Landscape Architecture Ecology Environmental Planning & Assessment Arboriculture
17 Chorley Old Road,
Bolton,
Lancashire
BL1 3AD
Tel: 01204 393 006
Fax: 01204 388 792
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appletons
www.appletons.uk.com @Appletons_LArch
LAND AT BROWNSIDE AND WORSTHORNE, BURNLEY
For
H & F ECCLES & SON
EXTENDED PHASE 1 HABITAT SURVEY
APRIL 2016
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appletons
appletons
17 Chorley Old Road
Bolton
Lancashire
BL1 3AD
Tel: 01204 393006
Email: [email protected]
Web: www.appletons.uk.com
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DOCUMENT CONTROL TITLE: EXTENDED PHASE 1 HABITAT SURVEY PROJECT: LAND AT BROWNSIDE AND WORSTHORNE, BURNLEY JOB NO: 2056 CLIENT: H & F ECCLES AND SON
Document
Status
Description
Rev date
By
Approved
by
Issued
to
Issue date
Comments
DRAFT Extended Phase 1 Habitat Survey
PB LC Martin Birkett 24.06.16
FINAL Extended Phase 1 Habitat Survey
PB LC Martin Birkett 11.07.16
Revisions to Final Document
Rev
Description
Rev date
By
Approved
by
Issued
to
Issue date
Comments
A Extended Phase 1 Habitat Survey
15/09/16
PB LC Amy James –
Indigo Planning 16/09/16
Amended to reflect updated red line boundary
Prepared by: Paula Bateson
Date: 17.05.16
Surveyor: Paula Bateson
Date: 22.04.16
Checked by: Lorna Cruice
Date: 24.06.16
Approved for distribution by: Lorna Cruice
Date: 24.06.16
APPLETONS REF:2056
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NON-TECHNICAL SUMMARY
In April 2016, Appletons was commissioned by H & F Eccles and Son to carry out an initial ecological
appraisal of the site of proposed residential development at land at Brownside and Worsthorne, Burnley. To
fulfil this brief an ecological desk study data search and a Phase 1 Habitat Survey were undertaken.
The ecological desk study identified a number of protected species records within 2 km of the site areas
including bats, badger, great crested newt, bullhead and several bird species. In addition, eleven designated
nature conservation sites and eight district wildlife sites were identified by the desk study, all located over
400 m from the site.
The Phase 1 Habitat Survey was undertaken on 21st April 2016 by Paula Bateson, Project Ecologist. The
survey site comprised two separate areas, referred to as Areas A and B throughout the current report. At
the time of the survey, Area A included the buildings and structures of Butchers Farm, and small sections
of adjacent cattle grazed fields of improved grassland. Area B comprised an open area of improved
grassland and an old field boundary defined by an earth bank, dry ditch and low number of scattered trees
and scrub.
The key potential ecological concerns in relation to the proposed works are the potential presence of nesting
birds and roosting bats. In order to ensure compliance with wildlife legislation and relevant planning policy,
the following recommendations are made:
Hedgerow and scattered trees: Any retained trees and hedgerows should be protected.
Running water: All works should be undertaken in accordance with best practice to ensure that
the watercourse close to Site Area A is not adversely impacted by the proposed works.
Roosting bats: A daytime bat survey should be undertaken on any buildings and trees on site
which may be impacted by the proposed development works.
White-clawed Crayfish and Bullhead: If any disturbance to the stream adjacent to Site Area A is
anticipated, a survey for white-clawed crayfish and bullhead should be undertaken.
Terrestrial mammals including Badger: Any excavations that need to be left overnight should be
covered or fitted with mammal ramps. Any open pipework should be blanked off at the end of each
work day.
Birds: Any vegetation clearance, building demolition or dismantling of dry stone walls should be
undertaken outside of the nesting bird season.
To comply with Chapter 11 of the National Planning Policy Framework (Conserving and Enhancing the
Natural Environment) and Local Planning Policy, the following recommendation is made:
Habitat Loss and Enhancement: Biodiversity enhancement measures should be incorporated into
landscape proposals, which for example could include areas of wildflower grassland, bird and bat
boxes and habitat enhancement of the adjacent stream for water vole.
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CONTENTS:
1.0 Introduction
2.0 Methodologies
3.0 Desk Study
4.0 Phase 1 Habitat Survey
5.0 Ecological Evaluation
6.0 Recommendations
7.0 References
APPENDIX 1:
Phase 1 Habitat Survey Map
APPENDIX 2: Site Photographs
APPENDIX 3: Desk Study Data
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1.0 INTRODUCTION
Project background
1.1 In April 2016, Appletons was commissioned by H & F Eccles and Son to undertake an ecological appraisal
of the site of proposed residential development at land at Brownside and Worsthorne, Burnley. To assess
the ecological value of the site, an ecological desk study data search was undertaken and a Phase 1 Habitat
Survey was completed on 21st April 2016.
Site description and context
1.2 The site comprised two separate survey areas, referred to throughout the current report as Area A and Area
B. Area A is centred at Ordnance Survey Grid Reference SD 874 322, immediately south-west of
Worsthorne Village, and Area B is centred at Ordnance Survey Grid Reference SD 871 325, on the eastern
edge of Brownside Village. The site areas are located approximately 210 m apart, separated by grazed
fields of improved grassland.
1.3 Area A measures approximately 1.18 ha, and is bound by residential properties of Ormerod Street to the
east, whilst agricultural fields are present to the north, south and west. A stream valley is located directly
west of the site, which joins the River Brun 375 m west of the site. At the time of the survey, Area A included
the buildings and structures of Butchers Farm and small sections of adjacent fields.
