SWT Air quality annual status report 2019 - West Somerset · LAQM Annual Status Report 2019 v . The...
Transcript of SWT Air quality annual status report 2019 - West Somerset · LAQM Annual Status Report 2019 v . The...
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Somerset West and Taunton Council
LAQM Annual Status Report 2019
2019 Air Quality Annual Status Report (ASR) In fulfilment of Part IV of the Environment Act 1995 Local Air Quality Management January 2020
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Somerset West and Taunton Council
LAQM Annual Status Report 2019
Local Authority Officer Matthew Hill
Department Environmental Health
Address The Deane House, Belvedere Road, Taunton TA1 1HE
Telephone 0800 304 8000
E-mail [email protected]
Report Reference number SWT ASR 2019
Date January 2020
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LAQM Annual Status Report 2019 i
Executive Summary: Air Quality in Our Area Air Quality in Somerset West and Taunton Air pollution is associated with a number of adverse health impacts. It is recognised as
a contributing factor in the onset of heart disease and cancer. Additionally, air pollution
particularly affects the most vulnerable in society: children and older people, and those
with heart and lung conditions. There is also often a strong correlation with equalities
issues, because areas with poor air quality are also often the less affluent areas1,2.
The annual health cost to society of the impacts of particulate matter alone in the UK
is estimated to be around £16 billion3.
Somerset West & Taunton Council covers the whole of the former West Somerset
Council and Taunton Deane Borough Council areas. The new Council area is a mixed
urban and rural district within Somerset, covering 459.5 square miles and serving a
population of just under 150,000. There are approximately 65,000 households and
over 6,000 businesses within the area. The local economy is underpinned by jobs in
public services; professional and other private services; tourism; wholesale and retail;
and accommodation, food services and recreation. Construction will account for a
larger percentage of jobs now that construction works at Hinkley Point C are under
way. There are four major roads, the M5 motorway and A38, the A358 trunk road and
the A39. Parts of Taunton get congested during peak times. Parts of the strategic road
network along the A38 and A358 also get severally congested when accidents close
the M5.
The main source of air pollution in the area is road traffic, and monitoring of a number
of pollutants over the years has found that nitrogen dioxide is the main pollutant of
concern. There are no major industrial sources of pollution in the area. There are
emissions associated with solid fuel appliances. Because large parts of the area is not
on mains gas the district has the largest number of boilers burning biomass (wood)
1 Environmental equity, air quality, socioeconomic status and respiratory health, 2010 2 Air quality and social deprivation in the UK: an environmental inequalities analysis, 2006 3 Defra. Abatement cost guidance for valuing changes in air quality, May 2013
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LAQM Annual Status Report 2019 ii
fuel in Somerset. The principal pollutants from burning wood are nitrogen dioxide (NO2)
and particulate matter of less than 10 microns (PM10 and PM2.5).
For new emission sources, Hinkley Point-C remains the largest development of
potential impact on air quality in the area. Consent was granted in March 2013 to build
and operate two nuclear European Pressurised Reactors (EPR) at Hinkley Point C and
works started in September 2015. The principal pollutants associated with this site are
from particulate matter emissions associated with the construction activities (on-going),
traffic entering the site and once operational emissions from associated diesel backup
generators (35 MW capacity).
There are two Air Quality Management Areas (AQMAs) in the district, one on the A358
trunk road in Henlade and one at East Reach, a main road on the edge of the town
centre in Taunton. Both have been declared due to elevated levels of nitrogen dioxide.
Action Plans have been prepared to try and improve air quality in the AQMAs (and
across the District as a whole); some details are included in this report and further
information can be found on the Councils website at
https://www.somersetwestandtaunton.gov.uk/environmental-health/environmental-
protection/air-quality/
Monitoring of nitrogen dioxide (NO2) has been carried out at 52 locations across the
District using diffusion tubes. These are changed every month and can be used to
record the annual average level of NO2. The monitoring locations have been reviewed,
in 2016 monitoring started in four new sites within the AQMAs, two in Henlade and two
in East Reach. In January 2018 a decision was made to cease monitoring at five sites
where the levels had been consistently low for many years.
The results of the diffusion tube monitoring for 2018 show an increase in nitrogen
dioxide levels at all sites when compared to the results from 2017. However, the 2018
levels are similar to those that have been monitored in previous years, and it should
be noted that levels of NO2 can vary due to a number of factors, including the weather
Therefore, it is best to look at long term trends rather than results for individual years.
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The results showed exceedances of the air quality objective for nitrogen dioxide at five
locations, two in the Henlade AQMA, two in the East Reach AQMA and one just outside
the East Reach AQMA. The objective is an annual mean of 40 µg/m3 and the levels
measured at the sites was between 44 and 54 µg/m3. When these results were
corrected for the distance to the nearest sensitive receptors they were between 43 and
48 µg/m3. (Details are in Appendix A)
Somerset West and Taunton Council is working with the other district Councils in
Somerset, and Somerset County Council to update the Somerset Air Quality Strategy.
The aim is to achieve a consistent approach to air quality across the County and to
provide a link to wider initiatives such as local transport plans.
Actions to Improve Air Quality The main source of pollution in Somerset West and Taunton is from vehicle emissions.
The Council’s action plan includes monitoring of air quality, and initiatives to try and
reduce traffic in areas of poor air quality and to restrict increases in traffic as a result
of new development. Actions taken over the last year include:
• Highways England have announced their preferred route for the A358
Expressway. When completed it is predicted that this could result in a reduction
in traffic through Henlade from 33,500 to 4,000 vehicles per day, potentially
removing the need for an AQMA.
• Continued monitoring of nitrogen dioxide levels using diffusion tubes
• Implementation of the first part of the trial pedestrianisation in Taunton town
centre, with plans to extend this to further streets.
• Introduction of Variable Message Signage for car parks in Taunton.
• The Council has obtained “Garden Town” status for Taunton, which should
allow access to additional funding to support planning work to deliver the
Garden Town Principles.
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LAQM Annual Status Report 2019 iv
• Somerset West and Taunton Council has declared a Climate Emergency which
includes a resolution to enable more cycling, walking and use of public
transport.
• Ensuring that air quality assessments are required for new roads or
developments that could affect the AQMAs
• As part of the design of new developments the Council is ensuring the provision
of new Green Wedges which will serve as “green lungs” providing attractive
corridors for walking and cycling into the town centre and beyond to open
countryside.
• After Somerset County Council announced plans to suspend the Taunton Park
and Ride service in 2018, Taunton Deane Borough Council and then Somerset
West and Taunton Council stepped in with financial contributions, which at
present keep the service open until April 2020 and reintroduced a Saturday
service.
Conclusions and Priorities The exceedances of the national Air Quality Objectives at the monitoring locations
within the two AQMAs, confirm that they still need to be in place. Monitoring will
continue to be carried out within the AQMAs to provide more data.
Somerset West and Taunton Council’s priorities for the coming year are:
• Continuing with the implementation of the pedestrianisation of the town centre
• Trying to secure the long term funding of the Park and Ride service
• Working with Highways England to help ensure that the implementation of the
A358 scheme fits with the Council’s existing development policies and leads to
improvements in the local environment.
• Preparing the Local Cycling and Walking Infrastructure Plan
• As part of the design of new developments the Council is ensuring the provision
of new Green Wedges which will serve as “green lungs” providing attractive
corridors for walking and cycling into the town centre and beyond to open
countryside.
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The principal challenges and barriers to implementation that Somerset West and
Taunton Council anticipates facing are:
• Current policy, both national and locally, seeks to deliver major new housing
growth and there are plans to attract new business to the area. New houses and
businesses will mean an increase in traffic, as Somerset West and Taunton is
a rural area, without the public transport infrastructure of large towns or cities
• It is very difficult to restrict access to the roads within the AQMAs as they are
both through-roads.
While Somerset West and Taunton Council can take some action to try and improve
air quality in the District it is likely that the large amount of development in the area will
lead to an increase in traffic across the District.
To actually reduce traffic levels (rather than manage the expected increase) the
agencies responsible for the roads (Somerset County Council and Highways England)
would have to make hard changes to road layouts and infrastructure to encourage
alternatives to car use, by making cycling, walking and public transport a more
attractive alternative. However, this will mean that the authorities will have to accept
that some schemes will reduce the priority and space given to cars and other vehicles.
