existing AQMA boundaries year to year. Trends between 2019 and 2023 are shown below:
The maximum annual mean NO2 concentration monitored at a relevant location in 2023 was 42.6µg/m3 (Diffusion tube A1 near the junction of Gillygate and Bootham). Maximum concentrations of NO2 in all other areas in 2023 were below the annual mean NO2 objective and decreased between 2022 and 2023. Of the 3 areas that exhibited breaches of the annual mean NO2 objective in 2022, namely Blossom St/Holgate, Gillygate/Lord Mayor’s Walk and Rougier Street/George Hudson St, all areas exhibited improvements in 2023 (10%, 10% and 16% respectively).
Whilst there is a long-term downward trend in NO2 concentrations over the last 10+ years for most areas of the AQMA, maximum concentrations of NO2 in and around Gillygate have been more variable over the last 5/6 years. It should, however, be noted that the current 2023 maximum value of 42.6µg/m3 in Gillygate is lower than that monitored in 2021 and 2022 and indeed the lowest concentration recorded over the last 13 years (with the exception of 2020 during the pandemic).
Indicator CAN038: Average of maximum annual mean nitrogen dioxide concentrations recorded across three areas of technical breach (at points of relevant public exposure). With the exception of the current monitoring year of 2023 (and 2020 during the pandemic), CYC’s air quality monitoring network has previously demonstrated sustained exceedances of the NO2 objective of 40µg/m3 in 3 areas of the city, namely Gillygate/Lord Mayor’s Walk, Blossom Street/Holgate Road, and Rougier Street / George Hudson Street. These are referred to as ‘technical breach areas’ and fall within CYC’s AQMA. Whilst not all monitoring points within these areas are exceeding health-based standards, there has previously been at least one monitor at a point of relevant public exposure within each area that is above the annual mean objective of 40µg/m3. Indicator CAN038 considers an average of the maximum annual mean concentrations of NO2 in these three areas (specific values for the 3 respective areas are shown in indicator CAN028 above).
Whilst the (draft) AQAP4 target value of 43µg/m3 was met in 2023 (and the indictor is lower than 40µg/m3) it should be noted that the Gillygate area remains in breach of the 40µg/m3 annual mean NO2 objective as shown by indicator CAN028 above).
For the purpose of monitoring the impact of York’s Local Transport Plan a local air quality indicator was established and has been reported over the last 20+ years. This indicator measures the mean of annual average results obtained from 36 diffusion tubes located within CYC’s city centre AQMA. Trends in this indicator between 2002 and 2023 are shown below:
This indicator suggests that NO2 concentrations across the city were in general decline between 2002 and 2005. This was followed by a steady increase in concentrations between 2006 and 2010. There has been an ongoing downward trend in NO2 concentrations across the city centre AQMA over the last 13 years. The figure of 23µg/m3 recorded in 2023 is the lowest recorded value since the indicator was established in 2002 and was comparable to that monitored in 2020 during the pandemic (a result of significantly lower traffic levels and associated emissions in the city as a result of the Covid-19 lockdowns). This reinforces trends seen with other council air quality indicators described above.
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) |
CM1 |
Bootham |
Urban Background |
460022 |
452777 |
NOx, PM10, PM2.5 |
No |
C, BAM |
60 |
49.6 |
3.0 |
CM2 |
Fishergate |
Roadside |
460746 |
451038 |
NOx, PM10, PM2.5 |
Yes - AQMA No.5 |
C, BAM |
10 |
3.2 |
2.7 |
CM3 |
Holgate |
Roadside |
459512 |
451282 |
NOx, PM10, PM2.5 |
Yes - AQMA No.5 |
C, TEOM, TEOM 1405 |
12 |
2.5 |
1.7 |
CM4 |
Nunnery Lane |
Roadside |
460068 |
451199 |
NOx |
Yes - AQMA No.5 |
C |
4 |
1.7 |
1.7 |
CM5 |
Gillygate |
Roadside |
460147 |
452345 |
NOx, PM2.5 |
Yes - AQMA No.5 |
C, TEOM 1405 |
3 |
2.1 |
2.5 |
CM6 |
Lawrence Street |
Roadside |
461256 |
451340 |
NOx |
Yes - AQMA No.5 |
C |
5 |
3.2 |
1.7 |
CM7 |
Heworth Green |
Roadside |
461126 |
452602 |
NOx |
No |
C |
3 |
1.2 |
1.5 |
CM8 |
Plantation Drive |
Roadside |
457428 |
452620 |
PM10 |
No |
TEOM |
17 |
1.0 |
1.7 |
CM9 |
Fulford Road |
Roadside |
460937 |
449464 |
NOx |
No |
C |
19 |
5.0 |
1.7 |
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
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) |
5 |
Lamp post 15 Forge Close, Jockey Lane |
Roadside |
462040 |
454883 |
NO2 |
NO |
16.9 |
1.9 |
N |
~2.75 |
6 |
Lamp post top of Nunnery Lane Car Park |
Roadside |
459777 |
451406 |
NO2 |
YES |
7.7 |
2.8 |
N |
~2.75 |
7 |
Gillygate opposite Portland Street |
Roadside |
460217 |
452421 |
NO2 |
YES |
2.3 |
0.3 |
N |
~2.75 |
8 |
Portland Street - triplicate |
Urban Background |
460163 |
452468 |
NO2 |
NO |
3.7 |
1.8 |
N |
~2.75 |
9 |
Portland Street - triplicate |
Urban Background |
460163 |
452468 |
NO2 |
NO |
3.7 |
1.8 |
N |
~2.75 |
11 |
Holly Bank |
Urban Background |
458846 |
450946 |
NO2 |
NO |
7.7 |
0.7 |
N |
~2.75 |
13 |
Papillion hotel, Gillygate |
Roadside |
460176 |
452377 |
NO2 |
YES |
0.1 |
1.5 |
N |
~2.75 |
14 |
Gillygate Surgery |
Roadside |
460167 |
452347 |
NO2 |
YES |
0.2 |
2.3 |
N |
~2.75 |
15 |
Foss Islands Rd |
Roadside |
461105 |
451458 |
NO2 |
YES |
1.9 |
1.9 |
N |
~2.75 |
16 |
Prices Lane |
Roadside |
460160 |
451152 |
NO2 |
YES |
2.5 |
1.2 |
N |
~2.75 |
17 |
Drainpipe of house 18 Queen St |
Roadside |
459646 |
451500 |
NO2 |
YES |
0.2 |
1.3 |
N |
~2.75 |
18 |
Lamp post 4 Haxby Road |
Roadside |
460457 |
452903 |
NO2 |
YES |
3.3 |
1.9 |
N |
~2.75 |
25 |
Heworth Road - Lamp post 6 |
Roadside |
461721 |
452709 |
NO2 |
NO |
7.2 |
1.4 |
N |
~2.75 |
26 |
Haleys Terrace (previously Longwood Road) |
Roadside |
460829 |
453524 |
NO2 |
NO |
8.5 |
0.4 |
N |
~2.75 |
33 |
Haxby Road (nr Whitecross Rd) |
Roadside |
460598 |
453227 |
NO2 |
NO |
14.5 |
1.7 |
N |
~2.75 |
35 |
Carr Lane |
Roadside |
457603 |
451492 |
NO2 |
NO |
6.2 |
2.9 |
N |
~2.75 |
37 |
Jarvis Abbey Park |
Roadside |
459522 |
451187 |
NO2 |
YES |
21.6 |
2.7 |
N |
~2.75 |
44 |
Lamp post 8 Monkgate Cloisters |
Roadside |
460679 |
452326 |
NO2 |
YES |
2 |
1.6 |
N |
~2.75 |
45 |
Clarence St |
Roadside |
460319 |
452754 |
NO2 |
YES |
3.6 |
2 |
N |
~2.75 |
47 |
Strensall Road |
Roadside |
462009 |
456996 |
NO2 |
NO |
19.2 |
0.8 |
N |
~2.75 |
50 |
BLANK |
N/A |
N/A |
N/A |
NO2 |
N/A |
N |
N/A |
N |
N/A |
60 |
First Lamp post on Navigation Road |
Roadside |
461017 |
451781 |
NO2 |
YES |
13 |
0.2 |
N |
~2.75 |
78 |
Gillygate Monitoring Station - triplicate |
Roadside |
460149 |
452342 |
NO2 |
YES |
3.4 |
2.3 |
Y |
~2.75 |
79 |
Gillygate Monitoring Station - triplicate |
Roadside |
460149 |
452342 |
NO2 |
YES |
3.4 |
2.3 |
Y |
~2.75 |
80 |
Gillygate Monitoring Station - triplicate |
Roadside |
460149 |
452342 |
NO2 |
YES |
3.4 |
2.3 |
Y |
~2.75 |
83 |
Drainpipe 6 Stockton Lane - nr Heworth Rd roundabout |
Urban Background |
461597 |
452830 |
NO2 |
NO |
0.1 |
8.8 |
N |
~2.75 |
88 |
Lamp post 1 Yew Tree Mews Osbaldwick Village |
Urban Background |
463354 |
451972 |
NO2 |
NO |
4.9 |
0.6 |
N |
~2.75 |
90 |
Lamp post Opposite Montaque Street on Cambleshon Road |
Roadside |
459997 |
450109 |
NO2 |
NO |
19.8 |
1 |
N |
~2.75 |
96 |
Heslington Lane |
Roadside |
460978 |
449452 |
NO2 |
NO |
1.5 |
2.5 |
N |
~2.75 |
100 |
House Near A59 Ringroad Roundabout |
Roadside |
456228 |
453312 |
NO2 |
NO |
0.2 |
15 |
N |
~2.75 |
101 |
Wiggington Road near the ring road roundabout |
Roadside |
459746 |
455897 |
NO2 |
NO |
15 |
0.5 |
N |
~2.75 |
102 |
Signpost between houses 252 & 254 on Salisbury Terrace - triplicate |
Roadside |
458703 |
452429 |
NO2 |
NO |
0.2 |
1 |
N |
~2.75 |
103 |
Signpost between houses 252 & 254 on Salisbury Terrace - triplicate |
Roadside |
458703 |
452429 |
NO2 |
NO |
0.1 |
1.4 |
N |
~2.75 |
104 |
Signpost between houses 252 & 254 on Salisbury Terrace - triplicate |
Roadside |
458703 |
452429 |
NO2 |
NO |
0.1 |
1.4 |
N |
~2.75 |
107 |
Inbetween corner shop & betting office |
Roadside |
458779 |
452387 |
NO2 |
NO |
3 |
3.8 |
N |
~2.75 |
108 |
On signpost opposite side of road from 200 Salisbury Terrace |
Roadside |
458814 |
452373 |
NO2 |
NO |
0.2 |
1.5 |
N |
~2.75 |
109 |
Signpost outside 16 Rougier Street |
Roadside |
459924 |
451833 |
NO2 |
YES |
0.2 |
2.5 |
N |
~2.75 |
110 |
Signpost inbetween Club Salvation & 31 George Hudson Street |
Roadside |
459985 |
451727 |
NO2 |
YES |
0.2 |
2.3 |
N |
~2.75 |
111 |
Lamp post at side of Cedar Court opposite entrance to Multi-storey Car Park on Tanner Row |
Roadside |
459917 |
451728 |
NO2 |
NO |
26 |
2.6 |
N |
~2.75 |
112 |
Lamp post outside St Gregorys Mews, opposite Council HQ Toft Green |
Roadside |
459873 |
451684 |
NO2 |
NO |
1 |
2.3 |
N |
~2.75 |
114 |
Bus Stop outside Society bar/cafe Rougier Street |
Roadside |
459981 |
451778 |
NO2 |
YES |
3.5 |
2.7 |
N |
~2.75 |
116 |
111 Poppleton Road, drainpipe |
Roadside |
458212 |
452037 |
NO2 |
NO |
0.1 |
5.3 |
N |
~2.75 |
125 |
Osbaldwick Derwenthorpe |
Roadside |
463194 |
451967 |
NO2 |
NO |
20 |
1.6 |
N |
~2.75 |
126 |
New Tube (Osbalwick Parish Council) nr Bridge |
Roadside |
463482 |
451896 |
NO2 |
NO |
17.5 |
0.9 |
N |
~2.75 |
127 |
Lamp post to left of 102 Layerthorpe (flats) |
Roadside |
461108 |
452313 |
NO2 |
NO |
3.3 |
1.8 |
N |
~2.75 |
128 |
Drainpipe between 7-9 Livingstone Street |
Roadside |
458686 |
452369 |
NO2 |
NO |
0.1 |
1.6 |
N |
~2.75 |
129 |
Drainpipe to front of 88 Station Road |
Roadside |
455968 |
453397 |
NO2 |
NO |
0.1 |
14.5 |
N |
~2.75 |
2a |
Fishergate Monitoring station - triplicate |
Roadside |
460746 |
451034 |
NO2 |
YES |
16.3 |
3.5 |
Y |
~2.75 |
2b |
Fishergate Monitoring station - triplicate |
Roadside |
460746 |
451034 |
NO2 |
YES |
16.3 |
3.5 |
Y |
~2.75 |
2c |
Fishergate Monitoring station - triplicate |
Roadside |
460746 |
451034 |
NO2 |
YES |
16.3 |
3.5 |
Y |
~2.75 |
3a |
Bootham Monitoring Station - triplicate |
Urban Background |
460024 |
452767 |
NO2 |
NO |
39 |
49.6 |
Y |
~2.75 |
3b |
Bootham Monitoring Station - triplicate |
Urban Background |
460024 |
452767 |
NO2 |
NO |
39 |
49.6 |
Y |
~2.75 |
3c |
Bootham Monitoring Station - triplicate |
Urban Background |
460024 |
452767 |
NO2 |
NO |
39 |
49.6 |
Y |
~2.75 |
95a |
Fulford Monitoring Station - triplicate |
Roadside |
460938 |
449465 |
NO2 |
NO |
19 |
6.5 |
Y |
~2.75 |
95b |
Fulford Monitoring Station - triplicate |
Roadside |
460938 |
449465 |
NO2 |
NO |
19 |
6.5 |
Y |
~2.75 |
95c |
Fulford Monitoring Station - triplicate |
Roadside |
460938 |
449465 |
NO2 |
NO |
19 |
6.5 |
Y |
~2.75 |
9a |
Portland Street - triplicate |
Urban Background |
460163 |
452468 |
NO2 |
NO |
3.7 |
1.8 |
N |
~2.75 |
A1 |
Bootham traffic light outside dance shop |
Roadside |
460088 |
452263 |
NO2 |
YES |
0.2 |
2.3 |
N |
~2.75 |
A11 |
Traffic lights end of Water Lane |
Roadside |
459341 |
453042 |
NO2 |
YES |
13.6 |
0.4 |
N |
~2.75 |
A12 |
Lamp post 7 Clifton Green |
Roadside |
459251 |
453008 |
NO2 |
YES |
12.9 |
2.2 |
N |
~2.75 |
A13 |
Lamp post 1 Clifton Dale - triplicate |
Urban Background |
459335 |
452931 |
NO2 |
NO |
2.7 |
1.6 |
N |
~2.75 |
A14 |
Lamp post 1 Clifton Dale - triplicate |
Urban Background |
459335 |
452931 |
NO2 |
NO |
2.7 |
1.6 |
N |
~2.75 |
A14a |
Lamp post 1 Clifton Dale - triplicate |
Urban Background |
459335 |
452931 |
NO2 |
NO |
2.7 |
1.6 |
N |
~2.75 |
A17 |
Sailsbury Road |
Roadside |
458578 |
452472 |
NO2 |
NO |
8.7 |
1.5 |
N |
~2.75 |
A19 |
17 Sailsbury Terrace - triplicate |
Roadside |
458713 |
452414 |
NO2 |
NO |
0.2 |
1.3 |
N |
~2.75 |
A19a |
17 Sailsbury Terrace - triplicate |
Roadside |
458713 |
452414 |
NO2 |
NO |
0.2 |
1.3 |
N |
~2.75 |
A19b |
17 Sailsbury Terrace - triplicate |
Roadside |
458713 |
452414 |
NO2 |
NO |
0.2 |
1.3 |
N |
~2.75 |
A2 |
Drainpipe on front of registry office |
Roadside |
459917 |
452405 |
NO2 |
YES |
0.2 |
3.4 |
N |
~2.75 |
A20 |
224 Sailsbury Terrace - triplicate |
Roadside |
458760 |
452404 |
NO2 |
NO |
0.2 |
1.1 |
N |
~2.75 |
A20a |
224 Sailsbury Terrace - triplicate |
Roadside |
458760 |
452404 |
NO2 |
NO |
0.2 |
1.1 |
N |
~2.75 |
A20b |
224 Sailsbury Terrace - triplicate |
Roadside |
458760 |
452404 |
NO2 |
NO |
0.2 |
1.1 |
N |
~2.75 |
A21 |
Kingsland Terrace |
Urban Background |
458806 |
452326 |
NO2 |
NO |
0.2 |
1.4 |
N |
~2.75 |
A22 |
Kingsland Terrace |
Urban Background |
458792 |
452242 |
NO2 |
NO |
0.2 |
23.8 |
N |
~2.75 |
A25 |
Garfield Terrace |
Roadside |
458706 |
452225 |
NO2 |
NO |
0.2 |
1.5 |
N |
~2.75 |
A29 |
Low Poppleton Lane |
Urban Background |
456939 |
453013 |
NO2 |
NO |
23.6 |
1.1 |
N |
~2.75 |
A3 |
WRVS building -Bootham |
Roadside |
459822 |
452492 |
NO2 |
YES |
0.2 |
2.6 |
N |
~2.75 |
A30 |
Boroughbridge Road |
Urban Background |
457060 |
452888 |
NO2 |
NO |
8.3 |
6.2 |
N |
~2.75 |
A36 |
Boroughbridge Road |
Urban Background |
457625 |
452446 |
NO2 |
NO |
0.2 |
9.4 |
N |
~2.75 |
A38 |
Boroughbridge Road |
Urban Background |
457857 |
452334 |
NO2 |
NO |
0.2 |
10.3 |
N |
~2.75 |
A4 |
St Olaves Road |
Urban Background |
459699 |
452638 |
NO2 |
YES |
5.8 |
0.7 |
N |
~2.75 |
A40 |
Poppleton Road School |
Urban Background |
458109 |
452196 |
NO2 |
NO |
0.2 |
7.9 |
N |
~2.75 |
A41 |
140 Poppleton Road |
Roadside |
458172 |
452108 |
NO2 |
NO |
0.2 |
5.3 |
N |
~2.75 |
A45 |
Grantham Drive |
Urban Background |
458384 |
451817 |
NO2 |
NO |
0.2 |
10.5 |
N |
~2.75 |
A98 |
8 Poppleton Road |
Roadside |
458666 |
451468 |
NO2 |
NO |
0.2 |
4.9 |
N |
~2.75 |
A50 |
Outside Fox pub -Holgate Rd |
Roadside |
458732 |
451393 |
NO2 |
YES |
16.1 |
0.3 |
N |
~2.75 |
A51 |
Thrall entrance |
Urban Background |
458827 |
451348 |
NO2 |
YES |
18 |
2.2 |
N |
~2.75 |
A52 |
Holgate Road (corner of Hamilton Dr East) |
Roadside |
458945 |
451254 |
NO2 |
YES |
10.9 |
2 |
N |
~2.75 |
A53 |
Holgate Road |
Roadside |
459066 |
451239 |
NO2 |
YES |
7.9 |
2.7 |
N |
~2.75 |
A54 |
Dalton Terrace |
Roadside |
459254 |
451223 |
NO2 |
YES |
17.1 |
3.3 |
N |
~2.75 |
A55 |
Holgate Road |
Roadside |
459351 |
451221 |
NO2 |
YES |
5.5 |
0.2 |
N |
~2.75 |
A56 |
Holgate Road |
Urban Background |
459470 |
451268 |
NO2 |
YES |
0.2 |
10.2 |
N |
~2.75 |
A57 |
Hairdressers Holgate Road |
Roadside |
459533 |
451280 |
NO2 |
YES |
0.2 |
2.8 |
N |
~2.75 |
A6 |
Clifton Bingo Hall |
Roadside |
459536 |
452811 |
NO2 |
YES |
6.2 |
3 |
N |
~2.75 |
A60 |
Shipton Road |
Urban Background |
458906 |
453276 |
NO2 |
NO |
0.2 |
21.5 |
N |
~2.75 |
A62 |
42 Shipton Road |
Urban Background |
458806 |
453483 |
NO2 |
NO |
0.2 |
15.7 |
N |
~2.75 |
A64 |
Lamp post outside Charlie Browns |
Roadside |
460030 |