1.4 Area B measures approximately 2.44 ha, and is bound by residential properties of Lindsay Park to the west,
Brownside Road to the north, Worsthorne Primary School to the east and agricultural fields to the south. At
the time of the survey, Area B was dominated by an open area of improved grassland. An old field boundary
crossed the south of the site, defined by an earth bank and dry ditch with a low number of scattered trees
and scrub.
1.5 Within the wider area, residential areas of Burnley are located to the west of the site areas, and aside from
the villages of Brownside and Worsthorne, the remainder of the local landscape is dominated by rural
farmland with wooded river valleys. Reservoirs and moorland of the South Pennines come within 1.6 km of
the site areas to the east.
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2.0 METHODOLOGIES
Ecological desk study
2.1 A desk top study was undertaken to determine the presence of any designated nature conservation sites
and records of protected species within a 2 km radius of the site survey boundary. Data was provided by
Lancashire Ecological Records Network, and the Natural England website ‘MAGIC’ (Multi Agency
Geographical Information for the Countryside) was utilised to search locations of statutory nature
conservation sites.
Phase 1 Habitat survey
2.2 A Phase 1 Habitat Survey was conducted following the methodology of the Joint Nature Conservation
Committee (JNCC, 2010) and the Institute of Environmental Assessment (IEA, 1995). Phase 1 Habitat Survey
is a standard technique for classifying and mapping British habitats. During the survey, the potential for the
site to support protected species was assessed.
2.3 Whilst every effort is made to identify and map any invasive plant species listed on Schedule 9 of the Wildlife
and Countryside Act (1981, as amended), it should be noted that this is not a specific survey for these species.
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3.0 ECOLOGICAL DESK STUDY
3.1 A summary of relevant ecological data from the desk study search is provided within this section. Selected
raw data is provided in Appendix 3.
Nature Conservation Sites
3.2 The data provided by the local biological records centre and reference to the Natural England MAGIC
website indicates that two statutory and nine non-statutory nature conservation sites occur within a 2 km
radius of the survey areas, summarized in Table 3.1.
Nature Conservation Site
Designation Proximity
to site Description
Statutory Sites
South Pennine Moors
SSSI & SAC & LGS
1.54 km north-east
The largest area of unenclosed moorland within West Yorkshire which contains the most diverse and extensive examples of upland plant communities in the county. Extensive areas of blanket bog occur on the upland plateaux and are punctuated by species rich acidic flushes and mires. There are also wet and dry heaths and acid grasslands. Three habitat types which occur on the site are rare enough within Europe to be listed on Annex 1 of the EC habitats and Species Directive (92/43) EEC. These communities are typical of and represent the full range of upland vegetation classes found in the South Pennines. This mosaic of habitats supports a moorland breeding bird assemblage which, because of the range of species and number of breeding birds it contains, is of regional and national importance. The large numbers of breeding merlin Falco columbarius, golden plover Pluvialis apricaria and twite Carduelis flavirostris are of international importance. The site is designated as a SAC due to the presence of dry heath, blanket bog and old sessile oak woodland.
Deer Pond LNR & BHS 1.56 km
south-west
A pond and surrounding habitat in the grounds of Towneley Park. The site supports a notable assemblage of dragonflies and damselflies and four species of amphibians.
Non-statutory Sites
Houghton Hag BHS 495 m north
Semi-natural, ancient woodland occupying sloping ground on the northern side of Swinden Water. The wood is listed in the Lancashire Inventory of Ancient Woodland (Provisional), (English Nature, 1994). The site also includes a small section of land on the southern side of Swinden Water which supports a series of flushes.
Ormerod and Gin Woods
BHS 510 m south
Two adjacent woodlands – Ormerod Wood and Gin Wood - situated on gently sloping ground along the southern side of the River Brun, to the west of Hurstwood. Although trees have been planted, the woodland ground flora is ancient, semi-natural in character.
Hurst Well Valley
BHS 820 m
north-east
A section of the valley of Swinden Water between Houghton Hag and Lee Green Reservoir to the east of Burnley. Habitats within the site in addition to the river include woodland, scrub, species-rich grassland, flushes and swamp vegetation in a former mill lodge.
Rock Water Valley
BHS 1.09 km
South-east
Land along the steeply sloping sides of Rock Water, to the south of Hurstwood. The valley supports a mosaic of habitats, including woodland that is ancient, semi-natural in character and areas of species-rich grassland.
River Don – Brun Valley
BHS 1.26 km
north-west
An extensive mosaic of habitats situated along approximately 3.5km of the Rivers Don and Brun. Included are areas of species-rich grassland, flushes, broad-leaved woodland and scrub. Some of the woodland is ancient, semi-natural in character.
Swinden Bridge Valley
BHS 1.34 km
north-east
The site comprises a section of the valley of Swinden Water between Swinden Bridge and Swinden Reservoir and supports, in addition to the stream, species-rich neutral grassland, acidic grassland and flushes.
Table 3.1: Summary of Nature Conservation Sites within 2 km of Survey Area (Continues)
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Nature Conservation Site
Designation Proximity
to site Description
Michelin Factory and Shallshaw Industrial Estate Grounds
BHS 1.49 km
north-west
An area of land to the east of the Michelin Tyre Factory and adjacent industrial units. Of particular interest is a pond with a seasonally fluctuating water level and associated areas of swamp, grassland and scrub. The amphibians present include breeding great crested newts Triturus cristatus with smooth newts Lissotriton vulgaris and common toad Bufo bufo. The pond supports an assemblage of breeding dragonflies and damselflies.
Thursden Valley
BHS 1.7 km
north-east
Land extending along both sides of Thursden Brook for approximately 3 km. The valley supports a mosaic of habitats, including species-rich grassland, flushes, scrub and woodland. The site contains old “hushings” - areas worked for the limestone content of the local boulder clay - and these typically support flush/dry grassland mosaics. A nationally scarce cranefly and horsetail weevil have been recorded in the valley.
