Air Quality Updating and Screening Assessment and 2010 Progress Report

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London Borough of Bromley - England

Combined 2009 Air Quality Updating and Screening Assessment and 2010 Progress Report

In fulfillment of Part IV of the Environment Act 1995 Local Air Quality Management

October 2011

London Borough of Bromley - England

Local Authority Hedley Pugh (Environmental Health Officer) Officer Department Environmental Health Address London Borough Bromley Civic Centre Stockwell close Bromley BR1 3UH Telephone 0208 313 4764 e-mail [email protected] Report Reference number Date September 2011

Report Prepared by: Approved by: James Rawlinson Sam Pollard Senior Environmental Scientist Principal Environmental Scientist AECOM AECOM

London Borough of Bromley Combined 2009 Air Quality Updating and Screening Assessment and 2010 Progress Report

Rev No Comments Date 1 Final October 2011

10th Floor, Sunley House, 4 Bedford Park, Croydon, CR0 2AP, UK Telephone: 0870 905 0906 Website: http://www.aecom.com

Job No 60155020 Reference JAR Date Created October 2011

This document has been prepared by AECOM Limited ("AECOM") for the sole use of our client (London Borough of Bromley) and in accordance with generally accepted consultancy principles, the budget for fees and the terms of reference agreed between AECOM and the Client. Any information provided by third parties and referred to herein has not been checked or verified by AECOM, unless otherwise expressly stated in the document. No third party may rely upon this document without the prior and express written agreement of AECOM.

1 London Borough of Bromley - England

Executive Summary

An assessment of the current air quality situation within the administrative area of the London Borough of Bromley has been undertaken in line with the Defra LAQM Technical Guidance TG(09). The report has assessed all available air quality monitoring data within the Borough against the air quality objectives, as well as any significant changes within the Borough since the last round of review and assessment that could impact on local air quality. These include any changes to the local road network, new industrial installations or new local development that would result in increased human exposure to the pollutants listed in the Air Quality Strategy 2007. The Council has historically monitored at five continuous monitoring sites (all now closed) and ten NO2 diffusion tube sites within the Borough. Analysis of the 2007 – 2009 datasets shows there were exceedences of the annual mean NO2 objective at two of the remaining sites (Crystal Palace and Harwood Avenue) in all years. Both sites are within the current AQMA.

The results also indicate there to have been no exceedences of the 1 hour mean NO2 air quality objective.

Assessment of the measured PM10 concentrations at both sites shows a general downward trend during the period 1999 – 2009, with no identified exceedences. Further to this, no significant changes or developments were identified since the 2006 Updating and Screening Assessment (USA), which were considered likely to lead to significant increases in any prescribed pollutants. Given the draft nature of the Council’s Air Quality Action Plan, progress reporting on the implementation of the listed actions will be detailed in subsequent LAQM reports. The overall results of this Combined 2009 Updating and Screening Assessment and 2010 Progress Report indicate that a Detailed Assessment is not required for any pollutant.

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Table of contents

1 Introduction 5 1.1 Description of Local Authority Area 5 1.2 Purpose of Report 5 1.3 Air Quality Objectives 5 1.4 Summary of Previous Review and Assessments 8 2 New Monitoring Data 10 2.1 Summary of Monitoring Undertaken 10 2.2 Comparison of Monitoring Results with AQ Objectives 15 3 Road Traffic Sources 20 3.1 Narrow Congested Streets with Residential Properties Close to the Kerb 20 3.2 Busy Streets Where People May Spend 1-hour or More Close to Traffic 20 3.3 Roads with a High Flow of Buses and/or HGVs. 21 3.4 Junctions 21 3.5 New Roads Constructed/Proposed Since the Last Round of Review and Assessment 21 3.6 Roads with Significantly Changed Traffic Flows 21 3.7 Bus and Coach Stations 21 4 Other Transport Sources 23 4.1 Airports 23 4.2 Railways (Diesel and Steam Trains) 23 4.3 Ports (Shipping) 23 5 Industrial Sources 24 5.1 Industrial Installations 24 5.2 Major Fuel (Petrol) Storage Depots 24 5.3 Petrol Stations 24 5.4 Poultry Farms 25 6 Commercial and Domestic Sources 26 6.1 Biomass Combustion – Individual Installations 26 6.2 Biomass Combustion – Combined Impacts 26 6.3 Domestic Solid-Fuel Burning 26 7 Fugitive or Uncontrolled Sources 27 8 Local / Regional Air Quality Strategy 28 9 Planning Applications 29 10 Air Quality Planning Policies 30 11 Local Transport Plans and Strategies 31 12 Climate Change Strategies 33

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13 Implementation of Action Plans 35 14 Conclusions and Proposed Actions 38 14.1 Conclusions from New Monitoring Data 38 14.2 Conclusions from Assessment of Sources 38 14.2 Conclusions relating to New Local Developments 38 14.3 Other Conclusions 38 References 39 Appendices

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1 Introduction

1.1 Description of Local Authority Area

The London Borough of Bromley is located in the south east of the capital and, with 58.5 square miles, is geographically the largest London borough. It includes Beckenham, Orpington, West Wickham, Crystal Palace, Cray Valley, Penge and Biggin Hill. It shares boundaries with the London Boroughs of Bexley, Lewisham, Greenwich, Lambeth, Southwark, Croydon and the Counties of Kent and Surrey. Although the Borough is only 12 miles from central London, it contains more than 35 square miles of protected countryside, woodland and parks. This mixture of rural space and suburban development defines much of the Borough’s unique character. The transport networks in Bromley reflect the Boroughs geography, with different travel characteristics in the densely populated northern areas, the suburban town centres and the rural green belt areas in the south. Public transport includes bus and rail with some twenty six stations and Tramlink. There is also a small commercial airport, Biggin Hill, to the southwest of the borough.

The pollutant of most concern in Bromley is nitrogen dioxide (NO2) which in certain parts of the borough is exceeding the air annual mean air quality objective.

1.2 Purpose of Report

Updating and Screening Report This report fulfils the requirements of the Local Air Quality Management process as set out in Part IV of the Environment Act (1995), the Air Quality Strategy for England, Scotland, Wales and Northern Ireland 2007 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 exceedences are considered likely, the local authority must then 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.

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 LAQM in England are set out in the Air Quality (England) Regulations 2000 (SI 928), The Air Quality (England) (Amendment) Regulations 2002 (SI 3043), and are shown in Table 1.1. This table shows the objectives in units of microgrammes per cubic metre g/m3 (milligrammes per cubic metre, mg/m3 for carbon

5 London Borough of Bromley - England monoxide) with the number of exceedences in each year that are permitted (where applicable).

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Table 1.1 Air Quality Objectives included in Regulations for the purpose of Local Air Quality Management in England. Pollutant Air Quality Objective 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 1-hour mean 31.12.2005 exceeded more than 18 times a year 40 µg/m3 Annual mean 31.12.2005 3 Particles (PM10) 50 µg/m , not to be 24-hour mean 31.12.2004 (gravimetric) exceeded more than 35 times a year 3 Annual mean 31.12.2004 40 µg/m Sulphur dioxide 350 µg/m3, not to be 1-hour mean 31.12.2004 exceeded more than 24 times a year 125 µg/m3, not to be 24-hour mean 31.12.2004 exceeded more than 3 times a year 266 µg/m3, not to be exceeded more than 35 15-minute mean 31.12.2005 times a year

7 London Borough of Bromley - England 1.4 Summary of Previous Review and Assessments

1.4.1 First Round of Review and Assessment

Unlike the current format of the Updating and Screening Assessment, Detailed Assessment and Further Assessment, the first round of the review and assessment process was split into four staged reports, with each being more detailed than the last. Through these assessments the Council concluded there were no locations of relevant public exposure where any of the air quality objectives (Table 1.1) were likely to be exceeded.

1.4.2 Second Round of Review and Assessment

The assessment concluded that exceedences of the Air Quality Objectives were unlikely; therefore a Detailed Assessment was not required. Additionally in 2003, the Council published its Local Air Quality Strategy which set out local policies in line with the then Mayor of London’s Air Quality Strategy.