452327 |
NO2 |
YES |
2.4 |
0.6 |
N |
~2.75 |
A66 |
70 Shipton Road |
Urban Background |
458672 |
453685 |
NO2 |
NO |
0.2 |
18.4 |
N |
~2.75 |
A69 |
6 South Cottages |
Urban Background |
458375 |
453958 |
NO2 |
NO |
0.2 |
10 |
N |
~2.75 |
A7 |
51 Clifton |
Roadside |
459441 |
452892 |
NO2 |
YES |
3.3 |
2.1 |
N |
~2.75 |
A70 |
120 Shipton Road |
Urban Background |
458299 |
454070 |
NO2 |
NO |
0.2 |
13 |
N |
~2.75 |
A71 |
154 Shipton road |
Urban Background |
458121 |
454254 |
NO2 |
NO |
0.2 |
9.6 |
N |
~2.75 |
A74 |
176 Shipton Road |
Urban Background |
458041 |
454371 |
NO2 |
NO |
0.2 |
7.1 |
N |
~2.75 |
A77 |
Lamp post outside 206 Shipton Road |
Urban Background |
457929 |
454537 |
NO2 |
NO |
6.1 |
1.7 |
N |
~2.75 |
A81 |
Lamp post outside 276 Shipton Rd |
Urban Background |
457733 |
454805 |
NO2 |
NO |
0.2 |
8.4 |
N |
~2.75 |
A85 |
Drainpipe front of Greenside guest house |
Urban Background |
459364 |
453009 |
NO2 |
NO |
0.2 |
11.5 |
N |
~2.75 |
A88 |
111 Boroughbridge Road, Drainpipe nearest Garage at side of the door |
Urban Background |
457470 |
452550 |
NO2 |
NO |
0.2 |
12.9 |
N |
~2.75 |
A9 |
Lime Tree House |
Roadside |
459295 |
453067 |
NO2 |
YES |
12.6 |
1.7 |
N |
~2.75 |
A90 |
Lamp post 25 Shipton Rd |
Roadside |
459238 |
453157 |
NO2 |
YES |
8.2 |
1.9 |
N |
~2.75 |
A94 |
5 Salisbury Road |
Roadside |
458651 |
452426 |
NO2 |
NO |
0.2 |
13.7 |
N |
~2.75 |
A96 |
Ousecliffe Gardens signpost, outside 31 Water End |
Roadside |
459038 |
452850 |
NO2 |
NO |
10 |
0.6 |
N |
~2.75 |
A97 |
Lamp post next to Air Quality Monitoring Station on Plantation Drive |
Roadside |
457431 |
452616 |
NO2 |
NO |
18.7 |
2.2 |
N |
~2.75 |
B1 |
Lamp post 1 Lowther Street opposite Riverside House Flats |
Roadside |
460848 |
452582 |
NO2 |
YES |
0.2 |
1.3 |
N |
~2.75 |
B15 |
Lamp post 99 Huntington Road |
Roadside |
461294 |
455305 |
NO2 |
NO |
28 |
1.6 |
N |
~2.75 |
B19 |
Lamp post 5 outside Huntington Primary School |
Roadside |
461891 |
455876 |
NO2 |
NO |
17.2 |
1.6 |
N |
~2.75 |
B2 |
Lamp post 7 Huntington Road opposite Park Grove |
Roadside |
460924 |
452697 |
NO2 |
YES |
2.5 |
1.3 |
N |
~2.75 |
B29 |
Eastern Terrace |
Roadside |
461453 |
452750 |
NO2 |
NO |
0.3 |
1 |
N |
~2.75 |
B3 |
Lamp post 11 Huntington Road outside no 70 |
Roadside |
460952 |
452826 |
NO2 |
NO |
2.9 |
1.4 |
N |
~2.75 |
B36 |
Lamp post 60 Malton Road - triplicate |
Urban Background |
462565 |
454194 |
NO2 |
NO |
16.9 |
0.6 |
N |
~2.75 |
B37 |
Lamp post 60 Malton Road - triplicate |
Urban Background |
462565 |
454194 |
NO2 |
NO |
16.9 |
0.6 |
N |
~2.75 |
B37a |
Lamp post 60 Malton Road - triplicate |
Urban Background |
462565 |
454194 |
NO2 |
NO |
16.9 |
0.6 |
N |
~2.75 |
B38 |
482 Malton Road |
Urban Background |
463757 |
455155 |
NO2 |
NO |
0.2 |
11.7 |
N |
~2.75 |
B41 |
76 Lawrence Street |
Urban Background |
461326 |
451330 |
NO2 |
YES |
0.2 |
6.5 |
N |
~2.75 |
B42 |
83 Lawrence Street |
Urban Background |
461430 |
451348 |
NO2 |
YES |
0.2 |
7.2 |
N |
~2.75 |
B43 |
117 Lawrence Street |
Urban Background |
461557 |
451343 |
NO2 |
YES |
0.2 |
7.9 |
N |
~2.75 |
B44 |
Outside nursing home, Lawrence Street |
Roadside |
461643 |
451343 |
NO2 |
YES |
8.6 |
1.9 |
N |
~2.75 |
B45 |
Pedestrian crossing Traffic Light Melrosegate Crossroads |
Roadside |
461849 |
451284 |
NO2 |
YES |
17.3 |
0.5 |
N |
~2.75 |
B47 |
47 Hull Road |
Urban Background |
462019 |
451289 |
NO2 |
NO |
0.2 |
12.2 |
N |
~2.75 |
B48 |
61 Hull Road |
Urban Background |
462122 |
451289 |
NO2 |
NO |
0.2 |
12.8 |
N |
~2.75 |
B50 |
134 Hull Road |
Roadside |
462291 |
451269 |
NO2 |
NO |
0.2 |
3.7 |
N |
~2.75 |
B51 |
117 Hull Road |
Urban Background |
462384 |
451298 |
NO2 |
NO |
0.2 |
13.2 |
N |
~2.75 |
B56 |
Lamp post 40 Hull Road |
Roadside |
462888 |
451289 |
NO2 |
NO |
14.4 |
2.3 |
N |
~2.75 |
B58 |
231 Hull Road |
Urban Background |
462970 |
451300 |
NO2 |
NO |
0.2 |
14 |
N |
~2.75 |
B60 |
Lamp post 1 Nursery Gardens |
Urban Background |
463234 |
451339 |
NO2 |
NO |
10.7 |
1.3 |
N |
~2.75 |
B63 |
Lamp post 54 Tang Hall Lane |
Roadside |
462704 |
451300 |
NO2 |
NO |
13.2 |
0.9 |
N |
~2.75 |
B72 |
Front of York Cycleworks |
Roadside |
461122 |
451374 |
NO2 |
YES |
10 |
2.9 |
N |
~2.75 |
B74 |
Heworth Court Hotel sign outside Sutherland House on side of house on drainpipe. |
Urban Background |
461371 |
452708 |
NO2 |
NO |
5.2 |
17.8 |
N |
~2.75 |
B80 |
On drainpipe on front of Heworth Surgery. |
Urban Background |
461185 |
452663 |
NO2 |
NO |
24.5 |
13.4 |
N |
~2.75 |
B82 |
Lamp post Dalguise Grove |
Urban Background |
460974 |
452563 |
NO2 |
NO |
3.1 |
1.1 |
N |
~2.75 |
B83 |
Lamp post 24 Outside No.55 Heworth Green |
Roadside |
461285 |
452695 |
NO2 |
NO |
11.3 |
1 |
N |
~2.75 |
B84 |
Drainpipe to the left of the front door on 167 Hull Road |
Urban Background |
462654 |
451293 |
NO2 |
NO |
0.2 |
13.4 |
N |
~2.75 |
B85 |
Lamp post 7 Outside St Lawrences Working Mens Club |
Roadside |
461227 |
451368 |
NO2 |
YES |
18.8 |
5.6 |
N |
~2.75 |
B86 |
Lamp post 16 Heworth Green, next to Air Quality Station |
Roadside |
461116 |
452602 |
NO2 |
NO |
5 |
0.7 |
N |
~2.75 |
B88 |
Telegraph Pole 381 Hull Road |
Roadside |
462799 |
451291 |
NO2 |
NO |
10 |
6.8 |
N |
~2.75 |
B90 |
11 Lawrence Street |
Roadside |
461133 |
451394 |
NO2 |
YES |
0.1 |
4.4 |
N |
~2.75 |
B91 |
Lamp post 4 outside flats, opposite Rose and Crown Pub |
Roadside |
461143 |
451364 |
NO2 |
YES |
0.9 |
3.1 |
N |
~2.75 |
C12 |
Lamp post 1 Ainsty Grove |
Urban Background |
458825 |
449928 |
NO2 |
NO |
10.8 |
0.3 |
N |
~2.75 |
C17 |
248 Tadcaster Rd |
Urban Background |
459085 |
450544 |
NO2 |
NO |
0.2 |
20.6 |
N |
~2.75 |
C18 |
196 Mount Vale |
Urban Background |
459204 |
450772 |
NO2 |
YES |
0.2 |
9.2 |
N |
~2.75 |
C19 |
Trentholme Dr |
Urban Background |
459271 |
450819 |
NO2 |
YES |
7.7 |
0.4 |
N |
~2.75 |
C2 |
Lamp post 66 Tesco roundabout |
Roadside |
458333 |
448974 |
NO2 |
NO |
16.9 |
1.1 |
N |
~2.75 |
C20 |
Elmbank hotel |
Urban Background |
459280 |
450923 |
NO2 |
YES |
21.4 |
0.5 |
N |
~2.75 |
C21 |
Dalton Terrace |
Roadside |
459410 |
451040 |
NO2 |
YES |
3.8 |
3.5 |
N |
~2.75 |
C22 |
Park Street |
Urban Background |
459570 |
451195 |
NO2 |
YES |
14.4 |
1.1 |
N |
~2.75 |
C23 |
The Mount |
Roadside |
459553 |
451252 |
NO2 |
YES |
0.2 |
3 |
N |
~2.75 |
C26 |
Outside Odean |
Roadside |
459639 |
451334 |
NO2 |
YES |
12.9 |
0.8 |
N |
~2.75 |
C27 |
Windmill Pub |
Roadside |
459717 |
451433 |
NO2 |
YES |
0.2 |
3.2 |
N |
~2.75 |
C28 |
House top of Selby Rd |
Urban Background |
461201 |
448386 |
NO2 |
NO |
0.2 |
15.3 |
N |
~2.75 |
C29 |
Lamp post 34 Selby Road |
Roadside |
461196 |
448426 |
NO2 |
NO |
21.7 |
0.5 |
N |
~2.75 |
C30 |
Lamp post 2 Selby Rd |
Roadside |
461185 |
448462 |
NO2 |
NO |
13.1 |
1.2 |
N |
~2.75 |
C31 |
2 Selby Rd |
Urban Background |
461193 |
448473 |
NO2 |
NO |
0.2 |
14.1 |
N |
~2.75 |
C32 |
Fordlands Rd |
Urban Background |
461128 |
448823 |
NO2 |
NO |
5.4 |
6.8 |
N |
~2.75 |
C33 |
124 Main St |
Urban Background |
461085 |
448933 |
NO2 |
NO |
1 |
11.2 |
N |
~2.75 |
C34 |
103 Main St |
Roadside |
461085 |
449067 |
NO2 |
NO |
0.2 |
3.5 |
N |
~2.75 |
C36 |
50 Main St |
Roadside |
461052 |
449146 |
NO2 |
NO |
0.2 |
3.7 |
N |
~2.75 |
C37 |
59 Main St |
Urban Background |
461045 |
449223 |
NO2 |
NO |
0.2 |
6.7 |
N |
~2.75 |
C38 |
Lamp post 8 Main St |
Roadside |
461038 |
449225 |
NO2 |
NO |
6 |
0.4 |
N |
~2.75 |
C39 |
18 Main St |
Roadside |
460974 |
449336 |
NO2 |
NO |
0.2 |
2.4 |
N |
~2.75 |
C4 |
147 Tadcaster Rd |
Urban Background |
458470 |
449126 |
NO2 |
NO |
0.2 |
14.3 |
N |
~2.75 |
C40 |
Adams House B&B |
Urban Background |
460910 |
449628 |
NO2 |
NO |
0.2 |
8.7 |
N |
~2.75 |
C42 |
300 Fulford Rd |
Urban Background |
460857 |
449748 |
NO2 |
NO |
0.2 |
10 |
N |
~2.75 |
C43 |
Lamp post 39 Fulford Rd - triplicate |
Roadside |
460869 |
449730 |
NO2 |
NO |
8.7 |
0.3 |
N |
~2.75 |
C43a |
Lamp post 39 Fulford Rd - triplicate |
Roadside |
460869 |
449730 |
NO2 |
NO |
8.7 |
0.3 |
N |
~2.75 |
C44 |
Lamp post 39 Fulford Rd - triplicate |
Roadside |
460869 |
449730 |
NO2 |
NO |
8.7 |
0.3 |
N |
~2.75 |
C49 |
Alma terrace |
Urban Background |
460860 |
450530 |
NO2 |
YES |
6 |
0.9 |
N |
~2.75 |
C51 |
Conservative Club |
Roadside |
460871 |
450727 |
NO2 |
YES |
9.8 |
1 |
N |
~2.75 |
C52 |
Howard St |
Roadside |
460853 |
450781 |
NO2 |
YES |
9.9 |
1.4 |
N |
~2.75 |
C53 |
Winterscale St |
Roadside |
460766 |
450924 |
NO2 |
YES |
14.7 |
2.1 |
N |
~2.75 |
C54 |
Escrick St |
Roadside |
460762 |
451069 |
NO2 |
YES |
1.7 |
3.2 |
N |
~2.75 |
C56 |
Pedestrian crossing on junction of Scarcroft Road/The Mount |
Roadside |
459484 |
451141 |
NO2 |
YES |
25.1 |
1.3 |
N |
~2.75 |
C57 |
Lamp post 1 Nelson's Lane |
Urban Background |
458912 |
450111 |
NO2 |
NO |
5.9 |
1.3 |
N |
~2.75 |
C58 |
Drainpipe of 4 Main Street Fulford |
Roadside |
460926 |
449429 |
NO2 |
NO |
0.2 |
3.6 |
N |
~2.75 |
C59 |
Drainpipe of 34 Tadcaster Road |
Roadside |
458735 |
449713 |
NO2 |
NO |
0.2 |
3.6 |
N |
~2.75 |
C62 |
East Mount Road |
Roadside |
459579 |
451251 |
NO2 |
YES |
0.1 |
1 |
N |
~2.75 |
C63 |
1 St Edwards Close |
Roadside |
458790 |
449740 |
NO2 |
NO |
0.1 |
15.6 |
N |
~2.75 |
C7 |
Slingsby Grove |
Roadside |
458611 |
449477 |
NO2 |
NO |
1.4 |
2.6 |
N |
~2.75 |
D10 |
Daisy Taylors Card Shop, Kings Square |
Urban Background |
460443 |
451927 |
NO2 |
NO |
0.2 |
0.9 |
N |
~2.75 |
D12 |
On signpost outside 26 Fossgate |
Roadside |
460567 |
451740 |
NO2 |
YES |
0.2 |
1.6 |
N |
~2.75 |
D13 |
Lamp post 4 Skeldergate, opposite City Mills |
Roadside |
460271 |
451358 |
NO2 |
YES |
1.6 |
1.6 |
N |
~2.75 |
D14 |
Lamp post 3 Barbican Road outside No.7 |
Roadside |
461077 |
451354 |
NO2 |
YES |
1.9 |
0.2 |
N |
~2.75 |
D16 |
Lamp post 1 , Paragon St |
Roadside |
460708 |
451231 |
NO2 |
YES |
0.2 |
3 |
N |
~2.75 |
D17 |
Piccadilly/ Merchantgate junction |
Roadside |
460575 |
451616 |
NO2 |
YES |
19.3 |
0.3 |
N |
~2.75 |
D18 |
Lamp post 6 Clifford St opposite Peckitt Street |
Roadside |
460395 |
451502 |
NO2 |
YES |
0.4 |
1.8 |
N |
~2.75 |
D19 |
Bridge St/ Micklegate Junction |
Roadside |
460038 |
451626 |
NO2 |
YES |
1.7 |
0.2 |
N |
~2.75 |
D20 |
Low Ousegate / Clifford St junction, outside Waterstones |
Roadside |
460323 |
451685 |
NO2 |
YES |
13 |
0.5 |
N |
~2.75 |
D22 |
Outside Museum Gardens |
Roadside |
460035 |
452010 |
NO2 |
YES |
7.9 |
2.1 |
N |
~2.75 |
D24 |
Priory St sign Micklegate |
Roadside |
459805 |
451543 |
NO2 |
NO |
3.4 |
0.5 |
N |
~2.75 |
D25 |
Bus Stop E outside Royal York Hotel |
Roadside |
459693 |
451750 |
NO2 |
YES |
169.3 |
0.4 |
N |
~2.75 |
D26 |
Lamp post 14 Piccadilly (near Travellodge) |
Roadside |
460671 |
451400 |
NO2 |
YES |
15.5 |
2.1 |
N |
~2.75 |
D27 |
Lamp post 2 St Deny's Road - outside hotel |
Roadside |
460734 |
451563 |
NO2 |
NO |
11.7 |
1.5 |
N |
~2.75 |
D28 |
Lamp post 4 outside The Garden of India restaurant on Fawcett Street |
Roadside |
460764 |
451185 |
NO2 |
YES |
23.6 |
2.4 |
N |
~2.75 |
D30 |
Lamp post outside Barbican Centre |
Roadside |
460834 |
451252 |
NO2 |
YES |
35.5 |
0.1 |
N |
~2.75 |
D31 |
Lamp post 9 Barbican road outside No.24 |
Roadside |
461002 |
451229 |
NO2 |
YES |
2 |
0.3 |
N |
~2.75 |
D32 |
Lamp post 3 Bishopgate Street -next to bench |
Roadside |
460258 |
451208 |
NO2 |
YES |
22.2 |
1.9 |
N |
~2.75 |
D33 |
Lamp post 17 Nunnery Lane outside 81 |
Roadside |
460075 |
451174 |
NO2 |
YES |
3.9 |
0.2 |
N |
~2.75 |
D35 |
Drainpipe of house 22, Prices Lane |
Roadside |
460134 |
451170 |
NO2 |
YES |
0.2 |
1.6 |
N |
~2.75 |
D36 |
Lamp post 7 Bishopthorpe Road, opposite entrance to Charlton St |
Roadside |
460135 |
450884 |
NO2 |
YES |
6.1 |
0.2 |
N |
~2.75 |
D37 |
Lamp post 3, Bishopthorpe Road, outside house 26 |
Roadside |
460157 |
450988 |
NO2 |
YES |
2 |
2 |
N |
~2.75 |
D38 |
Lamp post 2 Scarcroft Rd |
Roadside |
460088 |
450929 |
NO2 |
YES |
2.7 |
1.6 |
N |
~2.75 |
D39 |
Lamp post 1 Bishopthorpe Road |
Roadside |
460185 |
451055 |
NO2 |
YES |
1.5 |
0.5 |
N |
~2.75 |
D4 |
Lamp post 11 Lord Mayor's Walk - opposite bike shop |
Roadside |
460560 |
452300 |
NO2 |
YES |
25.1 |
2.3 |
N |
~2.75 |
D40 |
Lamp post 16 Nunnery Lane |
Roadside |
460069 |
451196 |
NO2 |
YES |
3.3 |
1.6 |
N |
~2.75 |
D41 |
Drainpipe of 55 Lord Mayor's Walk |
Roadside |
460286 |
452487 |
NO2 |
YES |
0.2 |
3.8 |
N |
~2.75 |
D43 |
Rougier Street Signpost 1, has "Except for Access" sign on it. |
Roadside |
459920 |
451834 |
NO2 |
YES |
3 |
0.3 |
N |
~2.75 |
D45 |
Lamp post 6 The Stonebow Opposite Windsors World of Shoes |
Roadside |
460673 |
451869 |
NO2 |
YES |
15.6 |
1 |
N |
~2.75 |
D47 |
Lamp post 8 Jewbury |
Roadside |
460682 |
452187 |
NO2 |
YES |
0.6 |
2.4 |
N |
~2.75 |
D48 |
Outside De Grey House right hand side of side entrance gate post |
Roadside |
460103 |
452180 |
NO2 |
YES |
33.6 |
2.3 |
N |
~2.75 |
D49 |
Lamp post 1 Fishergate |
Roadside |
460656 |
451269 |
NO2 |
YES |
0.2 |
2.8 |
N |
~2.75 |
D50 |
Drainpipe side of Cardshop Coppergate |
Roadside |
460371 |
451682 |
NO2 |
YES |
0.2 |
1.9 |
N |
~2.75 |
D51 |
Inside Taxi Rank @ York Railway Station |
Roadside |
459640 |
451722 |
NO2 |
NO |
N |
40 |
N |
~2.75 |
D52 |
Lamp post 3 Kent Street at side of car park |
Roadside |
460887 |
451140 |
NO2 |
NO |
2 |
2 |
N |
~2.75 |
D53 |
58 Nunnery Lane |
Roadside |
460115 |
451146 |
NO2 |
YES |
0.1 |
3.6 |
N |
~2.75 |
D54 |
76 Nunnery Lane |
Roadside |
460146 |
451116 |
NO2 |
YES |
0.1 |
5.5 |
N |
~2.75 |
D55 |
Museum Street - Opposite Thomas's Pub |
Roadside |
460087 |
452065 |
NO2 |
YES |
1.8 |
2.2 |
N |
~2.75 |
D6 |
Margaret Phillipson Court, Aldwalk |
Urban Background |
460570 |
452177 |
NO2 |
NO |
0.2 |
2.6 |
N |
~2.75 |
D8 |
Lamp post 2, The Stonebow - Jorvick café |
Roadside |
460553 |
451843 |
NO2 |
NO |
27.3 |
0.5 |
N |
~2.75 |
D9 |
Lamp post 8, Lord Mayor's Walk outside no 34 |
Roadside |
460483 |
452357 |
NO2 |
YES |
1.8 |
0.1 |
N |
~2.75 |
D56 |
Three Tuns Pub, 12 Coppergate |
Roadside |
460400 |
451685 |
NO2 |
YES |
0.1 |
1.6 |
N |
~2.75 |
D57 |
Lamp post 4, Pedestrian Crossing, Coppergate |
Roadside |
460416 |
451708 |
NO2 |
YES |
11.9 |
2.4 |
N |
~2.75 |
D58 |
Traffic lights, opposite Duttons, Coppergate |
Roadside |
460435 |
451732 |
NO2 |
YES |
8 |
0.1 |
N |
~2.75 |
D59 |
Bus Stop outside 8/9 SLP |
Roadside |
460087 |
452156 |
NO2 |
YES |
1.8 |
2.7 |
N |
~2.75 |
D60 |
No entry sign outside 'Schuh' Shoe Shop |
Roadside |
460294 |
451883 |
NO2 |
NO |
N |
1.7 |
N |
~2.75 |
130 |
Outside 81 Low Mill Close |
Roadside |
463663 |
451054 |
NO2 |
NO |
13.6 |
1.1 |
N |
~2.75 |
115 |
Inside Bus Stop (opposite side of road from tube 114) Rougier Street |
Roadside |
459962 |
451771 |
NO2 |
YES |
47 |
1.5 |
N |
~2.75 |
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.
