2010 air quality progress report for tendring district council · 2010-06-21 · date april 2010...

Tendring District Council – England Date April 2010

Progress Report i

2010 Air Quality Progress Report for Tendring District Council In fulfillment of Part IV of the Environment Act 1995 Local Air Quality Management Date April 2010

Date April 2010 Tendring District Council - England

Progress Report ii

Local Authority Officer

Andy Rutson-Edwards

Department Tendring District Council Environmental Services

Address Council Offices Thorpe Road Weeley CO16 9AJ

Telephone 01255 686761

e-mail [email protected]

Report Reference number

TEN/PR2010 Final Copy 01/ 29March

Date 29th March 2010

Report written by: Paul Hinsley Environment, Strategy and Highways Essex County Council County Hall Chelmsford Essex CM1 1QH On behalf of the : Essex Air Quality Consortium Monitoring Network.

mailto:[email protected]

mailto:[email protected]


Progress Report iii

Executive Summary

The 2010 Progress Report on the monitoring data from 2009 has showed that there have been no exceedence of the NO2 annual mean objective level, benzene nor SO2 within the monitoring sites. There were no exceedences of the hourly NO2 objective observed at the automatic monitoring station.


Progress Report iv

Table of contents

1 Introduction 6

1.1 Description of Local Authority Area 6

1.2 Purpose of Progress Report 6

1.3 Air Quality Objectives 6

1.4 Summary of Previous Review and Assessments 8

2 New Monitoring Data 9

2.1 Summary of Monitoring Undertaken 9

2.2 Comparison of Monitoring Results with Air Quality 14

3 New Local Developments 18

4 Local Transport Plans and Strategies 19

5 Conclusions and Proposed Actions 20

5.1 Conclusions from New Monitoring Data 20

5.2 Proposed Actions 20

6 References 21


Progress Report v

Appendices

Appendix 1 Appendix 1: ARUN Data

Appendix 2 Tendring District Council Monitoring Data 2009

Appendix 3 QA:QC data

Appendix 4 Tendring District Council Processes 2009

List of Tables

Table 1.1 Air Quality Objectives included in Regulations for the purpose of Local Air Quality Management in England.

Table 2.1 Details of Automatic Monitoring Sites

Table 2.2 Details of Non- Automatic Monitoring Sites

Table 2.3 Results of Automatic Monitoring for Nitrogen Dioxide: Comparison with Annual Mean Objective, hourly mean >200 µgm

3 and data capture.

Table 2.4 Results of Nitrogen Dioxide Diffusion Tubes

Table 2.5 Results of SO2 Diffusion tube monitoring

Table 2.6 Results of Benzene monitoring

List of Figures

Figure 2.1a Map of Automatic Monitoring Site at St OSyth Figure 2.1b Map of Automatic Monitoring Station: Clacton Town Hall Figure 2.2 Map of Non-Automatic Monitoring Sites

Figure 2.3 Figure 2.3 Trends in Annual Mean Nitrogen Dioxide Concentration Measured at Automatic Monitoring Site St Osyth Figure 2.4 Trends in Annual Mean PM10 Concentration Measured at Automatic Monitoring Sites Figure 2.5 Trends in Annual Mean Sulphur Dioxide Concentration Measured at Automatic Monitoring Sites.


Progress Report 6

1 Introduction

1.1 Description of Local Authority Area

The district of Tendring is a predomiantantly rural, coastal district with Clacton-on-Sea as its main administrative centre. The district also conatins the coastal towns of Frinton-on-Sea and Harwich. The main source of air pollution in the area is road traiffic emissions from the major roads in the district, namely the A133 and A120 trunk roads.

1.2 Purpose of Progress Report

Progress Reports are required in the intervening years between the three-yearly Updating and Screening Assessment reports. Their purpose is to maintain continuity in the Local Air Quality Management process. They are not intended to be as detailed as Updating and Screening Assessment Reports, or to require as much effort. However, if the Progress Report identifies the risk of exceedence of an Air Quality Objective, the Local Authority (LA) should undertake a Detailed Assessment immediately, and not wait until the next round of Review and Assessment.