1.4.3 Third Round of Review and Assessment

In 2005, monitoring data indicated that there were several areas where exceedences of the annual mean objective for nitrogen dioxide were likely. The subsequent 2006 Detailed Assessment indicated there to be eight locations where exceedences were likely and a further three areas where exceedences were possible. The report recommended an AQMA be declared to cover these areas.

1.4.4 Air Quality Management Area (AQMA) 2007

th An AQMA for nitrogen dioxide (NO2) was declared on 15 March 2007 (Figure 1). The area of the AQMA is the north-west of the Borough, encompassing Penge, Beckenham and part of Bromley, including the wards of: Crystal Palace; Penge and Cator; Kelsey and Eden Park; Copers Cope; Bromley Town; Shortlands; and Plaistow and Sundridge.

1.4.5 Air Quality Action Plan 2009 (Draft)

Following the declaration of the 2007 Air Quality Management Area to the North and North West of the Borough, due to exceedences of the nitrogen dioxide annual mean Air Quality Objective (AQO), the Council published its draft Air Quality Action Plan. The draft Action Plan sets out a package of measures, using both existing powers available to the Council and working with other organisations, aimed at addressing the nitrogen dioxide exceedences in line with meeting the annual mean AQO.

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Figure 1: 2007 NO2 AQMA

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2 New Monitoring Data

2.1 Summary of Monitoring Undertaken

The Council has historically monitored at five continuous monitoring sites (all now closed) and ten NO2 diffusion tube sites within the borough.

2.1.1 Automatic Monitoring Sites:

Crystal Palace Parade (29th Sept 1999 to 29th July 2010): nitrogen dioxide, particulate matter (PM10), sulphur dioxide and carbon monoxide; Bromley Tweedy Road (28th Jan 1996 to 6th July 1998): carbon monoxide and nitrogen dioxide; Bromley Harwood Avenue (06 Jul 1998 to present): carbon monoxide, nitrogen dioxide and PM10; Bromley Rent Office (1st Jan 1993 to 11th Jan 1996): carbon monoxide, nitrogen dioxide and ozone; and Biggin Hill (1st April 1996 to 9th July 2010): ozone. Seven Oaks Way (1st January 2003 -1st January 2006): nitrogen dioxide.

Further details on these sites are given in Table 2.1 and Figures 2 to 4. In order to provide confidence in the data sets, continuous monitoring was subject to the following QA/QC: Fortnightly manual zero/span calibration using certified cylinders (carried out by trained Local Site Operators (LSOs) at LB Bromley); Full data analysis and ratification through ERG, Kings College London; and Six monthly service visits and site audits.

Figure 2: Crystal Palace Parade Continuous Monitoring Location

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Figure 3: Bromley Tweedy Road, Harwood Avenue and Rent Office Continuous Monitoring Locations

Figure 4: Biggin Hill Continuous Monitoring Location

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Table 2.1: Details of Automatic Monitoring Sites

Relevant Distance Exposure? to kerb of Worst- Site OS Grid Pollutants In (Y/N with nearest case Site Name Type Ref Monitored AQMA? distance (m) to road Location relevant (N/A if not ? exposure) applicable) 60 m Y Crystal NO , PM (diagonally (roadside 533901, x 10 Palace RS (TEOM), Y opposite on 4 m with no 171290 Parade SO2, CO the other side relevant of A212) exposure) Tweedy 540630, RS CO, NO Y Y 80 m N Road 169140 x Harwood 540518, NO , PM 12 m (back RS x 10 Y N Y Avenue 169324 (BAM), CO from site) Bromley 539893, UB NO , O ,CO Y N N/A N Rent Office 169786 x 3 542408, Biggin Hill SU O N Y N/A N/A 159251 3

2.1.2 Non-Automatic Monitoring

The Council operates ten triplicate NO2 diffusion tube sites and one duplicate site (Harwood Avenue) within the borough. All site locations are shown in Figures 5 to 9 with site details given in Table 2.2. The annual mean results for years 2007-2009 are given in Table 2.4. Figure 5: Area 1 (Elmers End)

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Figure 6: Area 3 (Beckenham Lane), Area 4 (London Road Hope Park), Area 5 (Widmore Road), Area 6 (Burnt Ash Lane) Area 17 (Harwood Avenue AQ Site)

Figure 7: Area 13 (Bromley Common)

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Figure 8: Area 14 (Anerley Hill), Area 16 (Beckenham Road)

Figure 9: Area 15 (A214 Anerley Road)

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Table 2.2: Details of Non- Automatic Monitoring Sites

Relevant Distance Exposure? to kerb of (Y/N with *Worst- Site In nearest Site Name OS Grid Ref distance case Type AQMA? road (m) to Location? (N/A if not relevant applicable) exposure) Area 1 Elmers End R/S 536073 168434 Y N (4 m) 1 m Y (R/S) Area 3 Beckenham R/S 539557 169448 Y N (3 m) 3 m Y (R/S) Lane Area 4 London R/S 539786 170051 Y N (4 m) 2 m Y (R/S) Road Area 5 Widmore R/S 540519 169406 Y **N (0 m) 3 m Y (R/S) Road Area 6 Burnt Ash K/S 540326 170248 Y N (8 m) 0.5 m Y (K/S) Lane Area 13 Bromley R/S 541039 168229 Y N (2 m) 2 m Y (R/S) Common Area 14 Anerley K/S 535042 169558 Y N (13 m) 0.5 m Y (K/S) Hill Area 15 Anerley K/S 533950 170623 Y N (3 m) 0.5 m Y (K/S) Road Area 16 K/S 535945 169767 Y N (10 m) 0.5 m Y (K/S) Beckenham Road Harwood Avenue R/S 540519 169325 Y N (14 m) 3 m Y (R/S) Site type: K = kerbside, B = urban background *where N is given for worst case receptor, this denotes that the monitoring site is closer to the road source than the nearest façade. **not directly on a facade, but is representative of adjacent facade road distance.

2.2 Comparison of Monitoring Results with AQ Objectives

In order to assess measured concentrations against the annual mean nitrogen dioxide air quality objective, both the tubes and the data need to be subject to quality assurance/quality control protocols. These allow for inherent uncertainty in the measured concentrations to be minimised. All details of the QA/QC procedures that have been applied to the diffusion tube monitoring are given in Appendix A. The overall purpose of the combined USA and Progress Report is to identify any possible exceedences of the air quality objectives or significant local changes that are therefore required to be considered as part of a Detailed Assessment. In doing so, it is vital to consider not only the measured concentrations in relation to the objectives, but also whether it represents relevant exposure. In cases where monitoring locations do not represent relevant exposure, the façade distance calculation method as described in LAQM.TG(09) can be used.

2.2.1 Nitrogen Dioxide

The two air quality objectives that ambient concentrations of NO2 need to be assessed against are as follows:

An annual mean of 40 µg/m3; and

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The number of exceedences of the 1 hour mean of 200 µg/m3 (18 allowable exceedences in total).

It should be noted that it is only possible to directly assess against the 1-hour objective if hourly monitoring data is available. In the case of NO2 diffusion tube monitoring the approach suggested in LAQM.TG(09) has been adopted. The approach, based on empirical studies, suggests that where the annual mean is less than 60 µg/m3, exceedences of the short-term objective are unlikely.

Automatic Monitoring Data

The Council has undertaken long-term continuous monitoring for NO2 at two sites within the borough since 1999/2000 (Crystal Palace Parade and Bromley Harwood Avenue). The 2009 annual means for these two sites were 49 µg/m3.and 45 µg/m3 respectively. Results for 2007 to 2009 are given in Table 2.3a, with long term trends in annual mean concentrations since 1999 shown in Figure 10.