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 2023 (%) (2) |
2019 |
2020 |
2021 |
2022 |
2023 |
Bootham |
460022 |
452777 |
Urban Background |
99.1 |
99.1 |
14.9 |
12.9 |
12.7 |
12.6 |
11.8 |
Fishergate |
460746 |
451038 |
Roadside |
98.7 |
98.7 |
26.1 |
18.8 |
19.8 |
19.2 |
17.3 |
Holgate |
459512 |
451282 |
Roadside |
95.9 |
95.9 |
25.2 |
20.7 |
23.6 |
21.1 |
21.4 |
Nunnery Lane |
460068 |
451199 |
Roadside |
87.8 |
87.8 |
22.9 |
16.7 |
19.8 |
19.1 |
17.8 |
Gillygate |
460147 |
452345 |
Roadside |
98.3 |
98.3 |
27.3 |
23.5 |
25.5 |
27.1 |
25.3 |
Lawrence Street |
461256 |
451340 |
Roadside |
99.3 |
99.3 |
26.9 |
19.5 |
21.3 |
20.0 |
18.4 |
Heworth Green |
461126 |
452602 |
Roadside |
98.4 |
98.4 |
25.6 |
19.5 |
20.3 |
20.4 |
17.7 |
Fulford Road |
460937 |
449464 |
Roadside |
96.3 |
96.3 |
22.3 |
16.6 |
17.3 |
16.8 |
17.0 |
☒ 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 2023.
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) |
2019 |
2020 |
2021 |
2022 |
2023 |
5 |
462040 |
454883 |
Roadside |
91.7 |
91.7 |
16.2 |
14.3 |
12.1 |
12.1 |
11.7 |
6 |
459777 |
451406 |
Roadside |
91.7 |
91.7 |
37.3 |
29.1 |
33.9 |
31.1 |
28.3 |
7 |
460217 |
452421 |
Roadside |
91.7 |
91.7 |
45.4 |
38.2 |
46.2 |
49.5 |
41.7 |
8 |
460163 |
452468 |
Urban Background |
91.7 |
91.7 |
18.1 |
12.5 |
12.7 |
13.4 |
13.6 |
9 |
460163 |
452468 |
Urban Background |
91.7 |
91.7 |
17.6 |
12.3 |
12.6 |
13.6 |
13.2 |
11 |
458846 |
450946 |
Urban Background |
91.7 |
91.7 |
17.9 |
12.5 |
13.2 |
13.6 |
12.6 |
13 |
460176 |
452377 |
Roadside |
91.7 |
91.7 |
40.7 |
38.0 |
46.5 |
45.5 |
39.8 |
14 |
460167 |
452347 |
Roadside |
66.7 |
66.7 |
44.3 |
40.2 |
47.5 |
47.3 |
39.9 (estimate) |
15 |
461105 |
451458 |
Roadside |
83.3 |
83.3 |
34.7 |
28.7 |
30.7 |
29.5 |
27.8 |
16 |
460160 |
451152 |
Roadside |
91.7 |
91.7 |
35.9 |
26.2 |
30.4 |
29.1 |
24.1 |
17 |
459646 |
451500 |
Roadside |
91.7 |
91.7 |
31.4 |
25.0 |
26.0 |
27.4 |
22.5 |
18 |
460457 |
452903 |
Roadside |
83.3 |
83.3 |
29.9 |
24.0 |
30.3 |
29.7 |
25.4 |
25 |
461721 |
452709 |
Roadside |
91.7 |
91.7 |
22.4 |
17.1 |
18.8 |
18.0 |
17.6 |
26 |
460829 |
453524 |
Roadside |
83.3 |
83.3 |
26.7 |
21.0 |
26.4 |
25.8 |
24.0 |
33 |
460598 |
453227 |
Roadside |
91.7 |
91.7 |
23.5 |
20.0 |
22.5 |
21.8 |
19.4 |
35 |
457603 |
451492 |
Roadside |
91.7 |
91.7 |
23.5 |
18.4 |
19.7 |
18.8 |
17.6 |
37 |
459522 |
451187 |
Roadside |
91.7 |
91.7 |
29.6 |
22.6 |
23.2 |
23.1 |
21.0 |
44 |
460679 |
452326 |
Roadside |
91.7 |
91.7 |
22.3 |
18.4 |
18.9 |
17.8 |
16.2 |
45 |
460319 |
452754 |
Roadside |
91.7 |
91.7 |
31.4 |
25.7 |
28.9 |
29.5 |
25.1 |
47 |
462009 |
456996 |
Roadside |
91.7 |
91.7 |
26.8 |
21.0 |
22.1 |
22.6 |
21.8 |
60 |
461017 |
451781 |
Roadside |
91.7 |
91.7 |
22.9 |
17.2 |
17.2 |
15.0 |
15.3 |
78 |
460149 |
452342 |
Roadside |
83.3 |
83.3 |
28.6 |
23.9 |
27.2 |
27.1 |
23.1 |
79 |
460149 |
452342 |
Roadside |
75.0 |
75.0 |
29.4 |
24.3 |
26.2 |
26.7 |
24.4 |
80 |
460149 |
452342 |
Roadside |
75.0 |
75.0 |
29.8 |
24.8 |
29.4 |
26.5 |
23.7 |
83 |
461597 |
452830 |
Urban Background |
83.3 |
83.3 |
19.9 |
13.8 |
14.9 |
14.6 |
13.8 |
88 |
463354 |
451972 |
Urban Background |
91.7 |
91.7 |
13.8 (estimate) |
9.9 |
9.3 |
10.4 |
9.2 |
90 |
459997 |
450109 |
Roadside |
91.7 |
91.7 |
15.7 |
10.9 |
11.0 |
11.4 |
10.1 |
96 |
460978 |
449452 |
Roadside |
91.7 |
91.7 |
20.9 |
14.4 |
15.2 |
14.8 |
14.2 |
100 |
456228 |
453312 |
Roadside |
91.7 |
91.7 |
18.3 |
13.2 |
14.3 |
14.1 |
11.2 |
101 |
459746 |
455897 |
Roadside |
91.7 |
91.7 |
31.2 |
23.0 |
24.5 |
22.5 |
22.3 |
102 |
458703 |
452429 |
Roadside |
91.7 |
91.7 |
30.8 |
23.7 |
28.8 |
25.4 |
25.9 |
103 |
458703 |
452429 |
Roadside |
91.7 |
91.7 |
30.5 |
21.7 |
29.1 |
28.5 |
26.3 |
104 |
458703 |
452429 |
Roadside |
91.7 |
91.7 |
31.4 |
24.4 |
29.2 |
28.4 |
27.0 |
107 |
458779 |
452387 |
Roadside |
91.7 |
91.7 |
18.7 |
14.0 |
15.9 |
15.5 |
14.1 |
108 |
458814 |
452373 |
Roadside |
75.0 |
75.0 |
22.3 |
18.8 |
20.1 |
20.6 |
19.3 |
109 |
459924 |
451833 |
Roadside |
91.7 |
91.7 |
46.7 |
38.8 |
39.3 |
43.7 |
36.6 |
110 |
459985 |
451727 |
Roadside |
75.0 |
75.0 |
45.3 |
34.4 |
39.3 |
37.2 |
31.6 |
111 |
459917 |
451728 |
Roadside |
66.7 |
66.7 |
28.0 |
19.8 |
20.6 |
17.8 |
19.6 (estimate) |
112 |
459873 |
451684 |
Roadside |
91.7 |
91.7 |
23.3 |
17.7 |
17.3 |
17.0 |
16.3 |
114 |
459981 |
451778 |
Roadside |
91.7 |
91.7 |
38.5 |
29.0 |
33.8 |
34.4 |
30.0 |
116 |
458212 |
452037 |
Roadside |
75.0 |
75.0 |
25.9 |
19.4 |
22.5 |
21.6 |
20.6 |
125 |
463194 |
451967 |
Roadside |
83.3 |
83.3 |
14.2 |
12.0 |
10.6 |
11.5 |
11.3 |
126 |
463482 |
451896 |
Roadside |
75.0 |
75.0 |
16.0 |
13.9 |
13.9 |
13.0 |
11.9 |
127 |
461108 |
452313 |
Roadside |
91.7 |
91.7 |
19.5 |
17.6 |
18.3 |
20.1 |
16.9 |
128 |
458686 |
452369 |
Roadside |
91.7 |
91.7 |
19.1 |
13.5 |
14.9 |
15.1 |
13.8 |
129 |
455968 |
453397 |
Roadside |
83.3 |
83.3 |
16.7 |
11.2 |
12.7 |
12.4 |
11.2 |
2a |
460746 |
451034 |
Roadside |
91.7 |
91.7 |
24.1 |
17.6 |
18.7 |
17.9 |
16.4 |
2b |
460746 |
451034 |
Roadside |
91.7 |
91.7 |
24.8 |
18.1 |
18.4 |
18.1 |
16.9 |
2c |
460746 |
451034 |
Roadside |
83.3 |
83.3 |
23.4 |
18.0 |
18.8 |
18.4 |
17.8 |
3a |
460024 |
452767 |
Urban Background |
91.7 |
91.7 |
16.4 |
12.3 |
12.0 |
12.0 |
11.8 |
3b |
460024 |
452767 |
Urban Background |
91.7 |
91.7 |
16.8 |
11.6 |
12.5 |
11.7 |
10.8 |
3c |
460024 |
452767 |
Urban Background |
91.7 |
91.7 |
16.8 |
11.9 |
13.8 |
12.5 |
11.7 |
95a |
460938 |
449465 |
Roadside |
83.3 |
83.3 |
21.9 |
16.8 |
16.9 |
16.4 |
15.9 |
95b |
460938 |
449465 |
Roadside |
75.0 |
75.0 |
22.4 |
16.6 |
16.3 |
17.3 |
16.8 |
95c |
460938 |
449465 |
Roadside |
75.0 |
75.0 |
22.7 |
16.5 |
16.5 |
16.6 |
17.1 |
9a |
460163 |
452468 |
Urban Background |
91.7 |
91.7 |
18.3 |
12.4 |
12.6 |
13.3 |
13.3 |
A1 |
460088 |
452263 |
Roadside |
91.7 |
91.7 |
43.0 |
36.4 |
43.6 |
44.1 |
42.6 |
A11 |
459341 |
453042 |
Roadside |
91.7 |
91.7 |
29.8 |
23.6 |
25.8 |
24.8 |
25.6 |
A12 |
459251 |
453008 |
Roadside |
91.7 |
91.7 |
27.7 |
20.1 |
22.4 |
22.6 |
22.3 |
A13 |
459335 |
452931 |
Urban Background |
91.7 |
91.7 |
17.3 |
12.9 |
13.8 |
13.0 |
12.4 |
A14 |
459335 |
452931 |
Urban Background |
91.7 |
91.7 |
17.7 |
13.0 |
13.6 |
12.4 |
13.3 |
A14a |
459335 |
452931 |
Urban Background |
91.7 |
91.7 |
17.8 |
12.3 |
13.5 |
12.8 |
12.9 |
A17 |
458578 |
452472 |
Roadside |
91.7 |
91.7 |
27.6 |
21.5 |
24.7 |
23.0 |
22.9 |
A19 |
458713 |
452414 |
Roadside |
91.7 |
91.7 |
27.2 |
21.7 |
22.7 |
23.6 |
22.5 |
A19a |
458713 |
452414 |
Roadside |
83.3 |
83.3 |
27.4 |
20.9 |
23.3 |
23.1 |
21.9 |
A19b |
458713 |
452414 |
Roadside |
91.7 |
91.7 |
27.2 |
21.3 |
22.7 |
22.7 |
21.7 |
A2 |
459917 |
452405 |
Roadside |
91.7 |
91.7 |
30.0 |
23.8 |
25.7 |
26.1 |
23.7 |
A20 |
458760 |
452404 |
Roadside |
91.7 |
91.7 |
30.0 |
23.5 |
27.2 |
25.4 |
26.1 |
A20a |
458760 |
452404 |
Roadside |
91.7 |
91.7 |
29.4 |
22.5 |
28.6 |
25.4 |
25.8 |
A20b |
458760 |
452404 |
Roadside |
91.7 |
91.7 |
29.1 |
23.7 |
28.9 |
26.6 |
26.3 |
A21 |
458806 |
452326 |
Urban Background |
91.7 |
91.7 |
21.5 |
15.5 |
14.9 |
16.6 |
15.1 |
A22 |
458792 |
452242 |
Urban Background |
91.7 |
91.7 |
21.2 |
14.5 |
15.8 |
16.9 |
16.2 |
A25 |
458706 |
452225 |
Roadside |
91.7 |
91.7 |
20.2 |
15.0 |
18.0 |
18.2 |
17.5 |
A29 |
456939 |
453013 |
Urban Background |
91.7 |
91.7 |
19.3 |
12.9 |
15.2 |
17.0 |
15.1 |
A3 |
459822 |
452492 |
Roadside |
83.3 |
83.3 |
27.4 |
21.7 |
23.4 |
22.2 |
22.4 |
A30 |
457060 |
452888 |
Urban Background |
91.7 |
91.7 |
19.7 |
13.3 |
15.8 |
15.1 |
14.8 |
A36 |
457625 |
452446 |
Urban Background |
75.0 |
75.0 |
18.4 (estimate) |
11.4 (estimate) |
13.7 (estimate) |
14.1 (estimate) |
11.8 |
A38 |
457857 |
452334 |
Urban Background |
91.7 |
91.7 |
16.3 |
11.8 |
12.6 |
13.0 |
12.1 |
A4 |
459699 |
452638 |
Urban Background |
91.7 |
91.7 |
20.0 |
13.9 |
14.5 |
15.6 |
15.5 |
A40 |
458109 |
452196 |
Urban Background |
91.7 |
91.7 |
21.2 |
14.0 |
16.3 |
16.1 |
15.3 |
A41 |
458172 |
452108 |
Roadside |
83.3 |
83.3 |
20.7 |
15.3 |
18.1 |
16.8 |
15.6 |
A45 |
458384 |
451817 |
Urban Background |
91.7 |
91.7 |
16.3 |
10.6 |
12.0 |
12.5 |
12.2 |
A50 |
458732 |
451393 |
Roadside |
91.7 |
91.7 |
26.2 |
21.4 |
22.5 |
23.8 |
21.0 |
A51 |
458827 |
451348 |
Urban Background |
83.3 |
83.3 |
22.1 |
15.4 |
17.9 |
18.4 |
16.7 |
A52 |
458945 |
451254 |
Roadside |
91.7 |
91.7 |
30.7 |
24.6 |
27.9 |
26.6 |
25.3 |
A53 |
459066 |
451239 |
Roadside |
91.7 |
91.7 |
30.6 |
23.4 |
28.1 |
27.5 |
24.2 |
A54 |
459254 |
451223 |
Roadside |
58.3 |
58.3 |
31.4 |
25.1 |
30.9 |
27.9 |
28.5 (estimate) |
A55 |
459351 |
451221 |
Roadside |
91.7 |
91.7 |
30.1 |
24.2 |
28.0 |
26.8 |
24.6 |
A56 |
459470 |
451268 |
Urban Background |
83.3 |
83.3 |
28.1 |
19.8 |
21.7 |
22.3 |
22.0 |
A57 |
459533 |
451280 |
Roadside |
91.7 |
91.7 |
45.5 |
33.7 |
43.5 |
38.1 |
35.9 |
A6 |
459536 |
452811 |
Roadside |
91.7 |
91.7 |
23.5 |
17.9 |
18.5 |
18.9 |
17.5 |
A60 |
458906 |
453276 |
Urban Background |
91.7 |
91.7 |
14.7 |
9.7 |
10.7 |
11.2 |
10.9 |
A62 |
458806 |
453483 |
Urban Background |
91.7 |
91.7 |
15.3 |
10.1 |
11.2 |
11.9 |
11.5 |
A64 |
460030 |
452327 |
Roadside |
91.7 |
91.7 |
28.6 |
20.8 |
24.8 |
23.7 |
23.8 |
A66 |
458672 |
453685 |
Urban Background |
83.3 |
83.3 |
16.3 |
10.6 |
12.0 |
12.7 |
11.8 |
A69 |
458375 |
453958 |
Urban Background |
75.0 |
75.0 |
14.8 |
9.7 |
11.7 |
11.7 |
10.4 |
A7 |
459441 |
452892 |
Roadside |
91.7 |
91.7 |
24.3 |
18.8 |
20.8 |
19.4 |
18.7 |
A70 |
458299 |
454070 |
Urban Background |
91.7 |
91.7 |
17.5 |
11.5 |
13.6 |
13.7 |
13.2 |
A71 |
458121 |
454254 |
Urban Background |
91.7 |
91.7 |
14.7 |
10.0 |
10.5 |
10.4 |
10.6 |
A74 |
458041 |
454371 |
Urban Background |
75.0 |
75.0 |
14.4 |
9.7 |
10.8 |
11.5 |
9.8 |
A77 |
457929 |
454537 |
Urban Background |
91.7 |
91.7 |
20.1 |
13.4 |
13.9 |
15.7 |
14.6 |
A81 |
457733 |
454805 |
Urban Background |
83.3 |
83.3 |
17.9 |
12.3 |
12.0 |
12.8 |
12.5 |
A85 |
459364 |
453009 |
Urban Background |
91.7 |
91.7 |
21.4 |
14.5 |
16.1 |
17.3 |
16.1 |
A88 |
457470 |
452550 |
Urban Background |
91.7 |
91.7 |
17.9 |
11.4 |
12.9 |
13.5 |
13.0 |
A9 |
459295 |
453067 |
Roadside |
75.0 |
75.0 |
28.8 |
22.8 |
25.7 |
25.2 |
23.7 |
A90 |
459238 |
453157 |
Roadside |
91.7 |
91.7 |
32.1 |
25.6 |
32.7 |
30.3 |
31.7 |
A94 |
458651 |
452426 |
Roadside |
83.3 |
83.3 |
27.8 |
20.1 |
23.2 |
18.3 |
19.2 |
A96 |
459038 |
452850 |
Roadside |
91.7 |
91.7 |
29.9 |
21.5 |
25.7 |
25.0 |
24.1 |
A97 |
457431 |
452616 |
Roadside |
91.7 |
91.7 |
18.9 |
14.3 |
16.0 |
16.7 |
14.9 |
A98 |
458666 |
451468 |
Roadside |
91.7 |
91.7 |
22.8 |
17.0 |
19.4 |
18.5 |
16.8 |
B1 |
460848 |
452582 |
Roadside |
83.3 |
83.3 |
28.9 |
18.2 |
15.9 |
15.2 |
15.1 |
B15 |
461294 |
455305 |
Roadside |
91.7 |
91.7 |
18.5 |
15.1 |
15.5 |
15.2 |
14.4 |
B19 |
461891 |
455876 |
Roadside |
91.7 |
91.7 |
19.3 |
16.2 |
15.4 |
15.9 |
15.0 |
B2 |
460924 |
452697 |
Roadside |
83.3 |
83.3 |
24.0 |
17.9 |
19.4 |
18.7 |
17.3 |
B29 |
461453 |
452750 |
Roadside |
91.7 |
91.7 |
19.3 |
15.6 |
15.7 |
14.6 |
14.7 |
B3 |
460952 |
452826 |
Roadside |
91.7 |
91.7 |
21.5 |
15.9 |
17.7 |
16.8 |
16.0 |
B36 |
462565 |
454194 |
Urban Background |
75.0 |
75.0 |
15.4 |
10.4 |
10.9 |
9.9 |
10.8 |
B37 |
462565 |
454194 |
Urban Background |
83.3 |
83.3 |
14.5 |
9.6 |
9.8 |
10.4 |
10.4 |
B37a |
462565 |
454194 |
Urban Background |
83.3 |
83.3 |
13.9 |
10.5 |
10.2 |
10.9 |
10.1 |
B38 |
463757 |
455155 |
Urban Background |
91.7 |
91.7 |
17.2 |
11.9 |
12.5 |
12.7 |
12.0 |
B41 |
461326 |
451330 |
Urban Background |
91.7 |
91.7 |
30.1 |
20.0 |
23.7 |
23.2 |
21.8 |
B42 |
461430 |
451348 |
Urban Background |
91.7 |
91.7 |
23.3 |
15.5 |
18.4 |
17.3 |
15.7 |
B43 |
461557 |
451343 |
Urban Background |
91.7 |
91.7 |
20.0 |
14.3 |
15.9 |
15.7 |
14.4 |
B44 |
461643 |
451343 |
Roadside |
91.7 |
91.7 |
28.9 |
23.1 |
25.3 |
23.6 |
21.5 |
B45 |
461849 |
451284 |
Roadside |
91.7 |
91.7 |
26.2 |
