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Northamptonshire Office 7-8 Melbourne House Corbygate Business Park Weldon, Corby Northamptonshire NN17 5JG

Oxfordshire Office Greystones House Burford Road Chipping Norton Oxfordshire OX7 5UY

01536 408 840 info@lgluk.com

01608 656 167 info@lgluk.com

www.lgluk.com www.lgluk.com

Ref: 21-0395

Version: 1

Date: June 2021

Author: Joanne Alderton

Position: Ecological Consultant

Preliminary Ecological Appraisal (PEA) Report

Rockingham Forest Park

Recycling Yard

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DOCUMENT CONTROL SHEET

Ecological Team

Jo Alderton FdSc BA(Hons) BSc (Hons) PGDip Law Business Unit Manager

Samantha Hodgson BSc (Hons) GradCIEEM Senior Ecological Consultant

Natasha Hannah-Lyons BSc (Hons) Assistant Ecological Consultant

Alison Saunders BSc (Hons) Assistant Ecological Consultant

Rachel Jackson BSc (Hons) Assistant Ecological Consultant

Elliot Williams BSc (Hons) Graduate Ecological Consultant

Marie Allcoat Project Administrator

REVISION HISTORY

Rev Description of change Date Initials

1 Original Report 29.06.21 JA

COPYRIGHT © The copyright of this document remains with Lockhart Garratt Ltd. Its contents must not be copied or

reproduced in whole or in part for any purpose without the written consent of Lockhart Garratt Ltd.

DISCLAIMER

It should be noted that the information above provides details of the Site’s current ecological

situation. In the event that the proposed development does not commence within 12 months of the

date of this report, further advice should be sought from a suitably qualified ecologist as to whether

the information provided requires updating in light of changing ecological conditions.

............

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TABLE OF CONTENTS

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1. EXECUTIVE SUMMARY

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5

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2. INTRODUCTION

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......................................................................... 6 ................................

3. METHODOLOGY

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8

4. LEGISLATION AND PLANNING POLICY OVERVIEW 12

5. DESK STUDY RESULTS 15

6. PHASE 1 HABITAT SURVEY RESULTS 20

7. EVALUATION OF ECOLOGICAL CONTEXT 26

8. RECOMMENDATIONS 29

9. REFERENCES AND BIBLIOGRAPHY 31

10. APPENDICES 32

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1. EXECUTIVE SUMMARY

1.1 Lockhart Garratt Ltd was commissioned by Rockingham Forest Park to carry out a Preliminary

Ecological Appraisal (PEA) survey including desk study for land associated with the recycling

yard.

1.2 The Site itself is not subject to any statutory or non-statutory designation. There are two

statutory designations within 2km of the Site, and 16 non-statutory designations, the closest

being Great Byards Sale and Great Morton Sale. Both woodlands are Local Wildlife Sites

designated as ancient woodland. A range of protected mammal and bird species were identified

within 2km of the Site by the desk study.

1.3 The PEA survey was undertaken on 22nd June 2021. The habitat within the Site consisted of a

bund which was mainly bare ground with some tall ruderal and dense scrub vegetation on the

slopes nearest the boundary fence.

1.4 The report considers the ecological conditions within the Site in the context of landscaping of

the bund with scrub and grassland planting.

1.5 On the assumption that the Proposed Development will require no further earthworks or soil

movement it is considered that this work will have a positive impact on the Site.

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2. INTRODUCTION

Terms of Instruction

2.1 Lockhart Garratt Ltd has been commissioned by Rockingham Forest Park to undertake an

ecological assessment of land in respect of a proposed screening bund along with a landscape

planting scheme.

Aim of the study

2.2 The purpose of this report is to provide an assessment of ecological features present within the

site and immediately adjacent, to identify any ecological constraints and provide appropriate

mitigation, compensation and avoidance measures, as appropriate.

Documents Provided

2.3 As background information, the following documentation was provided:

• 20-4068 – Screening bund planting design (Lockhart Garratt) (“the Planting Design”)

• Planning statement dated February 2021 (SF Planning)

Site Description

2.4 The site is located to the south-west of Kings Cliffe industrial estate at grid reference TL 04183

98595 (hereafter referred to as “the Site”). The assessment covered the whole of the Site, which

is approximately 1.7ha in area. The survey also included the habitats immediately adjacent to

the Site, hereinafter referred to as the “Wider Site Area”.

2.5 At the time of the assessment, the Site comprised mostly of a bare earth bund which was

vegetated with some tall ruderal habitat and dense scrub.

2.6 The Site was surrounded by a predominantly rural landscape with arable farmland to the east

and west of the Site. There was a woodland parcel to the north, with the industrial estate to the

north-east. The Site location plan is provided below at Figure 1 and a red line Site boundary plan

and Wider Site survey area is provided below at Figure 2.

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Figure 1: Site Location Plan

Figure 2: Red Line Site boundary and the Blue Line Wider Site Area

Reproduced with the permission of The Controller of Her Majesty’s Stationery Office Crown Copyright © Licence Number:

100015654. Lockhart Garratt Ltd 8 Melbourne House, Corbygate Business Park, Weldon, Corby, Northants NN17 5JG.

Proposed Development

2.7 The development will involve the planting of the soil bund within the Site, which had previously

been created as a result of screening materials within the Wider Site Area The boundary fence

will be retained and no further earthworks will be required, “the Proposed Development”.

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3. METHODOLOGY

3.1 The methodology for the ecological assessment was split into two main areas: a desk study and

a habitat and faunal survey. These are discussed in more detail below.

