extended phase 1 habitat survey south of tytton lane east...

Extended Phase 1 Habitat Survey Quadrant 1: Land either side of the A16, South of Tytton Lane East, Boston For Chestnut Homes Land Ltd. Delta-Simons Project No. 13-0525.02

This Report was issued in April 2014 and prepared by:

Delta-Simons Environmental Consultants,

3 Henley Office Park, Doddington Road, Lincoln, LN6 3QR

Tel: 0870 0400 012 Fax: 01522 882567 www.deltasimons.com

Reports printed by Delta-Simons are printed on 100% recycled paper

Extended Phase 1 Habitat Survey Quadrant 1: Land either side of the A16, South of Tytton Lane East, Boston For Chestnut Homes Land Ltd. Delta-Simons Project No. 13-0525.02

EXECUTIVE SUMMARY

EXTENDED PHASE 1 HABITAT SURVEY

QUADRANT 1: LAND EITHER SIDE OF THE A16, SOUTH OF TYTTON LANE EAST,

BOSTONFOR

CHESTNUT HOMES LAND LTD.

DELTA-SIMONS PROJECT No. 13-0525.02

Purpose Delta-Simons Environmental Consultants Limited (‘Delta-Simons’) was instructed by Chestnut Homes Land Ltd (the ‘Client’) to undertake an Extended Phase 1 Habitat survey of Quadrant 1: Land either side of the A16, South of Tytton Lane East, Boston in Lincolnshire. The survey was undertaken on 16th September 2013. Habitats and the potential of the Site for protected species were assessed during the Extended Phase 1 Habitat Survey. The survey was undertaken in order to inform a planning application for the Site.

Current Site Status The Site is characterised by arable fields separated by a series of wet and dry ditches with areas of scattered broadleaved trees and boundary hedgerows.

Proposed Development

The proposals comprise a sustainable mixed-use scheme including new community stadium for Boston United Football Club, housing, retail, commercial and leisure uses.

Results: Habitats on-Site Habitats within Land Adjoining the Site

∆ Broadleaved plantation;

∆ Scattered broadleaved trees;

∆ Dense scrub;

∆ Ditch – standing water;

∆ Arable;

∆ Intact species-poor hedgerow;

∆ Defunct species-poor hedgerow;

∆ Dry ditch; and

∆ Hardstanding – cycle/footpath.

The Site is situated within a predominately agricultural setting with further arable fields and a network of hedgerows characterising the surrounding landscape. Tytton Lane lies adjacent to the northern Site boundary with residential housing beyond. Further residential housing is situated to the west and beyond Towns Drain to the south of the western area of the Site.

Recommendations The detailed recommendations set out within the Report are summarised below: Recommendation 1 (Nesting Birds): Any habitat removal or felling works to be undertaken to the woodland, scattered trees, dense scrub, hedgerows and dry ditches at the Site should be performed either before early March or after late July in order to avoid affecting any birds during the main period in which they are nesting. Conflict with the development can be avoided by clearing the Site of any suitable nesting habitat outside of the breeding period in advance of any proposed works, and delays due to potential ground nesting birds can also be avoided by cutting back the grassland outside the nesting bird season and then maintaining the grassland at a height of approximately 15 cm in order to discourage birds from nesting. If, however, Site clearance works are deemed necessary during the nesting period an experienced ecologist will be required to check the Site

habitats to confirm that no nesting birds will be affected by the proposed works. Recommendation 2 (Bats): Although it is not known which trees and hedgerows are to be retained following the development, it is recommended that lighting along these linear features, if retained, is avoided and that lighting as part of the proposed development is kept to a minimum in order to avoid discouraging any bats within the local area from using the Site for foraging and commuting. Since the Extended Phase 1 Habitat survey was completed in September 2013, the proposals have been updated and, therefore, a Bat Roost Potential survey was recommended of two properties due to be demolished to facilitate an access road onto the Site from London Road on the western Site boundary. The Bat Roost Potential survey was undertaken in March 2014 and the results of the survey are outlined within the report (Delta-Simons 13-0525.04). Recommendation 3 (Badgers & Brown Hare): A further badger survey should be conducted before construction works start, to determine whether or not the disused setts present on-Site are still inactive. If a sett is found to be active it may be necessary to apply for a licence from Natural England to close the sett. It should be noted that if the sett is found to be active, a survey of the wider area will then be required to inform the licence application, and once the licence has been granted, a sett cannot be closed from December to June (inclusive) in order to avoid potentially disturbing cubs. Until a further survey is undertaken, no construction works should take place within 30 m of the sett. It is recommended as a precautionary measure that either no excavations are left uncovered overnight during the construction phase of the works or mammal ramps are installed in order to prevent these species from becoming trapped. Recommendation 4 (Pollution Prevention): Contractors should adhere to the recommendations outlined in Pollution Prevention Guideline 5 (PPG 5): Works in, near or liable to affect watercourses (Environment Agency n.d.) to minimise the risk of pollution events to the water course during construction. Recommendation 5 (Water Voles): It is recommended that a water vole survey is carried out to determine their presence or likely absence within the ditch on-Site and drains immediately off-Site. The survey can be carried out from mid-April to September (inclusive) when the voles are most active. Recommendation 6 (Common Ragwort): Care should be taken during Site clearance works in order to prevent the spread of common ragwort to off-Site habitats. Recommendation 7 (Planning and Ecological Enhancements): Following the issue of the National Planning Policy Framework (NPPF, 2012) by the Department for Communities and Local Government (DCLG), “The planning system should contribute to and enhance the natural and local environment by: Minimising impacts on biodiversity and providing net gains in biodiversity where possible, contributing to the Government’s commitment to halt the overall decline in biodiversity…”; and, therefore, for this particular development the use of native plant species sourced from local nurseries is recommended in landscape proposals to enhance foraging opportunities for

local birds and bats, by increasing the invertebrate diversity on-Site. A species list of recommended trees and shrubs is included within the recommendations section of this Report.

This Extended Phase 1 Habitat Survey Executive Summary is intended as a summary of the assessment of the Site based on information received by Delta-Simons at the time of production. This Executive Summary should be read in conjunction with the full Report.

TABLE OF CONTENTS

1.0 INTRODUCTION ...................................................................................................................... 1 1.1 Purpose and Scope of the Survey ....................................................................................... 1 1.2 Site Description .................................................................................................................... 1 1.3 Proposed Developments ...................................................................................................... 2

2.0 LEGISLATION .......................................................................................................................... 3 2.1 Birds ..................................................................................................................................... 3 2.2 Amphibians ........................................................................................................................... 3 2.3 Reptiles ................................................................................................................................ 3 2.4 Bats ...................................................................................................................................... 4 2.5 Badgers ................................................................................................................................ 4 2.6 Water Voles .......................................................................................................................... 4 2.7 Plant Species Prohibited from Release into the Wild ........................................................... 5 2.8 Hedgerow ............................................................................................................................. 5 2.9 Planning ............................................................................................................................... 5

3.0 METHODOLOGY ..................................................................................................................... 6 3.1 Data Search ......................................................................................................................... 6 3.2 Review of Previous Surveys ................................................................................................ 6 3.3 Extended Phase 1 Habitat Survey ....................................................................................... 6

3.3.1 Birds .............................................................................................................................. 7 3.3.2 Amphibians ................................................................................................................... 7 3.3.3 Reptiles ......................................................................................................................... 7 3.3.4 Bats ............................................................................................................................... 7 3.3.5 Badgers ......................................................................................................................... 7 3.3.6 Water Voles .................................................................................................................. 8 3.3.7 Other Protected Species ............................................................................................... 8 3.3.8 Plant Species Prohibited from Release into the Wild ................................................... 8 3.3.9 Hedgerows .................................................................................................................... 8 3.3.10 Surrounding Area ........................................................................................................ 8

4.0 RESULTS ................................................................................................................................. 9 4.1 Data Search ......................................................................................................................... 9

4.1.1 Habitats ......................................................................................................................... 9 4.1.2 Species ......................................................................................................................... 9

4.2 Review of Previous Surveys .............................................................................................. 10 4.3 Extended Phase 1 Habitat Survey – Site ........................................................................... 11

4.3.1 Birds ............................................................................................................................ 13 4.3.2 Great Crested Newts .................................................................................................. 14 4.3.3 Reptiles ....................................................................................................................... 15 4.3.4 Bats ............................................................................................................................. 15 4.3.5 Badgers ....................................................................................................................... 15 4.3.6 Water Vole .................................................................................................................. 15 4.3.7 Other Protected Species ............................................................................................. 16 4.3.8 Plant Species Prohibited from Release into the Wild ................................................. 16 4.3.9 Hedgerows .................................................................................................................. 16

4.4 Extended Phase 1 Habitat Survey – Land Adjoining the Site ............................................ 16 5.0 CONCLUSIONS AND RECOMMENDATIONS ...................................................................... 17

5.1 Conclusions ........................................................................................................................ 17 5.2 Recommendations ............................................................................................................. 18

6.0 LIMITATIONS OF SURVEY ................................................................................................... 21 6.1 Limitations .......................................................................................................................... 21 6.2 Disclaimer ........................................................................................................................... 21

Tables

Table 1 Habitat Suitability Index Assessment

Figures

Figure 1 Site Location Map

Figure 2 Extended Phase 1 Habitat Survey

Figure 3 Proposed Development Plan

Appendices

Appendix I References

Appendix II Categorisation of Bat Roosting Potential – Trees

Appendix III Data Search Results

Appendix IV Target Notes

Appendix V Photographs

EXTENDED PHASE 1 HABITAT SURVEY

QUADRANT 1: LAND EITHER SIDE OF THE A16, SOUTH OF TYTTON LANE

EAST, BOSTON

FOR

CHESTNUT HOMES LAND LTD.