18.7 |
22.4 |
21.1 |
18.2 |
B47 |
462019 |
451289 |
Urban Background |
83.3 |
83.3 |
15.8 |
11.2 |
11.8 |
11.7 |
10.2 |
B48 |
462122 |
451289 |
Urban Background |
91.7 |
91.7 |
19.0 |
11.8 |
14.5 |
14.5 |
13.7 |
B50 |
462291 |
451269 |
Roadside |
91.7 |
91.7 |
22.7 |
15.8 |
17.1 |
17.1 |
15.7 |
B51 |
462384 |
451298 |
Urban Background |
91.7 |
91.7 |
18.2 |
12.8 |
13.0 |
12.9 |
12.4 |
B56 |
462888 |
451289 |
Roadside |
91.7 |
91.7 |
28.6 |
20.8 |
22.7 |
21.3 |
21.1 |
B58 |
462970 |
451300 |
Urban Background |
91.7 |
91.7 |
19.0 |
12.7 |
12.6 |
13.8 |
13.0 |
B60 |
463234 |
451339 |
Urban Background |
91.7 |
91.7 |
19.0 |
12.1 |
13.7 |
13.4 |
13.6 |
B63 |
462704 |
451300 |
Roadside |
91.7 |
91.7 |
29.2 |
22.4 |
23.2 |
22.4 |
22.2 |
B72 |
461122 |
451374 |
Roadside |
75.0 |
75.0 |
38.9 |
32.5 |
33.7 |
33.8 |
30.9 |
B74 |
461371 |
452708 |
Urban Background |
83.3 |
83.3 |
18.9 |
13.7 |
13.4 |
14.1 (estimate) |
12.5 |
B80 |
461185 |
452663 |
Urban Background |
91.7 |
91.7 |
17.3 |
12.2 |
12.5 |
11.8 |
12.4 |
B82 |
460974 |
452563 |
Urban Background |
91.7 |
91.7 |
24.1 |
17.4 |
17.3 |
19.7 |
17.5 |
B83 |
461285 |
452695 |
Roadside |
91.7 |
91.7 |
24.6 |
21.1 |
20.7 |
19.1 |
20.5 |
B84 |
462654 |
451293 |
Urban Background |
91.7 |
91.7 |
22.3 |
15.1 |
16.9 |
17.1 |
16.8 |
B85 |
461227 |
451368 |
Roadside |
91.7 |
91.7 |
28.7 |
20.8 |
24.9 |
22.8 |
20.6 |
B86 |
461116 |
452602 |
Roadside |
91.7 |
91.7 |
23.0 |
18.6 |
21.1 |
17.3 |
16.8 |
B88 |
462799 |
451291 |
Roadside |
91.7 |
91.7 |
26.8 |
19.9 |
20.4 |
20.9 |
18.7 |
B90 |
461133 |
451394 |
Roadside |
91.7 |
91.7 |
36.0 |
27.5 |
28.5 |
25.1 |
24.3 |
B91 |
461142 |
451365 |
Roadside |
83.3 |
83.3 |
- |
- |
- |
28.8 |
27.7 |
C12 |
458825 |
449928 |
Urban Background |
91.7 |
91.7 |
18.6 |
12.1 |
13.1 |
13.0 |
12.3 |
C17 |
459085 |
450544 |
Urban Background |
91.7 |
91.7 |
16.2 |
11.4 |
12.1 |
12.8 |
12.0 |
C18 |
459204 |
450772 |
Urban Background |
91.7 |
91.7 |
25.3 |
17.0 |
16.8 |
16.6 |
21.6 |
C19 |
459271 |
450819 |
Urban Background |
91.7 |
91.7 |
17.5 |
11.7 |
12.8 |
12.8 |
13.2 |
C2 |
458333 |
448974 |
Roadside |
83.3 |
83.3 |
29.8 |
24.4 |
25.8 |
25.8 |
21.7 |
C20 |
459280 |
450923 |
Urban Background |
91.7 |
91.7 |
19.3 |
14.9 |
14.1 |
16.4 |
16.1 |
C21 |
459410 |
451040 |
Roadside |
91.7 |
91.7 |
24.9 |
20.6 |
18.7 |
18.4 |
18.1 |
C22 |
459570 |
451195 |
Urban Background |
91.7 |
91.7 |
21.0 |
15.2 |
15.4 |
15.4 |
14.9 |
C23 |
459553 |
451252 |
Roadside |
91.7 |
91.7 |
35.7 |
29.5 |
28.9 |
30.4 |
27.3 |
C26 |
459639 |
451334 |
Roadside |
91.7 |
91.7 |
38.3 |
31.2 |
34.1 |
31.7 |
30.6 |
C27 |
459717 |
451433 |
Roadside |
91.7 |
91.7 |
44.0 |
35.0 |
40.7 |
41.3 |
37.1 |
C28 |
461201 |
448386 |
Urban Background |
91.7 |
91.7 |
16.4 |
10.8 |
11.1 |
11.3 |
10.4 |
C29 |
461196 |
448426 |
Roadside |
91.7 |
91.7 |
26.8 |
19.6 |
20.3 |
20.6 |
20.7 |
C30 |
461185 |
448462 |
Roadside |
83.3 |
83.3 |
30.0 |
22.7 |
23.7 |
21.5 |
21.7 |
C31 |
461193 |
448473 |
Urban Background |
91.7 |
91.7 |
18.0 |
12.0 |
12.7 |
13.0 |
13.2 |
C32 |
461128 |
448823 |
Urban Background |
91.7 |
91.7 |
22.9 |
15.0 |
15.8 |
17.1 |
17.5 |
C33 |
461085 |
448933 |
Urban Background |
83.3 |
83.3 |
16.7 |
10.5 |
11.0 |
11.5 |
10.8 |
C34 |
461085 |
449067 |
Roadside |
83.3 |
83.3 |
23.5 |
16.2 |
17.3 |
17.2 |
17.3 |
C36 |
461052 |
449146 |
Roadside |
91.7 |
91.7 |
25.3 |
19.7 |
20.1 |
20.6 |
19.7 |
C37 |
461045 |
449223 |
Urban Background |
91.7 |
91.7 |
21.2 |
14.2 |
15.7 |
16.1 |
15.1 |
C38 |
461038 |
449225 |
Roadside |
91.7 |
91.7 |
25.2 |
17.1 |
18.2 |
18.1 |
18.7 |
C39 |
460974 |
449336 |
Roadside |
83.3 |
83.3 |
33.1 |
22.9 |
22.8 |
22.2 |
24.9 |
C4 |
458470 |
449126 |
Urban Background |
91.7 |
91.7 |
18.2 |
12.5 |
12.5 |
12.9 |
12.0 |
C40 |
460910 |
449628 |
Urban Background |
83.3 |
83.3 |
18.7 |
12.6 |
12.9 |
13.7 |
13.4 |
C42 |
460857 |
449748 |
Urban Background |
91.7 |
91.7 |
21.8 |
14.3 |
15.2 |
15.9 |
16.5 |
C43 |
460869 |
449730 |
Roadside |
91.7 |
91.7 |
25.1 |
18.4 |
19.3 |
19.7 |
20.0 |
C43a |
460869 |
449730 |
Roadside |
91.7 |
91.7 |
26.5 |
19.3 |
20.2 |
20.6 |
20.9 |
C44 |
460869 |
449730 |
Roadside |
91.7 |
91.7 |
27.0 |
19.6 |
19.7 |
20.6 |
20.1 |
C49 |
460860 |
450530 |
Urban Background |
91.7 |
91.7 |
20.0 |
13.0 |
14.3 |
14.2 |
13.1 |
C51 |
460871 |
450727 |
Roadside |
66.7 |
66.7 |
25.5 |
17.9 |
19.3 |
18.1 |
18.9 (estimate) |
C52 |
460853 |
450781 |
Roadside |
91.7 |
91.7 |
22.6 |
17.8 |
17.2 |
18.1 |
16.3 |
C53 |
460766 |
450924 |
Roadside |
25.0 |
25.0 |
22.0 |
15.2 (estimate) |
16.0 (estimate) |
16.5 (estimate) |
16.7 (estimate) |
C54 |
460762 |
451069 |
Roadside |
91.7 |
91.7 |
24.7 |
18.4 |
21.3 |
20.0 |
19.7 |
C56 |
459484 |
451141 |
Roadside |
83.3 |
83.3 |
30.5 |
21.8 |
25.0 |
24.8 |
22.4 |
C57 |
458912 |
450111 |
Urban Background |
91.7 |
91.7 |
20.6 |
14.4 |
14.4 |
15.3 |
14.4 |
C58 |
460926 |
449429 |
Roadside |
91.7 |
91.7 |
33.0 |
24.6 |
25.4 |
26.0 |
25.0 |
C59 |
458735 |
449713 |
Roadside |
91.7 |
91.7 |
27.1 |
22.3 |
23.3 |
25.0 |
21.7 |
C62 |
459579 |
451251 |
Roadside |
91.7 |
91.7 |
26.4 |
20.1 |
20.8 |
21.3 |
19.1 |
C63 |
458790 |
449740 |
Roadside |
91.7 |
91.7 |
18.1 |
13.3 |
13.8 |
12.0 |
12.1 |
C7 |
458611 |
449477 |
Roadside |
91.7 |
91.7 |
19.2 |
14.9 |
15.4 |
13.1 |
13.3 |
D10 |
460443 |
451927 |
Urban Background |
91.7 |
91.7 |
19.1 |
11.3 |
12.5 |
13.3 |
12.6 |
D12 |
460567 |
451740 |
Roadside |
91.7 |
91.7 |
19.4 |
15.7 |
14.3 |
14.2 |
12.9 |
D13 |
460271 |
451358 |
Roadside |
91.7 |
91.7 |
24.9 |
20.4 |
17.6 |
18.4 |
16.7 |
D14 |
461077 |
451354 |
Roadside |
83.3 |
83.3 |
36.6 |
28.2 |
30.8 |
28.0 |
28.4 |
D16 |
460708 |
451231 |
Roadside |
91.7 |
91.7 |
37.8 |
29.2 |
32.9 |
30.4 |
28.8 |
D17 |
460575 |
451616 |
Roadside |
83.3 |
83.3 |
29.6 |
23.7 |
28.5 |
30.9 |
24.7 |
D18 |
460395 |
451502 |
Roadside |
75.0 |
75.0 |
28.7 |
23.1 |
24.2 |
22.7 |
20.4 |
D19 |
460038 |
451626 |
Roadside |
91.7 |
91.7 |
45.9 |
34.8 |
40.5 |
38.2 |
32.4 |
D20 |
460323 |
451685 |
Roadside |
83.3 |
83.3 |
38.9 |
30.1 |
33.4 |
36.6 |
31.2 |
D22 |
460035 |
452010 |
Roadside |
58.3 |
58.3 |
31.5 |
27.2 |
32.3 |
30.7 |
28.9 (estimate) |
D24 |
459805 |
451543 |
Roadside |
91.7 |
91.7 |
27.5 |
18.9 |
20.5 |
19.6 |
18.0 |
D25 |
459693 |
451750 |
Roadside |
91.7 |
91.7 |
37.4 |
29.0 |
33.0 |
34.7 |
31.9 |
D26 |
460671 |
451400 |
Roadside |
91.7 |
91.7 |
25.1 |
20.2 |
25.1 |
23.6 |
20.7 |
D27 |
460734 |
451563 |
Roadside |
91.7 |
91.7 |
22.8 |
19.5 |
20.8 |
19.0 |
15.9 |
D28 |
460764 |
451185 |
Roadside |
91.7 |
91.7 |
32.4 |
25.0 |
27.4 |
26.1 |
23.5 |
D30 |
460834 |
451252 |
Roadside |
91.7 |
91.7 |
24.7 |
18.6 |
20.4 |
18.4 |
18.0 |
D31 |
461002 |
451229 |
Roadside |
91.7 |
91.7 |
28.0 |
20.6 |
24.4 |
22.9 |
22.2 |
D32 |
460258 |
451208 |
Roadside |
91.7 |
91.7 |
34.6 |
26.4 |
29.1 |
27.9 |
25.0 |
D33 |
460075 |
451174 |
Roadside |
83.3 |
83.3 |
26.3 |
20.7 |
24.4 |
24.4 |
24.4 |
D35 |
460134 |
451170 |
Roadside |
91.7 |
91.7 |
37.4 |
27.2 |
32.8 |
30.6 |
25.7 |
D36 |
460135 |
450884 |
Roadside |
91.7 |
91.7 |
31.6 |
22.8 |
25.2 |
24.9 |
22.8 |
D37 |
460157 |
450988 |
Roadside |
83.3 |
83.3 |
27.5 |
18.7 |
22.6 |
20.9 |
19.7 |
D38 |
460088 |
450929 |
Roadside |
91.7 |
91.7 |
22.1 |
16.8 |
18.2 |
16.6 |
15.8 |
D39 |
460185 |
451055 |
Roadside |
91.7 |
91.7 |
29.5 |
20.4 |
23.5 |
23.8 |
20.7 |
D4 |
460560 |
452300 |
Roadside |
91.7 |
91.7 |
25.5 |
19.2 |
22.2 |
21.1 |
19.6 |
D40 |
460069 |
451196 |
Roadside |
91.7 |
91.7 |
25.5 |
18.9 |
21.7 |
19.2 |
17.4 |
D41 |
460286 |
452487 |
Roadside |
83.3 |
83.3 |
32.8 |
27.9 |
30.8 |
31.9 |
30.8 |
D43 |
459920 |
451834 |
Roadside |
91.7 |
91.7 |
43.6 |
34.2 |
36.9 |
39.3 |
30.7 |
D45 |
460673 |
451869 |
Roadside |
91.7 |
91.7 |
23.9 |
17.7 |
18.7 |
17.9 |
16.1 |
D47 |
460682 |
452187 |
Roadside |
83.3 |
83.3 |
25.9 |
20.8 |
19.3 |
18.0 |
18.7 |
D48 |
460103 |
452180 |
Roadside |
83.3 |
83.3 |
34.3 |
28.0 |
35.1 |
35.4 (estimate) |
30.4 |
D49 |
460656 |
451269 |
Roadside |
91.7 |
91.7 |
35.0 |
24.4 |
30.0 |
29.8 |
25.7 |
D50 |
460371 |
451682 |
Roadside |
83.3 |
83.3 |
34.7 |
27.2 |
29.1 |
29.4 |
27.0 |
D51 |
459640 |
451722 |
Roadside |
91.7 |
91.7 |
55.5 |
34.4 |
35.9 |
41.4 |
40.4 |
D52 |
460887 |
451140 |
Roadside |
91.7 |
91.7 |
23.7 |
17.4 |
19.3 |
19.4 |
13.9 |
D53 |
460115 |
451146 |
Roadside |
91.7 |
91.7 |
24.3 |
19.6 |
21.9 |
19.8 |
17.8 |
D54 |
460146 |
451116 |
Roadside |
91.7 |
91.7 |
23.9 |
18.5 |
20.6 |
19.3 |
18.1 |
D55 |
460087 |
452065 |
Roadside |
91.7 |
91.7 |
38.2 |
33.5 |
44.9 |
39.2 |
37.1 |
D6 |
460570 |
452177 |
Urban Background |
91.7 |
91.7 |
19.5 |
13.5 |
16.2 |
14.8 |
13.3 |
D8 |
460553 |
451843 |
Roadside |
75.0 |
75.0 |
31.7 |
28.4 |
32.2 |
33.0 |
30.4 |
D9 |
460483 |
452357 |
Roadside |
83.3 |
83.3 |
33.6 |
25.3 |
27.7 |
31.0 |
28.4 |
D56 |
460400 |
451685 |
Roadside |
83.3 |
83.3 |
38.2 |
31.2 |
31.8 |
35.9 |
35.1 |
D57 |
460416 |
451708 |
Roadside |
83.3 |
83.3 |
29.4 |
25.0 |
26.1 |
24.9 |
22.7 |
D58 |
460435 |
451732 |
Roadside |
91.7 |
91.7 |
34.6 |
26.1 |
29.5 |
31.2 |
29.5 |
D59 |
460087 |
452156 |
Roadside |
91.7 |
91.7 |
39.7 |
35.4 |
43.2 |
44.7 |
37.5 |
D60 |
460294 |
451883 |
Roadside |
91.7 |
91.7 |
21.4 |
15.6 |
14.2 |
15.7 |
14.4 |
130 |
463663 |
451054 |
Roadside |
50.0 |
50.0 |
13.3 |
10.5 |
10.1 |
10.5 (estimate) |
9.8 (estimate) |
115 |
459962 |
451771 |
Roadside |
91.7 |
91.7 |
59.2 |
48.8 |
44.7 |
50.9 |
45.0 |
☒ 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
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 2023 (%) (2) |
2019 |
2020 |
2021 |
2022 |
2023 |
Bootham |
460022 |
452777 |
Urban Background |
99.1 |
99.1 |
0 |
0 |
0 |
0 |
0 |
Fishergate |
460746 |
451038 |
Roadside |
98.7 |
98.7 |
0 |
0 |
0 |
0 |
0 |
Holgate |
459512 |
451282 |
Roadside |
95.9 |
95.9 |
0 |
0 |
0 |
0 |
0 |
Nunnery Lane |
460068 |
451199 |
Roadside |
87.8 |
87.8 |
0 |
0 |
0 |
0 |
0 |
Gillygate |
460147 |
452345 |
Roadside |
98.3 |
98.3 |
0 |
0 |
0 |
0 |
0 |
Lawrence Street |
461256 |
451340 |
Roadside |
99.3 |
99.3 |
0 |
0 |
0 |
0 |
0 |
Heworth Green |
461126 |
452602 |
Roadside |
98.4 |
98.4 |
0 |
0 |
0 |
0 |
0 |
Fulford Road |
460937 |
449464 |
Roadside |
96.3 |
96.3 |
0 (80.3) |
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%).
Figure A.2 – Trends in Number of NO2 1-Hour Means > 200µg/m3
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 2023 (%) (2) |
2019 |
2020 |
2021 |
2022 |
2023 |
Bootham |
460022 |
452777 |
Urban Background |
96.4 |
96.4 |
14.0 |
15.2 |
13.4 |
15.2 |
11.6 |
Fishergate |
460746 |
451038 |
Roadside |
97.3 |
97.3 |
21.9 |
19.2 |
15.8 |
16.8 |
13.7 |
Holgate Road |
459512 |
451282 |
Roadside |
96.2 |
50.4 |
13.9 |
18.4 |
17.2 |
17.9 |
16.8 |
Plantation Drive |
457428 |
452620 |
Roadside |
95.6 |
95.6 |
16.4 |
15.8 |
16.0 |
16.3 |
15.4 |
☒ 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.3 – 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 2023 (%) (2) |
2019 |
2020 |
2021 |
2022 |
2023 |
Bootham |
460022 |
452777 |
Urban Background |
96.4 |
96.4 |
0 |
2 |
0 |
3 |
0 |
Fishergate |
460746 |
451038 |
Roadside |
97.3 |
97.3 |
8 |
1 |
0 |
6 |
0 |
Holgate Road |
459512 |
451282 |
Roadside |
96.2 |
50.4 |
0 |
2 |
0 |
2 |
0 (27.5) |
Plantation Drive |
457428 |
452620 |
Roadside |
95.6 |
95.6 |
4 |
1 |
0 |
0 |
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.4 – Trends in Number of 24-Hour Mean PM10 Results > 50µg/m3
Table A.8– Annual Mean PM2.5 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 2023 (%) (2) |
2019 |
2020 |
2021 |
2022 |
2023 |
Bootham |
460022 |
452777 |
Urban Background |
97.9 |
97.9 |
11.1 |
8.6 |
8.4 |
8.2 |
7.4 |
Fishergate |
460746 |
451038 |
Roadside |
93.4 |
93.4 |
10.7 |
7.6 |
7.9 |
8.8 |
8.0 |
Gillygate |
460147 |
452345 |
Roadside |
79.6 |
79.6 |
7.6 |
7.1 |
6.1 |
7.2 |
7.2 |
Holgate Road |
459512 |
451282 |
Roadside |
94.9 |
45.0 |
- |
- |
- |
- |
7.8 |
☒ 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.