Desk Study

3.2 Existing ecological information on the Site and surrounding area was requested from the

Northamptonshire Biological Records Centre (NBRC) and the Northants Bat Group (NBG). The

purpose of the desk study was to collect baseline information to identify statutory and non-

statutory designated sites, legally protected species and species of conservation concern within

a 2km radius of the Site in line with CIEEM Guidelines for Preliminary Ecological Appraisal

(2017). A full copy of the information can be provided upon request.

3.3 A review of online resources, including the Multi Agency Geographic Information for the

Countryside (MAGIC) database was also undertaken to establish the ecological context for the

Site (accessed 19th June 2021). The MAGIC website was also reviewed to identify any designated

sites of European Importance within 2km of the Site.

3.4 In addition, Ordnance Survey and aerial mapping was reviewed to identify any ponds within

500m of the Site.

Phase 1 habitat survey

3.1 A Phase 1 habitat survey was undertaken by Joanne Alderton on 22nd June 2021 in order to

ascertain the general ecological value of the Site and Wider Survey Area to determine the need

for further assessment.

3.2 The Phase 1 habitat survey was undertaken in accordance with standard methodology (JNCC,

20101). The Phase 1 methodology involves the classification of habitat types based on

vegetation present. The Site was classified into areas of similar botanical community types, with

a representative species list provided for each habitat type identified. In addition, invasive

weeds were also searched for during the Phase 1 habitat survey, as listed on Schedule 9 of the

Wildlife and Countryside Act 1981 (as amended).

3.3 The information is presented in accordance with the standard Phase 1 habitat survey format

with habitat descriptions and a habitat map, provided at Appendix 1. In addition, target notes

providing supplementary information, for example relating to species, habitat composition,

structure and management are also presented on the habitat map.

Faunal Surveys

3.4 General faunal activity was recorded during the habitat survey, including mammals and birds

observed or heard. Specific attention was also paid to the potential presence of any protected,

rare or notable species, as described below.

Badger Appraisal

3.5 During the habitat survey conducted on 22nd June any incidental signs of current badger Meles

meles activity were recorded within the Site and within 30m of the Site where access could be

1 Joint Nature Conservation Committee (2010). Handbook for Phase 1 Habitat Survey – A Technique for Environmental Audit.

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obtained. The survey method was based on a standard approach as in ‘The history, distribution,

status and habitat requirements of the Badger in Britain, (Cresswell, P. 1990)’.

3.6 The appraisal involved a systematic search of the survey area for all signs of badger activity

including badger setts, worn pathways in vegetation and/or across field boundaries, footprints,

hairs, dung pits/latrines, bedding and evidence of foraging activity including snuffle holes.

Particular attention was paid to habitats of suitable topography or supporting suitable

vegetation for sett-building as well as to those features particularly favoured by badgers

including hedgerows, areas of dense scrub, woodland, ditches and banks.

3.7 Any holes of an identified sett were examined closely and the number of active and inactive

entrances and evidence of its usage were recorded. Where possible, setts identified during the

survey were categorised using nationally recognised sett classification as described below:

• Main sett: These are large setts comprising a number of well-used, active holes with

conspicuous spoil heaps. They are well established with worn paths to and from the sett

and between entrances. Main setts are breeding setts and are normally in continuous use

throughout the year, with only one main sett per social group of badgers;

• Annexe sett: Where present they occur in close association with the main sett (normally

less than 150m away) and are linked to them by clear, well-worn paths. Annexe setts arise

for the purposes of rear cubs should a second litter be born, and have several entrances

(though not all in use at the same time);

• Subsidiary sett: These setts usually consist of three to five entrances which are not in

continuous use. They are usually more than 50m away and may not have well-used paths

connecting them to other setts; and

• Outlier sett: These typically comprise one to three holes with small spoil heaps indicating

that they are not very extensive underground. They are used sporadically and are thought

to serve multiple functions, including allowing efficient and safe travel to important parts

of their home range.

Principles of Ecological Evaluation

3.8 The evaluation of ecological features and an assessment of likely impacts should be based on

available resources and the professional judgement of the ecologist concerned. Ecological value

of features should be undertaken in accordance with the approach outlined in the Guidelines

for Ecological Impact Assessment in the UK and Ireland (CIEEM, 2018).

3.9 A five-point evaluation scale has been applied to assist with the identification of key features of

ecological significance in relation to the proposed development. This is an arbitrary scale based

upon characteristics of ecological importance as listed in CIEEM (2018), which experience has

shown is effective at this level of assessment.

3.10 The value of an ecological feature is determined within a defined geographical frame of

reference as detailed in Table 2:

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Table 1: Classification of the value of ecological features and resources

Value Importance Species Habitat

Very High

International

A regularly occurring population of an internationally important species, which is threatened or rare in the UK, where the population is a critical part of a wider population or where a species is at a critical phase in its life cycle at this scale.

An internationally designated site including SAC, SPA, Ramsar, or one proposed for designation.

Sites supporting areas of priority habitats which are scarce at an international level of where it is needed to maintain the viability of a larger area at that level.

High National

A regularly occurring population / number of a nationally important species which is threatened, or rare, where the population is a critical part of wider population or where a species is at a critical phase in its life cycle at this scale. A regularly occurring population of a nationally important species on the edge of its natural range. A species assemblage of national significance.

A nationally designated site ie SSSI, or one that meets the published criteria.

Sites supporting areas of priority habitats which are scarce at a national level or where it is needed to maintain the viability of a larger area at that level.