DELTA-SIMONS PROJECT No. 13-0525.02

1.0 INTRODUCTION

1.1 Purpose and Scope of the Survey

Delta-Simons Environmental Consultants Limited (‘Delta-Simons’) has been

requested by Signet Planning (the ‘Planning Consultant’) on behalf of Chestnut

Homes Land Ltd. (the ‘Client’) to undertake an Extended Phase 1 Habitat Survey of

Quadrant 1: Land either side of the A16, South of Tytton Lane East, Boston in

Lincolnshire (hereafter referred to as the ‘Site’). In addition, public land immediately

surrounding the Site was surveyed. The survey was undertaken in order to inform a

planning application for the Site.

The aims of the Extended Phase 1 Habitat Survey were to:

∆ Identify habitat types on the Site using the standardised Phase 1 Habitat

Survey technique;

∆ Identify areas of potential for protected species/species of conservation

concern within the Site;

∆ Identify areas of potential for protected species/species of conservation

concern immediately outside the Site;

∆ Prepare a Phase 1 Habitat Survey Plan of the Site; and

∆ Propose recommendations for further surveys, where necessary.

The Site location and the area surveyed are shown in Figure 1.

1.2 Site Description

The Site is centred at Ordnance Survey (OS) grid reference TF 3225 4153 to the

south of Tytton Lane within the southern extent of Boston. The Site is divided into

two separate areas, one to the east of the A16 and one to the west of the A16. The

two sites cover a total area of approximately 28 hectares. To the west of the A16 the

land comprises three arable fields, divided by dry ditches and a defunct hedgerow.

The northern and western boundaries are marked by a combination of garden

Extended Phase 1 Habitat Survey Quadrant 1: Land either side of the A16, South of Tytton Lane East, Boston Delta-Simons Project No. 13-0525.02 Page 2

hedges, fences and walls. Farm buildings are located to the south-western corner of

the Site. Towns Drain runs adjacent to the southern boundary. The A16 forms the

eastern boundary. Running parallel to the A16 were a wet ditch and hardstanding

cycle/footpath. Two areas of young broadleaved plantation were also present along

the eastern extent of the Site.

An arable field characterises the land to the east of the A16 with housing beyond the

northern extent of the Site. Species poor hedgerows defined the eastern and

southern extent of the Site. A dry ditch and hedgerow bounded an area of dense

scrub at the western extent of the Site. A dry ditch defined the western boundary.

The land appeared well drained and did not support any standing water at the time of

the survey.

The Site is situated on the edge of a predominately urban area with residential

housing to the north, south and west. Further arable fields and a network of

hedgerows characterise the landscape to the east.

The Site layout is shown in Figure 2.

1.3 Proposed Developments

The proposals are for a sustainable mixed-use scheme including new community

stadium for Boston United Football Club, housing, retail, commercial and leisure uses

(Figure 3).


2.0 LEGISLATION

2.1 Birds

All wild birds are protected under Section 1 of the Wildlife and Countryside Act

(WCA) 1981 (as amended). Subsection 1(1) makes it an offence to intentionally kill,

injure, or take any wild bird, take, damage or destroy the nest of any such bird whilst

it is in use or being built; or take or destroy an egg of any such wild bird. It is, further,

an offence to either intentionally, or recklessly, disturb any wild bird listed on

Schedule 1 while it is nest building, or at a nest containing eggs or young, or disturb

the dependent young of such a bird. The law covers all species of wild birds

including common, pest or opportunistic species.

2.2 Amphibians

All amphibians are protected under the WCA 1981 (as amended), with some species

also protected under the European Habitats and Species Directive (92/43/EC), and

enacted in the UK through Annex IV of the Habitats and Species Regulations 2010

(as amended). All amphibians are protected from keeping, transporting, selling or

exchanging. This means that in practice reasonable measures must be taken to

avoid their incidental mortality.

The Great Crested Newt (GCN) is protected under Schedule 2 of the Habitats

Regulations and Schedule 5 Sections 9(1) and 9(4) of the WCA 1981 (as amended).

As such it is illegal to deliberately or recklessly kill, injure, capture or disturb these

species or to obstruct access to, damage or destroy areas where they live or breed.

The legislation applies to all stages of the life cycle including eggs, larvae and

juveniles. GCNs spend the majority of their lives on land, venturing up to 500 m (but

more usually 250 m) from their breeding ponds and as such any groundworks within

500 m of a breeding pond could have an adverse effect on GCNs.

2.3 Reptiles

All six native species of reptiles are protected under the 1981 WCA (as amended),

from deliberate or reckless killing or injury. As such, all reasonable steps must be

taken to avoid their incidental mortality when carrying out works.


2.4 Bats

All bats and their roosts are protected under Section 9 of the WCA 1981 (as

amended) and Annex IV of the Habitats and Species Regulations 2010 (as

amended).

It is an offence, either deliberately or recklessly, to destroy, damage or obstruct

access to any bat roost, or to disturb a bat using such a place. It should be noted

that a roost is protected whether or not bats are present and any activity or works

affecting a roost, even when bats are absent, is likely to require a Natural England

European Protected Species Licence.

2.5 Badgers

Badgers and their setts are protected under the 1992 Protection of Badgers Act.

Under this Act it is an offence to wilfully kill, injure, take, possess or cruelly ill-treat

badgers, or to attempt to do so. It is also an offence to intentionally or recklessly

damage, destroy, or obstruct access to any part of a sett, or to disturb an occupied

sett, either by intent or negligence. When interpreting the Act, Natural England

defines a sett as any structure within an area used by badgers that shows signs of

having been occupied by badgers within the last 12 months. In addition, if a badger

social group is likely to be adversely affected by a planned development then the

planning authority can refuse planning permission under guidelines given in the

Government Circular (ODPM, 2005).

2.6 Water Voles

The water vole received limited legal protection up until April 1998 through its

inclusion in Schedule 5 of the Wildlife & Countryside Act (WCA) 1981 (as amended)

for some offences. This protection was extended on 6th April 2008, so the water vole

is now fully protected under Section 9.

Legal protection makes it an offence to:

Intentionally kill, injure or take (capture) a water vole;

Possess or control a live or dead water vole, or any part of a water vole;

Intentionally or recklessly damage, destroy or obstruct access to any structure

or place which water voles use for shelter or protection or disturb water voles

while they are using such a place; and

Sell, offer for sale or advertise for live or dead water voles.


Offences under Section 9 carry a maximum penalty of a fine not exceeding Level 5

on the standard scale (currently £5,000), imprisonment for up to six months, or both.

In addition, the courts may order the forfeiture of any vehicle or other thing that was

used to commit the offence.

2.7 Plant Species Prohibited from Release into the Wild

The handling and disposal of Japanese knotweed Fallopia japonica and giant

hogweed Heracleum mantegazzianum is covered by several pieces of legislation.

The main piece of legislation is Section 14(2) of the WCA 1981 (as amended) which

states that ‘if any person plants or otherwise causes to grow in the wild any plant

which is included in Part II of Schedule 9, he shall be guilty of an offence’. Japanese

knotweed and giant hogweed are listed in the Schedule. The Environmental

Protection Act 1990 (as amended) is a broad ranging piece of legislation that singles

out Japanese knotweed and giant hogweed for special mention. The Act places a

'Duty of Care' on the producer and anyone they employ to dispose of soil or other

material contaminated with Japanese knotweed or giant hogweed, such material

becomes a controlled waste, which can only be taken to licensed landfill sites who

must deal with it in an appropriate way.

2.8 Hedgerow

The Hedgerows Regulations 1997 applies to any hedgerow which has a continuous

length of, or exceeding, 20 m, or is less than 20 m but adjoins another hedgerow at

each end. A hedgerow can be categorised as ‘important’ if it is 30 years old or older

and satisfies at least one of the criteria listed in Part II of Schedule 1 of the

Regulations. The removal of a hedgerow which is protected under these criteria is

prohibited without appropriate measures being taken and it is an offence to

intentionally or recklessly remove, or cause or permit another person to remove, a

hedgerow in contravention of Regulation 5(1) or (9).

2.9 Planning

With reference to the National Planning Policy Framework (NPPF), the Office of the

Deputy Prime Minister Circular (2005) advises that ecological surveys are

undertaken before planning permission is determined. The circular states “The need

to ensure that ecological surveys are carried out should therefore only be left to

coverage under planning conditions in exceptional circumstances” (see References,

Appendix I).


3.0 METHODOLOGY

3.1 Data Search

A data search was undertaken by the Greater Lincolnshire Nature Partnership

(GLNP) to identify statutory and non-statutory sites and protected and notable

species within a 2 km radius of the centre of the Site. In addition, a search for

designated sites for nature conservation on, or within, 2 km of the Site was

performed using the Multi-Agency Geographic Information for the Countryside

(MAGIC).

3.2 Review of Previous Surveys

Where possible, information was gathered on any previous surveys that have been

conducted at the Site and the results and conclusions were reviewed. The following

survey report was reviewed:

∆ Ecological Baseline Survey of Land South-West of Boston and Land off

Tytton Lane, Boston Lincolnshire. July 2007 ESL (Ecological Services) Ltd.