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 PM2.5 Concentrations
Table B.1– NO2 2023 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 (B=0.78, R=0.77) |
Annual Mean: Distance Corrected to Nearest Exposure |
Comment |
5 |
462040 |
454883 |
18.2 |
23.5 |
17.2 |
- |
11.2 |
10.4 |
4.7 |
10.0 |
13.7 |
20.2 |
20.2 |
18.4 |
15.2 |
11.7 |
- |
|
6 |
459777 |
451406 |
46.6 |
50.4 |
39.3 |
- |
37.3 |
26.2 |
29.2 |
34.0 |
34.6 |
37.0 |
48.0 |
21.3 |
36.7 |
28.3 |
- |
|
7 |
460217 |
452421 |
59.1 |
62.2 |
67.8 |
- |
65.1 |
58.3 |
55.6 |
48.2 |
45.4 |
43.7 |
50.5 |
40.5 |
54.2 |
41.7 |
31.6 |
|
8 |
460163 |
452468 |
22.2 |
22.6 |
21.2 |
- |
13.3 |
10.6 |
17.8 |
13.1 |
17.0 |
19.2 |
20.8 |
14.0 |
17.4 |
13.6 |
- |
Part of triplicate set - see bottom of table for triplicate average |
9 |
460163 |
452468 |
20.4 |
22.2 |
20.1 |
- |
14.6 |
11.5 |
12.5 |
12.9 |
15.8 |
18.7 |
20.5 |
16.9 |
16.9 |
13.2 |
- |
Part of triplicate set - see bottom of table for triplicate average |
11 |
458846 |
450946 |
11.0 |
20.5 |
19.0 |
- |
15.5 |
13.0 |
10.5 |
12.0 |
15.9 |
20.4 |
20.9 |
18.5 |
16.1 |
12.6 |
- |
|
13 |
460176 |
452377 |
63.9 |
65.7 |
56.0 |
- |
57.0 |
44.9 |
51.8 |
49.7 |
51.9 |
46.0 |
41.9 |
39.9 |
51.7 |
39.8 |
- |
|
14 |
460167 |
452347 |
|
59.4 |
68.9 |
- |
|
|
55.8 |
49.5 |
56.2 |
43.0 |
47.0 |
45.5 |
53.2 |
39.9 |
- |
|
15 |
461105 |
451458 |
|
43.5 |
42.1 |
- |
33.3 |
31.5 |
29.4 |
31.3 |
38.5 |
37.7 |
37.8 |
36.0 |
36.1 |
27.8 |
- |
|
16 |
460160 |
451152 |
36.5 |
41.0 |
34.8 |
- |
28.3 |
24.2 |
26.6 |
31.2 |
32.8 |
18.9 |
39.2 |
30.2 |
31.2 |
24.1 |
- |
|
17 |
459646 |
451500 |
38.0 |
38.3 |
33.6 |
- |
28.4 |
20.8 |
26.8 |
26.6 |
30.2 |
17.5 |
37.3 |
24.5 |
29.3 |
22.5 |
- |
|
18 |
460457 |
452903 |
26.4 |
43.7 |
39.5 |
- |
33.5 |
29.0 |
|
30.1 |
25.0 |
33.2 |
39.0 |
29.9 |
32.9 |
25.4 |
- |
|
25 |
461721 |
452709 |
30.9 |
29.4 |
25.1 |
- |
19.4 |
16.2 |
15.9 |
16.9 |
20.4 |
27.2 |
27.4 |
23.2 |
22.9 |
17.6 |
- |
|
26 |
460829 |
453524 |
|
41.6 |
36.9 |
- |
29.5 |
23.8 |
26.8 |
25.4 |
31.2 |
29.1 |
36.3 |
31.3 |
31.2 |
24.0 |
- |
|
33 |
460598 |
453227 |
36.2 |
37.0 |
32.6 |
- |
22.7 |
16.7 |
21.7 |
19.2 |
21.6 |
21.6 |
22.2 |
26.3 |
25.3 |
19.4 |
- |
|
35 |
457603 |
451492 |
26.7 |
30.8 |
25.3 |
- |
17.3 |
16.0 |
18.7 |
18.7 |
19.2 |
23.7 |
27.1 |
27.6 |
22.8 |
17.6 |
- |
|
37 |
459522 |
451187 |
30.7 |
37.2 |
31.8 |
- |
25.3 |
27.1 |
20.5 |
23.4 |
24.3 |
29.5 |
30.8 |
19.2 |
27.3 |
21.0 |
- |
|
44 |
460679 |
452326 |
32.1 |
28.0 |
22.1 |
- |
16.8 |
12.8 |
17.4 |
18.1 |
20.1 |
23.2 |
20.0 |
20.2 |
21.0 |
16.2 |
- |
|
45 |
460319 |
452754 |
38.9 |
44.9 |
39.6 |
- |
31.3 |
28.3 |
33.5 |
29.2 |
30.9 |
25.2 |
31.4 |
25.3 |
32.6 |
25.1 |
- |
|
47 |
462009 |
456996 |
32.7 |
35.3 |
30.5 |
- |
25.6 |
23.4 |
26.2 |
24.5 |
28.1 |
25.6 |
30.6 |
28.5 |
28.3 |
21.8 |
- |
|
60 |
461017 |
451781 |
27.3 |
20.9 |
21.6 |
- |
16.2 |
12.4 |
14.3 |
16.8 |
19.6 |
20.2 |
27.5 |
21.3 |
19.8 |
15.3 |
- |
|
78 |
460149 |
452342 |
35.7 |
41.1 |
|
- |
35.0 |
29.6 |
27.2 |
25.1 |
29.5 |
23.5 |
35.1 |
18.5 |
30.0 |
23.1 |
- |
Part of triplicate set - see bottom of table for triplicate average |
79 |
460149 |
452342 |
37.3 |
40.9 |
|
- |
36.3 |
28.5 |
28.1 |
28.9 |
32.2 |
|
33.2 |
19.9 |
31.7 |
24.4 |
- |
Part of triplicate set - see bottom of table for triplicate average |
80 |
460149 |
452342 |
39.4 |
|
|
- |
34.2 |
27.5 |
31.2 |
29.2 |
31.1 |
23.8 |
30.1 |
30.6 |
30.8 |
23.7 |
- |
Part of triplicate set - see bottom of table for triplicate average |
83 |
461597 |
452830 |
26.2 |
25.9 |
17.8 |
- |
14.0 |
11.3 |
15.6 |
|
13.6 |
16.1 |
19.6 |
16.7 |
17.7 |
13.8 |
- |
|
88 |
463354 |
451972 |
20.1 |
17.4 |
12.1 |
- |
7.9 |
7.4 |
9.2 |
9.6 |
4.0 |
12.4 |
16.7 |
12.9 |
11.8 |
9.2 |
- |
|
90 |
459997 |
450109 |
19.2 |
17.1 |
14.5 |
- |
11.9 |
11.0 |
10.1 |
9.2 |
12.2 |
11.3 |
16.5 |
10.7 |
13.1 |
10.1 |
- |
|
96 |
460978 |
449452 |
25.6 |
24.3 |
19.8 |
- |
11.3 |
11.9 |
13.4 |
13.3 |
18.9 |
22.4 |
25.2 |
17.0 |
18.5 |
14.2 |
- |
|
100 |
456228 |
453312 |
13.5 |
19.6 |
17.3 |
- |
16.2 |
12.7 |
13.4 |
15.1 |
17.1 |
14.3 |
5.2 |
15.9 |
14.6 |
11.2 |
- |
|
101 |
459746 |
455897 |
31.0 |
38.1 |
30.7 |
- |
24.8 |
21.2 |
27.1 |
27.0 |
30.3 |
28.5 |
32.4 |
27.0 |
28.9 |
22.3 |
- |
|
102 |
458703 |
452429 |
38.3 |
33.7 |
38.5 |
- |
39.1 |
32.5 |
23.8 |
30.3 |
34.2 |
36.0 |
37.4 |
26.2 |
33.6 |
25.9 |
- |
Part of triplicate set - see bottom of table for triplicate average |
103 |
458703 |
452429 |
35.6 |
39.3 |
40.7 |
- |
37.3 |
31.0 |
26.9 |
33.1 |
36.1 |
23.6 |
40.9 |
31.7 |
34.2 |
26.3 |
- |
Part of triplicate set - see bottom of table for triplicate average |
104 |
458703 |
452429 |
40.3 |
40.6 |
38.7 |
- |
38.8 |
33.6 |
26.9 |
29.0 |
37.8 |
27.5 |
42.6 |
30.4 |
35.1 |
27.0 |
- |
Part of triplicate set - see bottom of table for triplicate average |
107 |
458779 |
452387 |
17.7 |
20.8 |
21.5 |
- |
14.9 |
11.2 |
12.3 |
15.6 |
17.9 |
22.0 |
26.0 |
21.9 |
18.3 |
14.1 |
- |
|
108 |
458814 |
452373 |
35.0 |
32.2 |
26.8 |
- |
20.4 |
14.7 |
|
17.9 |
22.7 |
27.5 |
|
28.7 |
25.1 |
19.3 |
- |
|
109 |
459924 |
451833 |
50.1 |
56.2 |
56.1 |
- |
49.3 |
46.1 |
43.3 |
44.2 |
46.1 |
44.8 |
44.4 |
42.9 |
47.6 |
36.6 |
- |
|
110 |
459985 |
451727 |
38.7 |
48.3 |
49.7 |
- |
38.8 |
34.7 |
42.4 |
32.2 |
40.3 |
44.6 |
|
|
41.1 |
31.6 |
- |
|
111 |
459917 |
451728 |
33.1 |
31.7 |
|
- |
24.1 |
18.6 |
17.1 |
22.5 |
19.3 |
|
31.6 |
|
24.8 |
19.6 |
- |
|
112 |
459873 |
451684 |
26.7 |
25.4 |
22.4 |
- |
16.5 |
13.7 |
16.7 |
18.6 |
18.8 |
25.7 |
25.4 |
23.3 |
21.2 |
16.3 |
- |
|
114 |
459981 |
451778 |
53.1 |
49.3 |
33.6 |
- |
44.3 |
35.6 |
34.0 |
36.1 |
33.7 |
39.0 |
36.9 |
33.1 |
39.0 |
30.0 |
- |
|
115 |
459962 |
451771 |
72.9 |
67.4 |
54.2 |
- |
53.6 |
54.3 |
67.9 |
67.6 |
70.2 |
45.9 |
46.8 |
42.7 |
58.5 |
45.0 |
- |
|
116 |
458212 |
452037 |
36.0 |
34.3 |
27.7 |
- |
|
19.7 |
|
23.2 |
21.9 |
26.9 |
29.6 |
21.8 |
26.8 |
20.6 |
- |
|
125 |
463194 |
451967 |
20.7 |
18.9 |
13.3 |
- |
12.9 |
8.2 |
|
10.4 |
12.3 |
15.1 |
20.0 |
15.1 |
14.7 |
11.3 |
- |
|
126 |
463482 |
451896 |
|
22.8 |
17.3 |
- |
13.9 |
11.0 |
11.5 |
12.9 |
14.5 |
|
16.5 |
19.0 |
15.5 |
11.9 |
- |
|
127 |
461108 |
452313 |
29.9 |
35.1 |
27.4 |
- |
17.6 |
14.8 |
19.8 |
20.5 |
6.6 |
26.6 |
24.6 |
18.9 |
22.0 |
16.9 |
- |
|
128 |
458686 |
452369 |
23.1 |
20.3 |
21.9 |
- |
14.7 |
13.0 |
13.2 |
13.5 |
16.8 |
17.4 |
23.0 |
20.8 |
18.0 |
13.8 |
- |
|
129 |
455968 |
453397 |
|
19.0 |
14.3 |
- |
11.6 |
9.3 |
11.0 |
11.2 |
18.2 |
16.3 |
18.0 |
16.8 |
14.6 |
11.2 |
- |
|
130 |
463663 |
451054 |
18.2 |
17.2 |
12.9 |
- |
|
|
7.5 |
|
|
|
16.8 |
13.4 |
14.3 |
9.8 |
- |
|
2a |
460746 |
451034 |
19.2 |
26.3 |
25.7 |
- |
19.9 |
17.7 |
15.6 |
17.2 |
21.4 |
25.6 |
30.4 |
15.7 |
21.3 |
16.4 |
- |
Part of triplicate set - see bottom of table for triplicate average |
2b |
460746 |
451034 |
27.2 |
25.1 |
24.6 |
- |
17.8 |
17.9 |
16.3 |
19.5 |
20.5 |
22.4 |
29.0 |
21.6 |
22.0 |
16.9 |
- |
Part of triplicate set - see bottom of table for triplicate average |
2c |
460746 |
451034 |
|
26.2 |
25.7 |
- |
20.5 |
19.6 |
15.8 |
23.4 |
26.3 |
22.2 |
29.2 |
22.1 |
23.1 |
17.8 |
- |
Part of triplicate set - see bottom of table for triplicate average |
3a |
460024 |
452767 |
13.6 |
21.9 |
19.3 |
- |
10.8 |
8.4 |
12.5 |
9.8 |
14.6 |
16.6 |
20.8 |
18.0 |
15.1 |
11.8 |
- |
Part of triplicate set - see bottom of table for triplicate average |
3b |
460024 |
452767 |
19.9 |
21.8 |
17.5 |
- |
10.5 |
8.6 |
11.1 |
11.1 |
14.4 |
15.1 |
6.9 |
15.5 |
13.9 |
10.8 |
- |
Part of triplicate set - see bottom of table for triplicate average |
3c |
460024 |
452767 |
21.5 |
21.6 |
17.5 |
- |
9.9 |
8.8 |
9.6 |
10.7 |
15.2 |
16.6 |
17.6 |
16.2 |
15.0 |
11.7 |
- |
Part of triplicate set - see bottom of table for triplicate average |
95a |
460938 |
449465 |
26.1 |
28.0 |
24.1 |
- |
16.8 |
16.5 |
18.5 |
18.2 |
17.1 |
23.0 |
|
18.5 |
20.7 |
15.9 |
- |
Part of triplicate set - see bottom of table for triplicate average |
95b |
460938 |
449465 |
|
27.7 |
23.4 |
- |
18.3 |
24.7 |
18.6 |
19.8 |
20.1 |
22.6 |
|
21.4 |
21.8 |
16.8 |
- |
Part of triplicate set - see bottom of table for triplicate average |
95c |
460938 |
449465 |
30.5 |
27.8 |
23.9 |
- |
19.5 |
|
17.8 |
18.3 |
19.6 |
23.8 |
|
19.1 |
22.3 |
17.1 |
- |
Part of triplicate set - see bottom of table for triplicate average |
9a |
460163 |
452468 |
24.2 |
21.4 |
20.7 |
- |
12.8 |
10.0 |
12.7 |
11.7 |
15.7 |
15.4 |
22.5 |
20.0 |
17.0 |
13.3 |
- |
Part of triplicate set - see bottom of table for triplicate average |
A1 |
460088 |
452263 |
63.4 |
67.9 |
67.0 |
- |
52.6 |
47.8 |
53.4 |
44.8 |
53.4 |
51.3 |
52.3 |
54.4 |
55.3 |
42.6 |
- |
|
A11 |
459341 |
453042 |
32.3 |
41.4 |
38.0 |
- |
32.0 |
28.7 |
28.1 |
31.3 |
29.0 |
29.6 |
40.1 |
35.0 |
33.2 |
25.6 |
- |
|
A12 |
459251 |
453008 |
35.3 |
35.1 |
34.0 |
- |
26.5 |
27.9 |
22.4 |
27.1 |
25.9 |
23.7 |
37.5 |
23.3 |
29.0 |
22.3 |
- |
|
A13 |
459335 |
452931 |
20.8 |
22.3 |
19.0 |
- |
12.5 |
10.7 |
10.5 |
12.2 |
14.1 |
14.8 |
23.9 |
13.4 |
15.8 |
12.4 |
- |
Part of triplicate set - see bottom of table for triplicate average |
A14 |
459335 |
452931 |
21.0 |
22.0 |
19.5 |
- |
13.4 |
11.0 |
10.4 |
11.8 |
13.9 |
18.6 |
20.9 |
25.1 |
17.1 |
13.3 |
- |
Part of triplicate set - see bottom of table for triplicate average |
A14a |
459335 |
452931 |
21.0 |
22.5 |
17.2 |
- |
13.7 |
11.6 |
11.1 |
12.5 |
15.4 |
18.0 |
23.8 |
15.8 |
16.6 |
12.9 |
- |
Part of triplicate set - see bottom of table for triplicate average |
A17 |
458578 |
452472 |
37.6 |
35.3 |
31.9 |
- |
26.5 |
21.6 |
21.9 |
26.2 |
27.8 |
33.1 |
33.8 |
31.1 |
29.7 |
22.9 |
- |
|
A19 |
458713 |
452414 |
37.9 |
28.2 |
31.3 |
- |
24.3 |
23.4 |
28.2 |
24.7 |
28.9 |
31.3 |
36.7 |
26.2 |
29.2 |
22.5 |
- |
Part of triplicate set - see bottom of table for triplicate average |
A19a |
458713 |
452414 |
36.0 |
35.3 |
31.1 |
- |
24.3 |
19.4 |
22.2 |
24.7 |
29.9 |
28.3 |
33.1 |
|
28.4 |
21.9 |
- |
Part of triplicate set - see bottom of table for triplicate average |
A19b |
458713 |
452414 |
34.9 |
35.3 |
30.4 |
- |
25.2 |
21.2 |
24.4 |
24.2 |
29.4 |
29.4 |
33.4 |
22.5 |
28.2 |
21.7 |
- |
Part of triplicate set - see bottom of table for triplicate average |
A2 |
459917 |
452405 |
37.0 |
38.9 |
33.2 |
- |
24.8 |
20.4 |
23.4 |
28.3 |
31.1 |
31.8 |
36.2 |
33.2 |
30.8 |
23.7 |
- |
|
A20 |
458760 |
452404 |
39.6 |
38.3 |
36.7 |
- |
41.3 |
29.1 |
22.9 |
26.2 |
34.9 |
40.9 |
38.0 |
25.5 |
33.9 |
26.1 |
- |
Part of triplicate set - see bottom of table for triplicate average |
A20a |
458760 |
452404 |
37.6 |
38.9 |
38.2 |
- |
35.7 |
30.8 |
25.2 |
29.7 |
32.6 |
36.6 |
38.2 |
25.3 |
33.5 |
25.8 |
- |
Part of triplicate set - see bottom of table for triplicate average |
A20b |
458760 |
452404 |
37.4 |
38.3 |
38.2 |
- |
37.1 |
28.0 |
24.6 |
29.7 |
35.7 |
33.6 |
41.8 |
31.1 |
34.1 |
26.3 |
- |
Part of triplicate set - see bottom of table for triplicate average |
A21 |
458806 |
452326 |
25.0 |
26.0 |
21.1 |
- |
14.0 |
12.5 |
15.9 |
13.7 |
14.7 |
22.0 |
24.3 |
23.2 |
19.3 |
15.1 |
- |
|
A22 |
458792 |
452242 |
27.8 |
25.8 |
22.4 |
- |
17.5 |
12.5 |
17.0 |
16.4 |
20.5 |
18.3 |
26.3 |
24.3 |
20.8 |
16.2 |
- |
|
A25 |
458706 |
452225 |
27.3 |
28.1 |
25.3 |
- |
21.6 |
16.5 |
16.5 |
18.0 |
21.9 |
24.4 |
28.6 |
22.3 |
22.8 |
17.5 |
- |
|
A29 |
456939 |
453013 |
25.9 |
24.5 |
21.5 |
- |
16.2 |
13.5 |
16.2 |
13.4 |
20.3 |
19.5 |
22.9 |
19.3 |
19.4 |
15.1 |
- |
|
A3 |
459822 |
452492 |
28.5 |
34.2 |
29.9 |
- |
27.0 |
24.8 |
|
23.8 |
34.8 |
27.4 |
28.9 |
31.9 |
29.1 |
22.4 |
- |
|
A30 |
457060 |
452888 |
