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TRUSTEES VISCOUNT FITZHARRIS 1981 SETTLEMENT, AND
H.H. AND D.E. DREW LIMITED
PLANNING APPLICATION FOR AN EXTENSION TO SAND AND GRAVEL
EXTRACTION AT HURN QUARRY, DORSET FOLLOWED BY FILLING WITH
IMPORTED INERT MATERIALS AND RESTORATION
NON-TECHNICAL SUMMARY (NTS)
MARCH 2015
Wardell Armstrong
Sir Henry Doulton House, Forge Lane, Etruria, Stoke-on-Trent, ST1 5BD, United Kingdom
Telephone: +44 (0)845 111 7777 Facsimile: +44 (0)845 111 8888 www.wardell-armstrong.com
Wardell Armstrong is the trading name of Wardell Armstrong LLP, Registered in England No. OC307138.
Registered office: Sir Henry Doulton House, Forge Lane, Etruria, Stoke-on-Trent, ST1 5BD, United Kingdom
UK Offices: Stoke-on-Trent, Birmingham, Cardiff, Carlisle, Edinburgh, Greater Manchester, London, Newcastle upon Tyne,
Penryn, Sheffield, Truro, West Bromwich. International Offices: Almaty, Moscow
ENERGY AND CLIMATE CHANGE
ENVIRONMENT AND SUSTAINABILITY
INFRASTRUCTURE AND UTILITIES
LAND AND PROPERTY
MINING AND MINERAL PROCESSING
MINERAL ESTATES AND QUARRYING
WASTE RESOURCE MANAGEMENT
DATE ISSUED: MARCH 2015
JOB NUMBER: ST14186
REPORT NUMBER: 004
TRUSTEES VISCOUNT FITZHARRIS 1981 SETTLEMENT, AND
H.H. AND D.E. DREW LIMITED
PLANNING APPLICATION FOR AN EXTENSION TO SAND AND GRAVEL EXTRACTION AT
HURN QUARRY, DORSET FOLLOWED BY FILLING WITH IMPORTED INERT MATERIALS
AND RESTORATION
NON-TECHNICAL SUMMARY (NTS) PLANNING APPLICATION FOR AN EXTENSION TO
SAND AND GRAVEL EXTRACTION AT HURN QUARRY, DORSET FOLLOWED BY FILLING
WITH IMPORTED INERT MATERIALS AND RESTORATION
MARCH 20155
This report has been prepared by Wardell Armstrong LLP with all reasonable skill, care and diligence, within the terms of the Contract
with the Client. The report is confidential to the Client and Wardell Armstrong LLP accepts no responsibility of whatever nature to third
parties to whom this report may be made known.
No part of this document may be reproduced without the prior written approval of Wardell Armstrong LLP.
HURN QUARRY EXTENSION
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CONTENTS
1 INTRODUCTION ............................................................................................................. 1
2 EIA APPROACH AND SCOPE OF ASSESSMENT................................................................. 2
3 SITE LOCATION .............................................................................................................. 5
4 DESCRIPTION OF PROPOSALS ........................................................................................ 6
5 ENVIRONMENTAL IMPACT PREDICTION, EVALUATION AND MITIGATION ...................... 7
DRAWINGS
ST14186-001 Site Location Plan
ST14186-004 Site Setting
ST14186-005 Extraction Phasing
ST14186-008 Restoration Plan
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1 INTRODUCTION
1.1 Purpose of this Non-Technical Summary
1.1.1 This Non-Technical Summary (NTS) presents (in non-technical language) the findings
of an Environmental Impact Assessment (EIA) undertaken in support of a proposed
extension to an existing sand and gravel operation at Hurn Quarry, Bournemouth.
1.1.2 This NTS has been prepared by Wardell Armstrong LLP on behalf of Trustees Viscount
FitzHarris 1981 Settlement. The full Environmental Statement (ES) has been submitted
with the planning application. The ES has been prepared in accordance with the
requirements of the Town and Country Planning (Environmental Impact Assessment)
Regulations 2011 and other relevant guidance.
1.1.3 This NTS provides a brief site description, a discussion of the proposals and then
presents the assessment findings for each technical section of the ES, in non-technical
language. Anyone with interest in exploring specific technical assessment findings can
refer to the main ES.
1.2 Introduction
1.2.1 The site is located to the west of an existing sand and gravel quarry, south of
Bournemouth International Airport, in Dorset.
1.2.2 The site is approximately 17.5ha in size, and currently comprises a number of
agricultural fields used to grow crops, small paddocks, and part of the car park for the
adjacent amusement park.