MediumRegional /

County

A regularly occurring locally significant population of a species listed as being nationally scarce or a county Red Data book or BAP on account of its rarity. A regularly occurring, locally significant number of a regionally / county important species or where the population is a critical part of a wider population or where a species is at a critical phase in its life cycle at this scale. A species assemblage of regional or county significance.

Sites supporting a viable area of a priority habitat which is scarce at a regionally or county level or where is needed to maintain the viability of a larger area.

A County designated site or one that meets published criteria.

Local Nature Reserves, Local Wildlife Sites / potential Local Wildlife Sites at that level.

Low Local

A population of a species that is listed in a district BAP because of its rarity in the locality and a species assemblage of local or district significance. A regularly occurring, locally significant number of district importance or where the population is a critical phase in its life cycle at this scale.

Sites / features that are scarce within the local area or district. Areas of habitat considered enriching appreciably the habitat resource within the context of the locality or which buffer those of a more important nature.

Site Site Only

Species, which are not protected or rare in the local area and are not at a critical phase in its life cycle at this scale.

Habitats of very low importance and rarity but of ecological importance within the Site.

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3.11 Ecological features may also be deemed to be of negligible value if they are deemed to be of

very low ecological importance and / or rarity.

3.12 Ecological features may be defined as:

• Statutorily protected (Natura 2000, National Nature Reserves, Sites of Special Scientific

Interest and Local Nature Reserves) or locally designated sites (local Wildlife Sites or Sites

of Importance to Nature Conservation);

• Sites and features of biodiversity value not designated in this way such as ancient woodland;

or

• Species of biodiversity value or other significance, including those protected and controlled

by law.

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4. LEGISLATION AND PLANNING POLICY OVERVIEW

4.1 A summary of the legislative and planning context which has been used to inform this ecological

assessment is provided below.

Legislation

4.2 A number of tiers of legislation protect wildlife and habitats within England and Wales, the

highest of which being European legislation. A summary of relevant legislation is provided

below:

• The Wildlife and Countryside Act 1981 (as amended).

• The Natural Environment and Rural Communities Act 2006 (NERC).

• The Conservation of Habitats and Species Regulations 2017.

Policy

4.3 The planning policy framework that relates to nature conservation in Kings Cliffe is provided at

two levels; nationally through the National Planning Policy Framework (NPPF) and locally

through policies in the North Northamptonshire Joint Core Strategy 2011-2031.

Local Policy – North Northamptonshire Joint Core Strategy 2011-2031.

4.4 Specific nature conservation policies to consider are:

4.5 POLICY 4 – Biodiversity and Geodiversity

“A net gain in biodiversity will be sought and features of geological interest will be protected

and enhanced through:

a) Protecting existing biodiversity and geodiversity assets by:

i. Refusing development proposals where significant harm to an asset cannot be avoided,

mitigated or, as a last resort, compensated. The weight accorded to an asset will reflect its

status in the hierarchy of biodiversity and geodiversity designations;

ii. Protecting key assets for wildlife and geology, in particular the Upper Nene Valley Gravel

Pits Special Protection Area and Ramsar Site, from unacceptable levels of access and

managing pressures for access to and disturbance of sensitive habitats;

iii. Protecting the natural environment from adverse effects from noise, air and light

pollution;

iv. Where appropriate requiring developments to provide or contribute to alternative green

infrastructure (Policy 19); and

v. Ensuring that habitats are managed in an ecologically appropriate manner.

b) Enhancing ecological networks by managing development and investment to:

i. Reverse the decline in biodiversity and restore the ecological network at a landscape scale

in the Nene Valley Nature Improvement Area (NIA);

ii. Reverse habitat fragmentation and increase connectivity of habitats where possible by

structuring and locating biodiversity gain in such a way as to enlarge and/or connect to

existing biodiversity assets such as wildlife corridors;

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iii. Preserve, restore and create priority and other natural and semi-natural habitats within

and adjacent to development schemes.

c) Supporting, through developer contributions or development design, the protection

and recovery of priority habitats and species linked to national and local targets. Such measures

could include the retention of, and provision of areas of open green space, and hard and soft

landscaping to address habitat and visitor management.

d) Developments that are likely to have an adverse impact, either alone or in-

combination, on the Upper Nene Valley Gravel Pits Special Protection Area or other European

Designated Sites must satisfy the requirements of the Habitats Regulations, determining site

specific impacts and avoiding or mitigating against impacts where identified. Mitigation may

involve providing or contributing towards a combination of the following measures:

i. Access and visitor management measures within the SPA;

ii. Improvement of existing greenspace and recreational routes;

iii. Provision of alternative natural greenspace and recreational routes;

iv. Monitoring of the impacts of new development on European designated sites to inform

the necessary mitigation requirements and future refinement of any mitigation measures.”

4.6 POLICY 21 – Rockingham Forest

“The Rockingham Forest will be regenerated to increase carbon storage, strengthen biodiversity,

landscape character and green infrastructure, support a prosperous rural economy and provide

appropriate leisure and recreational opportunities.

This will be achieved through:

a) 40ha a year of new tree planting appropriately sited and using suitable species secured

through direct input of landowners, local communities and businesses, supported by funding

mechanisms including development contributions;

b) Linking fragmented habitats and protecting and reinforcing ancient woodland, particularly

in and around urban areas supported through landscaping associated with development

proposals;

c) Supporting rural economic development in accordance with Policy 25, with a focus on

woodland based activities including sustainable food and fuel production;

d) Protecting or enhancing tourism and recreation attractions and supporting new green

infrastructure and heritage attractions of a type and scale that can be accommodated by

existing or new infrastructure and which strike an appropriate balance between visitor

numbers and biodiversity, landscape, local amenity and heritage interests;

e) Enhancing green links in accordance with Policy 19 to enable residents of towns and villages

easy access to the forest on foot, horseback or bicycle.”

