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Cannock Chase Council LAQM Annual Status Report 2016 2016 Air Quality Annual Status Report (ASR) In fulfilment of Part IV of the Environment Act 1995 Local Air Quality Management August, 2016
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Page 1: 2016 Air Quality Annual Status Report (ASR) · Keep wood stoves and fireplaces well maintained, and make sure that wood burners are exempted8 for use in smoke control areas. Before

Cannock Chase Council

LAQM Annual Status Report 2016

2016 Air Quality Annual Status Report (ASR) In fulfilment of Part IV of the Environment Act 1995 Local Air Quality Management August, 2016

Page 2: 2016 Air Quality Annual Status Report (ASR) · Keep wood stoves and fireplaces well maintained, and make sure that wood burners are exempted8 for use in smoke control areas. Before

Cannock Chase Council

LAQM Annual Status Report 2016

Local Authority Officer

Stephen Moore

Department Environmental Health

Address

Cannock Chase Council, Civic Centre, Beecroft Road, Cannock, Staffordshire. WS11 1BG

Telephone 01543 462621

E-mail [email protected]

Report Reference number

ASR2016

Date August 2016

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Cannock Chase Council

LAQM Annual Status Report 2016 i

Endorsement from the Director of Health and Care, Staffordshire County Council

Staffordshire County Council is committed to working with partners to ensure that

Staffordshire will be a place where improved health and wellbeing is experienced by

all. Poor air quality has a negative impact on public health, with potentially serious

consequences for individuals, families and communities. Identifying problem areas

and ensuring that actions are taken to improve air quality forms an important element

in protecting the health and wellbeing of Staffordshire residents. Improving air quality

is often a complex issue, presenting a multi-agency challenge – so it is essential that

all agencies work together effectively to deliver improvements where they are

needed. As Director of Health and Care across Staffordshire I endorse this Annual

Status Report which sets out the position in Cannock Chase District Council and

which will support an ongoing work programme to address air quality issues.

Dr Richard Harling Director of Health and Care Staffordshire County Council August 2016

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LAQM Annual Status Report 2016 ii

Executive Summary: Air Quality in Our Area

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.

The main pollutant of concern in the Cannock Chase Council area is nitrogen

dioxide. Nitrogen dioxide is a gas, with the chemical formula NO2. It is chemically

related to nitric oxide (nitrogen monoxide), a colourless gas with the chemical formula

NO.

Together, NO and NO2 are known as NOX. NOX is released into the atmosphere

when fuels are burned (for example, petrol or diesel in a car engine, or natural gas in

a domestic central heating boiler or power station). NO2 can affect our health. There

is evidence that high levels of it can inflame the airways in our lungs and, over

a long period of time, affect how well our lungs work. People with asthma are

particularly affected. NO2 can also affect vegetation.

NOX is produced when fossil fuels (coal, natural gas and so on) are burned.

Road transport is the largest source of NOX emissions in the UK and is the main

contributor to localised problems in Cannock Chase district.

However, emissions from road transport have fallen and continue to fall 2000. This is

due to improvements in engine design and fitting three-way catalysts to petrol cars,

to meet increasingly strict European standards. The importance of road transport is

even greater in urban areas.

NOX emissions from burning fossil fuels are mainly as NO, although some sources

can release a lot of NOX as NO2. Reactions in the atmosphere can subsequently turn

NO into NO2.

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 2016 iii

Air Quality in Cannock Chase District

Cannock Chase Council has monitored for nitrogen dioxide over a number of years,

which has identified hotspots where national objectives are exceeded, and people

are likely to be exposed to poor air quality for prolonged lengths of time whereby

health impacts could be experienced. These are at locations next to the A5 Watling

Street in Bridgtown and between Churchbridge and the Turf Island.

Levels at these hotspots have shown some decrease in recent years, primarily due to

improvements in engine technology, together with changes to the highway and traffic

management in the locality. It is hoped that if improved pollution levels are sustained,

the designation of ‘Air Quality Management Area’ assigned to the A5 can be revoked.

Monitoring on the A5190 Cannock Road, Heath Hayes near Five Ways Island has

shown that annual levels of nitrogen dioxide exceed the national objective for that

pollutant. Supplementary monitoring, started in June 2015, confirms that to be the

case, and that an AQMA is required for that area.

No new major sources of pollution have been identified. However, the district

continues to attract new businesses and housing, which has an incremental impact

on traffic and therefore pollution. For example, one housing developer in the Pye

Green area of Cannock has calculated that transport related emissions associated

with development will be 4,816.15 kg/annum (NOx) & 479.79 kg/annum (PM10).

Industrial emissions are not deemed to have changed significantly in 2015.

Air Quality Management Areas (‘AQMA’) for the A5 Watling Street has previously

been formally declared, and an action plan is in place to address the issue. To view

past review and assessments, and the action plan see link4 and link5. Progress on

actions identified in the action plan is provided in this report. Most actions involve

partnership working with other organisations such as Staffordshire County Council,

Highways England, other local authorities and the M6Toll. This is necessary because

air quality issues are heavily influenced by road traffic and measures to encourage

cleaner vehicles, reducing traffic, junction management and alternative transport

require the input of organisations able to deliver these results. Formal groups such as

4 https://uk-air.defra.gov.uk/aqma/local-authorities?la_id=45

5 http://www.cannockchasedc.gov.uk/business/environmental-health/environmental-protection/local-air-quality-management

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LAQM Annual Status Report 2016 iv

the Staffordshire Air Quality Forum and the A5 Transport Partnership Group bring all

of these organisations together.

Actions to Improve Air Quality

There are a number of actions within the Action Plan, aimed at improving air quality,

but the core actions undertaken to reduce include the following:

Declare an Air Quality Management Area for the Five Ways Island Area of

Heath Hayes, and develop an action plan.

Junction improvements at Churchbridge have now been completed, which are

intended to reduce congestion, which in turn should reduce east bound vehicle

exhaust emissions in close proximity to residential premises on the A5 in

Bridgtown.

Junction improvements at the A5 / Walkmill Lane / North Street in Bridgtown

are currently in the planning stage, but are intended to re-position west bound

traffic further from residential premises, thereby reducing exposure to pollution.

Additionally, more efficient junction performance should help reduce emissions.

In partnership with a consortium of other Staffordshire and Stoke authorities, a Fleet

fuel efficiency scheme called ECO Stars Fleet Recognition Scheme has been

funded for an initial two year period, commencing in Jun 2015. The scheme has been

funded by a Defra air quality grant. ECO Stars is a franchise owned by South

Yorkshire authorities. The scheme entails auditing commercial and public sector

vehicle fleets to assess their fuel efficiency, award a star rating and provide an

advisory ‘roadmap’. Measures recommended to fleet operators will in turn improve

emissions. This approach will help improve overall road emissions both within this

and other neighbouring areas where the fleets operate.

Work is undertaken by a contractor on behalf of the consortium, and fleet recruitment

statistics are formally reported via ECO Stars general meetings. The most recent

statistics were that Staffordshire and Stoke had 24 members. Cannock Chase

Council’s own vehicle fleet has been assessed, and provided with a roadmap.

Cannock Chase Council will therefore contribute to and benefit from neighbouring

authority participation in the scheme.

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LAQM Annual Status Report 2016 v

Local Priorities and Challenges

The key priorities for the forthcoming year are to identify a funding source or

mechanism, which will allow the Eco Stars scheme to continue operating beyond the

initial two year funding period. At this stage, no definitive funding stream has been

identified, although options are being explored with SBEN (The Staffordshire

Business and Environment Network - http://www.sben.co.uk/Home).

Potentially the scheme may extend to include local authority areas along the A5

Transport Partnership Group area, covering the A5 corridor between Staffordshire

and Northamptonshire. However, again funding options have yet to be identified.

A further priority is for Highways England to complete their study of the A5/Walkmill

lane/ North Street junction improvement proposal. Plans would require submission of

a funding bid, competing against other schemes.

Utilisation of developer contributions towards mitigation schemes is considered to be

a key means to deliver air quality improvements. The challenge is to ensure that the

planning system enables developer contributions to be required. Furthermore, where

developers make financial contributions to the Community Infrastructure Levy then a

competitive bidding process for mitigation schemes is involved.

How to Get Involved

If residents and businesses reduce the amount of fuel and chemicals used, it will

improve air quality. The following ways can help:

Commute

Leaving the car at home one day a week. Further guidance can be found within

http://www.staffssaferroads.co.uk/

Using public transport whenever practicable will reduce traffic congestion and

improve air quality.

By avoiding idling engines and/or air conditioning running continuously - switch

your engine off; to save fuel, money and improve local air quality.

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LAQM Annual Status Report 2016 vi

School Run

Walking or cycling to school is not only good for health but it will save on fuel

costs and help reduce local air pollution. Further guidance can be found within

Travel into School6.

Take turns with friends, neighbours or family to drive or walk the children to

school. Check whether your school has a travel plan.

Energy Efficiency

Improving the energy efficiency of your home / school / workplace will help reduce

energy bills, as well reducing the air pollution associated with power generation.

For further information, please visit the Energy Savings Trust (EST) website7,

which is a non-profit organisation that promotes energy savings, funded by the

Government and private sector.

Around The Home

Use water-based or low solvent paints, glues, varnishes and wood

preservatives, look for brands with a low VOC content.

Make sure your home is well ventilated especially during DIY or cleaning.

Have your central heating system checked regularly to avoid risking exposure

to toxic carbon monoxide.

Keep wood stoves and fireplaces well maintained, and make sure that wood

burners are exempted8 for use in smoke control areas.

Before organising days out, check the air pollution forecast.

Purchase "Green Power" for the electricity in your home. (Contact your power

supplier).

Be energy efficient- make sure your house is well insulated and use energy

efficient appliances.

Use trigger sprays rather than aerosols.

Don't light bonfires or barbecues when air pollution levels are high.

6 https://www.staffordshire.gov.uk/transport/Stafford/Schools/Schools.aspx

7 http://www.energysavingtrust.org.uk/

8 https://smokecontrol.defra.gov.uk/appliances.php?country=england

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LAQM Annual Status Report 2016 vii

Never burn household waste, especially plastics, rubber and treated timber.

Cannock Chase Council’s air quality reports and action plan documents are

accessible from the following link9.

For enquires or suggestions on how to improve air quality please use one of the

following:

Write to: The Environmental Protection Section,

Cannock Chase Council,

Beecroft Road,

Cannock,

Staffordshire.

ST18 0YS

Email: [email protected]

Telephone: 01543 462621

For general information and air quality forecasts, Defra provide information at the

following website: https://uk-air.defra.gov.uk/. Forecasting uses a user friendly index

band to quickly demonstrate general short term air levels in a localised area, and

supplements this with advice for ‘at risk individuals’ and the general public.

9 http://www.cannockchasedc.gov.uk/business/environmental-health/environmental-

protection/local-air-quality-management.