Fulledge Swamp
BHS 1.9 km west
The site comprises an area of swamp surrounded by woodland, scrub and marshy grassland. The swamp area is noteworthy for the presence of Slender Tufted-sedge Carex acuta and Greater Spearwort Ranunculus lingua, categorised as Vulnerable and Sensitive respectively in the Provisional Lancashire Red Data List of Vascular Plants.
Key:
SSSI: Site of Special Scientific Interest SAC: Special Area of Conservation LGS: Local Geodiversity Site LNR: Local Nature Reserve BHS: Biological Heritage Site
Table 3.1: Summary of Nature Conservation Sites within 2 km of Survey Area (Continued)
3.3 In addition to the nature conservation sites listed in Table 3.1, eight District Wildlife Sites were identified by
the ecological desk study search within 2 km of the survey area, the closest of which is located 480 m north
of the survey area. As with the Biological Heritage Sites, these District Wildlife Sites are afforded protection
through their inclusion in the development plan system for Lancashire.
3.4 The site is located within a SSSI Risk Impact Zone for the South Pennine Moors. SSSI Risk Impact Zones
are utilised by Local Planning Authorities to assess planning applications for likely impacts on Sites of
Special Scientific Interest.
Protected species
3.5 Table 3.2 provides a summary of protected species records identified by the desk study within a 2 km radius
of the site. Absence of a species record should not be taken as confirmation that a species is absent from the
search area.
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Species No. of
Records Most Recent
Record Proximity of Nearest Record to Study Area
Legislation / Conservation Status
Mammals
Badger Meles meles
2 2012 Confidential † PBA
Common pipistrelle Pipistrellus pipistrellus
6 2009 920 m west ECH 4, WCA 5, WCA 6
Daubenton's bat Myotis daubentonii
1 1998 # ECH 4, WCA 5, WCA 6
Natterer's bat Myotis nattereri
1 1998 # ECH 4, WCA 5, WCA 6
Soprano pipistrelle Pipistrellus pygmaeus
1 1998 # ECH 4, WCA 5, WCA 6
Noctule bat Nyctalus noctula
1 1998 # ECH 4, WCA 5, WCA 6
Brown long-eared bat Plecotus auritus
1 1998 # ECH 4, WCA 5, WCA 6
Amphibians
Great crested newt Triturus cristatus
35 2013 1.35 km west ECH 2, ECH 4, WCA 5
Flora
Bog-moss Sphagnum sp.
15 2007 810 m north ECH 5
Bluebell Hyacinthoides non-scripta
38 2012 585 m south WCA 8
Birds
Kingfisher Alcedo atthis
5 1999 1.57 km south-west WCA1i
Peregrine Falco peregrinus
1 1999 # WCA1i
Barn owl Tyto alba
1 2001 # WCA1i
Little ringed plover Charadrius dubius
1 1988 1.65 km north-west WCA1i
Fieldfare Turdus pilaris
1 1998 1.57 km south-west WCA1i
Fish
Bullhead Cottus gobio
8 2011 385 m south-west ECH 2
Key:
*: Species dependent #: Grid reference provided less than 6 figures †: Badger records are confidential and therefore proximity is not provided within the report. ECH 2: Annex II of the European Communities Council Directive on the Conservation of Natural Habitats and Wild Fauna and Flora. Animal and plant species of community interest whose conservation requires the designation of Special Areas of Conservation. ECH 4: Annex IV of the European Communities Council Directive on the Conservation of Natural Habitats and Wild Fauna and Flora. Animal and plant species of community interest in need of strict protection. ECH 5: Annex V of the European Communities Council Directive on the Conservation of Natural Habitats and Wild Fauna and Flora. Animal and plant species of community interest whose taking in the wild and exploitation may be subject to management measures PBA: Protection of Badgers Act 1992. WCA 1i: Schedule 1 Part 1 of Wildlife and Countryside Act 1981 (as amended). Birds protected by special penalties at all times. WCA 5: Schedule 5 of Wildlife and Countryside Act 1981 (as amended). Protected animals (other than birds). WCA 6: Schedule 6 of Wildlife and Countryside Act 1981 (as amended). Animals which may not be killed or taken by certain methods. WCA 8: Schedule 8 of Wildlife and Countryside Act 1981 (as amended). Protected plants and fungi. Note. These tables do not includes reference to the Berne Convention (Convention on the Conservation of European Wildlife and Natural Habitats), the Bonn Convention on the Conservation of Migratory Species of Wild Animals or the Convention on International Trade in Endangered Species of Wild Fauna and Flora (CITES).
Table 3.2: Summary of Protected Species Records Within 2 km of Survey Area
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3.6 In addition to the species listed in Table 3.2, the desk study identified records of white-letter Hairstreak
butterfly Satyrium w-album, smooth newt Lissotriton vulgaris, palmate newt Lissotriton helveticus, common
toad Bufo bufo and common frog Rana temporaria, which are species protected by legislation from sale.
Common toad is also listed as a Species of Principal Importance for Nature Conservation in England.
3.7 In addition to legally protected species, the desk study identified records of Species of Principal Importance
for Nature Conservation in England and species listed on the Lancashire Biodiversity Action Plan, including
over 2000 records of over 30 moth and butterfly species, and several bird species including house sparrow
Passer domesticus, skylark Alauda arvensis, lapwing Vanellus vanellus, grey partridge Perdix perdix,
curlew Numenius arquata, lesser redpoll Acanthis cabaret, reed bunting Emberiza schoeniclus and wood
warbler Phylloscopus sibilatrix.
3.8 A single species record was identified within the site area, close to Butchers Farm. This record was of
meadow pipit Anthus pratensis, which is a species included on the Lancashire Biodiversity Action Plan.