1.3 Air Quality Objectives

The air quality objectives applicable to Local Air Quality Management (LAQM) in England are set out in the Air Quality (England) Regulations 2000 (SI 928), and the Air Quality (England) (Amendment) Regulations 2002 (SI 3043). They are shown in Table

1.1. This table shows the objectives in units of microgrammes per cubic metre g/m3 (for carbon monoxide the units used are milligrammes per cubic metre, mg/m3). Table 1.1. includes the number of permitted exceedences in any given year (where applicable).


Progress Report 7

Table 1.1 Air Quality Objectives included in Regulations for the purpose of Local Air Quality Management in England.

Pollutant

Date to be achieved by Concentration Measured as

Benzene

16.25 µg/m3 Running annual mean

31.12.2003

5.00 µg/m3 Running annual mean

31.12.2010

1,3-Butadiene 2.25 µg/m3 Running annual mean

31.12.2003

Carbon monoxide 10.0 mg/m3 Running 8-hour mean

31.12.2003

Lead 0.5 µg/m3 Annual mean 31.12.2004

0.25 µg/m3 Annual mean 31.12.2008

Nitrogen dioxide 200 µg/m3 not to be exceeded more than 18 times a year

1-hour mean

31.12.2005

40 µg/m3 Annual mean 31.12.2005

Particles (PM10) (gravimetric)

50 µg/m3, not to be exceeded more than 35 times a year

24-hour mean

31.12.2004

40 µg/m3 Annual mean 31.12.2004

Sulphur dioxide 350 µg/m3, not to be exceeded more than 24 times a year

1-hour mean

31.12.2004


24-hour mean

31.12.2004


15-minute mean 31.12.2005


Progress Report 8

1.4 Summary of Previous Review and Assessments

Tendring District Council undertook their First Round of review and assessment, including Stage 1 and 2 reports, between 1999 – 2000. The main air quality issues were found to be emissions of NO2 and PM10 from vehicles on the A120. It was predicted that all of the AQS objectives would be achieved and that it was therefore not necessary to declare an AQMA for any pollutant. The second round of Review and Assessment was undertaken between 2003 and 2005. The 2003 USA considered the seven LAQM pollutants and found that the AQS objectives would be met by the target dates. The 2005 Annual Progress Report (APR) showed that the Council was still meeting the aqs objectives. The third round USA was completed in 2006 and revisited the results of previous assessments to determine whether there were any areas of concern for air quality within Tendring District. The USA concluded that there was still no risk of exceedances of the AQS objectives, therefore a Detailed Assessment is not required at this stage. The 2008 APR concluded that the AQS objectives are being met in Tendring and there was no requirement to proceed to a Detailed Assessment. The 2009 USA review identified one exceedance of the NO2 annual mean objective in 2008, at Harwich Train Station (Site 10). It was recommended that the Council relocate this diffusion tube site to a nearby receptor façade where potential exceedances of the AQS annual mean objective maybe better assessed.


Progress Report 9

2 New Monitoring Data

2.1 Summary of Monitoring Undertaken

2.1.1 Automatic Monitoring Sites

Tendring District Council measures air quality in the District using two automatic air quality monitoring stations as shown in figure 2.1.and 2.2. One of the automatic monitoring stations is located in St Osyth and has been operating since May 2002. The site is classified as rural and measures concentrations of ozone, oxides of nitrogen and carbon monoxide. This site is part of the UK Automatic Urban and Rural Network, which is operated on behalf of DEFRA.

Figure 2.1a Map of Automatic Monitoring Site at St Osyth

Site is located next to a water pumping station in marshland near Clacton-on-Sea. Nearest road is approx 2km north of site, St Osyth village is approx 3km north. 5m above sea level, inlet 4m above ground

SITE ADDRESS: Environment Agency, Leewick Yard,Leewick Lane St Osyth Essex

OS Grid Reference: TM104132 Site Type: Rural Pollutants Measured:

Pollutant Start Date End Date

Nitrogen Oxides 11/05/2002 -

Ozone 11/05/2002 -

Carbon Monoxide 11/05/2002 -

http://www.bv-aurnsiteinfo.co.uk/default.asp?pageref=142


Progress Report 10

The second automatic monitor in Tendring is located at the Town Hall in Clacton and has been measuring concentrations of oxides of nitrogen and PM10 since late 2001.