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Cannock Chase Council

LAQM Annual Status Report 2016 viii

Table of Contents

Endorsement from the Director of Health and Care, Staffordshire County Council .............. i

Executive Summary: Air Quality in Our Area ......................................................... ii

Air Quality in Cannock Chase District ............................................................................... iii

Actions to Improve Air Quality ........................................................................................... iv

Local Priorities and Challenges .......................................................................................... v

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 Cannock Chase

District 3

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

Concentrations.................................................................................................................17

2.3.1 Particulate Matter (PM2.5) Levels in Staffordshire and Stoke-on-Trent ........................ 18

2.3.2 PM2.5 and Mortality in Staffordshire & Stoke-on-Trent ............................................... 19

2.3.3 Actions being taken within Staffordshire to reduce PM2.5 .......................................... 20

3 Air Quality Monitoring Data and Comparison with Air Quality

Objectives and National Compliance .................................................................... 37

3.1 Summary of Monitoring Undertaken .....................................................................37

3.1.1 Automatic Monitoring Sites .......................................................................................... 37

3.1.2 Non-Automatic Monitoring Sites................................................................................... 38

3.2 Individual Pollutants .............................................................................................38

3.2.1 Nitrogen Dioxide (NO2)................................................................................................. 38

3.2.2 Particulate Matter (PM10) .............................................................................................. 42

Appendix A: Monitoring Results ........................................................................... 44

Appendix B: Full Monthly Diffusion Tube Results for 2015 ................................ 55

Appendix C: Supporting Technical Information / Air Quality Monitoring

Data QA/QC ............................................................................................................. 58

3.2.3 Significant Changes to Sources ................................................................................... 58

3.2.4 New Monitoring Sites ................................................................................................... 59

3.2.5 QA/QC Data ................................................................................................................. 63

Appendix D: Maps of Monitoring Locations ......................................................... 68

Appendix E: Summary of Air Quality Objectives in England .............................. 72

Glossary of Terms .................................................................................................. 73

References .............................................................................................................. 74

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LAQM Annual Status Report 2016 ix

List of Tables

Table 2.1 – Declared Air Quality Management Areas .................................................. 2 Table 2.2 – Progress on Measures to Improve Air Quality .......................................... 7

Table 1: Annual Mean PM10 and PM2.5 Results of monitoring by Staffordshire Authorities 2011 to 2015 ........................................................................... 18

Table 2: Public Health Outcomes Framework Indicator 3.01- Fraction of annual all cause adult mortality attributable to anthropogenic (human made) particulate air pollution (measured as fine particulate matter, PM2.5 ) for Staffordshire Authorities 2010 to 2013. ..................................................... 19

Table 3: Estimated number of deaths by local authority area attributable to PM2.5 within Staffordshire for adults over 30- 2011 to 2013 ................................ 20

Table 4: Existing Staffordshire & Stoke Authority Actions for PM2.5 ......................... 21

Table 5: Monitored and Predicted Annual Mean NO2 for AQMA1, based on BTL-B . 41 Table 6: Monitored and Predicted Annual Mean NO2 for AQMA2, based on 268 WS41 Table 7: Diffusion Tube Bias Calculation for Staffordshire Analytical Services.......... 64

Table 8: Deavall Farm (Jan-May & Dec) ................................................................... 65 Table 9: Hislop (Jan - June) ....................................................................................... 65 Table 10: 414a PGRd (Jul - Dec) .............................................................................. 65

Table 11: A51 (Jan - May) ......................................................................................... 66 Table 12: CnKRd ( Jun - Dec) ................................................................................... 66

Table 13: HfrdRd (Jun - Aug & Oct - Dec) ................................................................. 66

List of Figures

Figure 1: 'CNKRD' diffusion tube site ........................................................................ 60

Figure 2: 'HHFW' diffusion tube site .......................................................................... 61 Figure 3: 'HFRDRD' diffusion tube site ...................................................................... 62 Figure 4: Map of Automatic Monitoring Sites, Whole District ..................................... 68 Figure 5: Map of Diffusion Tube Monitoring Sites, Whole District .............................. 69

Figure 6: Map of Diffusion Monitoring Sites, Bridgtown ............................................. 70 Figure 7: Map of Diffusion Monitoring Sites, Heath Hayes ........................................ 71

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Cannock Chase Council

LAQM Annual Status Report 2016 1

1 Local Air Quality Management

This report provides an overview of air quality in Cannock Chase district during 2015.

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 Cannock Chase 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

Table E.1 in Appendix E.

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LAQM Annual Status Report 2016 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 the objectives.

A summary of AQMAs declared by Cannock Chase Council can be found in Table

2.1. Further information related to declared or revoked AQMAs, including maps of

AQMA boundaries are available online10.

We propose to declare a new AQMA in the Heath Hayes area (see monitoring

section).

Table 2.1 – Declared Air Quality Management Areas

AQMA Name

Pollutants and Air Quality

Objectives

City / Town One Line Description Action Plan

AQMA No.1

NO2 annual mean

Churchbridge to Longford

An area encompassing the A5 Watling Street between the junction with the A34 Walsall Road and the district boundary with South Staffordshire, and the stretch of the A460 Wolverhampton Road between the junction with the A5 Watling Street and the district boundary.

The Action Plan can be found at: Link11

AQMA No. 2

NO2 annual mean

Churchbridge

to Norton

Canes

A5 Watling Street between Churchbridge Traffic Islands and the District boundary with Walsall. Effectively continuing the existing AQMA to include all of the A5 within the district.

Proposed AQMA No. 3

NO2 annual mean

Heath Hayes An area centred on ‘Five Ways Island’, Heath Hayes. This is a junction

Not yet developed.

10

http://www.cannockchasedc.gov.uk/business/environmental-health/environmental-protection/local-air-quality-management 11

Air Quality Action Plan: http://www.cannockchasedc.gov.uk/sites/default/files/aqap_nov13.pdf

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LAQM Annual Status Report 2016 3

AQMA Name

Pollutants and Air Quality

Objectives

City / Town One Line Description Action Plan

(Five Ways

Island)

where the A5190 (Cannock Road), B4154 (Hednesford Road) and Wimblebury Road intersect.

2.2 Progress and Impact of Measures to address Air Quality in Cannock Chase District

Cannock Chase Council has taken forward a number of measures during the current

reporting year of 2015 in pursuit of improving local air quality. Details of all measures

completed, in progress or planned are set out in Table 2.2. More detail on these

measures can be found in the overarching Action Plan12.

Key completed measures are:

2a Partnership working: A5 - Commenced & ongoing.

Outcome: ongoing development of an A5

sustainability strategy through the A5 Transport

Partnership Group, and possible extension of

the ECO Stars scheme along the corridor.

3b Junction improvements:

Churchbridge

- Initial scheme completed in 2015.

Reduced congestion on A5 in Bridgtown area

of AQMA1.

4 Smoky vehicle hotline - Ongoing.

Outcome: Facility for public to report smoky

vehicles. Unlikely to have significant impact.

5 Local transport plans - Plans completed.

Outcome: Implementation of measures to

12

http://www.cannockchasedc.gov.uk/sites/default/files/aqap_nov13.pdf

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LAQM Annual Status Report 2016 4

encourage modal shift ongoing.

6

&

7

Travel plans for

businesses within

AQMAs

&

Staffordshire share-a-

lift scheme

- Promotional exercise undertaken in

October/November 2015.

Ongoing scheme implementation.

8 Review of speed

hierarchy

- Review completed.

Recommendations being considered and

implemented where appropriate.

9 Improved cycle facilities - A number of schemes completed, and others

identified for future development.

10 Design guidance - District SPD adopted.

11 Control emissions from

industrial premises

- Continued regulation.

12 Develop policies for

developer contribution

to mitigation measures

- Completion of Planning Design SPD.

13 ECO Stars Fleet

Recognition Scheme

- Commenced 2015.

Progress on the following measures has been slower than expected due to:

2b Partnership Working: M6Toll - Commenced, but slow progress.

3a Junction Improvements:

Watling Street / Walkmill

- HE study ongoing.

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LAQM Annual Status Report 2016 5

Cannock Chase Council expects the following measures to be completed over the

course of the next reporting year:

13 ECO Stars Fleet

Recognition

Scheme

- Initial funding runs for the period 2015/17. The

scheme is being run across Staffordshire & Stoke

and intended to reduce emissions from transport

fleets operating in the area.

Cannock Chase Council’s priorities for the coming year are:

Declare an air quality

management area and

develop an action plan

for the ‘Five Ways Island’

area, Heath Hayes.

- This report demonstrates that an exceedance of

the annual mean NO2 objective is occurring at

roadside locations on the A5190 approaching the

‘Five Ways Island’, where congestion occurs

during peak traffic hours.

- An automatic analyser has been installed in the

area, to provide further evidence.

Continue implementation

of the ECO Stars fleet

recognition scheme and

seek options to fund

continued operation of

the scheme.

- Current funding ends in 2017.

To continue operating the scheme, alternative

funds / operational model are required.

Several potential options are being examined,

involving the A5 Transport Partnership Group and

SBEN

Work with Highways

England to seek junction

improvements at A5 /

Walkmill Lane / North

Street

- Prohibition of right turns into North Street has been

included in Highways England wider pedestrian

facilities scheme. This scheme is currently

included in Highways England’s 5-year bid for

funding. Highways England is continuing to liaise

with CCDC and Staffs County Council regarding

progress with this scheme.

Contributions towards junction alterations would

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LAQM Annual Status Report 2016 6

need securing in order to undertake this option. To

this end an evidential case will be required,

considering appropriate data, the works to be

included, and likelihood of securing contributions.

Request mitigation

measures / developer

contributions from major

developments in the

district.

- As developments occur in the vicinity of the

AQMAs or significant developments elsewhere in

the district, Environmental Health Dept. will request

that appropriate mitigation measures are included

or developer contributions towards sustainable

travel.

Emission costs to be calculated based on Defra’s

damage cost approach utilising guidance found at

Link13 and Link14.

13

https://www.gov.uk/government/publications/green-book-supplementary-guidance-air-quality 14

https://www.gov.uk/air-quality-economic-analysis

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Cannock Chase Council

LAQM Annual Status Report 2016 www.cannockchasedc.gov.uk

This table provides a summary of revised action plan measures reported the Air Quality Action Plan Progress Report 2015, and

progress since the report was published. See link15 for 2015 report.

Table 2.2 – Progress on Measures to Improve Air Quality

Measure No.

Measure EU Category EU

Classification Lead

Authority Planning

Phase Implementation

Phase

Key Performance

Indicator

Target Pollution

Reduction in the AQMA

Progress to Date Estimated

Completion Date

Comments

1 LDV/HDV advice on routing

Traffic Management

Other Highways England

Ongoing Not identified

Evaluate potential benefits and to

continue to work to secure funding for

this option.