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Biodiversity Action Plan (BAP) and 2006 NERC Act Habitats and Species of Principal

Importance

4.7 In 2007, the UK Biodiversity Action Plan (BAP) Partnership published an updated list of priority

UK species and habitats covering terrestrial, freshwater and marine biodiversity to focus

conservation action for species and habitats in the UK. The UK Post-2010 Biodiversity

Framework succeeds the UK BAP. The Framework continues the conservation work initiated by

the UK BAP following the establishment of the Convention on Biological Diversity in 1992.

4.8 The purpose of the Framework is to set a broad structure for conservation across the UK until

2020. In summary:

• To set out a shared vision and priorities for UK-wide activities, in a framework jointly owned

by the four countries, and to which their own strategies will contribute;

• To identify priorities at a UK scale which will help deliver biodiversity targets and the EU

Biodiversity Strategy;

• To facilitate the aggregation and collation of information on activity and outcomes across

all countries of the UK; and

• To streamline governance arrangements for UK-wide activities.

4.9 The habitats and species are identified as Habitats and Species of Principal Importance for the

conservation of biological diversity in England under Section 41 of the 2006 Natural

Environment and Rural Communities (NERC) Act. The NERC Act and NPPF make these species

had habitats a material consideration in the planning process.

4.10 The Northamptonshire Local Biodiversity Action Plan (LBAP) produced in 2008, lists two priority

habitats of particular relevance to this Site, namely lowland meadows and lowland deciduous

woodland. The LBAP also lists many priority species including amphibians, such as GCN, reptiles

such as common lizard, grass snake and adder and many bird species, which have relevance to

this Site. The presence of these species and / or habitats within the Site is considered within this

report.

4.11 The LBAP contains objectives and targets for the species and habitats identified above. They

should be considered in relation to the Proposed Development in order to identify opportunities

for avoidance, mitigation and enhancement.

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5. DESK STUDY RESULTS

5.1 The full information collected during the desk study from the NBRC and NBG is available upon

request and summarised below.

Sites of Nature Conservation Interest

5.2 The Site itself is not subject to any statutory or non-statutory nature conservation designation.

5.3 The records search identified two statutory protected sites and 16 non-statutory sites within

2km of the Site, as summarised in Table 2:

Table 2: Summary of Ecology Designations

Designated

Site Name

Designation Proximity

to Project

Description

Bedford

Purlieus

SSSI/ NNR 0.35km

north

214.29 ha of ancient woodland supporting a variety of

woodland community types which are largely restricted

nationally to lowland England. Noted for its diversity of

herbaceous plants and associated fauna, and for the wide

range of coppice woodland types.

Kings Cliffe

Banks

SSSI 2.5km

south-west

7.74ha This site is a small, disused quarry with a ‘hills and

holes’ topography. A high quality, species-rich closed

calcareous grassland sward has developed on the thinner

soils. Neutral grassland and scrub communities are

associated with deeper soils.

Great Byards

Sale

LWS 0.35km

south

18.4ha of ancient woodland with a well-developed oak-ash

canopy with 15 ancient woodland species.

Little Morton

Sale

LWS 0.4km south

east

12.3ha of semi-natural ancient woodland with 14 ancient

woodland indicator species.

Fair Oak Sale

Quarry

LWS 0.75km

south

11.2ha of open mosaic habitat with a large extent of early

successional species rich calcareous grassland.

Great Morton

Sale

LWS 0.8km

south

12.9ha of ancient woodland ground flora contains large

areas of dogs mercury and bluebell. Contains 13 ancient

woodland indicator species.

Great Morton

Sale

Grassland

LWS 0.8km

south

0.25ha of calcareous grassland with 19 calcareous

grassland species developed on turf covering a road of the

World War 2 airfield.

Fair Oak Sale LWS 0.8km

south

3.4ha of ancient semi-natural woodland with 14 ancient

woodland indicator species.

Ring Haw

Quarry

Grassland

LWS/LGS 1km

south-east

5.2ha with a mosaic of habitats including calcareous

grassland, scrub and woodland.

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Designated

Site Name

Designation Proximity

to Project

Description

Great Morton

Sale Disused

Railway

LWS 1.2km

south

0.94ha of woodland developing on a disused railway that

runs between two ancient woodlands.

Little Morton

Sale Quarry

LWS/ LGS 1.4km

south

4.38ha disused quarry area with a mixture of habitats

mainly early successional patches of species rich

calcareous grassland and developing woodland.

Little Morton

Sale Quarry

East

LWS/LGS 1.5km

south-east

3.12ha ex-quarry with a rich calcareous grassland flora

with 15 strong and 9 standard calcareous grassland

indicator species.

Ring Haw

Quarry Gullet

LWS/LGS 1.5km

south-east

2.4ha an old sand and limestone gullet that has retained

areas of bare ground and developed areas of species rich

grassland with pools and scrub.

Ring Haw

Green Lane

LWS 1.5km

south-east

2.7ha of ancient by way with a thick and varied hedge

containing a variety of ancient woodland species.

Ring Haw

Woodland

LWS 1.5km

south-east

7.2ha of ancient woodland predominantly ash and oak

with a good number of other tree species and ancient

woodland indicators.