Figure 2.1b Map of Automatic Monitoring Station: Clacton Town Hall Information

Data corrupted, mechanical faults on machine has resulted in less than less than 20% data capture for this site.

Table 2.1 Details of Automatic Monitoring Sites

Site Name Site Type Pollutants Monitored

In AQMA?

Relevant Exposure?

(Y/N with Distance

(m) to Relevant

Exposure)

Distance to Kerb of Nearest

Road (m) (N/A if not Applicable)

St Osyth Roadside NO2 N N 2.1

Clacton Town Hall Roadside NO2, PM10 N Y - 29.3 9.1


Progress Report 11

2.1.2 Non-Automatic Monitoring

Tendring District Council undertook monitoring at 7 NO2 diffusion tubes sites in 2009.

The diffusion tubes are supplied and analysed by Gradko International Ltd

Preparation method : 50% TEA in acetone

United Kingdom Accreditation Services (Testing Laboratory number 2187).

WASP – Annual Performance Criteria for NO2 Diffusion Tubes used in Local Air Quality Management (LAQM), 2008 onwards, and Summary of Laboratory Performance in Rounds 103 -107. Prepared by AEA on behalf of Defra and the Devolved Administrations.

Table 1 Laboratories that have demonstrated satisfactory performance in the WASP scheme for analysis of NO2 diffusion tubes, October 2008 – October 2009 Laboratory

Performance on basis of RPI, OLD CRITERIA, best 4 out of the 5 rounds 103 – 107

Performance on basis of RPI, NEW CRITERIA ,best 4 out of the 5 rounds 103 – 107

Gradko International Good Good

With regard to the application of a bias adjustment factor for the diffusion tubes, the technical guidance LAQM.TG (09) and Review and Assessment Helpdesk recommends use of a local bias adjustment factor where available and relevant to diffusion tube sites. However data capture at the Town Hall site was insufficient. A bias adjustment factor was calculated using the co-located tubes at the St Osyth ARUN site. Due to the exceptionally low ratio generated the bias adjustment factor supplied by R& A support for Gradko 50% in Acetone Overall Factor (7 Studies) has been used : 0.92

http://www.ukas.com/


Progress Report 12

Figure 2.2 Map of Non-Automatic Monitoring Sites

Tendring District Council Diffusion Tube Locations

2009


Progress Report 13

Table 2.2 Details of Non- Automatic Monitoring Sites

,

Site No. Location X Y Pollutant Monitored

In AQMA?

Relevant Exposure? (Y/N with Distance (m) to Relevant

Exposure)

Distance to Kerb of Nearest Road

(N/A if not Applicable)

9 Harwich Hospital 624294 231255 NO2 N Y - 21.4 3.8

10 Harwich Train Station 626000 232384 NO2 N Y - 39.2 2.9

11/12/13 Clacton Town Hall A/B/C 617272 215021 NO2 N Y - 29.3 9.1

14/15/16 St Osyth, Bypass A133 1/2/3 616062 218517 NO2 N N 2.1

18 Bathside Bay 625625 231976 NO2 N N 0.5

19 Wix 613924 227789 NO2 N N 1.0

20 Hempstalls Farm 612619 227395 NO2 N


Progress Report 14

2.2 Comparison of Monitoring Results with Air Quality

2.2.1 Nitrogen Dioxide

Automatic Monitoring Data

Table 2.3 Results of Automatic Monitoring for Nitrogen Dioxide: Comparison with Annual Mean Objective

Figure 2.3 Trends in Annual Mean Nitrogen Dioxide Concentration Measured at Automatic Monitoring Site St Osyth.