3.3 Extended Phase 1 Habitat Survey

The habitats on the Site and on adjoining land were surveyed on 16th September

2013 by two Delta-Simons ecologists using the standardised Joint Nature

Conservation Committee Phase 1 habitat classification and mapping methodology

(JNCC, 2010). Dominant plant species were observed and recorded in each habitat.

The plant species nomenclature follows that of Stace (2010).

The following list indicates the species groups that were targeted:

∆ Birds: All species with special reference to key species (such as those on

Schedule 1 of the Wildlife and Countryside Act, 1981 (as amended) (WCA

1981)), UK Biodiversity Action Plan (UKBAP) species and Birds of

Conservation Concern (BoCC) (Gregory et al., 2002);

∆ Amphibians: GCN;

∆ Reptiles: common lizard, adder, slow-worm, grass snake; and

∆ Mammals: bat (all species), badger, water vole, otter.


3.3.1 Birds

Visual and/or audible identification was made of any birds on the Site or flying over

the Site during the survey period. Suitable habitat was, where possible, inspected

and any evidence of nesting activity was recorded.

3.3.2 Amphibians

All terrestrial and aquatic habitats on the Site were assessed for their potential to

support amphibian species.

A GCN Habitat Suitability Index (HSI) was carried out to evaluate the suitability of the

water bodies and adjoining habitats for GCNs (Oldham et al., 2000). It is a

quantitative measure of habitat quality.

The HSI is the number between 0 and 1, derived from an assessment of ten habitat

variables known to influence the presence of newts. An HSI of 1 is optimal habitat

(high probability of occurrence), while a HSI of 0 is very poor habitat (minimal

probability of occurrence). The HSI is calculated on an individual pond basis, but

takes into account surrounding terrestrial habitat and local pond density.

3.3.3 Reptiles

A cold-searching method was employed which involved identifying suitable habitats

for reptiles within areas on-Site and immediately off-Site. Natural and artificial refugia

(logs, large debris and so on) were lifted and examined for the presence of reptiles

and their field signs (such as shed skins).

3.3.4 Bats

An assessment of Bat Roost Potential (BRP) of the trees and buildings on the Site,

and within land immediately surrounding the Site, was completed, guided by the Bat

Survey: Good Practice Guidelines (Hundt, 2012). The survey method enables the

categorisation of each tree in relation to its value for bats (see Appendix II).

3.3.5 Badgers

The Site was inspected for badger activity including sett entrances, latrines,

footprints, runs through vegetation, guard hairs caught on fences and snuffle holes.


3.3.6 Water Voles

Suitable habitats for water vole were identified within areas on-Site and immediately

off-Site.

3.3.7 Other Protected Species

Where applicable, during the survey, evidence was recorded of any protected

species, including UKBAP priority species, which have not been acknowledged within

this section of the Report. Habitats known to support additional protected species

were also recorded, if present, during the survey.

3.3.8 Plant Species Prohibited from Release into the Wild

The occurrence of any terrestrial invasive weeds on the Site was identified in terms

of species and stand size.

3.3.9 Hedgerows

An assessment of any hedgerows present at the Site, which will be adversely

affected by the proposed development, was undertaken using the standard

hedgerow surveying methodology outlined in the Hedgerow Regulations 1997. The

purpose of the assessment was to ascertain whether the hedgerows are classified as

‘nationally important’ and therefore protected under the Hedgerow Regulations 1997.

The assessment involves a scoring system which relies on particular features,

number of woody and floral species present within the hedgerow habitat, and the age

of the hedgerow.

3.3.10 Surrounding Area

The land immediately surrounding the Site, beyond the Site boundary, was surveyed.

Where access was not available to these areas, observations were made from the

Site boundary or via public land and highways.


4.0 RESULTS

4.1 Data Search

4.1.1 Habitats

The results of the MAGIC data search and the GLNP desk search revealed four non-

statutory designated sites within 2 km of the centre of the Site:

∆ Tytton Lane West Pits East Local Wildlife Site (LWS) is situated approximately

220 m to the north-west of the Site and comprises a flooded pit and dense

scrub;

∆ Tytton Lane West Pit West LWS is situated approximately 360 m to the north-

west of the Site and comprises a flooded pit and dense scrub;

∆ Botolphs Park Pond LWS is situated approximately 385 m to the north-west of

the Site and comprises a pond and gardens;

∆ Frampton Hall LWS is situated approximately 1.5 km to the south of the Site

and comprises parkland with semi-natural woodland; and

∆ South Forty Drain LWS is situated approximately 1.6 km to the north of the

Site and comprises semi-improved grassland and a drain.

No statutory designated sites were identified within 2 km of the Site.

4.1.2 Species

Birds

The data search revealed numerous records of protected and notable bird species

within the local area. Those most likely to occur at the Site include field fare Turdus

pilaris (WCA Schedule 1), common linnet Carduelis cannabina, house sparrow

Passer domesticus, starling Sturnus vulgaris and song thrush Turdus philomelos (all

red list species), and graylag goose Anser anser, reed bunting Emberiza

schoeniclus, and common bullfinch Pyrrhula pyrrhula (all amber list species).

Amphibians

The GLNP data search revealed a total of one record of GCNs and four records of

smooth newts Triturus vulgaris. These records are over 15 years old and are,

therefore, not considered to accurately represent the current status of the species in

the local area.


Common frogs Rana temporaria and common toads Bufo bufo have been recorded

at a number of locations within the search area, the closest being approximately 300

m to the north-west of the Site recorded in 2010.

Reptiles

The desk search did not reveal any records of reptiles within the search area.

Terrestrial Mammals

The data search revealed extensive bat records within the search area, including

records of common pipistrelle Pipistrellus pipistrellus, soprano pipistrelle Pipistrellus

pygmaeus and Daubenton’s bat Myotis daubentonii. The closest record from the

past 15 years is of a pipistrelle, recorded approximately 200 m to the west of the Site

in 2008.

Four records of badger Meles meles have been identified from the data search.

These are from locations approximately 1.4 km to the south recorded in 2004, 1.9 km

and 800 m to the south and 800 m to the west of the Site, recorded in 2009.

Water vole Arvicola amphibius have been recorded 37 times within Towns Drain at

the northern extent of the Site in 2006.

The data search revealed sixteen records for brown hare Lepus europaeus. The

closest record being from a location approximately 600 m to the east of the Site,

recorded in 2001.

Other Protected and Notable Species

The GLNP data search revealed a number of records for notable butterfly species

within the search area.

The Results of the GLNP data search are included as Appendix III.

4.2 Review of Previous Surveys

An Ecological Survey of the Site was undertaken by ESL in April 2007 (Ecological

Baseline Survey of Land South-West of Boston and Land off Tytton Lane, Boston

Lincolnshire, July 2007 ESL (Ecological Services) Ltd. The following summarises the

report:


∆ The survey reported the potential for GCNs within the ditch along the eastern

extent of Site 2. A GCN survey was conducted but stopped due to the dense

vegetation preventing surveying;

∆ A water vole survey reported evidence of water vole activity within both the on-

Site and off-Site wet ditches; and

∆ No further protected or notable species were recorded.

4.3 Extended Phase 1 Habitat Survey – Site

The Site is characterised by arable fields with boundary ditches and hedgerows, with

areas of broadleaved plantation and dense scrub. Figure 2 shows the extent of

habitat types and boundary features. Descriptions of the habitat types and dominant

plant species found at the Site are provided below. Habitat descriptions and codings

are by broad habitat type, as listed in the Phase 1 Habitat Survey Manual (JNCC,

2010). Target Notes (TNs) are listed under Appendix IV whilst photographs of the

Site survey are located in Appendix V.

A1.1.1 Broadleaved Plantation

The western area of the Site’s eastern boundary featured two shelter belts,

comprising pedunculate oak Quercus robur, field maple Acer campestre, hazel

Corylus avellana, crack willow Salix fragilis, dogwood Cornus sanguinea, guelder

rose Viburnum opulus and alder Alnus glutinosa (Photograph 1). This habitat formed

a vegetation buffer between the Site and the adjacent road. The trees were all young

or semi-mature and lacked any significant features suitable to support roosting bats.

A3.1 Scattered Broadleaved Trees

A single semi-mature ash Fraxinus excelsior and single semi-mature crack willow

were present on the western edge of the land to the east of the A16 adjacent to the

off-Site scrub. Both trees were recorded to support trunks and branches with no

obvious features, such as storm damage or lifted bark, suitable to support roosting

bats.

A 2.1 Dense Scrub

A small area of dense hawthorn Cratageus monogyna and elder Sambucus nigra

scrub was present along the north-western boundary of the eastern area of the Site,

beyond which was further dense scrub (Photograph 2). Common nettle Urtica dioica,


hogweed Heracleum sphondylium, dog rose Rosa canina, ivy Hedra helix and

creeping thistle Cirsium arvense, formed an understorey.

G2 Ditch – Standing Water

A ditch ran along the eastern boundary of the land to the west of the A16

(Photograph 3). At the time of the survey there was no flow. The surface had a

covering of duckweed (Lemna sp.) with no trails to indicate the possible presence of

water vole. The ditch was heavily shaded in places by common reed Phragmites

australis, and ruderals on the banks including great willowherb Epilobium hirsutum,

nettle and occasional common ragwort Senecio jacobaea.