Table 2.3a Results of Automatic Monitoring for Nitrogen Dioxide: Comparison with Annual Mean Objective Data Capture for full Annual mean NO2 concentration Within 3 Location calendar year (2009) ( g/m ) AQMA? % 2007 2008 2009 Crystal Palace Parade Y 94 50 49 49 Bromley Harwood Avenue Y 99 47 46 45

Figure 10: Annual NO2 Continuous Monitoring Results (1999-2009)

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Table 2.3b: Results of Automatic Monitoring for Nitrogen Dioxide: Comparison with 1-hour Mean Objective Data Number of Exceedences of Hourly Within Capture 3 Location Mean Standard (200 g/m ) AQMA? 2009 2007 2008 2009 % Crystal Palace Parade Y 94 0 0 0 Bromley Harwood Avenue Y 99 2 0 0

The results given in Table 2.3b relating to the 1 hour objective, show there to have been no exceedences of the hourly mean standard during 2009, with only two previously in 2007 (which is well within the 35 allowable exceedences of 200 g/m3).

Diffusion Tube Monitoring Data

The Council has been monitoring NO2 using passive diffusion tubes for a number of years. The 2007-2009 results for all sites including data capture percentages are given in Table 2.4

Table 2.4: Results of Nitrogen Dioxide Diffusion Tubes Data Capture for Annual mean concentrations Within 3 Site ID and Location full calendar year ( g/m )** AQMA? a 2009 (%) 2007* 2008 2009 1 Y 95 77.2 63.7 49.9 Area 1 2 Y 95 78.2 65.2 54.6 3 Y 95 77.4 66.6 52.0 4 Y 95 52.0 43.8 38.6 Area 3 5 Y 95 50.7 42.4 37.8 6 Y 95 51.6 43.7 39.1 7 Y 95 61.9 45.7 40.2 Area 4 8 Y 95 61.0 55.1 42.7 9 Y 95 60.0 51.5 42.8 10 Y 95 76.7 61.3 49.5 Area 5 11 Y 95 74.6 57.9 51.0 12 Y 95 77.3 59.6 52.8 13 Y 74 53.1 43.3 43.2 Area 6 14 Y 83 49.9 44.9 36.8 15 Y 83 51.1 44.6 39.2 16 Y 95 65.7 52.0 49.3 Area 13 17 Y 79 69.9 51.7 47.7 18 Y 95 63.4 51.7 44.0 19 Y 95 62.0 49.1 44.1 Area 14 20 Y 95 60.4 47.3 43.5 21 Y 95 57.7 49.2 42.3 22 Y 79 74.8 46.2 41.5 Area 15 23 Y 79 61.0 45.7 41.0 24 Y 63 56.7 49.0 45.4 25 Y 63 63.0 49.7 45.2 Area 16 26 Y 63 67.4 47.9 44.0 27 Y 38 73.7 50.1 46.6 Harwood Avenue 28 Y 83 50.1 39.2 37.1 (Site 17) Harwood Avenue 29 Y 83 49.9 37.4 38.8 (Site 17) *2007 data set only represents three months. **Some of the monitoring exposure periods are out of sync and in some cases longer than those given in the UK NO2 Diffusion Tube Calendar, meaning the presented annual mean results may be less precise that would otherwise be expected. This is considered further in the conclusions.

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2.2.2 PM10

The Council has been monitoring PM10 within the borough since October 1999. The results for 2007 to 2009 are given in Table 2.5a with the long term annual means since 2000 shown in Figure 11.

Table 2.5a: Results of PM10 Automatic Monitoring: Comparison with Annual Mean Objective Data Capture for Annual Mean PM10 Concentration Within full calendar year 3 Location ( g/m ) AQMA? 2009 2007 2008 2009 % Crystal Palace Parade Y 87 26 24 24 Bromley Harwood Avenue Y 87 22 23 18

Figure 11: Annual PM10 Continuous Monitoring Results 1999-2009

The results given in Table 2.5a and Figure 11 show there were no exceedences of the 3 annual mean PM10 air quality objective of 40 µg/m in any monitored year. The data presented in Table 2.5b shows the number of exceedences of the hourly mean concentrations for years 2007 to 2009. The results for all years are shown to be well below the objective (i.e. 35 allowable exceedences).

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Table 2.5b Results of PM10 Automatic Monitoring: Comparison with 24-hour Mean Objective Data Number of Exceedences of Daily Mean Within Capture 3 Location Standard (50 g/m ) AQMA? 2009 2007 2008 2009 % Crystal Palace Parade Y 87 24 6 5 Bromley Harwood Avenue Y 87 8 5 2

2.2.3 Sulphur Dioxide

London Borough of Bromley does not monitor for sulphur dioxide and has no AQMA’s for sulphur dioxide.

2.2.4 Benzene

London Borough of Bromley does not monitor for benzene and has no AQMA’s for benzene.

2.2.5 Other pollutants monitored

London Borough of Bromley does not monitor for any other pollutant other than those previously stated.

2.2.6 Summary of Compliance with AQS Objectives

London Borough of Bromley has examined the results from monitoring in the borough. As all monitored concentrations above the nitrogen dioxide annual mean are within the existing AQMA, there is no need to proceed to a Detailed Assessment.

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3 Road Traffic Sources

The Council has reviewed the key changes in terms of road traffic sources that have the potential to impact significantly on local air quality. In line with the criteria set out below, only those changes deemed to be significant have been detailed. The assessment of any such sources has been considered in terms of whether a Detailed Assessment is required. 3.1 Narrow Congested Streets with Residential Properties Close to the Kerb

For the purpose of this assessment the criteria are as follows: Congested street One with slow moving traffic that is frequently stopping and starting due to pedestrian crossings, parked vehicles etc throughout much of the day (not just during rush hours). The average speed is likely to be less than about 25 kph (15 mph). Narrow street One with residential properties within 2 m of the kerb, and buildings on both sides of the road (the buildings on the other side of the road can be further from the road than 2 m). The Council monitors traffic at 40 locations throughout the Borough, which include strategic, secondary and local distribution roads. Having assessed these roads, only one was considered narrow in line with the above criteria, although traffic flows were less than 5000 vehicles per day (vpd). None of the 40 monitored road links are considered to be congested in line with the above criteria. Additionally, whilst some of the Boroughs more strategic routes are congested during peak periods, they are significantly more free flowing for the remainder of the day.

London Borough of Bromley confirms that there are no new/newly identified congested streets with a flow above 5,000 vehicles per day and residential properties close to the kerb, that have not been adequately considered in previous rounds of Review and Assessment.

3.2 Busy Streets Where People May Spend 1-hour or More Close to Traffic

Relevant locations are areas where individuals may regularly spend 1-hour or more, for example, streets with many shops and streets with outdoor cafes and bars. People occupationally exposed in such locations should not be included, as they are not covered by the regulations. The assessment only needs to consider NO2.

London Borough of Bromley confirms that there are no new/newly identified busy streets where people may spend 1 hour or more close to traffic.

20 London Borough of Bromley - England 3.3 Roads with a High Flow of Buses and/or HGVs.

Relevant locations are streets where traffic flows are not necessarily high (fewer than 20,000 vehicles per day) but there is an unusually high proportion of buses and/or HGVs. The assessment needs to consider both NO2 and PM10.

London Borough of Bromley confirms that there are no new/newly identified roads with high flows (20% or more) of buses/HDVs.

3.4 Junctions

Relevant locations are close to junctions where concentrations are usually higher due to the combined impact of traffic emissions on two roads with higher emissions due to stop start driving. The assessment needs to consider both NO2 and PM10.

London Borough of Bromley confirms that there are no new/newly identified busy junctions.

3.5 New Roads Constructed/Proposed Since the Last Round of Review and Assessment

London Borough of Bromley confirms that there are no new roads constructed or proposed since the last round of Review and Assessment

3.6 Roads with Significantly Changed Traffic Flows

Relevant locations are road sections of 10,000 vpd (or more) that have seen more than 25% increase in traffic flow. Roads where such an increase is identified due to improved traffic data also need to be considered. The highest traffic increase since 2006 was shown to be 17.8% on Bromley Common.

London Borough of Bromley confirms that there are no new/newly identified roads with significantly changed traffic flows.

3.7 Bus and Coach Stations

The assessment is only required for bus stations or sections of bus stations that are not enclosed, and where there is relevant exposure, including at nearby residential properties. The assessment is against both the annual mean and the 1-hour NO2 objectives. (The term bus is used to signify both buses and coaches).

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For the purpose of the assessment the criteria are as follows:

relevant exposure within 10 m of any part of the bus station where buses are present (20 m in major conurbations); and the number of movements of buses is greater than 2,500 per day.