Key:

SSSI: Site of Special Scientific Interest

NNR: National Nature Reserve

LNR: Local Nature Reserve

LWS: Local Wildlife Site

LGS: Local Geological Site

Protected Species

5.4 Below provides a summary of protected species, which have been recorded within 2km of the

Site. It should be noted that the absence of records should not be taken as confirmation that a

species is absent from the search area.

5.5 Records of amphibians, badgers, bats, birds, dormice, invertebrates, protected / notable plants

and reptiles were recorded within 2km of the Site. No notable protected species were recorded

within the Site.

Amphibians

5.6 Three records of great crested newt Triturus cristatus (“GCN”) were received for within 2km of

the Site, the closest record was at Fair Oak Sale Quarry in 1985. Other amphibians recorded

within 2km of the Site were common toad Bufo bufo, palmate newt Lissotriton helveticus,

smooth newt Lissotriton vulgaris and common frog Rana temporaria. No records of amphibians

were received for within the Site.

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Badgers

5.7 21 records of badgers were received for within 2km of the Site. The closest record, dated 2018,

is located approximately 0.3km south of the Site within Great Byards Sale wood. Seven records

were from within Bedford Purlieus 0.3km north. No records of badgers were received for within

the Site.

Bats

5.8 Six species of bat have been recorded within 2km of the Site, namely common pipistrelle

Pipistrellus pipistrellus, soprano pipistrelle Pipistrellus pygmaeus, brown long-eared bat

Plecotus auritus, whiskered/brant’s bat Myotis sp., noctule Nyctalus noctula and barbastelle

Barbastella barbastellus. The closest record, dated 2016, relates to common pipistrelle, soprano

pipistrelle, noctule and barbastelle all found to be roosting within the Old Sulehay Wood. No

records of bats were received for within the Site.

Birds

5.9 50 species of protected or notable species of the birds were received for within 2km of the Site.

The majority of records related to Bedford Purlieus NNR and SSSI. No records of protected or

notable bird species were received for within the Site.

5.10 Table 3 summarises the species of birds recorded within 2km of the Site.

Table 3: Summary of bird species recorded within desk study

Species / Group No. of Records

Closest record

Most Recent record

Legislation / Conservation Status

Dunnock Prunella modularis

140.2km

north east2019

CRoW, WCA 1i, BoCC_Amber

Cuckoo Cuculus canorus

15 1.4km east 2018 NERC S.41, BoCC Red

Lesser Spotted Woodpecker Dendrocopos minor

391.5km north

2013 NERC S.41

Snipe Gallinago gallinago

4 1.8km east 2018 BoCC Amber

Red Kite Milvus milvus

300.25km

north east2018 BDIR1, CRoW, WCA 1i

Lapwing Vanellus vanellus

31.9km north

2016BDIR1, NERC S.41, BoCC Red

Barm Owl Tyto Alba

21.7km

south west1996 CRoW, WCA 1i

Fieldfare Turdus pilaris

121.5km north

2013 WCA 1i, BoCC Red

Turtle Dove Streptopelia turtur

5 1.7km east 2019 NERC S.41, BoCC_Red

Marsh Tit Poecile palustris

450.65km

north east2013 NERC S.41, BoCC_Red

Hen Harrier Circus cyaneus

3 2km south 2002BDIR1, CRoW, WCA 1i, BoCC Red

Skylark Alauda arvensis

1.4 km north east

2018 NERC S.41, BoCC_Red

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Species / Group No. ofRecords

Closest record

Most Recent record

Legislation / ConservationStatus

Lesser RedpollAcanthis cabaret

110.65 km

north east2011 NERC S.41, BoCC_Red

Key: NERC S.41: Natural Environment and Rural communities Act 2006, Section 41; habitats and species of principle importance in England. BoCC Red: Birds of Conservation Concern Red. BoCC Amber: Birds of Conservation Concern Amber. BDIR1: Birds Directive, 2009. Crow: Countryside Rights of Way Act, 2000:Protection of certain birds and animals amended) WCA 1i: Wildlife and Countryside Act (1981) (as amended); Birds protected by special penalties at all times, species specific.

Dormice

5.11 53 records of dormice were received for within 2km of the Site. The closest record, dated 2014,

is located within Bedford Purlieus where a reintroduction program was conducted in 2001 by

the Peoples Trust for Endangered Species (PTES). The 2019 PTES dormouse report states that

the re-introduction program at Bedford Purlieus was successful and animals are continuing to

disperse. No records of dormice were received for within the Site.

Invertebrates

5.12 Many records of notable or protected invertebrates were received for within 2km of the Site

including many UK BAP and NERC section 41 priority species such as white ermine moth

Spilosoma lubricipeda and oak hook-tip moth Watsonalla binaria. There were also a number of

notable rare and scarce invertebrate species such as barley flee beetle Phyllotreta vittula.

Butterflies such as Purple Emperor Apatura iris, Pearl-bordered Fritillary Boloria selene and

chequered skipper Carterocephalus palaemon all of which are Schedule 5 of the Wildlife and

Countryside Act (1981) species and were all recorded within 2km of the Site.

Plants

5.13 Many records of protected or notable plants were received for within 2km of the Site. None of

those recorded pertained to the Site. Limestone grassland indicator species such as Quaking

grass Briza media and stinking hellebore Helleborus foetidus along with woodland indicator

species such as bluebell Hyacinthoides non-scripta, wood-sorrel Oxalis acetosella and hard fern

Blechnum spicant were all recorded within 2km of the Site. Bluebells were recorded within

Great Morton sale 0.8km south. This species is protected under Schedule 8 of the Wildlife and

Countryside Act (1981) (as amended) against commercial exploitation only.