Not identified

None reported Not identified

Lodge Lane provides an

alternative route for traffic travelling

between junction 11 of the M6 and

Churchbridge, which would

otherwise use the A5 Watling

Street.

Optimising its use will direct

traffic away from the Bridgtown

AQMA and thereby reduce emissions in the

locality.

Liaison with Staffordshire

County Council. Consider potential impacts on local

roads.

2a Partnership

Working:

Transport Planning and Infrastructure

Other CCDC:

Environmental

Ongoing Not identified Complete

accessibility mapping

Not identified

Action Plan for the A5 from A449 Gailey (Staffordshire) to

Ongoing See AQAP

Progress Report 2015

16

15

Cannock Chase Council Air Quality Action Plan Progress Report: http://www.cannockchasedc.gov.uk/sites/default/files/aqap_progress.pdf 16

http://www.cannockchasedc.gov.uk/sites/default/files/aqap_progress.pdf

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LAQM Annual Status Report 2016 www.cannockchasedc.gov.uk

Measure No.

Measure EU Category EU

Classification Lead

Authority Planning

Phase Implementation

Phase

Key Performance

Indicator

Target Pollution

Reduction in the AQMA

Progress to Date Estimated

Completion Date

Comments

A5 Health

Local Planning & Economic Development

Completion of A5 Sustainability

Strategy

A508/A422 Old Stratford

(Northamptonshire) published Sept 2015

Members have agreed

to pursue development of an ECO Stars Fleet

Recognition Scheme.

2b

Partnership Working:

M6Toll

Transport Planning and Infrastructure

Other

CCDC:

Environmental Health

Ongoing Not identified

Dialogue with Midlands

Expressway Ltd., to explore options for encouraging HDVs onto the

M6Toll in preference to the

A5.

Not identified

MEL have provided data relating

to a traffic study undertaken in 2014.

N/A See AQAP

Progress Report 2015

17

3a

Junction Improvements:

Watling Street / Walkmill Lane /

North Street

Traffic Management

Strategic highway improvements, Re-

prioritising road space away from

cars, including Access

management, Selective vehicle

priority, bus priority, high

vehicle occupancy lane

Highways England

Cannock Chase Council

2015/16 Not identified

Completion of Highways England

study work to investigate

potential options for the junction.:

Not identified

Link Not identified Link

17

http://www.cannockchasedc.gov.uk/sites/default/files/aqap_progress.pdf

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Measure No.

Measure EU Category EU

Classification Lead

Authority Planning

Phase Implementation

Phase

Key Performance

Indicator

Target Pollution

Reduction in the AQMA

Progress to Date Estimated

Completion Date

Comments

3b

Junction Improvements:

Churchbridge

Traffic Management

Strategic highway improvements, Re-

prioritising road space away from

cars, including Access

management, Selective vehicle

priority, bus priority, high

vehicle occupancy lane

Highways England

Cannock Chase Council

2020 Not identified

Completion of Highways England assessment of the

requirement for further capacity improvements to

Churchbridge Junction, post

2020.

Not identified

Pinchpoint funding allowed junction

improvements to be undertaken in 2015.

Not identified

This measure is intended to improve the

efficiency of the complex of traffic

islands at Churchbridge.

Eastbound traffic congestion on the A5, feeding into

the Churchbridge junction adds to

the pollution levels in

Bridgtown. Reduced

congestion is expected to reduce this

impact.

Further study beyond 2020 required to account for

projected future traffic growth.

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Measure No.

Measure EU Category EU

Classification Lead

Authority Planning

Phase Implementation

Phase

Key Performance

Indicator

Target Pollution

Reduction in the AQMA

Progress to Date Estimated

Completion Date

Comments

4 Smoky Vehicle

Hotline Pubic

Information Other Cannock

Chase Council N/A Ongoing

Continue publicising the

VOSA service on the CCDC website.

18

Not identified

Ongoing Ongoing

Focus: To discourage dirty,

un-serviced vehicles from

operating in the district.

Smoky emissions are not directly correlated with NOx emissions.

However, servicing and

maintenance of vehicles will

improve overall emissions.

Impact likely to be insignificant. In

2014 only 5 smoky diesel reports were made for the

entire Staffordshire and Derbyshire region. VOSA are unable

to report on a district level.

18

https://www.gov.uk/report-smoky-vehicle

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Measure No.

Measure EU Category EU

Classification Lead

Authority Planning

Phase Implementation

Phase

Key Performance

Indicator

Target Pollution

Reduction in the AQMA

Progress to Date Estimated

Completion Date

Comments

5 Local Transport

Plans

Transport Planning and Infrastructure

Various Staffordshire

County Council

N/A 2013 - 2028

Improve public transport to the West Midlands

Support A5(T) Churchbridge Improvements

Encourage Sustainable Transport

Not identified

Transport Plan completed:

Link

19 to local

transport plans.

Ongoing implementation.

To encourage modal shift from private vehicle use to public

transport. Thereby reducing overall

emissions.

6 Travel Plans for

Businesses within AQMAs.

Promoting Travel

Alternatives

Workplace Travel Planning

Staffordshire County Council

N/A Ongoing Continue to

operate function. Not

identified

A mailing exercise has been undertaken

during October/November

2015 for all businesses in

postcodes within 500 metres of the A5.

Aim: to inform businesses of:

existing programmes designed to reduce

emissions and congestion.

The ECO Stars

Scheme.

Ongoing

Staffordshire County Council to

process any expressions of interest from businesses. 7

Staffordshire’s Share-a-Lift

Scheme

Promoting Travel

Alternatives

Workplace Travel Planning

Staffordshire County Council

N/A Ongoing

Continue to operate function.

Link

20

Not identified

Ongoing

19

http://www.staffordshire.gov.uk/transport/transportplanning/localtransportplan/Integrated-transport-documents/Cannock-Transport.pdf 20

https://share-a-lift.co.uk/x.jsp?ano=0

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Measure No.

Measure EU Category EU

Classification Lead

Authority Planning

Phase Implementation

Phase

Key Performance

Indicator

Target Pollution

Reduction in the AQMA

Progress to Date Estimated

Completion Date

Comments

8

Review of Road Hierarchy

and Speed Limits

Traffic Management

Reduction of speed limits, 20mph zones

Other

Highways England

Completed Completed

Consideration being given to the matter and funding

being sought

Not identified

It is understood that the speed limit review has been concluded

and recommendations are being

implemented at individual sites on a local priority basis

through the Divisional Highway Programme.

Completed

9 Improved Local Cycle Facilities

Transport Planning and Infrastructure

Cycle network

Public transport improvements-interchanges stations and

services

Cannock Chase Council

Staffordshire County Council

Implementation of Local Plans:

- Provision of segregated cycling routes within new commercial and residential. Development (in excess of 200 dwellings). a. Red Lion Lane Development, Norton Canes. Pursue upgrade of mineral line upon completion of housing development.

Not identified

Link Ongoing

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Measure No.

Measure EU Category EU

Classification Lead

Authority Planning

Phase Implementation

Phase

Key Performance

Indicator

Target Pollution

Reduction in the AQMA

Progress to Date Estimated

Completion Date

Comments

- Provision of demarcated cycle corridors and cycle crossings in existing highways, new road schemes, traffic management and traffic calming schemes. - Provision of secure cycle parking facilities in town centres, railway stations and new retail development creating at least 2500 sqm gross under the requirements of a planning application.

10 Design

Guidance

Policy Guidance and Development

Control

Air Quality Planning and

Policy Guidance

Cannock Chase Council

Planning Department

2016 Ongoing Adoption of District Design Guidance

SPD

Not identified

Completed Completed Link21

11

Control emissions from

industrial premises

Environmental Permits

Other

Cannock Chase Council

Environment Agency

N/A Ongoing Continued Regulation

Not identified

Ongoing N/A Link22

21

http://www.cannockchasedc.gov.uk/residents/planning/planning-policy/supplementary-planning-policy-documents 22

https://www.cannockchasedc.gov.uk/residents/environmental-health/environmental-protection/environmental-permitting-regulations

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Measure No.

Measure EU Category EU

Classification Lead

Authority Planning

Phase Implementation

Phase

Key Performance

Indicator

Target Pollution

Reduction in the AQMA

Progress to Date Estimated

Completion Date

Comments

12

Develop policies for developer

contribution to mitigation measures

Policy Guidance and Development

Air Quality Planning and

Policy Guidance

Cannock Chase Council

Planning

& Environmental

Health Departments

N/A N/A

Liaise with Planning

Department to identify/ develop procedures to

obtain developer contributions

towards mitigation measures.

Not identified

Completed Completed

Link23

to

Policy CP10 Sustainable Transport

Link

24 to

Infrastructure Delivery Plan for projects requiring

funding.

13

ECO Stars Fleet

Recognition Scheme

Vehicle Fleet Efficiency

Fleet efficiency and recognition

schemes

Cannock Chase Council

7 other Staffordshire &

Stoke authorities

TTR Ltd (transport

consultants)

N/A

2015/17

Continuation of scheme. Under the

terms of the contract, TTR will recruit 40 vehicle fleets that operate in the combined local authority

areas.

Not identified.

However, a calculation

tool has been

developed by TTR to

allow emission

savings to be

evaluated.

Scheme commenced in 2015.

Official scheme launch

in February 2016.

Staffordshire and Stoke recruitment

update as of 8 December 2015:

24 members

Initial funding phase 2017.

Details of how the scheme operates can be found at

Link25

and Link26

.

2016

Investigate potential funding

sources to continue the

scheme beyond the initial two year

period.

23

http://www.cannockchasedc.gov.uk/sites/default/files/local_plan_part_1_09.04.14_low_res.pdf 24

http://www.cannockchasedc.gov.uk/sites/default/files/infrastructure_delivery_plan_may_2014_update.pdf 25

http://www.ecostars-uk.com/about-eco-stars/introduction/ 26

http://www.cannockchasedc.gov.uk/business/environmental-health/environmental-protection/eco-stars-fleet-recognition-scheme

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Progress: Highways England Summary for the proposed Walkmill Lane junction improvements, January 2016

The scheme was first developed in 2011, when the then Highways Agency asked Amey to add the air quality considerations on to a pedestrian facilities scheme.

The original scheme required drivers to turn at Delta Way. This is no longer desirable, as the Delta Way junction is an accident cluster site.

Staffordshire County Council previously investigated a similar scheme in the 1990s, but this was shelved due to significant negative feedback from local residents.

The junctions have been improved since 2011, for example the signals at the Walkmill Lane junctions have been upgraded to MOVA. This has improved traffic flows.

New options are available, such as directing traffic to turn left down Walkmill Lane at the Bridge Street junction.

Consideration can be given to including NMU improvements and safety improvements at Delta Way. Way Forward

Updated air quality and traffic survey data is required (the data for the previous scheme was gathered in 2009-2011).