Also, this work will require funding, which can be difficult to obtain.
Therefore, to be able to meet air quality objectives the Council is likely to have to rely
on the support of other agencies, for example, Highways England to ensure the
proposed re-routing of the A358 can reduce traffic levels in the Henlade AQMA, and
national government to continue to regulate to reduce vehicle exhaust emissions.
Local Engagement and How to get Involved Everyone in Somerset West and Taunton can try to help improve air quality by trying
to use alternatives to driving where possible.
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Somerset County Council has information on their Travel Somerset webpages which
aims to reduce congestion and pollution by helping people to explore sustainable
transport options. More information can be found at
https://www.travelsomerset.co.uk/about/
Information on alternative means of transport for specific areas has also been
produced and can be found at Getting Around Somerset.
https://www.travelsomerset.co.uk/getting-around/
Information on Somerset West and Taunton Council’s air quality monitoring and
reporting can be found on the Council’s website at
https://www.somersetwestandtaunton.gov.uk/environmental-health/environmental-
protection/air-quality/
https://www.travelsomerset.co.uk/about/https://www.travelsomerset.co.uk/getting-around/https://www.somersetwestandtaunton.gov.uk/environmental-health/environmental-protection/air-quality/https://www.somersetwestandtaunton.gov.uk/environmental-health/environmental-protection/air-quality/
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LAQM Annual Status Report 2019 vii
Table of Contents Executive Summary: Air Quality in Our Area .......................................................... i
Air Quality in Somerset West and Taunton ............................................................. i
Actions to Improve Air Quality ................................................................................ iii
Conclusions and Priorities ...................................................................................... iv
Local Engagement and How to get Involved ........................................................... v
1 Local Air Quality Management ........................................................................ 1 2 Actions to Improve Air Quality ........................................................................ 2
2.1 Air Quality Management Areas .................................................................... 2
2.2 Progress and Impact of Measures to address Air Quality in Somerset
West and Taunton .................................................................................................. 5
2.3 PM2.5 – Local Authority Approach to Reducing Emissions and/or
Concentrations ..................................................................................................... 15
3 Air Quality Monitoring Data and Comparison with Air Quality Objectives and National Compliance .................................................................... 17
3.1 Summary of Monitoring Undertaken .......................................................... 17
3.11 Non-automatic monitoring
3.2 Individual Pollutants ................................................................................... 17
3.2.1 Nitrogen Dioxide (NO2) ........................................................................ 17
Appendix A: Monitoring Results ........................................................................... 21 Appendix B: Full Monthly Diffusion Tube Results for 2017 ................................ 31 Appendix C: Supporting Technical Information / Air Quality Monitoring Data QA/QC ............................................................................................................. 34 Annualisation of monthly results for NOx tubes
NOx tubes. Bias adjustment
Distance correction calculations
Historic PM10 monitoring data
Appendix D: Map(s) of Monitoring Locations and AQMAs ..... Error! Bookmark not defined.8 Appendix E: Summary of Air Quality Objectives in England .............................. 42 Glossary of Terms .................................................................................................. 43 References .............................................................................................................. 44
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List of Tables Table 2.1 – Declared Air Quality Management Areas .................................................. 4
Table 2.2 – Progress on Measures to Improve Air Quality ........................................ 13
Table A.1 – Details of Non-Automatic Monitoring Sites ............................................. 21
Table A.2 – Annual Mean NO2 Monitoring Results .................................................... 25
Table B.1 – NO2 Monthly Diffusion Tube Results - 2018 ........................................... 31
Table E.1 – Air Quality Objectives in England ........................................................... 42
List of Figures Figure 1 – Plan of Air Quality Management Area in East Reach …………………... 2
Figure 2 – Plan of Air Quality Management Area in Henlade ................................ 3
Figure 3 - A358/A303 Consultation, proposed routes ……………………….……. 9
Figure 4 – The Preferred Route for the A358 …………………………………………..10
Figure A.1 – Trends in Annual Mean NO2 Concentrations ………………………….. 30
Figure D1 - East Reach AQMA and monitoring sites ………………………………… 38
Figure D2 - Henlade AQMA and monitoring sites …………………………………… 38
Figure D3 - Monitoring sites in Taunton town centre ……………………………….. 39
Figure D4 - Monitoring sites in Taunton east and Henlade …………………………. 39
Figure D5 - Monitoring sites in Wellington …………………………………………….. 40
Figure D6 - Monitoring sites in Williton and Washford ………………………………. 40
Figure D7 – Monitoring sites in Minehead …………………………………………… 41
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LAQM Annual Status Report 2019 1
1 Local Air Quality Management
This report provides an overview of air quality in Somerset West and Taunton during
2018. It fulfils the requirements of Local Air Quality Management (LAQM) as set out
in Part IV of the Environment Act (1995) 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
pursuit of the objectives. This Annual Status Report (ASR) is an annual requirement
showing the strategies employed by Somerset West and Taunton Council to improve
air quality and any progress that has been made.
The statutory air quality objectives applicable to LAQM in England can be found in
Appendix E.
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LAQM Annual Status Report 2019 2
2 Actions to Improve Air Quality 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 must
prepare an Air Quality Action Plan (AQAP) within 12-18 months setting out measures
it intends to put in place in pursuit of compliance with the objectives.
A summary of AQMAs in Somerset West and Taunton Council can be found in Table
2.1. Plans of the AQMAs are in figures 1 and 2. Maps showing the location of
monitoring sites within of close to the AQMAs are in Appendix D.
Figure 1. Plan of AQMA in East Reach, Taunton
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LAQM Annual Status Report 2019 3
Figure 2. Plan of AQMA in Henlade
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Table 2.1 – Declared Air Quality Management Areas
AQMA
Name
Date of Declarat
ion
Pollutants and
Air Quality Objecti
ves
City / Town
One Line Description
Is air quality in the AQMA influenced by roads
controlled by Highways
England?
Level of Exceedance (maximum
monitored/modelled concentration at a location
of relevant exposure)
Action Plan
At Declaration Now Name Date of Publication Link
AQMA
East Reac
h
2003 NO2
annual mean
Taunton
An area encompassing a number of
residential properties at
the western/town centre end of East Reach, a
busy main road through
Taunton.
NO
50 μgm-3 (Monitored 2002)
Predicted 2005 47 μgm-3
μgm-3 40
μgm-3
2013 Air Quality
Progress Report
and Action Plan
2013 Has been updated
with each annual report
www.somersetwestandt aunton.gov.uk/e nvironmental-
health/environmental-protection/air-quality/
AQMA
Henlade
2003 NO2
annual mean
Henlade
Taunton
An area covering
some residential properties
that are close to the
carriageway of the A358, a
trunk road between the M5 and the
A303.
YES
52 μgm-3 (monitored 2002). Predicted for 2005
46 μgm-3
μgm-3 35
μgm-3
2013 Air Quality
Progress Report
and Action Plan
2013 Has been updated
with each annual report
www.somersetwestandt aunton.gov.uk/e nvironmental-
health/environmental-protection/air-quality/
☐ Somerset West and Taunton Council has sent information to UK-Air regarding their AQMAs as the website had not been updated with the details ofthe new local authority.
https://www.somersetwestandt aunton.gov.uk/e nvironmental-health/environmental-protection/air-quality/https://www.somersetwestandt aunton.gov.uk/e nvironmental-health/environmental-protection/air-quality/
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2.2 Progress and Impact of Measures to address Air Quality in Somerset West and Taunton
Somerset West and Taunton Council is a new authority and so has not submitted any
air quality reports to Defra. However, reports were submitted in 2018 and previous
years by both Taunton Deane Borough Council and West Somerset Council which
covered the same area as the new authority. The two Air Quality Management Areas
were both in the Taunton Deane area.
Defra’s appraisal of last year’s ASR reports concluded that both were well structured,
detailed, and provided the information specified in the Guidance. For the Taunton
Deane report it noted the continuing exceedances, particularly within the Henlade
AQMA linked to the A358 trunk road, and within the East Reach AQMA. The report
provided a good discussion on local developments that may impact future air quality,
most notably the A358 upgrade between the A303 and the M5. It noted that the Action
Plan has been updated periodically.
Some additional comments were made
• Many established monitoring sites have a history of recorded concentrations
far below objective limits, and these resources could be redeployed
elsewhere.