Invasive species
3.9 Table 3.3 provides a summary of invasive species records identified by the desk study within a 2 km radius
of the site. Absence of a species record should not be taken as confirmation that a species is absent from
the search area.
Species No. of
Records
Most Recent Record
Proximity of Nearest Record to Study Area
Legislation / Conservation Status
Rhododendron Rhododendron ponticum
13 2012 520 m south WCA 9
Blood-drop-emlets Mimulus luteus
3 1994 520 m south WCA9
Himalayan balsam Impatiens glandulifera
30 2012 580 m north WCA9
Hybrid monkeyflower Mimulus robertsii
6 2007 635 m south-west WCA 9
Japanese knotweed Fallopia japonica
10 2013 670 m south-west WCA9
Water fern Azolla filiculoides
1 1998 1.4 km south-west WCA9
Canadian waterweed Elodea canadensis
7 2007 1.49 km north-west WCA9
Key:
WCA9: Schedule 9 of Wildlife and Countryside Act 1981 (as amended). Invasive, non-native, plants and animals.
Table 3.3: Summary of Invasive Species Records Within 2 km of Survey Area
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4.0 PHASE 1 HABITAT SURVEY
Introduction
4.1 This section provides the results of the Phase 1 Habitat Survey. Phase 1 Habitat Survey maps are provided
in Appendix 1, which illustrate the location and extent of all habitat types recorded within and adjacent to
Areas A and B. Any notable features or features too small to map are detailed using target notes.
Photographs taken during the field survey are presented in Appendix 2.
4.2 The survey was carried out on 21st April 2016 by Paula Bateson BSc(Hons) ACIEEM, Project Ecologist.
Survey constraints
4.3 The survey was not subject to any constraints.
The current report was updated in September 2016, to reflect an amended edge red site boundary. The
finalised edge red of Site Area A included a 120 m2 area of land which was not covered by the Phase 1
survey. Based on aerial imagery, this area includes a small building, driveway and mown grassland of a
residential garden.
Site habitats
4.4 The following habitats were recorded on and adjacent to the site areas during the survey. These are listed
in alphabetical order, not in order of ecological importance.
Area A
Bare Ground
Building
Hardstanding
Hedgerow
Improved Grassland
Running Water
Wall
Area B
Dry Ditch
Hedgerow
Improved Grassland
Scattered Trees
Scrub
Area A
Bare Ground
4.5 A track of bare earth connecting the south of Butchers Farm to Ormerod Street, and an area of cattle
poached bare ground was present within the south of Area A.
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Building
4.6 Three barns were included in Area A, which were in active use as cattle sheds at the time of the survey.
These possessed metal corrugated roofs and were supported by a combination of wooden and metal
frames.
Hardstanding
4.6 Site Area A was dominated by hardstanding. Stored farm equipment and stacked materials were present
across the areas of hardstanding throughout the farm complex along with rubble piles, caravans and metal
containers.
Hedgerow
Species-poor Intact Hedgerow
4.7 The driveway from Brownside Road into Butchers Farm was lined by two hedgerows, the eastern-most
which was dominated by Leyland cypress Cupressus × leylandii and managed to two meters in height and
1 m in width. The western-most hedgerow comprised several hawthorns Crataegus monogyna planted
between concrete slabs along a wall top, which were unmanaged and measured approximately 5 m in
height, and a row of hawthorn, Leyland cypress and semi-mature birch Betula sp., all trimmed to a height
of approximately 5 m.
Improved grassland
4.8 Small sections of three cattle grazed fields adjacent to the farm complex were included within the site area.
The sward height of the grassland measured between 50 and 100 mm at the time of the survey, and was
dominated by rye-grass Lolium sp. with clover Trifolium sp., dandelion Taraxacum officinale, broad-leaved
dock Rumex obtusifolius, creeping buttercup Ranunculus repens and lesser celandine Ficaria verna also
recorded.
Running Water
4.9 A stream issued into a small valley through a field immediately west of the farm complex, from a concrete
pipe 8 m from the western site boundary. This meandering stream measured approximately 1 m in width
with a substrate of cobbles, pebbles and boulders. The water was clear and considered unpolluted. The
stream was largely unshaded, though no aquatic or marginal vegetation was recorded, perhaps due to the
presence of grazing cattle. The stream banks measured up to approximately 0.3 m in height and ranged
from vertical exposed bare earth on the outside of meanders to gently sloping banks of cobbles. Bankside
vegetation included species such as soft rush Juncus effusus, nettle Urtica dioica, lesser celandine,
willowherb Epilobium sp., broad-leaved dock, watercress Nasturtium officinale and garlic mustard Alliaria
petiolata. Occasional sections of heavily poached ground were present where cattle could easily access the
stream. Occasional tipped urban debris was recorded within the upper eastern most third of the stream.
Wall
4.10 A dry stone wall formed the north-western site boundary, which measured approximately 0.5 m in width and
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1.2 m in height.
Area B
Dry Ditch
4.11 A dry ditch, adjacent to a linear earth bund, was present across the south of Area B. Occasional sections
of a collapsed dry stone wall were recorded along the earth bund. Vegetation recorded within the dry ditch
included rush Juncus sp., grasses such as Yorkshire fog Holcus lanatus and tufted hair grass Deschampsia
cespitosa, and occasional common reed Phragmites australis.
4.12 An ornamental channel dominated by yellow flag Iris pseudacorus was also recorded within an adjacent
residential garden. No standing water was present at the time of the survey.
Hedgerow
4.13 A short Leyland cypress hedgerow was present along the western site boundary, which formed the rear
boundary of an adjacent residential garden.
Improved Grassland
4.14 Area B was dominated by a shortly grazed field of improved grassland, dominated by rye-grass with forbs
such as creeping buttercup, chickweed Stellaria media, bittercress Cardamine sp. and broad-leaved dock
also recorded.