Reptiles

5.14 Four species of reptiles have been recorded within 2km of the Site, namely adder Vipera berus,

grass snake Natrix natrix, common lizard Zootoca vivipara and slow worm Anguis fragilis. The

closest record, dated 1985, relates to a sighting of an adder and common lizard within Fair Oak

Sale 0.8km south.

Other Species

21-0395 PEAR V1 JA 070721

Page 19 of 34

5.15 Brown hare Lepus europaeus, otter Lutra lutra and water vole Arvicola amphibious were also

recorded within 2km of the Site.

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6. PHASE 1 HABITAT SURVEY RESULTS

6.1 The Phase 1 habitat survey was conducted on 22nd June 2021 in good weather conditions (100%

cloud cover, 19-24 °C, Beaufort scale 2-3).

Field Survey Limitations

6.2 There were no limitations to the survey.

Habitat Descriptions

6.3 The full Phase 1 habitat survey map detailing the location of the above habitats and other

features of ecological interest with target notes is presented at Appendix 1. The habitat

descriptions below should be read in conjunction with this plan and any associated Target

Notes.

6.4 Habitats identified during the Phase 1 habitat survey are detailed below in alphabetical order

(not in order of ecological importance):

• Bare ground

• Dense scrub

• Hardstanding

• Tall ruderal

Bare ground

6.5 The majority of the Site comprised the earth bund which was sparsely vegetated with ruderal

and ‘weed’ type plants, common to disturbed ground. The bund was approximately 2-2.5m in

height and 5m-6m in width. The bund directly abutted the boundary fence which formed the

southern and south-western boundaries of the Site.

6.6 Species present within the bund included fumitory fumaria officinalis, wild parsnip Pastinaca

sativa, field pennycress Thlaspi arvense, scented mayweed Matricaria chamomilla, cleavers

Gallium aparine, creeping cinquefoil Potentilla reptans, creeping buttercup Ranunculus repens,

bristly oxtongue Helminthotheca echioides and teasel Dipsacus fullonum.

6.7 This habitat was considered to be of site only ecological value.

21-0395 PEAR V1 JA 070721

Page 21 of 34

Figure 3: Sparsely vegetated soil bund within the Site

Dense scrub

6.8 In the area between the bund and the boundary fence, patches of dense scrub had developed.

6.9 Species present included blackthorn Prunus spinosa, bramble Rubus fruticosus, dog rose Rosa

canina and hawthorn Crataegus monogyna.

6.10 This habitat was considered to be of site only ecological value.

Figure 4: Slopes of bund against fence vegetated with dense scrub

Hardstanding

6.11 The Wider Survey Area comprised hardstanding from crushed aggregates and bare earth

following the historic materials screening operations. There were piles of graded material

heaped within the Wider Survey Area and following recent heavy rainfall the occasional

ephemeral pool.

6.12 This habitat was considered to be of negligible ecological value.

21-0395 PEAR V1 JA 070721

Page 22 of 34

Figure 5: Wider Survey Area with piles of graded material

Standing water

6.13 Immediately to the south of the Site was a rectangular shaped pond, shown as P1 on the plan

presented at Appendix 1.

6.14 This pond was heavily vegetated with rushes and curly dock Rumex crispus and was known to

dry frequently. This was further evidence by large cracks present within the pond’s bare earth

base. This pond had been subject to GCN surveys in 2014 when a small population of GCN (peak

count of 7) was recorded. Further survey work was undertaken for this species in 2020, but this

pond was not surveyed as it was dry.

6.15 This habitat was considered to be of moderate ecological value.

Figure 6: P1 to the south of the Site

21-0395 PEAR V1 JA 070721

Page 23 of 34

Figure 7: Cracked base of P1

Tall ruderal

6.16 Interspersed with the patches of dense scrub were areas of tall ruderal habitat, which was

located on the slopes of the bund closest to the fence.

6.17 Species present included teasel, spear thistle Cirsium vulgare, rosebay willowherb Chamerion

angustifolium, poppies Papaver sp. and hogweed Heracleum sphodylium.

6.18 This habitat was also present on the western and southern sides of the boundary fence. The

western side had recently been planted with some conifer species to provide screening. In this

area, hogweed and thistle were present along with broadleaved dock Rumex obtusifolius,

scarlet pimpernel Anagallis arvensis, meadow grass Poa annua and Yorkshire fog Holcus

lanatus.

6.19 Along the southern boundary the tall ruderal habitat included a ditch, which was barely holding

water. Rosebay willowherb and creeping buttercup were dominant in this area along with some

charlock Sinapis arvensis, tufted hairgrass Deschampsia cespitosa and rushes Juncus sp. There

was also some scrub species in this area, which had grown under the fence line.

6.20 This habitat was considered to be of low ecological value.

21-0395 PEAR V1 JA 070721

Page 24 of 34

Figure 8: Ditch with tall ruderal vegetation on southern side of the Site boundary.

Evidence of Protected Species and Other Faunal Interest.

6.21 There were no obvious mammal holes within the Site, possibly due to the fact that the bund

and Wider Survey Area was so compacted from the historic works digging by an animal would

be quite difficult.

6.22 Bird species noted within the Site and Wider Survey Area included skylark Alauda arvensis and

linnet Linaria cannabina.