• The report could draw further links between PM2.5 and the Public Health
Outcomes Framework.
• The results of the Highways England report for the A358 upgrade could be
incorporated into the next report
It is accepted that the location of the monitoring sites needs to be reviewed. This has
not happened for the start of 2020, but it is planned to review the sites during the
coming year
Additional information on PM2.5 is included in Section 2.5 of this report.
Highways England have now announced their preferred route for the A358, which
should result in a large reduction in traffic using the A358 through the AQMA in
Henlade. More information is given at the end of this section.
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Somerset West and Taunton Council has taken forward a number of direct measures
during the current reporting year of 2019 in pursuit of improving local air quality. Details
of all measures completed, in progress or planned are set out in Table 2.2.
Key completed measures are
• Highways England have announced their preferred route for the A358
Expressway, which could result in a reduction in traffic through Henlade from
33,500 to 4,000 vehicles per day, potentially removing the need for an AQMA.
Although no timescales have been given for completion of the scheme.
• Implementation of the first part of the trial pedestrianisation in Taunton town
centre, with plans to extend this to further streets.
• Introduction of Variable Message Signage for car parks in Taunton. Became
operational in January 2019, along with pay on exit car parks.
• The Council has obtained “Garden Town” status for Taunton, which should
allow access to additional funding to support planning work to deliver the
Garden Town Principles.
• Somerset West and Taunton Council has declared a Climate Emergency which
includes a resolution to enable more cycling, walking and use of public
transport.
• Continued monitoring of air quality, in the District, including sites within the two
Air Quality Management Areas in the District.
Somerset West and Taunton expects the following measures to be completed over the
course of the next reporting year:
• Securing the long term funding of the Park and Ride service. After Somerset
County Council announced plans to suspend the Taunton Park and Ride service
in 2018, Taunton Deane Borough Council and then Somerset West and
Taunton Council stepped in with financial contributions. At present these keep
the service open until April 2020 and have reintroduced a Saturday service. It is
proposed to extend the conditional funding until September 2020 and to report
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LAQM Annual Status Report 2019 7
on the options for placing the Park and Ride service on a long term sustainable
future in late 2020.
• Preparing the Local Cycling and Walking Infrastructure Plan and associated
schemes. The Council is also working on a funding bid to central government
for the Future High Streets Fund, which includes proposals to develop 3 town
centre cycle routes. Somerset County Council are bidding for funding from the
Local Pinch Point Fund to improve a cycle route across Taunton.
Somerset West and Taunton Council’s priorities for the coming year are
• Trying to secure the long term funding of the Park and Ride service
• Working with Highways England to help ensure that the implementation of the
A358 scheme fits with the Council’s existing development policies and leads to
improvements in the local environment.
• Preparing the Local Cycling and Walking Infrastructure Plan and associated
schemes..
• Continuing with the implementation of the pedestrianisation of the town centre
• As part of the design of new developments the Council is ensuring the provision
of new Green Wedges which will serve as “green lungs” providing attractive
corridors for walking and cycling into the town centre and beyond to open
countryside.
The principal challenges and barriers to implementation that Somerset West and
Taunton Council anticipates facing are:
• Current policy, both national and locally, seeks to deliver major new housing
growth and there are plans to attract new business to the area. There is existing
planning permission for several thousand new houses in Taunton, mainly on
greenfield sites to the north and east, and hundreds of houses in Wellington
eight miles to the west of Taunton. Other areas around Taunton are outlined for
development in the Council’s Local Plan. Somerset West and Taunton is a rural
area, and people often have to travel to a different town for work or other
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LAQM Annual Status Report 2019 8
activities. The county does not have the public transport infrastructure of larger
towns or cities and so many people rely on their cars. Although both SWT and
SCC will try to encourage alternatives to car use through the planning process,
new houses and businesses will mean an increase in traffic. This is reflected in
the statement on Air Quality in Somerset County Council’s Future Transport
Plan 2011 “HLT3 - We will work to minimise the effect any changes to
Somerset’s transport systems will have on air pollution”.
• Some local authorities have improved air quality by restricting the vehicles that
can enter AQMAs or other areas, for example, by implementing low emission
zones. Both of the roads within the AQMAs in Somerset West and Taunton are
through-roads which would make it very difficult to restrict access. The A358 in
Henlade is a major trunk road managed by Highways England; East Reach is a
route across Taunton, as well as a road into town centre; if it was restricted,
through traffic would have to divert a mile or two around the town (causing an
increase in traffic on other busy roads) or try and cut through residential streets.
Progress on the following measures has been slower than expected:
• The trial pedestrianisation of Taunton town centre was delayed to allow further
consultation with local businesses and other agencies. The first phase has been
implemented and the impact is being monitored, however, there is no set date
for implementation of the next phase.
Regarding the Henlade AQMA, the proposal from Highways England for the re-routing
of the A358 is likely to achieve compliance in the Henlade AQMA once it has been
completed. However, there is no confirmation on when work will start on the scheme.
Regarding the East Reach AQMA, whilst the measures stated above and in Table 2.2
will help to contribute towards compliance, Somerset West and Taunton Council
anticipates that further additional measures not yet prescribed will be required in
subsequent years to achieve compliance and enable the revocation of East Reach
AQMA
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LAQM Annual Status Report 2019 9
A358 re-routing scheme
One of the main developments that could affect the local air quality is the proposed
dualling and re-routing of a stretch of the A358 between the M5 motorway at Taunton
and the A303. This is part of the proposal for the strategic improvement to the
A303/A30 trunk road (linking London the South West). Currently traffic on the
A303/A30 passes from the A303 in South Somerset along a single lane route into
Devon and then on to Exeter and the rest of South West. The proposal is to make the
A358 between the A303 in South Somerset and the M5 at Taunton a limited junction
dual carriageway, with the aim to encourage traffic to use the new A358/M5 route
instead of the existing route.
The consultation in 2018 had three proposed routes (pink, blue and orange)
Figure 3 A358, Taunton, routes for consultation
The route proposed after the consultation was actually a revised version of one of the
proposed options. (See Figure 4 below)
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LAQM Annual Status Report 2019 10
Figure 4. The preferred route for A358 (Pink modified option)
The Scheme Assessment Report estimates that the proposed route could result in a
reduction in traffic through Henlade from 33,500 to 4,000 vehicles per day. This is likely
to lead to a reduction in pollutant levels and the opportunity to revoke the Henlade
AQMA.
However, the proposed road would lead to an increase in traffic in the area as drivers
will be encouraged to use the new A358/M5 route between the A303 and the South
West, rather than the existing A303/A30 through East Devon.
Highways England have not provided details of the course of the proposed route. They
have stated that they are continuing to carry out additional surveying work and are in
the process of appointing a designer to take the scheme through the statutory phase
and into construction. When more details of the route are know the Council will look at
siting some of the NOx monitoring tubes at locations on the proposed route to be able
to provide information on the impact of the scheme.
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LAQM Annual Status Report 2019 11
HInkley Point C development
The building of two European Pressurised Reactors (EPR) at Hinkley Point C is one of
the largest construction projects in the country. Work started in 2015 and is on-going.
The principal pollutants associated with this site are particulate matter emissions from
construction activities, emissions from traffic accessing the site and, once operational,
emissions from associated diesel backup generators (35 MW capacity).
Planning obligations have been agreed for the site, which include a scheme to monitor
the dust, particulate matter and noise outside the southern boundary, at locations close
to residential properties. There are four automatic monitoring stations that analyse
and report on PM10, PM2.5 and TSP, with trigger levels set for PM10 200ug/m3 for 15min
and 1-hr. If concentrations exceed these trigger levels it requires actions by EDF and,
if prolonged, notification to this Council. The scheme is intended to prevent complaints
about particulate matter and dust, rather than to quantify results suitable for this review
and assessment work as they are considered non-reference.
Given the scale of the development at Hinkley Point C, the following actions have been
agreed by both West Somerset Council (now Somerset West and Taunton Council)
and neighbouring Sedgemoor Council;
• To limit the parking on site to reduce need for travel to and from the site
• Construction of four park and ride facilities (one in West Somerset and other
three in Sedgemoor). The site in West Somerset (Williton) is still to be
completed.
• New campus type development (opened in 2018) to house employees on site
consisting of 510 modular bed space accommodation and with associated
parking. This will reduce need to travel to the site.