1.2.3 The existing quarry is nearing the end of its operation, and so the proposals are to
extend the quarry on the land to the west in order to continue operations there.
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2 EIA APPROACH AND SCOPE OF ASSESSMENT
2.1 Introduction
2.1.1 In accordance with the 2011 Regulations a full ES has been prepared in order to
identify, describe and assess the environmental impacts of the proposals.
2.1.2 The scope of the ES was determined in accordance with the Scoping Opinion received
from Dorset County Council. The following topic areas were considered in the ES:
• Landscape and Visual Impact Assessment;
• Ecology;
• Land Use and Soils;
• Hydrogeology and Hydrology;
• Noise and Vibration;
• Air Quality;
• Archaeology and Cultural Heritage;
• Climate Change; and
• Traffic.
2.1.3 In addition, a Site Investigation and Flood Risk Assessment were undertaken.
2.1.4 Due to the size and scale of the proposals it was considered that all environmental
issues would require consideration. As such, no topics were scoped out.
2.2 EIA Approach
Baseline
2.2.1 The baseline for the study, against which impacts have been assessed, has been taken
as the current position of the site as agricultural fields and a section of a car park. It is
in this context that the extension of mineral extraction within the site has been
considered and assessed.
Significance Criteria
2.2.2 The criteria for the assessment of significance has been selected and applied in
accordance with published guidance specific to the individual topic areas covered in
the technical assessments. Such guidance represents the industry standard method
for assessing potential impacts and is consistent with EIA best practice. The published
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guidance used in the undertaking of the assessments is referenced in each technical
chapter. Where published guidance or criteria is not available the chosen method for
assessing impacts and their significance is explained in detail to ensure transparency.
2.2.3 Where significant impacts have been identified, mitigation measures have been
recommended to avoid, reduce or remedy such impacts. These have involved
alterations to the basic design or operation of the development or the introduction of
specific safeguards to ameliorate potential effects. The assessment methodology has
therefore been used to refine the development proposals in an iterative process.
Local Engagement
2.2.4 In addition to Dorset County Council being consulted via the request for scoping, a
letter was sent to the residents of properties located close to the site. The letter
provided summary details of the proposals, directed residents to the location of the
scoping request and consultation page on Dorset County Council’s web site, and
invited comments on the proposals prior to the submission of this application.
Discussions were also held between a local resident and the landscape architect
during a site visit.
2.2.5 A number of responses arising from the letter to residents have been received, mainly
in relation to the distance of the workings from residential properties; and visual,
noise and vibration impacts. Comments from local residents have been considered
within the assessment, in the design of the operations, and in the design of
appropriate mitigation.
Mitigation
2.2.6 The development proposals incorporate measures to avoid, reduce and remedy any
potential adverse environmental impacts, and to enhance the environmental benefits
of the scheme. This has been done by ensuring that potential adverse effects, issues
or constraints are designed out of the scheme as far as practicably possible, with
impacts that cannot be adequately mitigated through site design addressed through
a combination of operational methods and techniques, best working practices, or
specific strategies or action plans.
Residual Impacts
2.2.7 Assessment and mitigation of the key environmental issues have been used to reduce
impacts to the lowest practicable level consistent with the overall objectives. Any
residual impacts (the remaining effects following mitigation) are identified.
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2.3 Consideration of Alternatives
2.3.1 The consideration of alternatives helps to provide a scheme which reduces the
environmental effects of a project.
2.3.2 There are three possible alternatives to the proposed scheme:
• The ‘do nothing’ option
• An alternative location
• An alternative design
2.3.3 The ‘do nothing’ option considers the alternative of not developing the site, and
allowing it to continue in its current land use. This option would eliminate the
potential environmental impacts resulting from the development. However, as
described within the Planning Supporting Statement submitted with this application,
in view of the demonstrated need for mineral and relatively limited harm of the
proposals, it is considered that the ‘do nothing’ alternative can be discounted.
2.3.4 The scope for considering alternative locations is limited by the need for minerals to
be present. It is preferable to consider an extension to the existing quarry rather than
a new quarry, as this will allow the existing infrastructure to be used and prevent a
new site having to be developed. It is not possible to extend to the west due to the
presence of Conservation Area and a Site of Special Scientific Interest. Extension to
the south would have significant impacts on ecology and the landscape through
extensive tree and hedgerow removal. Extension to the north is limited by the
proximity to the airport, and would lead to traffic and access issues. Therefore an
extension to the west is the preferred alternative, as it is easily accessible from the
existing quarry and would result in the least environmental impact.