26.0 |
25.5 |
20.3 |
- |
19.5 |
16.9 |
14.9 |
15.7 |
13.3 |
19.2 |
23.5 |
14.2 |
19.0 |
14.8 |
- |
|
A36 |
457625 |
452446 |
24.4 |
|
|
- |
15.6 |
12.3 |
11.7 |
10.6 |
13.5 |
14.1 |
17.9 |
16.0 |
15.1 |
11.8 |
- |
|
A38 |
457857 |
452334 |
21.3 |
17.1 |
18.6 |
- |
14.8 |
11.9 |
10.0 |
11.3 |
14.4 |
17.2 |
16.5 |
17.1 |
15.5 |
12.1 |
- |
|
A4 |
459699 |
452638 |
23.4 |
24.7 |
19.9 |
- |
13.6 |
12.4 |
16.8 |
15.8 |
20.0 |
21.7 |
25.7 |
23.9 |
19.8 |
15.5 |
- |
|
A40 |
458109 |
452196 |
21.8 |
23.3 |
22.6 |
- |
21.8 |
21.6 |
11.4 |
16.7 |
18.3 |
20.6 |
20.3 |
17.7 |
19.6 |
15.3 |
- |
|
A41 |
458172 |
452108 |
24.3 |
24.7 |
26.1 |
- |
22.5 |
21.7 |
13.8 |
17.7 |
12.2 |
|
21.4 |
18.3 |
20.3 |
15.6 |
- |
|
A45 |
458384 |
451817 |
20.1 |
19.9 |
18.2 |
- |
14.2 |
9.6 |
7.1 |
11.3 |
13.2 |
19.8 |
21.1 |
17.5 |
15.6 |
12.2 |
- |
|
A50 |
458732 |
451393 |
31.3 |
32.5 |
30.9 |
- |
29.2 |
26.6 |
23.8 |
20.2 |
24.1 |
28.0 |
29.1 |
24.8 |
27.3 |
21.0 |
- |
|
A51 |
458827 |
451348 |
27.0 |
27.8 |
23.1 |
- |
16.6 |
|
19.5 |
18.4 |
19.6 |
20.3 |
24.4 |
17.7 |
21.4 |
16.7 |
- |
|
A52 |
458945 |
451254 |
39.9 |
39.9 |
36.0 |
- |
32.3 |
32.5 |
24.1 |
28.0 |
26.8 |
31.9 |
39.4 |
31.3 |
32.9 |
25.3 |
- |
|
A53 |
459066 |
451239 |
41.1 |
38.9 |
37.5 |
- |
29.1 |
28.2 |
31.2 |
24.6 |
28.8 |
26.4 |
34.2 |
25.2 |
31.4 |
24.2 |
- |
|
A54 |
459254 |
451223 |
|
|
37.8 |
- |
33.8 |
32.7 |
30.5 |
|
33.8 |
33.0 |
40.4 |
|
34.6 |
28.5 |
- |
|
A55 |
459351 |
451221 |
36.1 |
41.0 |
35.8 |
- |
31.5 |
27.6 |
28.3 |
29.9 |
28.8 |
30.0 |
30.4 |
32.2 |
32.0 |
24.6 |
- |
|
A56 |
459470 |
451268 |
33.4 |
29.5 |
30.7 |
- |
27.9 |
15.4 |
20.3 |
46.3 |
20.9 |
25.6 |
32.3 |
|
28.2 |
22.0 |
- |
|
A57 |
459533 |
451280 |
54.1 |
59.8 |
60.7 |
- |
60.6 |
54.8 |
40.6 |
23.4 |
43.4 |
47.8 |
41.6 |
26.4 |
46.7 |
35.9 |
- |
|
A6 |
459536 |
452811 |
29.0 |
27.4 |
23.8 |
- |
16.9 |
14.8 |
19.2 |
17.0 |
25.2 |
23.1 |
29.9 |
24.3 |
22.8 |
17.5 |
- |
|
A60 |
458906 |
453276 |
19.1 |
19.1 |
14.5 |
- |
12.1 |
11.9 |
8.5 |
11.0 |
12.7 |
14.8 |
15.8 |
14.9 |
14.0 |
10.9 |
- |
|
A62 |
458806 |
453483 |
21.7 |
20.4 |
15.9 |
- |
10.6 |
9.0 |
9.9 |
11.3 |
13.7 |
15.9 |
17.6 |
16.5 |
14.8 |
11.5 |
- |
|
A64 |
460030 |
452327 |
27.9 |
33.1 |
34.5 |
- |
35.1 |
31.5 |
23.7 |
30.5 |
33.2 |
27.3 |
35.5 |
27.0 |
30.8 |
23.8 |
- |
|
A66 |
458672 |
453685 |
20.9 |
20.1 |
16.4 |
- |
11.8 |
10.2 |
11.6 |
9.6 |
12.1 |
16.5 |
22.0 |
|
15.1 |
11.8 |
- |
|
A69 |
458375 |
453958 |
15.5 |
15.4 |
17.5 |
- |
12.5 |
9.7 |
8.2 |
10.4 |
13.9 |
|
16.5 |
|
13.3 |
10.4 |
- |
|
A7 |
459441 |
452892 |
32.3 |
34.3 |
28.3 |
- |
18.4 |
14.8 |
21.2 |
21.1 |
23.0 |
27.1 |
30.3 |
16.1 |
24.3 |
18.7 |
- |
|
A70 |
458299 |
454070 |
22.2 |
20.8 |
19.1 |
- |
15.0 |
12.4 |
11.3 |
14.4 |
19.0 |
17.1 |
20.4 |
13.9 |
16.9 |
13.2 |
- |
|
A71 |
458121 |
454254 |
18.7 |
18.1 |
13.9 |
- |
10.3 |
7.4 |
8.3 |
9.2 |
12.6 |
14.2 |
19.0 |
17.2 |
13.5 |
10.6 |
- |
|
A74 |
458041 |
454371 |
|
18.9 |
14.4 |
- |
9.7 |
7.4 |
10.0 |
10.1 |
12.5 |
14.2 |
|
16.2 |
12.6 |
9.8 |
- |
|
A77 |
457929 |
454537 |
28.6 |
26.7 |
20.6 |
- |
13.7 |
9.6 |
13.1 |
13.3 |
14.1 |
20.8 |
25.2 |
19.5 |
18.7 |
14.6 |
- |
|
A81 |
457733 |
454805 |
24.6 |
22.5 |
17.4 |
- |
14.6 |
9.5 |
9.4 |
|
12.9 |
16.6 |
19.0 |
13.2 |
16.0 |
12.5 |
- |
|
A85 |
459364 |
453009 |
23.3 |
26.1 |
20.2 |
- |
15.9 |
13.2 |
18.2 |
17.2 |
21.7 |
22.2 |
26.5 |
22.1 |
20.6 |
16.1 |
- |
|
A88 |
457470 |
452550 |
22.6 |
22.3 |
19.5 |
- |
13.7 |
13.2 |
11.0 |
11.6 |
13.6 |
19.3 |
19.5 |
17.6 |
16.7 |
13.0 |
- |
|
A9 |
459295 |
453067 |
36.3 |
40.3 |
36.7 |
- |
32.4 |
22.6 |
|
24.5 |
22.4 |
30.9 |
|
31.3 |
30.8 |
23.7 |
- |
|
A90 |
459238 |
453157 |
51.1 |
51.5 |
42.8 |
- |
35.5 |
30.6 |
39.7 |
38.6 |
40.8 |
40.0 |
36.3 |
45.6 |
41.1 |
31.7 |
- |
|
A94 |
458651 |
452426 |
40.4 |
36.6 |
38.3 |
- |
31.1 |
8.9 |
10.9 |
12.2 |
14.3 |
|
27.8 |
29.1 |
25.0 |
19.2 |
- |
|
A96 |
459038 |
452850 |
33.2 |
39.5 |
34.2 |
- |
31.1 |
23.6 |
26.7 |
29.1 |
25.6 |
32.5 |
41.6 |
26.6 |
31.2 |
24.1 |
- |
|
A97 |
457431 |
452616 |
23.8 |
26.5 |
20.5 |
- |
14.6 |
13.2 |
15.2 |
11.9 |
17.7 |
22.6 |
25.8 |
21.2 |
19.4 |
14.9 |
- |
|
A98 |
458666 |
451468 |
30.8 |
24.2 |
23.5 |
- |
21.3 |
16.1 |
16.3 |
17.8 |
18.9 |
24.1 |
22.2 |
24.3 |
21.8 |
16.8 |
- |
|
B1 |
460848 |
452582 |
25.4 |
|
22.1 |
- |
14.7 |
11.8 |
16.0 |
15.1 |
19.3 |
21.2 |
25.7 |
24.6 |
19.6 |
15.1 |
- |
|
B15 |
461294 |
455305 |
22.7 |
27.5 |
24.6 |
- |
17.0 |
14.6 |
16.3 |
15.6 |
17.0 |
9.9 |
21.0 |
19.7 |
18.7 |
14.4 |
- |
|
B19 |
461891 |
455876 |
26.1 |
30.2 |
21.8 |
- |
16.6 |
12.8 |
14.5 |
15.8 |
16.7 |
18.1 |
21.9 |
20.3 |
19.5 |
15.0 |
- |
|
B2 |
460924 |
452697 |
28.6 |
30.0 |
26.0 |
- |
18.4 |
14.7 |
16.2 |
17.3 |
22.7 |
|
27.4 |
22.9 |
22.4 |
17.3 |
- |
|
B29 |
461453 |
452750 |
27.1 |
24.0 |
19.6 |
- |
17.8 |
11.8 |
13.8 |
14.9 |
17.5 |
19.8 |
27.1 |
16.5 |
19.1 |
14.7 |
- |
|
B3 |
460952 |
452826 |
23.8 |
27.9 |
25.7 |
- |
17.5 |
14.6 |
15.2 |
15.8 |
19.4 |
23.1 |
23.5 |
21.4 |
20.7 |
16.0 |
- |
|
B36 |
462565 |
454194 |
|
21.1 |
14.6 |
- |
10.4 |
8.5 |
|
10.1 |
9.9 |
14.5 |
20.4 |
15.6 |
13.9 |
10.8 |
- |
Part of triplicate set - see bottom of table for triplicate average |
B37 |
462565 |
454194 |
19.2 |
21.7 |
11.4 |
- |
9.3 |
8.4 |
9.0 |
10.1 |
11.6 |
12.2 |
20.9 |
|
13.4 |
10.4 |
- |
Part of triplicate set - see bottom of table for triplicate average |
B37a |
462565 |
454194 |
|
20.0 |
14.2 |
- |
11.0 |
8.9 |
8.9 |
11.9 |
11.3 |
13.0 |
14.9 |
15.5 |
13.0 |
10.1 |
- |
Part of triplicate set - see bottom of table for triplicate average |
B38 |
463757 |
455155 |
16.6 |
20.4 |
19.1 |
- |
11.9 |
9.0 |
9.8 |
10.7 |
14.3 |
16.8 |
22.5 |
18.6 |
15.4 |
12.0 |
- |
|
B41 |
461326 |
451330 |
29.9 |
34.6 |
31.0 |
- |
24.4 |
19.8 |
22.2 |
26.1 |
27.5 |
31.1 |
34.9 |
25.6 |
27.9 |
21.8 |
- |
|
B42 |
461430 |
451348 |
24.7 |
25.9 |
23.2 |
- |
18.4 |
16.5 |
14.7 |
19.0 |
18.4 |
23.5 |
19.7 |
17.2 |
20.1 |
15.7 |
- |
|
B43 |
461557 |
451343 |
22.8 |
24.1 |
21.2 |
- |
18.2 |
17.4 |
12.8 |
15.8 |
17.8 |
21.9 |
14.3 |
16.8 |
18.5 |
14.4 |
- |
|
B44 |
461643 |
451343 |
36.4 |
37.8 |
29.1 |
- |
23.0 |
21.4 |
22.1 |
23.2 |
28.9 |
28.9 |
30.0 |
26.9 |
28.0 |
21.5 |
- |
|
B45 |
461849 |
451284 |
28.0 |
33.8 |
29.5 |
- |
23.7 |
19.2 |
20.3 |
18.1 |
23.3 |
25.9 |
31.6 |
6.6 |
23.6 |
18.2 |
- |
|
B47 |
462019 |
451289 |
17.0 |
19.1 |
13.9 |
- |
8.8 |
8.9 |
10.1 |
10.1 |
8.3 |
14.3 |
20.3 |
|
13.1 |
10.2 |
- |
|
B48 |
462122 |
451289 |
21.3 |
24.0 |
19.6 |
- |
14.6 |
11.1 |
12.4 |
11.9 |
17.2 |
18.8 |
23.7 |
18.7 |
17.6 |
13.7 |
- |
|
B50 |
462291 |
451269 |
26.1 |
27.0 |
22.3 |
- |
18.1 |
14.6 |
16.4 |
16.4 |
20.9 |
22.5 |
20.1 |
20.3 |
20.4 |
15.7 |
- |
|
B51 |
462384 |
451298 |
19.4 |
22.4 |
16.1 |
- |
11.6 |
9.6 |
10.0 |
11.8 |
15.1 |
18.1 |
22.2 |
18.7 |
15.9 |
12.4 |
- |
|
B56 |
462888 |
451289 |
26.3 |
34.3 |
30.1 |
- |
21.3 |
30.4 |
20.5 |
20.5 |
26.7 |
30.7 |
38.4 |
22.0 |
27.4 |
21.1 |
- |
|
B58 |
462970 |
451300 |
22.1 |
23.6 |
17.4 |
- |
12.9 |
10.9 |
13.5 |
12.7 |
15.5 |
17.0 |
22.9 |
15.5 |
16.7 |
13.0 |
- |
|
B60 |
463234 |
451339 |
20.4 |
25.2 |
17.2 |
- |
11.4 |
10.5 |
13.0 |
10.8 |
17.4 |
20.4 |
23.2 |
22.5 |
17.5 |
13.6 |
- |
|
B63 |
462704 |
451300 |
33.4 |
34.0 |
30.6 |
- |
23.3 |
25.6 |
28.5 |
25.8 |
30.4 |
28.4 |
29.3 |
27.4 |
28.8 |
22.2 |
- |
|
B72 |
461122 |
451374 |
44.5 |
47.9 |
37.4 |
- |
33.9 |
31.4 |
33.8 |
41.6 |
46.5 |
44.1 |
|
|
40.1 |
30.9 |
- |
|
B74 |
461371 |
452708 |
|
24.7 |
18.8 |
- |
12.4 |
10.1 |
11.1 |
12.9 |
14.3 |
20.7 |
23.8 |
11.9 |
16.1 |
12.5 |
- |
|
B80 |
461185 |
452663 |
20.2 |
23.5 |
16.2 |
- |
10.7 |
10.6 |
10.7 |
10.6 |
14.8 |
16.6 |
23.0 |
18.3 |
15.9 |
12.4 |
- |
|
B82 |
460974 |
452563 |
27.4 |
28.7 |
24.9 |
- |
16.2 |
15.3 |
21.8 |
18.3 |
24.0 |
19.1 |
28.3 |
22.9 |
22.4 |
17.5 |
- |
|
B83 |
461285 |
452695 |
32.6 |
35.3 |
27.2 |
- |
23.9 |
21.1 |
19.9 |
21.1 |
25.5 |
26.1 |
34.3 |
25.3 |
26.6 |
20.5 |
- |
|
B84 |
462654 |
451293 |
25.3 |
26.0 |
22.7 |
- |
18.5 |
16.5 |
19.9 |
18.4 |
22.8 |
22.5 |
24.2 |
19.6 |
21.5 |
16.8 |
- |
|
B85 |
461227 |
451368 |
33.2 |
34.2 |
30.6 |
- |
23.9 |
22.9 |
21.8 |
24.0 |
24.8 |
17.0 |
34.2 |
28.2 |
26.8 |
20.6 |
- |
|
B86 |
461116 |
452602 |
30.5 |
28.7 |
24.0 |
- |
16.7 |
15.4 |
14.3 |
15.4 |
19.8 |
22.8 |
29.2 |
22.8 |
21.8 |
16.8 |
- |
|
B88 |
462799 |
451291 |
33.2 |
34.3 |
26.5 |
- |
19.4 |
14.5 |
19.5 |
21.1 |
23.2 |
20.9 |
29.9 |
25.2 |
24.3 |
18.7 |
- |
|
B91 |
461143 |
451364 |
41.7 |
45.8 |
34.9 |
- |
30.2 |
|
33.0 |
34.6 |
35.9 |
28.6 |
36.8 |
38.7 |
36.0 |
27.7 |
- |
|
B90 |
461133 |
451394 |
33.7 |
39.2 |
33.4 |
- |
30.9 |
28.2 |
24.2 |
29.3 |
31.3 |
33.6 |
35.0 |
28.7 |
31.6 |
24.3 |
- |
|
C12 |
458825 |
449928 |
20.8 |
22.8 |
19.6 |
- |
8.2 |
12.0 |
10.6 |
11.7 |
13.8 |
14.0 |
22.4 |
17.5 |
15.8 |
12.3 |
- |
|
C17 |
459085 |
450544 |
18.6 |
21.8 |
17.4 |
- |
13.6 |
12.6 |
9.8 |
11.7 |
14.4 |
16.9 |
19.1 |
13.5 |
15.4 |
12.0 |
- |
|
C18 |
459204 |
450772 |
88.2 |
33.5 |
23.0 |
- |
18.0 |
17.0 |
19.8 |
17.2 |
21.3 |
18.7 |
26.3 |
21.1 |
27.6 |
21.6 |
- |
|
C19 |
459271 |
450819 |
19.6 |
23.9 |
20.7 |
- |
12.3 |
10.3 |
15.2 |
14.4 |
15.2 |
18.7 |
21.6 |
14.9 |
17.0 |
13.2 |
- |
|
C2 |
458333 |
448974 |
38.1 |
41.5 |
30.8 |
- |
24.8 |
23.9 |
|
25.1 |
29.3 |
29.1 |
20.7 |
18.7 |
28.2 |
21.7 |
- |
|
C20 |
459280 |
450923 |
22.9 |
27.9 |
23.1 |
- |
17.4 |
14.2 |
15.2 |
20.4 |
20.4 |
19.9 |
25.3 |
19.9 |
20.6 |
16.1 |
- |
|
C21 |
459410 |
451040 |
26.9 |
30.2 |
26.2 |
- |
20.3 |
18.5 |
18.6 |
19.3 |
19.5 |
25.1 |
32.1 |
21.5 |
23.5 |
18.1 |
- |
|
C22 |
459570 |
451195 |
21.6 |
29.2 |
23.4 |
- |
15.8 |
11.6 |
12.6 |
14.3 |
15.6 |
20.3 |
24.6 |
20.8 |
19.1 |
14.9 |
- |
|
C23 |
459553 |
451252 |
43.3 |
48.9 |
36.1 |
- |
37.1 |
29.5 |
30.3 |
31.4 |
27.8 |
36.8 |
38.3 |
30.9 |
35.5 |
27.3 |
- |
|
C26 |
459639 |
451334 |
46.5 |
53.8 |
48.0 |
- |
43.6 |
38.8 |
34.7 |
33.6 |
34.9 |
32.8 |
37.7 |
33.0 |
39.8 |
30.6 |
- |
|
C27 |
459717 |
451433 |
59.4 |
58.6 |
55.0 |
- |
50.1 |
43.6 |
45.3 |
45.3 |
42.4 |
44.7 |
41.5 |
43.9 |
48.2 |
37.1 |
- |
|
C28 |
461201 |
448386 |
13.9 |
18.3 |
14.6 |
- |
11.8 |
10.2 |
10.2 |
10.6 |
13.8 |
13.2 |
16.4 |
14.2 |
13.4 |
10.4 |
- |
|
C29 |
461196 |
448426 |
30.8 |
31.7 |
29.6 |
- |
22.2 |
26.7 |
22.6 |
21.1 |
27.0 |
28.5 |
32.6 |
23.6 |
26.9 |
20.7 |
- |
|
C30 |
461185 |
448462 |
30.2 |
36.8 |
31.0 |
- |
28.4 |
|
26.0 |
23.1 |
29.6 |
26.1 |
35.1 |
15.9 |
28.2 |
21.7 |
- |
|
C31 |
461193 |
448473 |
21.2 |
23.4 |
18.8 |
- |
15.1 |
12.3 |
14.6 |
11.0 |
16.9 |
16.3 |
19.0 |
17.6 |
16.9 |
13.2 |
- |
|
C32 |
461128 |
448823 |
30.8 |
29.1 |
24.8 |
- |
17.6 |
13.1 |
14.8 |
18.6 |
22.2 |
23.8 |
29.1 |
22.6 |
22.4 |
17.5 |
- |
|
C33 |
461085 |
448933 |
|
20.3 |
16.5 |
- |
12.0 |
9.0 |
10.7 |
9.1 |
13.5 |
14.4 |
16.3 |
17.2 |
13.9 |
10.8 |
- |
|
C34 |
461085 |
449067 |
24.8 |
25.7 |
27.5 |
- |
22.0 |
|
16.4 |
17.6 |
22.8 |
23.7 |
24.1 |
19.6 |
22.4 |
17.3 |
- |
|
C36 |
461052 |
449146 |
31.7 |
32.3 |
28.6 |
- |
21.7 |
19.6 |
24.7 |
24.0 |
20.0 |
25.3 |
27.1 |
27.1 |
25.6 |
19.7 |
- |
|
C37 |
461045 |
449223 |
15.9 |
26.1 |
23.6 |
- |
18.2 |
15.3 |
13.6 |
15.4 |
20.6 |
18.4 |
25.7 |
20.3 |
19.4 |
15.1 |
- |
|
C38 |
461038 |
449225 |
31.2 |
30.0 |
29.5 |
- |
22.0 |
18.5 |
17.4 |
18.3 |
23.8 |
23.4 |
29.3 |
24.3 |
24.3 |
18.7 |
- |
|
C39 |
460974 |
449336 |
41.5 |
40.2 |
36.0 |
- |
28.9 |
23.2 |
|
23.9 |
32.0 |
30.6 |
31.0 |
35.8 |
32.3 |
24.9 |
- |
|
C4 |
458470 |
449126 |
18.7 |
21.7 |
17.1 |
- |
10.4 |
10.2 |
10.9 |
11.9 |
15.1 |
16.9 |
20.8 |
16.1 |
15.4 |
12.0 |
- |
|
C40 |