Data curtsy of

Paul Willis Environmental Quality AEA Building 551.11 Harwell Didcot Oxfordshire OX11 0QJ

Direct line 0870 190 6602 Direct facsimile 0870 190 6377 e-mail [email protected]

Location Within

AQMA? Description

Annual Mean

Concentrations ( g/m3)

2007

2008

2009

St Osyth N

Annual Mean NO2 > 40 µgm3 12.4 - 0

NO2 Hourly Mean > 200 µgm

3 for more than 18 times

per year 0 - 0

% Data Capture 92.3 - 97.6

Clacton Town Hall

N

Annual Mean NO2 > 40 µgm3 - 34.1 -

NO2 Hourly Mean > 200 µgm

3 for more than 18 times

per year - 0 -

% Data Capture - 75 <20


Progress Report 15

Diffusion Tube Monitoring Data

Table 2.4 Results of Nitrogen Dioxide Diffusion Tubes

Site ID

Location

Within AQMA?

Data Capture

2009 %

Annual Mean Concentrations ( g/m3)

Adjusted for Bias

2007 (Bias Factor: 0.89)

2008 (Bias Factor: 1.36)

2009 (bias Factor 0.92) 9 Harwich Hospital N 19.1 29.9 22.23

10 Harwich Train Station N 31.4 43.6 29.83

11/12/13 Clacton Town Hall A/B/C

N 22.1 32.9 21.19

14/15/16 St Osyth, Bypass A133 1/2/3

N 20.6 32.1 21.86

8 Bathside Bay N - 20.5 10.18

19 Wix N - 29.8 16.76

20 Hempstalls Farm N 13.24

Co – location of tubes Annual Mean

Average of site

Local Bias factor

Bypass A133 St Osyths NO2 24.39 24.12 0.49

Bypass A133 NO2 23.85

Bypass A133 NO2 24.30

St Osyths Average 01 Jan – 31 Dec 2009

NO2 11.8 µg m-3

2.2.2 PM10

There is no reliable data capture of PM10 for the reporting period.


Progress Report 16

2.2.3 Sulphur Dioxide

Table 2.5 Results of SO2 Diffusion Tube monitoring

Site ID Location Within

AQMA?

Data Capture for full

calendar year

2009b %

Annual mean concentrations

( g/m3)

2009 c

3 Parkeston Train Station

N 92

3.68

4 Refinery Road, Parkeston

N 83

3.16

5 Harwich quay (floating pontoon)

N 67

3.31

6 Hawich Quay (lift)

N 100

3.99

7 Harwich Station

N 100

2.68

8 Harwich Hospital

N 83

1.66

2.2.4 Benzene

Benzene levels are monitored at the town hall, using passive diffusion tube collection, there are no exceedences

Table 2.6 Results of Benzene monitoring

Site ID

Location Within

AQMA?

Data Capture for full calendar year

2009b %

Annual mean

concentrations ( g/m3)

2009 c

1

Clacton Town Hall

N 92 0.80

2

Refinery Road Parkeston

N 92 1.63


Progress Report 17

2.2.5 Other pollutants monitored

Ozone is monitored at the St Osyths ARUN site the results are as follows:

Pollutant Air Quality (England) Regulations 2000 and

(Amendment) Regulations 2002

Exceedences Days Data Captur

e

Ozone

Running 8-hour mean > 100 µg m-3 72 16 98.2 %

2.2.6 Summary of Compliance with AQS Objectives

Tendering District Council has examined the results from monitoring in the district. Concentrations are all below the objectives, therefore there is no need to proceed to a Detailed Assessment.


Progress Report 18

3 New Local Developments

Tendring District Council confirms that there are no new or newly identified local developments which may have an impact on air quality within the Local Authority area.


Progress Report 19

4 Local Transport Plans and Strategies

Tendring is covered by the Essex County Council Local Transport Plan 2 (LTP2). There are a number of general measures in the Essex LTP2 which are aimed at reducing the impact of road transport on air quality across the County. In the LTP Tendring was identified as a potential hotspot for Air Quality. This is due to the fact that the Bathside Bay development will increase freight traffic in the area and particularly on the A120 leading to concern that NO2 will exceed its limit in the future. The local transport plan identifies the need to reduce congestion and improve the junctions to improve the flow of traffic and allow the roads to cope with the potential increase in traffic flow. There are other general measures that will impact positively on the air quality in the area via the local transport plan. The District Council is working in partnership with the Development, Highways and Transportation department of Essex County Council to ensure that new traffic management schemes consider the potential impact on air quality.


