2012 Air Quality Updating and Screening Assessment for Harrogate Borough Council

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

April 2012

Harrogate Borough Council

Local Authority Emily Revill Officer Department Community Services Springfield House, Kings Road, Address Harrogate, HG1 5NX Telephone 01423 556865 e-mail [email protected] Report Reference USA2012 number Date April 2012

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Executive Summary

The Environment Act 1995, Part IV established a national framework for air quality management requiring all Local Authorities to conduct air quality reviews of their areas in accordance with relevant government guidance. This report forms part of this review, being the 2012 Updating and Screening Assessment of air quality for the district. The report considers each pollutant listed in the air quality regulations; these are carbon monoxide, benzene, 1,3-butadiene, lead, nitrogen dioxide, sulphur dioxide, and PM10.

The report follows on from the 2011 Progress Report and considers the changes in the local area since the previous Updating and Screening Assessment carried out in 2009. If, based on this information, it is considered that if any of the objectives are not likely to be achieved then a Detailed Assessment must be carried out.

The report considers the results from monitoring carried out in 2011 and identifies York Place, Knaresborough as an area where further monitoring needs to be carried out to identify whether an exceedence is occurring at residential properties and identifies that the air quality objective has been exceeded at the Woodlands Junction, Wetherby Road.

The report shows that there is continued exceedence of the Air Quality Objective at Bond End, Knaresborough and Low and High Skellgate, Ripon, and that the extent of the current Air Quality Management areas is correct.

LAQM USA 2012 2 Harrogate Borough Council Table of contents

1 Introduction ...... 6 1.1 Description of Local Authority Area ...... 6 1.2 Purpose of Report ...... 6 1.3 Air Quality Objectives ...... 7 1.4 Summary of Previous Review and Assessments ...... 10 1.4.1 2006 Updating and Screening Assessment Report ...... 14 1.4.2 2007 Annual Progress Report ...... 14 1.4.3 2008 Interim Annual Progress Report ...... 14 1.4.4 2009 Detailed Assessment Report ...... 15 2 New Monitoring Data ...... 20 2.1 Summary of Monitoring Undertaken ...... 20 2.1.1 Automatic Monitoring Sites ...... 20 2.1.2 Non-Automatic Monitoring Sites ...... 20 2.1.3 Details of Quality Assurance/Quality Control (QA/QC)...... 23 2.2 Comparison of Monitoring Results with AQ Objectives ...... 24 2.2.1 Nitrogen Dioxide ...... 24 2.2.1.3 Wetherby Road/Hookstone Drive Junction Harrogate Survey ...... 27 2.2.1.4 General District Survey ...... 28

2.2.2 PM10 ...... 32 2.2.3 Sulphur Dioxide...... 32 2.2.4 Benzene ...... 32 2.2.5 Summary of Compliance with AQS Objectives ...... 32 3 Road Traffic Sources ...... 33 3.1 Narrow Congested Streets with Residential Properties Close to the Kerb ...... 33 3.2 Busy Streets Where People May Spend 1 hour or More Close to Traffic ...... 33 3.3 Roads with a High Flow of Buses and/or HGVs...... 34 3.4 Junctions ...... 34 3.5 New Roads Constructed or Proposed Since the Last Round of Review and Assessment ...... 35 3.6 Roads with Significantly Changed Traffic Flows ...... 35 3.7 Bus and Coach Stations ...... 35 4 Other Transport Sources ...... 37 4.1 Airports ...... 37 4.2 Railways (Diesel and Steam Trains) ...... 37 4.2.1 Stationary Trains ...... 37 4.2.2 Moving Trains ...... 38 4.3 Ports (Shipping) ...... 38

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5 Industrial Sources ...... 39 5.1 Industrial Installations ...... 39 5.1.1 New or Proposed Installations for which an Air Quality Assessment has been Carried Out………………………...... 39 5.1.2 Existing Installations where Emissions have Increased Substantially or New Relevant Exposure has been Introduced ...... 39 5.1.3 New or Significantly Changed Installations with No Previous Air Quality Assessment ... 40 5.2 Major Fuel (Petrol) Storage Depots ...... 40 5.3 Petrol Stations...... 40 5.4 Poultry Farms...... 40 6 Commercial and Domestic Sources ...... 42 6.1 Biomass Combustion – Individual Installations ...... 42 6.2 Biomass Combustion – Combined Impacts ...... 42 6.3 Domestic Solid-Fuel Burning ...... 42 7 Fugitive or Uncontrolled Sources ...... 44 8 Conclusions and Proposed Actions ...... 45 8.1 Conclusions from New Monitoring Data ...... 45 8.2 Conclusions from Assessment of Sources ...... 45 8.3 Proposed Actions ...... 45 9 References ...... 47

List of Tables

Table 1. Air Quality Objectives included in Regulations for the purpose of LAQM in England

Table 2. Summary of Previous Review and Assessments Table 3. Details of Non-Automatic Monitoring Sites Table 4. Results of Nitrogen Dioxide Diffusion Tubes - Ripon Central Survey Table 5. Results of Nitrogen Dioxide Diffusion Tubes - Knaresborough Central Survey Table 6. Results of Nitrogen Dioxide Diffusion Tubes – Wetherby Road/Hookstone Chase Junction Harrogate Survey Table 7. Results of Nitrogen Dioxide Diffusion Tubes – General District Survey Table 8. Maximum number of daily bus movements at the busiest three bus stations in the Harrogate District (2009 figures)

List of Figures

Figure 1.1 Map of Knaresborough AQMA Figure 1.2 Map of Ripon AQMA

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Figure 2.4 Trends in Annual Mean Nitrogen Dioxide Concentrations measured at Diffusion Tube Monitoring Sites Figure 2.5 Trends in Annual Mean Nitrogen Dioxide Concentrations measured at Diffusion Tube Monitoring Sites Figure 2.6 Trends in Annual Mean Nitrogen Dioxide Concentrations measured at Diffusion Tube Monitoring Sites Figure 2.8 Trends in Annual Mean Nitrogen Dioxide Concentrations measured at Urban Background Sites

Appendices

Appendix A Locations of NO2 diffusion tubes

Appendix B QA/QC Data

Appendix C Industrial Activities – Regulated Under the Environmental Permitting Regulations 2010 at 1 April 2012

Appendix D Full dataset (monthly mean values) of Nitrogen Dioxide Diffusion Tubes.

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1 Introduction 1.1 Description of Local Authority Area

The Harrogate district is part of the County of North Yorkshire and extends over an area of 1,305 square kilometres. It has boundaries with the Leeds/Bradford conurbation to the south, has Nidderdale to the west and extends across part of the Vale of York to the east. The district consists of both rural and urban areas, having large, sparsely populated areas alongside the major settlements of Harrogate, Knaresborough and Ripon.

The district has an estimated population of 158,000. Approximately 70% of the population is centred in the three main towns, with Harrogate having around 78,000 residents, and Knaresborough and Ripon having around 33,000.

Seven local authorities surround Harrogate namely Richmondshire, Hambleton, York, Selby, Leeds, Bradford and Craven.

The most significant source of pollutants likely to impact on air quality objectives is the road network in the district. The A1 (M) motorway, A1 dual carriageway and a small part of the A168 dual carriageway run to the east of the district. There is very little relevant exposure to these roads. Other major roads are the A59 and A61, which both pass through the urban areas of the district.

As the Harrogate district is predominantly rural, consideration is given to emissions associated with agricultural activities especially intensive poultry farming, and domestic solid fuel burning in villages not on the mains gas network, in particular to the north and east of the district.

There are a number of industrial installations and waste facilities in the district of varying sizes that are mostly regulated under the Environmental Permitting Regulations. The Leeds-Harrogate-York railway line runs to the south of the district.

1.2 Purpose of 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.

The objective of this Updating and Screening Assessment is to identify any matters that have changed which may lead to risk of an air quality objective being exceeded. A checklist approach and screening tools are used to identify significant new sources or changes and whether there is a need for a Detailed Assessment. The USA report

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Harrogate Borough Council should provide an update of any outstanding information requested previously in Review and Assessment reports.

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 monoxide) with the number of exceedences in each year that are permitted (where applicable).

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Table 1. Air Quality Objectives included in Regulations for the purpose of LAQM in England Air Quality Objective Date to be Pollutant Concentration Measured as achieved by Running annual 16.25 µg/m3 31.12.2003 mean Benzene Running annual 5.00 µg/m3 31.12.2010 mean Running annual 1,3-Butadiene 2.25 µg/m3 31.12.2003 mean Running 8-hour Carbon monoxide 10.0 mg/m3 31.12.2003 mean 0.5 µg/m3 Annual mean 31.12.2004 Lead 0.25 µg/m3 Annual mean 31.12.2008 200 µg/m3 not to be exceeded more 1-hour mean 31.12.2005 Nitrogen dioxide than 18 times a year 40 µg/m3 Annual mean 31.12.2005 50 µg/m3, not to be exceeded more 24-hour mean 31.12.2004 Particles (PM10) than 35 times a (gravimetric) year 40 µg/m3 Annual mean 31.12.2004 350 µg/m3, not to be exceeded more 1-hour mean 31.12.2004 than 24 times a year 125 µg/m3, not to Sulphur dioxide be exceeded more 24-hour mean 31.12.2004 than 3 times a year 266 µg/m3, not to be exceeded more 15-minute mean 31.12.2005 than 35 times a year

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Harrogate Borough Council 1.4 Summary of Previous Review and Assessments

Table 2. Summary of Previous Review and Assessments Report Title and Date Outcome

Detailed Assessment required for sulphur 2006 Updating and Screening dioxide at Knaresborough Railway Station. Assessment Report Nitrogen dioxide Annual Mean Objective not met at the Woodlands public house, but September 2006 progress to Detailed Assessment not required. Sulphur dioxide Detailed Assessment at 2007 Annual Progress Report Knaresborough Railway Station not carried out as initial investigative work identified no July 2007 relevant exposure.

Nitrogen dioxide Annual Mean exceedence at Low Skellgate, Ripon and Bond End, Knaresborough reported. Detailed Assessment required.

Nitrogen dioxide Annual Mean Objective not met at the Woodlands public house, but progress to a Detailed Assessment not required. Detailed Assessment continues to be 2008 Interim Annual Progress Report required for nitrogen dioxide in central Ripon and central Knaresborough (as per previous June 2008 year).

Continuation of nitrogen dioxide Annual Mean Objective not being met at the Woodlands public house, leads to recommendation for progress to a Detailed Assessment. Progress to declaration of Air Quality 2009 Detailed Assessment Report Management Areas (AQMAs) was recommended at the locations in February 2009 Knaresborough and Ripon, due to a predicted exceedence of the nitrogen dioxide annual mean. Nitrogen dioxide monitoring data for 2008 2009 Updating and Screening continues to indicate an exceedence of the Assessment Report annual mean Air Quality Objective at; Bond End Knaresborough; Low and High September 2009 Skellgate, Ripon; Skipton Road, Harrogate and the junction of Wetherby Road and Hookstone Chase in Harrogate. A number of recommendations were made for future monitoring.

Screening for other pollutants did not identify any other potential exceedences of Air Quality Objectives in the district.

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New monitoring data for nitrogen dioxide 2010 Annual Progress Report confirmed that Air Quality Management Areas should be declared at Low and High June 2010 Skellgate, Ripon and Bond End, Knaresborough.

Re-siting the diffusion tube to first floor level at Woodlands public house has indicated that the annual mean Air Quality Objective for nitrogen dioxide was not exceeded. Air Quality Management Areas (AQMA‟s) Declaration declared for Low and High Skellgate, Ripon and Bond End, Knaresborough for November 2010 exceedences of the annual mean Air Quality Objective for nitrogen dioxide. The report concluded that the following 2011 Annual Progress Report actions are required; - Continue with developing the Further June 2011 Assessment and Air Quality Action Plan - Continue monitoring at locations close to the limits - Carry out triplicate tube monitoring within the Air Quality Management Areas - Continue to monitor the nitrogen dioxide concentration at the Woodlands public house at the 1st floor level, which is the relevant exposure. The Further Assessment concluded that 2012 Further Assessment there remain exceedences of the Air Quality Objective within the AQMA‟s, and that the April 2012 extent of the AQMA‟s is correct. It was found that at least a 16% reduction in NOx was needed to meet the AQO.