An options appraisal will be required to identify the most effective scheme.

Consultation will be required for the TRO to ban right-turns if this option is selected. Improvements to the Walkmill Lane/Walkmill Lane junction on the local road network could be considered.

Any scheme will be required to go through Highways England’s value management process, and will be assessed for funding in competition with other schemes. Funding will be dependent upon the outcome of this process.

Actions

Kier & Environmental Health to exchange air quality monitoring data and location of monitoring equipment;

HE to seek funding for traffic surveys and air quality study;

Highways England Air Quality team to be consulted on how this sits with Highways England’s Air Quality policies;

HE, Kier and Environmental Health to review.

Cycleways Progress The Local Plan Part 1, adopted in June 2014, includes the following measures:

Policy CP3 Design - ‘ optimise promotion of active design increasing opportunities for physical activity and community interaction’

Policy CP5 Social Inclusion and Healthy Living – key elements of infrastructure to support healthy living listed include ‘cycling/pedestrian routes and pathways’

District’s strategic cycle network as identified on the Policies map and introduce measures to improve and provide facilities for cyclists including

the provision of segregated cycling routes within new commercial and residential development (in excess of 200 dwellings)

the provision of demarcated cycle corridors and cycle crossings in existing highways, new road schemes, traffic management and traffic calming schemes

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the provision of secure cycle parking facilities in town centres, railway stations and new retail development creating at least 2500 sqm gross trading floor space

the provision of secure cycle parking, showers and lockers at all major new employment sites, existing commercial premises, as part of a travel plan submitted under the requirements of an planning application

Policy CP15 Historic Environment – ‘The sustainable access and enjoyment of heritage assets District wide will also be promoted through the strengthening of the District’s green infrastructure and creation of footway/cycleway routes’.

Cycleways also feature in our Infrastructure Delivery Plan, which is the mechanism for identifying infrastructure required, for which either S106 funds or CIL payments can be based. Examples of cycling facility provision include the following: Within the vicinity of the AQMAs:

Red Lion Lane development, Norton Canes. - This housing development commenced 2014. Upgrade of mineral line will potentially follow completion of housing dev site.

Elsewhere in the district

Heritage Trail (2008/9). - There is potential for improved links on Hagley Park, Rugeley subject to an Environment Agency flood alleviation scheme in 2015-6. This scheme is to be confirmed.

Pye Green Valley. - A cycleway has been installed by Staffordshire County Council as part of road scheme to serve a new development site.

Pye Green Road Developments - Plans for cycleways linking to green corridor and Pye Green Valley.

Rugeley - Cycleway scheme to connect Rugeley town centre to the new Tescos/canal implemented 2014 and completed spring 2015.

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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.

Particulate matter, or PM, is the term use to describe particles found in the air,

including dust, dirt and liquid droplets. PM comes from both natural and man-made

sources, including traffic emissions and Saharan-Sahel dust. These particles can be

suspended in the air for long periods of time, and can travel across large distances.

PM less than 10 micrometers in diameter (PM10) pose a health concern because they

can be inhaled into and accumulate in the respiratory system. PM less than 2.5

micrometers in diameter (PM2.5) are referred to as "fine" particles and are believed to

pose the greatest health risks, as they can lodge deeply into the lungs and also pass

into the bloodstream.

PM2.5 is the pollutant which has the biggest impact on public health and on which the

Public Health Outcomes Framework (PHOF) indicator 3.0127 is based.

The Royal College of Physicians (RCP) undertook a review in February 2016 28

where they found that long term exposure to air pollution impairs lung function growth

in children, and that outdoor exposure is linked to lung cancer in adults. Within

Staffordshire it is estimated that 5%of all deaths can be attributed to exposure to

PM2.5, compared to 5.3% across England (40,000 deaths annually). Overall, the

estimated cost to individuals and society is more than £20 billion annually for the UK.

27 27 Public Health Outcomes Framework 2016-2019Indicator 3.01 Fraction of mortality attributable to particulate air pollution

https://www.gov.uk/government/uploads/system/uploads/attachment_data/file/520457/At_a_glance.pdf

28

[‘Every Breath we Take: The Lifelong Impact of Air Pollution; Report of a working Party, February 2016, ISBN 978-1-86016-567-2],

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2.3.1 Particulate Matter (PM2.5) Levels in Staffordshire and Stoke-on-Trent

A number of the Staffordshire Authorities currently monitor locally for PM10. Defra’s

Automatic Urban and Rural Network (AURN) site, Stoke-on-Trent Centre, has a

dedicated PM2.5 monitor. Error! Reference source not found. presents data on the local

level of PM2.5 annual mean concentrations for the Staffordshire Authorities. Where

the data is derived from PM10 monitoring this has been adjusted by applying a

correction factor of 0.7 to derive the PM2.5 component. The correction factor has been

derived from the average of all ratios of PM2.5/PM10 for the years from 2010 to 2014

for forty sites within the Automatic Urban and Rural Network (AURN) where these

substances are measured on an hourly basis and follows the guidance published in

LAQM (TG16).

Table 1: Annual Mean PM10 and PM2.5 Results of monitoring by Staffordshire Authorities 2011 to 2015

Annual Mean PM10 and PM2.5

Results from monitoring by Staffordshire Authorities 2011 to 2015

Authority Site Type Monitor Location

OS Grid Ref

Year

2011 2012 2013 2014 2015

Newcastle under Lyme

Roadside Queen’s Gardens

E385057 N346137

PM10 - 14.9 22.5 22 22.9

PM2.5 - 10.43(1)

15.75(1)

15.4(1)

16(1)

Cannock Chase

Roadside Watling Street,

Bridgtown SJ980086

PM10 22 23 21 19.6 -(2)

PM2.5 15.4(1)

16.1(1)

14.7(1)

13.7(1)

Stoke on Trent

Roadside A50 Meir Tunnel

E392548 N342572

PM10 - - - - 20(3)

PM2.5 - - - - 14(3)

Urban background

Stoke on Trent

Central

E388351 N347895

PM2.5 12 11 10 10 12

Roadside Middleport E385780 N349376

PM10

25 24 25 24 22

PM2.5 18(1)

17(1)1

18(1)

17(1)

15(1)

East Staffordshir

e Roadside Derby Turn

E424671 N324019

PM10 26.9 25.4 29 31 23

PM2.5 18.8(1) 17.8(1) 20.3(1) 21.7(1) 16.1(1)

Notes: (1)

PM2.5 results are derived from PM10 monitored results corrected with a 0.7 correction factor in accordance with TG16 - Annex B: Derivation of PM2.5 to PM10 Ratio. All other results are directly monitored. (2)

Cannock Chase Watling Street Bridgwtown PM10 monitor decommissioned (3)

Valid data capture for 2015 was 59%. The site was commissioned on 22 May 2015.

As can be seen from the results, concentrations of PM2.5 within the Staffordshire

Authorities are below the 2020 EU limit value of 25µg/m3.

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2.3.2 PM2.5 and Mortality in Staffordshire & Stoke-on-Trent

Although the levels of PM2.5 within the County and City of Stoke on Trent are below

the 2020 EU Limit value, the impact on adult mortality directly attributable to PM2.5 is

nonetheless still an important public health issue within Staffordshire and Stoke-on-

Trent. This is revealed in data obtained from Public Health England used to inform

Public Health Outcomes Framework indicator 3.0129, as shown in Table 2. The data

presented to 2013 is the latest data available at time of publication of this report.

Approximately 5% of deaths within the County can be attributed to PM2.5.

The percentage estimated number of deaths attributable to PM2.5 in adults over 30

has been translated into the estimated number of attributable deaths for each local

authority area within Staffordshire, and are shown in Table 3.

Table 2: Public Health Outcomes Framework Indicator 3.01- Fraction of annual all cause adult mortality attributable to anthropogenic (human made) particulate air pollution (measured as fine particulate matter, PM2.5 ) for Staffordshire Authorities 2010 to 201330.

District/County Percentage

Newcastle-under-Lyme 4.8%

Stafford 4.8%

East Staffordshire 5.0%

South Staffordshire 4.9%

Lichfield 5.1%

Staffordshire Moorlands 4.4%

Cannock Chase 5.0%

Tamworth 5.4%

Stoke 5.1%

Staffordshire County 4.9%

England 5.3%

29 Public Health Outcomes Framework 2016-2019Indicator 3.01 Fraction of mortality attributable to particulate air pollution

https://www.gov.uk/government/uploads/system/uploads/attachment_data/file/520457/At_a_glance.pdf

30

Source Public Health England www.fingertips.phe.org.uk- Public Health Outcomes Framework Indicator 3.01

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Table 3: Estimated number of deaths by local authority area attributable to PM2.5 within Staffordshire for adults over 30- 2011 to 2013

Estimated numbers of annual all-cause adult mortality attributable to anthropogenic (human-made) particulate air pollution (measured as fine particulate matter, PM2.5*) for Staffordshire 2011 to 2013

Error!

Bookmark not defined.

* Fraction of annual all-cause adult mortality attributable to anthropogenic (human-made) particulate air pollution (measured as fine particulate matter, PM2.5*)

2011 2012 2013

District/County Deaths - all

causes persons 30+

Percentage* Estimated attributable

deaths

Deaths - all causes

persons 30+ Percentage*

Estimated attributable

deaths

Deaths - all causes

persons 30+ Percentage*

Estimated attributable

deaths

Newcastle-under-Lyme

1187 4.8% 57 1218 4.6% 56 1295 4.9% 63

Stafford 1178 4.7% 55 1195 4.6% 55 1261 4.9% 62

East Staffordshire 972 4.9% 48 966 4.8% 46 1097 5.1% 56

South Staffordshire 1009 4.9% 49 1162 4.8% 56 1102 5.1% 56

Lichfield 902 5.1% 46 953 5.0% 47 1050 5.1% 54

Staffordshire Moorlands

927 4.4% 41 1020 4.2% 43 1085 4.7% 51

Cannock Chase 766 5.0% 38 844 4.8% 41 787 5.1% 40

Tamworth 532 5.4% 29 553 5.2% 29 592 5.5% 33

Staffordshire

County 7473 4.9% 366 7911 4.7% 372 8269 5.0% 417

2.3.3 Actions being taken within Staffordshire to reduce PM2.5

A number of the Staffordshire Authorities are currently involved in implementing measures to reduce levels of N02 within their areas, which are detailed elsewhere in this report. Whilst there is currently no statutory duty imposed on Local Authorities in England to reduce PM2.5, a number of the measures are complementary. A mapping exercise completed by the Staffordshire Air Quality Forum members details the measures currently in place which are considered to have an impact in reducing PM2.5 within the County. These are produced in Table 4.