Progress Report 20

5 Conclusions and Proposed Actions

5.1 Conclusions from New Monitoring Data

The Progress Report shows that Tendring District is currently meeting the air quality objectives and is not at risk of exceeding the objectives by the relevant target dates. The District Council is working in partnership with key stakeholders to ensure that the air quality in Tendring remains below objective limits and continues to improve. The District Council is currently working to improve the data capture of the monitoring equipment it uses.

5.2 Proposed Actions

The District Council does not need to carry out any detailed assessment as a result of any findings of the Progress Report. The next air quality report to be prepared and submitted to DeFRA will be the 2011 Progress report.


Progress Report 21

6 References

Local Air Quality Management Technical Guidance LAQM.TG(09). February 2009. Published by Defra in partnership with the Scottish Government, Welsh Assembly Government and Department of the Environment Northern Ireland

Tendring District Council 2008 Local Air Quality Management Annual Progress Report

Tendring District Council 2006 Local Air Quality Management Updating

Tendring District Council 2009 LAQM Updating and Screening Assessment


Progress Report 22

Appendices

Appendix 1: ARUN Data

ST OSYTH 01 January to 31 December 2009

POLLUTANT CO NO2 NOX O3

Number Very High 0 0 - 0

Number High 0 0 - 7

Number Moderate 0 0 - 220

Number Low 8348 8549 - 8430

Maximum 15-minute mean 0.77 mg m-3 192.5 µg m

-3 672.7 µg m

-3 266 µg m

-3

Maximum hourly mean 0.65 mg m-3 138.9 µg m

-3 473.1 µg m

-3 258 µg m

-3

Maximum running 8-hour mean 0.47 mg m-3 68.3 µg m

-3 154.9 µg m

-3 188 µg m

-3

Maximum running 24-hour mean 0.41 mg m-3 53.2 µg m

-3 111.2 µg m

-3 113 µg m

-3

Maximum daily mean 0.40 mg m-3 52.6 µg m

-3 109.2 µg m

-3 94 µg m

-3

Average 0.19 mg m-3 11.8 µg m

-3 14.4 µg m

-3 52 µg m

-3

Data capture 95.4 % 97.6 % 97.6 % 98.2 %

All mass units are at 20'C and 1013mb

NOX mass units are NOX as NO2 µg m-3

Pollutant Air Quality (England) Regulations 2000 and (Amendment) Regulations 2002

Exceedences Days

Carbon Monoxide Running 8-hour mean > 10.00 mg m-3

0 0

Nitrogen Dioxide Annual mean > 40.0 µg m-3

0 -

Nitrogen Dioxide Hourly mean > 200.0 µg m-3

0 0

Nitrogen Oxides (NO2) Annual mean > 30.0 µg m-3

0 -

Ozone Running 8-hour mean > 100 µg m-3

72 16

These data are provisional from 01/10/2009 and may be subject to further quality control


Progress Report 23

Appendix 2 : Tendring District Council Monitoring Data 2009

Location Pollutant Jan-09 Feb-09 Mar-09 Apr-09 May-09 Jun-09 Jul-09 Aug-09 Sep-09 Oct-09 Nov-09 Dec-09

Clacton Town Hall Benzene 1.25 1.17 0.92 0.86 0.68 0.67 0.77 0.38 1.18 0.26 0.8

Refinery Road, Parkeston Benzene 2.68 0.67 3.93 1.18 1.5 0.06 1.37 2.24 0.26 1.19 2.87

Location Pollutant Jan-09 Feb-09 Mar-09 Apr-09 May-09 Jun-09 Jul-09 Aug-09 Sep-09 Oct-09 Nov-09 Dec-

09

Harwich Hospital NO2 28.04 30.67 23.91 30.07 21.04 23.94 16.16 15.41 19.24 24.89 24.22 32.4

Harwich Train Station NO2 35.09 53.66 33.15 45.54 31.09 43 17.84 16.99 30.02 27.34 22.01 33.32