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3 75.1m 13 a 2

2 37 72.4m 32 to 1 1 6 House On The Knaresborough Scriven Park El Sub Sta 63.6m 1 Hill 4 House On The Byard's Hill Lodge 1 9 20 1 Byards 2 Cottage to 12 to 18 1 2 B 1 1 1 Y 0 to A 1 1 R 0 3 7 D 2 to 8 The New Row b Rectory Cottage to S 9 1 P 4 64.0m BOROUGHBRIDGEA R 0 B ROAD 10a O 26 K N 1 El Sub Sta CR 9 D KnaresboroughS East E 8 T 60.5m N Dray M D Cottage 1 A Shire R 16 to 22 0 Cottage G 28 Royal 5 10 6 2 A 1 to 38 12 Oak Vale 2 R Dower House BOND Court 60.9m E Hotel END 1 9 T' Shelter 3 1 S 19 1 81 G 21a 2 2 21 3 A4 9a 1 23 1 2 R 4 1 D 6 1 1 1 E 5 Shelter 1 1 7 7 N 1 to 4 to PC 6 Church 1 1 S 55.9m 25 2 1 a Mews to Forest 1 RC 1 0 Collins 2 Court 0 6 Church Parish 1 6 Court 1 6 to 9 44 27 2 15 1 1 5 7 4 to a 5 Works C Knaresborough King James 1 64.0m Stead's H 0 5 U Yard4 Car Park 5 R 5 C H Hi El Sub Sta FS g L Knaresborough h A House N C El Sub Sta E P o U ur St Mews 1 t 5 M 1Margaret's 0 P 0 2 5 9 1 P 4 HI 2 56.6m 9 HI9 at L to G8 h VICARAGE L 1 H Tunnel 9 LANE 0 S 7 9 3 T 1 5 Harrogate9R Borough Council Boundary 1 1E 2 9 E 94a 8 6 St John the T 9 C 9 Church Beeche 8 R 4 Baptist's 7 8 1 s Church 5 Terrace STATION ROAD Tank 72.0m View 2 83 86 5 84 Cliff 7 55.9m 9 77 2 Parish Post 75 Hall Metres Knaresborough Town Centre NOx Exceedences 0 510 20 30 40 Sarah Whittaker 28 September 2010

This map is based upon Ordnance Survey material with the permission of Ordnance Survey on behalf of the Controller of ¯ Her Majesty‟s Stationery Office © Crown copyright. Unauthorised reproduction infringes Crown copyright and may lead to prosecution or civil proceedings. (100019628) (2009).

Figure 1.1 Map of Knaresborough AQMA

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58 W 3a es 60 tg 39.0m at e 4 62 M 27 e MARKET 11c ws Lands PLACE 3 14 Court 1 28 Posts 5 12 25 Obelisk 11a 1 Bk 30 17 9 5 30 SM 36.6m 4a 20 4 a 3a 2 1 P 31 22 WESTGATE H TCBs 27 28 31 34

Bl Ba 37.4m ac 32 33 25 nk k 33 PC 34 LB Jacksons 37 Court Youngs Court Ba S nk 39 w 22 3 24 21 21 1 to 3 To an H a 20 w Ya Be all Ba 15 3 n rd lle 16 nk Ripon Spa vu e S 22 19 Te 8a K rra 8 EL ce PH L 21 Georgias G 9 A 21 Mews Wks T b HI E 4 G 18 2 H 1 11 Fisher's Court Church 17 22 20 19 27 14 Hall WATER SKELLGATE M SOMERSET ROW 7 to 6 AL 6a LA 4 1 R 11 1 Ripon Minster D 23 21 19 15 2 C 3 L 37 Y 1 7 Ri M po 6 1 C Hall 5 n 4 PH to A 9 Cr Cit Heath's Court 6 8 4 8 o y 34 w 8a Cl n ub L C O ou 23 W rt 19 S K 13 EL 28 Cl L CLOSE ub 16 G27 WI A 14 11 13 S LL T IA K El Harrogate Borough Council E 7 MBoundary EL Su L 2 S 24 b G O St N 10 A a T WILLIAMSON CLOSE D LOW E RI 1 V E Riverside House 4 1

Ripon Town Centre NOx Exceedences Metres Sarah Whittaker 28 September 2010 0 5 10 20 30 40 This map is based upon Ordnance Survey material with the permission of Ordnance Survey on behalf of the ControllerHer Majesty‟s of Stationery Office © Crown ¯ copyright.Unauthorised reproduction infringes Crown copyright and may lead to prosecution or civil proceedings. (100019628) (2009).

Figure 1.2 Map of Ripon AQMA

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1.4.1 2006 Updating and Screening Assessment Report

The 2006 Updating and Screening Assessment Report concluded that all air quality objectives for lead, 1,3-butadiene, benzene, carbon dioxide and PM10 would be likely to be achieved throughout the district.

The report showed an exceedence of the Annual Mean Objective for nitrogen dioxide at the junction of Wetherby Road and Hookstone Chase in Harrogate. The result was considered to be irregular due to the placing of the passive diffusion tube close to a ventilation outlet from the public house. In accordance with current guidance it was not considered further.

A potential exceedence of the objective mean for sulphur dioxide was identified at Knaresborough Railway Station. The report recommended progress to a Detailed Assessment for sulphur dioxide at this location.

The report did not identify any other potential or actual exceedences of the objectives for nitrogen dioxide within the Harrogate district.

1.4.2 2007 Annual Progress Report

The 2007 Annual Progress Report reported on findings that led to a detailed assessment for sulphur dioxide at Knaresborough Railway Station being considered unnecessary due to the lack of relevant exposure. It also concluded that monitoring for nitrogen dioxide had identified an exceedence of the Annual Mean Objective at Low Skellgate in Ripon and Bond End in Knaresborough, and recommended progress to a Detailed Assessment for these locations.

The Report also highlighted monitoring, which indicated a potential exceedence of the nitrogen dioxide Air Quality Objective at the Hookstone Chase/Wetherby Road junction in Harrogate, but concluded that progress to a Detailed Assessment at this location was unnecessary.

It reported that real time monitoring of nitrogen dioxide and particulate matter at the air quality monitoring station located on Skipton Road, Harrogate had not identified any potential exceedence of the relevant Air Quality Objective, and that monitoring had been suspended at the end of 2006.

1.4.3 2008 Interim Annual Progress Report

Due to a delay in producing the Detailed Assessment required by the findings of the 2007 Annual Progress Report, an interim Annual Progress Report was produced in June 2008.

The report predicted a continuing exceedence of the nitrogen dioxide Annual Mean Objective at the same locations as the previous year at Bond End in Knaresborough and Low and High Skellgate in Ripon. It also predicted an exceedence at the

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Woodlands public house in Harrogate due to its close proximity to the junction of Wetherby Road and Hookstone Chase. It recommended that a Detailed Assessment is produced for the three areas.

Passive diffusion tube monitoring of nitrogen dioxide indicated no other potential or actual exceedences of Air Quality Objectives in the district.

1.4.4 2009 Detailed Assessment Report

The Detailed Assessment was carried out in response to the identification of possible breaches of the nitrogen dioxide annual mean Air Quality Objective in the Harrogate district, caused by vehicle emissions, at the junction of Wetherby Road and Hookstone Chase in Harrogate, at Bond End, Knaresborough and Low and High Skellgate, Ripon. The assessment was carried out on behalf of Harrogate Borough Council by Air Quality Consultants using a combination of monitoring data collected by the Council and modelled concentrations produced by the consultants using the ADMS (Advanced Dispersion Modelling Software) Roads dispersion model. It made the following conclusions:-

The nitrogen dioxide Annual Mean Objective was predicted to be exceeded at ground floor level at the façade of the Woodlands public house at the junction of Wetherby Road and Hookstone Chase in Harrogate; however the objective applies only to the first floor level at the flat above. The predictions for the first floor were that the objective was not being exceeded, and so the assessment concluded that an AQMA would not be required. It recommended that monitoring be carried out on the upper floor of the public house for a period of twelve months, following which, if the measurements showed that the Annual Mean Objective was being exceeded, then an AQMA should be declared to cover the public house. There were no other potential exceedences of the nitrogen dioxide Annual Mean Objective in the area of this junction.

The nitrogen dioxide Annual Mean Objective was predicted to be exceeded both at ground floor level and at first floor level, at Low and High Skellgate in central Ripon with an estimated 30 properties being affected.

At Bond End, Knaresborough, the nitrogen dioxide Annual Mean Objective was predicted to be exceeded at ground floor level, and, in the worst-case locations, first floor levels too. It estimated that approximately 21 properties were affected.

It recommended that an AQMA be declared to include at least the residential properties whose exposure was predicted to be above the Annual Mean Objective for nitrogen dioxide at both the area in central Ripon and in Bond End Knaresborough.

In addition it was found at both the locations in Ripon and Knaresborough that the area with an Annual Mean above the objective extended beyond the area in which air quality had been modelled; the monitoring domain. It thus recommended that the Further Assessment report consider a wider road network.

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1.4.5 2009 Updating and Screening Assessment Report

Monitoring data in 2008 indicated that the nitrogen dioxide Annual Mean Objective had been exceeded at various locations in the district. None of the exceedences were with existing AQMAs, although the majority are within areas covered by the 2009 Detailed Assessment, and therefore are in areas likely to be declared AQMAs in the near future. In the Central Ripon Survey monitoring indicated exceedences of the nitrogen dioxide Annual Mean Objective at four monitoring locations that are all representative of relevant exposure, two of which had shown exceedences in previous years, and two of which had not.

In the Central Knaresborough Survey, monitoring indicated exceedences of the nitrogen dioxide Annual Mean Objective at four monitoring locations, all of which were representative of relevant exposure, one of which had shown an exceedence in previous years. The other three monitoring locations had shown an exceedence for the first time. Of these locations three are on the Bond End junction and the remaining location is on York Place.

The three locations on Bond End are within the modelling domain and were therefore assessed in the 2009 Detailed Assessment and so a further Detailed Assessment was not required. The monitoring location on York Place was not considered in the 2009 Detailed Assessment and is outside the monitoring domain, however rather than conducting a further Detailed Assessment it was recommended that the monitoring domain assessed in the ADMS Roads model was extended to include the new area of exceedence and the findings included in the 2010 Annual Progress Report.

In the Woodlands junction Harrogate survey the 2008 monitoring data identified an exceedence of the nitrogen dioxide Annual Mean Objective at the façade of the Woodlands public house facing Wetherby Road, although only ten months of monitoring data were collected at this location. In accordance with the recommendations of the 2009 Detailed Assessment this monitoring location and the other monitoring location on the façade of the public house were moved to first floor level, as there is relevant exposure at this location at first floor only. The annual mean nitrogen dioxide concentration measured once twelve months of monitoring data has been collected will be reported in the 2010 Annual Progress Report. If an exceedence of the Annual Mean Objective is predicted then progress straight to declaration of an AQMA will be made, as a Detailed Assessment has already been completed in this location.

In the General District Survey the 2008 monitoring data identified exceedences of the nitrogen dioxide Annual Mean Objective at two locations, one at Skipton Road, Harrogate (borderline exceedence), and the other at Devonshire Place (off Skipton Road), Harrogate. These two residential receptors are located in close proximity to the kerbside of Skipton Road, a busy and congested road, which is one of the main routes through Harrogate.

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The assessment of likely impacts of local developments including road transport, other transport, industrial installations, commercial/domestic, residential and fugitive emissions did not identified any potential exceedences of any of the air quality objectives.

The assessment of poultry farms identified one installation which met the criteria stated in TG.09 regarding capacity and relevant exposure, however it is concluded that progress to a Detailed Assessment at this location, Oaklands Farm near Moor Monkton, was not required due to the geographical separation of the poultry units which meant that relevant receptors were only exposed to a portion of the poultry houses.

The assessment of the biomass district -heating scheme at Denton Hall using the Review and Assessment Tool for biomass combustion stacks identified potential exceedences of the air quality objectives for PM10 and nitrogen dioxide, with regard to the one-hour mean objective. Use of the „Approaches to adding industrial contributions to the background‟ methodology taken from TG.09 and emission rate data specific to the type of appliance have ruled out these potential exceedences and it was concluded that there is no requirement to proceed to a Detailed Assessment with respect to emissions from the district-heating scheme.

The report concluded that it was not necessary to carry out any additional Detailed Assessments (other than those reported in 2009). A number of recommendations were made in the report for additional monitoring to be undertaken during 2009. These are reported in this Progress Report.

1.4.6 2010 Annual Progress Report

The monitoring data for 2009 confirmed the conclusions from the Detailed Assessment undertaken, that AQMA‟s should be declared at Low Skellgate and High Skellgate, Ripon and Bond End, Knaresborough. The re-siting of diffusion tubes at the Woodlands public house at the Wetherby Road/Hookstone Drive junction, has confirmed that at the first floor level (relevant exposure) the annual mean Air Quality Objective for nitrogen dioxide was not exceeded and that it is not necessary to declare an AQMA at this location at this time,

The exposure of extra tubes at locations in Ripon and Knaresborough, for 5 months only, has suggested that the nitrogen dioxide concentration is below the Air Quality Objective with the exception of the Royal Oak, Bond End Knaresborough. This was calculated using the annualised mean from the Knaresborough town centre study. The 18 diffusion tubes forming the general district survey indicated that no location was breaching the annual or 1-hour mean for nitrogen dioxide. The background nitrogen dioxide concentration has remained fairly constant for the past five years, at between 14µg/m³ and 16µg/m³.

The main actions arising from the report were to complete the declaration of the two proposed AQMAs, develop an Air Quality Action Plan for the areas, to continue to monitor the nitrogen dioxide concentration at the Woodlands Public House at the 1st floor level (the relevant exposure) and to evaluate the data from the additional

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Harrogate Borough Council diffusion tube monitoring undertaken in Knaresborough and Ripon, when a full 12 months of data has been obtained.

1.4.7 2010 Air Quality Management Area Declaration

The Air Quality Management Areas for Low and High Skellgate, Ripon and Bond End, Knaresborough were declared on the 26 November 2010, figures 1.1 and 1.2 show maps of the AQMA boundaries. Work on the Further Assessment and planning for the Air Quality Action Plan has commenced.

1.4.8 2011 Annual Progress Report

The monitoring data has shown that the only relevant breaches of the annual mean Air Quality Objective for nitrogen dioxide have been within the areas that were declared Air Quality Management Areas in November 2010. The full years monitoring results for the Royal Oak at Bond End, Knaresborough (tube H51) has confirmed that the annual mean Air Quality Objective has been exceeded.