London Borough of Bromley confirms that there are no relevant bus stations in the Local Authority area that have not been assessed in previous assessments.

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4 Other Transport Sources

4.1 Airports

Biggin Hill Airport whilst located in the District has been found through previous air quality monitoring not to be a significant impact on air quality. There are also airports in the wider region, however none significantly impact on the Boroughs local air quality

London Borough of Bromley confirms that a Detailed Assessment for Biggin Hill Airport is not required.

4.2 Railways (Diesel and Steam Trains)

This item has changed since the last round of Review and Assessment in terms of moving locomotives, therefore in line with LAQM.TG(09) reference has been made to Para 5.24 prior to completing the checklist items. Stationary locomotives, both diesel and coal fired, can give rise to high levels of sulphur dioxide close to the point of emission. Recent evidence suggests that moving diesel locomotives, in sufficient numbers, can also give rise to high NO2 concentrations close to the track. These two potentially significant sources are considered separately below.

4.2.1 Stationary Trains

London Borough of Bromley confirms that there are no locations where diesel or steam trains are regularly stationary for periods of 15 minutes or more, with potential for relevant exposure within 15m.

4.2.2 Moving Trains

London Borough of Bromley confirms that there are no locations with a large number of movements of diesel locomotives, and potential long-term relevant exposure within 30m.

4.3 Ports (Shipping)

London Borough of Bromley confirms that there are no ports or shipping that meet the specified criteria within the Local Authority area.

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5 Industrial Sources

5.1 Industrial Installations

5.1.1 New or Proposed Installations for which an Air Quality Assessment has been carried out

Significant industrial sources have either not been identified or have been assessed in previous LAQM reports.

London Borough of Bromley confirms that there are no new or proposed industrial installations for which planning approval has been granted within its area or nearby in a neighbouring authority.

5.1.2 Existing Installations where Emissions have Increased Substantially or New Relevant Exposure has been Introduced

London Borough of Bromley confirms that there are no industrial installations with substantially increased emissions or new relevant exposure in their vicinity within its area or nearby in a neighbouring authority.

5.1.3 New or Significantly Changed Installations with No Previous Air Quality Assessment

London Borough of Bromley confirms that there are no new or proposed industrial installations for which planning approval has been granted within its area or nearby in a neighbouring authority.

5.2 Major Fuel (Petrol) Storage Depots

Relevant locations are any major fuel storage depots handling petrol that have not been covered by previous Review and Assessment reports. Nearby sources in neighbouring authorities should also be considered.

There are no major fuel (petrol) storage depots within the Local Authority area.

5.3 Petrol Stations

For the purpose of the assessment the criteria are as follows:

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Petrol stations with an annual throughput of more than 2000 m3 of petrol (2 million litres per annum), and with a busy road nearby, that have not been covered by previous Review and Assessment reports; and Relevant exposure within 10 m of the pumps.

London Borough of Bromley confirms that there are no petrol stations meeting the specified criteria.

5.4 Poultry Farms

This item has changed since the last round of Review and Assessment and should be considered by all authorities.

London Borough of Bromley confirms that there are no poultry farms meeting the specified criteria.

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6 Commercial and Domestic Sources

6.1 Biomass Combustion – Individual Installations

London Borough of Bromley confirms that there are no biomass combustion plants in the Local Authority area.

6.2 Biomass Combustion – Combined Impacts

London Borough of Bromley confirms that there are no biomass combustion plants in the Local Authority area.

6.3 Domestic Solid-Fuel Burning

Relevant locations are areas where the density of coal burning premises exceeds 100 per 500 x 500m area.

London Borough of Bromley confirms that there are no areas of significant domestic fuel use in the Local Authority area.

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7 Fugitive or Uncontrolled Sources

Relevant locations are areas either not covered by previous rounds of Review and Assessment, or where there is new relevant exposure.

London Borough of Bromley confirms that there are no potential sources of fugitive particulate matter emissions in the Local Authority area.

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8 Local / Regional Air Quality Strategy 8.1 Local Air Quality Strategy The Councils Stage 3 Review and Assessment report in 2001 concluded there were no areas within the Borough expected to exceeded any of the AQO’s as set out in the then National Air Quality Strategy 1997. As such, the Council was not statutorily obliged to declare any Air Quality Management Areas. However, in line with Proposal 63 of the 2002 Mayor of London’s Air Quality Strategy, the Mayor required those London Boroughs not declaring an AQMA to instead produce their own local air quality strategy. The London Borough of Bromley published its Strategy in 2003, which is summarised below. Introduction This section ‘sets the scene’ and places the Bromley Air Quality Strategy in the context of other air quality issues and especially the London Air Quality Strategy. Historical Nature of Air Pollution This section looks at the historical nature of air pollution and the key legislation. It includes an account of the ‘great smog’ of 1952 and an example of how this was experienced in Orpington. Air Quality Standards and Objectives Summarises the situation with regard to the air quality standards and objectives as set out in the 2003 Air Quality Strategy for England, Scotland, Wales and Northern Ireland. The Mayors Air Quality Strategy Highlights each of the proposals in the Mayors Air Quality Strategy that require a response by the London Borough of Bromley. There are 87 proposals in total and the ones of relevance to the London Borough of Bromley Air Quality Strategy are set out in this section. Air Quality within the London Borough of Bromley Provides an overview of air quality within the borough (2003) and an indication of what the council anticipates happening in the future. Air Quality and Transport Discusses the impact of transport, especially road traffic as the largest single contributor, to poor air quality in the Borough. Air Quality and Land Use Planning Discusses the role that land use planning can have in helping to reduce air quality problems in the Borough. Action Not Words Discusses the role that land use planning can have in helping to reduce air quality problems in the Borough.

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9 Planning Applications

The London Borough of Bromley confirms there are no significant planning applications that could affect air quality. This situation will be kept under review through the LAQM reporting process.

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10 Air Quality Planning Policies

10.1 The Local Plan Saved Policies (Air Quality) Whilst the new Local Development Framework documents are drawn up under the Planning and Compulsory Purchase Act 2004, a number of Development Plans within the existing Unitary Development Plan (UDP) have been ‘saved’ and form the basis of local planning policy until the new LDF is formulated. In terms of air quality the Council states the following policy: Environmental Resources, Air Quality Policy ER5 In considering proposals for development with a potentially significant direct or indirect impact on air quality, the Council will require submission of an assessment of that impact. The Council will resist development that is likely to cause air quality objectives to be breached, particularly within designated Air Quality Management Areas (AQMAs). UDP Transportation In terms of air quality there are no specific policies set out in the Transport Section of the UDP, but it does state the following objective:

To improve the environment and reduce air and noise pollution by restricting non-essential traffic, particularly in residential areas.

10.2 Core (Spatial) Strategy The strategy will set out a vision, key strategic policies and a spatial strategy for the Borough. It will be based on the objectives of the revised UDP and will establish the key elements of the planning framework for the area. It will reflect national planning policy as well as the London Plan and, once adopted, all other development plan documents will be in conformity with it. Once finalised, details of air quality related policies developed through the LDF, will be detailed in subsequent LAQM reports.

10.3 Supplementary Planning Document: Planning Obligations Currently in draft form, the main aim of the document, is to explain and provide non-statutory guidance on the Council’s general approach to planning obligations, and where possible the requirements and mechanisms for infrastructure contributions. In terms of air quality, the document states that as opposed to the development of a formula, any contribution will be calculated on a case by case basis depending on the scale and impact of the development.

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11 Local Transport Plans and Strategies

The integrated transport strategy for the Borough is laid out in Part 2, Chapter 5 of the current Unitary Development Plan and in detail within the Local (Transport) Implementation Plan. For the purpose of this report only the more detailed LIP is discussed.

11.1 Local (Transport) Implementation Plan. This is a statutory document prepared by each London Borough under the Greater London Authority Act 1999, and sets out the policy context and proposals of the Borough for the implementation of the Mayor of London's Transport Strategy. It is a five-year plan (2005/06 to 2010/11) for the improvement, enhancement and maintenance of a sustainable transport system in the Borough.