• Freight consolidation facilities located in Sedgemoor at junctions off the M5 to
ensure deliveries are bulked to help reduce overall number of vehicles travelling
into the site. Whilst this is within the neighbouring authority (Sedgemoor) it will
help to ensure HGV movements do not travel through the western approach
(West Somerset)
• Construction of a jetty to transport construction materials e.g. aggregates
• A by-pass around Cannington, Sedgemoor (already completed)
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LAQM Annual Status Report 2019 12
• Grants for local housing improvements e.g. housing improvements that
potentially reduce emissions from heating.
• Contingency funding where necessary, for additional air quality monitoring
owing to the predicted additional traffic flows occurring in West Somerset. The
total predicted additional vehicles through Williton as a result of the Hinkley
Point development was predicted as 827 vehicles per day at all scenarios
modelled.
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LAQM Annual Status Report 2019 13
Table 2.2 – Progress on Measures to Improve Air Quality
Measure No. Measure
EU Category
EU Classification
Organisations involved and
Funding Source
Planning Phase
Implementation Phase
Key Performance
Indicator
Reduction in Pollutant /
Emission from Measure
Progress to Date Estimated /
Actual Completion
Date
Comments / Barriers to implementation
1
By-pass for
Henlade as part of
the A303/A35
8 expressw
ay
Transport Managem
ent
Strategic Highway
Improvements
Highways England (HE) Government
funding
. Preferred route
announced June 2019
To be confirmed. Subject
Development Consent Order
Process
Road completed and chosen route does reduce
traffic levels in AQMA
Highways England have
not yet provided details of their
air quality assessment
Consultation phase Not known
Preferred route reduces traffic flows
through Henlade from 33,500 to 4,000 vehicles per day.
Potentially removes the AQMA
2
Trial pedestrianisation of
town centre roads
Alternatives to
private vehicle
use
Other SCC with
funding from SWT
St James St trial
commenced May
19. Plans to also
trial East St, and
Hammet St
Started summer 2019
Reduction in town centre
traffic. (although
could affect traffic on
nearby roads, including the East Reach
AQMA)
Data on potential
change in traffic flows are not
yet available, so not able to estimate emission reduction.
On-going No known
Implementation was delayed after a
consultation. Will be an 18 month trial. Traffic levels in surrounding
roads will be monitored
3
Enhanced pedestrian and cycle
links in new
developments
Promoting Travel
Alternatives
Promotion of cycling and
walking
SWT/ Developer funding via planning process
On-going On-going
Hard to set a measurable
target, however, this
is being carried out at
most new developments
N/A (proposals try to minimise the increase in emissions that will come from
new developments)
On-going On-going
SWT has obtained "Garden Town" status
for Taunton which could allow access to
additional funding. SWT declared a
Climate Emergency (Feb 19). Resolution
involves enabling more cycling, walking and use of shared and public transport.
4
Air quality assessme
nt required
for developm
ents
Transport Planning
and Infrastruct
ure
Other SWT and SWT funded Completed Completed
Each relevant planning
application includes an air
quality assessment.
Has been met
N/A (proposals try to minimise the increase in emissions that will come from
new developments)
On-going On-going
Liaison between Environmental Health
and Planning Departments and SCC
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LAQM Annual Status Report 2019 14
Measure No. Measure
EU Category
EU Classification
Organisations involved and
Funding Source
Planning Phase
Implementation Phase
Key Performance
Indicator
Reduction in Pollutant /
Emission from Measure
Progress to Date Estimated /
Actual Completion
Date
Comments / Barriers to implementation
affecting the
AQMAs
5 Park and Ride
Alternatives to
private vehicle
use
Bus based park and ride
SCC and SWT operated and
funded On-going
After SCC announced
plans to suspend the
service in 2018. TDBC and then SWT stepped in
with financial contributions. The current contribution keeps the
service open until April 2020
and reintroduces a Saturday
service.
Increased use of existing
park and ride sites.
Additional Park and Bus
sites being considered as
part of new garden
communities being
implemented at Monkton
Heathfield and Comeytrowe
Between 2015 and 2017, patronage
increased from 800 to 840
vehicles a day. Patronage increased
further by just under 2%
between March 2018 and March
2019. No information on what drivers would have
done if no P&R so not possible
to estimate emission reduction
SCC / SWT reviewing management of
existing service & sites. SWT Exec July 2019 approved £20k
to explore further measures to attempt
to secure the long term funding of the
P&R service.
On-going
Taunton P&R Service is a key component in
the regeneration / pedestrianisation plans
for Taunton town centre. Use of P&R
sites being reviewed. Included in Refresh of
Parking Strategy (2018)
6 Review parking
strategies
Alternatives to
private vehicle
use
Other SCC/SWT and
SCC/SWT funded
Completed On-going N/A
There could be a reduction in traffic in town centre if some car parks are closed and/or long stay car
parking charges are increased. However, no
decisions made yet. And no
information is available on the affect this would have on traffic
levels.
Refresh of Parking Strategy published in
Feb 2018 On-going
Parking policy ECN3 in SCC Future Transport
Plan
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LAQM Annual Status Report 2019 15
Measure No. Measure
EU Category
EU Classification
Organisations involved and
Funding Source
Planning Phase
Implementation Phase
Key Performance
Indicator
Reduction in Pollutant /
Emission from Measure
Progress to Date Estimated /
Actual Completion
Date
Comments / Barriers to implementation
7
Variable Message Signage
for parking in Taunton
Traffic Managem
ent Other SWT organised and funded Completed
Starting May 2018
Improve the flow of traffic
and help drivers find
spaces more efficiently
Should reduce number of
vehicles driving around town looking for spaces, but
actual numbers not known.
Could increase traffic driving
into the town if parking made
more attractive.
Signs installed in 2018
Became operational Jan
2019
Scheme also includes introduction of pay on
exit car parks.
8
Local Cycling
and Walking
Infrastructure Plan
Promoting Travel
Alternatives
Promotion of cycling and
walking
SWT /SCC Funding from councils and garden town
funding
On-going To be confirmed
Will identify performance
measures and targets based
upon implementation of network infrastructure
N/A. The Plan should lead to more detailed
proposals.
Funding identified. Work being planned. Not known
Will provide understanding of existing networks, barriers and route
priorities.
9
SWT to purchase
low emission vehicles for their
own fleet
Promoting Low
Emission Transport
Company Vehicle
Procurement – Prioritising
uptake of low emission vehicles
SWT and funded by SWT Completed On-going
Number of low emission
vehicles in fleet
There is information on the vehicles in
service and annual mileage, but there are so
many other factors affecting emissions (e.g. where they are
being driven and how) that it is not practical to try and make an estimate of
emission reduction.
New vehicles being purchased using
Government guidance
On-going
The Council's structure and services
underwent a major transformation during 2019, which will affect how vehicles are used and the number that
are needed
10
Update Somerset Air Quality Strategy
Policy Guidance
and Developm
ent
Air Quality Planning and
Policy Guidance
All Somerset District Councils and SCC (Public
Health and
Completed
Strategy completed. To be adopted by
local authorities during 2018
New Strategy adopted by
local authorities
N/A. Is a Strategy and so will not have a
direct impact on emissions.
Strategy completed.
Strategy has been
completed, awaiting formal
adoption.
The Strategy will be a working document with
measures being implemented by the
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LAQM Annual Status Report 2019 16
Measure No. Measure
EU Category
EU Classification
Organisations involved and
Funding Source
Planning Phase
Implementation Phase
Key Performance
Indicator
Reduction in Pollutant /
Emission from Measure
Progress to Date Estimated /
Actual Completion
Date
Comments / Barriers to implementation
Transport) (and funded)
Somerset local authorities
11 Travel
Somerset Website
Promoting Travel
Alternatives
Other SCC Completed Completed
Increase use of alternative
means of transport to
cars
N/A Not possible to
measure how effective this is.
On-going On-going
Website provides local transport information. Does include driving,
but also promotes other means of
transport
12
Optimisation of the SCOOT Urban Traffic Control
system in East
Reach AQMA
and all of the town centre
Transport Managem
ent
Congestion management
Somerset County Council. SCC Funding
Partially completed
Partially completed N/A
Data is not available to
make an assessment of any changes in level of traffic or
emissions.