The results for the Woodlands public house at the Wetherby Road/Hookstone Drive junction have shown that whilst the Air Quality Objective for nitrogen dioxide has not been breached, there is a borderline figure. Monitoring will carry on at this location and a further assessment of the results will be made at the next round.

The tubes for the general district survey did not exceed the annual mean or the 1- hour mean Air Quality Objective for nitrogen dioxide. Tube H45 (Westmoreland Street/Skipton Road junction) reached a level of 38.48µg/m³, this will be considered at the next round of assessment.

The background concentration of nitrogen dioxide across the Harrogate district has reduced when compared with results from the past 5 years.

The report concludes that the following actions are required; Continue with developing the Further Assessment and Air Quality Action Plan Continue monitoring at locations close to the limits Carry out triplicate tube monitoring within the Air Quality Management Areas Continue to monitor the nitrogen dioxide concentration at the Woodlands public house at the 1st floor level, which is the relevant exposure.

1.4.9 2012 Further Assessment

The main aims of the Further Assessment are: to show that the decision to declare the AQMA and the extent of the AQMA remain appropriate; and to identify and quantify the principle pollution sources contributing to the Air Quality Objective (AQO) exceedences at location within the AQMA, this is called source apportionment. This will support the development of an Air Quality Action plan by determining the

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Harrogate Borough Council improvements in air quality needed and allowing a targeted approach to improving local air quality through measures to be identified by the action plan.

The main findings of the report were:

The extents of the AQMA‟s are accurate and we do not need to increase or reduce the area. A 15% reduction in NOx emissions are required to meet the emission limit in Knaresborough and Ripon. Heavy Duty Vehicles make up 2.7% of vehicles in the Ripon Air Quality Management Area. Heavy Duty Vehicles make up 3.6% of vehicles in the Knaresborough Air Quality Management Area. Heavy Duty Vehicles account for around 40% of road traffic emissions in Ripon and 46% in Knaresborough.

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2 New Monitoring Data 2.1 Summary of Monitoring Undertaken

2.1.1 Automatic Monitoring Sites

Harrogate Borough Council has not undertaken any automatic monitoring since January 2007.

2.1.2 Non-Automatic Monitoring Sites

Non-automatic monitoring conducted in the 2011 calendar year consisted of 56 nitrogen dioxide diffusion tubes in 50 locations. The monitoring focussed on areas that are thought to be at potential risk of exceeding the Annual Mean Objective because of traffic volume, narrow congested streets and junctions. Additional monitoring has been undertaken at urban background locations.

Location maps of each passive diffusion tube monitoring location are shown in Appendix A.

Table 3 Details of Non-Automatic Monitoring Sites Relevant Exposure? Distance Does this (Y/N with to kerb of location distance nearest represent (m) to road worst- Pollutants In relevant (N/A if not case Site Name Site Type OS Grid Ref Monitored AQMA? exposure) applicable) exposure? H 1 Roadside X 428594 Nitrogen N Y (0m) 1.5m Y 5 Otley Road Y 458666 dioxide Killinghall H 2 Roadside X 431044 Nitrogen Y Y (0m) 1m N 24 Low Y 471039 dioxide Skellgate, Ripon H 3 Roadside X 431071 Nitrogen Y Y (0m) 1m Y 8a Heath‟s Y 471085 dioxide Court, Ripon H 4/H 5 Roadside X 431087 Nitrogen Y Y (0m) 1m Y 5 Low Duplicate Y 471100 dioxide Skellgate, Ripon H 6 Roadside X 431189 Nitrogen N Y (0m) 3m N 27 Water Y 471146 dioxide Skellgate, Ripon H 7 Roadside X 431110 Nitrogen Y Y (0m) 1.5m N 1 Low Y 471124 dioxide Skellgate, Ripon H 8 Roadside X 431155 Nitrogen Y Y (0m) 1m Y 24 High Y 471216 dioxide Skellgate, Ripon H 9 Roadside X 431135 Nitrogen Y Y (0m) 1m Y 9 High Y 471186 dioxide Skellgate, Ripon H 10 Roadside X 431146 Nitrogen Y Y (0m) 1m Y 3a Westgate, Y 471258 dioxide Ripon

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Relevant Exposure? Distance Does this (Y/N with to kerb of location distance nearest represent (m) to road worst- Pollutants In relevant (N/A if not case Site Name Site Type OS Grid Ref Monitored AQMA? exposure) applicable) exposure? H 12 Roadside X 434706 Nitrogen N Y (0m) 5m N Vale Court, Y 457380 dioxide Bond End, Knares. H 13 Roadside X 434716 Nitrogen Y Y (0m) 1 m N 21 Bond End, Y 457369 dioxide Knares. H 14 Roadside X 434759 Nitrogen Y Y (0m) 1 m Y 9 Bond End, Y 457375 dioxide Knares. H 15/ H 59/ H Roadside X 434804 Nitrogen Y Y (0m) 2 m N 60 Y 457358 dioxide 117 High St. Knares. H 16 Roadside X 434763 Nitrogen Y Y (0m) 2 m N 10 Bond End, Y 457388 dioxide Knares. H 17 Roadside X 434725 Nitrogen Y Y (0m) 1.5 m N 16-18 Bond Y 457405 dioxide End, Knares. H 18 Roadside X 435040 Nitrogen N Y (0m) 1.5 m Y 46 High St. Y 457082 dioxide Knares. H 19 Roadside X 435012 Nitrogen N Y (0m) 1 m N 35 High St. Y 457084 dioxide Knares. H 20 Roadside X 435133 Nitrogen N Y (0m) 2 m N 22 High St. Y 457009 dioxide Knares. H 21 Roadside X 435158 Nitrogen N Y (0m) 1.5 m N 10 High St. Y 456992 dioxide Knares. H 22 Roadside X 435224 Nitrogen N N 2 m Y 14 York Pl. Y 456913 dioxide Knares. H 23 Roadside X 432904 Nitrogen N Y (0m) 3 m N 32 High St. Y 455940 dioxide Harrogate H 24 Roadside X 432477 Nitrogen N Y (0m) 2 m N st Woodlands Y 454805 dioxide 1 floor only Pub, Hookstone Dr. facade H 25 Roadside X 430063 Nitrogen N Y (0m) 2m N Wagamama, Y 455354 dioxide Parliament St, facade H 26 Roadside X 432494 Nitrogen N Y (0m) 1 m Y Woodlands Y 454808 dioxide 1st floor only Pub, Wetherby Rd. facade H 27/H 44 Roadside X 441851 Nitrogen N Y (0m) 15 m Y The Old Police Duplicate Y 453686 dioxide House, nr Walshford H 28 Urban X 429313 Nitrogen N Y (0m) 5m Y 77 Harlow background Y 453820 dioxide Crescent, Harrogate H 29 Roadside X 429538 Nitrogen N N 2 m Y Little Wonder, Y 456893 dioxide Ripon Road, Harrogate, HG1 2BY H 33 Roadside X 430224 Nitrogen N Y (0m) 2 m Y 207 Skipton Y 456727 dioxide Road,

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Harrogate Borough Council

Relevant Exposure? Distance Does this (Y/N with to kerb of location distance nearest represent (m) to road worst- Pollutants In relevant (N/A if not case Site Name Site Type OS Grid Ref Monitored AQMA? exposure) applicable) exposure? Harrogate, HG1 3EX H34 Roadside X 432525 Nitrogen N Y (3m) 1.5 m N Woodlands Y 454792 dioxide Pub Lamppost, Wetherby Rd. H 35 Roadside X 430513 Nitrogen N Y (5m) 2 m N 208 Kings Y 456467 dioxide Road, Harrogate, HG1 5JG H 36 Roadside X 430925 Nitrogen N Y (0m) 1.5m N 8-10 Y 455804 dioxide Westmoreland Street, Harrogate, HG1 5AT H 37 Roadside X 430573 Nitrogen N Y (0m) 8 m N 87 Skipton Y 456436 dioxide Road, Harrogate H 38 Roadside X 430647 Nitrogen N Y (0m) 3 m Y 59 Skipton Y 456324 dioxide Road, Harrogate, HG1 4LF H 39 Roadside X 430951 Nitrogen N N 2 m Y 6 Devonshire Y 455870 dioxide Place, Harrogate, HG1 4AA H 40 Roadside X 430935 Nitrogen N Y (0m) 1.5 m Y Music Shop, Y 455826 dioxide Westmoreland Street, Harrogate HG1 5AZ H 41 Roadside X 430361 Nitrogen N Y (10m) 1 m Y Entrance to Y 455501 dioxide Harrogate Bus Station, Station Parade, Harrogate H 42 Kerbside X 430367 Nitrogen N Y (2m) 0.1 m Y Adjacent to Y 455339 dioxide Taxi Rank, Station Parade, Harrogate H 43 Roadside X 430397 Nitrogen N Y (1m) 0.5 m Y 1 Station Sq. Y 455194 dioxide Harrogate HG1 1TB H 45 Roadside X 430991 Nitrogen N Y (0m) 2 m N 15 Devons Pl Y 455828 dioxide Harrogate HG1 4NN H 44/H 27 Roadside X 441851 Nitrogen N Y (0m) 15 m Y The Old Police Duplicate Y 453686 dioxide House, nr Walshford H 46 Roadside X 43053 Nitrogen N Y (0m) 5 m Y 93 Skipton Rd, Y 456499 dioxide Hgte, HG1 4LJ H 47 Urban X 430800 Nitrogen N Y (0m) 30 m N

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Harrogate Borough Council

Relevant Exposure? Distance Does this (Y/N with to kerb of location distance nearest represent (m) to road worst- Pollutants In relevant (N/A if not case Site Name Site Type OS Grid Ref Monitored AQMA? exposure) applicable) exposure? 43 Woodfield Background Y 456572 dioxide Road, Hgte, HG1 4LN H49 Roadside X434623 Nitrogen N Y (0m) 1 m Y 29 Bond End Y457314 dioxide Knares H50 Roadside X434578 Nitrogen N Y (0m) 1.5 m Y 55 Bond end Y457260 dioxide Knares H51 Roadside X434796 Nitrogen Y Y (0m) 1 m Y Royal Oak Y457393 dioxide Knares H52 Roadside X434835 Nitrogen Y Y (0m) 2 m Y High Street Y457329 dioxide Knares H53 Roadside X435253 Nitrogen N N 2.5 m Y Royal Tannery Y456893 dioxide York Pl Knares H54 Roadside X431075 Nitrogen Y Y (0m) 1.3 m Y 30 Low Y471077 dioxide Skellgate Ripon H55 Roadside X431102 Nitrogen Y N 1.3 m Y Turks Head Y471101 dioxide Low Skellgate Ripon H56 Roadside X431151 Nitrogen N Y (0m) 3 m Y Crown Court Y471119 dioxide Ripon H57 Roadside X431193 Nitrogen N Y (0m) 3 m Y 6.6a Y471132 dioxide Waterskellgate Ripon H58 Roadside X431242 Nitrogen N Y (0m) 1.6 m Y 17 Y471135 dioxide Waterskellgate Ripon

2.1.3 Details of Quality Assurance/Quality Control (QA/QC)

Monitoring of nitrogen dioxide by way of passive diffusion tubes has been carried out in the Harrogate district since 1993. Over the years more monitoring sites have been added in order to gain a better understanding of air quality within the district. By December 2009 diffusion tube monitoring was being undertaken in 11 general areas, covering 52 sites, with two tubes forming part of the national nitrogen dioxide survey network.

The council‟s nitrogen dioxide diffusion tubes are supplied and analysed by Kirklees Metropolitan District Council‟s (MDC), Environment and Transportation Service, Scientific Services in Huddersfield.

Details of the QA/QC process and bias adjustment factor used throughout this report are shown in Appendix B.

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Harrogate Borough Council

2.2 Comparison of Monitoring Results with AQ Objectives

2.2.1 Nitrogen Dioxide

Automatic Monitoring Data

Harrogate Borough Council has not undertaken any automatic monitoring since January 2007.

Diffusion Tube Monitoring Data

A summary of nitrogen dioxide diffusion tube data is shown below in Tables 2.2 -2.8. The full dataset (monthly mean values) are at Appendix D.

The results of diffusion tube monitoring are discussed below in detail. Conclusions are drawn from them on whether progress towards Detailed Assessment is required. Please note all sites are roadside sites and have not been distance corrected.

2.2.1.1 Ripon Central Survey

Data capture is above 90% for all but one site, H2 Low Skellgate as such the results are considered to be an accurate reflection of nitrogen dioxide concentrations in the area. There are three locations within the Ripon survey which breach the Air Quality Objective (AQO) of 40µg/m3; all of these locations are within the current Air Quality Management Area (AQMA). There is one location which is close to breaching the AQO which is tube H10 Westgate, this location is not within the current AQMA.

All locations, bar two, have seen an increase in the annual mean concentration of Nitrogen Dioxide. These increases do not currently affect the extent of the Declared Air Quality Management Area.

We are currently undertaking public consultation for the Air Quality Action Plan, the conclusion for the Ripon Central Survey is to carry on with the Air Quality Action Plan and to carry on monitoring on Westgate, Ripon. We would hope that any measures implemented as part of the current AQMA would also have a positive impact on this area.