The Local (Transport) Implementation Plan also sets out the Council's costed programme of transport schemes to achieve the Mayor’s and the Council's objectives. It is accompanied by a Strategic Environmental Assessment statement that sets out how the plan will be implemented throughout the Borough to produce a better environmental outcome.

LIP Guidance sets out a list of 14 targets that the boroughs must address in their LIP. These targets can be summarised as follows:

1. Road Safety: To achieve a 50% reduction in number of killed and seriously injured (KSI) by 2010 compared to 1994-98 overall.

2. School Road Safety: To review road safety around all primary and secondary schools by 2008 and to implement any accident remedial measures identified by 2011.

3. Bus Excess Waiting Time: To reduce Excess Waiting Time to 1.3 minutes per passenger journey by 2009/10.

4. Borough bus target: To reduce, or maintain at 2005 levels, bus journey times on London Bus Initiative (LBI) bus routes.

5. Traffic volumes: Between 2001 and 2011 to achieve, in the southern sub-region of Outer London, a reduction in weekday traffic growth from 7.5% to 4% and a reduction of 1% in Bromley town centre.

6. General traffic journey reliability: To contribute to London-wide targets to ensure disruption and variability of journey times for general traffic on „A‟ roads and busy bus routes is reduced or not increased year on year.

7. Modal shift: Boroughs and TfL are to maintain or increase the proportion of trips made other than by the car.

8. School Travel Plans: To review travel to all schools by 2008 with significant progress towards this having been made by 2006.

9. Parking and loading regulations: To achieve improvements in compliance from a baseline to be established by TfL (to be supplied by December 2004)

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10. Access: To achieve year on year improvements in the proportion of trips made by equality and inclusion groups underrepresented in the public transport market, particularly disabled people, older people and women travelling at night.

11. Taxicard: To ensure all boroughs conform to a new London-wide standard for Taxicard eligibility and subsidy.

12. Walking: To achieve at least a 10% increase in journeys made by foot between 2001 and 2015.

13. Cycling: To achieve at least an 80% increase in cycling between 2001 and 2011.

14. Roads: To bring all „A‟ roads and busy bus routes to a serviceable standard by 2010.

11.1.1 Air Quality Specifically in reference to air quality, the Local (Transport) Implementation Plan identifies that boroughs must have regard to the Mayor's Air Quality Strategy and encourages them to set out how they are addressing its priorities relevant to their transport responsibilities. Boroughs were also required to set out their policy response to the key proposal for the Low Emission Zone (LEZ). Reference must be made to boroughs' Air Quality Management Area Action Plans where relevant.

The Council’s strategy measures for improving air quality in Bromley as stated in the LIP are as follows:

Implementing an Air Quality Management Area (AQMA) in the north and north-west of the Borough.

Keeping the need for further air quality management measures under regular review.

Securing the implementation of a Low Emission Zone (LEZ) for London in co- operation with TfL, the ALG and other London Boroughs.

Reducing emissions from the council‟s fleet and contractors‟ vehicles, including establishing pilot projects to run fleet vehicles on cleaner fuels/natural gas. Most council vehicles run on natural gas.

Working with the Seltrans partnership and other businesses and TfL to promote the BISTRO bio-diesel project (which is described in more detail in the response to Proposal 4K.Pr4).

To improve the environment and reduce air pollution by restricting nonessential traffic, particularly in residential areas.

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12 Climate Change Strategies 12.1 Bromley’s Carbon Footprint Progress Report: 2008/09 The London Borough of Bromley has set out a policy to reduce its direct carbon dioxide emissions by 25% (over five years) to tackle rising energy costs and its contribution to climate change. In 2006/07, the Council established its carbon footprint for the first time. The carbon baseline was calculated as 37,780 tonnes (t) carbon dioxide equivalent (CO2e).

In 2008/09, the first action year, there was a reduction of 1,177t CO2e (3%) of the Council’s emissions: strong evidence of positive outcomes (across the board) resulting from a comprehensive approach to reducing use of natural resources and environmental impacts. Initiatives resulting in these reductions included installing voltage optimisation of the Civic Centre electrical intake; introducing flexible purchasing of good quality CHP for street lighting; establishing an Environmental Champions Network; and taking action on improving water monitoring and conservation. Bromley’s approach is to monitor (and report on) the effectiveness of such initiatives by measuring energy/fuel/water consumption and waste production and expressing this data as a ‘carbon equivalent’ (CO2e) figure. In this way, much more than just energy use is measured, providing a more rounded assessment of the Council’s environmental impacts. The key areas of the report are structured as follows: Detail on which sectors have been included in the Councils carbon footprint; A discussion of annual progress against the preset baseline; and Detailed sector-by-sector analysis, including how the data was obtained, the action that has been taken, and what carbon impact there has been.

12.1.1 Future Challenges and Targets The foundation of the Carbon Footprint Plan is the five-year Carbon Management Programme1 which aims to reduce the Council’s carbon footprint, by 25% over five years, through a range of initiatives (see Executive Report, October 2008, ED08067). These actions will help to mitigate the Councils climate impacts and reduce revenue costs. The plan will be updated as new projects are implemented. The Council is also committed to reducing its own carbon emissions through National Indicator 185 and has agreed a reduction target and will be assessed on NI 186 (included in Bromley’s Local Area Agreement) which relates to reducing the carbon footprint for the Borough as a whole. Finally, the Council is also committed under the CRC Energy Efficiency Scheme, a new regulatory incentive to improve energy efficiency in large public and private sector organisations. It is a mandatory scheme that aims to improve energy efficiency and reduce the amount of carbon dioxide (CO2) emitted in the UK. CRC will affect large organisations in both the public and private sector. Organisations that meet the qualification criteria, which are based on how much electricity they were supplied in 2008, will be obliged to participate in CRC. Participating organisations will have to monitor their emissions and purchase allowances, initially sold by Government, for each tonne of CO2

1 During 2007/08, the council’s Sustainability Team led a cross-departmental initiative (in partnership with the Carbon Trust’s Local Authority Carbon Management Programme) to develop a Strategy and Implementation Plan to tackle emissions from the council estate (and schools and Mytime properties). A set of action plans outlining both technical and behavioural measures will be implemented over the next five years with a view to significantly reducing our carbon footprint.

33 London Borough of Bromley - England they emit. The more CO2 an organisation emits, the more allowances it has to purchase. So there is a direct incentive for these organisations to reduce their emissions.

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13 Implementation of Action Plans

Following the declaration of the 2007 Air Quality Management Area to the North and North West of the Borough, due to exceedences of the nitrogen dioxide annual mean AQO, the Council published its Action Plan in March 2010. The Action Plan sets out a package of measures, using both existing powers available to the Council and working with other organisations, aimed at addressing the nitrogen dioxide exceedences in line with meeting the annual mean AQO. As publication of the Action Plan coincides with the revision of the Council’s Local (Transport) Implementation Plan, there is an excellent opportunity to integrate the two.

In line with Defra guidance, the Air Quality Action Plan is annually reviewed through Action Plan Progress Reports which allows the local authority to continually assess and amend the mitigation measures as deemed necessary. Given the LB Bromley Action Plan is in its first year (in relation to the review period of this report), it is not appropriate to assess progress at this stage, so instead the list of Actions detailed in the plan are set out below.

Proposal 1. The Council will mitigate against or resist development that is likely to cause air quality objectives to be breached, particularly within designated Air Quality Management Areas.

Proposal 2. The Council will support and investigate the case for promoting a restriction on bonfires based on area and time.

Proposal 3. Investigate the use of Section 106 agreements for future developments within the AQMA.

Proposal 4. Encourage the use of the Mayor of London‟s sustainable design and construction supplementary planning guidance to mitigate against inappropriate design, layout, orientation and construction to avoid increased exposure.

Proposal 5. The Council will ensure all new installations are bought into the relevant regime and existing installations are kept informed of new legislative requirements under the Pollution Prevention and Control Act 1999 and Solvent Emissions Directive.

Proposal 6. The Council will continue to inform residents of the smoke control areas and where necessary take enforcement action if un authorized fuels are burned or unauthorized appliances used.