6.23 A smooth newt Lissotriton vulgaris was seen within one of the ephemeral pools within the

Wider Site Area.

21-0395 PEAR V1 JA 070721

Page 25 of 34

Figure 9: Smooth newt within pool in the Wider Site Area

21-0395 PEAR V1 JA 070721

Page 26 of 34

7. EVALUATION OF ECOLOGICAL CONTEXT

The Site

7.1 The Site is located within the National Character Area (NCA) known as Rockingham Forest. The

Site was surrounded by a predominantly rural landscape with arable farmland to the west and

south of the Site. A mosaic of habitatssurrounded the Site to the north, east and south including

habitats such as ancient woodland, grazing pasture, ponds and calcareous grassland habitats,

much of these habitats were formed by disused quarry workings allowed to naturally

regenerate on a limestone soil.

7.2 The connectivity of the Site is good to the wider landscape for many species through a network

of hedgerows and woodland blocks.

Statutory Sites

7.3 The Site itself is not subject to any nature conservation designation.

7.4 The nearest statutory designated nature conservation site is Bedford Purlieus SSSI and NNR

located 0.3km north of the Site, designated due to its ancient woodland habitat supporting a

variety of woodland community types including ancient coppice.

7.5 Impact Risk Zones (IRZs) are a tool developed by Natural England to provide an initial

assessment of the potential risks to SSSIs. The Site falls within one IRZ for the Bedford Purlieus

SSSI. However, given the nature of the Proposed Development, no further consultation is

required.

Non-statutory Sites

7.6 The nearest non-statutory designated nature conservation site is Great Byards Sale which is a

Local Wildlife Site 360m to the south of the Site. There is a Potential Wildlife Site, Great Byards

Sale Quarry, which lies immediately to the south-west of the Site.

7.7 Based on the nature of the Proposed Development and minimal impact there is no expected to

be any adverse effects on these sites.

Habitats

7.8 The habitat to be lost within the Site is bare earth, which will be planted as per the Planting

Design. This will include the planting of native species of shrub on the western and southern

boundary of the bund with a wildflower seed mix on the western and northern sides of the

bund.

7.9 The Wider Survey Area will remain as hardstanding.

Off-site Habitats

7.10 The pond immediately to the south of the Site (P1) was considered to be of moderate ecological

value and will not be impacted by the Proposed Development. The creation of more scrub and

grassland within the Proposed Development will serve to promote connectivity to P1.

Faunal

7.11 The desk study located a variety of protected species records for the local area.

21-0395 PEAR V1 JA 070721

Page 27 of 34

7.12 The Site has been assessed on the suitability of the habitats to support such protected species

and the likelihood of those species being present. Table 5 provides a summary account of

protected species within the Site and local area.

7.13 In the absence of mitigation and further assessment the impacts on each species have been

assessed using the following scale:

Table 4: Impact Levels and Criteria

Classification Criteria

Negative (Significant) Likely to create a significant effect, including loss, or long-term irreversible damage on the integrity / status of a valued ecological feature

Negative (non-significant) Likely to create a negative effect without causing long-term or irreversible damage on the integrity / status of a valued ecological feature

Neutral Effects are either absent or such that no overall net change to the ecological feature occurs.

Positive (non-significant) Likely to create a beneficial effect on an ecological feature, or providing a new (lower value) ecological feature, without improving its conservation status markedly

Positive (significant) Activity is likely to create a significant beneficial effect, including long-term enhancement and favourable condition of an existing valued ecological feature, or creation of a new valued ecological feature.

21-0395 PEAR V1 JA 070721

Page 28 of 34

Table 5: Summary of Protected Species Associated with the Site

Species Recorded in Desk Study Evidence on Site

Potential on Site to Support Presence

Description of likely Impact on Species

Likely Impact

Amphibians Yes – great crested newts at 1.2km from the Site. Common toad, palmate newt, smooth newt and common frog all recorded with 2km of the Site.

Yes – smooth

newt

Yes – there is terrestrial habitat in the form of dense scrub and tall ruderal vegetation.

The creation of grassland and scrub will provide additional foraging habitat.

Neutral

Badgers Yes – there were several records of badgers with 2km of the Site, the closest being within Great

Byards Sale.

None Yes –There is potential foraging habitat within the Site.

The creation of grassland and scrub will provide additional foraging habitat.

Neutral

Bats Yes – several common species including soprano, common pipistrelle and brown-long eared bat.

Three less common species Whiskered bat, barbastelle and noctule bat have also been recorded

within 2km of the Site.

None No The Proposed Development will provide potential foraging habitat for bats in the form of scrub / grassland

Neutral

Birds Yes – a large number of farmland and garden birds. Yes – common species

Yes – there is potential for birds to be utilising the dense scrub for nesting

The Proposed Development will increase the scrub habitat within the Site.

Positive (non-significant)

Dormouse Yes – 53 recorded within Bedford Purlieus NNR 1km north of the Site.

None No there is no potential for this species within the Site

No woodland is to be removed as part of the Proposed development.

Neutral

Invertebrates Yes – many species of nationally and European protected species within 2km of the Site.

Yes- peacock butterfly

Yes –the Site has potential to support many invertebrates.

The creation of grassland and scrub will provide additional foraging habitat.

Neutral

Reptiles Yes – adder, grass snake, common lizard and slowworm have all been recorded within 2km of the Site.

None Yes – there is some potential for reptiles to be present within the tall ruderal and dense scrub

The Proposed Development will increase the scrub and grassland habitat within the Site.