Table 4. Results of Nitrogen Dioxide Diffusion Tubes - Ripon Central Survey Data AQ Capture for Obj Within full calendar Level Annual Mean Site ID. Location AQMA year % (µg/m³) Concentrations (µg/m³) 2011 2010 2009 2008

H2 Low Skellgate N 83 40 27.7 25.12 25.9 30.3

H3 Low Skellgate Y 92 40 46.3 43.36 46.9 50.6 H4/5 Duplicate Low Skellgate (5A) Y 100 40 45.02 44.00 50.6 52.2

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Harrogate Borough Council

H6 Water Skellgate (26) N 100 40 26.22 25.29 29.7 30.7

H7 Low/Water Skellgate Y 100 40 31.9 28.60 33.4 41.1

H8 High Skellgate Y 92 40 43.98 41.60 43.0 43.5

H9 High Skellgate Y 100 40 34.58 34.81 39.2 37.2

H10 Westgate Y 100 40 39.65 33.56 41.0 39.5

H54 Low Skellgate (30) Y 100 40 33.26 29.39 Low Skellgate H55 (Turks Head) Y 100 40 33.68 29.83 Water Skellgate H56 (Crown Ct) N 100 40 31.64 25.96 Water Skellgate H57 (6/6a) N 100 40 34.63 33.39

H58 Water Skellgate (17) N 100 40 28.91 29.84 * Bias adjustment factor for 2011 = 0.75; 2010 = 0.78; 2009 = 0.85; 2008 = 0.8

The graphs of the annual mean nitrogen dioxide concentrations for the Ripon central sites are shown for each of the past four years at Figure 2.4

Air Quality Objective 40µg/m³

Figure 2.4 Trends in Annual Mean Nitrogen Dioxide Concentrations measured at Diffusion Tube Monitoring Sites

2.2.1.2 Knaresborough Central Survey Data capture is at 100% for all sites except H15 which achieved 83%, and H21, which had 67%, this tube will be relocated. Two further tubes have been added

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Harrogate Borough Council alongside H15 (H59, H60), but results were collected for only 7 months so have not been included.

There is one location which has breached the 40µg/m3 limit; this is tube H22 at York Place, Knaresborough. However this tube was found to be on a commercial property. Further monitoring will take place at this location to establish if an exceedence is likely at residential properties.

Most locations have seen an increase in the annual mean concentration of Nitrogen Dioxide. These increases do not currently affect the extent of the Declared Air Quality Management Area.

We are currently undertaking public consultation for the Air Quality Action Plan, the conclusion for the Knaresborough Survey is to carry on with the Air Quality Action Plan and to carry out additional monitoring at York place, we expect that any measures implemented as part of the Air Quality Action Plan for the current AQMA would also have a positive impact in this area and along Knaresborough High Street.

Table 5. Results of Nitrogen Dioxide Diffusion Tubes - Knaresborough Central Survey Data Capture for full AQ Obj Within calendar Level Annual Mean Concentrations Site ID. Location AQMA year % (µg/m³) (µg/m³) 2011 2010 2009 2008

H12 VC, Bond End N 100 40 30.32 31.61 32.6 37.3

H13 Bond End (21) Y 100 40 46.95 39.83

H14 Bond End (11) Y 100 40 54.07 43.61 53.6 55.6 H15/59/60 Triplicate Bond End (117) Y 83 40 39.59 34.42 38.7 42.2

H16 Bond End (HHJ) Y 100 40 34.99 29.28 36.6 38.5

H17 Bond End (22) Y 100 40 32.44 28.86 33.2 36.2 High Street (Dry H18 Cleaners) N 100 40 26.69 29.91 30.5 34.4 High Street (Gift H19 Shop) N 100 40 32.41 26.81 29.9 35.3 High Street (Music H20 Shop) N 100 40 34.24 31.73 35.5 36.1

H21 High Street (Barbers) N 67 40 30.89 34.49 38.5 33.4

H22 York Place (14) N 100 40 41.26 37.01 38.9 41.0

H49 Bond End (29) N 100 40 36.07 27.82

H50 Bond End (55) N 100 40 31.10 33.13 Bond End (The H51 Royal Oak) Y 100 40 40.92 44.17

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Harrogate Borough Council

H52 High Street (120) Y 100 40 34.04 33.00 York Place (The H53 Royal Tannery) N 100 40 35.34 31.51 * Bias adjustment factor for 2011 = 0.75; 2010 = 0.78; 2009 = 0.85; 2008 = 0.8

The graphs of the annual mean nitrogen dioxide concentrations for the Knaresborough sites are shown for each of the past four years at Figure 2.5

Air Quality Objective 40µg/m³

Figure 2.5 Trends in Annual Mean Nitrogen Dioxide Concentrations measured at Diffusion Tube Monitoring Sites

2.2.1.3 Wetherby Road/Hookstone Drive Junction Harrogate Survey

Data capture is 100% for all sites in the survey. One of the three locations in the survey is breaching the 40µg/m3 objective for Nitrogen Dioxide, this tube is situated at the 1st Floor level, where the residential receptors are located. A Detailed Assessment was previously carried out for this location in 2009, the main conclusion from this assessment was to relocate the diffusion tubes to the 1st floor level. Further work will now take place with a view to declaring an Air Quality Management Area in this location.

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Harrogate Borough Council

Table 6. Results of Nitrogen Dioxide Diffusion Tubes – Wetherby Road/Hookstone Chase Junction Harrogate Survey Data Capture for full AQ Obj Within calendar Level Annual Mean Concentrations Site ID. Location AQMA year % (µg/m³) (µg/m³) 2011 2010 2009 2008 Hookstone Drive H24 (Pub) N 100 40 30.85 32.02 29.9 38.2 Wetherby Road H26 (Pub) N 100 40 43.00 39.18 36.9 55.6 Wetherby Road H34 (Pub/Lamppost) N 100 40 32.23 35.77 31.8 37.5 * Bias adjustment factor for 2011 = 0.75; 2010 = 0.78; 2009 = 0.85; 2008 = 0.8

The graphs of the annual mean nitrogen dioxide concentrations for the Wetherby Road/Hookstone Drive Junction are shown for each of the past four years at Figure 2.6. The graphs show that after a large decrease in concentrations in 2009, after the diffusion tubes were moved to the first floor level, concentrations have risen again to the point that tube H26 is now breaching the 40µg/m3 limit.

Air Quality Objective 40µg/m³

Figure 2.6 Trends in Annual Mean Nitrogen Dioxide Concentrations measured at Diffusion Tube Monitoring Sites

2.2.1.4 General District Survey

The data of the diffusion tube monitoring for the remainder of the district (ie not targeted around recognised “hotspots” in connection with the possible declaration of an AQMA) are shown in Table 7.

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Harrogate Borough Council

Table 7. Results of Nitrogen Dioxide Diffusion Tubes – General District Survey Data Capture for full AQ Obj Within calendar Level Annual Mean Concentrations Site ID. Location AQMA year % (µg/m³) (µg/m³) 2011 2010 2009 2008

H1 Killinghall N 100 40 27.43 22.36 27.1 31.7 Kn Rd (Level H23 Crossing) N 100 40 22.84 21.49 24.6 27.6 Parliament St

H25 (Wagamama) N 58 40 19.41 17.39 H27/44 Duplicate Old Police House N 100 40 36.76 33.22 35.4 35.6 77 Harlow H28 Crescent N 100 40 12.25 10.74 14.1 14.3 Skipton Rd (Little H29 Wonder) N 100 40 35.05 32.83 34.7 36.1

H33 Skipton Rd (207) N 100 40 29.74 27.04 31.8 35.6 Kings/Sk Rd H35 Junction N 75 40 24.02 24.61 28.1 31.9 Westmoreland St H36 (8-10) N 100 40 30.19 25.65

H37 Skipton Rd (Bingo) N 100 40 33.01 32.26 33.7 35.5

H38 Skipton Rd (59) N 100 40 36.95 31.94 34.4 40.2 Devonshire Place H39 (6) N 92 40 33.24 34.98 34.5 42.2 Westmoreland St H40 (Music Shop) N 100 40 32.59 31.77 32.5 37.5 Station Parade H41 (Into Bus Station) N 100 60 32.20 28.95 29.9 35.9 Station Parade (Opposite Railway H42 Station) N 100 60 52.24 40.97 48.0 58.9 Station Parade H43 (Edisons) N 100 40 24.33 24.88 25.6 23.7 Devonshire Place H45 (15) N 100 40 37.73 38.48 34.6 39.9

H46 Skipton Rd (93) N 100 40 29.04 26.02 29.8 31.8

H47 Woodfield Rd (45) N 100 40 16.18 13.21 16.3 17.2 * Bias adjustment factor for 2011 = 0.75; 2010 = 0.78; 2009 = 0.85; 2008 = 0.8

Data capture is over 90% for all bar two sites, H25; which was removed part way through the survey year, and H35 which achieved data capture of 75%. All annual means, except for the two mentioned above are considered to be valid results from which conclusions can be drawn.

Most of the locations are representative of public exposure, being located on the facades of residential receptors, and are compared to the nitrogen dioxide Annual Mean Objective. Location reference H23 is intended to approximate residential

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Harrogate Borough Council exposure to standing traffic on High Street, Starbeck caused by the Starbeck level crossing, but is not representative of relevant exposure.

Location references H41 and H42 are places where members of the public may spend an hour or more, and so are compared against the short-term nitrogen dioxide objective level. Research undertaken on behalf of DEFRA and the Devolved Administration suggested that local authorities could reliably base decisions on likely exceedences of the 1-hour objective for nitrogen dioxide alongside busy streets using an annual mean of 60 g/m3 and above. This concentration has been adopted for the assessment criteria at these sites. Both sites have an annual mean nitrogen dioxide concentration lower than 60µg/m3; however there has been an increase in concentrations in comparison with last year‟s results.

Location references H28 and H47 are urban background locations, which had reported annual mean nitrogen dioxide concentrations of 12.25 g/m3 and 16.18 g/m3 respectively. These figures how an increase on last year‟s results, this appears to the pattern for the whole survey, with a few exceptions. The trend in the annual mean nitrogen dioxide concentration at the two background sites between 2000 and 2011 is shown in Figure 2.8.

Air Quality Objective 40µg/m³

Figure 2.7 Trends in Annual Mean Nitrogen Dioxide Concentrations measured at Diffusion Tube Monitoring Sites

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Harrogate Borough Council

Air Quality Objective 40µg/m³

H47 Woodfield Road H28 77 Harlow Crescent

Figure 2.8 Trends in Annual Mean Nitrogen Dioxide Concentrations measured at Urban Background Sites

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Harrogate Borough Council

2.2.2 PM10

Harrogate Borough Council has not undertaken any monitoring of PM10 since the beginning of 2007.

2.2.3 Sulphur Dioxide

Harrogate Borough Council has not undertaken any monitoring of Sulphur Dioxide since the beginning of 2007.

2.2.4 Benzene

Harrogate Borough Council has not undertaken any monitoring of Benzene since the beginning of 2007.

2.2.5 Summary of Compliance with AQS Objectives

Harrogate Borough Council has measured concentrations of NO2 above the annual mean objective at relevant locations outside of the AQMA‟s, and will need to proceed to a Detailed Assessment, for Wetherby Road/Hookstone Drive.

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3 Road Traffic Sources 3.1 Narrow Congested Streets with Residential Properties Close to the Kerb

Concentrations are often higher where traffic is slow moving, with stop/start driving, and where buildings on either side reduce dispersion. Typical locations will be congested street with traffic that is frequently stopping and starting due to pedestrian crossings, parked vehicles etc, and a daily traffic flow (AADT) of around 5,000 vehicles per day or more.

The following locations in the district have been considered in previous rounds of review and assessment:

High Skellgate, Ripon Low Skellgate, Ripon High Street, Knaresborough Kings Road Skipton Road Station Parade

Passive diffusion tube monitoring continues to be conducted at these locations, the results of which are reported in Sections 2.2.1.1 and 2.2.1.2. Air Quality Management Areas were declared in Ripon and Knaresborough in November 2010.

The following roads have been considered previously, however none of them meet all the criteria:

Cheltenham Crescent Otley Road Leeds Road Cold Bath Road

Harrogate Borough Council 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

TG.09 identifies street locations where individuals may regularly spend 1-hour or more, for example streets with many shops and streets with outdoor cafes and bars as locations where there is a potential exceedence of the short-term nitrogen dioxide objective.

In the previous round of review and assessment three locations have been identified:

Station Parade, Harrogate High Street, Knaresborough Market Square, Ripon

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Two of these, Station Parade, Harrogate and High Street, Knaresborough are discussed elsewhere in the report (Section 2.2.1.4) as passive diffusion tube monitoring continues at these locations. Monitoring at Market Square, Ripon ceased in 2007 as no potential exceedence of the short-term nitrogen dioxide objective had been identified in this location.

No new areas meeting these criteria have been identified during the screening process.

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

3.3 Roads with a High Flow of Buses and/or HGVs.

TG.09 states that there may be a potential exceedence of the nitrogen dioxide and PM10 air quality objectives at some street locations 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. It defines an unusually high proportion as greater than 20% heavy duty vehicles.

No such roads have been identified in the Harrogate district.

Harrogate Borough Council confirms that there are no new/newly identified roads with high flows of buses/HDVs.

3.4 Junctions

TG.09 states that concentrations are usually higher close to junctions, due to the combined impact of traffic emissions on two roads, and to the higher emissions due to stop start driving. Such locations need to be assessed against both the nitrogen dioxide and PM10 air quality objectives. Only busy junctions need to be considered, where a busy junction is defined by TG.09 as one with more than 10,000 vehicles per day, it is also only necessary to consider junctions with relevant exposure within 10 metres of the kerb.