East Reach completed. Town
centre work shelved until there is more
certainty on the plans for pedestrianisation
On-hold
Trial pedestrianisation scheme of St James St commenced May 2019.
Other schemes planned which could lead to review of the scheme, if funding
available.
13
Rapid Bus Link on A38 in
Taunton
Alternatives to
private vehicle
use
Other
First phase part of successful
Housing Infrastructure
Bid (HIF) (March 18)
Govt/ SCC/
SWT/ Developer
On-going Awaiting funding Increased use of buses
No data available on
predicted use or resulting
reduction in vehicle use.
In TDBC adopted Core Strategy 2011-
20128 Not known Depends on funding
14 Target school trips
Promoting Travel
Alternatives
School Travel Plans
SCC No funding available Completed
On hold awaiting funding
Mode of journeys to
school
No information available on the scheme as no longer place
Up to 2011 95% of LEA schools had a
travel plan
SCC still have a School Travel
Strategy
Funding for School Travel Advisor
removed so work likely to be minimal
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LAQM Annual Status Report 2019 17
2.3 PM2.5 – Local Authority Approach to Reducing Emissions and/or Concentrations
As detailed in Policy Guidance LAQM.PG16 (Chapter 7), local authorities are expected
to work towards reducing emissions and/or concentrations of PM2.5 (particulate matter
with an aerodynamic diameter of 2.5µm or less). There is clear evidence that PM2.5
has a significant impact on human health, including premature mortality, allergic
reactions, and cardiovascular diseases.
Apart from the monitoring associated with the Hinkley Point C development (which is
non-reference), there is no monitoring of in PM2.5 being carried out in the Somerset
West and Taunton area. However, Taunton Deane Borough Council did carry out
monitoring for PM10 for a number of years at sites across the district, including sites in
Taunton town centre and adjacent to the A358 trunk road in Henlade. This data can
be used to estimate levels of PM2.5 by using a correction factor as outlined in Local Air
Quality Management Technical Guidance (TG16). The estimates suggest that the
levels of PM2.5 in the Somerset West and Taunton area are likely to be below the EU
limit level of 25 µg/m3. Details of historic PM10 monitoring and estimates of PM2.5 levels
are given in Appendix C.
The updated policy guidance as introduced by Defra (2016) explains that whilst there
is no regulatory standard specific to PM2.5, it is still important to consider a wider
exposure reduction approach to the pollution sources of particulate matter.
Public Health England have produced a range of public health indicators, one of which
relates to PM2.5 (Public Health Indicators 3.01, Fraction of mortality attributable to
particulate air pollution). The technical guidance estimates that an increase of 10
μg/m3 in population-weighted annual average background concentration of PM2.5 is
assumed to increase all-cause mortality rates by a unit relative risk (RR) factor of 1.06.
While it is recognised that a large percentage of the PM2.5 in an area could be from
cross-border sources, the contribution from local sources could still account 50% or
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LAQM Annual Status Report 2019 18
more. In terms of pollution sources, the National Atmospheric Emission Inventory
(NAEI) shows that largest source of PM2.5 by mass is from the domestic sector burning
wood and that this source is increasing. Somerset West and Taunton has large rural
areas and so has more domestic wood burners than many other authorities. PM2.5 is
also one of the pollutants released in road traffic emissions, and NOx from traffic is one
of the precursors to secondary particulates.
Somerset West and Taunton Council recognises the public health benefits of seeking
to reduce exposure to the wider range of pollution source of particulate matter. The on-
going proposals to reduce emissions from traffic should also lead to a reduction in fine
particulates. The Council will also provide advice and information to help ensure best
practice is followed when choosing to burn wood and also when selecting a combustion
appliance by the lowest emission factor. For larger biomass boilers we will continue
to assess the emission rates and ensure that none will lead to an exceedance in the
relevant air quality objectives, but moreover do not lead to significant increase in
exposure to the principal emissions (PM2.5 and NO2).
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LAQM Annual Status Report 2019 19
3 Air Quality Monitoring Data and Comparison with Air Quality Objectives and National Compliance 3.1 Summary of Monitoring Undertaken 3.1.1 Non-Automatic Monitoring Sites
Somerset West and Taunton Council undertook non-automatic (passive) monitoring of
NO2 at 56 sites during 2018. Table A.1 in Appendix A shows the details of the sites.
Maps showing the location of the monitoring sites are provided in Appendix D. Further
details on Quality Assurance/Quality Control (QA/QC) for the diffusion tubes, including
bias adjustments and any other adjustments applied (e.g. “annualisation” and/or
distance correction), are included in Appendix C.
3.2 Individual Pollutants The air quality monitoring results presented in this section are, where relevant,
adjusted for bias, “annualisation” and distance correction. Further details on
adjustments are provided in Appendix C.
3.2.1 Nitrogen Dioxide (NO2)
Table A.2 in Appendix A compares the ratified and adjusted monitored NO2 annual
mean concentrations for the past 5 years with the air quality objective of 40µg/m3.
For diffusion tubes, the full 2018 dataset of monthly mean values is provided in
Appendix B.
The results of the diffusion tube monitoring for 2018 show an increase in nitrogen
dioxide levels at all sites when compared to the results from 2017. There were
exceedances of the air quality objective for nitrogen dioxide at five locations, the two
sites in the Henlade AQMA, the two in the East Reach AQMA and one just outside the
East Reach AQMA. The objective is an annual mean of 40 µg/m3 and the levels
measured at the sites was between 44 and 54 µg/m3. When these results were
corrected for the distance to the nearest sensitive receptors they were between 43 and
48 µg/m3.
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LAQM Annual Status Report 2019 20
The monitoring at the four sites within the AQMAs has now been carried out for three
years. The results are in line with the monitoring at sites just outside the AQMAs which
show slightly lower levels of NO2. It is not surprising that higher levels have been
measured at the new sites as, although they are at a similar distance from the road,
they are at locations where there are buildings closer to the highway which could
reduce the dispersal of pollutants
Although the 2018 levels are higher than in 2017 they are similar to those that have
been monitored in previous years. It is not clear why the levels were higher in 2018
and lower in 2017, as there is no evidence that traffic volumes have varied significantly
over this period. Pollutant levels can be affected by the weather, which is why, when
looking at annual average results, the long term trend should be used to indicate any
changes, rather than comparing the difference between individual years.
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LAQM Annual Status Report 2019 21
Appendix A: Monitoring Results
Table A.1 – Details of Non-Automatic Monitoring Sites
Site ID Site Name Site Type X OS Grid
Ref Y OS Grid
Ref Pollutants Monitored
In AQMA?
Distance to
Relevant Exposure
(m) (1)
Distance to kerb of nearest road (m)
(2)
Tube collocated
with a Continuous Analyser?
Height (m)
2 Henlade East Roadside 3269720 1240710 NO2 N 24 7 NO 2
3 Monks Close Roadside 3236681 1251096 NO2 N 10 39 NO 2
6 Wellington High Kerbside 3140414 1207733 NO2 N 1.2 1.5 NO 2
10 Market House Urban Centre 3227190 1244738 NO2 N 3 2.5 NO 2
12 Bridge Street Roadside 3225400 1250070 NO2 N 1 2.5 NO 2
13 Station Road Roadside 3227168 1252055 NO2 N 0 3 NO 2
14 Wellington Road/Crem Roadside 3204950 1241113 NO2 N 10 24 NO 2
15 Haydon Road Roadside 3233495 1245958 NO2 N 1 1 NO 2
16 Park Gate Roadside 3235233 1246272 NO2 N 0 7.5 NO 2
18 Hurdle Way Roadside 3229866 1243485 NO2 N 3.5 3 NO 2 19 Ilminster Road Roadside 3250017 1248375 NO2 N 12 2 NO 2
21 Cann Street Roadside 3223053 1242758 NO2 N 10 5 NO 2
22 Priory Bridge Road Roadside 3231029 1250346 NO2 N 0 3 NO 2
25 Creech Castle Roadside 3249458 1256018 NO2 N 26 4 NO 2
26 Westerkirk Gate Roadside 3211709 1261706 NO2 N 30 3 NO 2
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LAQM Annual Status Report 2019 22
Site ID Site Name Site Type X OS Grid
Ref Y OS Grid
Ref Pollutants Monitored
In AQMA?
Distance to
Relevant Exposure
(m) (1)
Distance to kerb of nearest road (m)
(2)
Tube collocated
with a Continuous Analyser?