460910 |
449628 |
17.3 |
20.9 |
19.7 |
- |
|
11.0 |
15.6 |
13.8 |
18.2 |
19.4 |
22.0 |
13.7 |
17.2 |
13.4 |
- |
|
C42 |
460857 |
449748 |
29.2 |
28.4 |
22.8 |
- |
17.8 |
13.6 |
17.4 |
16.9 |
17.4 |
19.7 |
27.4 |
22.0 |
21.1 |
16.5 |
- |
|
C43 |
460869 |
449730 |
27.4 |
35.5 |
30.9 |
- |
25.1 |
17.4 |
20.9 |
23.5 |
32.5 |
29.1 |
17.9 |
25.0 |
25.9 |
20.0 |
- |
Part of triplicate set - see bottom of table for triplicate average |
C43a |
460869 |
449730 |
33.9 |
36.2 |
30.2 |
- |
26.1 |
21.0 |
23.5 |
22.8 |
26.3 |
27.5 |
28.9 |
22.5 |
27.2 |
20.9 |
- |
Part of triplicate set - see bottom of table for triplicate average |
C44 |
460869 |
449730 |
31.0 |
36.6 |
28.7 |
- |
26.4 |
20.0 |
20.5 |
23.9 |
27.0 |
23.7 |
22.1 |
26.8 |
26.1 |
20.1 |
- |
Part of triplicate set - see bottom of table for triplicate average |
C49 |
460860 |
450530 |
23.4 |
22.5 |
21.6 |
- |
14.2 |
12.5 |
11.8 |
13.2 |
17.1 |
15.6 |
17.1 |
15.4 |
16.8 |
13.1 |
- |
|
C51 |
460871 |
450727 |
|
29.5 |
27.6 |
- |
20.3 |
17.5 |
17.8 |
19.3 |
24.6 |
|
29.7 |
|
23.3 |
18.9 |
- |
|
C52 |
460853 |
450781 |
27.4 |
29.3 |
23.2 |
- |
16.9 |
14.4 |
16.0 |
15.9 |
19.2 |
23.3 |
27.4 |
19.7 |
21.2 |
16.3 |
- |
|
C53 |
460766 |
450924 |
24.4 |
26.6 |
30.2 |
- |
|
|
|
|
|
|
|
|
27.1 |
16.7 |
- |
|
C54 |
460762 |
451069 |
32.4 |
29.1 |
22.5 |
- |
25.5 |
22.6 |
17.1 |
20.6 |
26.7 |
23.5 |
36.1 |
25.2 |
25.6 |
19.7 |
- |
|
C56 |
459484 |
451141 |
37.7 |
41.5 |
32.3 |
- |
27.2 |
22.0 |
24.3 |
22.2 |
21.6 |
|
33.0 |
28.8 |
29.1 |
22.4 |
- |
|
C57 |
458912 |
450111 |
21.8 |
25.8 |
19.0 |
- |
16.2 |
16.2 |
15.1 |
15.2 |
18.3 |
16.3 |
22.1 |
17.4 |
18.5 |
14.4 |
- |
|
C58 |
460926 |
449429 |
41.5 |
41.6 |
40.3 |
- |
28.1 |
24.1 |
32.6 |
29.8 |
35.6 |
28.1 |
33.0 |
22.4 |
32.5 |
25.0 |
- |
|
C59 |
458735 |
449713 |
34.1 |
39.5 |
33.0 |
- |
27.0 |
23.2 |
25.8 |
22.6 |
25.1 |
27.6 |
29.2 |
23.2 |
28.2 |
21.7 |
- |
|
C62 |
459579 |
451251 |
29.8 |
35.6 |
29.2 |
- |
21.7 |
16.9 |
21.0 |
21.2 |
21.2 |
22.6 |
28.5 |
24.6 |
24.8 |
19.1 |
- |
|
C63 |
458790 |
449740 |
20.2 |
24.1 |
18.9 |
- |
12.1 |
10.7 |
12.7 |
12.9 |
12.5 |
14.1 |
18.0 |
16.0 |
15.7 |
12.1 |
- |
|
C7 |
458611 |
449477 |
20.3 |
21.9 |
14.6 |
- |
14.1 |
13.2 |
12.8 |
13.7 |
19.4 |
17.2 |
23.0 |
19.1 |
17.2 |
13.3 |
- |
|
D10 |
460443 |
451927 |
22.9 |
22.6 |
16.5 |
- |
11.6 |
9.8 |
11.7 |
10.3 |
14.4 |
20.2 |
25.7 |
12.5 |
16.2 |
12.6 |
- |
|
D12 |
460567 |
451740 |
25.5 |
20.1 |
17.8 |
- |
12.0 |
10.4 |
12.6 |
11.9 |
14.7 |
16.7 |
24.2 |
17.7 |
16.7 |
12.9 |
- |
|
D13 |
460271 |
451358 |
28.9 |
22.7 |
26.0 |
- |
22.2 |
19.0 |
21.6 |
15.4 |
13.3 |
22.8 |
27.4 |
18.9 |
21.7 |
16.7 |
- |
|
D14 |
461077 |
451354 |
38.9 |
41.5 |
39.6 |
- |
36.5 |
32.5 |
31.6 |
34.1 |
42.0 |
34.8 |
37.5 |
|
36.9 |
28.4 |
- |
|
D16 |
460708 |
451231 |
42.3 |
38.8 |
34.3 |
- |
41.4 |
35.6 |
32.6 |
35.0 |
40.4 |
47.4 |
38.6 |
25.4 |
37.4 |
28.8 |
- |
|
D17 |
460575 |
451616 |
49.3 |
43.1 |
27.6 |
- |
|
19.4 |
25.8 |
29.6 |
33.8 |
32.5 |
36.2 |
22.9 |
32.0 |
24.7 |
- |
|
D18 |
460395 |
451502 |
|
37.6 |
32.0 |
- |
26.8 |
20.0 |
21.8 |
22.3 |
26.0 |
|
25.8 |
25.9 |
26.5 |
20.4 |
- |
|
D19 |
460038 |
451626 |
47.6 |
46.1 |
39.9 |
- |
47.6 |
45.0 |
38.3 |
41.1 |
38.8 |
40.5 |
41.9 |
35.9 |
42.1 |
32.4 |
- |
|
D20 |
460323 |
451685 |
49.7 |
44.3 |
41.3 |
- |
39.9 |
36.1 |
40.2 |
|
39.7 |
43.4 |
39.2 |
31.2 |
40.5 |
31.2 |
- |
|
D22 |
460035 |
452010 |
|
|
39.7 |
- |
38.0 |
|
36.8 |
33.9 |
36.7 |
31.5 |
32.1 |
|
35.5 |
28.9 |
- |
|
D24 |
459805 |
451543 |
25.8 |
30.8 |
20.7 |
- |
21.1 |
15.2 |
19.7 |
22.9 |
23.3 |
20.4 |
37.6 |
20.1 |
23.4 |
18.0 |
- |
|
D25 |
459693 |
451750 |
57.8 |
52.9 |
38.0 |
- |
42.4 |
33.5 |
33.7 |
37.0 |
36.1 |
41.2 |
47.8 |
35.6 |
41.5 |
31.9 |
- |
|
D26 |
460671 |
451400 |
30.6 |
32.8 |
29.4 |
- |
23.0 |
19.7 |
21.8 |
21.7 |
24.4 |
31.9 |
35.0 |
25.1 |
26.9 |
20.7 |
- |
|
D27 |
460734 |
451563 |
26.4 |
24.3 |
22.4 |
- |
17.7 |
15.3 |
14.9 |
18.2 |
16.0 |
24.2 |
25.8 |
21.4 |
20.6 |
15.9 |
- |
|
D28 |
460764 |
451185 |
34.6 |
41.4 |
34.0 |
- |
31.8 |
24.3 |
28.1 |
32.4 |
35.3 |
32.2 |
25.6 |
15.4 |
30.5 |
23.5 |
- |
|
D30 |
460834 |
451252 |
30.8 |
27.8 |
27.1 |
- |
22.3 |
17.0 |
17.6 |
19.2 |
25.1 |
19.7 |
29.1 |
20.9 |
23.3 |
18.0 |
- |
|
D31 |
461002 |
451229 |
28.8 |
32.3 |
27.8 |
- |
30.6 |
25.0 |
17.7 |
26.1 |
34.1 |
34.1 |
36.8 |
23.9 |
28.8 |
22.2 |
- |
|
D32 |
460258 |
451208 |
36.9 |
39.4 |
33.0 |
- |
34.2 |
27.7 |
25.9 |
28.4 |
33.2 |
31.8 |
38.5 |
27.7 |
32.4 |
25.0 |
- |
|
D33 |
460075 |
451174 |
42.8 |
35.7 |
31.5 |
- |
28.2 |
24.2 |
24.7 |
26.8 |
32.4 |
31.8 |
38.5 |
|
31.7 |
24.4 |
- |
|
D35 |
460134 |
451170 |
37.3 |
41.4 |
34.0 |
- |
34.0 |
26.4 |
28.0 |
32.6 |
24.8 |
32.6 |
45.4 |
30.2 |
33.3 |
25.7 |
- |
|
D36 |
460135 |
450884 |
19.1 |
38.4 |
36.3 |
- |
25.7 |
23.3 |
23.6 |
24.4 |
29.8 |
31.3 |
41.9 |
32.3 |
29.6 |
22.8 |
- |
|
D37 |
460157 |
450988 |
35.9 |
28.3 |
32.0 |
- |
26.3 |
|
20.3 |
20.6 |
25.5 |
11.9 |
31.7 |
23.5 |
25.6 |
19.7 |
- |
|
D38 |
460088 |
450929 |
31.7 |
29.0 |
22.6 |
- |
19.5 |
13.2 |
13.5 |
17.5 |
18.3 |
23.4 |
28.1 |
8.8 |
20.5 |
15.8 |
- |
|
D39 |
460185 |
451055 |
34.1 |
31.0 |
32.0 |
- |
25.2 |
20.8 |
22.0 |
22.4 |
26.8 |
25.7 |
31.8 |
23.8 |
26.9 |
20.7 |
- |
|
D4 |
460560 |
452300 |
33.1 |
31.5 |
28.2 |
- |
20.9 |
16.3 |
21.6 |
21.0 |
24.9 |
26.6 |
30.1 |
25.3 |
25.4 |
19.6 |
- |
|
D40 |
460069 |
451196 |
27.6 |
27.4 |
17.6 |
- |
21.6 |
18.4 |
17.5 |
20.9 |
23.0 |
26.4 |
25.9 |
22.2 |
22.6 |
17.4 |
- |
|
D41 |
460286 |
452487 |
44.7 |
46.6 |
39.9 |
- |
|
27.1 |
41.5 |
39.4 |
42.3 |
39.4 |
40.5 |
38.5 |
40.0 |
30.8 |
- |
|
D43 |
459920 |
451834 |
32.5 |
46.9 |
44.1 |
- |
42.1 |
39.2 |
42.3 |
38.6 |
44.7 |
40.9 |
36.6 |
30.8 |
39.9 |
30.7 |
- |
|
D45 |
460673 |
451869 |
7.6 |
32.0 |
25.5 |
- |
19.6 |
17.0 |
17.1 |
18.3 |
21.6 |
23.1 |
29.0 |
18.6 |
20.9 |
16.1 |
- |
|
D47 |
460682 |
452187 |
32.8 |
27.6 |
26.1 |
- |
21.5 |
18.4 |
17.5 |
20.2 |
24.9 |
25.9 |
28.5 |
|
24.3 |
18.7 |
- |
|
D48 |
460103 |
452180 |
42.3 |
48.0 |
50.2 |
- |
43.8 |
41.3 |
34.8 |
35.9 |
|
33.8 |
38.7 |
25.5 |
39.4 |
30.4 |
- |
|
D49 |
460656 |
451269 |
39.0 |
39.8 |
37.5 |
- |
33.3 |
25.0 |
31.0 |
31.1 |
39.0 |
34.0 |
34.3 |
22.8 |
33.3 |
25.7 |
- |
|
D50 |
460371 |
451682 |
44.5 |
42.8 |
|
- |
35.2 |
33.7 |
33.5 |
32.1 |
31.7 |
34.6 |
42.3 |
20.6 |
35.1 |
27.0 |
- |
|
D51 |
459640 |
451722 |
58.1 |
60.9 |
54.8 |
- |
53.5 |
47.9 |
52.3 |
53.5 |
52.7 |
46.0 |
47.0 |
50.6 |
52.5 |
40.4 |
- |
|
D52 |
460887 |
451140 |
28.2 |
25.0 |
20.7 |
- |
18.2 |
13.8 |
14.6 |
11.9 |
14.9 |
20.7 |
21.0 |
8.9 |
18.0 |
13.9 |
- |
|
D53 |
460115 |
451146 |
26.1 |
27.1 |
26.9 |
- |
26.0 |
24.1 |
16.9 |
20.1 |
23.8 |
25.1 |
22.7 |
14.9 |
23.1 |
17.8 |
- |
|
D54 |
460146 |
451116 |
26.2 |
27.4 |
28.3 |
- |
24.6 |
22.2 |
15.1 |
20.2 |
21.8 |
24.5 |
30.0 |
18.8 |
23.6 |
18.1 |
- |
|
D55 |
460087 |
452065 |
50.1 |
59.3 |
53.3 |
- |
56.2 |
46.4 |
49.8 |
47.2 |
47.0 |
37.7 |
46.5 |
36.4 |
48.2 |
37.1 |
33.6 |
|
D56 |
460400 |
451685 |
50.2 |
48.1 |
42.7 |
- |
42.1 |
|
50.1 |
44.9 |
45.7 |
50.8 |
48.2 |
33.5 |
45.6 |
35.1 |
- |
|
D57 |
460416 |
451708 |
34.4 |
34.9 |
30.8 |
- |
30.1 |
28.2 |
|
27.2 |
25.5 |
23.4 |
33.2 |
27.2 |
29.5 |
22.7 |
- |
|
D58 |
460435 |
451732 |
42.8 |
43.8 |
34.8 |
- |
33.1 |
35.8 |
41.3 |
38.0 |
40.6 |
41.0 |
38.3 |
32.1 |
38.3 |
29.5 |
- |
|
D59 |
460087 |
452156 |
63.0 |
66.1 |
46.6 |
- |
52.3 |
49.2 |
59.7 |
52.2 |
45.4 |
23.4 |
38.2 |
39.9 |
48.7 |
37.5 |
34.3 |
|
D6 |
460570 |
452177 |
27.4 |
24.7 |
19.9 |
- |
11.4 |
10.7 |
11.5 |
13.0 |
15.8 |
15.9 |
19.3 |
18.1 |
17.1 |
13.3 |
- |
|
D60 |
460294 |
451883 |
23.7 |
26.0 |
21.0 |
- |
16.4 |
12.6 |
16.3 |
15.8 |
18.8 |
20.8 |
15.2 |
19.1 |
18.7 |
14.4 |
- |
|
D8 |
460553 |
451843 |
38.6 |
46.4 |
41.1 |
- |
41.4 |
37.8 |
29.3 |
30.4 |
|
45.1 |
45.5 |
|
39.5 |
30.4 |
- |
|
D9 |
460483 |
452357 |
39.1 |
41.8 |
40.0 |
- |
41.0 |
34.4 |
25.3 |
|
39.9 |
39.9 |
42.6 |
25.2 |
36.9 |
28.4 |
- |
|
8, 9, 9a |
460163 |
452468 |
22.3 |
22.1 |
20.7 |
- |
13.6 |
10.7 |
14.3 |
12.6 |
16.2 |
17.8 |
21.3 |
17.0 |
17.1 |
13.4 |
- |
Triplicate Average for sites 8, 9 and 9a (Portland Street) |
A13, A14, A14a |
459335 |
452931 |
20.9 |
22.3 |
18.6 |
- |
13.2 |
11.1 |
10.7 |
12.2 |
14.5 |
17.1 |
22.9 |
18.1 |
16.5 |
12.9 |
- |
Triplicate Average for sites A13, A14 and A14a (Clifton Dale) |
78, 79, 80 |
460149 |
452342 |
37.5 |
41.0 |
|
- |
35.2 |
28.5 |
28.8 |
27.7 |
30.9 |
23.7 |
32.8 |
23.0 |
30.9 |
23.8 |
- |
Triplicate Average for sites 78, 79 and 80 (Gillygate) |
102, 103, 104 |
458703 |
452429 |
38.1 |
37.9 |
39.3 |
- |
38.4 |
32.4 |
25.9 |
30.8 |
36.0 |
29.0 |
40.3 |
29.4 |
34.3 |
26.4 |
- |
Triplicate Average for sites 102, 103 and 104 (Salisbury Terrace) |
2a, 2b, 2c |
460746 |
451034 |
23.2 |
25.9 |
25.3 |
- |
19.4 |
18.4 |
15.9 |
20.0 |
22.7 |
23.4 |
29.5 |
19.8 |
22.1 |
17.1 |
- |
Triplicate Average for sites 2a, 2b and 2c (Fishergate) |
3a, 3b, 3c |
460024 |
452767 |
18.3 |
21.8 |
18.1 |
- |
10.4 |
8.6 |
11.1 |
10.5 |
14.7 |
16.1 |
15.1 |
16.6 |
14.7 |
11.4 |
- |
Triplicate Average for sites 3a, 3b and 3c (Bootham) |
95a, 95b, 95c |
460938 |
449465 |
28.3 |
27.8 |
23.8 |
- |
18.2 |
20.6 |
18.3 |
18.8 |
18.9 |
23.1 |
|
19.7 |
21.8 |
16.8 |
- |
Triplicate Average for sites 95a, 95b and 95c (Fulford) |
A19, A19a, A19b |
458713 |
452414 |
36.3 |
32.9 |
30.9 |
- |
24.6 |
21.3 |
24.9 |
24.5 |
29.4 |
29.7 |
34.4 |
24.4 |
28.5 |
21.9 |
- |
Triplicate Average for sites A19, A19a and A19b (Salisbury Terrace) |
A20, A20a, A20b |
458760 |
452404 |
38.2 |
38.5 |
37.7 |
- |
38.0 |
29.3 |
24.2 |
28.5 |
34.4 |
37.0 |
39.3 |
27.3 |
33.9 |
26.1 |
- |
Triplicate Average for sites A20, A20a and A20b (Salisbury Terrace) |
B36, B37, B37a |
462565 |
454194 |
19.2 |
20.9 |
13.4 |
- |
10.2 |
8.6 |
9.0 |
10.7 |
10.9 |
13.2 |
18.7 |
15.6 |
13.7 |
10.7 |
- |
Triplicate Average for sites B36, B37 and B37a (Malton Road) |
C43, C43a, C44 |
460869 |
449730 |
30.8 |
36.1 |
29.9 |
- |
25.9 |
19.5 |
21.6 |
23.4 |
28.6 |
26.8 |
23.0 |
24.8 |
26.4 |
20.3 |
- |
Triplicate Average for sites C43, C43a and C44 (Fulford Road) |
☒ 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.
☒ City of York Council confirm that all 2023 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.
CYC regularly reviews planning applications with respect to potential air quality and other environmental impacts. The main sources identified include road traffic emissions associated with new developments. Developments are required to assess their impacts on air quality where necessary in line with CYC’s Low Emission Planning Guidance.
The table below provides an overview of planning applications (including discharge of condition applications) that have been considered in relation to air quality by CYC’s Public Protection team during 2023. A formal air quality impact assessment has been requested for some of these applications.
The Annual Status Report provides an opportunity to keep a record of such applications to provide a picture of where changes in air quality may occur in the future. The information presented is also useful to identify where combined impacts of several developments may become important. It should be noted that electric vehicle (EV) recharging was requested for a large number of applications in 2023 and as such not all of these have been referenced below.
Comments on all planning applications processed by CYC are available by searching the planning reference number at Search Planning Applications received by City of York Council.