The previous Updating and Screening Assessment identified two busy junctions, and exceedences at the Woodlands Public House and at the Bond End junction. There is now an Air Quality Management Area at Bond End, Knaresborough, and the latest round of monitoring has identified an exceedence of the annual mean at first floor level at Woodlands Public House.

No other busy junctions have been identified.

Harrogate Borough Council confirms that there are no new/newly identified busy junctions/busy roads.

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

Since the previous round of review and assessment the A1 improvements have almost been completed. The route of the motorway has changed very little between Dishforth and the edge of the district

Harrogate Borough Council has assessed new/proposed roads meeting the criteria in Section A.5 of Box 5.3 in TG(09), and concluded that it will not be necessary to proceed to a Detailed Assessment.

3.6 Roads with Significantly Changed Traffic Flows

Harrogate Borough Council confirms that there are no new/newly identified roads with significantly changed traffic flows.

3.7 Bus and Coach Stations

There is a risk of the annual mean and 1-hour nitrogen dioxide objectives and the annual mean and 24-hour PM10 objectives being breached near to bus and coach stations where there is relevant exposure nearby, including residential properties, and the number of movements of buses at the bus station is greater than 2500 per day.

Information obtained from Harrogate and District travel in 2009, is shown in Table 3.2. The number of bus movements at all these bus stations is well below the level at which there may be a risk of exceeding the nitrogen dioxide and PM10 air quality objectives, and having discussed current numbers with Harrogate and District travel it is considered that the timetable has not changed much in the intervening years.

This conclusion is supported by monitoring evidence obtained from the passive diffusion tube located at the entrance to Harrogate Bus Station, which recorded an annual mean concentration of nitrogen dioxide in 2011 of 32.2 g/m3, indicating that neither of the nitrogen dioxide objectives are likely to be exceeded at Harrogate Bus Station.

Table 8. Maximum number of daily bus movements at the busiest three bus stations in the Harrogate District (2009 figures)

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Maximum Number of Bus Monday to Friday Movements

Harrogate 1038

Knaresborough 305

Ripon 99

Maximum Number of Bus Saturday Movements

Harrogate 1015

Knaresborough 266

Ripon 97

Maximum Number of Bus Sunday Movements

Harrogate 360

Knaresborough 104

Ripon 40

Harrogate Borough Council confirms that there are no relevant bus stations in the Local Authority area.

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4 Other Transport Sources

4.1 Airports

Harrogate Borough Council confirms that there are no airports in the Local Authority area.

4.2 Railways (Diesel and Steam Trains)

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 nitrogen dioxide concentrations close to the track. These two potentially significant sources are considered separately in the sections below. Relevant exposure does not include people occupationally exposed to these sources.

4.2.1 Stationary Trains

To the south of the district runs the Harrogate railway line from York to Leeds. The line is used for passenger trains and has regular stops at seven local stations in the district. The trains operated by Northern Rail on the line are Diesel Multiple Units (DMUs).

Previous rounds of review and assessment have identified one location, Knaresborough railway station in which there were 12 occasions per day where a train was likely to be stationary for greater than 15 minutes. Observation of passenger movements at the station determined that there was no relevant exposure and as such no further action was required. Since this time Northern Rail have implemented an “Eco-Driving” policy whereby the locomotive engines are switched off when stationary for any length of time, including when stopped at Knaresborough railway station.

In the intervening years the train timetable has changed very little and the latest version of the timetable shows 10 locations per day where a train was likely to be stationary for greater than 15 minutes and as such it is not considered necessary to proceed further.

Harrogate Borough Council 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.

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4.2.2 Moving Trains

Harrogate Borough Council 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)

Harrogate Borough Council confirms that there are no ports or shipping that meet the specified criteria within the Local Authority area.

LAQM USA 2012 38 Harrogate Borough Council

5 Industrial Sources 5.1 Industrial Installations

Industrial sources, although unlikely to make a significant local contribution to annual mean concentrations, could be significant in terms of the short-term air quality objectives.

Many industrial activities are controlled by the Pollution Prevention and Control regime, and are required to obtain and comply with a permit that puts controls on the emissions to air from the installation, and is issued under the Environmental Permitting Regulations. Such activities, regulated by the Environment Agency (larger polluters) and Harrogate Borough Council as the local authority (smaller polluters) are listed in Appendix E. Local authorities also have controls over smaller industrial and commercial sources, largely through the Clean Air Act, with its associated control of stack heights. As a result of these controls, there are relatively few sources that may be relevant under the Local Air Quality Management (LAQM) regime. Many of these sources have been addressed during previous rounds of Review and Assessment. TG.09 therefore recommends that the focus should be on new installations and those with significantly changed emissions.

Industrial sources have been broken into four sections: Industrial installations; Major fuel (petrol) storage depots; Petrol stations; and Poultry farms.

5.1.1 New or Proposed Installations for which an Air Quality Assessment has been Carried Out

TG.09 recommends that only proposed sources which planning approval has been granted should be considered. At the time of writing there is an application on hand with North Yorkshire County Council for a Waste Recovery Park at Allerton Park Quarry. If planning permission for this installation is granted then the associated air quality assessment should be included in the next review and assessment.

Harrogate Borough Council 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

A screening process similar to that in the previous section has been carried out for existing installations where emissions have increased substantially or new relevant exposure has been introduced.

LAQM USA 2012 39 Harrogate Borough Council

Harrogate Borough Council 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

The installations, which have been recently permitted by Harrogate Borough Council under the Environmental Permitting Regulations regime are considered to be unlikely to give rise to a potential exceedence of any of the air quality objectives.

Harrogate Borough Council 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

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

5.3 Petrol Stations

Harrogate Borough Council confirms that there are no petrol stations meeting the specified criteria.

5.4 Poultry Farms

A small number of local authorities have identified potential exceedences of the PM10 objective associated with emissions from poultry farms (defined as chickens (laying hens and broilers), turkeys, ducks and guinea fowl).

Any farms in excess of 40,000 birds are required to have an Environmental Permit issued by the Environment Agency. Previously the following installations have been found not to need a Detailed Assessment; Ouseburn Farm Oaklands Farm Ltd Treble Sykes Farm Sike Lane

LAQM USA 2012 40 Harrogate Borough Council

Two further locations have been identified as having Environmental Permits for poultry farms, however these do not meet the thresholds, so do not require a Detailed Assessment. These farms are; Sandy Bank Farm Grange Farm

Harrogate Borough Council 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

TG(09) states that biomass burning can lead to an increase in PM10 emissions, due to the process of combustion. Aerosol formation from volatile materials distilled from the wood is also an issue. Compared to conventional gas-burning, burning biomass can also result in an increase in the overall NOx emissions due to the fuel-derived portion that is not present in gas combustion.

Previous rounds of review and assessment had considered plant at Harrogate District Hospital and Denton Hall estate, near Ilkley. The 2009 Updating and Screening Assessment identified the need to proceed to a Detailed Assessment for the biomass plant at Denton Hall, however appliance specific data was submitted, which showed a Detailed Assessment was not required.

No further biomass plants have been permitted since that time.

Harrogate Borough Council has assessed the biomass combustion plant, and concluded that it will not be necessary to proceed to a Detailed Assessment.

6.2 Biomass Combustion – Combined Impacts

TG(09) considers that there is the potential for many small biomass combustion installations (including domestic solid-fuel burning), whilst individually acceptable, in combination could lead to unacceptably high PM10 concentrations, especially in locations where PM10 concentrations are close to or above the objectives.

There are no known locations in the district where PM10 concentrations are near to or above the objectives set out, combined with this there is little information regarding the installation of biomass combustion appliances in domestic dwellings is available.

Harrogate Borough Council has assessed the biomass combustion plant, and concluded that it will not be necessary to proceed to a Detailed Assessment.

6.3 Domestic Solid-Fuel Burning

Previous rounds of review and assessment have concluded that there was no risk of exceedence of the objective for Sulphur Dioxide due to domestic solid fuel burning. Since the previous round of assessment, there has been no significant change in the

LAQM USA 2012 42 Harrogate Borough Council district with regard to solid fuel use. Analysis of complaints has shown the majority of complaints to be from the urban areas of Harrogate Knaresborough and Ripon.

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

LAQM USA 2012 43 Harrogate Borough Council

7 Fugitive or Uncontrolled Sources

Dust emissions from a number of uncontrolled and fugitive sources can give rise to elevated PM10 concentrations.

These sources include, but are not limited to: Quarrying and mineral extractions sites; Landfill sites; Coal and material stockyards, or materials handling; Major construction works; Waste Management sites.

Short lived construction sites will not normally need to be considered for the purpose of review and assessment.

Previous rounds of review and assessment have identified and assessed all activity quarries and landfill sites in the district, with the exception of Asenby Quarry, which operates a landfill site. The Environmental Permit for the landfill site contains conditions for dust prevention on site and a review of nuisance complaints has not revealed problems.

The following waste management sites have also been identified and considered: Ripon Recycling Ltd Lusher, Victor - Harrogate Vehicle Recycle Yorwaste Ltd - Claro Road Waste Transfer Station Balfour Beatty Living Places Ltd - Stump Cross Depot Biffa Waste Services Ltd Dobson, Paul – Greystones Farm Manton Addyman, Russel - A1 Skip Hire

A review of nuisance complaints about dust has not revealed any problems associated with any specific facilities.

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

LAQM USA 2012 44 Harrogate Borough Council

8 Conclusions and Proposed Actions

8.1 Conclusions from New Monitoring Data

The new monitoring data for 2011 has identified two exceedences of the annual mean objective for Nitrogen Dioxide outside of the current AQMA‟s. The first location is at York Place, Knaresborough; this has since been identified as being a commercial property. In order to establish whether there is the potential for exceedences at residential properties further diffusion tubes will be added in this location. The second location is at the Woodlands Pub, Wetherby Road/Hookstone Road junction, a Detailed Assessment for this location, was carried out in 2009 and identified the need for monitoring to take place at the first floor level, this monitoring has now identified an exceedence of the annual mean objective, further work should now take place with the aim of Declaring an Air Quality Management area. However we are aware that planned works are to be carried out at this location, therefore a request is to be sent to Defra to postpone this work, as the changes may affect the concentrations found.

The monitoring data from the locations within the current Air Quality Management Area have shown that the extent of the Air Quality Management Areas is still current. 8.2 Conclusions from Assessment of Sources

The assessment of likely impacts of local development including road transport, other transport, industrial installations, commercial and domestic sources and fugitive or uncontrolled sources has not identified any potential exceedences of any of the air quality objectives. 8.3 Proposed Actions

The updating and screening assessment has identified the need to proceed to a Detailed Assessment for Nitrogen Dioxide due to an exceedence of the annual mean objective of 40µg/m3 at the first floor level of the Woodlands Pub at the Wetherby Road/Hookstone Chase Junction, however a Detailed Assessment was previously carried out, so should proceed straight to a Declaration. However, we will be contacting Defra with a view to postponing this work, until works are carried out by North Yorkshire County Council.

Additional monitoring will need to be carried out at York Place, Knaresborough in order to establish whether there is likely to be an exceedence of the annual mean objective for Nitrogen Dioxide at residential receptors.

The report has found no evidence to suggest that the extents of the current AQMA‟s should be increased or decreased.

The following actions will be carried out:

LAQM USA 2012 45 Harrogate Borough Council

A letter will be sent to Defra to request that the Declaration of an Air Quality Management Area is postponed at the Woodlands pub, Wetherby Road/Hookstone Road junction. Extra diffusion tubes will be added to York Place, Knaresborough to establish if an exceedence of the Air Quality Objective is likely at residential properties.

LAQM USA 2012 46 Harrogate Borough Council

9 References

Local Air Quality Management, Technical Guidance LAQM.TG(09). Department for Environment, Food and Rural Affairs, February 2009.

Local Air Quality Management, Policy Guidance LAQM.PG(09). Department for Environment, Food and Rural Affairs, February 2009.