Town Hall A NO2 31.6 31.55 24.17 27.12 18.86 17.62 14.04 15.74 19.79 25.18 20.96 26.82

Town Hall B (AQMS) NO2 32.75 30.29 28 28.44 17.22 19.99 13.45 15.04 19.31 26.21 20.28 28.16

Town Hall C (Station Road) NO2 31.66 32.9 28.03 26.99 18.12 17.97 14.02 13.72 20.35 25.25 19.18 28.42

Bypass A133 NO2 29.92 32.12 20.52 36.01 20.41 25.39 13.47 16.29 21.12 26.12 20.22 31.05

Bypass A133 NO2 33.21 34.68 23.42 30.7 19.07 27.17 11.06 15.6 21.01 24.51 18.36 27.38

Bypass A133 NO2 37.46 33.33 24.07 33.62 17.94 27.31 12.04 16.84 19.17 24.11 18.11 27.64

Control NO2 0.28 0 0.21 0.2 0.28 0.03 0.35 0.27 0.32 0.14 0.42 0.2

Bathside Bay NO2 14.22 0.64 13.62 13.37 9.17 7.34 9.16 16.2 15.45 7.15 15.34

Wix NO2 19.23 0.77 23.8 16.17 27.38 17.8 20.24 23.18 19.18 15.2 17.45

Hempstalls Farm NO2 18.34 0.66 19.72 14.66 16.05 10.4 15.54 18.7 17.62 12.47 14.12

Location Pollutant Jan-09 Feb-09 Mar-09 Apr-09 May-09 Jun-09 Jul-09 Aug-09 Sep-09 Oct-09 Nov-09 Dec-09

Parkeston Train Station SO2 1.02 6.37 4.84 1.15 3.83 3.96 3.65 3.08 3.49 5.44 3.65

Refinery Road, Parkeston SO2 BLD* 7.52 1.35 2.83 BLD* 2.56 2.56 1.22 6.26 3.23 0.92 3.47

Harwich quay (floating pontoon) SO2 BLD* 3 3.05 0.73 2.96 1.78 8.34 4.28

Hawich Quay (lift) SO2 1.79 11.22 1.05 2.14 3.97 2.05 2.96 2.23 6.26 3.58 6.60 2.36

Harwich Station SO2 1.61 2.99 2.74 1.66 3.93 1.86 2.05 1.65 6.18 0.92 3.93 2.6

Harwich Hospital SO2 1.59 1.69 0.56 1.25 BLD* BLD* 1.86 1.5 2.68 0.67 3.14 4.63

Bathside Bay SO2 1.51 BLD* BLD* 2.52 1 1.1 1.76 2.54 1.53 2.74 0.22

Wix SO2 0.99 BLD* 0.38 1.99 2.36 42.96 1.49 1.94 0.9 2.22 0.39

Hempstalls Farm SO2 4.88 BLD* 0.91 2.89 BLD* 0.3 1.18 2.18 1 1.19 0.54

*BLD :Below Limit of Detection


Progress Report 24

Appendix 3: QA:QC Data Discussion of Choice of Factor to Use With regard to the application of a bias adjustment factor for the diffusion tubes, the technical guidance LAQM.TG (09) and Review and Assessment Helpdesk recommends use of a local bias adjustment factor where available and relevant to diffusion tube sites. However data capture at the Town Hall site was insufficient to calculate a factor from. A bias adjustment factor has been calculated using the bias adjustment factor supplied by R& A support for Gradko 50% in Acetone Overall Factor (7 Studies) : 0.92 QA/QC of automatic monitoring ARUN Standard QA/QC QA/QC of diffusion tube monitoring

WASP – Annual Performance Criteria for NO2 Diffusion Tubes used in Local Air Quality Management (LAQM), 2008 onwards, and Summary of Laboratory Performance in Rounds 103 -107. Prepared by AEA on behalf of Defra and the Devolved Administrations.