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Table 4: Existing Staffordshire & Stoke Authority Actions for PM2.5

Measures category

Measure Classification

Effect on reducing NOx and

PM10 emissions(l

ow, medium,

high)

Reduces PM2.5 emissio

ns

Local Authority

Stoke on Trent CC

Staffordshire

Moorlands DC

Newcastle- under- Lyme

BC

Stafford BC

Cannock Chase

DC

East Staffs

BC

Lichfield DC

South Staffs

DC

Tamworth BC

Traffic Management

Urban Traffic Control systems, Congestion management, traffic reduction

low Link

UTC in Leek town

centre

UTC in areas of Newcastle Town

Centre AQMA and Kidsgrove AQMA

UTC in Stafford

town centre

UTC in Cannock

town centre

UTC in Burton town

centre

- -

UTC in Tamworth

town centre and

Ventura Park

Reduction of speed limits, 20mph zones

low

multiple 20mph

zones in place as shown on cycle map:

Link

nil nil

20 mph zones near

some schools in residential

areas

nil

Road User Charging (RUC)/ Congestion charging

low nil nil nil nil M6 Toll nil M6 Toll M6 Toll nil

Anti-idling enforcement

low nil Advisory None

Other -

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Measures category

Measure Classification

Effect on reducing NOx and

PM10 emissions(l

ow, medium,

high)

Reduces PM2.5 emissio

ns

Local Authority

Stoke on Trent CC

Staffordshire

Moorlands DC

Newcastle- under- Lyme

BC

Stafford BC

Cannock Chase

DC

East Staffs

BC

Lichfield DC

South Staffs

DC

Tamworth BC

Promoting Travel Alternatives

Workplace Travel Planning

low

Travel Plan Grant Scheme Link

https://www.staffordshire.gov.uk/transport/greentravel/travelplans/home.aspx

Encourage / Facilitate home-working

low

Agile working

adopted by Stoke-on-Trent CC

Agile working adopted by

Newcastle under Lyme B.C.

Homeworking policy adopted

Workstyle adopted by South Staffs

Council

Agile working

adopted by Tamworth

B.C.

School Travel Plans

low Link https://www.staffordshire.gov.uk/transport/Stafford/Schools/School-Travel-STARS.aspx

Promotion of cycling

low Link https://www.staffordshire.gov.uk/transport/greentravel/cycling/Cycling.aspx

Promotion of walking

low Link https://www.staffordshire.gov.uk/Search.aspx?search_keywords=walking

Staffordshire Share a Lift Scheme

Link https://www.staffordshire.gov.uk/transport/greentravel/carsharing/Q002.aspx

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Measures category

Measure Classification

Effect on reducing NOx and

PM10 emissions(l

ow, medium,

high)

Reduces PM2.5 emissio

ns

Local Authority

Stoke on Trent CC

Staffordshire

Moorlands DC

Newcastle- under- Lyme

BC

Stafford BC

Cannock Chase

DC

East Staffs

BC

Lichfield DC

South Staffs

DC

Tamworth BC

Promote use of rail and inland waterways

medium Link

Staffordshire County Council

Draft Rail Strategy is available

from: Link

& Link

Community Rail Partnership

operating along the North Staffordshire

Line including Kidsgrove Rail Station which

heavily involves the local community.

The County Council is a member of Rail

North Ltd whose role includes the

local management of rail services operating to Manchester Piccadilly.

Staffordshire County Council

Draft Rail Strategy is available from:

Link &

Community Rail

Partnership operating along the

North Staffordshire Line and

includes Blythe

Bridge Rail Station.

Staffordshire County Council is a member of West

Midlands Rail Ltd

which will bring a

change in the way

that local rail

services are

managed and

operated. The

County Council

Draft Rail Strategy is available

from: Link

Staffordshire County Council is a member of West

Midlands Rail Ltd

which will bring a

change in the way

that local rail

services are

managed and

operated. The

County Council

Draft Rail Strategy is available

from: Link

31

& Link

32

Community Rail

Partnership operating along the

North Staffordshire Line and

includes Uttoxeter

Rail Station.

The County Council

Draft Rail Strategy is available

from: Link

Staffordshire County Council is a member of West

Midlands Rail Ltd

which will bring a

change in the way

that local rail

services are

managed and

operated. The

County Council

Draft Rail Strategy is available

from: Link

Staffordshire County

Council is a member of

West Midlands Rail Ltd

which will bring a

change in the way that

local rail services are

managed and

operated. The County

Council Draft Rail Strategy is available

from: Link

Staffordshire County Council is a member of West

Midlands Rail Ltd

which will bring a

change in the way

that local rail

services are

managed and

operated. The

County Council

Draft Rail Strategy is available

from: Link

& Link

31

http://moderngov.staffordshire.gov.uk/documents/s69891/Appendix%201%20for%20Rail%20Strategy.pdf 32

https://www.staffordshire.gov.uk/transport/transportplanning/localtransportplan/draftcannockchasedistricttransportstrategy2011.pdf

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Measures category

Measure Classification

Effect on reducing NOx and

PM10 emissions(l

ow, medium,

high)

Reduces PM2.5 emissio

ns

Local Authority

Stoke on Trent CC

Staffordshire

Moorlands DC

Newcastle- under- Lyme

BC

Stafford BC

Cannock Chase

DC

East Staffs

BC

Lichfield DC

South Staffs

DC

Tamworth BC

Transport Planning and Infrastructure

Local Transport Plans and District Strategies

high Link Link

& Link

Public transport improvements-interchanges stations and services

low

Improvements around Stoke-on-

Trent railway

station in developme

nt

Kidsgrove Station Interchange planned for 2018 Link

Recent improveme

nts completed at Stafford

Rail Station

Planned Improveme

nts at Cannock Station as part of Mill

Green developme

nt

Planned improveme

nts at Burton Rail

Station

Planned improveme

nts at Lichfield

City as part of

Friarsgate Developme

nt. LTV improveme

nts to make the

station accessible

-

Planned improveme

nts at Tamworth

Rail Station

including future

aspirations to integrate buses with Tamworth

Rail Station

Public cycle hire scheme

low

Stoke Railway Station

'Brompton Dock' Bike

Hire &

Nil

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Measures category

Measure Classification

Effect on reducing NOx and

PM10 emissions(l

ow, medium,

high)

Reduces PM2.5 emissio

ns

Local Authority

Stoke on Trent CC

Staffordshire

Moorlands DC

Newcastle- under- Lyme

BC

Stafford BC

Cannock Chase

DC

East Staffs

BC

Lichfield DC

South Staffs

DC

Tamworth BC

Cycle Hub Link

Cycle network low

Link Stoke-on-

Trent Cycle Map & Guide

https://www.staffordshire.gov.uk/transport/greentravel/cycling/Cycling.aspx

Bus route improvements

high

Improvements around Stoke-on-

Trent railway

station in development - station road bus

routes

Proposed improvements to route 9 Biddulph-Hanley and

route 99 Biddulph-

Macclesfield

Proposed improvements to routes 3 and 4

Newcastle Town Centre

Proposed installation of RTPI on

radial routes in Stafford

Proposed improveme

nts to services

23,24 and 26 in

Rugeley, service 2 Cannock-Walsall

and service 32/33 Pye

Green

RTPI Burton Town

Centre

Proposed new or

extended services linked to the City Centre

funded via developer contributio

ns

Proposed improvemen

ts to services

linking to i54 plus RTPI,

improvements to Gt Wyrley-Bloxwich corridor,

Wombourne routes 256 and 255, Codsall-

Wolverhampton route 5, Huntington-

Walsall route 1 and

Stafford-Wolverhampton route 76

Proposed improvements to local service 2 and RTPI

at key locations

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Measures category

Measure Classification

Effect on reducing NOx and

PM10 emissions(l

ow, medium,

high)

Reduces PM2.5 emissio

ns

Local Authority

Stoke on Trent CC

Staffordshire

Moorlands DC

Newcastle- under- Lyme

BC

Stafford BC

Cannock Chase

DC

East Staffs

BC

Lichfield DC

South Staffs

DC

Tamworth BC

Alternatives to private vehicle use

Bus based Park & Ride

medium nil

Kidsgrove Station Interchange planned for 2018 Link

nil nil nil nil nil nil

Car Clubs low nil nil nil nil nil nil nil nil nil

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Measures category

Measure Classification

Effect on reducing NOx and

PM10 emissions(l

ow, medium,

high)

Reduces PM2.5 emissio

ns

Local Authority

Stoke on Trent CC

Staffordshire

Moorlands DC

Newcastle- under- Lyme

BC

Stafford BC

Cannock Chase

DC

East Staffs

BC

Lichfield DC

South Staffs

DC

Tamworth BC

Policy Guidance and Development Control

Planning applications to require assessment of exposure / emissions for development requiring air quality impact assessment

high

Public Procection

Division consulted

on all planning

application and

included in pre-

planning advice

Local Validation List Link -applications/information-requirements-and-validation-planning. Development screened following IAQM air quality for planning guidance. Link

Local plan - Policy CP16 - Climate Change

and Sustainable Resource

Use Cannock chase.

Link

33

Link

Link

We ask for AQ

assessments on all large

scale developmen

ts

Link

Air Quality Strategy

Local Air Quality

Strategy - Stoke-on-Trent City Council

Link

To include PM2.5 in emerging AQS

nil Yes To be

updated

33

http://www.cannockchasedc.gov.uk/sites/default/files/local_plan_part_1_09.04.14_low_res.pdf

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Measures category

Measure Classification

Effect on reducing NOx and

PM10 emissions(l

ow, medium,

high)

Reduces PM2.5 emissio

ns

Local Authority

Stoke on Trent CC

Staffordshire

Moorlands DC

Newcastle- under- Lyme

BC

Stafford BC

Cannock Chase

DC

East Staffs

BC

Lichfield DC

South Staffs

DC

Tamworth BC

Planning Guidance for developers

To develop planning guidance for developers and to develop into SPD once Local Plan Polices in Place

To develop planning guidance for developers and to develop into SPD once Local Plan Polices in Place

Link34

Developer Contributions based on damage cost calcualtion

To develop polices to secure contributions to offset pollution

To develop polices to secure contributions to offset pollution

Link

35

34

http://www.cannockchasedc.gov.uk/residents/planning/planning-policy/supplementary-planning-policy-documents 35

http://www.cannockchasedc.gov.uk/sites/default/files/local_plan_part_1_09.04.14_low_res.pdf

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Measures category

Measure Classification

Effect on reducing NOx and

PM10 emissions(l

ow, medium,

high)

Reduces PM2.5 emissio

ns

Local Authority

Stoke on Trent CC

Staffordshire

Moorlands DC

Newcastle- under- Lyme

BC

Stafford BC

Cannock Chase

DC

East Staffs

BC

Lichfield DC

South Staffs

DC

Tamworth BC

Planning Policies

To influence polices to support

improvement in

emissions through

development of

Staffordshire and

Stoke on Trent Joint Local Plan

Link

To influence polices to support improvement in emissions through development of Staffordshire and Stoke on Trent Joint Local Plan Link