2011 Further Assessment Harrogate Borough Council, April 2012.

2011 Air Quality Progress Report Harrogate Borough Council, April 2011. http://www.harrogate.gov.uk/harrogate-917

2010 Air Quality Progress Report Harrogate Borough Council, June 2010. http://www.harrogate.gov.uk/harrogate-917

2009 Detailed Assessment of Air Quality Harrogate Borough Council, Air Quality Consultants, February 2009. http://www.harrogate.gov.uk/harrogate-917

2008 Interim Annual Progress Report Harrogate Borough Council. June 2008 http://www.harrogate.gov.uk/harrogate-917

2007 Annual Progress Report Harrogate Borough Council. July 2007 http://www.harrogate.gov.uk/harrogate-917

2006 Updating and Screening Assessment Report, September 2006 http://www.harrogate.gov.uk/harrogate-917

2003 Private Sector Stock Condition Survey, Final Draft. Harrogate Borough Council, June 2004

LAQM USA 2012 47

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HIGH Bellevue Terrace 44 Ripon & District 18 E 22 11 HIGH 18 11 N 32 " Fisher'sFisher's 11 32.8m 32 E 32.8m 30 E Church 30 Church 19 55 17 22 2020 5a5a 29 22 6 KIRKGATE 17 6 23 to 26 27 6 DUCK HILL 27 KIRKGATE E 44 22

14 B 6265 5 5 Mill House PHPH MALLARD CL 11 14 HallHall 58 B 6265 11 E E 15 16 57 15 DUCK HILL 10 Ripon City Club 10 SOMERSET ROW WATER SKELLGATE 1717 SOMERSET ROW 6a 7 to 1 to 8 55 7 E SKELLBANK WATER SKELLGATE 6 6a 12 Mill House 11a 7 11a B 6265 44 18 1 to 8 11 SKELLGARTHS 56 18 1 to 4 B 6265 YMCA E 11 1 11 1 Crown Court ! Heath's Court 1 to 4 23 21 2 1919 1515 2 Ripon City Club 29.7m29.7m 1 to 8 YMCA 7 3 7 3 3737 1 1 St Margaret's

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10 9 19 42 L " Montpellier 1 Bank 21 HARROGATE " 10 23 2 25 Market Place FB Arthington L 8 7 2 Bank 19 L L CAMBRIDGE ROAD 9 TCB 27 to 31 " 3 Bank 8 E118.3m " L L 7 6 33 17 TCPs E 12 3 35 L L 5 7 37 25 4 CR L 4 L 5 ! E E Posts 116.7m 15 Victoria Gardens L L 26 2 MONTPELLIER SQUARE Bank 3 7 to 10 ! E Parade E Harrogate L CAMBRIDGE CRESCENT Prospect MONTPELLIER HILL 13 L L L E " Sub 1 13 L 15 Sta 6 E E 16 9 EAST 14 Buildings E 7 L L Prospect L L E " Montpellier Parade E 13 8 115.2m Crescent E 13a 11 9 21 The Exchange E 10 STATION PARADE Petergate L War L L 19 " 2 Memorial " L E " Parade " " 2 TCB's E 1 15 L E 1 L 48 Cross James Street 123.2m 46 40 EAST PARADE 3836a 34 Cinema E 28 to 32 47 L L L L E LOW 26 20 18 10 to 14 STATION SQUARE L E 18 to 21 JAMES STREET 3 49 6 to 2 ! ! " 47 Jubilee E E MONTPELLIER HILL " 45 E Monument E E ! TCBs PC 31 27 120.4m Roof " Car Park E ! " The Stray LB L " " Shelter Bank 21 17 L L Bank 23 13 11 Two Hundred Acre Hotel 1 Bank 9 7 55 L 3 1a John Street 1 Copthall Bridge House PRINCES STREET 3 23 L 8 11 E E L Warehouse 9 19 21 8a L E ESPLANADE 3 17 E 1 L E PC 1 1 L L PROSPECT PLACE 10 59 11 124.4m FB E L 7 to 11 Baptist Church PH STATION BRIDGE L L E " 15 L Esplanade Court 3 L E E 43 L 16 E E ! E E 2a 7 L E 2 5 6 L E Hotel 4 4 17 3 E Hotel 4 2b 2 L E E L 8 6 1 E 12 10 6 L L L 2 L ! 63 14 4 Harrogate L 16 122.2mALBERT STREET E 11 20 18 E E 26 22 1 to 7 L L 28 ! L L ! El Sub Sta Sloane Cottage PH 9 " ! 10 Victoria House L ! E 1 E ! ! E VICTORIA ROAD E 2 3 ! L 1 E 1311 11a L L ! E L " E " L E E L E L L E C ! Harrogate Town Centre, Harrogate. ! ! L L E L E L L " E " L L L E L E L L L " L " " L " ! " L L L E ! ! ! E E ! ! L L " E E L E L " L ! L E L L E " L L " L " E ! L ! E ! E L L L L E L E ! ! E E E L L L E ! E L E E L L L L E E E L L E L E E L L L E E Syke Dike L L L ! L L ! E L L L E ! E L E E L L L E ! L L L ! L L ! E E L E " E L L L L L E E L L L L L " E L L L L L L E E L L L L L L L L E E L E E ! E ! L L L ! " L ! ! L L ! E E ! L L L E Water E ! ! E L ! L L L " L L L L L L E E E L L L L L ! L L The Old Police House E ! L L L E L E L L L L E L L L ! L E " ! L L L E E L L L " L L ! " L E 2744 L L E E L L L L L L E E L L L L L E L E E L L L E ! L L E L L E L L L E E ! E L E " L E ! L LE L L L A 168 # L ! L L " L E " L E L ! L L L L E ! L ! E L L E E L L " E L L L L E E !

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Appendix B: QA:QC Data

The details of the nitrogen dioxide diffusion tube preparation and analysis and QA/QC information are as follows:

Preparation Method

The laboratory prepares the tubes by dosing with Triethalanamine/Acetone 50/50 on to the grids before assembly. The exposed tubes are desorbed using distilled water and the extract analysed using 0.14% N.E.D.A., 2% Sulphanilamide, 5% Orthophosphoric Acid combined reagent and a DR2800 spectrophotometer.

The Laboratory follows the procedures set out in the Harmonisation Practical Guidance.

Bias-adjustment factor and co-location study

Harrogate Borough Council used to conduct a co-location survey of nitrogen dioxide diffusion tubes since, allowing the concentrations of nitrogen dioxide obtained from the diffusion tubes to be compared with the concentrations of nitrogen dioxide measured by the continuous chemiluminescent analyser housed in the council‟s air quality monitoring station (AQMS). Automatic monitoring ceased in 2007, so an alternative means of obtaining a co-location was required.

For this reason since July 2007 triplicate tubes have been sent to Hambleton District Council forming an in-house co-location study. However, in the past the results of this study have been poor and, so the national bias adjustment factor is currently preferred.

Using this spreadsheet, (as reproduced in Appendix D) the bias adjustment factor based on other local authorities that use the same tube supplier and preparation method (Kirklees MBC Scientific Services) for 2011 is 0.75.

LAQM USA 2012 55 Harrogate Borough Council

The bias adjustment factor used for the monitoring throughout the report is 0.75

Results of laboratory precision and WASP scheme

Kirklees MDC Scientific Services take part in the Workplace Analysis Scheme for Proficiency (WASP) inter comparison scheme. The laboratory performance in the latest round of testing (Jan 2010 – Dec 2011) it was ranked as satisfactory for 56.25% of the time period.

LAQM USA 2012 56 Harrogate Borough Council

Appendix C: Industrial Activities – Regulated Under The Environmental Permitting Regulations 2010 at 1 April 2012

E (i) Part A1 Activities IPPC Environment Agency

Name Installation Name Grid Ref Type Sector Effective Permit Oakland Farms Limited Oaklands Farms Ltd SE51845608 Poultry Farming FP3030UT Food and Primary Diets Limited Melmerby Feed Mill SE33897566 Feedmill Drink KP3439MK Mr Philip, Mr John and Mrs Ann Cornforth Scalibar Farm SE37355440 Pigs Farming YP3733UP Mr Steven R Blaken and Mr Geoffrey Blaken Monkton Mains SE04310465 Pigs Farming AP3733UP Waste Recycling Group (Yorkshire) Limited Allerton Park Landfill SE41205973 Landfill Waste VP3536XS Yorkshire Water Services Non-haz Limited Harrogate North SE30275817 treatment Waste AP3237UJ Yorkshire Water Services Harrogate South Non-haz Limited STW SE37055257 treatment Waste AP3736UK Webster Farming (Farnham) Limited Sandy Bank Farm SE35656000 Farming NP3536MG Wilkin White Syke Farm SE50805413 Pigs Farming NP3230UY Hook2sisters Ltd Sike Lane SE39507560 Poultry Farming CP3533UJ Hook2sisters Ltd Ouseburn SE43696276 Poultry Farming LP3039GR Coldstone Unit and A Alton one Unit SE33507970 Pigs Farming NG3437MG Thorpe Road Feed I'Anson Bros Ltd Mill SE22428029 Feedmill Food & Drink GP3038US Whitwell Grange K & J.A. Hornshaw Farm SE43306380 Pigs Farming NP3730UG Deighton Grange Pig Mr E & Mr M Alton Unit SE40865167 Pigs Farming NP3530UL J.C Lister Farms Ltd Ellenthorpe Lodge SE41186737 Pigs Farming CP3730UD Lingham Lane Joseph E. Swiers Ltd Piggeries SE38807290 Pigs Farming LP3637MT

E (i) Part A1 Activities WML Environment Agency

Name Installation Name Grid Ref Type Sector Effective Permit Manton's Egg Waste SE2237856736 Manton Products Management DB3739RK West Harrogate May Gurney Household Waste Household Waste Waste Limited Recycling Centre SE2536255740 Recycling Centre Management ZP3797EQ K A Anderson ( K A Anderson ( Vehicle dismantler & Metal Recyclers) Metal Recyclers) metal merchant Waste Ltd Ltd SE31757036 Management EP3696LU Vehicle dismantler/transfer Harrogate Vehicle station Waste Lusher Victor Recycle SE2893557834 Management QP3298VQ Ripon Car and Commercial Waste Ward D Spares SE3187270500 Vehicle dismantler Management AP3791LW Household, Commercial and Claro Waste Industrial Waste Waste Yorwaste Limited Transfer Station SE3130956398 Transfer Station Management FB3135AT Ripon Recycling Ripon Recycling WEEE treatment Waste Ltd Ltd SE30705127 facility Management FP3494EE W. Dale And Son SE3364670344 Waste ZP3796EY

LAQM USA 2012 57 Harrogate Borough Council

Management Hanson Quarry Products Europe Allerton Park Waste Ltd Quarry SE4059360091 Management XP3595VX Hanson Quarry Products Europe Waste Ltd Ure Valley Quarry SE2963476913 Management RP3696EF Inert and excavation waste transfer Waste Balfour Beatty Boroughbridge station with Management Living Places Ltd Depot SE3965165081 treatment Licence AB3732RE Biffa Waste Ripley Transfer Waste Services Ltd Station SE2856559762 Transfer Station Management SP3090ZT Vehicle Waste Addyman's Plant SE31605880 Dismantler/Metal Management And Skip Hire Merchant Licence Addyman Carl CP3992LB Waste Management Addyman Russel A1 Skip Hire SE2615059950 Licence FP3791SU Household, Commercial and Industrial Waste Waste Transfer Station with Management Dobson Paul Greystones Farm Treatment Licence NP3398EU Waste Management Bradley David Treacle Jug Farm SE3660660211 Licence GB3336AM Household, Commercial and Industrial Waste Waste Transfer Station with Management C W Skips Ltd C W Skips Ltd SE4470055906 Treatment Licence ZP3997EL

E (iii) Part A2 Activities LA-IPPC Harrogate Borough Council

Installation Sector Guidance Grid First Permit Operator Address Note Reference Issued Ref

SG6 Secretary of Flaxby Moor, Flaxby, State's Guidance for the A2 RR Donnelley Knaresborough, HG5 SE 401 056 20/09/2000 PPC/A2/1/V1 Surface Treatment Using 0XJ Organic Solvents Sector

E (iv) Part B Activities LAPPC Harrogate Borough Council

Process Grid Operator Installation Address First Issued Permit Ref Guidance Note Reference

Harrogate Stonefall Cemetery Borough Council 5/2 (04) Crematoria SE 334 544 26/08/1992 PPC/01/V2 Wetherby Road (Crematorium) Harrogate HG3 1DE

3/01 (04) Blending, The Gravel Works Milby Lafarge Packing, Boroughbridge Y05 SE 397 673 04/03/1992 PPC/06/V2 Aggregates Ltd Loading, Unloading 9BN and Use of Bulk Cement

3/01 (04) Blending, Allerton Park Plant, Allerton Park Packing, Hanson Pit SE 406 598 14/03/1993 PPC/09 Loading, Unloading Aggregates Allerton Park Allerton and Use Mauleverer HG5 OSD of Bulk Cement Lightwater Potgate Quarry, North Stainley, 3/08 (04) Quarry SE 278 762 18/03/1997 PPC/12/V1 Quarries Limited Ripon, HG4 3JN Processes

LAQM USA 2012 58 Harrogate Borough Council

3/08 (04) Quarry Processes Hanson Coldstones Quarry, Greenhow 3/15a (04) SE 124 641 15/03/1993 PPC/13/ V1 Aggregates Hill, Pateley Bridge, HG4 5JQ Roadstone Coating Processes