Plantation Woodland
4.15 Two areas of plantation woodland were recorded immediately adjacent to the site area, dominated by willow
Salix sp. and birch. The woodland area to the east of the site was recorded as newly planted, whilst the
triangle of woodland adjacent to the eastern boundary was semi-mature in age within a residential garden.
Scrub
4.16 Hawthorns were present along the earth bund and a small area of dense bramble scrub was recorded within
the south-west of the site.
Scattered Trees
4.17 A single dead tree was located within the field of improved grassland.
4.18 Two semi-mature oak Quercus sp. trees and a single semi-mature sycamore were present along the earth
bund. A rot hole was recorded on the sycamore.
Invasive plant species
4.19 Himalayan balsam Impatiens glandulifera seedlings were recorded along the banks of stream to the west
of Site Area A.
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5.0 ECOLOGICAL EVALUATION
Proposed development overview
5.1 Outline proposals include the erection of up to 24 residential dwellings within Area A, and up to 47 residential
dwellings within Area B. As proposals are not yet finalised, a precautionary approach has been adopted in
relation to impacts upon species, habitats and nature conservation sites.
Nature Conservation Areas
Statutory and non-statutory nature conservation sites
5.2 Two statutory, nine non-statutory and eight district nature conservation sites were identified by the
ecological desk study within a 2 km radius of the survey area.
5.3 The stream adjacent to Site Area A connects to The River Brun which connects to Rowley Lane district
wildlife site and River Don, Brun Valley BHS, both of which are located over 750 m from the closest site
boundary. Considering the distance of these sites from the proposed development, it is not considered that
the sites would be adversely impacted upon by the proposed development, however as a precaution a
recommendation in made in Section 6 for the protection of running water.
5.4 The South Peninne Moors SSSI and SAC comes within 1.6 km of the site areas, and the site areas are
located within a Risk Impact Zone for the SSSI. SSSI Risk Impact Zones assist in judging whether a
proposed development may have a negative impact on SSSIs and whether Natural England should be
consulted. Consultation is required for development that is in, or likely to affect, a SSSI. The proposed
development area is separated from the South Pennine Moors by agricultural land, and as such there is
limited habitat connectivity between the site and the SSSI and it is not considered that the proposed
development would directly or indirectly impact upon the habitats of the South Pennine Moors. The potential
impacts upon breeding bird assemblage of the South Pennine Moors is considered in Section 5.26.
5.5 The remainder of the nature conservation sites identified by the ecological desk study are located over
450 m from the proposed development site areas with no habitat connectivity. It is not considered that the
development would result in any adverse impacts to these conservation sites.
Site habitats
5.6 The ecological importance of the habitats present on site is determined by their presence on the list of
Habitats of Principal Importance in England and on the Local BAP, along with the intrinsic value of the
habitat. The ecological value of the habitats on site is considered below in terms of the likely impact of site
proposals.
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Hedgerow
5.7 All native hedgerows measuring over 20 m in length qualify as habitats of principle importance for nature
conservation in England, which includes the hawthorn hedgerow along the farm driveway within Area A. A
recommendation is made in Section 6 in relation to the retention and protection of hedgerow habitat.
Scattered Trees
5.8 Any retained scattered trees on and/or adjacent to the site areas should be protected throughout
development works, a recommendation for which is made in Section 6.
Running Water
5.9 The stream adjacent to Site Area A, and the River Brun which the stream connects to, may qualify as
Habitats of Principle Importance. The stream is outside of the proposed development area and as such
would not be directly impacted upon, however considering the proximity of the habitat to the site, a
recommendation to protect the habitat from indirect impacts throughout development works is made in
Section 6.
Remaining Habitats on Site
5.10 The remaining habitats on site are of low integral ecological value and are well represented within the
surrounding area. A general recommendation is made in Section 6 in relation to habitat loss and
enhancement.
Protected species
5.11 Species that have been identified by the desk study and those which potentially suitable habitat occurs
within or adjacent to the site are considered within this section, in terms of the likely impact of site proposals.
Mammals
Badger
5.12 Two records of badger were identified by the ecological desk study. The stream valley adjacent to Site Area
A was considered to provide suitable sett building habitat for badgers. A detailed search for evidence of
badger was undertaken as part of the survey, and no evidence of badger presence was identified (e.g. sett
entrances, footprints, mammal trails or latrines), however considering the suitability of the site for foraging
badgers and the proximity of suitable sett building habitat such as the River Brun valley and Hog Wood, a
precautionary recommendation is made in Section 6 in relation to deep excavations.
Bats
5.13 A low number of records of bat species were identified by the ecological desk study within 2 km of the site,
including species associated with running and standing water, dense woodland, habitat edges and open
habitats.
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5.14 Any buildings and/or trees that are to be impacted upon by the development should be subject to a daytime
bat survey, a recommendation for which is made in Section 6. This should include an assessment of the
habitats on site for foraging and commuting bats.
Water vole
5.15 The water course adjacent to Area A was considered suboptimal for water vole due to the low stream banks,
presence of cattle and minimal marginal vegetation, however the River Brun was considered suitable habitat
for water vole, which the stream on site connects to 380 m from the proposed development. As water voles
rely on good water quality, a recommendation is made for the protection of the stream on site, and thus the
River Brun throughout development works.
5.16 As water vole can readily disperse into newly suitable habitats, it is recommended that the grassland within
the stream valley is kept heavily grazed up until development work commences.
5.17 As part of the development, there is an opportunity for habitat enhancement of the stream valley to increase
its suitability for water vole a recommendation for which is made in Section 6.
Otter
5.18 The River Brun comes within 200 m of Area A, and may provide suitable habitat for otter along its length.
No features within the site areas were identified as potential lay-up sites or holts. Due to the distance of the
site areas from potentially suitable otter habitat, otter is not considered a notable species in relation to the
proposed development and no recommendations are made.