Air quality policy

adopted for development control

None

STOR Sites (Short Term Operating Reserve) Energy Generation . Regulation via planning / permitting regime

high To lobby Central Government via appropriate forums (e.g. Staffordshire Air Quality Forum / Midlands Joint Advisory Council) for

consideration of air quality implications at a national level and to support local authorities and developers with apprpropiate guidance

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Measures category

Measure Classification

Effect on reducing NOx and

PM10 emissions(l

ow, medium,

high)

Reduces PM2.5 emissio

ns

Local Authority

Stoke on Trent CC

Staffordshire

Moorlands DC

Newcastle- under- Lyme

BC

Stafford BC

Cannock Chase

DC

East Staffs

BC

Lichfield DC

South Staffs

DC

Tamworth BC

Low Emissions Strategy

high

Freight and Delivery Management

Freight Consolidation Centre

medium

Route Management Plans/ Strategic routing strategy for HGV's

high https://www.staffordshire.gov.uk/transport/transportplanning/localtransportplan/appendixl-staffordshirefreightstrategy.pdf

Quiet & out of hours delivery

low

Delivery and Service plans

medium

Freight Partnerships for city centre deliveries

high

Vehicle Fleet Efficiency

Driver training and ECO driving aids

medium

Promoting low emission public transport

high

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Measures category

Measure Classification

Effect on reducing NOx and

PM10 emissions(l

ow, medium,

high)

Reduces PM2.5 emissio

ns

Local Authority

Stoke on Trent CC

Staffordshire

Moorlands DC

Newcastle- under- Lyme

BC

Stafford BC

Cannock Chase

DC

East Staffs

BC

Lichfield DC

South Staffs

DC

Tamworth BC

Vehicle retrofitting programmes

medium

Fleet efficiency and recognition schemes

medium Staffordshire and Stoke-on-Trent Eco-Stars http://www.ecostars-uk.com/eco-stars-schemes/

Promoting low emission transport

Low emission zone (LEZ) Clean Air Zone (CAZ)

high

Public Vehicle Procurement -Prioritising uptake of low emission vehicles

high

Company Vehicle Procurement -Prioritising uptake of low emission vehicles

high

Procuring alternative Refuelling infrastructure to promote Low Emission Vehicles, EV recharging, Gas fuel recharging

high

Electricity Re-charge Points at some car-

parks

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Measures category

Measure Classification

Effect on reducing NOx and

PM10 emissions(l

ow, medium,

high)

Reduces PM2.5 emissio

ns

Local Authority

Stoke on Trent CC

Staffordshire

Moorlands DC

Newcastle- under- Lyme

BC

Stafford BC

Cannock Chase

DC

East Staffs

BC

Lichfield DC

South Staffs

DC

Tamworth BC

Priority parking for LEV's

high Link

Taxi Licensing conditions

medium

Hackney Carriage &

Private Hire

Licensing Policy

2016-2019 (Draft)

Taxi emission incentives

medium

Environmental permits

Introduction/increase of environment charges through permit systems and economic instruments (Permit fees set centrally)

medium Unable to achieve at a local level without central government approval

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Measures category

Measure Classification

Effect on reducing NOx and

PM10 emissions(l

ow, medium,

high)

Reduces PM2.5 emissio

ns

Local Authority

Stoke on Trent CC

Staffordshire

Moorlands DC

Newcastle- under- Lyme

BC

Stafford BC

Cannock Chase

DC

East Staffs

BC

Lichfield DC

South Staffs

DC

Tamworth BC

Measures to reduce pollution through IPPC Permits going beyond BAT

medium https://www.gov.uk/government/uploads/system/uploads/attachment_data/file/211863/env-permitting-general-guidance-a.pdf (Chapter

15)

Large Combustion Plant Permits and National Plans going beyond BAT

high

Other ??

Other measures

Smoky Diesel Hotline

https://www.gov.uk/report-smoky-vehicle

A5 and M6 Partnership

Link36

Link

36

http://www.hinckley-bosworth.gov.uk/info/10020/strategies_plans_and_policies/1272/a5_partnership

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Measures category

Measure Classification

Effect on reducing NOx and

PM10 emissions(l

ow, medium,

high)

Reduces PM2.5 emissio

ns

Local Authority

Stoke on Trent CC

Staffordshire

Moorlands DC

Newcastle- under- Lyme

BC

Stafford BC

Cannock Chase

DC

East Staffs

BC

Lichfield DC

South Staffs

DC

Tamworth BC

Domestic Smoke Control advice and Enforcement

Link Link Link37

Link Link Link

37

http://www.cannockchasedc.gov.uk/residents/environmental-health/environmental-protection/chimney-smoke

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Measures category

Measure Classification

Effect on reducing NOx and

PM10 emissions(l

ow, medium,

high)

Reduces PM2.5 emissio

ns

Local Authority

Stoke on Trent CC

Staffordshire

Moorlands DC

Newcastle- under- Lyme

BC

Stafford BC

Cannock Chase

DC

East Staffs

BC

Lichfield DC

South Staffs

DC

Tamworth BC

Garden Bonfires - Advice and nuisance enforcement

Link Link38

Link Link Link Link

Commercial burning advice and enforcement

Link

Legislation enforced - web page currently

being developed

Legislation enforced - web page currently

being developed

38

http://www.cannockchasedc.gov.uk/residents/environmental-health/environmental-protection/bonfire-smoke-nuisance

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Measures category

Measure Classification

Effect on reducing NOx and

PM10 emissions(l

ow, medium,

high)

Reduces PM2.5 emissio

ns

Local Authority

Stoke on Trent CC

Staffordshire

Moorlands DC

Newcastle- under- Lyme

BC

Stafford BC

Cannock Chase

DC

East Staffs

BC

Lichfield DC

South Staffs

DC

Tamworth BC

Multi agency working with Fire Service and Environment Agency for trade burning

Information shared as appropriate

Multi agency working with Staffordshire Fire Service and Local Authority Building Controlregarding chimney fires and complaints about DIY domestic heating systems

Information shared as appropriate

Stoke on Trent Low Carbon District Heat Network

High

Stoke-on-Trent Low

Carbon Distric

Heating Network

Stoke-on-Trent Low

Carbon Distric Heating Network

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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

This section sets out what monitoring has taken place and how it compares with

objectives.

Cannock Chase Council did not undertake automatic (continuous) monitoring during

2015. The automatic monitoring site for oxides of nitrogen (NOx) and PM10, located in

Bridgtown ceased operation in 2014 for technical reasons, and recommissioning of

this site is not feasible. However, a new site for the same pollutants has been

commissioned at a site on the A5190, Cannock Road, Heath Hayes. This is affiliated

with the national Automatic Urban and Rural Network (AURN) (Link39) and given the

name ‘Cannock A5190 Roadside’. No calibrated data has yet been polled.

National monitoring results for AURN sites are available at: Link40

Maps showing the location of the former and planned monitoring sites are provided in

Appendix D: Maps of Monitoring Locations.

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.

39

https://uk-air.defra.gov.uk/networks/network-info?view=aurn 40

https://uk-air.defra.gov.uk/networks/find-sites?site_name=&group_id=4&country_id=9999&region_id=9999&pollutant=&location_type=9999&view=advanced&action=results

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3.1.2 Non-Automatic Monitoring Sites

Cannock Chase Council undertook non-automatic (passive) monitoring of NO2 at 18

sites during 2015.

Appendix A shows the details of the sites.

Maps showing the location of the monitoring sites are provided in Appendix D: Maps

of Monitoring Locations. Further details on Quality Assurance/Quality Control

(QA/QC) and bias adjustment for the diffusion tubes are included in Appendix C.

3.2 Individual Pollutants

The air quality monitoring results presented in this section are, where relevant,

adjusted for “annualisation” and bias. Further details on adjustments are provided in

Appendix C.

3.2.1 Nitrogen Dioxide (NO2)

Table A.3 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 2015 dataset of monthly mean values is provided in

Appendix B.

Table A.4 in Appendix A compares the ratified continuous monitored NO2 hourly

mean concentrations for the past 5 years with the air quality objective of 200µg/m3,

not to be exceeded more than 18 times per year.

Exceedences of 40µg/m3 have neen detected at BTL, HHFW and CNKRD.

Potential New AQMA

HHFW and CNKRD are representative of relevant receptors and are therefore

considered as exceedences of the annual mean NO2 objective.

These are located in the Heath Hayes area of the district, near to the ‘Five Ways

Island’ junction of the A5190, B4194 and Wimblebury Road. This was identified in

the previous Updating and Screening Assessment, 2015 as requiring further

assessment. These results confirm that an Air Quality Management Area (AQMA) is

now required for the area.

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Existing AQMA

The relevant exposure locations within the existing AQMAs along the A5 Watling

Street are represented by monitoring results at BTL-B, 67WS, 54WS and 268WS.

Results for BTL-B and 268WS are the maximum values within AQMAs 1 and 2

respectively, values of 36.5 and 35.9 µg/m3. LAQM.TG(16) recommends that AQMAs

are revoked only after a detailed study, providing the same level of confidence as the

original investigation, and after several years of compliance with the objective. This is

to allow for variations in meteorological conditions that can be experienced over time.

Account should also be taken of national trends in emissions, as well as local factors

that may affect the AQMA, including measures introduced as part of the Air Quality

Action Plan, together with information from national monitoring on high and low

pollution years.

In this instance, dispersion modelling is not considered as a resource efficient means

to assess whether the existing AQMAs now reliably comply with objectives. The main

advantages of modelling are considered as:

to quantify the contribution of pollutant emissions arising from different sources

types on overall concentrations;

concentrations can be predicted across a wider geographical area than is

possible through monitoring alone;

geographic boundaries of any exceedances of the air quality objectives can be

determined;

concentrations can be predicted for future years, taking into account changes in

emissions sources and emissions data; and

scenario testing can be undertaken in order to determine the source contributions

and effects of AQAP measures on predicted concentrations.

Of these advantages, only the capacity to predict future years is particularly useful.

As such, it has been decided to utlise the ‘compare monitoring data with the

predicted future concentrations’ method described in LAQM.TG(16) Table 7.6. The

following charts demonstrate how monitoring results have varied over time, and what

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the anticipated levels will be, based on upper and lower values monitored since

2011.

It can be seen that monitoring results are broadly following anticipated reductions in

NO2, resulting from improved technology. However, peaks occuring in 2010 show

that values can occur above the projected upper limit. Therefore, it is recommended

Table 5: Monitored and Predicted Annual Mean NO2 for AQMA1, based on BTL-B

Table 6: Monitored and Predicted Annual Mean NO2 for AQMA2, based on 268 WS

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that a further 12 months monitoring data be aqcuired before a decision is made upon

revoking AQMAs 1 and 2.