Height (m)
27 Henlade West Roadside 3264261 1243323 NO2 N 17 3 NO 2
29 Linden Grove Roadside 3221859 1250784 NO2 N 2 1 NO 2
30 Malvern Terrace Roadside 3228792 1256438 NO2 N 5 2 NO 2
31 St Augustine’s School Roadside 3232795 1258531 NO2 N 40 11 NO 2
32 Monkton Heathfield Roadside 3255934 1269875 NO2 N 22 2 NO 2
34 Oldway Roadside 3143434 1196557 NO2 N 10 3 NO 2
35 Wellington Centre Roadside 3139421 1206669 NO2 N 6 4.5 NO 2
36 Trinity Close Roadside 3133324 1202517 NO2 N 1 2 NO 2
37 Norton Fitzwarren Kerbside 3195698 1258384 NO2 N 1 2 NO 2
39 Badgers Close Roadside 3207388 1243583 NO2 N 6 2 NO 2
40 Wellington Road SCAT Roadside 3217120 1245700 NO2 N 3 4 NO 2
44 East Reach Lights Roadside 3231193 1245322 NO2 N 0 3.5 NO 2
45 East Street Roadside 3230635 1245082 NO2 N 1 1 NO 2
50 Priory Avenue/Shell Roadside 3233460 1249740 NO2 N 6 1.5 NO 2
51 Bridgewater Road Kerbside 3249230 1254280 NO2 N 8 1 NO 2
52 Park Street Roadside 3222710 1243460 NO2 N 4 3 NO 2
53 Upper High Street Roadside 3224710 1242030 NO2 N 1 3 NO 2
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LAQM Annual Status Report 2019 23
Site ID Site Name Site Type X OS Grid
Ref Y OS Grid
Ref Pollutants Monitored
In AQMA?
Distance to
Relevant Exposure
(m) (1)
Distance to kerb of nearest road (m)
(2)
Tube collocated
with a Continuous Analyser?
Height (m)
54 Wellington New Road Kerbside 3209590 1242880 NO2 N 2 2 NO 2
55 Obridge
/Priorswood Rd
Roadside 3234910 1259060 NO2 N 12 3 NO 2
56 St Andrews Road Roadside 3226750 1257290 NO2 N 5 1 NO 2
57 St James Street Kerbside 3227050 1247600 NO2 N 13 7 NO 2
58 Tangier/Castle Street Roadside 3222980 1245520 NO2 N n/a 2 NO 2
59 Bindon
Road/Silk Mills
Kerbside 3206680 1259500 NO2 N 13 5 NO 2
60 Greenway Road Roadside 3223290 1258930 NO2 N 4 4 NO 2
61 Trull Road Roadside 3222290 1241780 NO2 N 12 1 NO 2
62 Thornfalcon Roadside 3275850 1237240 NO2 N 37 20 NO 2
66 Castle Street/Tesco Roadside 3220770 1244620 NO2 N 7 4.6 NO 2
67 Wood Street Roadside 3225160 1247660 NO2 N 1.2 1.9 NO 2
68 Staplegrove Rd/Chip Lane Roadside 3220600 1254770 NO2 N 11 1 NO 2
69 Whitehall Roadside 3226420 1253220 NO2 N 1.6 1.3 NO 2
70 Priory Park Roadside 3232930 1251860 NO2 N 5 1 NO 2
71 Henlade AQMA West Roadside 3267830 1241380 NO2 Y 4.8 1.6 NO 2
72 Henlade AQMA East Roadside 3268710 1240930 NO2 Y 5.4 1.5 NO 2
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LAQM Annual Status Report 2019 24
Site ID Site Name Site Type X OS Grid
Ref Y OS Grid
Ref Pollutants Monitored
In AQMA?
Distance to
Relevant Exposure
(m) (1)
Distance to kerb of nearest road (m)
(2)
Tube collocated
with a Continuous Analyser?
Height (m)
73 East Reach AQMA east Roadside 3232710 1245530 NO2 Y 0.4 3.1 NO 2
74 East Reach AQMA west Roadside 3231880 1245390 NO2 Y 0.4 3.2 NO 2
101 Williton CS Roadside 307737 140954 NO2 NO 0.1 0.5 NO 2 102 Williton PO Roadside 307715 141013 NO2 NO 0.1 0.5 NO 2
103 Vulcan Rd, Minehead Roadside 297804 145956 NO2 NO 162m 0.5 NO 2
104 The Avenue, Minehead Roadside 296950 146248 NO2 NO 1 0.5 NO 2
105 May Terrace, Washford Roadside 304694 141030 NO2 NO 5 0.5 NO 2
106 Silvermead, Alcombe Roadside 297700 145164 NO2 NO 9.9 0.5 NO 2
Notes: (1) 0m if the monitoring site is at a location of exposure (e.g. installed on/adjacent to the façade of a residential property). (2) N/A if not applicable.
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LAQM Annual Status Report 2019 25
Table A.2 – Annual Mean NO2 Monitoring Results
Site ID Site Type Monitoring Type
Valid Data Capture for Monitoring
Period (%) (1)
Valid Data Capture
2018 (%) (2)
NO2 Annual Mean Concentration (µg/m3) (3)
2014 2015 2016 2017 2018
2 Roadside Diffusion Tube 100 100 31 27 32 21 30
3 Roadside Diffusion Tube 26 24 25 23 Ceased
6 Kerbside Diffusion Tube 100 100 33 31 33 27 34
10 Urban Centre Diffusion Tube 83 83 35 31 31 25 31
12 Roadside Diffusion Tube 100 100 36 32 34 29 37
13 Roadside Diffusion Tube 83 83 31 29 31 26 32
14 Roadside Diffusion Tube 100 100 27 23 27 24 27
15 Roadside Diffusion Tube 100 100 26 23 26 20 24
16 Roadside Diffusion Tube 100 100 22 20 22 17 20
18 Roadside Diffusion Tube 100 100 31 28 32 27 32
19 Roadside Diffusion Tube 100 100 30 28 30 27 31
21 Roadside Diffusion Tube 100 100 28 32 25 32
22 Roadside Diffusion Tube 100 100 23 19 20 16 19
25 Roadside Diffusion Tube 100 100 29 25 26 23 28
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LAQM Annual Status Report 2019 26
Site ID Site Type Monitoring Type
Valid Data Capture for Monitoring
Period (%) (1)
Valid Data Capture
2018 (%) (2)
NO2 Annual Mean Concentration (µg/m3) (3)
2014 2015 2016 2017 2018
26 Roadside Diffusion Tube 21 20 Ceased
27 Roadside Diffusion Tube 100 100 35 31 30 27 30
29 Roadside Diffusion Tube 18 13 Ceased
30 Roadside Diffusion Tube 24 21 23 18 Ceased
31 Roadside Diffusion Tube 23 19 19 16 Ceased
32 Roadside Diffusion Tube 23 22 23 19 Ceased
34 Roadside Diffusion Tube 20 16 19 15 Ceased
35 Roadside Diffusion Tube 100 100 25 26 28 25 27
36 Roadside Diffusion Tube 15 14 Ceased
37 Kerbside Diffusion Tube 18 16 18 14 Ceased
39 Roadside Diffusion Tube 19 16 Ceased
40 Roadside Diffusion Tube 100 100 29 23 28 23 27
44 Roadside Diffusion Tube 100 100 41 37 37 33 44
45 Roadside Diffusion Tube 100 100 38 33 34 30 36
50 Roadside Diffusion Tube 100 100 27 22 27 22 29
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LAQM Annual Status Report 2019 27
Site ID Site Type Monitoring Type
Valid Data Capture for Monitoring
Period (%) (1)
Valid Data Capture
2018 (%) (2)
NO2 Annual Mean Concentration (µg/m3) (3)
2014 2015 2016 2017 2018
51 Kerbside Diffusion Tube 100 100 29 25 30 25 33
52 Roadside Diffusion Tube 100 100 34 30 32 27 32
53 Roadside Diffusion Tube 92 92 27 24 28 23 28
54 Kerbside Diffusion Tube 100 100 31 28 33 27 34
55 Roadside Diffusion Tube 75 75 25 20 24 18 24
56 Roadside Diffusion Tube 100 100 35 29 32 27 34
57 Kerbside Diffusion Tube 92 92 28 24 26 21 25
58 Roadside Diffusion Tube 92 92 22 19 22 18 19
59 Kerbside Diffusion Tube 92 92 28 24 25 22 27
60 Roadside Diffusion Tube 100 100 26 23 24 21 23
61 Roadside Diffusion Tube 100 100 28 26 29 24 31
62 Roadside Diffusion Tube 83 83 25 23 25 23 23
66 Roadside Diffusion Tube 100 100 29 26 28 24 30
67 Roadside Diffusion Tube 100 100 28 25 26 22 26
68 Roadside Diffusion Tube 100 100 26 n/a 21 19 20
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LAQM Annual Status Report 2019 28
Site ID Site Type Monitoring Type
Valid Data Capture for Monitoring
Period (%) (1)
Valid Data Capture
2018 (%) (2)
NO2 Annual Mean Concentration (µg/m3) (3)
2014 2015 2016 2017 2018
69 Roadside Diffusion Tube 100 100 18 17 18 14 19
70 Roadside Diffusion Tube 100 100 n/a n/a 17 14 17
71 (Henlade AQMA West) Roadside
Diffusion Tube 100 100 47 32 54
72 (Henlade AQMA East) Roadside
Diffusion Tube 95 95 49 41 45
73 (East Rch AQMA East) Roadside
Diffusion Tube 92 92 42 41 46
74 (East Rch AQMA West) Roadside
Diffusion Tube 100 100 42 41 50
101 Roadside Diffusion Tube 92 92 32 30 33 26 34
102 Roadside Diffusion Tube 100 100 34 31 33 28 32
103 Roadside Diffusion Tube 100 100 13 13 16 12 17
104 Roadside Diffusion Tube 100 100 20 20 21 17 33
105 Roadside Diffusion Tube 83 83 31 26 23 14 16
106 Roadside Diffusion Tube 100 100 17 18 18 13 21
☐ Diffusion tube data has been bias corrected ☐ Annualisation has been conducted where data capture is
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LAQM Annual Status Report 2019 29
NO2 annual means exceeding 60µg/m3, indicating a potential exceedance of the NO2 1-hour mean objective are shown in bold and underlined. (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%). (3) Means for diffusion tubes have been corrected for bias. All means have been “annualised” as per Boxes 7.9 and 7.10 in LAQM.TG16 if valid data capture for the full calendar year is less than 75%. See Appendix C for details.