Positive (non-significant)

8. RECOMMENDATIONS

Overview

8.1 Recommendations have been provided within this report that will safeguard the existing

ecological interest features within the Site. Wherever possible, measures to enhance ecological

and biodiversity value have also been set out.

8.2 Based on the survey undertaken to date and the recommendations for further surveys, the

presence and potential presence of protected species has been given due regard.

8.3 In conclusion, implementation of the measures provided within this report enable the Proposed

Development to accord with national and local planning policy for nature conservation.

Habitats

8.4 The Proposed Development will result in the creation of better quality habitats in the form of

scrub grassland. This will provide foraging, sheltering and nesting opportunities for a variety of

species.

Pollution Prevention

8.5 During construction, safeguards should be put in place in accordance with the Environment

Agency’s Pollution Prevention Guidelines (2013). Whilst these guidelines are no longer current

they provide good practice guidelines to follow. Following these safeguards will reduce

potential pollution events to nil, minimising harm to wildlife associated with the watercourse.

Safeguards will include:

• Storage areas of chemicals, fuels, etc. will be located well away from the watercourse;

• Water washing of vehicles, for example those carrying concrete, should be carried out in a

contained area so as to avoid contaminated water entering the watercourse; and

• Refuelling of plant will take place in a designated area, preferably on an impermeable

surface.

Species

Amphibians

8.6 The pond adjacent to the Site (P1) is known to have historically supported a GCN population.

On the basis that no further earthworks are required and the Proposed Development will

require landscape planting only. As such, the Proposed Development is not considered to have

an impact on P1 and will increase suitable terrestrial habitat for this species. No further

recommendations are to be made.

8.7 In the event that any further earth moving is required, additional consideration for this species

will be required and an ecologist should be consulted.

Badger

8.8 No evidence of Badger activity was found within or immediately adjacent to the Site. Badgers

readily establish new setts, therefore should any evidence of badger activity be found prior to

construction, a member of the Lockhart Garratt ecology team contacted for advice.

Nesting Birds

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Page 30 of 34

8.9 As the scrub may potentially offer breeding opportunities for birds’ works affecting these

habitats should take place outside the bird breeding season (March to August inclusive). It is

not expected that any scrub If in the event works need to proceed within this period then

specialist advice from a suitably qualified ecologist should be sought.

General

8.10 If in the event any protected species (e.g. amphibians, badgers, bats, reptiles, or nesting birds)

are encountered as part of the works, then all works must stop, with advice sought immediately

from Lockhart Garratt (01536 408840).

21-0395 PEAR V1 JA 070721

Page 31 of 34

9. REFERENCES AND BIBLIOGRAPHY

Bat Conservation Trust (2016) Bat Surveys: Good Practice Guidelines 3rd Edition.

British Standards Institution (2013). British Standard 42020:2013. Biodiversity – Code of Practice

for planning and development.

CIEEM (2018) Guidelines for Ecological Impact Assessment in the UK and Ireland: Terrestrial,

Freshwater, Coastal and Marine. Chartered Institute of Ecology and Environmental

Management, Winchester.

CIEEM (2017) Guidelines for Preliminary Ecological Appraisal (GPEA).

English Nature (2001) Great Crested Newt Mitigation Guidelines.

Froglife (1999) Reptile Survey – Advice Sheet 10.

JNCC (2010). Handbook for Phase 1 Habitat Survey: A technique for environmental audit.

JNCC (1998) The Herpetofauna Worker’s Manual.

Langton et al (2001) The Great Crested Newt Conservation Handbook.

Mammal Society (2013) How to Find and Identify Mammals, 2nd Edition.

Natural England (2004) Bat Mitigation Guidelines.

Oldham R.S., Keeble J., Swan M.J.S & Jeffcote M. (2000). Evaluating the suitability of habitat for

the Great Crested Newt (triturus Cristatus). Herpetological Journal 10(4), 143-155.

21-0395 PEAR V1 JA 070721

Page 32 of 34

10. APPENDICES

21-0395 PEAR V1 JA 070721

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Appendix 1: Phase 1 Habitat Map

Ref: 21-0371

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P1

504050.000000

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5029

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2982

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8300

29

8350

29

8350

29

Greystones HouseBurford Road

Chipping NortonOxfordshire OX7 5UY

01608 656167

Reproduced with the permission of The Controller of Her Majesty's Stationery Office Crown Copyright (c) Licence number: AL 52281A000Lockhart Garratt Ltd 8 Melbourne House, Corbygate Business Park, Weldon, Corby, Northants NN17 5JG. For identification purposes only. Not to be reproduced without the permission of Lockhart Garratt Ltd.

7 - 8 Melbourne HouseCorbygate Business Park

Weldon, CorbyNorthamptonshire NN17 5JG

01536 408840www.lockhart-garratt.co.uk

TITLE:

PROJECT/SITE:

CLIENT:

DATE:

APPROVED BY:

VERSION:

MAP REF:

Preliminary Ecological AppraisalRecycling Centre Bund

Rockingham Forest ParkRockingham Forest Park

3297/02/21-0371v1

25/06/21 @A3JA SM

1:1,000SCALE:

PRODUCED BY:

0 50 10025 Metres

Legend.

Wet Ditch = 80m

Woodern Close Board Fence= 235m

Bare Ground = 0.484ha

Hardstanding = 0.014ha

Site Boundary = 0.828ha

Standing Water ( Off Site)0.151ha=

Tall Ruderal = 0.304ha

!! !!

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Dense Scrub = 0.026ha

21-0395 PEAR V1 JA 070721

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