Birds
5.19 Several records of protected bird species were identified over 1.3 km from the site by the ecological desk
study; kingfisher, peregrine, barn owl, little ringed plover and fieldfare.
5.20 The stream adjacent to Area A was not considered to possess suitable nesting habitat for kingfisher due to
the low height of the stream banks, however the stream may provide suitable hunting habitat for the species.
This habitat would not be impacted upon by the proposed development.
5.21 Barn owls generally nest within undisturbed sheltered areas with open access points such as large cavities
within hollow trees or old hay lofts. None of the trees on site were recorded to possess large enough features
to support nesting barn owl, and no permanently open hay lofts or similar features were recorded within the
farm buildings. The open grassland may provide suitable hunting habitat for barn owl. As open grassland is
widely represented within the immediately surrounding area, it is not considered that the conservation status
of any local populations of barn owl potentially present would be adversely impacted upon by the proposals.
5.22 Fieldfare are generally an over-wintering species in the UK associated with arable and grass fields with
nearby trees or hedgerows. The improved grassland may provide feeding habitat for fieldfare, however as
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this habitat is widely represented within the immediately surrounding area, it is not considered that the
conservation status of any local populations of field fare potentially present would be adversely impacted
upon by the proposals.
5.23 Little ringed plover is a species associated with open habitats such as gravel pits, reservoirs and shingle
banks, and peregrine falcons require extensive open terrane for hunting, and nest on tall, exposed features
such as cliffs or tall buildings. As such it is not considered that the site is of value to either species.
5.24 The dry stone wall, farm buildings and structures, trees and scrub across the site areas were considered to
provide suitable nesting habitat for a range of common bird species. As all nesting and nest building birds
are protected, a recommendation is made in Section 6 in relation to the timing of any vegetation removal,
dry stone wall removal and/or building demolition. A recommendation is also included in Section 6 for the
inclusion of nesting habitat and bird boxes within proposed landscape plans.
5.25 The South Pennine Moors SSSI comes within 1.6 km of the proposed development, which supports
internationally important breeding populations of merlin, golden plover and twite, which are species
associated with upland moorland habitats, and coastal habitats over winter. One record of meadow pipit
was identified within Area A by the desk study, a species also associated with heathland and coastal habitat.
The proposed development site areas were not considered to provide suitable breeding habitat for any of
these moorland bird species. As the site is located 1.6 km west of the South Pennine Moors, in the direction
of the Lancashire Coast, the site could occasionally be utilised for feeding by migrating birds, however
considering the suboptimal nature of the habitats on site for moorland bird species, and the well represented
nature of the habitats on site within the surrounding area, it is not considered that the development would
impact upon the breeding bird assemblage of the South Pennine Moors.
Fish
Bullhead
5.26 Bullhead are often an indicator species of unmodified watercourses with good water quality and refuges
such as pebbles and boulders. The stream adjacent to the site was considered suitable habitat for bullhead,
as was the River Brun which the stream connects to. A record of bullhead was identified by the desk study
within the River Brun. As bullhead depend on good water quality, a recommendation is made for the
protection of the stream throughout development works.
5.27 As the stream is located outside of the proposed development site area, the habitat would not be directly
impacted upon by the proposed development, however the proposed drainage plans are not yet known and
may impact upon the stream valley. If proposed works are likely to impact upon the stream a survey should
be undertaken, detailed in Chapter 6.
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Amphibians
Great Crested Newts
5.28 No suitable breeding habitat for amphibians was present within the site areas, as the ditches on site were
recorded as dry at the time of the survey, which was undertaken within the amphibian breeding season.
5.29 Thirty-five records of great crested newt were identified by the ecological desk study, the closest of which
was located 1.35 km from the proposed development site areas. Great crested newts can use suitable
terrestrial habitat up to 500 m from a breeding pond, and as such it is not considered that great crested
newts from this population would disperse onto site. According to Ordnance Survey maps and aerial
imagery, four ponds are present within 500 m of Site A, one of which is also located within 500 m of Area
B. Two of the ponds are located across the River Brun from the site, which was fast flowing and considered
a dispersal to great crested newt dispersal. The nearest pond is located 305 m from the closest site
boundary, within the north of Worsthorne Village. Great crested newts are not likely to travel more than
250 m from ponds where suitable foraging and hibernation habitat exists (English Nature, 2004), and the
habitats surrounding the each of the ponds within 500 m of the site areas were considered to provide good
quality foraging habitat for newts. As such it is not considered that great crested newts would be present on
site and no recommendations in relation to this species are made.
Invertebrates
White-clawed Crayfish
5.30 White clawed crayfish are associated with clean watercourses with refuges such as pebbles and boulders.
The stream adjacent to Site Area A was considered suitable habitat for crayfish, as was the River Brun
which the stream connects to. A record of bullhead was identified by the desk study within the River Brun
close to the site, which is traditionally an indicator species of good water quality and is often found within
the same habitats as white-clawed crayfish. As white-clawed crayfish depend on good water quality, a
recommendation is made for the protection of the stream throughout development works.
5.31 It is understood that the stream will not be directly impacted upon by the proposed development, however
the proposed drainage plans are not yet known and may impact upon the stream valley and the stream may
be indirectly impacted by siltation or run-off. As such, as a precaution a white-clawed crayfish survey is
recommended in Chapter 6.
Moths and butterfly species
5.32 The desk study identified over 2000 records of over 30 moth and butterfly species within 2 km of the site
areas. The species poor grassland which dominated the site areas was not considered to provide valuable
habitat for invertebrates. Recommendations are made in Section 6 for the incorporation of wildlife friendly
landscaping and habitat creation to enhance the potential value of the site for invertebrates.