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LAQM Annual Status Report 2019 30
Figure A.1 Trends in Annual Mean NO2 Concentrations
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LAQM Annual Status Report 2019 31
Appendix B: Full Monthly Diffusion Tube Results for 2018 Table B.1 – NO2 Monthly Diffusion Tube Results – 2018
Site ID
NO2 Mean Concentrations (µg/m3)
Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec
Annual Mean
Raw Data
Bias Adjusted (factor)
and Annualised
(1)
Distance Corrected
to Nearest
Exposure (2)
2 38.2 38.8 35.0 34.5 32.0 31.8 34.5 30.0 31.9 35.8 28.8 30.6 33.5 30.5
6 32.7 34.8 33.8 36.6 40.1 39.0 46.0 32.7 37.8 42.6 35.7 36.2 37.3 34.0
10 41.9 34.7 30.9 33.2 31.8 35.9 28.0 31.5 38.0 36.9 34.3 31.2
12 40.9 45.8 45.3 44.5 45.1 46.2 35.6 28.3 33.7 41.9 44.0 37.9 40.8 37.1
13 41.2 38.2 34.7 34.4 33.7 28.3 28.8 37.8 34.3 35.2 34.7 31.5
14 33.6 31.1 30.2 30.7 24.7 24.7 31.2 25.6 29.1 27.3 31.8 32.9 29.4 26.8
15 33.3 30.1 26.3 26.4 19.3 19.0 19.4 19.8 22.9 27.4 32.9 33.3 25.8 23.5
16 26.0 26.0 23.7 20.7 18.2 16.5 16.2 15.6 18.7 23.1 25.8 29.0 21.6 19.7
18 41.1 38.9 36.7 33.3 35.7 33.9 33.2 27.7 34.5 40.3 34.3 38.1 35.6 32.4
19 42.8 34.4 35.4 36.3 35.0 27.9 30.1 25.1 31.6 36.6 35.7 38.8 34.1 31.1
21 36.3 38.6 36.5 37.3 34.2 33.0 33.7 28.4 33.3 34.2 35.0 37.2 34.8 31.7
22 26.7 29.7 22.9 21.2 17.9 16.5 15.6 14.1 17.4 23.8 24.8 26.3 21.4 19.5
25 33.7 36.2 33.4 36.5 31.3 24.6 28.2 23.7 26.2 31.4 37.2 31.6 31.2 28.3
27 38.6 38.4 36.9 31.8 27.5 21.0 32.8 31.0 35.0 38.0 29.2 32.9 32.8 29.8
35 36.1 33.3 30.8 28.2 29.1 29.6 34.0 14.5 30.0 34.3 27.1 28.3 29.6 26.9
40 31.9 33.2 34.4 33.0 27.3 29.2 26.1 20.6 27.6 31.9 34.2 32.6 30.2 27.4
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Site ID
NO2 Mean Concentrations (µg/m3)
Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec
Annual Mean
Raw Data
Bias Adjusted (factor)
and Annualised
(1)
Distance Corrected
to Nearest
Exposure (2)
44 53.6 48.0 49.4 55.8 54.9 49.2 46.4 38.1 40.5 50.3 45.3 50.7 48.5 44.2 42.9
45 44.9 38.1 43.2 43.5 38.9 35.5 34.9 31.8 33.4 39.2 43.8 45.9 39.4 35.9
50 33.5 40.3 33.1 35.0 33.5 31.6 24.1 23.7 26.4 34.6 35.1 37.4 32.4 29.5
51 36.0 38.5 36.4 38.1 40.6 40.5 33.7 27.5 31.8 40.1 36.7 36.0 36.3 33.1
52 40.6 36.4 36.9 36.8 33.5 28.9 33.3 29.7 34.5 35.6 38.2 41.6 35.5 32.3
53 37.4 34.1 30.2 30.6 30.1 27.1 22.2 27.3 32.4 30.7 31.3 30.3 27.6
54 37.9 41.4 36.4 42.2 40.8 37.0 36.0 29.4 33.7 41.1 38.2 40.8 37.9 34.5
55 42.4 30.0 24.8 24.9 23.9 19.7 20.8 27.9 25.5 26.7 24.3
56 28.9 40.6 40.2 40.4 40.6 41.0 36.6 28.5 32.8 41.1 41.1 34.6 37.2 33.8
57 29.5 31.8 28.4 26.3 25.6 24.3 20.4 24.8 30.0 32.5 27.2 27.3 24.9
58 27.9 23.7 19.3 16.9 17.2 16.6 15.7 17.7 22.7 25.8 26.8 20.9 19.0
59 33.8 32.5 32.5 30.8 26.6 24.5 22.7 28.5 29.1 30.3 32.7 29.4 26.8
60 40.1 28.0 28.0 25.2 22.5 21.3 20.5 17.6 22.3 27.5 29.2 25.2 25.6 23.3
61 33.9 39.7 33.5 36.8 39.5 35.0 31.7 27.9 31.8 35.3 34.1 33.9 34.4 31.3
62 31.7 30.7 21.8 17.0 26.4 26.3 26.4 26.5 23.7 25.9 25.6 23.3
66 34.7 37.0 34.9 33.5 33.8 34.5 31.4 26.1 29.6 34.0 34.4 31.1 32.9 30.0
67 37.5 31.5 28.8 26.6 28.6 23.9 26.3 23.3 29.0 30.9 31.1 31.4 29.1 26.5
68 31.0 26.3 23.4 23.2 19.7 17.3 18.0 16.7 19.3 23.3 24.2 22.9 22.1 20.1
69 23.4 28.4 24.2 22.7 20.1 15.6 15.5 12.8 15.8 23.5 27.4 24.5 21.2 19.3
70 22.6 27.5 21.2 17.4 15.2 13.5 13.2 12.1 14.2 19.7 23.7 24.7 18.7 17.0
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Site ID
NO2 Mean Concentrations (µg/m3)
Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec
Annual Mean
Raw Data
Bias Adjusted (factor)
and Annualised
(1)
Distance Corrected
to Nearest
Exposure (2)
71 48.9 65.8 65.2 66.2 58.6 59.1 63.0 54.6 55.2 62.3 56.8 54.3 59.2 53.8 44.6
72 48.7 55.5 52.3 55.3 51.3 42.8 40.9 46.4 57.7 51.6 46.6 49.9 45.4 44.5
73 65.8 50.3 64.1 49.8 50.8 42.1 42.0 48.7 50.8 44.7 48.7 50.7 46.1 45.0
74 63.7 55.2 56.6 62.8 62.3 54.3 49.5 42.1 51.6 56.1 46.5 55.4 54.7 49.8 47.6
101 38.2 39.4 35.1 46.6 46.5 41.0 30.1 32.4 33.6 33.6 33.7 37.3 33.9
102 36.7 33.0 37.0 34.3 36.8 31.4 40.0 35.3 37.7 31.4 31.4 36.4 35.1 32.0
103 21.6 19.2 22.0 18.6 16.6 13.9 14.5 14.0 15.8 24.4 24.4 18.3 18.6 16.9
104 33.3 35.0 34.7 39.9 42.1 43.6 42.2 39.1 36.6 30.7 30.7 29.6 36.5 33.2
105 17.7 17.8 21.7 20.3 14.6 12.8 14.6 19.8 19.8 20.2 17.9 16.3
106 24.7 24.4 25.9 21.9 24.4 21.1 21.8 18.2 20.8 22.3 22.3 24.5 22.7 20.6
☒ Local bias adjustment factor used (not applicable, no local correction factor) ☒ National bias adjustment factor used (see details in Appendix C)
☒ Annualisation has been conducted where data capture is
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Appendix C: Supporting Technical Information / Air Quality Monitoring Data QA/QC Diffusion Tube Bias Adjustment Factors
Somerset West and Taunton Council does not take part in any co-location studies.