No annual mean results are greater than 60 µg/m3. Guidance suggests that this

value is indicative of exceedence of the 1-hour mean objective. As such, the 1-hour

mean objective contuinues to be complied with in Cannock Chase district.

3.2.2 Particulate Matter (PM10)

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Table A.5 in Appendix A compares the ratified and adjusted monitored PM10 annual

mean concentrations for the past 5 years with the air quality objective of 40µg/m3.

Table A.6 in Appendix A compares the ratified continuous monitored PM10 daily

mean concentrations for the past 5 years with the air quality objective of 50µg/m3, not

to be exceeded more than 35 times per year.

PM10 has not been monitored in 2015. However, data from previous years has shown

no exceedence of either the annual or daily mean objectives.

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Appendix A: Monitoring Results

Table A.1 – Details of Automatic Monitoring Sites

Site ID Site

Name Site Type

X OS Grid Ref

Y OS Grid Ref

Pollutants Monitored

In AQMA?

Monitoring Technique

Distance to Relevant Exposure

(m) (1)

Distance to kerb of nearest road (m)

(2)

Inlet Height

(m)

Stile Cop

Stile Cop Rural

Background 403840 316100

SO2 NO2

N Chemiluminescence /

UV Flourescence

Bungalow approx. 45

metres distance

n/a >5

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Table A.2 – 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)

MORT Cannock Mortuary

Urban Background

397589 309724 NO2 N 10 n/a N

2.7

OXRD

Oxford

Road,

Rumer Hill

Urban Background

398529 309529 NO2 N 6.3 n/a N

2.8

BTL

Bridgtown

Traffic

Lights

Roadside 398009 308563 NO2 Y N 0 N

3.5

BTL-B

Bridgtown

Trafic Lights

(Bungalow

façade)

Roadside 397952 308567 NO2 Y Y 5 N

1.75

67WS 67 Watling

Street, Roadside 398051 308512 NO2 Y Y 7.8 N

1.1

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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)

Bridgtown

54WS

54 Watling

Street,

Bridgtown

Roadside 398250 308428 NO2 Y Y 5.1 N

1.2

BLNC1

Betty’s

Lane,

Norton

Canes

Suburban 401349 312196 NO2 N N 6.3 N

3

HF Horsefair,

Rugeley Roadside 404465 317741 NO2 N Y 7.2 N

2.4

DF

Deavall’s

Farm,

Hawks

Green

Urban

Background 399688 310686 NO2 N Y n/a N

3.0

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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)

HISLOP

Hislop Rd.,

Pear Tree,

Rugeley

Urban

Background 404125 316903 NO2 N Y n/a N

3

BTMS

Bridgtown

Monitoring

Station

Roadside 398009 308563 NO2 Y N 6.8 Y

3

268WS

268 Watling

Street,

Norton

Canes

Roadside 400731 307419 NO2 Y Y 3.75 N

2.25

414aPG 414a Pye

Green Road Roadside 398480 312757 NO2 N N 2.2 N

2.25

A51 A51,

Rugeley By-Roadside 704725 318804 NO2 N N 4 N

2.5

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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)

pass

CH

Mews

Church Hill

Mews,

Hednesford

Kerbside 400320 312265 NO2 N N 0.7 N

2.4

HHFW

Five Ways

Island,

Heath

Hayes

Roadside 401563 309940 NO2 N Y 1.6 N

2.4

CNKRD

Cannock

Road, Heath

Hayes

Roadside 401421 309965 NO2 N Y 2 N

2.4

HFRDRD

Hednesford

Road, Heath

Hayes

Roadside 401536 310001 NO2 N Y 3.2 N

2.2

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Table A.3 – Annual Mean NO2 Monitoring Results

Site ID Site Type Monitoring Type

Valid Data Capture for Monitoring

Period (%) (1)

Valid Data Capture 2015

(%) (2)

NO2 Annual Mean Concentration (µg/m3) (3)

2011 2012 2013 2014 2015

BTMS Roadside Automatic - - 36 39 36 34.4 -

Stile Cop

Rural Background

Automatic 99.6 99.6 13.1 12.9 14.4 11.9 10.4

MORT Urban

Background Diffusion Tube 100 100 19.1 18.5 17.5 15.1 16.8

OXRD Urban Background

Diffusion Tube 100 100 21.7 23.2 22.8 21 21.2

BTL Roadside Diffusion Tube 100 100 39.1 39.1 38.2 39.1 41.1

BTL-B Roadside Diffusion Tube 100 100 40.4 40.5 33.7 33 36.5

67WS 100 100 27.2 28.1 27.6 24.9 27.5

54WS Roadside Diffusion Tube 100 100 51.5 34.2 33.5 35.7 31.2

BLNC1 Suburban Diffusion Tube 100 81 21.8 19.5 19.1 16.6 16.9

HF Roadside Diffusion Tube 100 100 - - - - 30.8

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Site ID Site Type Monitoring Type

Valid Data Capture for Monitoring

Period (%) (1)

Valid Data Capture 2015

(%) (2)

NO2 Annual Mean Concentration (µg/m3) (3)

2011 2012 2013 2014 2015

DF Urban

Background Diffusion Tube 58 58 28.8 18.7 17.1 16.2 20.6*

HISLO

P Urban Diffusion Tube 100 49 14.7 14.7 14.8 12 13.3*

BTMS Roadside Diffusion Tube 100 100 37 38.6 35.7 34.1 39

268W

S Roadside Diffusion Tube 100 100 35.6 39.5 36.2 32.5 35.9

414aP

G Roadside Diffusion Tube 100 49 - - - - 37.4*

A51 Roadside Diffusion Tube 100 40 - - - 22.7 24.2*

CH

Mews Kerbside Diffusion Tube 100 100 - - - 30.5 35.5

HHFW Roadside Roadside 100 100 - - - 42.9 45.9

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Site ID Site Type Monitoring Type

Valid Data Capture for Monitoring

Period (%) (1)

Valid Data Capture 2015

(%) (2)

NO2 Annual Mean Concentration (µg/m3) (3)

2011 2012 2013 2014 2015

CNKR

D Roadside Roadside 100 59 - - - - 49.2

HFRD

RD Roadside Roadside 100 59 - - - - 29.7

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.

(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 Technical Guidance LAQM.TG16 if valid data capture for the full calendar year is less than 75%. See Appendix C for details.

* denotes annualised data

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Table A.4 – 1-Hour Mean NO2 Monitoring Results

Site ID Site Type Monitoring

Type

Valid Data Capture for

Monitoring Period (%) (1)

Valid Data Capture 2015

(%) (2)

NO2 1-Hour Means > 200µg/m3 (3)

2011 2012 2013 2014 2015

BTMS Roadside Automatic - - 0 5 1 0 -

Stile Cop

Rural Background

Automatic 99.6 99.6 0 0 0 0 0

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Table A.5 – Annual Mean PM10 Monitoring Results

Site ID Site Type Valid Data Capture

for Monitoring Period (%)

Valid Data Capture 2015

(%)

PM10 Annual Mean Concentration (µg/m3)

2011 2012 2013 2014 2015

BTMS Roadside - - 22 23 21 19.6 -

No Monitoring undertaken in 2015

Table A.6 – 24-Hour Mean PM10 Monitoring Results

Site ID Site Type Valid Data Capture for Monitoring Period (%)

Valid Data Capture 2015 (%)

PM10 24-Hour Means > 50µg/m3

2011 2012 2013 2014 2015

BTMS Roadside - - 9 16 6 4 -

No Monitoring undertaken in 2015

Table A.7 – PM2.5 Monitoring Results

Site ID Site Type Valid Data Capture

for Monitoring Period (%)

Valid Data Capture 2015

(%)

PM2.5 Annual Mean Concentration (µg/m3)

2011 2012 2013 2014 2015

n/a - - - - - - - -

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Table A.8 – SO2 Monitoring Results

Site ID Site Type

Valid Data Capture for monitoring

Period (%) (1)

Valid Data Capture

2014 (%) (2)

Number of Exceedances (percentile in bracket) (3)

15-minute Objective (266 µg/m3)

1-hour Objective (350 µg/m3)

24-hour Objective (125 µg/m3)

Stile Cop Rural Background 97.6 97.6 0 0 0

Notes: Exceedances of the SO2 objectives are shown in bold (15-min mean = 35 allowed a year, 1-hour mean = 24 allowed a year, 24-hour mean = 3 allowed a year)

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Appendix B: Full Monthly Diffusion Tube Results for 2015

Table B.1 – NO2 Monthly Diffusion Tube Results - 2015

Site ID

NO2 Mean Concentrations (µg/m3)

Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Annual Mean (time weighted)

Raw Data Bias Adjusted (1)

MORT 24.4 28.6 20.5 15.1 11.9 12.2 14.0 17.0 23.7 23.8 23.9 25.3 20.1 16.8

OXRD 27.0 36.9 23.6 21.8 17.4 19.1 18.8 I/S 28.7 34.8 28.0 I/S 25.2 21.2

BTL 57.2 59.1 47.3 34.6 39.5 45.5 46.6 52.6 53.6 57.0 53.8 < 1.0

48.9 41.1

BTL-B 46.4 54.0 43.7 36.7 31.4 37.5 39.6 43.7 49.0 50.5 46.3 43.0

43.4 36.5

67WS 37.3 33.4 29.3 29.0 20.9 28.5 27.8 32.4 39.9 38.5 34.7 39.3

32.7 27.5

54WS 37.8 37.9 39.0 48.3 31.6 48.7 36.3 42.0 51.1 60.5 31.7 31.8

41.6 34.9

BLNC1 25.5 28.3 16.9 18.3 13.5 21.1 17.5 20.7 21.1 18.3 I/S I/S

20.1 16.9

HF 39.0 44.7 34.9 28.7 29.3 31.9 34.2 34.7 39.4 41.9 44.1 38.5

36.6 30.8

DF 24.0 26.6 22.7 16.9 14.1 N/A N/A N/A N/A N/A N/A 25.5

24.5***

20.6***

HISLOP 21.2 17.6 18.3 10.9 8.8 10.1 N/A N/A N/A N/A N/A N/A

15.8*** 13.3***

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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 (time weighted)

Raw Data Bias Adjusted (1)

BTMS1 < 1.0 105.1* 43.0 38.9 42.6 45.1 46.3 53.2 54.9 59.4 48.7 45.5

46.4

39

BTMS2 47.7 54.9 43.0 33.5 41.4 39.4 44.8 50.7 48.3 60.4 48.4 37.2

BTMS3 52.8 48.3 44.3 37.6 36.2 43.6 44.9 46.5 51.1 58.3 44.7 37.8

268WS 42.8 43.6 45.0 40.8 31.0 37.8 36.0 42.1 59.0 67.5 32.6 34.9

42.7 35.9

414aPG N/A N/A N/A N/A N/A N/A 25.3 28.1 22.4 40.8 26.2 36.0

31*** 26.0***

A51 27.1 28.2 28.2 28.7 13.1 N/A N/A N/A N/A N/A N/A N/A

28.8*** 24.2***

CH Mews 45.4 52.9 36.1 36.0 30.1 36.0 39.4 43.1 38.9 51.7 49.7 49.7

42.3 35.5

HHFW 58.6 62.4 53.5 58.1 45.5 58.3 48.9 61.0 45.9 71.7 54.4 41.5

54.6 45.9

CNKRD N/A N/A N/A N/A N/A 34.5 33.1 40.4 73.4 101.7 43.4 39.7

58.6 49.2***

HFRDRD N/A N/A N/A N/A N/A 28.0 27.5 29.5 < 1.0 39.4 34.6 33.1

35.3 26.7***

Winshill - Brookside (B)** 27.1 23.6 16.7 14.3 10.7 16.4 12.6 12.4 15.6 20.6 22.9 21.6 17.9 n/a

(1) See Appendix C for details on bias adjustment

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(2) * outlier data removed from mean

(3) ** Background data from East Staffs BC for annualising data purposes.