J1.1 Arable

The majority of the Site is characterised by arable land, which at the time of the

survey comprised cereal crop stubble that had begun to regrow with a cereal crop

and recolonising grassland and ruderal vegetation (Photograph 4). Species included

perennial ryegrass Lolium perenene, Yorkshire fog Holcus lanatus, bristly oxtongue

Picris echioides, white dead nettle Lamium album, spear thistle Cirsium vulgare,

creeping buttercup Ranunculus repens, dandelion Taraxucum officinale, ribwort

plantain Plantago lanceolata, red dead nettle Lamium purpureum, common nettle

and field forget-me-not Myosotis arvensis. In addition, cow parsley Anthriscus

sylvestris and hogweed Heracleum sphondylium were recorded at the field

boundaries. The vegetation was scattered with areas of bare ground also present.

J2.1.2 Intact Species-poor Hedgerow

Three boundary hedgerows within the land to the west of the A16 and one in the

north-western extent of land to the east were recorded to be intact. The hedgerows

were assessed as being species poor, as they were dominated by hawthorn

Crataegus monogyna with occasional elder, ash, bramble Rubus fruiticosus agg. and

dog rose. The hedgerows appeared largely managed (Photograph 5) with bramble

growing in some areas. Frequent rabbit Oryctolagus cuniculus burrows and digging

were recorded at the base of the hedgerows at the southern and eastern boundaries

of land to the west of the road.


J2.2.1 Defunct Species-poor Hedgerow

A defunct hedgerow separates two fields within the north-western extent of land to

the west of the A16. The hedgerow was assessed to be species poor, comprising

predominately hawthorn with occasional bramble and dog rose.

J2.6 Dry Ditch

A series of dry ditches divided the fields of land to the west of the A16 (Photograph

5). The ditches were approximately 3 m wide with a depth of 2 m. At the time of the

survey there was no evidence of standing water. Common reed was present in a

numbers of stretches of the ditches, indicating that the ditches had previously

supported water. In places bankside vegetation had recently been cut, where this

had not taken place great willowherb, common nettle and hedge bindweed

Caylystegia sepium dominated.

J4 Hardstanding Cycle/Footpath

A tarmac cycle/footpath runs along the eastern extent of land to the west of the A16

(Photograph 6). This was not seen to support any significant vegetation growth and

was considered to have negligible ecological value.

4.3.1 Birds

Bird species recorded during the survey include pheasant Phasianus colchicus, wood

pigeon Columba palumbus, collared dove Streptopelia decaocto, wren Troglodytes

troglodytes, blackbird Turdus merula, blue tit Parus caeruleus, great tit Parus major,

carrion crow Corvus corone, starling Sturnus vulgaris (a UK Biodiversity Action Plan

Priority Species), and reed bunting Emberiza schoeniclus (a UKBAP Priority

Species).

The trees, dense scrub and hedgerows provide suitable habitat for nesting birds,

although no evidence to indicate recent nesting activity was recorded at the time of

the survey. In addition, the banks of the ditches at the Site provide opportunities for

ground nesting birds, particularly due to the surrounding agricultural landscape.

However, no ground nesting species were recorded at the Site, or within land

immediately surrounding the Site, at the time of the survey.


No birds listed on Schedule 1 of the WCA (1981), as amended, were recorded at the

Site. It should be noted that this is not a comprehensive inventory of the bird species

which may be present at the Site.

4.3.2 Great Crested Newts

The stretch of ditch within the eastern extent of land to the west of the A16 supported

standing water during the survey. The terrestrial habitats at the Site were not

considered ideal to support foraging, sheltering or dispersing GCNs. The majority of

the Site comprised arable and hardstanding habitat, which is considered likely to

discourage GCNs from dispersing across much of the Site. The hedgerows and dry

ditches at the Site may provide limited opportunities for this species, however, a

review of aerial photographs and OS maps revealed the presence of four ponds

within 500 m of the Site, which are all separated from the Site by expanses of

hardstanding and residential housing. It is considered unlikely that, if GCNs occur

within these ponds, they would venture to on-Site habitats. The data search did not

reveal any recent records of GCNs within 500 m of the Site.

A GCN HSI was undertaken of the wet ditch on the edge of the land to the west of

the A16, the results of which are provided in Table 1 (below).

Table 1 - Habitat Suitability Index Assessment

Variables of Habitat Suitability Ditch

SI1 Location 1 SI2 Pond area 1 SI3 Pond drying 0.5 SI4 Water quality 0.33 SI5 Shade 0.4 SI6 Fowl 0.67 SI7 Fish 0.67 SI8 Ponds 0.72 SI9 Terrestrial habitat 0.33

SI10 Macrophytes 0.36

Habitat Suitability

Index0.55

Below

Average

The overall HSI score for the ditch is 0.55. With reference to the criteria specified

within the methodology (Section 3.3.2) the likelihood of GCNs occurring within the

ditch is ‘Below average’. There are, therefore, no further recommendations with

regards to GCNs at the Site.


4.3.3 Reptiles

No evidence of reptiles was recorded on the Site. The majority of the Site was

considered unsuitable to support reptile species, however, the dry ditches and

hedgerow bases may provide limited opportunities for reptiles if they occur in the

local area. The data search did not reveal any records of reptiles within 1 km of the

Site and there are, therefore, no further recommendations with regards to reptiles at

the Site.

4.3.4 Bats

The trees at the Site lacked the necessary structural features such as storm damage,

rot holes and lifted bark suitable to support roosting bats. The trees were assessed

as having negligible BRP. The trees and hedgerows at the Site do provide ideal

habitat for commuting and foraging bats which may occur in the local area.

Since the Extended Phase 1 Habitat survey was undertaken in September 2013, the

proposals have been updated to include two properties beyond the western Site

boundary, 262 and 264, London Road within the red line boundary. A separate Bat

Roost Potential survey report (13-0525.04, April 2014) assesses the potential of the

buildings to support roosting bats.

4.3.5 Badgers

A disused single-hole badger sett was present within the bank of a dry ditch on land

to the west of the A16 (TN 1). Two further disused setts were present within the

eastern extent of the dense scrub on land to the east of the A16 (TN 2). A number of

dung pits were recorded at the south-western extent of this land (TN 3). The data

search revealed two records of badger within 800 m of the Site.

4.3.6 Water Vole

The wet ditch within land to the west of the A16 was not considered ideal habitat for

water vole. The banks appeared steep sided and although there was taller

vegetation to provide shelter and protection from predators, foraging potential in the

form of submerged and marginal vegetation was limited. No evidence of water vole

activity, such as burrows, feeding remains or latrines, were recorded from the banks.

Towns Drain immediately adjacent to the southern boundary of land was considered

suitable to support this species, although in low numbers due to encroaching and

overshading from bankside vegetation. The previous water vole survey of the drain

before it became overgrown did reveal evidence of water voles at the Site. The data


search revealed 37 records for this species within the Towns Drain on the stretch

bordering the Site.

4.3.7 Other Protected Species

The Site provides suitable habitat for brown hare Lepus europaeus.

4.3.8 Plant Species Prohibited from Release into the Wild

Invasive weeds such as Japanese knotweed, Himalayan balsam, and giant hogweed

were not recorded on the Site. Common ragwort was recorded within the rough

grassland at the Site and is subject to the Weeds Act 1959 to control its spread.

4.3.9 Hedgerows

The hedgerows at the Site were recorded to be species-poor, supporting

predominantly hawthorn with occasional ash, bramble and dog rose. It was,

therefore, not considered necessary to assess the hedgerow against the Hedgerow

Regulations criteria (1997).

4.4 Extended Phase 1 Habitat Survey – Land Adjoining the Site

The Site is situated within a predominately agricultural setting with further arable

fields and a network of hedgerows characterising the surrounding landscape. Tytton

Lane lies adjacent to the northern Site boundary with residential housing beyond.

Further residential housing is situated to west and beyond Towns Drain to the south

of land to west of the Site (see 4.3.6 Water Vole).


5.0 CONCLUSIONS AND RECOMMENDATIONS

5.1 Conclusions

The results of the MAGIC data search and the GLNP desk search revealed five non-

statutorily designated sites situated approximately 300 m to the north-west, 1.5 km to

the north and 1.6 km to the south of the Site. At these distances and with barriers to

dispersal including major roads and urban development, it is considered unlikely that

the proposed development will have any significant impact on the designated sites.

The Site is characterised by arable land with a network of dry and wet ditches and

boundary hedgerows, with limited areas of dense scrub and broadleaved plantation.

A cycle/footpath ran along the eastern extent of land to west of the A16. The A16,

running north-south separates the two areas of the Site.

The Site supported a variety of habitats suitable for both tree and ground nesting

birds, including woodland, dense scrub and arable land. Few bird species were

identified at the time of the survey, however, the results of the data search revealed a

variety of records of bird species listed under Schedule 1 of the WCA (1981) and

UKBAP species. No birds listed on Schedule 1 of the WCA (1981), as amended,

were recorded at the Site or flying over the Site at the time of the survey.

The trees at the Site were assessed as having negligible BRP. However, the trees

and hedgerows at the Site provide opportunities for foraging birds and ideal habitat

for commuting and foraging bats. It is understood that the majority of these habitats

are to be retained following the development and additional landscaping will enhance

the Site further for these species. Since the Extended Phase 1 Habitat survey was

undertaken, the proposals for the Site have changed and as a consequence a BRP

survey has been undertaken of two properties, 262 and 264, London Road, that are

due to be demolished to facilitate an access road onto the Site. The results of the

survey are outlined within a separate report (13-0535.04).