2.3.5 The proposed scheme has been designed in conjunction with the production of the
ES. As far as possible, potential significant adverse environmental impacts have been
‘designed out’ of the scheme. However, measures have also been incorporated into
the proposals to mitigate any impacts that cannot be adequately addressed through
design. This includes avoiding areas at risk of flooding, and an increase in stand-off
from properties, bund size, change in standard working methods, and additional
planting in order to reduce noise and visual impacts.
2.3.6 The current proposals are therefore considered to be the most suitable alternative in
environmental terms.
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3 DESCRIPTION OF THE SITE
3.1.1 The site is approximately 17.5ha in size is located immediately to the south of
Bournemouth International Airport, within the borough of Christchurch and the
county of Dorset. The relevant planning authority is Dorset County Council.
3.1.2 The majority of the site comprises a number of large agricultural fields used to grow
crops and a number of smaller paddocks, separated by hedgerows. The remainder of
the site, to the east, comprises part of the car park for the adjacent Adventure
Wonderland Amusement Park. There are hedgerows and trees on the northern,
western and eastern site boundaries.
3.1.3 The site is bound by:
• Parley Lane to the north, with Bournemouth Airport beyond;
• Hurn Court Lane and the existing quarry to the east;
• Dales Lane to the south, with agricultural land beyond; and
• The Adventure Wonderland amusement park to the west.
3.1.4 There are a number of properties locate on Dales Lane. Dales House is located
adjacent to the centre of the southern site boundary, and the remaining properties
are located adjacent to the south-western corner of the site at the junction of Dales
Lane and Hurn Court Lane.
3.1.5 See Drawing ST14186-001 for the Site Location Plan and Drawing ST14186-004 for the
Site Setting.
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4 DESCRIPTION OF PROPOSALS
4.1 Introduction
4.1.1 As the existing Hurn Quarry is coming to the end of its operational life, this ES has been
prepared in support of an application to extend mineral operations on to the land to
the west of the existing quarry.
4.1.2 Extraction of minerals within the new site will be split into five phases, each lasting
approximately two years (see Drawing ST14186-005). The direction of phasing
progresses in a clockwise direction, from the south-west of the site to the north-west.
Before mineral extraction takes place in each phase, soils will be stripped and used to
create bunds on the site boundary. These bunds will screen views of the quarry, and
reduce noise levels.
4.1.3 Mineral extracted from the site will be transported to the existing processing plant,
via a new access road to be constructed between the existing quarry and the proposed
extension. The exact position of the new access road will be confirmed with the
highways agency.
4.1.4 Restoration of each phase (via infill) will begin approximately one year after extraction
within that phase has finished. Restoration of each phase will take approximately two
year. The entire site will eventually be restored back to its current use as agricultural
fields, with the car park restored to grassland. This will include the replanting of any
trees and hedgerows removed as part of the extraction operations (see Drawing
ST14186-008).
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5 ENVIRONMENTAL IMPACT PREDICTION, EVALUATION AND MITIGATION
5.1 Introduction
5.1.1 Potential impacts have been identified and evaluated with reference to magnitude
and significance and where required, measures to avoid, reduce, remedy or
compensate any adverse effects have been incorporated into the site design and
working methods.
5.1.2 An overview of each of the environmental assessments is provided below.
5.2 Landscape and Visual Impact Assessment
5.2.1 The site is located on a remnant of an agricultural landscape located along the River
Stour. This area has traditionally been rural in character, however development
surrounding the B3073, including the airport and amusement park, has changed the
perception of the landscape character. Mineral extraction has adversely affected the
landscape, and aircraft and road noise reduce the tranquillity of the area.
5.2.2 The proposals have incorporated mitigation measures to screen the proposals,
including the construction of a bund on the site boundary, the enhancement of
existing vegetation, and additional planting done in advance of proposals. These
measures were taken account of in the assessment.
5.2.3 The proposals will change the land use of the area from agricultural to a mineral
extraction site. However the landscape is already affected by the existing quarry, the
airport, the amusement park and the B3073. Therefore the proposals will have a
moderate adverse effect on the landscape character. These effects will be temporary,
and following restoration there will be a negligible to slight beneficial impact on the
landscape character, due to the additional planting and enhancement of the existing
vegetation.
5.2.4 The key receptors which will experience views of the proposals are the houses, roads
and footpaths located adjacent to the site boundaries. Impacts on views will be
highest when works are being undertaken in the adjacent section of the site. However
following construction of the bund the majority of views will be screened, and impacts
will greatly reduce.