3/01 (04) Blending, Packing, Newlay Wath, Near Ripon, North Loading, Unloading SE 148 678 16/03/1993 PPC/14/V1 Concrete Yorkshire, HG4 5EP and Use of Bulk Cement 6/23 (04) Coating of Econ Boroughbridge Road, Metal SE 323 705 21/01/1994 PPC/20/V1 Engineering Ltd Ripon, HG4 1UE and Plastic 6/26 (05) Animal W E Jameson & Foxholme Lane Mill, feed SE 221 811 07/09/1993 PPC/27 Son Ltd Masham, HG4 4ER Compounding 6/26 (05) Animal A-One Feeds North Hill Road, RAF Dishforth, feed SE 390 710 27/09/1993 PPC/29/V2 Ltd Y07 3DJ Compounding 3/16 (04) Mobile Peacock Mobile Plant Crushing n/a 09/10/1995 PPC/39/V2 Brothers and Screening Trelleborg Halfpenny Lane, Knaresborough, 6/29 (04) Di- Industries UK HG5 isocyanate SE 357 585 13/08/1996 PPC/43 Limited 0PB Processes 6/29 (04) Di- Belzona Claro Road, Harrogate, HG1 4AY isocyanate SE 313 565 27/09/1996 PPC/45 Polymerics Ltd Processes 3/01 (04) Blending, Ure Bank Top, Ripon, North Packing, Ebor Concretes Yorkshire Loading, Unloading SE 317 725 11/02/1997 PPC/46 Ltd HG4 1JE and Use of Bulk Cement 3/01 (04) Blending, Packing, Brown and Ripon City Quarry, Boroughbridge Loading, Unloading SE 331 697 04/03/1998 PPC/50/V1 Potter Ltd Road, Ripon, HG4 1UG and Use of Bulk Cement 3/01 (04) Blending, Packing, Lafarge Marfield Quarry, Masham, Ripon, Loading, Unloading SE 218 822 11/01/1999 PPC/53/V1 Aggregates Ltd HG4 4NH and Use of Bulk Cement 3/01 (04) Blending, Ure Valley Quarry, North Stainley, Packing, Hanson Ripon, Loading, Unloading SE 302 702 21/10/1998 PPC/54 Aggregates HG4 3HT and Use of Bulk Cement 6/29 (04) Di- Farnham Lane, Farnham, HG5 Trèves UK Ltd isocyanate SE 366 560 08/02/2000 PPC/56 9JR Processes 3/16 (04) Mobile Peacock Mobile Plant Crushing n/a 06/03/2008 PPC/92 Brothers and Screening Grange Farm, Milby, 6/26 (05) Animal Vitrition Boroughbridge, North Yorkshire, feed SE 402 679 19/02/2008 PPC/93 YO51 9HQ compounding 6/2 (04) John Boddy Riverside Sawmills, Valuation Manufacture of SE 392 669 06/03/2008 PPC/94 Timber Ltd Lane, Boroughbridge, YO51 9LJ Timber and Wood- based Products 6/31 (04) Powder Coating Including Craven & Co. Manse Lane, Knaresborough, Sherardizing and SE 362 563 26/11/2008 PPC/95 Ltd HG5 8ET Vitreous Enamelling Dry Nationwide 6/34b (06) Sykes Grove, Harrogate, HG1 Crash Repairs Respraying of SE 297 567 22/09/1992 PPC/VRF/01 2DB Ltd Road Vehicles Knaresborough 6/34b (06) Body Repairs Manse Lane, Knaresborough, PPC/VRF/03 Respraying of SE 363 565 05/10/1993 (Harper HG5 8LF /V1 Road Vehicles Holdings) Nidd Vale 6/34b (06) SE 314 535 07/03/1996 PPC/VRF/04

LAQM USA 2012 59 Harrogate Borough Council

Motors Hornbeam Park, Hookstone Respraying of Ltd Road, Harrogate, HG2 8QT Road Vehicles 6/34b (06) Ripon Farm Dallamires Lane, Ripon, HG4 Respraying of SE 318 404 12/03/1997 PPC/VRF/05 Services Ltd 1TS Road Vehicles 1/14 (06) Unloading Total Garage, Leeds Road, of Petrol Pace Petroleum Pannal, into Storage at SE 310 566 24/08/1998 PPC/PFS/1 GB LTD HG3 1EP Petrol Stations 1/14 (06) Unloading Wm Morrison Hookstone Park, Hookstone of Petrol PPC/PFS/2 Supermarkets Chase, into Storage at SE 332 563 20/12/1999 /V1 Plc Ltd Harrogate, HG2 7LD Petrol Stations 1/14 (06) Unloading Manse Services, 29 Wetherby of Petrol Co-operative Road into Storage at SE 360 567 20/12/1999 PPC/PFS/3 Trading Group Knaresborough, HG5 8LH Petrol Stations 1/14 (06) Unloading of Petrol Nidderdale Central Garages, Pateley Bridge, into Storage at SE 155 656 20/12/1999 PPC/PFS/5 Motors Ltd Harrogate, HG3 5HQ Petrol Stations 1/14 (06) Unloading of Petrol Fina Filling Leeds Road Pannal into Storage at SE 309 517 29/06/1999 PPC/PFS/6 Station HG3 1ER Petrol Stations 1/14 (06) Unloading Wm Morrison of Petrol Harrogate Road, Ripon, HG4 2SB Supermarkets into Storage at SE 312 694 20/12/1998 PPC/PFS/8/V1

Plc Ltd Petrol Stations 1/14 (06) Unloading Quarry Moor Service Station, of Petrol Co-operative Harrogate Road, Ripon, HG4 into Storage at SE 309 695 20/12/1998 PPC/PFS/9 Trading Group 2SD Petrol Stations 1/14 (06) Unloading of Petrol Woodlands Stop 135 Wetherby Road, Harrogate, into Storage at SE 325 548 20/12/1998 PPC/PFS/10/V2 and Shop HG2 7AA Petrol Stations 1/14 (06) Unloading Skipbridge Petrol Filling Station, of Petrol Co-operative Green Hammerton, Nr York, into Storage at SE 478 561 20/12/1998 PPC/PFS/11 Trading Group Y026 8EQ Petrol Stations 1/14 (06) Unloading of Petrol Wensleydale 10 Leyburn Road, Masham, HG4 into Storage at SE 226 814 20/12/1999 PPC/PFS/13 Garage 4ER Petrol Stations 1/14 (06) Unloading Wm Morrison Stump Cross Garage, Wetherby of Petrol Supermarkets Road, into Storage at SE 400 660 26/01/2000 PPC/PFS/14/V1 Plc Ltd Boroughbridge, Y05 9HS Petrol Stations 1/14 (06) Unloading Sainsbury‟s of Petrol J Sainsbury Plc, Wetherby Road, Supermarkets into Storage at SE 329 545 23/12/1998 PPC/PFS/15/V1 Harrogate, HG2 8QZ Ltd Petrol Stations 1/14 (06) Unloading of Petrol Co-operative Oakdale Service Station, Ripon into Storage at SE 298 564 31/12/1998 PPC/PFS/16 Trading Group Road, Harrogate, HG1 2BS Petrol Stations

LAQM USA 2012 60 Harrogate Borough Council

E (iii) Part B Activities (cont.)

Process Guidance Grid Operator Installation Address First Issued Permit Ref Note Reference

Knaresborough Filling 1/14 (06) Unloading of Co-operative Station, 18 Boroughbridge Petrol SE 359 575 28/06/1999 PPC/PFS/17 Group Road, Knaresborough HG5 into Storage at Petrol 0NG Stations 1/14 (06) Unloading of Jennyfield Ripon Road, Harrogate, Petrol SE 297 565 24/06/1999 PPC/PFS/18 Service Station HG1 2BS into Storage at Petrol Stations 1/14 (06) Unloading of BP Broadway 30 North Street, Ripon, HG3 Petrol SE 305 719 27/12/1998 PPC/PFS/21 Ripon Limited 1HJ into Storage at Petrol Stations 1/14 (06) Unloading of Dragon Service Station, Esso Service Petrol Skipton Road, SE 304 568 20/12/1999 PPC/PFS/22/V1 Station into Storage at Petrol Harrogate, HG1 4PS Stations 1/14 (06) Unloading of Tesco Harrogate Express, Tesco Stores Petrol Knaresborough Road, SE 326 558 31/12/1998 PPC/PFS/23 Ltd into Storage at Petrol Harrogate, HG2 7LY Stations 1/14 (06) Unloading of Riffa Service Harrogate Road, Pool In Petrol SE 247 462 14/12/1999 PPC/PFS/24 Station Wharfedale, LS21 2PS into Storage at Petrol Stations 1/14 (06) Unloading of Rontec Watford 9A/13 Dragon Road, Petrol SE 304 557 31/12/1999 PPC/PFS/25 Plc Harrogate, HG1 1DB into Storage at Petrol Stations 1/14 (06) Unloading of A1(M) Motorway Junction Moto Hospitality Petrol 46, Kirk Deighton, SE 415 501 15/07/2008 PPC/PFS/26 Limited into Storage at Petrol Wetherby, LS22 5GT Stations Wm.Morrison Wetherby Road, Supermarkets Boroughbridge, Y051 6/46 (06) Dry Cleaning SE 396 653 05/06/2005 PPC/DC/01 Plc 9HS Johnson 100 Knaresborough, Road 6/46 (06) Dry Cleaning SE 324 555 03/01/2007 PPC/DC/02/V2 Cleaners UK Ltd Harrogate, HG2 7NN Johnson 28 Leeds Road, Harrogate, 6/46 (06) Dry Cleaning SE 303 543 03/01/2007 PPC/DC/03 Cleaners UK Ltd HG2 8AA 46 High Street, Johnson Knaresborough, HG5 6/46 (06) Dry Cleaning SE 351 750 03/01/2007 PPC/DC/04/V1 Cleaners UK Ltd 0EQ Johnson 8/10 Beulah Street, 6/46 (06) Dry Cleaning SE 304 554 03/01/2007 PPC/DC/05/V1 Cleaners UK Ltd Harrogate, HG1 1QQ Johnson 19 Market Place, Ripon, 6/46 (06) Dry Cleaning SE 312 713 03/01/2007 PPC/DC/06/V1 Cleaners UK Ltd HG4 1BW 34 Cold Bath Road, Harrogate Harrogate, North Yorkshire, 6/46 (06) Dry Cleaning SE 297 550 23/07/2007 PPC/DC/07 Cleaners & Intrim HG2 0NA Classiclean of 26a East Parade, 6/46 (06) Dry Cleaning SE 306 556 03/01/2007 PPC/DC/08 Harrogate Harrogate, HG1 5LT 40 Cold Bath Road, Prontaclean Harrogate, North Yorkshire, 6/46 (06) Dry Cleaning SE 296 548 07/11/2007 PPC/DC/09 HG2 0NX 1/1 (04) Waste Oil and Simon J V Spa Garage, Horsefair, Recovered Oil Burners less SE 395 694 18/12/1992 PPC/WB/1 Charlton Boroughbridge, YO51 9HR than 0.4MW 1/1 (04) Waste Oil and Pratt Brothers Ripon Road, Harrogate, Recovered Oil Burners less SE 290 570 17/12/1992 PPC/WB/2/V1 (Harrogate) Ltd HG1 3HL than 0.4MW Fair Deal Motors, Manse 1/1 (04) Waste Oil and Fair Deal Motors Lane, Knaresborough, HG5, Recovered Oil Burners less SE 363 566 17/12/1992 PPC/WB/4 8LF than 0.4MW 1/1 (04) Waste Oil and 2 Newnham Street, Apex Garage Recovered Oil Burners less SE 318 555 14/01/1993 PPC/WB/7 Harrogate, HG2 7SS than 0.4MW Harrogate Auto Claro House, Claro Road, 1/1 (04) Waste Oil and SE 313 563 13/01/1998 PPC/WB/10

LAQM USA 2012 61 Harrogate Borough Council

Electric Harrogate Recovered Oil Burners less North Yorkshire, HG1 4AU than 0.4MW 1/1 (04) Waste Oil and Hi Q Ripon Tyre Boroughbridge Road Recovered Oil Burners less SE 326 705 24/08/2004 PPC/WB/13/V1 Services Ltd Ripon HG4 1UE than 0.4MW 1/1 (04) Waste Oil and Pannal Motor Station Buildings, Station PPC/WB/14 Recovered Oil Burners less SE 306 516 27/11/2004 Centre Road, Pannal, HG3 1JN than 0.4MW 1/1 (04) Waste Oil and Intune Car 33 Camwal Road, Recovered Oil Burners less SE 327 562 17/01/2005 PPC/WB/15 Services Harrogate, HG1 4PT than 0.4MW 1/1 (04) Waste Oil and Moorlands Otley Road, Harrogate, Recovered Oil Burners less SE 278 571 17/01/2005 PPC/WB/16 Garage HG3 2AS, Unit 1 than 0.4MW 1/1 (04) Waste Oil and Houseman Auto 29 Camwal Road, Recovered Oil Burners less SE 327 561 17/01/2005 PPC/WB/17/V1 Repair Centre Harrogate, HG1 4PT than 0.4MW 1/1 (04) Waste Oil and Hammerton Cars York Road, Green Recovered Oil Burners less SE 477 560 17/01/2005 PPC/WB/18 Limited Hammerton, Y026 8EQ than 0.4MW 1/1 (04) Waste Oil and 32 Camwal Road, MDR Motors Recovered Oil Burners less SE 328 561 17/01/2005 PPC/WB19/V1 Harrogate, HG1 4PT than 0.4MW 1/1 (04) Waste Oil and Ripon Farm Dallamires Lane, Ripon, Recovered Oil Burners less SE 319 704 06/04/2005 PPC/WB/22 Services Limited HG4 1TT than 0.4MW 1/1 (04) Waste Oil and Ure Bank Top, Ripon, HG4 Powells Of Ripon Recovered Oil Burners less SE 317 724 06/04/2005 PPC/WB/23/V1 1JD than 0.4MW Bellwood House, Minskip 1/1 (04) Waste Oil and Ainsty Timber Road, Boroughbridge, Y051 Recovered Oil Burners less SE 392 656 12/12/2006 PPC/WB/25 Marketing Ltd 9HY than 0.4MW 1/1 (04) Waste Oil and Estate Office, Asenby, Guy Reed Farms Recovered Oil Burners less SE 397 756 01/05/2008 PPC/WB/26 Thirsk, YO7 3QR than 0.4MW Unit 4, 29 Camwal Road, 1/1 (04) Waste Oil and ADP Automotive Starbeck, Harrogate, HG1 Recovered Oil Burners less SE 327 561 01/05/2008 PPC/WB/27 Ltd 4PT than 0.4MW 1/1 (04) Waste Oil and Ripon Road Garage, Ripon Premier Autos Recovered Oil Burners less SE 293 571 02/02/2009 PPC/WB/28 Road, Harrogate, HG1 3HJ than 0.4MW Blackbull Garage, Blackbull 1/1 (04) Waste Oil and Waite R & E Yard, Masham, Ripon, HG4 Recovered Oil Burners less SE 224 809 13/02/2009 PPC/WB/29 4HD than 0.4MW H.W. Baines Industrial 1/1 (04) Waste Oil and Steve Pilmoor Estate, Fishergreen, Ripon, Recovered Oil Burners less SE 319 708 31/03/2009 PPC/WB/30 North Yorkshire, HG4 1NN than 0.4MW Unit 22, Marston Moor 1/1 (04) Waste Oil and Tockwith MOT Business Park, Rudgate, Recovered Oil Burners less SE 548 237 09/12/2011 PPC/WB/34 Tockwith, YO26 7QF than 0.4MW 1/1 (04) Waste Oil and Blythes Garage, Green End, Blythes Garage Recovered Oil Burners less SE 339 767 26/01/2011 PPC/WB/32 Melmerby, HG4 5HL than 0.4MW 1/1 (04) Waste Oil and Lightwater Farm, North Mr D Almack Recovered Oil Burners less SE 287 764 27/10/2011 PPC/WB/33 Stainley, Ripon, HG4 3HT than 0.4MW Grimbald Park, Wetherby 1/1 (04) Waste Oil and Roundwood Road, Knaresborough, HG5 Recovered Oil Burners less SE 364 563 18/05/2010 PPC/WB/31 Garage 8LJ than 0.4MW 3/01 (04) Blending, Pannal Business Park, Packing, Hanson Concrete Building 16, Station Road, Loading, Unloading and SE 306 513 11/08/2011 PPC 98 Pannal, HG3 1JL Use of Bulk Cement 6/2 (04) Manufacture of Green Lane, Melmerby, Duffield Timber Timber and Wood-based SE 334 759 12/04/2010 PPC/97 HG4 5JB Products 3/16 (04) Mobile Crushing Lickley Group Ltd Mobile Plant n/a 12/03/2010 PPC/100 and Screening 3/16 (04) Mobile Crushing Lickley Group Ltd Mobile Plant n/a 28/10/2011 PPC/99 and Screening