Table 1 Laboratories that have demonstrated satisfactory performance in the WASP scheme for analysis of NO2 diffusion tubes, October 2008 – October 2009 Laboratory

Performance on basis of RPI, OLD CRITERIA, best 4 out of the 5 rounds 103 – 107

Performance on basis of RPI, NEW CRITERIA ,best 4 out of the 5 rounds 103 – 107

Gradko International Good Good


Progress Report 25

Appendix 4: Processes 2009

Company

Name

Process

Auth

number

Address Site

DB Concrete Batching plant EPR082a Martells Pit, Slough Lane, Ardleigh, Essex, CO7 7RU.

Martells Pit, Slough Lane, Ardleigh, Essex, CO7 7RU.

Brett Concrete Ltd

Concrete Batching Plant

PPC020a Brett House, Bysing Wood Road, Faversham,

Kent, ME13 7UD

Ford Lane, Alresford, Colchester, Essex

Brett Concrete Ltd

Concrete Batching Plant

PPC062 Brett House, Bysing Wood Road, Faversham,

Kent, ME13 7UD

Parkeston Concrete plant, West dock Road, Parkeston

Cemex Concrete Batching Plant

PPC058 Camden House, Clearwater Business

Park, Thornby, Stockon-on-Tees, TS17 6QY

Martells Pit, Slough Lane,Ardleigh, Essex

CEMEX Concrete Batching Plant

PPC013B Camden House, Clearwater Business

Park, Thornby, Stockon-on-Tees, TS17 6QY

Martells Pit, Slough Lane,Ardleigh, Essex

Carlson Contracts

Concrete Crusher PPC032 Pond Hall Farm, Bradfield Road, Wix, CO11 2SP

Pond Hall Farm, Bradfield, Wix

Silverton Aggregates

Concrete Crusher EPR80a Mr Thurgood, Devereux Farm, Walton Road, Kirby Le Soken, Essex, CO13

0DR

Devereux Farm, Walton Road, Kirby Le Soken, Essex,

CO13 0DR

Silverton Aggregates

Concrete Crusher EPR81a Mr Thurgood, Devereux Farm, Walton Road, Kirby Le Soken, Essex, CO13 0DR

Devereux Farm, Walton Road, Kirby Le Soken, Essex, CO13 0DR

Eastern Waste Disposal

Concrete Crusher PPC059a Morses Lane, Brightlingsea, Essex

Morses Lane, Brightlingsea


Progress Report 26

Company

Name Process

Auth

number Address Site

Weeley Crematorium

Crematorium PPC009a Colchester Road, Weeley, Essex, CO16 9AH

Colchester Road, Weeley

Manningtree Laundry Centre

Ltd

Dry Cleaners PPC071 High Street, Manningtree, Essex, CO11 1AJ

High Street, Manningtree

Quality Dry Cleaners

Dry Cleaners PPC077a 9, Old Road, Frinton-on-Sea, Essex

9, Old Road, Frinton-on-Sea, Essex

Smiths Service Centre

Dry Cleaners PPC074a 21-25 Orwell Road, Clacton-on-Sea Essex

21-25 Orwell Road, Clacton-on-Sea Essex

Triangle cleaners

Dry Cleaners PPC072 2 Admiral House, Cardinal Way, Harrow, Middlesex. HA3 5UT

16, The Triangle Shopping Centre, Rochford Way, Frinton on Sea. Essex CO13 0AU

WM Morrisons Supermarket

Dry Cleaners PPC073a Hillmore House, Thorton Road, Bradford, West Yorkshire, BD8 9AX