5.3 Ecology
5.3.1 An ecological assessment is required to identify and evaluate the elements that make
up the local ecosystem and consider how the impacts of the development may affect
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these in accordance with NPPF and the CIEEM Guidelines for Ecological Impact
Assessment (2006).
5.3.2 At this stage of the application, a complete detailed evaluation of potential impacts
has not been carried out and further survey for Great Crested Newts and the
subsequent base line data is required in order to do so. Consequently, this assessment
has been unable to fully evaluate the potential impacts in accordance with NPPF and
the CIEEM Guidelines for Ecological Impact Assessment (2006).
5.3.3 The assessment has established that the construction and operation of the proposed
development will not significantly impact upon the habitats and species that are
present within the site.
5.3.4 Mitigation measures have been recommended for the loss of habitats and impacts
upon bats, in order to maintain best practice and to adhere to relevant legislation for
ecological receptors which non-significant effects have been identified.
5.3.5 Further survey effort and subsequent assessment of impacts will enable more detailed
mitigation measures to be included, addressing the remainder of ecological receptors
within the site.
5.3.6 Following completion of the additional ecological survey, assessment of residual and
cumulative impacts can be undertaken.
5.4 Land Use and Soils
5.4.1 Historically the site was used as agricultural fields. More recently, the land in the west
has been used as parking for the Bournemouth Aviation Museum and the amusement
park, however the majority of the site remains in agricultural use. The existing Hurn
Quarry will be restored to agricultural land of similar quality following completion of
extraction operations.
5.4.2 A detailed site survey was undertaken in order to establish the Agricultural Land
Classification (ALC) of the soils across the site. The survey determined that the
majority of the site is Grade 3a (good quality), just over a third is Grade 2 (very good
quality), and a small amount is Grade 3b (moderate quality). There is also a small
amount of non-agricultural land.
5.4.3 The proposed quarry extension would result in a temporary change of use of 13.6ha
of Best and Most Versatile (BMV) and 1.2ha of non-BMV agricultural land. Due to the
temporary change of the land use, and planned restoration back to agricultural land
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of the same quality, the proposals would not result in a significant effect on the
agricultural land.
5.4.4 The impact upon the soil resources can be properly mitigated and minimised through
phased working and use of best practice methods in soil handling, storage and
restoration. It would not result in a significant effect.
5.4.5 Provided that the water runoff from the site is properly managed and appropriate
agricultural drainage is installed following restoration, the impact on drainage on and
off the site would not be significant.
5.5 Hydrogeology and Hydrology
5.5.1 An investigation of the hydrogeological and hydrological conditions of the site and the
surrounding water environment has been undertaken, and an assessment of the
impact the proposals will have upon the surrounding water environment.
5.5.2 A Conceptual Site Model was produced, which identified that groundwater within the
river terrace deposits was the primary water receptor. The River Moors is not a
receptor as the groundwater flow direction is not towards the River Moors. The River
Stour is also not a receptor given the distance between the Site and the river. The desk
study did not identify any other groundwater dependant systems within 2km of the
Site.
5.5.3 It is proposed that the workings are limited to above the water table. During the
winter, when the water table is higher, there will be a reduction in the working depth.
5.5.4 The impact assessment identified that vehicle activities during the operation,
construction and closure phases of the project have the potential to affect
groundwater quality from accidental releases of fuels and oils.
5.5.5 The implementation of best available techniques and appropriate mitigation
measures will reduce the level of the previously identified impacts to low.
5.6 Noise and Vibration
5.6.1 Noise monitoring was undertaken in order to establish baseline noise levels. During
the survey, noise from road traffic, aircraft, birdsong and the amusement park were
established as existing significant noise sources.
5.6.2 Potential noise impacts at existing sensitive receptors were assessed, with noise
predictions carried out using computer modelling software.
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5.6.3 Without mitigation measures vibration is likely to be perceptible whilst operations
take place closest to existing sensitive receptors, resulting in a slight adverse impact.
However the vibration levels will be well below the threshold for any structural
damage to buildings. Appropriate mitigation measures have been recommended to
reduce vibration impacts at existing sensitive receptors.
5.6.4 Without mitigation the noise generated by the extraction operations would have short
term minor to moderate adverse impacts, and long term minor to major adverse
impacts at the sensitive receptors located in the immediate vicinity of the
development.
5.6.5 Following the implementation of appropriate mitigation measures, predicted noise
levels are lower than the noise limits defined in accordance with Planning Practice
Guidance, resulting in a minor adverse impact, which is considered to be acceptable
in the context of the site.