Proposal 7. Where possible the Council will encourage, through the planning process, developers or new business premises to use low NOx burners or other cleaner fuels including the Sulphur Content of Liquid Fuels (England and Wales) Regulations 2007.

Proposal 8. The Council will promote energy efficiency and sustainability on new developments by supporting the Council sustainability and energy efficiency policy through the planning process.

Proposal 9. The Council will encourage efficient local energy generating schemes, particularly combined heat and power and community heating schemes

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through the Mayor‟s Energy Strategy and the Mayor‟s London Plan (Spatial Development Strategy).

Proposal 10. The Council will encourage energy efficiency measures and insulation of domestic dwellings to reduce energy use.

Proposal 11. Improve links with the energy and housing officers in order to adopt a more holistic approach to air quality.

Proposal 12. Continue to monitor air quality in Bromley, particularly for pollutants of concern such as Nitrogen Dioxide and PM10.

Proposal 13. The Council will seek ways to improve publicity of pollution data and its availability to the public.

Proposal 14. Develop the London Borough of Bromley website to include real time air quality monitoring data.

Proposal 15. Provide data and monitoring services to target problematic junctions in order to improve the movement of traffic.

Proposal 16. Introduction of real time traffic with variable messages for Bromley town centre.

Proposal 17. Provide data or monitoring services to target problematic junctions in order to improve the movement of council vehicles.

Proposal 18. New drivers will be trained in fuel efficient driving.

Proposal 19. Ensure the Councils fleet complies with vehicle standard requirements of Section 83 of the Environment Act 1995.

Proposal 20. We will continue to ensure our fleet vehicles comply with European emission standards.

Proposal 21. The Council will encourage and support employers and other organisations wishing to establish Car Clubs and investigate the possibility of providing on road spaces available for car club vehicles where suitable off-road provision cannot be made.

Proposal 22. The Council will promote workplace car sharing schemes.

Proposal 23. The Council will play an active role in the further development and adoption of the SLFQP including among other initiative trailing of night time deliveries, loading bay optimization and feasibility studies of consolidation centres.

Proposal 24. The Council will reduce pollution from unnecessarily idling vehicles through an awareness campaign and enforcement.

Proposal 25. The Air Quality Officer and Pollution Team will continue to support the LBBWTP and as appropriate provide air quality data and expertise to maximize the potential improvements to air quality.

Proposal 26. The Council will develop strong links with the school travel plan coordinator to help identify and target those schools that due to their proximity to the more congested junctions have a proportionally greater impact on the quality of air.

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Proposal 27. The Council will continue to provide and collect additional air quality data to assist in the identification of problematic junctions adjacent to large employers and schools.

Proposal 28. The Council will support and help promote the numerous initiatives as outlined in Bromley LIPS 2007 such as Bike Week, Walk to School Weeks, EU mobility week and the London Wide “Good going” campaign.

Proposal 29. The Council will seek funding to implement an air quality awareness campaign at local schools that will dovetail with current schemes such as WOW (Walk on Wednesdays, Bike week, Don‟t stop to drop).

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14 Conclusions and Proposed Actions

14.1 Conclusions from New Monitoring Data

The London Borough of Bromley has historically monitored at five continuous monitoring sites (all now closed) and ten NO2 diffusion tube sites within the Borough.

Assessment of the 2007 – 2009 NO2 datasets shows there were exceedences of the annual mean objective at the Crystal Palace and Harwood Avenue continuous monitoring sites in all years. Both these sites are with the current AQMA. The results also show there to have been no exceedences of the hourly mean air quality objective. Figure 10 shows the annual results at the continuous monitoring sites in LB Bromley since 1999. The results for Bromley Harwood Avenue show a clear downward trend up until 2003, after which ambient concentrations increased until 2005. Since this time a gradual downward trend has been apparent. The annual mean results for the Crystal Palace site have remained relatively stable since monitoring began in 2000.

In 2009, the annual mean NO2 objective was exceeded at 9 of the 12 diffusion tubes sites in LB Bromley, all of which are in the existing AQMA.

Analysis of measured PM10 concentrations at both continuous monitoring sites shows a general downward trend during the period 1999 – 2009. In conclusion, neither a Detailed Assessment nor additional monitoring is considered necessary. However it should be noted that some of the monitoring exposure periods are out of sync and in some cases longer than those given in the UK NO2 Diffusion Tube Calendar, meaning the presented annual mean results may be less precise that would otherwise be expected. Nevertheless the ratified data sets given in the report are considered to be as accurate as possible and therefore indicative of local ambient concentrations. For future monitoring, the changeover dates for the diffusion tubes will (where possible) tightly adhere to the official changeover timetable.

14.2 Conclusions from Assessment of Sources

No significant changes or developments have been identified since the 2006 USA, which are likely to lead to significant increases in any pollutant prescribed in the Air Quality Strategy, and therefore a Detailed Assessment is not required. 14.2 Conclusions relating to New Local Developments

The London Borough of Bromley confirms there are no significant planning applications that could affect air quality. This situation will be kept under review through the LAQM reporting process.

14.3 Other Conclusions

Given the draft nature of the Council Air Quality Action Plan, progress reporting on the implementation of the listed actions will be detailed in subsequent LAQM reports.

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References

London Borough of Bromley, Round One Review and Assessment.

London Borough of Bromley, Round Two Review and Assessment.

London Borough of Bromley, Round Three Review and Assessment.

London Borough of Bromley, Air Quality Action Plan 2009.

Defra, Part IV of the Environmental Act 1995 Local Air Quality Management Technical Guidance LAQM.TG(09), 2009.

Defra, Part IV of the Environmental Act 1995 Local Air Quality Management Policy Guidance LAQM.PG(09), 2009.

Local Authority Air Quality Support, NO2 Diffusion Tube QA/QC, WASP Rounds

Air Quality Review and Assessment Website, Nitrogen Dioxide Diffusion Tube Bias Adjustment. (http://laqm.defra.gov.uk/bias-adjustment-factors/national-bias.html)

The London Air Quality Network (http://www.londonair.org.uk/)

The Volatile Correction Model (http://www.volatile-correction-model.info/)

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Appendices

Appendix A: QA/QC Data Appendix B: LAPPC Authorised Processes

40 London Borough of Bromley - England Appendix A: QA:QC Data

Diffusion Tube Bias Adjustment Factors Bias adjustment is effectively a calculated factor which shows whether diffusion tubes are over or under reading ambient concentrations and therefore allows for a correction to be made. London Borough of Bromley uses the national factor as given on the review and assessment help desk website for Gradko. The preparation method is 50% TEA/Acetone. Results of the last three years were as follows: 2007 - 0.99 2008 - 0.94 2009 - 0.97

PM Monitoring Adjustment The datasets given in the report for PM10 (TEOM) can be read at gravimetric results as they have been subject to the Volatile Correction Methodology.

QA/QC of automatic monitoring Details of automatic monitoring QA/QC is given in Section 2.1.1.

QA/QC of diffusion tube monitoring The Workplace Analysis Scheme for Proficiency (WASP) is an independent analytical performance testing scheme, operated by the Health and Safety Laboratory (HSL). WASP formed a key part of the former UK NO2 Network’s QA/QC, and remains an important QA/QC exercise for laboratories supplying diffusion tubes to Local Authorities for use in their Local Air Quality Management work.

Defra and the Devolved Administrations advise that diffusion tubes used for LAQM should be obtained from laboratories that have demonstrated satisfactory performance in the WASP scheme.

Out of a rating of GOOD, ACCEPETABLE, WARNING AND FAILURE, the results for WASP Rounds 103 - 107 (Oct 2008 - Oct 2009) show that Harwell Scientific where rated as GOOD. This is classified as follows:

GOOD: Results obtained by the participating laboratory are on average within 13% of the assigned value. This equates to an RPI of 169 or less.