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Flora
5.33 Records of bluebell and bog-moss were identified by the ecological desk study, over 400 m from the
proposed development areas. Neither of these species were identified within the survey area. No rare or
protected flora was recorded on site during the survey.
Invasive Species
Himalayan balsam
5.34 Himalayan balsam seedlings were recorded along the stream valley adjacent to Site Area A. This species
is listed on Schedule 9 of the Wildlife and Countryside Act 1981(as amended) and must not be caused to
spread into the wild. A recommendation is made in Section 6.
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6.0 RECOMMENDATIONS
6.1 As proposals are not yet finalised, a precautionary approach has been adopted in relation to impacts upon
species, habitats and nature conservation sites.
Nature Conservation areas
6.2 No recommendations are made in relation to statutory and non-statutory nature conservation sites.
Habitats
Running Water
6.3 All works should be undertaken in accordance with best practice, e.g. the Environment Agency’s Pollution
Prevention Guidelines, to ensure that the watercourse close to Site Area A is not adversely impacted by the
proposed works.
Hedgerows
6.4 As the hawthorn hedgerow within Area A has the potential to qualify as a Habitat of Principle Importance
for Nature Conservation in England, it is recommended that the hedgerow is retained and protected where
feasible. Any loss of hedgerow habitat should be compensated for with complementary planting of native
hedgerow species.
Scattered Trees
6.5 All trees which are to be retained as part of site development should be protected in accordance with British
Standard 5837: 2012 "Trees in relation to design, demolition and construction - recommendations".
Protection should be installed on site prior to the commencement of any works on site.
Habitat Loss and Enhancement
6.6 In accordance with the provision of Chapter 11 of the National Planning Policy Framework (Conserving and
Enhancing the Natural Environment), biodiversity enhancement measures should be incorporated into the
proposed landscaping scheme, for example, opportunities include:
o Planting appropriate native wild flower seed mixes along the adjacent stream valley, or/and around
the perimeters of any proposed open amenity spaces, which could include invertebrate attracting
plant species recommended by the Bat Conservation Trust (2015).
o Bird and bat box installation on any retained trees or/and proposed housing.
o The inclusion of linear areas of planting within landscaping plans, to retain and improve habitat
connectivity across the site. Species should include native and wildlife attracting species, for
example trees which support blossom and fruit, or flowering species such as Lavender, Rosemary,
or Hebe.
o Post-development, reduced grazing or exclusion of cattle from the stream valley could create
suitable habitat for water vole. Encouragement of tall grasses, sedges, rushes and heather could
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further enhance habitat suitability, along the planting of species that provide food over winter such
as crab-apple, dog-rose and gooseberry.
Protected / Notable Species
6.7 To ensure compliance with wildlife legislation and relevant planning policy, the following recommendations
are made:
Bats
6.8 A daytime bat survey should be undertaken on the buildings and trees on site which may be impacted by
the proposed development works. This survey should also include an assessment of the site for foraging
and commuting bats. Daytime bat surveys can be completed at any time of year. Depending upon the
results of the initial bat survey, emergence and return surveys could be required during the peak bat survey
period which occurs between mid-May and August (inclusive).
Terrestrial mammals including Badger
6.9 Any excavations that need to be left overnight should be covered or fitted with mammal ramps to ensure
that any animals that enter can safely escape. Any open pipework with an outside diameter of greater than
150 mm should be blanked off at the end of each work day to prevent badgers entering/becoming trapped.
Nesting Birds
6.10 To ensure compliance with the Wildlife and Countryside Act 1981 (as amended), any vegetation clearance,
building demolition or dry stone wall dismantling should be undertaken outside of the nesting bird
season. The nesting bird season is weather dependent but generally extends between March and
September inclusive. If this is not possible then any vegetation, dry stone walls or buildings that are to be
removed or disturbed should be checked by an experienced ecologist for nesting birds immediately prior to
works commencing. If birds are found to be nesting any works which may affect them would have to be
delayed until the young have fledged and the nest has been abandoned naturally.
Water vole
6.11 It is recommended that the grassland within the stream valley close to the development site area is kept
heavily grazed up until development work commences.
White-clawed crayfish and bullhead
6.12 If any disturbance to the adjacent stream is anticipated, a survey for white-clawed crayfish and bullhead
should be undertaken. Surveys can be completed between July and October inclusive, depending on water
temperature and survey methodology.
Invasive Plant Species
Himalayan balsam
6.13 Works must not cause Himalayan balsam to spread into the wild.
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7.0 REFERENCES
British Standards Institution (2013). British Standard 42020: 2013. Biodiversity – Code of practice for
planning and development. British Standards Institution, London.
British Standards Institution. (2012). British Standard 5837:2012, Trees in relation to design, demolition and
construction – recommendations. British Standards Institution, London.
Department for Communities and Local Government (2012). National Planning Policy Framework.
Available:
http://www.communities.gov.uk/planningandbuilding/planningsystem/planningpolicy/planningpolicyfram
ework/
Institute of Environmental Assessment. (1995). Guidelines for Baseline Ecological Assessment, Institute of
Environmental Assessment. E&FN Spon, An Imprint of Chapman and Hall. London.
Joint Nature Conservation Committee (2010). Handbook for Phase 1 Habitat Survey: A technique for
environmental audit (reprint). Joint Nature Conservation Committee, Peterborough.