The wet ditch at the Site supported limited standing water at the time of the survey. It

was densely vegetated with tall common reed, causing the water to be heavily

shaded and of poor quality. The water vole survey conducted by ESL in 2007

recorded a number of signs indicating the presence of water vole in both of the on-

Site and off-Site drains. The data search revealed a number of records of this


species within Towns Drain, directly adjacent to the southern boundary of land to the

west of the A16.

Disused badger setts were recorded on both Sites. Signs of recent activity were

present in the form of dung pits on land to the east of the A16. It can be concluded

that badgers are using the Site only for foraging currently.

Common ragwort was recorded within the rough grassland at the Site and is subject

to the Weeds Act 1959 to control its spread.

5.2 Recommendations

Recommendation 1 (Nesting Birds):

∆ It is not known which scattered trees and hedgerows are to be retained

following the development, however, all of the dense scrub will be removed.

Vegetation clearance or felling works should be performed either before early

March or after late July in order to avoid affecting any birds during the main

period in which they are nesting. In addition, any clearance works to the areas

of tall ruderals at the Site should be undertaken outside the main bird nesting

period. Conflict with the development can be avoided by clearing the Site of

any suitable nesting habitat outside of the breeding period in advance of any

proposed works, and delays due to potential ground nesting birds can also be

avoided by cutting back the grassland outside of the nesting bird season and

then maintaining it at a height of approximately 15 cm in order to discourage

birds from nesting; and

∆ If, however, Site clearance works are deemed necessary during the nesting

period an experienced ecologist will be required to check the Site habitats to

confirm that no nesting birds will be affected by the proposed works.

Recommendation 2 (Bats):

It is not known which hedgerows and scattered trees are to be retained following the

development. If these features are retained it is recommended that lighting along

these linear features is avoided and, that lighting as part of the proposed

development is kept to a minimum in order to avoid discouraging any bats within the

local area from using the Site for foraging and commuting.


The recommendations following the BRP of 262 and 264 London Road are included

within the Report (13-0525.04).

Recommendation 3 (Badgers & Brown Hare):

∆ Since disused badger setts have been identified within the Site, a further

badger survey should be conducted before construction works start, to

determine whether the setts are still inactive. If a sett is found to be active it

may be necessary to apply for a licence from Natural England to close the sett.

It should be noted that if this is required, a further survey of the wider area will

be required to inform the licence application and, once granted, sett closure

cannot be undertaken from December to June (inclusive) in order to avoid

potentially disturbing cubs. Until a further survey is undertaken, no construction

works should take place within 30m of the setts; and

∆ The Site and the surrounding habitats are suitable to support badgers and

brown hare, both of which may venture onto Site during the proposed works. It

is, therefore, recommended as a precautionary measure that either no

excavations are left uncovered overnight during the construction phase of the

works or mammal ramps are installed in order to prevent these species from

becoming trapped.

Recommendation 4 (Pollution Prevention):

Contractors should adhere to the recommendations outlined in Pollution Prevention

Guideline 5 (PPG 5): Works in, near or liable to affect watercourses (Environment

Agency n.d.) to minimize the risk of pollution events to the water course during

construction.

Recommendation 5 (Water Voles):

It is recommended that a water vole survey is carried out to determine their presence

or likely absence within the ditch on-Site and drains immediately off-Site. The survey

can be carried out from mid-April to September (inclusive) when the voles are most

active.

Recommendation 6 (Common Ragwort):

Care should be taken during Site clearance works in order to prevent the spread of

common ragwort to off-Site habitats.


Recommendation 7 (Planning and Ecological Enhancements):

Following the issue of the NPPF, 2012 by the Department for Communities and Local

Government (DCLG), “The planning system should contribute to and enhance the

natural and local environment by: Minimising impacts on biodiversity and providing

net gains in biodiversity where possible, contributing to the Government’s

commitment to halt the overall decline in biodiversity…”; and, therefore, for this

particular development we recommend the following:

∆ The use of native plant species sourced from local nurseries is recommended

in landscape proposals to enhance foraging opportunities for local birds and

bats, by increasing the invertebrate diversity on-Site. A species list of

recommended trees and shrubs is given below:

∆ Beech Fagus sylvatica;

∆ Elder Sambucus nigra;

∆ Field maple Acer campestre;

∆ Silver birch Betula pendula;

∆ Rowan Sorbus aucuparia;

∆ Small-leaved lime Tilia cordata;

∆ Bird cherry Prunus padus;

∆ Blackthorn Prunus spinosa;

∆ Hazel Corylus avellana;

∆ Hawthorn Crataegus monogyna;

∆ Holly Ilex aquifolium;

∆ Honeysuckle Lonicera periclynemum;

∆ Wild privet Ligustrum vulgare;

∆ Walnut Juglans regia; and

∆ Guelder-rose Viburnum opulus.


6.0 LIMITATIONS OF SURVEY

6.1 Limitations

The behaviour of animals can be unpredictable and may not conform to

characteristics recorded in current scientific literature. This Report, therefore, cannot

predict with absolute certainty that animal species will occur in apparently suitable

locations or habitats or that they will not occur in locations or habitats that appear

unsuitable.

Whilst every effort was made to access all parts of the Site, not all external regions

were able to be accessed for the inspection. It should be noted that on a single

inspection it is not possible to define the presence or absence of many species.

6.2 Disclaimer

The recommendations contained in this Report represent Delta-Simons’ professional

opinions, based upon the information referred to in Section 1.0 of this Report,

exercising the duty of care required of an experienced Ecology Consultant. Delta-

Simons does not warrant or guarantee that the Site is free of Bats or other protected

species.

No part of the survey included an assessment of the materials and conditions of any

buildings. No part of the survey included an asbestos assessment, nor did it

represent an appraisal of other deleterious materials or hazardous substances.

This Report was prepared by Delta-Simons for the sole and exclusive use of the

Client and for the specific purpose for which Delta-Simons was instructed as defined

in Section 1.0 of this Report. Nothing contained in this Report shall be construed to

give any rights or benefits to anyone other than the Client and Delta-Simons, and all

duties and responsibilities undertaken are for the sole and exclusive benefit of the

Client and not for the benefit of any other party. In particular, Delta-Simons does not

intend, without its written consent, for this Report to be disseminated to anyone other

than the Client or to be used or relied upon by anyone other than the Client. Use of

the Report by any other person is unauthorised and such use is at the sole risk of the

user. Anyone using or relying upon this Report, other than the Client, agrees by

virtue of its use to indemnify and hold harmless Delta-Simons from and against all

claims, losses and damages (of whatsoever nature and howsoever or whensoever


arising), arising out of or resulting from the performance of the work by the

Consultant.

Figures

Figures

A different perspective

Appendix

IAppendix I


References

Department for Communities and Local Government (2012). National Planning Policy

Framework.

English Nature (2001). Great crested newt mitigation guidelines. English Nature (now

Natural England). Peterborough.

Environment Agency (n.d.). Pollution Prevention Guideline 5: Works In, Near or Liable to

affect Watercourses [online]. Available from http://www.environment-

agency.gov.uk/commondata/acrobat/ppmwater.pdf

Gregory, R.D., Wilkinson, N.I., Noble, D.G., Robinson, J.A., Brown, A.F., Hughes, J.,

Procter, D., Gibbons, D.W. & Galbraith, C.A. (2002). The population status of birds in the

United Kingdom, the Channel Islands and Isle of Man: an analysis of conservation

concern: 2002-2007. British Birds 95; 410 - 48.

Hundt, L. (2012) Bat surveys: Good practice guidelines, 2nd edition. Bat Conservation

Trust.

Joint Nature Conservation Committee (2010). Phase 1 habitat classification and

mapping methodology. JNCC, UK.

Multi-Agency Geographic Information for the Countryside (MAGIC) [online]. Available at:

www.magic.gov.uk

Office of the Deputy Prime Minister (2005): Circular 06/05: Biodiversity and geological

conservation - statutory obligations and their impact within the planning system.

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

of habitat for the great crested newt (Triturus cristatus). Herpatological Journal. 10;143-

155.

Stace, C. (2010). New Flora of the British Isles 3rd edition. University Press, Cambridge.

The Conservation of Habitats and Species Regulations 2010 (as amended) HMSO

The Hedgerow Regulations 1997, HMSO

Wildlife and Countryside Act 1981 (as amended), HMSO.

Appendix

II

Appendix II


Categorisation of Bat Roosting Potential – Trees

Bat Roost Potential

Description

Negligible An inspected tree which is considered to have no features of importance for roosting bats. No further constraints apply to the method or timing of proposed works.

Low From the ground, the tree appears to have features (holes, cavities or cracks) that extend back into a cavity. Owing to the aspect, the feature may support singleton bats outside of hibernation. Alternatively, if no features are visible but owing to its size and age and structure, the tree is considered likely to have hidden features that only an elevated inspection may reveal. In respect of ivy cover, this is not dense (i.e. providing BRP in itself) but may mask the presence of BRP features. Emergence and activity surveys may be required. If following all surveys the feature remains categorised as low BRP, works typically proceed under supervision by an experienced bat worker, as a precautionary measure. For example, including a re-inspection immediately prior to works and sectioned felling of a tree. The requirements of Natural England European Protected Species licensing will be re-considered should bats or evidence of bat activity be identified during the supervision.