Centenary Way, Little Clacton

Bucbricks Co. Ltd

Mineral Process EPA015a Martells Quarry, Slough Lane, Ardleigh, Essex,

CO7 7RY

Martells Quarry, Slough Lane

Spartan Tiles Ltd

Mineral Process PPC068 Martells Quarry, Slough Lane, Ardleigh, Essex,

CO7 7RY

Slough Lane, Ardleigh


Progress Report 27

Company

Name Process

Auth

number Address Site

Ardleigh Service Station

Petrol Vapour Recovery

PPC065 Colchester Road, Ardleigh, CO7 7PA

Ardleigh Service Station

East Of England Co-op Society


PPC039 Victoria Place, Eld lane, Colchester Essex

Samsons Road, Brightlingsea

East Of England Co-op Society


PPC041 Victoria Place, Eld lane, Colchester Essex

Oxford Road, Clacton on Sea

Forbourn Motors Petrol Vapour Recovery

PPC060 Bennetts, High Street, Thorpe le Soken, Essex

High Street, Thorpe le Soken

Gulf Pump Hill Garage


PPC043 St. Johns Road, St. Osyth Clacton CO16 8HE

St. Johns Road, Clacton on Sea

Lawford Service Station


PPC056 206 Long Road, Lawford, Essex, CO11 2EH

Long Road, Lawford

London Road Garage


PPC055 2-10 London Road, Clacton on Sea, Essex

London Road, Garage

Malthurst Fuels, Weeley


EP063 Vincent House, 4 Grove Lane, Eppijng, Essex,

CM16 4LH

Malthurst Weeley, Colchester Road,

Weeley

Mr Sangarapillai

Petrol Vapour Recovery PPC043a

Shell Corner, Colchester Road. Great Bentley

Shell Corner, Colchester Road. Great Bentley

PACE Petroleum Ltd variation

needed


PPC040 Burgan House, The Courseway, Staines,

Middlesex, TW18 3PA

Colchester Road, Elmstead

ROC UK Ltd Petrol Vapour Recovery

PPC049 Exonmobil House, MP22, Ermyn Way, Leatherhead,

Surrey, KT22 8UX

Frinton Road Service Station, Frinton on

Sea

Shell UK Retail Petrol Vapour Recovery

PPC053 PO BOX 403, Staines Middlesex, TW18 3ZB

Old Road, Clacton on Sea, Essex

Tesco Stores Ltd


PPC070a Tesco house, Delamare Road, Chestnut, Herts,

EN8 9SL

Tesco Petrol Filling Station, Brook Park,

Clacton on Sea, Essex

Texaco A120 South


PPC51 A120 Ardleigh, Essex Ardleigh A120, South

Vine Service Station

Vine Service Station

PPC054 394 Main Road, Dovercourt, Essex

394 Main Road, Dovercourt, Essex



PPC044 Hillmore House, Thorotn Road, Bradford, West Yorkshire, BD8 9AX

Centenary Way, Little Clacton



PPC047 Hillmore House, Thorton Road, Bradford, West Yorkshire, BD8 9AX

Iconfield Park, Garland Road,

Parkeston


Progress Report 28

Company

Name

Process

Auth

number

Address Site

Dovercourt Motors

Vehicle Coating Process

PPC023b Valleybridge Road, Clacton on Sea, Essex

Valleybridge Road, Clacton on Sea

Simon Morris Vehicle Coating Process

PPC31a Unit 1, Rice Bridge Industrial Estate, Thorpe le Soken, Essex, CO16

0HH

Station Road, Thorpe le Soken

Belmont Motors of Wix

Waste Oil Burner PPC004a Harwich Road, Essex, CO11 2RY

Harwich Road, Wix

Dovercourt Motors

Waste Oil Burner PPC071b Valleybridge Road, Clacton on Sea, Essex

Valleybridge Road, Clacton on Sea

Frinton Autos Waste Oil Burner PPC010a Frinton Autos, Kirby Cross, Essex

Frinton Road, Kirby Cross

Manningtree Body Repair Centre

Waste Oil Burner PPC078a Riverside Avenue West, Lawford, Essex, CO11 1UN Riverside Avenue

West, Lawford

Oaktree Garage Waste Oil Burner PPC016a Riverside Avenue West, Lawford, Essex, CO11

1UN

Riverside Avenue West, Lawford

Orchard Garage Waste Oil Burner PPC002A High Street, Thorpe Le Soken, Essex

High Street, Thorpe le Soken

TBR UK Ltd Waste Oil Burner PPC075a TBR UK Ltd, Unit4 Phoenix Industrial Park, Parkeston Quay, Harwich, Essex

TBR UK Ltd, Unit4 Phoenix Industrial Park, Parkeston Quay, Harwich, Essex

2010 air quality progress report for tendring district council · 2010-06-21 · date april 2010...

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