(4) *** Annualised data – see Appendix C

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

3.2.3 Significant Changes to Sources

Transport

During 2015, there have been no significant changes to transport infrastructure that

would significantly impact upon air quality, other than those reported in Progress and

Impact of Measures to address Air Quality in Cannock Chase District.

Industrial Activities

Central Milled Lead, an Environmental Permitted activity for melting of pure and

clean scrap lead to form ingots. The Environmental Permit can be found at Link41.

In 2015 the activity added an additional furnace to the existing single furnace. The

model is exactly the same as the existing model, ducted into the same abatement

plant, and each furnace is only run when the other one is not. Annual monitoring has

not yet taken place, but it is deemed that emissions will be very similar to the existing

emissions.

Previous monitoring emission monitoring data demonstrated that particulate and lead

emissions are well within limit values, so the increased capacity is not deemed as

significant.

Pollutant Monitored emission value (mg/m3) Emission limit (mg/m3)

Particulate 0.28 20

Lead in particulate 0.0037 2

41

http://www.cannockchasedc.gov.uk/custom/EHPP/Files/IPPC1_2.2a(2)_02_P3.pdf

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3.2.4 New Monitoring Sites

In order to provide additional data to help assess air quality in the ‘Five Ways Island’

area of Heath Hayes, additional NO2 monitoring has been introduced.

Two diffusion tube locations, in addition to the existing ‘HHFW’ location, have been

monitored since June 2015 (‘CNKRD’ and ‘ HFRDRD’). These are roadside

locations, representative of relevant receptors in the area, as shown in the

photographs below, and described in Table A.2.

A new automated monitoring site is being commissioned at the time of writing. This

includes a chemiluminescent NOx monitoring unit and a TEOM particulate monitor. It

will operate as an affiliated AURN site for NOx.

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Figure 1: 'CNKRD' diffusion tube site

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Figure 2: 'HHFW' diffusion tube site

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Figure 3: 'HFRDRD' diffusion tube site

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3.2.5 QA/QC Data

Diffusion tubes are supplied and analysed by Staffordshire Scientific Services,

Staffordshire County Council. The preparation method is 20 % TEA, 80 % water –

pipetted.

The lab follows the procedures as set out in the Harmonisation Practical Guidance

and is UKAS accredited for this method.

The lab takes part in the NO2 Network Field Inter-comparison, managed by Health

and Safety Laboratory on behalf of AEA. Their lab code is 1017.

The bias factor for 2015 is 0.84, which is calculated using local co-location data. A

calculation sheet for determining the bias factor can be found below in Table 7 .

The lab takes part in the WASP scheme managed by Health and Safety Laboratory.

Lab code 1017.

The latest results for this can be found at Link42.

Discussion of Choice of Factor to Use

Both national and local bias factors can be used. In previous review and assessment

reports, use was made of a local bias factor, calculated using triplicate diffusion tubes

co-located with the automatic monitoring unit in Bridgtown. It was considered that

using this local factor in preference to a national factor would prove useful for

assessments associated with the A5 Watling Street where an air quality management

area is located, whereas a national factor may not be as representative. However,

due to the discontinuation of the Bridgtown monitor, this position is no longer

available and a national bias factor has been adopted. This has the benefit of being

less specific and in line with other authorities in the Staffordshire area.

Bias Factor from Co-location Studies

The following sheet shows the calculation of a local diffusion tube bias

factor for Cannock Chase Council’s monitoring programme for 2015.

Calculation is shown in the following table:

42

http://laqm.defra.gov.uk/diffusion-tubes/qa-qc-framework.html

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Table 7: Diffusion Tube Bias Calculation for Staffordshire Analytical Services

Analysed By1 Method Year

Site Type

Local Authority Length

of Study (months)

Diffusion Tube Mean Conc. (Dm)

(g/m3)

Automatic Monitor

Mean Conc. (Cm)

(g/m3)

Bias (B)

Tube Precision

Bias Adjustment Factor (A) (Cm/Dm)

Staffordshire Scientific Services 20% TEA in water 2015 UC Manchester City Council 12 42 40 6.9% G 0.94

Staffordshire Scientific Services 20% TEA in water 2015 SU Manchester City Council 12 25 20 24.5% G 0.80

Staffordshire Scientific Services 20% TEA in water 2015 KS Manchester City Council 11 72 66 9.3% G 0.91

Staffordshire Scientific Services 20% TEA in water 2015 R Trafford 9 35 30 17.6% G 0.85

Staffordshire Scientific Services 20% TEA in water 2015 UB Trafford 12 23 21 12.2% G 0.89

Staffordshire Scientific Services 20% TEA in water 2015 UB Wigan Council 11 27 20 32.7% G 0.75

Staffordshire Scientific Services 20% TEA in water 2015 KS Marylebone Road Intercomparison 11 95 81 18.0% G 0.85

Staffordshire Scientific Services 20% TEA in water 2015 R Stockport SMBC 12 31 24 27.1% G 0.79

Staffordshire Scientific Services 20% TEA in water 2015 R Stoke-on-Trent City Council 12 59 47 25.6% G 0.80

Staffordshire Scientific Services 20% TEA in water 2015 R Stoke-on-Trent City Council 10 37 29 29.9% G 0.77

Staffordshire Scientific Services 20% TEA in water 2015 UC Stoke-on-Trent City Council 12 32 28 13.7% G 0.88

Staffordshire Scientific Services 20% TEA in water 2015 R East Staffordshire Borough Council 10 51 39 29.2% G 0.77

Staffordshire Scientific Services 20% TEA in water 2015 R Oldham MBC 9 42 33 28.0% G 0.78

Staffordshire Scientific Services 20% TEA in water 2015 R Salford Council 10 53 53 -0.4% G 1.00

Staffordshire Scientific Services 20% TEA in water 2015 UB Salford Council 12 32 27 16.1% G 0.86

Staffordshire Scientific Services 20% TEA in water 2015 Overall Factor (15 studies) Use 0.84

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Annualisation of Diffusion Tube Data

Table 8: Deavall Farm (Jan-May & Dec)

Background Site Annual Mean 2015

(Am)

Period Mean 2015

(Pm)

Ratio (Am/Pm)

MORT* 20.1 21.2 0.95

Winshill -

Brookside (B)*

17.9 19.0 0.94

Average (Ra) 0.94

Table 9: Hislop (Jan - June)

Background Site Annual Mean 2015

(Am)

Period Mean 2015

(Pm)

Ratio (Am/Pm)

MORT* 20.1 18.5 1.09

Winshill -

Brookside (B)*

17.9 18.1 1.05

Average (Ra) 1.04

Table 10: 414a PGRd (Jul - Dec)

Background Site Annual Mean 2015

(Am)

Period Mean 2015

(Pm)

Ratio (Am/Pm)

MORT* 20.1 21.6 0.93

Winshill -

Brookside (B)*

17.9 17.6 1.02

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Average (Ra) 0.97

Table 11: A51 (Jan - May)

Background Site Annual Mean 2015

(Am)

Period Mean 2015

(Pm)

Ratio (Am/Pm)

MORT* 20.1 19.5 1.03

Winshill -

Brookside (B)*

17.9 18.5 0.97

Average (Ra) 1.00

Table 12: CnKRd ( Jun - Dec)

Background Site Annual Mean 2015

(Am)

Period Mean 2015

(Pm)

Ratio (Am/Pm)

MORT* 20.1 20.5 0.98

Winshill -

Brookside (B)*

17.9 17.4 1.03

Average (Ra) 1.00

Table 13: HfrdRd (Jun - Aug & Oct - Dec)

Background Site Annual Mean 2015

(Am)

Period Mean 2015

(Pm)

Ratio (Am/Pm)

MORT* 20.1 19.4 1.04

Winshill -

Brookside (B)*

17.9 17.8 1.01

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Average (Ra) 2.02

*All data un-adjusted for bias.

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Appendix D: Maps of Monitoring Locations

Figure 4: Map of Automatic Monitoring Sites, Whole District

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Figure 5: Map of Diffusion Tube Monitoring Sites, Whole District

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Figure 6: Map of Diffusion Monitoring Sites, Bridgtown

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Figure 7: Map of Diffusion Monitoring Sites, Heath Hayes

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Appendix E: Summary of Air Quality Objectives in England

Table E.1 – Air Quality Objectives in England

Pollutant Air Quality Objective43

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

43

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

… …

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References

Air Quality Action Plan:

http://www.cannockchasedc.gov.uk/sites/default/files/aqap_nov13.pdf

Green Book supplementary guidance: air quality -

https://www.gov.uk/government/publications/green-book-supplementary-

guidance-air-quality

Air quality: economic analysis - https://www.gov.uk/air-quality-economic-analysis

Cannock Chase Council Air Quality Action Plan Progress Report -

http://www.cannockchasedc.gov.uk/sites/default/files/aqap_progress.pdf

Cannock Chase Council Supplementary Planning Policy Documents -

http://www.cannockchasedc.gov.uk/residents/planning/planning-

policy/supplementary-planning-policy-documents

Cannock Chase Local Plan (Part 1) 2014

http://www.cannockchasedc.gov.uk/sites/default/files/local_plan_part_1_09.04.14

_low_res.pdf

Cannock Chase Council Infrastructure Delivery Plan, May 2014 -

http://www.cannockchasedc.gov.uk/sites/default/files/infrastructure_delivery_plan

_may_2014_update.pdf

Local Air Quality Management Technical Guidance (TG16), April 2016

http://laqm.defra.gov.uk/documents/LAQM-TG16-April-16-v1.pdf

Local Air Quality Management Policy Guidance (PG16), April 2016

http://laqm.defra.gov.uk/documents/LAQM-PG16-April-16-v1.pdf


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