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Appendix B: LAPPC Authorised Processes

Table B1. Part B Authorised Processes within the London Borough of Bromley PROCESS SITE NAME/ PROCESS DATE OF ISSUE SITE ADDRESS/LOCATION DESCRIPTION OPERATOR GUIDENCE NOTE Columbia Ribbon TQ 36686 71169 06/10/2006 Kangley Bridge Road, Lower Sydenham, London, SE26 5AW PG6/44(04) Manufacturing Company Ltd Beckenham Crematorium TQ 35398 68880 05/09/1991 Elmers End Road, Beckenham, BR3 4TD PG5/2(04) CEMEX UK Limited TQ 36621 71333 11/04/1990 Kangley Bridge Road, Lower Sydenham, London, SE26 5AJ PG3/01(04) Syd Bishop & Sons Waldens Depot, Waldens Road, St Mary Cray, Orpington, Kent, TQ 48703 67028 12/10/1993 PG 3/16(04) (Demolition) Ltd BR5 4EU McKenna Demolition Ltd TQ 40657 60781 04/03/2004 The Pump House, Saltbox Hill, Biggin Hill, Kent, TN16 3EE PG 3/16(04) Bournewood Sand and Gravel, Quarry Drive, A20 Bypass, J D Demolition TQ 50485 68522 09/02/2007 PG 3/16(04) Swanley, Kent, BR8 7DP Bournewood Sand and Gravel, Quarry Drive, A20 Bypass, J D Demolition TQ 50485 68522 09/02/2007 PG 3/16(04) Swanley, Kent, BR8 7DP Churchill Accident Repair UK Assistance accident Repair centre, Unit D, Brook Industrial TQ 47140 68318 15/03/2007 PG 6/34b (06) Centre Park, Millbrook Road, Orpington, Kent, BR5 3TX Units 10 and 11 Fitzroy Business Park, Sandy Lane, Sidcup, Spectrum Vehicles Repairers TQ 47970 70146 31/01/2007 PG 6/34b (06) Kent, DA14 5AH Tesco Petrol Filling Station, TQ 47609 70321 02/06/1998 Edgington Way, Sidcup, Kent, DA14 5BN PG1/14(06). Edgington Way Tesco Petrol Filling Station, TQ 47128 69083 02/06/1998 147 Sevenoaks way, Orpington, Kent BR5 3AQ PG1/14(06). Sevenoaks way, Tesco Petrol Filling Station, TQ 35884 68209 02/06/1998 36 Croydon Road, Beckenham, Kent, BR3 4AA PG1/14(06). Croydon Road Tesco Petrol Filling Station, TQ 41275 65760 02/06/1998 115-119 Westmoreland Road, Bromley Kent BR2 0UJ PG1/14(06). Westmoreland Road, BP Petrol Filling Station, TQ 47970 70146 30/01/2001 Edgington Way, Sidcup, Kent, DA14 5AH PG1/14(06). Edgington Way BP Petrol Filling Station, TQ 49230 70023 3001/2001 Swanley By-Pass, A20, Sidcup, Kent, DA14 5JA PG1/14(06). Swanley South BP Petrol Filling TQ 42104 72956 27/07/1998 21 Mottingham Road, London, SE9 4QN PG1/14(06). Station,Mottingham Road BP Petrol Filling Station, TQ 45231 64964 30/01/2001 318 Court Road, Orpington, Kent, BR6 9QB PG1/14(06). Court Road BP Petrol Filling TQ 40626 69470 08/07/1998 133-151 Widmore Road, Bromley, Kent, BR1 3AA PG1/14(06).

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PROCESS SITE NAME/ PROCESS DATE OF ISSUE SITE ADDRESS/LOCATION DESCRIPTION OPERATOR GUIDENCE NOTE Station,Widmore Road BP Petrol Filling Station, TQ 42347 66306 21/10/1998 53 Hastings Road, Bromley, BR2 8NA PG1/14(06). Hastings Road BP Petrol Filling Station, TQ 44785 71973 08/07/1998 Perry Street, Chislehurst, Kent BR7 6HB PG1/14(06). Perry Street Esso Petrol Station, Bromley TQ 36883 69244 24/09/2008 202 Bromley Road, Beckenham, Kent, BR3 3PR PG1/14(06). Road Chimes Petrol Station, TQ 47316 62692 30/10/1998 Sevenoaks Road, Pratts Bottom, Kent, BR6 7SG PG1/14(06). Sevenoaks Way Esso Petrol Station, Links TQ 37537 67285 24/08/1998 1-3 links Way, Beckenham, Kent, BR3 3DG PG1/14(06). Way Whitehouse Service Station, TQ 41909 65076 24/09/1998 69-71 Croydon Road, Keston, BR2 8HU PG1/14(06). Croydon Road Murco Petroleum, TQ 46405 69512 10/12/1998 Chipperfield, Orpington, BR5 2QR PG1/14(06). Chipperfield WJ King Service Station, TQ 41461 67898 30/10/1998 93-101 Bromley Common, Bromley, Kent, BR2 9RN PG1/14(06). Bromley Common Shell Petrol Filling Station, TQ 44420 67481 30/04/1998 52 Queensway, Petts Wood, Kent BR5 1DH PG1/14(06). Queensway Shell Petrol Filling Station, TQ 42431 65983 21/10/1998 116-118 Hastings Road, Bromley, Kent BR2 8NH PG1/14(06). Hastings Road Farnborough Hill Service TQ 45515 63937 21/10/1998 Farnborough, Kent, BR6 6DA PG1/14(06). Station, Farnborough Aperfield Petrol Station, Main TQ 41828 59291 25/09/1998 141 Main Road, Biggin Hill, TN16 3DX PG1/14(06). Road Texaco Petrol Station, High TQ 46592 66817 25/09/1998 2-4 High Street, Orpington, Kent BR6 0JG PG1/14(06). Street West Wickham Manor TQ 37825 66048 26/01/1999 171 High Street, West Wickham, Kent BR4 0LU PG1/14(06). Service Station, High Street Service Station, High Street TQ 45605 63423 08/02/1999 77 High Street, Green Street Green, Kent BR6 6BJ PG1/14(06). Service Station, Beckenham TQ 35978 69759 21/01/1999 128 Beckenham Road, Kent BR3 4RJ PG1/14(06). Road Beckenham s/stn, Croydon TQ 36883 69244 21/10/1998 291 Croydon Road, Beckenham, Kent, BR3 3PR PG1/14(06). Road Hayes S/stn, Station TQ 40074 66160 21/10/1998 1-3 Station Approach, Hayes, Kent, BR2 7EQ PG1/14(06). Approach