5.7 Dust
5.7.1 A dust assessment has been undertaken to assess the impact of the proposals on
existing dust levels in the vicinity of the site and at identified dust sensitive receptor
locations.
5.7.2 The site is located in a semi-rural setting, with open land and residential properties
surrounding the site to the north, east, west and south. Existing dust sources in the
vicinity of the site include traffic; domestic and aviation fuel burning; and agriculture.
Dust transported from more distant sources will also contribute to the total dust levels
experienced by the site and the surrounding receptors.
5.7.3 Dust emissions from the site have the potential to increase levels in the surrounding
area, both as short-term peaks and over a longer period. Dust could be blown off site
to affect surrounding receptors. The main potential sources of dust at the site are the
stripping, storage and handling of soils; the movement of material; and vehicle traffic.
5.7.4 The proposals have the potential to generate dust, and therefore mitigation measures
will need to be continually implemented to ensure effective control of dust emissions
is maintained. It is assumed that the existing mitigation measures currently
implemented for the existing quarry, as part of the Environmental Management Plan,
will be in place and will continue to operate during the entirety of the proposed
extension.
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5.7.5 The effective implementation of the dust mitigation measures will ensure that dust
generated at the site will have an insignificant effect on nearby sensitive receptors.
5.8 Archaeology and Cultural Heritage
5.8.1 There are no designated heritage assets within the boundary of the site. However
there are seven Grade II Listed Buildings and the Hurn Conservation Area within 1km
of the site.
5.8.2 No designated heritage assets would be physically impacted upon by the proposals.
Two Grade II Listed Buildings, Dales House and Merritown Farmhouse, may experience
an impact to their setting. However this would not exceed an impact of moderate
adverse significance. Visual impacts to the buildings would be mitigated by the
construction of the bund, and the site would be restored to agricultural use upon
completion of extraction. The restoration of the site would also mitigate the loss of
historic hedgerows which would be re-instated.
5.8.3 The assessment indicated a potential for buried remains, in particular remains dated
to the prehistoric period. However, there is no evidence to indicate that potential
remains within the boundary of the site would be of high importance. In order to allow
a suitable mitigation strategy to be put in place, it is anticipated that a programme of
archaeological evaluation would be required to determine the planning application.
5.9 Climate Change
5.9.1 The climate change impacts on the project and the impacts of the project on climate
were assessed.
5.9.2 Climate projections for the UK were assessed in order to establish what changes to
the climate are likely to occur over the lifetime of the project, within Dorset. It is
anticipated that summers are likely to get hotter and drier, and winters are likely to
get wetter. However overall annual average changes in temperature and rainfall are
not expected to be significant. Therefore it is not anticipated that climate change will
impact on conditions or operations at the site.
5.9.3 The main impact a development has on the climate is the generation of greenhouse
gas (GHG) emissions. Generation of GHG emissions within any development is
unavoidable, however within this proposal they will be minimised through the
location and design of the scheme, through the use of energy efficiency measures, and
the restoration of the site. The Flood Risk Assessment also outlines measures that will
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be incorporated within the design of the scheme to ensure that it is not at risk of
flooding.
5.9.4 In conclusion is considered that the proposals are in accordance with local policy on
climate change, as they will be resilient to the impacts of climate change, and will
ensure continued provision of a mineral resource whilst minimising GHG emissions.
5.10 Traffic
5.10.1 The extension area will not be operated at the same time as the existing quarry.
Therefore, the proposals will have a positive impact on Parley Lane as HGV traffic to
and from the quarry will be approximately halved.
5.10.2 The proposals will impact on traffic on Hurn Court Lane as mineral will need to move
from the western side of the lane to the existing quarry site on the eastern side.
Existing traffic on Hurn Court Lane is relatively light and generated by a small number
of residential dwellings and local businesses. There will be a relatively high increase of
traffic on Hurn Court Lane, however the impact would not be significant.
5.10.3 The layout of the crossing point on Hurn Court Lane will need to be agreed with Dorset
County Council and will consider traffic already using this section of the lane in order
to deliver a safe solution, with minimal impact on existing users.
5.11 Cumulative Impacts
5.11.1 No proposed mineral operations in the process of planning have been identified within
the surrounding area. Therefore the proposed extension is not anticipated to result in
cumulative impacts in combination with other developments.
5.11.2 There are no unacceptable impacts on the environment arising from the proposals.
Therefore it is unlikely that any receptor would experience significant cumulative
impacts from the combined effect of two or more sources; or from the impacts
continuing over an extended period of time.
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