Joint Nature Conservation Committee (2012). UK Post-2010 Biodiversity Framework. Available:
http://jncc.defra.gov.uk/pdf/UK_Post2010_Bio-Fwork.pdf
Natural England. Multi Agency Geographic Information for the Countryside (MAGIC). Available:
http://www.magic.gov.uk/
(
(
Key
Site boundaryDense scrubDry ditch
!!!!! Earth bankHardstandingImproved grasslandIntact hedgerowPlantation woodland
D Scattered scrub
! Scattered tree
( Target notes:
±
0 40 8020 Meters
Landscape Architecture Ecology Enviromental Planning & Assessment Aboriculture
appletons
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Brownside Road
Lindsay Park
Residential Estate
Lindsay Park
Residential Estate
1
#
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1 - Dead tree2 - Ornamental channel (dry)
LAND AT BROWNSIDE AND WORSTHORNE, BURNLEY
Figure 2Title: Area B - Phase 1 Habitat Survey
(Key
Site boundary
Area of site not surveyed - area notincluded in red edge at time ofsurvey
Bare ground
Building
Dry stone wall
Hardstanding
Improved grassland
Intact hedgerow
Running water
D Scattered scrub
! Scattered tree
( Target note: Himalayan balsam
±
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Landscape Architecture Ecology Enviromental Planning & Assessment Aboriculture
appletons
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LAND AT BROWNSIDE AND WORSTHORNE, BURNLEY
Figure 1Title: Area A - Phase 1 Habitat Survey
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Area A
Photo A.1: Butchers Farm looking from south Photo A.2: Bare ground
Photo A.3: Stream outlet Photo A.4: Stream valley west of site
Photos A.5 and A.6: Hedgerows along driveway into Area A
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Area B
Photo A.12: Improved grassland
Photo A.13: Scattered scrub and trees along earth
wall
Photo A.14: Dead tree
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APPLETONS REF:2056
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Site Check Report Report generated on Mon May 09 2016 You selected the location: Centroid Grid Ref: SD872323
The following features have been found in your search area: Local Nature Reserves (England) - points Reference 1009307 Name DEER POND Hectares 1.51 Hyperlink http://www.lnr.naturalengland.org.uk/special/lnr/lnr_details.asp?themeid=1009307 Local Nature Reserves (England)
Reference 1009307 Name DEER POND Hectares 1.51 Hyperlink http://www.lnr.naturalengland.org.uk/special/lnr/lnr_details.asp?themeid=1009307 Sites of Special Scientific Interest (England) Name SOUTH PENNINE MOORS Reference
1006648 Natural England Contact ANDREW CLARK Natural England Phone Number 0845 600 3078 Hectares 20944.5 Citation 1007196 Hyperlink http://designatedsites.naturalengland.org.uk/SiteDetail.aspx?SiteCode=s1007196 SSSI Impact Risk Zones – to assess planning applications for likely impacts on SSSIs/SACs/SPAs &
Ramsar sites (England) 1. DOES PLANNING PROPOSAL FALL INTO ONE OR MORE OF THE CATEGORIES BELOW? 2. IF YES, CHECK THE CORRESPONDING DESCRIPTION(S) BELOW. LPA SHOULD CONSULT NATURAL ENGLAND ON LIKELY RISKS FROM THE FOLLOWING: All Planning Applications Infrastructure Airports, helipads and other aviation proposals. Wind & Solar Energy Minerals, Oil & Gas Rural Non Residential Residential
Rural Residential Air Pollution Any industrial/agricultural development that could cause AIR POLLUTION (incl: industrial processes, pig & poultry units, slurry lagoons > 750m³ & manure stores > 3500t). Combustion General combustion processes >50MW energy input. Incl: energy from waste incineration, other incineration, landfill gas generation plant, pyrolysis/gasification, anaerobic digestion, sewage treatment works, other incineration/ combustion. Waste Composting Discharges Water Supply
Special Areas of Conservation (England) Name SOUTH PENNINE MOORS Reference UK0030280 Hectares 65025.5
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Hyperlink http://jncc.defra.gov.uk/protectedsites/sacselection/sac.asp?eucode=UK0030280
Special Protection Areas (England) Name SOUTH PENNINE MOORS PHASE 2 Reference UK9007022 Hectares 20944.5 National Nature Reserves (England) - points No Features found National Nature Reserves (England) No Features found
Ramsar Sites (England) - points No Features found Ramsar Sites (England) No Features found Sites of Special Scientific Interest (England) - points No Features found Special Areas of Conservation (England) - points No Features found Special Protection Areas (England) - points No Features found
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85
385000m .E
86
86
87
87
88
88
89
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4 31000m. N
31
32 32
33 33
34 34
This m ap is base d upon Ordnance S urve y m ate rial with the pe rm ission of Ordnance S urvey on behalf of the controlle r of He r Maje sty’s S tatione ry Office © Crown copyright. U nauthorise d re production infringe s Crown copyright and m ay lead to prosecution or civil proce edings. Lancashire County Council 100023320 2016.
Legend250 m Buffe r500 m Buffe r1 k m Buffe r2 k m Buffe r
d Lancashire Key S pe cie s# Bats subse t of LKS
Biological He ritage S ite sLocal Ge odive rsity S ite sNatura 2000District Wildlife S ite sLocal Nature Re se rveS S S I
±
Lancashire Environm e nt Record Ne tworkC/O Planning GroupEnvironm e nt Directorate, Lancashire County Council, PO Box 100,County Hall, Pre ston. PR1 0LDle rn@lancashire .gov.uk
1:15,0000 1,000
Me tre s
http://www.lancashire .gov.uk/le rn.aspx
Brownside We sthorneProject:
Apple tonsClient:
Grid Ref: 387250 432390
"Boundarie s of statutory de signations (Natura 2000, S S S I e tc)are include d for inform ation only.Definitive, information forthese designations should be obtained from Natural England."Lancashire Key Species records are plotted at the centre of thearea to which they relate (the precision of each record is givenin the accompanying attribute data and spreadsheet).
N.B. THIS IS AN INTERACTIVE PDFLAYERS CAN BE TURNED ON OR OFFTO AID CLARITY.