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PROCESS SITE NAME/ PROCESS DATE OF ISSUE SITE ADDRESS/LOCATION DESCRIPTION OPERATOR GUIDENCE NOTE Orpington S/stn, Sevenoaks TQ 45964 65161 08/02/1999 85-87 Sevenoaks Road, Orpington, Kent, BR6 9JW PG1/14(06). Road Shell Petrol Filling Station, TQ 41778 62582 08/02/1999 114-116 Leaves Green Road, Keston, Kent BR2 6DE PG1/14(06). Leaves Green BP Petrol Filling Station, TQ 35374 69882 08/02/1999 42 Croydon Road, Penge, London SE20 7AE PG1/14(06). Croydon Road BP Petrol Filling Station, TQ 34401 70074 26/01/1999 107-111 Anerley Road, Anerley, London, SE20 8AP PG1/14(06). Anerley Road BP Oil Uk, Crofton Road TQ 43123 65075 08/07/1998 391 Crofton Road, Orpington, Kent, BR6 8NL PG1/14(06). Alan Dry Cleaners, High St, TQ 38377 65640 31/10/2006 52 High Street, West Wickham, Bromley, Kent, BR4 ONH PG6/46(04) ACE Dry Cleaners TQ 38300 66013 31/01/2007 87 Station Road, West Wickham, BR4 0PX PG6/46(04) Aquar Dry Cleaners TQ 35073 70544 31/01/2007 29 High Street, Penge, London, SE20 7HJ PG6/46(04) Bandbox Ltd TQ 45443 64425 31/01/2007 20 Crescent Way, Orpington, BR6 9LS PG6/46(04) Bandbox Ltd TQ 44398 67706 31/01/2007 207 Pettswood Road, Pettswood, Orpington, BR5 1LA PG6/46(04) Belmont Dry Cleaners TQ 43995 71068 31/01/2007 11-12 Belmont Parade, Green Lane, Chiselhurst, BR7 6AN PG6/46(04) Belmont Drycleaners TQ 38103 66330 31/01/2007 3 Ravenswood Crsecent, West Wickham, Kent, BR4 0JH PG6/46(04) Benjamins Dry Cleaners TQ 42327 58487 23/02/2010 222 Main Road, Biggin Hill, Kent, TN16 3BD PG6/46(04) Bens Dry Cleaners TQ 36691 68977 31/01/2007 322 Croydon Road, Beckenham, Kent, BR3 4HR PG6/46(04) Blue Pearl TQ 42464 65907 31/01/2007 137 Hastings Road, Bromley, BR2 8NQ PG6/46(04) Blueline TQ 41525 59111 31/01/2007 8 Roundway, Biggin Hill, Kent, TN16 3XZ PG6/46(04) Bromley Express TQ 40550 70290 31/01/2007 18 Plaistow Lane, Bromley, Kent, BR1 3PA PG6/46(04) Bromley Express TQ 39948 69726 31/01/2007 22 London Road, Bromley, BR1 3QR PG6/46(04) Carmen TQ 40203 69887 31/01/2007 80 College Road, Bromley, BR1 3PE PG6/46(04) Chislehurst Dry Cleaners TQ 43397 71287 30/07/2006 9 Whitehorse Hill, Chislehurst, BR7 6DG PG6/46(04) Cleanpeople TQ 47505 65976 31/01/2007 51 Eldred Drive, Orpington, BR5 4PE PG6/46(04) Coney Hall Dry Cleaners TQ 39429 65292 31/01/2007 66 Croydon Road, West Wickham, BR4 9HU PG6/46(04) Domino Dry Cleaning TQ 37425 69685 31/01/2007 36 High Street, Beckenham, Kent, BR3 1AY PG6/46(04) Dry-Ice Dry Cleaners TQ 39416 69368 31/01/2007 75 Beckenham Lane, Shortlands, Bromley, BR2 0DN PG6/46(04) Eden Park TQ 37329 67583 31/01/2007 523 Upper Elmers End Road, Bromley, BR3 3DE PG6/46(04) Elmstead Dry Cleaners TQ 42688 70916 31/01/2007 2 Waldon Parade, Waldon Road, Chislehurst, BR7 5DW PG6/46(04) Expressions TQ 44333 67525 31/01/2007 Queensway, Petts Wood, Orpington, BR5 1DQ PG6/46(04) Fimas TQ 46560 68387 31/01/2007 62 Sayes Court Road, St Pauls Cray, Orpington, BR5 2PQ PG6/46(04) First Class Dry Cleaners TQ 40057 66085 31/01/2007 34 Station Approach, Hayes, Bromley, BR2 7EJ PG6/46(04) Glenair Cleaners TQ 43954 70659 31/01/2007 15 High Street, Chislehurst, Kent, BR7 5AB PG6/46(04) Golden Arrow Dry Cleaners TQ 34067 70393 31/01/2007 80 Anerley Road, Crystal Palace, London SE19 2AH PG6/46(04)

44 London Borough of Bromley - England

PROCESS SITE NAME/ PROCESS DATE OF ISSUE SITE ADDRESS/LOCATION DESCRIPTION OPERATOR GUIDENCE NOTE Goldstar Dry Cleaners TQ 46606 69281 31/01/2007 119 Cotmandene Crescent, St Pauls Cray, Kent, BR5 2RB PG6/46(04) Hudson TQ 34689 69739 31/01/2007 149 Anerley Road, Anerley, London, SE20 8EF PG6/46(04) Jays Dry Cleaners TQ 35254 69130 31/01/2007 92 Elmers End Road, Beckenham, Kent, BR3 4TA PG6/46(04) Johnson Cleaners TQ 37095 69325 31/01/2007 177 The Highstreet, Beckenham, Kent, BR3 1AH PG6/46(04) L K TQ 37905 66035 31/01/2007 113 High Street, West Wickham, BR4 0LT PG6/46(04) Macks Dry Cleaners TQ 36005 70363 31/01/2007 200 Kenthouse Road, Beckenham, BR3 1JN PG6/46(04) McKenzie Brentall TQ 40316 67653 31/01/2007 38 Letchworth Drive, Bromley, Kent, BR2 9BE PG6/46(04) Michigan Cleaners TQ 46184 66043 31/01/2007 275 High Street, Orpington, Kent, BR6 0NW PG6/46(04) Michigan Cleaners TQ 36935 69306 31/01/2007 413 Croydon Road, Beckenham, BR3 3PP PG6/46(04) Spot On dry Cleaners TQ 44790 66455 31/01/2007 98 Crofton La, Orpington, BR5 1HD PG6/46(04) Chancery Dry Cleaners TQ 37951 69401 11/01/2010 78 Bromley Road, Beckenham, Kent, BR3 5NP PG6/46(04) Orbit Cleaners TQ 36508 69611 31/01/2007 52 Beceknham Road, Beckenham, BR3 4LS PG6/46(04) Panda TQ 40301 69411 31/01/2007 4 East Street, Bromley, BR1 1QX PG6/46(04) Parish Cleaners TQ 35728 70373 31/01/2007 163 Parish Lane, Penge, London, SE20 7JH PG6/46(04) Penge Express Dry Cleaners TQ 35300 70366 31/01/2007 86 High Street, Penge, London, SE20 7HB PG6/46(04) Premier Dry Cleaners TQ 41678 69353 31/01/2007 193 Widmore Road, Bromley, BR1 2RG PG6/46(04) Pressys TQ 36632 67708 31/01/2007 293 Upper Elmers End Road, Beckenham, Kent, BR3 3QP PG6/46(04) Supreme Clean TQ 36286 68455 31/01/2007 127 Croydon Road, Beckenham, BR3 3RA PG6/46(04) Regal Cleaners TQ 36932 69369 31/01/2007 426 Croydon Road, Beckenham, Kent, BR3 4EP PG6/46(04) SE20 dry Cleaners TQ 35590 70057 16/04/2007 6 Central Parade, High Street, Penge, London, SE20 7TN PG6/46(04) Regency Dry Cleaners TQ 42379 71747 31/01/2007 62 Kimmeridge Road, Mottingham, SE9 4EB PG6/46(04) Royal Dry Cleaners TQ 44430 70100 31/01/2007 12 Royal Parade, Chiselhurst, BR7 6NR PG6/46(04) Smarty Pants TQ 44330 67598 31/01/2007 21 Chatwsorth Parade, Pettswood, BR5 1DF PG6/46(04) Splash Dry Cleaners TQ 43246 65153 31/01/2007 2 Princess Parade, Crofton Road, Orpington, BR6 8NP PG6/46(04) Streakers TQ 40652 71072 31/01/2007 109 Burnt Ash Lane, Bromley, BR1 5AB PG6/46(04) Surtex Textiles TQ 40309 68580 31/01/2007 3 Simpsons Road, Bromley, BR2 9AP PG6/46(04) Top Press TQ 46709 67828 31/01/2007 7 Stanley Way, Orpington, Kent, BR5 2HE PG6/46(04) Aqua Dry Cleaners TQ 39328 67775 31/01/2007 159 Westmoreland Road, Bromley, BR2 0TZ PG6/46(04) Novus Dry Cleaners TQ 46689 64017 31/01/2007 31 Windsor Drive, Orpington, BR6 6EY PG6/46(04) Orpington Express TQ 46735 66922 31/03/2010 11 Carlton Parade, Orpington, Kent, BR6 0JB PG6/46(04) Slacks Dry Cleaning TQ 42822 67683 16/12/2009 221 Southborough Lane, Bickley, Kent, BR2 8AT PG6/46(04) Parker’s Dry Cleaners TQ 42181 72833 07/01/2010 54-56 Mottingham Road, Eltham, London, SE9 4QR PG6/46(04) Village Dry Cleaners TQ 41776 67789 31/03/2010 46 Chatterton Road, Bromley, BR2 9QE PG6/46(04) Exclusive Dry Cleaners TQ 40516 66364 31/01/2007 48 Hayes Street, Hayes, Bromley, BR2 7LD PG6/46(04)