LAQM USA 2012 62 Harrogate Borough Council Appendix D: Full Dataset (Monthly Mean Values) of Nitrogen Dioxide Diffusion Tubes Corrected Data Jan- Feb- Mar- Apr- May- Jun- Jul- Aug- Sep- Oct- Nov- Dec- for lab Capture 11 11 11 11 11 11 11 11 11 11 11 11 Average bias % 1. Killinghall, Res 30.97 49.04 40.14 32.84 26.18 24.20 33.80 30.20 44.29 49.27 56.56 21.49 36.58 27.44 100 2. Rip, Low Skellgate, Res (24) 42.87 41.23 TM TM 17.48 27.02 38.30 29.87 36.49 44.19 65.66 26.55 36.97 27.72 83 3. Rip, Low Skellgate, Res (8a) 55.34 68.44 62.98 72.47 TM 61.74 59.92 55.36 56.04 60.88 71.74 54.71 61.78 46.34 92 4. Rip, Low Skellgate, Res (5A) 58.70 60.63 68.97 65.37 43.57 51.02 67.29 52.94 43.64 62.35 43.72 48.17 55.53 41.65 100 5. Rip, Low Skellgate, Res (5A) 70.26 71.09 72.08 64.89 52.44 57.09 62.66 59.09 62.25 65.38 80.72 56.40 64.53 48.40 100 6. Rip, Waterskellgate, Res (26) 42.23 43.60 36.90 30.32 26.42 27.09 35.52 31.92 35.44 36.79 46.07 27.21 34.96 26.22 100 7. Rip, Low Skellgate, Res (1) 63.79 46.45 45.83 39.76 36.34 40.63 39.38 37.25 47.29 37.20 43.84 32.70 42.54 31.90 100 8. Rip, High Skellgate, Res (24) 45.46 65.80 57.58 43.12 52.40 62.25 75.23 61.80 66.44 62.99 tm 52.03 58.65 43.98 92 9. Rip, High Skellgate, Res (9) 44.04 53.38 50.10 52.98 46.66 0.78 58.31 50.43 51.28 43.51 61.60 40.27 46.11 34.58 100 10.Rip, Westgate, Res (3a) 54.35 71.17 63.24 40.73 39.79 38.46 54.73 47.54 49.20 44.90 79.81 50.45 52.86 39.65 100 11. H3 X 45.98 58.30 61.23 42.64 38.54 37.13 44.19 23.13 48.22 65.47 67.62 45.87 48.19 36.14 100 12. Kn, VC, Bond End, Res 34.10 44.82 43.18 40.47 33.37 31.73 49.13 38.13 41.97 42.38 52.53 33.29 40.43 30.32 100 13. Kn, Bond End, Res (21a) 25.79 72.85 72.80 62.86 54.94 46.75 58.04 61.27 62.31 76.50 89.51 67.59 62.60 46.95 100 14. Kn, Bond End, Res (9) 43.10 92.71 75.54 62.53 59.31 62.34 75.50 70.72 83.34 89.21 87.20 63.56 72.09 54.07 100 15. Kn, Bond End, Res (117) 37.58 45.19 TM TM 57.61 48.18 52.46 58.15 59.87 59.10 60.34 49.45 52.79 39.59 83 16. Kn, Bond End, Res (HHJ) 38.24 58.14 54.26 63.43 30.60 32.07 51.50 41.01 39.97 46.80 65.10 38.67 46.65 34.99 100 17. Kn, Bond End, Res (22) 17.55 48.79 49.10 50.99 34.98 32.04 44.92 37.74 48.36 52.06 67.65 34.94 43.26 32.44 100 18. Kn, High Street, Res/1hr (Dry Cleaners) 48.60 24.43 44.17 38.97 28.75 30.37 44.23 37.63 27.95 27.45 56.41 18.15 35.59 26.69 100 19. Kn, High Street, Res/1hr (Gift Shop) 35.04 38.13 46.92 40.73 38.35 40.75 37.53 45.94 48.22 52.65 55.37 38.89 43.21 32.41 100 20. Kn, High Street, Res/1hr (Music Shop) 43.99 54.85 55.16 51.26 33.00 37.28 51.14 37.01 41.94 47.87 61.47 32.85 45.65 34.24 100 21. Kn, High Street, Res (Barbers) 58.02 TM 31.53 48.95 34.49 40.69 66.39 49.46 TM TM TM TM 41.19 30.89 67 22. Kn, York Place, Res (14) 45.72 65.30 58.96 44.06 41.55 40.55 49.97 57.16 63.29 72.20 71.85 49.52 55.01 41.26 100 23. Starbeck, Kn Rd, Res (Level Crossing) 36.14 43.51 38.91 31.87 23.18 23.95 29.12 28.00 33.77 -0.36 49.00 28.30 30.45 22.84 100 24. Harr, Hookstone Chase, Res (Pub) 32.76 44.47 49.40 39.53 32.15 34.50 44.82 44.24 40.19 45.04 51.07 35.50 41.14 30.85 100 25. Harr, Parliament St (Wagamama) 28.70 37.27 25.82 27.34 17.79 18.48 25.80 TM TM TM TM TM 25.89 19.41 58 26. Harr, Wetherby Rd, Res (Pub) 60.60 38.84 63.64 49.76 36.36 53.14 63.54 73.78 65.14 66.43 71.59 45.15 57.33 43.00 100 27. Whalsford, Old Police House. 58.15 49.92 47.58 48.76 49.30 50.29 55.09 48.21 45.39 46.91 42.93 45.79 49.03 36.77 100 28. Harr, 77 Harlow Cresecent, Res, Urban 19.37 24.65 16.84 10.68 12.40 8.48 10.90 11.05 13.17 20.70 34.70 13.08 16.33 12.25 100 29. Harr, Little Wonder, Res. 35.75 56.15 44.04 42.83 40.01 40.49 46.13 45.18 53.95 56.84 68.00 31.47 46.74 35.05 100 33. Harr, Skipton Rd, Res (207) 34.54 53.08 35.51 28.21 38.53 31.07 36.03 36.29 41.05 52.41 54.51 34.59 39.65 29.74 100 34. Harr, Wetherby Rd, (Pub Lamppost) 38.12 58.31 49.40 37.79 31.71 30.32 55.27 42.62 34.56 45.25 53.96 38.35 42.97 32.23 100 35. Harr, Kings/Sk Rd Jun, Res (208) 38.65 45.07 41.18 20.55 32.93 27.66 37.22 27.52 TM TM TM 17.48 32.03 24.02 75

LAQM USA 2012 63 Harrogate Borough Council

36. Harr, Westmoreland St, Res (8-10) 45.02 45.65 44.13 38.68 29.83 31.95 38.88 33.87 37.72 48.89 53.31 35.11 40.25 30.19 100 37. Harr, Skipton Rd, Res (87/Bingo) 38.22 49.75 46.48 38.74 40.20 32.53 41.14 41.05 36.38 49.30 51.15 63.28 44.02 33.01 100 38. Harr, Skipton Rd, Res (59) 66.57 52.16 50.17 37.05 45.68 38.08 43.79 41.26 52.76 55.82 55.67 52.22 49.27 36.95 100 39. Harr, Devonshire Place, Res (6) 52.25 56.17 54.93 47.35 41.17 38.41 51.73 45.98 46.29 53.27 TM TM 44.32 33.24 92 40. Harr, Westmoreland St, Res (Music Shop) 45.15 57.17 49.71 39.40 39.80 31.47 30.24 41.97 42.70 45.63 57.91 40.25 43.45 32.59 100 41. Harr, In to Bus Station, 1hr 44.19 38.30 37.49 32.76 37.90 33.83 40.56 41.18 47.89 55.21 62.26 43.57 42.93 32.20 100 42. Harr, Opposite Railway St, 1 hr 85.62 70.52 72.19 64.13 65.42 61.64 69.93 59.83 71.97 70.93 71.65 71.96 69.65 52.24 100 43. Harr, Edisons, Station Parade, Res 22.98 29.85 36.48 22.60 25.96 27.57 36.78 30.63 30.95 41.46 52.71 31.26 32.44 24.33 100 44. Walshford, Residential, Old Police House. 49.09 41.99 49.76 42.94 52.39 47.02 66.26 52.18 51.90 41.57 45.71 47.04 48.99 36.74 100 45. Harr, Devonshire Pl res. (15) 68.58 61.49 60.39 55.07 29.04 37.55 55.76 45.16 41.10 48.22 67.76 33.61 50.31 37.73 100 46. Harr, Skipton Rd res. (93) 41.42 44.99 37.59 31.57 35.84 28.70 33.37 31.54 36.24 46.31 57.11 39.90 38.71 29.04 100 47. Harr, Woodfield Road (43) 29.48 30.14 23.93 12.22 16.43 11.90 13.45 17.44 20.77 28.15 35.62 19.30 21.57 16.18 100 49. Kn, Bond End (29) 42.35 62.88 51.38 45.58 38.87 35.75 44.07 40.44 56.07 52.89 72.88 34.01 48.10 36.07 100 50. Kn, Bond End (55) 32.99 31.38 45.99 48.27 46.66 41.16 50.90 43.48 46.75 50.13 58.76 1.16 41.47 31.10 100 51. Kn, The Royal Oak 71.85 67.12 52.25 56.04 40.64 44.33 62.30 46.93 46.91 62.57 79.09 24.69 54.56 40.92 100 52. Kn, High St (120) 45.00 59.82 52.12 56.03 28.39 31.49 53.07 39.08 44.84 44.91 61.92 27.93 45.38 34.04 100 53. Kn, The Royal Tannery, York Pl 43.21 44.40 50.46 38.23 43.84 44.43 49.13 53.91 51.04 49.36 50.69 46.75 47.12 35.34 100 54. Rip, Low Skellgate (30) 42.83 36.95 50.53 53.16 36.18 37.20 49.29 45.71 45.81 52.85 60.48 21.16 44.35 33.26 100 55. Rip, Turks Head Low Skellgate 37.31 55.18 44.89 45.04 45.29 44.84 43.45 43.87 46.00 45.94 56.77 30.29 44.91 33.68 100 56. Rip, Crown Ct, Waterskellgate 33.95 52.26 52.85 38.42 37.34 35.33 39.91 36.93 43.27 49.14 54.28 32.50 42.18 31.64 100 57. Rip, Waterskellgate (6/6a) 42.01 50.09 40.77 44.32 44.65 36.12 46.87 40.40 59.42 54.49 51.28 43.61 46.17 34.63 100 58. Rip, Waterskellgate (17) 35.84 39.75 23.79 36.33 35.66 32.69 38.22 40.65 44.30 45.22 46.25 43.84 38.55 28.91 100 59. Kn, Bond End, Res (117) 45.99 46.96 54.64 61.13 56.30 62.71 64.29 56.00 42.00 58 60. Kn, Bond End, Res (117) 41.89 57.00 62.30 59.15 64.29 64.39 65.35 59.20 44.40 58

LAQM USA 2012 64