The Council uses Somerset County Council Scientific. The nitrogen dioxide diffusion
tubes are prepared with 20% Triethanolamine in water and are deployed according to
the procedures given in the UK Nitrogen dioxide Diffusion tube Network instruction
manual. A travel blank is included in each batch,
The diffusion tubes are analysed by Somerset County Council. This laboratory
participates in the national comparison scheme and the results are used to prepare the
National Bias Adjustment Spreadsheet which is then circulated to local authorities. A
copy of the relevant part of the spreadsheet is shown below. A Somerset County
Council tube using 20% Triethanolamine in water have a bias adjustment of 0.91
From National Bias Adjustment Factor Spreadsheet Version 9/19
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Distance Correction information for NO2 tube results
This has been carried out for sites where there was relevant exposure, which was the
four sites within the AQMAs
71 Henlade South West (AQMA)
72 Henlade South East (AQMA)
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73 East Reach AQMA East
74 East Reach AQMA West
44 East Reach Lights
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Historic PM10 monitoring data
Monitoring location
Year Annual mean PM10 concentrations (µg/m3)
Estimate of PM2.5 level (µg/m3)
Market House, Taunton 2001 30.2 21.4
East Reach, Taunton 2001-02 31.1 21.7 Shoreditch (by M5) 2002-03 30 21 Wellington New Road, Taunton
2006 28.2 19.7
Mantle Street, Wellington 2007 26.2 18.3 Mantle Street, Wellington 2008 23.2 16.2
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Appendix D: Map(s) of Monitoring Locations and AQMAs
Figure D1. East Reach AQMA and monitoring sites
Figure D2. Henlade AQMA and monitoring sites
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Figure D3 Monitoring sites in Taunton town centre
Figure D4 Monitoring sites in Taunton east and Henlade
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Figure D5. Monitoring sites in Wellington
Figure D6 Monitoring sites in Williton and Washford
May Terrace, WashfordDT5
Williton County StoresDT1
Williton P.O.DT2
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Figure D7 Monitoring sites in Minehead
Silvermead DT6
The Avenue DT4
Vulcan Rd DT3
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Appendix E: Summary of Air Quality Objectives in England Table E.1 – Air Quality Objectives in England
Pollutant Air Quality Objective4
Concentration Measured as
Nitrogen Dioxide (NO2)
200 µg/m3 not to be exceeded more than 18 times a year 1-hour mean
40 µg/m3 Annual mean
Particulate Matter (PM10)
50 µg/m3, not to be exceeded more than 35 times a year 24-hour mean
40 µg/m3 Annual mean
Sulphur Dioxide (SO2)
350 µg/m3, not to be exceeded more than 24 times a year 1-hour mean
125 µg/m3, not to be exceeded more than 3 times a year 24-hour mean
266 µg/m3, not to be exceeded more than 35 times a year 15-minute mean
4 The units are in microgrammes of pollutant per cubic metre of air (µg/m3).
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Glossary of Terms Abbreviation Description
AQAP Air Quality Action Plan - A detailed description of measures, outcomes, achievement dates and implementation methods, showing how the local authority intends to achieve air quality limit values’
AQMA Air Quality Management Area – An area where air pollutant concentrations exceed / are likely to exceed the relevant air quality objectives. AQMAs are declared for specific pollutants and objectives
ASR Air quality Annual Status Report
Defra Department for Environment, Food and Rural Affairs
DMRB Design Manual for Roads and Bridges – Air quality screening tool produced by Highways England
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 (micrometres or microns) 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
SCC Somerset County Council
SWT Somerset West and Taunton Council
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References
• HMSO Environment Act (1995) (Part IV)
• Department for the Environment, Food and Rural Affairs. Local Air Quality Management, Technical Guidance LAQM.TG(09), April 2016
• Department for the Environment, Food and Rural Affairs, Emissions of Air Pollutants in the UK, 1970 to 2014. 2016
• Highways England. A358 Taunton to Southfields Dualling Scheme, Technical Appraisal Report updated January 2018.
• Highways England. Taunton to Southfields Dualling Scheme, Preferred Route Scheme Assessment Report. 2019
• Taunton Deane Borough Council and West Somerset Council Air Quality Annual reports https://www.somersetwestandtaunton.gov.uk/environmental-health/environmental-protection/air-quality/
• Draft Taunton Transport Strategy: Taunton – Connecting our Garden Town http://www.somersetconsults.org.uk/consult.ti/TauntonTransportStrategy/consultationHome
• Somerset County Council. Somerset Future Transport Plan 2011
https://www.somerset.gov.uk/roads-and-transport/future-transport-plan/
• Defra. National bias adjustment factor spreadsheet: http://laqm.defra.gov.uk/bias-adjustment-factors/national-bias.html
• Taunton Deane Borough Council, Taunton Car Parking Strategy 2017
• Somerset County Council. Taunton Local Cycling and Walking Infrastructure Plan (LCWIP). Draft. November 2019
https://www.somersetwestandtaunton.gov.uk/environmental-health/environmental-protection/air-quality/https://www.somersetwestandtaunton.gov.uk/environmental-health/environmental-protection/air-quality/http://www.somersetconsults.org.uk/consult.ti/TauntonTransportStrategy/consultationHomehttp://www.somersetconsults.org.uk/consult.ti/TauntonTransportStrategy/consultationHomehttps://www.somerset.gov.uk/roads-and-transport/future-transport-plan/http://laqm.defra.gov.uk/bias-adjustment-factors/national-bias.html
Executive Summary: Air Quality in Our AreaAir Quality in Somerset West and TauntonActions to Improve Air QualityConclusions and PrioritiesLocal Engagement and How to get Involved
1 Local Air Quality Management2 Actions to Improve Air Quality2.1 Air Quality Management Areas2.2 Progress and Impact of Measures to address Air Quality in Somerset West and Taunton2.3 PM2.5 – Local Authority Approach to Reducing Emissions and/or Concentrations
3 Air Quality Monitoring Data and Comparison with Air Quality Objectives and National Compliance3.1 Summary of Monitoring Undertaken3.1.1 Non-Automatic Monitoring Sites
3.2 Individual Pollutants3.2.1 Nitrogen Dioxide (NO2)
Appendix A: Monitoring ResultsAppendix B: Full Monthly Diffusion Tube Results for 2018Appendix C: Supporting Technical Information / Air Quality Monitoring Data QA/QCAppendix D: Map(s) of Monitoring Locations and AQMAsAppendix E: Summary of Air Quality Objectives in EnglandGlossary of TermsReferences