Planning Reference |
Description |
AOD/22/00420 |
Condition 6 (EV charging) of 22/00542/FUL. The Clock Tower Bishopthorpe Road York |
23/00004/FUL |
Installation of replacement biomass boiler (retrospective). Vertigrow Garden Centre, Lawnswood House, Malton Road, Stockton On The Forest, York, YO32 9TL |
23/00157/FUL |
Use of land as temporary car park at Bootham Park Court (retrospective in part). York District Hospital, Wigginton Road, York, YO31 8HE |
23/00160/OUTM |
Outline application with all matters reserved except for access for circa 800 dwellings, provision of open space, flood storage measures, landscaping and associated infrastructure. Land To The South Of Rose Cottage Farm And The Lodge, Moor Lane, Haxby, York |
AOD/23/00038 |
Condition 5 (EV charging) of 22/01691/FUL. |
AOD/23/00073 |
Condition 13 (EV charging) of planning permission 22/02433/FUL. Fulford School, Fulfordgate, York, YO10 4FY |
AOD/23/00105 |
Condition 32 of 20/01546/FUL. North Selby Mine, New Road, Deighton, York, YO19 6EZ |
23/00633/FUL |
Variation of condition 1 of permitted application 22/00542/FUL to alter car parking allocation. The Clock Tower, Bishopthorpe Road, York |
23/00644/FUL |
Reconfiguration of car parking area serving Clifton House. Clifton House, Bluebeck Drive, York, YO30 5RA |
23/00391/FUL |
Erection of 4no. dwellings with associated access, parking and landscaping following demolition of existing commercial buildings. Moor Lane Construction Unit, 1 Moor Lane, Bishopthorpe, York, YO23 2UF |
23/00608/FULM |
Erection of extra care accommodation including no.72 apartments and decked car park. Chocolate Works Residents Parking, Bishopthorpe Road, York |
AOD/23/00127 |
Condition 6 (EV charging strategy) of 22/01288/FUL. York Pullman Bus Company Ltd, Rawcliffe Depot, Shipton Road, Rawcliffe, York, YO30 5YA |
23/00742/FUL |
One and two storey side extension, external alterations to existing building and creation of additional car and cycle parking provision. Poppleton Community Centre, Main Street, Upper Poppleton, York, YO26 6JT |
AOD/23/00147 |
Condition 25 (EV charging strategy) of 21/01371/FULM. Land At Cocoa West, Wigginton Road, York |
AOD/23/00176 |
Condition 3 (EV charging) of planning permission 21/02601/FULM. Former Storage Facility Site Derwent Valley Industrial Estate, Dunnington, York |
AOD/23/00267 |
Condition 19 (EV charging) of 18/02744/OUTM. Lindum Business Park, York Road, Elvington, York |
23/01494/REMM |
Reserved matters approval for layout, scale, appearance, landscaping and access for the creation of a new public realm with associated infrastructure and landscaping and alterations to the existing road network pursuant to outline planning permission 18/01884/OUTM. York Central, Leeman Road, York |
AOD/23/00268 |
Condition 10 (EV charging) of 22/02012/FULM. Abracs, George Cayley Drive, York, YO30 4XE |
AOD/23/00295 |
Condition 8 (EV charging) of 20/00940/FULM. Premier Inn, Layerthorpe York YO31 7YW |
AOD/23/00294 |
Condition 9 (EV charging) of 21/02220/FULM. Marrtree Business Park, Stirling Road, York |
AOD/23/00306 |
Condition 4 (EV charging) of 20/02012/FUL. Ryburn Dene, Grosvenor Road, York, YO30 7AN |
AOD/23/00357 |
Condition 23 (EV charging) of 20/02087/FUL. Former 86 Heworth, York, YO31 1AP |
AOD/23/00355 |
Conditions 12 (EV charging) of 20/02034/FULM. Luna, Fifth Avenue, York |
AOD/23/00354 |
Condition 24 (EV charging) of 22/00015/FULM. J H Shouksmith And Sons Ltd, Murton Way, York, YO19 5GS |
23/02200/FULM |
Erection of food store and drive-thru restaurant both with associated access, parking and landscaping. T.K.Maxx, Unit 2 Monks Cross Drive, Huntington, York, YO32 9GX |
22/02020/FULM |
Improvements to the A1237 York Outer Ring Road including dualling of existing carriageway, improvements to roundabouts, provision of 5.1km shared use cycle and pedestrian route, signalised crossing facilities for active travel users, 2no. overbridges and no.6 underpasses for pedestrians and cyclists with ancillary development including sustainable drainage measures, flood compensatory storage areas, woodland planting/landscaping, habitat creation, noise barriers, revised field accesses, associated infrastructure and earthworks |
Additional work carried out in 2023 to support the development of AQAP measures includes:
· ‘Fuel for Thought’ Campaign – we carried out research and insights into key target audience personas in York to inform the DEFRA funded solid fuel burning campaign. A pre-campaign awareness survey, issued via CYC Business Intelligence, ran for 3 weeks in August 2023. In addition, three public focus groups were progressed at CYC Library Venues across York. A summary of this research and a selection of materials developed for the final ‘Fuel for Thought’ campaign has already been shared with DEFRA as part of the AQ Grant quarterly update reports.
· York Air Alert - We progressed research and development into CYC’s new DEFRA funded Air Quality Forecasting and Alert Platform, York Air Alert. The platform can be used by residents and visitors (especially those with health conditions exacerbated by air pollution) to make informed decisions with respect to travel around the city to help reduce their own exposure to air pollution.
· Smoke Control Areas – we undertook further research in CYC’s historical Smoke Control Orders, collating the required evidence base, and consulted with CYC Legal Services and DEFRA about potential expansion of CYC Smoke Control Area to cover the whole of CYC’s administrative area. It is anticipated that this project will progress in 2024; further details are provided in AQAP4.
· Gillygate Air Quality Working Group - An officer working group was established in August 2023 to consider specific air quality improvement measures on Gillygate in response to continued exceedances of health-based standards. This group met monthly from Aug 2023 and has also met regularly with local residents since this time to further understand the local perspective and to jointly develop measures to address ongoing traffic and air quality issues.
· AQAP4 Consultation – we consulted with the public and other groups to gather feedback specifically on air quality in York and on measures to improve air quality proposed in our updated Air Quality Action Plan (AQAP4).
Diffusion tubes used by CYC in 2023 were supplied and analysed by SOCOTEC (Didcot), Unit 12 Moorbrook, Southmead Industrial Park, Didcot, Oxfordshire, OX11 7HP. The preparation method used for the diffusion tubes was 50% TEA in Acetone.
Diffusion tube monitoring was completed in line with the 2023 Diffusion Tube Monitoring Calendar as available on DEFRA’s LAQM webpage.
AIR is an independent analytical proficiency-testing (PT) scheme, operated by LGC Standards and supported by the Health and Safety Laboratory (HSL). AIR PT is a new scheme, started in April 2014, which combines two long running PT schemes: LGC Standards STACKS PT scheme and HSL WASP PT scheme. AIR offers a number of test samples designed to test the proficiency of laboratories undertaking analysis of chemical pollutants in ambient indoor, stack and workplace air. For the 2023 period, the percentage of results submitted by SOCTEC that were deemed to be satisfactory was 100% for all rounds reported at the time of writing (rounds AR055 [Jan – Feb 2023], AR056 [May – June 2023], AR058 [July – Aug 2023] and AR059 [Sept – Oct 2023]). Further information about this scheme is available on the DEFRA webpage.
Removal of April 2023 diffusion tube data
Following a mid-year review of CYC’s 2023 diffusion tube dataset it was noticed that many of the April 2023 results appeared much lower than expected (compared with months either side and compared with April in previous years). CYC raised this with the supplying laboratory who were unable to offer a satisfactory explanation.
Upon further investigation it was also revealed that other local authorities who used the same laboratory had also noticed anomalous data for April 2023. Following advice received from the LAQM Helpdesk on 26th Sept 2023 (query reference 8960), a decision was taken to exclude all April 2023 results from the final data. This was considered the most open and transparent way to handle the anomalous data and was considered to reflect a worst case based on the following:
· The bias corrected annual mean for 221 of 232 tubes (excluding blank) increased (with April data removed)
· The bias corrected annual mean for 4 of 232 tubes remained unchanged (with April data removed)
· Of the remaining 7 tubes, the bias corrected annual means with and without April removed, were all within 0.3µg/m3 with the exception of one tube (C26) that was 0.8µg/m3. Across these 7 tubes the maximum bias corrected mean was 31µg/m3 (well within the annual mean NO2 objective).
Annualisation is required for any diffusion tube monitoring site with data capture less than 75% but greater than 25%. The process of annualisation scales the available monitoring data to provide an estimate of the annual mean nitrogen dioxide concentration. This can then be compared with health-based Air Quality Objectives.
CYC undertook background diffusion tube monitoring of nitrogen dioxide at a number of background locations during 2023. Of these sites, 53 diffusion tubes had 11 months data available (i.e. a full year’s worth of data, excluding April as described above) and have been used to derive the period to annual ratios required for the annualisation. This methodology has previously been agreed with the LAQM Helpdesk and is in line with the methodology used in all CYC’s previous Annual Status Reports. The following steps were used:
· Step 1 - Calculate the period mean for the diffusion tube sample requiring annualisation
· Step 2 - Calculate the corresponding period means and annual means for each of the 53 background diffusion tube locations. Use these two figures to calculate the period mean to annual mean ratio for each of the 53 background diffusion tube sites.
· Step 3 – Calculate the average ratio across the 53 background monitoring sites (i.e. n = 53)
· Step 4 – Use the ratio in Step 3 to adjust the period mean (Step 1) to provide an estimate of the annual diffusion tube mean (non-bias adjusted)
· Step 5 – Bias correct the value calculated in step 4 using the appropriate bias correction factor.
Seven diffusion tube sites required annualisation, namely 14, 111, 130, A54, C51, C53 and D22. The calculations and annualisation factors are provided in Table C.1. All annualised diffusion tube results are below the annual mean objective for nitrogen dioxide (note that site 14 is broadly equal to the objective at 39.9µg/m3).
Table C.1 – Annualisation Summary (concentrations presented in µg/m3)
Site ID |
Average Annualisation Factor |
Raw Data Annual Mean (µg/m3) |
Annualised Annual Mean (µg/m3) |
Bias Corrected Annualised Annual Mean (µg/m3) |
14 |
0.976 |
53.2 |
51.9 |
39.9 |
111 |
1.027 |
24.8 |
25.4 |
19.6 |
130 |
0.889 |
14.3 |
12.7 |
9.8 |
A54 |
1.069 |
34.6 |
37.0 |
28.5 |
C51 |
1.051 |
23.3 |
24.5 |
18.9 |
C53 |
0.802 |
27.1 |
21.7 |
16.7 |
D22 |
1.057 |
35.5 |
37.6 |
28.9 |
The diffusion tube data presented within the 2023 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.
CYC have applied local roadside and background bias adjustment factors of 0.77 and 0.78 respectively to the 2023 monitoring data. A summary of bias adjustment factors used by CYC over the past five years is presented in Table C.2.
For the purposes of this ASR, local bias adjustment factors have been calculated for diffusion tubes located at roadside and urban background locations separately. This is in line with the approach used by CYC for the last 15+ years and in line with advice from the LAQM Helpdesk obtained in previous reporting years. AEA’s Precision and Accuracy spreadsheet has been used to consider co-location studies at 3 York roadside locations (Fishergate, Gillygate and Fulford Road) and one York urban-background location (Bootham).
Roadside bias adjustment factor
Data capture and tube precision for 2023 was shown to be ‘good’ at all 3 roadside sites and the resultant combined/average bias factor across the 3 sites (following methodology in TG22 para 7.222) was 0.77. This factor has been used to correct diffusion tube results at roadside locations in 2023. The methodology used to derive the combined factor was:
· Step 1 - Average of Bias Factor B’s = (30+30+30)/3 = 30
· Step 2 - Express as a factor = 0.3
· Step 3 - Add 1 to this value = 0.3 + 1 = 1.3
· Step 4 - Take the inverse to give the bias adjustment factor = 1/1.3 = 0.77
Urban background bias adjustment factor
Data capture and tube precision for 2023 was shown to be ‘good’ at the Bootham urban background site. The bias factor for this site was calculated to be 0.78. This factor has been used to correct diffusion tube results at urban background locations in 2023.
Comparison with national bias adjustment factor
The overall 2023 bias correction factor from the national diffusion tube bias adjustment factor spreadsheet for SOCOTEC Didcot [preparation method 50% TEA in acetone] from 28 studies was 0.77. This is the suggested figure to use for all site types in the absence of any local collocation data. It was considered that the locally derived bias correction factors were comparable to this national figure. Historically, locally derived bias correction factors have always used for the correction of CYC’s diffusion tube data and the local figures have therefore been used for correction of tube data presented in this report. Local bias factors in 2023 are also comparable to factors calculated for previous years and reported in historical Annual Status Reports, shown in Table C.2.
As CYC’s locally derived bias factors of 0.77 (roadside) / 0.78 (background) are equal to or above the national factor of 0.77, this also represents a robust, worse case approach for adjustment of CYC’s diffusion tube data.
Table C.2– Bias Adjustment Factor
Monitoring Year |
Local or National |
If National, Version of National Spreadsheet |
Adjustment Factor |
2023 |
Local |
- |
Background tubes 0.78 Roadside tubes 0.77 |
2022 |
Local |
- |
Background tubes 0.73 Roadside tubes 0.73 |
2021 |
Local |
- |
Background tubes 0.72 Roadside tubes 0.75 |
2020 |
Local |
- |
Background tubes 0.68 Roadside tubes 0.74 |
2019 |
Local |
- |
Background tubes 0.76 Roadside tubes 0.74 |
Table C.3– Local Bias Adjustment Calculation
|
Local Bias Adjustment Input 1 – Bootham (Urban Background) |
Local Bias Adjustment Input 2 – Fishergate (Roadside) |
Local Bias Adjustment Input 3 – Gillygate (Roadside) |
Local Bias Adjustment Input 4 – Fulford (Roadside) |
Periods used to calculate bias |
9 |
10 |
9 |
8 |
Bias Factor A |
0.78 (0.75 – 0.8) |
0.77 (0.72 – 0.82) |
0.77 (0.68 – 0.88) |
0.77 (0.74 – 0.8) |
Bias Factor B |
29% (25% - 33%) |
30% (21% - 38%) |
30% (13% - 47%) |
30% (25% - 36%) |
Diffusion Tube Mean (µg/m3) |
14 |
22 |
32 |
22 |
Mean CV (Precision) |
5 |
8 |
4 |
5 |
Automatic Mean (µg/m3) |
11 |
17 |
24 |
17 |
Data Capture |
99% |
98% |
98% |
99% |
Adjusted Tube Mean (µg/m3) |
11 (11 – 11) |
17 (16 – 18) |
24 (22 – 28) |
17 (16 – 18) |
Notes:
A single local bias adjustment factor of 0.78 has been used to bias adjust the 2023 diffusion tube results at urban background locations.
A combined local bias adjustment factor of 0.77 has been used to bias adjust the 2023 diffusion tube results at roadside locations.
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 has been considered at monitoring sites where the annual mean concentration is greater than 36µg/m3 and the monitoring site is not located at a point of relevant exposure (taking the limitations of the calculator into account). In 2023, 10 diffusion monitoring sites recorded bias corrected annual mean concentrations in excess of 36µg/m3, namely site references 7, 13, 14, 109, 115, A1, C27, D51, D55 and D59. Further commentary on each of these sites us provided in Table C.4.
Table C.4– Non-Automatic NO2 Fall off With Distance Calculations (concentrations presented in µg/m3)
Site ID |
Distance (m): Monitoring Site to Kerb |
Distance (m): Receptor to Kerb |
Monitored Concentration (Annualised and Bias Adjusted |
Background Concentration |
Concentration Predicted at Receptor |
Comments |
7 |
0.3 |
2.6 |
41.7 |
13.0 |
31.6 |
See calculation to left. Site located within current AQMA |
13 |
1.5 |
1.6 |
39.8 |
- |
- |
Location considered relevant without correction as mounted on a drainpipe attached to facade of building. Site located within current AQMA |
14 |
2.3 |
2.5 |
39.9 |
- |
- |
Location considered relevant without correction as mounted on a drainpipe attached to facade of building. Site located within current AQMA |
109 |
2.5 |
2.7 |
36.6 |
- |
- |
Location considered relevant without correction as mounted on a drainpipe attached to facade of building. Site located within current AQMA |
115 |
1.5 |
N/A |
45.0 |
- |
- |
Not relevant location with respect to annual mean as located at a bus stop. Only relevant with respect to hourly NO2 objective, but currently under 60µg/m3 so not of concern. Nevertheless, site located within current wider AQMA |
A1 |
2.3 |
2.5 |
42.6 |
- |
- |
Location considered relevant without correction as mounted on a drainpipe attached to facade of building. Site located within current AQMA |
C27 |
3.2 |
3.4 |
37.1 |
- |
- |
Location considered relevant without correction as mounted on a drainpipe attached to facade of building. Site located within current AQMA |
D51 |
N/A |
N/A |
40.4 |
- |
- |
Not relevant location with respect to annual mean as located at taxi rank, within railway station portico. Only potentially relevant with respect to hourly NO2 objective, but currently under 60µg/m3 so not of concern. |
D55 |
2.2 |
4.0 |
37.1 |
13.0 |
33.6 |
See calculation to left. Site located within current AQMA |
D59 |
2.7 |
4.5 |
37.5 |
13.0 |
34.3 |
See calculation to left. Site located within current AQMA |
To ensure that the air quality data collected by CYC fully complies with the requirements of the Review and Assessment process, a comprehensive set of QA/QC procedures are in place. The aims of the QA/QC programme were fully detailed in ‘Technical Annex 2: Air Pollution Monitoring in York’ which was submitted with the Second and Third Stage Review and Assessment of Air Quality in York.
All roadside automatic monitoring sites are calibrated fortnightly by CYC’s Public Protection Team. The Bootham urban background monitoring site is calibrated 4-weekly in line with AURN requirements. Sites are serviced by the equipment suppliers every 6 months and independently audited every 12 months. The annual audit also provides an independent check of site cylinder concentrations against reference standards. The latest round of station audits was carried out in January 2024 by Ricardo-AEA.
CYC’s continuous monitoring sites are currently serviced and maintained by ‘Matt’s Monitors’. Data management is currently undertaken by Ricardo-AEA with all results being published to the Air Quality England website. This website displays live and historical data for all automatic monitoring sites in York. All data presented in this ASR is fully ratified.
For Holgate Road and Plantation Drive TEOM (PM10) data in 2023 a correction factor of 1.3 has been applied (INDIC.GRAV) due to lack of nearby TEOM-FDMS data for VCM correction.
Gillygate PM2.5 data was collected as uncorrected TEOM data between 1st Jan 2023 – 1st Aug 2023 (as the VCM is not considered appropriate for correction of PM2.5 data). The PM2.5 monitor at Gillygate was upgraded in August 2023 to TEOM-FDMS (equivalent to the reference method without correction). Annual averages presented in this report for Gillygate PM2.5 utilise both data sets.
Holgate PM2.5 data was collected as TEOM-FDMS from 11th July 2023. This was a new monitor to replace the previous TEOM (PM10).
No correction factors have been applied to the BAM data presented in this report (Bootham and Fishergate) as this is this monitoring method provides reference method equivalent data.
In 2023, data capture for Holgate Road for automatic monitoring of PM10 and PM2.5 was less than 75% (due to the PM10 analyser being upgraded to a PM2.5 analyser mid-year). Data capture rates for PM10 and PM2.5 were 50.4% and 45.0% respectively.
Annualisation for PM10 and PM2.5 has been carried out in line with LAQM.TG22 and is summarised below. In summary, three nearby AURN background sites measuring the required pollutants and with the necessary data capture were available to derive an average annualisation factor.
Site ID |
Annualisation Factor – York Bootham |
Annualisation Factor – High Muffles |
Annualisation Factor – Leeds Centre |
Average Annualisation Factor |
Raw Data Annual Mean (µg/m3) |
Annualised Annual Mean (µg/m3) |
Holgate PM10 |
0.997 |
0.867 |
0.913 |
0.926 |
18.1 |
16.8 |
Holgate PM2.5 |
1.115 |
1.356 |
1.164 |
1.211 |
6.4 |
7.8 |
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. No automatic NO2 monitoring locations within CYC’s area required distance correction during 2023.
Figure D.1– Map of Non-Automatic Monitoring Site
Due to the number of tubes operated by City of York Council, an interactive diffusion tube map showing tube reference numbers has been made available online to accompany the 2024 ASR. View interactive diffusion tube map here. Expanded views showing diffusion tube locations across all areas of the AQMA are shown on the following pages.
Expanded views of diffusion tube locations in relation to the AQMA boundary:
Figure D.2 - Map of Automatic Monitoring Sites in relation to AQMA
Air Quality Management Area (AQMA) shown in red. Precise locations of automatic monitors are shown online at the Air Quality England website.
Table E.1 – Air Quality Objectives in England[9]
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 |
EU |
European Union |
FDMS |
Filter Dynamics Measurement System |
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 |
· Local Air Quality Management Technical Guidance LAQM.TG22. August 2022. Published by DEFRA in partnership with the Scottish Government, Welsh Assembly Government and Department of the Environment Northern Ireland.
· Local Air Quality Management Policy Guidance LAQM.PG22. August 2022. Published by DEFRA in partnership with the Scottish Government, Welsh Assembly Government and Department of the Environment Northern Ireland.
· Chemical hazards and poisons report: Issue 28. June 2022. Published by UK Health Security Agency
· Air Quality Strategy – Framework for Local Authority Delivery. August 2023. Published by DEFRA.
· City of York Council’s previous LAQM Review and Assessment reports can be found on City of York Council’s website
[1] UK Health Security Agency. Chemical Hazards and Poisons Report, Issue 28, 2022.
[2] DEFRA. Air quality and social deprivation in the UK: an environmental inequalities analysis, 2006
[3] Tube 115 located at a bus stop and therefore not a relevant location with respect to annual mean NO2 objective
[4] DEFRA. Environmental Improvement Plan 2023, January 2023
[6] DfT. The Road to Zero: Next steps towards cleaner road transport and delivering our Industrial Strategy, July 2018
[7] DEFRA. Air Quality Strategy – Framework for Local Authority Delivery, August 2023
[8] Tube 115 located at a bus stop and therefore not a relevant location with respect to annual mean NO2 objective
[9] The units are in microgrammes of pollutant per cubic metre of air (µg/m3).