Medium Features include holes, cracks, crevices that extend or appear to extend back to cavities suitable for bats. Alternatively, ivy cover is sufficiently well-established and matted so as to create potential crevices between the growth and the trunk. Emergence and activity surveys may be required. A Natural England European Protected Species (EPS) Licence is not required for works that affect unconfirmed roosts. However, if following all surveys the feature remains categorised as medium BRP, works should proceed only under supervision by a licensed bat worker following pre-agreed procedures. The requirements of Natural England European Protected Species licensing will be re-considered should bats or evidence of bat activity be identified during the watching brief.

Confirmed Roost

Bats or evidence of bats recorded – both of recent and/or historic activity. Emergence surveys will be required to qualify and quantify usage if such a feature is to be affected by proposed works. A Natural England European Protected Species (EPS) Licence is required for all works affecting features supporting confirmed roosts.

Appendix

III

Appendix III


LWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALL

LWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANEWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WEST

LWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK POND

LWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANEWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EAST

LWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAIN

TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839TF2839


























TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343TF3343 TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443TF3443



LWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALLLWS FRAMPTON HALL

LWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANEWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WESTWEST PITS, WEST

LWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK PONDLWS BOTOLPHS PARK POND

LWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANELWS TYTTON LANEWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EASTWEST PITS, EAST

LWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAINLWS SOUTH FORTY FOOT DRAIN

Lincolnshire EnvironmentalRecords Centre

Map:Non-statutory Sites

LERC Ref: 1314-170

LERC boundary

Search area

Roadside Nature Reserve

Lincolnshire Wildlife Trust Reserve

Regionally Important Geological/Geomorphological Site

Site of Nature Conservation Interest

Local Geological Site

Local Wildlife Site

Drawn by: Charlie Barnes 10/09/2013

OS copyright No. AL100016739 Banovallum House, Manor House Street, Horncastle, Lincolnshire, LN9 5HF

Taxon Group Taxon Name Common Name Location Location Type Grid Reference Date Record Typeamphibian Bufo bufo Common Toad TF318428 2010amphibian Lissotriton vulgaris Smooth Newt TF34L 1977amphibian Lissotriton vulgaris Smooth Newt TF34A 1977amphibian Lissotriton vulgaris Smooth Newt TF3239 1995amphibian Rana temporaria Common Frog TF34L 1977amphibian Rana temporaria Common Frog TF316411 2010amphibian Rana temporaria Common Frog TF318428 2010amphibian Triturus cristatus Great Crested Newt Skirbeck Quarter Brickpits Site of Nature Conservation Interest TF3141 1965bird Anser anser Greylag Goose Garden Grounds, Hessle Drive Site of Nature Conservation Interest TF316435 2007bird Carduelis cannabina Common Linnet Westgate Wood Boston Woods Trust TF303421 2007bird Emberiza schoeniclus Reed Bunting Westgate Wood Boston Woods Trust TF303421 2007bird Passer domesticus House Sparrow Garden Grounds, Hessle Drive Site of Nature Conservation Interest TF316435 2007bird Passer domesticus House Sparrow TF330421 2009bird Passer domesticus House Sparrow TF317429 2009bird Passer domesticus House Sparrow TF316411 2010bird Passer domesticus House Sparrow TF318428 2010bird Pyrrhula pyrrhula Common Bullfinch Westgate Wood Boston Woods Trust TF303421 2007bird Pyrrhula pyrrhula Common Bullfinch TF330421 2009bird Sturnus vulgaris Common Starling Garden Grounds, Hessle Drive Site of Nature Conservation Interest TF316435 2007bird Sturnus vulgaris Common Starling TF330421 2009bird Sturnus vulgaris Common Starling TF317429 2009bird Sturnus vulgaris Common Starling TF316411 2010bird Sturnus vulgaris Common Starling TF318428 2010bird Turdus philomelos Song Thrush TF330421 2009bird Turdus philomelos Song Thrush TF317429 2009bird Turdus pilaris Fieldfare Westgate Wood Boston Woods Trust TF303421 2007bony fish (Actinopterygii) Anguilla anguilla European Eel South Forty Foot Drain ‐ Wyberton High Bridge to London Road Bridge (11 Local Wildlife Site TF323429 1980bony fish (Actinopterygii) Lota lota Burbot Boston Town TF3243 1915insect ‐ butterfly Coenonympha pamphilus Small Heath TF321425 1973insect ‐ butterfly Coenonympha pamphilus Small Heath TF3141 1991insect ‐ butterfly Coenonympha pamphilus Small Heath TF3141 1992insect ‐ butterfly Coenonympha pamphilus Small Heath TF304418 2012insect ‐ butterfly Coenonympha pamphilus Small Heath TF304418 2012insect ‐ butterfly Coenonympha pamphilus Small Heath TF304418 2012insect ‐ butterfly Coenonympha pamphilus Small Heath TF304418 2012insect ‐ butterfly Coenonympha tullia Large Heath TF3141 1897insect ‐ butterfly Coenonympha tullia Large Heath TF3141 1897insect ‐ butterfly Coenonympha tullia Large Heath TF3141 1897insect ‐ butterfly Coenonympha tullia Large Heath TF3141 1897insect ‐ butterfly Lasiommata megera Wall TF3141 1970insect ‐ butterfly Lasiommata megera Wall TF3141 1970insect ‐ butterfly Lasiommata megera Wall TF3141 1971insect ‐ butterfly Lasiommata megera Wall TF3141 1972insect ‐ butterfly Lasiommata megera Wall TF321425 1973insect ‐ butterfly Lasiommata megera Wall TF3141 1988insect ‐ butterfly Lasiommata megera Wall TF3239 2010insect ‐ butterfly Nymphalis polychloros Large Tortoiseshell TF3141 1888insect ‐ butterfly Nymphalis polychloros Large Tortoiseshell TF3141 1888insect ‐ butterfly Nymphalis polychloros Large Tortoiseshell TF3141 1888insect ‐ butterfly Nymphalis polychloros Large Tortoiseshell TF3141 1888insect ‐ butterfly Satyrium w‐album White‐letter Hairstreak TF3241 1961reptile Natrix natrix Grass Snake TF34L 1977terrestrial mammal Arvicola amphibius European Water Vole TF34B 1977terrestrial mammal Arvicola amphibius European Water Vole TF337427 1999 sightingterrestrial mammal Arvicola amphibius European Water Vole TF315415 2002 sightingterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF313419 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF313419 2006 tracks/trailterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF313419 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF313419 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF313419 2006 Dung or other signsterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF313419 2006 tracks/trail

terrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF314417 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF314417 2006 Dung or other signsterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF314417 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF314417 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF314417 2006 feeding damage, etcterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF314417 2006 tracks/trailterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF314418 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF314418 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF314418 2006 Dung or other signsterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF314417 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF314417 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF314417 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF314417 2006 Dung or other signsterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF314417 2006 tracks/trailterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF315416 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF315416 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF315416 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF315416 2006 Dung or other signsterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF315416 2006 tracks/trailterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF315415 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF319413 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF319413 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF319413 2006 tracks/trailterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF320413 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF320413 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF320413 2006 Dung or other signsterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF320413 2006 feeding damage, etcterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF323412 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF323412 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Towns Drain, Wyberton TF323412 2006 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Bunker's Hill Drain, Wyberton TF330413 2007 feeding damage, etcterrestrial mammal Arvicola amphibius European Water Vole Bunker's Hill Drain, Wyberton TF329413 2007 feeding damage, etcterrestrial mammal Arvicola amphibius European Water Vole Bunker's Hill Drain, Wyberton TF329413 2007 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Bunker's Hill Drain, Wyberton TF329413 2007 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Bunker's Hill Drain, Wyberton TF329413 2007 Dung or other signsterrestrial mammal Arvicola amphibius European Water Vole Bunker's Hill Drain, Wyberton TF329413 2007 Dung or other signsterrestrial mammal Arvicola amphibius European Water Vole Bunker's Hill Drain, Wyberton TF329413 2007 feeding damage, etcterrestrial mammal Arvicola amphibius European Water Vole Bunker's Hill Drain, Wyberton TF329413 2007 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Bunker's Hill Drain, Wyberton TF329413 2007 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Bunker's Hill Drain, Wyberton TF329413 2007 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF331418 2007 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF331418 2007 Dung or other signsterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF331419 2007 feeding damage, etcterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF331419 2007 Dung or other signsterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF331419 2007 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF331420 2007 Dung or other signsterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF331420 2007 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF331420 2007 feeding damage, etcterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF331420 2007 feeding damage, etcterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF331420 2007 Dung or other signsterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF331420 2007 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF331421 2007 feeding damage, etcterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF331421 2007 Dung or other signsterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF331421 2007 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF331420 2007 feeding damage, etcterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF330421 2007 feeding damage, etcterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF331421 2007 Dung or other signsterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF331421 2007 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF330421 2007 Dung or other signsterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF330421 2007 feeding damage, etcterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF330421 2007 Dung or other signsterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF330421 2007 Dung or other signs

terrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF330421 2007 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Wyberton Low Road Drain Internal Drainage Board Drain TF331417 2007 burrow, nestholeterrestrial mammal Arvicola amphibius European Water Vole Boston, Chain Bridge Road Drain TF310431 2007 Dung or other signsterrestrial mammal Arvicola amphibius European Water Vole Boston, Chain Bridge Road Drain TF310431 2007 Dung or other signsterrestrial mammal Arvicola amphibius European Water Vole Boston, Chain Bridge Road Drain TF310431 2007 feeding damage, etcterrestrial mammal Arvicola amphibius European Water Vole Boston Town TF3243 2008terrestrial mammal Arvicola amphibius European Water Vole TF3243 2008 sightingterrestrial mammal Arvicola amphibius European Water Vole TF312404 2013 sightingterrestrial mammal Chiroptera Bats Boston Town TF310428 1899 sightingterrestrial mammal Chiroptera Bats Frampton Village TF3239 1990terrestrial mammal Chiroptera Bats Boston Town TF327425 1995terrestrial mammal Chiroptera Bats Boston Town TF3143 1997 sightingterrestrial mammal Chiroptera Bats Boston Town TF328424 1997 groundedterrestrial mammal Chiroptera Bats Wyberton Village TF3240 1997 roostterrestrial mammal Chiroptera Bats Boston Town TF316431 1998terrestrial mammal Chiroptera Bats Wyberton Village TF3141 1998 roostterrestrial mammal Chiroptera Bats Wyberton Village TF319418 1998 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF315418 1998terrestrial mammal Chiroptera Bats Boston Town TF3243 1999 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF314417 1999terrestrial mammal Chiroptera Bats Wyberton Village TF317416 1999 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF3141 1999 roostterrestrial mammal Chiroptera Bats Boston Town TF321423 2000 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF3141 2000 roostterrestrial mammal Chiroptera Bats Wyberton Village TF314417 2000terrestrial mammal Chiroptera Bats Wyberton Village TF316416 2000 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF3141 2000 roostterrestrial mammal Chiroptera Bats Boston Town TF326427 2001 sightingterrestrial mammal Chiroptera Bats Boston Town TF324435 2001terrestrial mammal Chiroptera Bats Wyberton Village TF319418 2001 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF3141 2001 roostterrestrial mammal Chiroptera Bats Wyberton Village TF3240 2002 roostterrestrial mammal Chiroptera Bats Wyberton Village TF3141 2002 roostterrestrial mammal Chiroptera Bats Boston Town TF331421 2003terrestrial mammal Chiroptera Bats Wyberton Village TF334415 2003 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF316416 2003terrestrial mammal Chiroptera Bats Wyberton Village TF3141 2003 roostterrestrial mammal Chiroptera Bats Boston Town TF313432 2004 sightingterrestrial mammal Chiroptera Bats Frampton Village TF312405 2004 sightingterrestrial mammal Chiroptera Bats Frampton Village TF314403 2004 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF318412 2004 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF304409 2004 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF317417 2004 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF329417 2004 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF328408 2004 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF3141 2004 roostterrestrial mammal Chiroptera Bats Wyberton Village TF327418 2004 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF3141 2004 roostterrestrial mammal Chiroptera Bats Boston Town TF321421 2005 sightingterrestrial mammal Chiroptera Bats Boston Town TF319429 2005 sightingterrestrial mammal Chiroptera Bats Frampton Village TF310403 2005 sightingterrestrial mammal Chiroptera Bats Frampton Village TF313405 2005 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF317413 2005 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF316415 2005 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF316414 2005terrestrial mammal Chiroptera Bats Wyberton Village TF316416 2005terrestrial mammal Chiroptera Bats Wyberton Village TF3141 2005 roostterrestrial mammal Chiroptera Bats Frampton West End Hamlet TF303415 2006 sightingterrestrial mammal Chiroptera Bats Boston Town TF319430 2006 sightingterrestrial mammal Chiroptera Bats Frampton Village TF314404 2006terrestrial mammal Chiroptera Bats Boston Town TF331423 2006 sightingterrestrial mammal Chiroptera Bats Boston Town TF3242 2006 roost

terrestrial mammal Chiroptera Bats Wyberton Village TF311418 2006 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF314415 2006 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF317415 2006 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF3141 2006 roostterrestrial mammal Chiroptera Bats Boston Town TF316433 2007 sightingterrestrial mammal Chiroptera Bats Boston Town TF317428 2007 sightingterrestrial mammal Chiroptera Bats Boston Town TF3042 2007 roostterrestrial mammal Chiroptera Bats Wyberton Village TF3142 2007 roostterrestrial mammal Chiroptera Bats Wyberton Village TF3141 2007 roostterrestrial mammal Chiroptera Bats Boston Town TF320424 2008 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF316412 2008 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF309421 2008 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF315417 2008 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF317407 2008 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF316416 2008 sightingterrestrial mammal Chiroptera Bats Boston Town TF328425 2008 sightingterrestrial mammal Chiroptera Bats Boston Town TF319421 2008 sightingterrestrial mammal Chiroptera Bats Boston Town TF312433 2008terrestrial mammal Chiroptera Bats Boston Town TF319429 2008 sightingterrestrial mammal Chiroptera Bats Boston Town TF321428 2008 sightingterrestrial mammal Chiroptera Bats Boston Town TF325426 2008 sightingterrestrial mammal Chiroptera Bats Boston Town TF328423 2008 sightingterrestrial mammal Chiroptera Bats Boston Town TF328425 2008terrestrial mammal Chiroptera Bats Wyberton Village TF311409 2008 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF328418 2008 sightingterrestrial mammal Chiroptera Bats Boston Town TF319429 2009 sightingterrestrial mammal Chiroptera Bats Boston Town TF320424 2009 sightingterrestrial mammal Chiroptera Bats Frampton Village TF313408 2009terrestrial mammal Chiroptera Bats Boston Town TF317434 2010 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF313418 2010 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF318408 2010 sightingterrestrial mammal Chiroptera Bats Boston Town TF321423 2010 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF324419 2011 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF318417 2011 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF315415 2011 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF315411 2011 sightingterrestrial mammal Chiroptera Bats Boston Town TF324426 2011 sightingterrestrial mammal Chiroptera Bats Boston Town TF316432 2011 sightingterrestrial mammal Chiroptera Bats Wyberton Village TF316418 2012terrestrial mammal Chiroptera Bats Boston Town TF322429 2012terrestrial mammal Erinaceus europaeus West European Hedgehog TF33E 1977terrestrial mammal Erinaceus europaeus West European Hedgehog TF33J 1977terrestrial mammal Erinaceus europaeus West European Hedgehog TF34L 1977terrestrial mammal Erinaceus europaeus West European Hedgehog TF34K 1977terrestrial mammal Erinaceus europaeus West European Hedgehog TF34G 1977terrestrial mammal Erinaceus europaeus West European Hedgehog TF34F 1977terrestrial mammal Erinaceus europaeus West European Hedgehog TF34B 1977terrestrial mammal Erinaceus europaeus West European Hedgehog TF34A 1977terrestrial mammal Erinaceus europaeus West European Hedgehog Boston Town TF3243 2007terrestrial mammal Erinaceus europaeus West European Hedgehog TF3243 2007 sightingterrestrial mammal Erinaceus europaeus West European Hedgehog TF330421 2009terrestrial mammal Erinaceus europaeus West European Hedgehog TF317429 2009terrestrial mammal Erinaceus europaeus West European Hedgehog TF316411 2009 sightingterrestrial mammal Erinaceus europaeus West European Hedgehog TF325422 2009 Road casualtyterrestrial mammal Erinaceus europaeus West European Hedgehog TF316411 2010terrestrial mammal Erinaceus europaeus West European Hedgehog Boston Town TF3143 2010terrestrial mammal Erinaceus europaeus West European Hedgehog TF317402 2010 Road casualtyterrestrial mammal Erinaceus europaeus West European Hedgehog TF327425 2012 sightingterrestrial mammal Erinaceus europaeus West European Hedgehog TF327425 2012 sightingterrestrial mammal Erinaceus europaeus West European Hedgehog TF327425 2013 sightingterrestrial mammal Lepus europaeus Brown Hare TF33E 1977terrestrial mammal Lepus europaeus Brown Hare TF33J 1977

terrestrial mammal Lepus europaeus Brown Hare TF34L 1977terrestrial mammal Lepus europaeus Brown Hare TF34K 1977terrestrial mammal Lepus europaeus Brown Hare TF34G 1977terrestrial mammal Lepus europaeus Brown Hare TF34F 1977terrestrial mammal Lepus europaeus Brown Hare TF34B 1977terrestrial mammal Lepus europaeus Brown Hare TF34A 1977terrestrial mammal Lepus europaeus Brown Hare South Wyberton TF3141 2001terrestrial mammal Lepus europaeus Brown Hare Frithville Village TF304407 2005terrestrial mammal Lepus europaeus Brown Hare TF336425 2005 sightingterrestrial mammal Lepus europaeus Brown Hare Wyberton Village TF3042 2007terrestrial mammal Lepus europaeus Brown Hare Wyberton Village TF3042 2007terrestrial mammal Lepus europaeus Brown Hare Frampton Hall LWS Local Wildlife Site TF324395 2007terrestrial mammal Lepus europaeus Brown Hare TF341419 2010 sightingterrestrial mammal Lepus europaeus Brown Hare TF341419 2010 sightingterrestrial mammal Meles meles Eurasian Badger Frampton Village TF3040 2004 dead on roadterrestrial mammal Meles meles Eurasian Badger Frampton Hall LWS Local Wildlife Site TF324395 2007terrestrial mammal Meles meles Eurasian Badger Wyberton Low Road Drain Internal Drainage Board Drain TF3341 2007 settterrestrial mammal Meles meles Eurasian Badger Kirton Village TF3140 2007 dead on roadterrestrial mammal Micromys minutus Harvest Mouse TF3241 1988 sightingterrestrial mammal Myotis daubentonii Daubenton's Bat Boston Town TF320430 2000terrestrial mammal Pipistrellus Pipistrelle Bat species Wyberton Village TF315415 1996terrestrial mammal Pipistrellus Pipistrelle Bat species Wyberton Village TF3141 1999terrestrial mammal Pipistrellus Pipistrelle Bat species Frampton Village TF3239 2000terrestrial mammal Pipistrellus Pipistrelle Bat species Wyberton Village TF3141 2001 roostterrestrial mammal Pipistrellus Pipistrelle Bat species Wyberton Village TF3141 2002 roostterrestrial mammal Pipistrellus Pipistrelle Bat species Wyberton Village TF3141 2002 roostterrestrial mammal Pipistrellus Pipistrelle Bat species Boston Town TF3343 2007 groundedterrestrial mammal Pipistrellus Pipistrelle Bat species Frampton Village TF312406 2007terrestrial mammal Pipistrellus Pipistrelle Bat species Wyberton Village TF3141 2007 roostterrestrial mammal Pipistrellus Pipistrelle Bat species Boston Town TF328424 2008 casualty (not road)terrestrial mammal Pipistrellus Pipistrelle Bat species Boston Town TF331420 2008 casualty (not road)terrestrial mammal Pipistrellus Pipistrelle Bat species Boston Town TF330421 2008 indoorsterrestrial mammal Pipistrellus Pipistrelle Bat species Wyberton Village TF317417 2008 casualty (not road)terrestrial mammal Pipistrellus Pipistrelle Bat species Boston Town TF317435 2011 groundedterrestrial mammal Pipistrellus Pipistrelle Bat species Boston Town TF318433 2011 groundedterrestrial mammal Pipistrellus pipistrellus sensu lato Pipistrelle Boston Town TF3343 1987 roostterrestrial mammal Pipistrellus pipistrellus sensu lato Pipistrelle Boston Town TF3343 1992 roostterrestrial mammal Pipistrellus pipistrellus sensu lato Pipistrelle Boston Town TF3343 1997 roostterrestrial mammal Pipistrellus pipistrellus sensu lato Pipistrelle Boston Town TF306428 1999terrestrial mammal Pipistrellus pipistrellus sensu lato Pipistrelle Boston Town TF320424 2000 sightingterrestrial mammal Pipistrellus pipistrellus sensu lato Pipistrelle Boston Town TF320430 2000terrestrial mammal Pipistrellus pipistrellus sensu lato Pipistrelle Boston Town TF320424 2002 sightingterrestrial mammal Pipistrellus pipistrellus sensu lato Pipistrelle Boston Town TF3143 2003 roostterrestrial mammal Pipistrellus pipistrellus sensu lato Pipistrelle Boston Town TF3243 2005 roostterrestrial mammal Pipistrellus pipistrellus sensu lato Pipistrelle Boston Town TF3242 2005 nursery roostterrestrial mammal Pipistrellus pipistrellus sensu lato Pipistrelle Boston Town TF3243 2005 roostterrestrial mammal Pipistrellus pipistrellus sensu stricto Common Pipistrelle Wyberton Village TF3141 2001 roostterrestrial mammal Pipistrellus pipistrellus sensu stricto Common Pipistrelle Boston Town TF328424 2010 groundedterrestrial mammal Pipistrellus pipistrellus sensu stricto Common Pipistrelle Boston Town TF3242 2010 roostterrestrial mammal Pipistrellus pygmaeus Soprano Pipistrelle Wyberton Village TF3141 2000 roost

297 records returnedLERC Ref: 1314‐170

Produced by Charlie Barnes on the 10/9/2013

Greater Lincolnshire Nature PartnershipBanovallum HouseHorncastleLN9 5HF

web www.glnp.org.ukemail [email protected]

tel 01507 528381 fax 01507 525732An ALERC accredited record centre

[v] Lb.125/100[v] Ba.2/19[v] Bu.23/11833[v] Ma.15/930

Abundance Designations Record Status Dataset KeyBern3, Sect.41, Sect.42, UKBAP, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata descriptionBern3, LBAP:3, WCA5/9.5a, WCA5/9.5b, WO5 Pending SR000351000000DLBern3, LBAP:3, WCA5/9.5a, WCA5/9.5b, WO5 Pending SR000351000000DLBern3, LBAP:3, WCA5/9.5a, WCA5/9.5b, WO5 Passed Awaiting metadata descriptionBern3, HSD5, WCA5/9.5a, WCA5/9.5b Pending SR000351000000DLBern3, HSD5, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata descriptionBern3, HSD5, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata descriptionBern2, FEP7/2, HabRegs2, HSD2p, HSD4, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata descriptionBAmb, BD2.1, CMS_A2, CMS_AEWA‐A2, Non‐native, WCA1ii Pending Awaiting metadata descriptionBern2, BRed, FEP7/2, LBAP:2, LBAP:3, ScotBL Pending Awaiting metadata descriptionBAmb, Bern2, FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP Pending Awaiting metadata descriptionBRed, LBAP:2, LBAP:3, Sect.41, Sect.42, UKBAP Pending Awaiting metadata descriptionBRed, LBAP:2, LBAP:3, Sect.41, Sect.42, UKBAP Pending Awaiting metadata descriptionBRed, LBAP:2, LBAP:3, Sect.41, Sect.42, UKBAP Pending Awaiting metadata descriptionBRed, LBAP:2, LBAP:3, Sect.41, Sect.42, UKBAP Pending Awaiting metadata descriptionBRed, LBAP:2, LBAP:3, Sect.41, Sect.42, UKBAP Pending Awaiting metadata descriptionBAmb, FEP7/2, LBAP:2, LBAP:3, ScotBL Pending Awaiting metadata descriptionBAmb, FEP7/2, LBAP:2, LBAP:3, ScotBL Pending Awaiting metadata descriptionBD2.2, BRed, FEP7/2, LBAP:2, LBAP:3 Pending Awaiting metadata descriptionBD2.2, BRed, FEP7/2, LBAP:2, LBAP:3 Pending Awaiting metadata descriptionBD2.2, BRed, FEP7/2, LBAP:2, LBAP:3 Pending Awaiting metadata descriptionBD2.2, BRed, FEP7/2, LBAP:2, LBAP:3 Pending Awaiting metadata descriptionBD2.2, BRed, FEP7/2, LBAP:2, LBAP:3 Pending Awaiting metadata descriptionBD2.2, BRed, FEP7/2, LBAP:2, LBAP:3, ScotBL Pending Awaiting metadata descriptionBD2.2, BRed, FEP7/2, LBAP:2, LBAP:3, ScotBL Pending Awaiting metadata descriptionBD2.2, BRed, WCA1i, WO1i Pending Awaiting metadata descriptionLBAP:3, OSPAR, RLGLB.CR, ScotBL, Sect.41, Sect.42, UKBAP Pending Awaiting metadata descriptionSect.41, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata descriptionRLGB.Lr(NT), Sect.41, Sect.42, UKBAP Passed Awaiting metadata description

A Present RLGB.Lr(NT), Sect.41, Sect.42, UKBAP Passed Awaiting metadata descriptionA Present RLGB.Lr(NT), Sect.41, Sect.42, UKBAP Passed Awaiting metadata description

RLGB.Lr(NT), Sect.41, Sect.42, UKBAP Passed Awaiting metadata descriptionRLGB.Lr(NT), Sect.41, Sect.42, UKBAP Passed Awaiting metadata descriptionRLGB.Lr(NT), Sect.41, Sect.42, UKBAP Passed Awaiting metadata descriptionRLGB.Lr(NT), Sect.41, Sect.42, UKBAP Passed Awaiting metadata descriptionRLGB.VU, Sect.41, Sect.42, UKBAP, WCA5/9.5a, WCA5/9.5b, WO5 Passed Awaiting metadata descriptionRLGB.VU, Sect.41, Sect.42, UKBAP, WCA5/9.5a, WCA5/9.5b, WO5 Passed Awaiting metadata descriptionRLGB.VU, Sect.41, Sect.42, UKBAP, WCA5/9.5a, WCA5/9.5b, WO5 Passed Awaiting metadata descriptionRLGB.VU, Sect.41, Sect.42, UKBAP, WCA5/9.5a, WCA5/9.5b, WO5 Passed Awaiting metadata description

A Present RLGB.Lr(NT), Sect.41, Sect.42, UKBAP Passed Awaiting metadata descriptionRLGB.Lr(NT), Sect.41, Sect.42, UKBAP Passed Awaiting metadata description

1 Present RLGB.Lr(NT), Sect.41, Sect.42, UKBAP Passed Awaiting metadata description1 Present RLGB.Lr(NT), Sect.41, Sect.42, UKBAP Passed Awaiting metadata description

RLGB.Lr(NT), Sect.41, Sect.42, UKBAP Passed Awaiting metadata descriptionA Present RLGB.Lr(NT), Sect.41, Sect.42, UKBAP Passed Awaiting metadata description1 Present (Count) RLGB.Lr(NT), Sect.41, Sect.42, UKBAP Passed Awaiting metadata description

RLGB.RE, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description2 Present RLGB.RE, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description

RLGB.RE, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description2 Present RLGB.RE, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description

RLGB.EN, Sect.41, Sect.42, UKBAP, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata descriptionBern3, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.5a, WCA5/9.5b Pending SR000351000000DLFEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed SR000351000000DL

Present Adult (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description1 Adult (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description

1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description

1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Pending Awaiting metadata description

FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description1 Adult (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description1 Adult (Count) FEP7/2, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.1k/I, WCA5/9.1t, WCA5/9.2, WCA5/9.4a, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description

Passed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata description

1 Female (Count) Passed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata description

1 Present (Count) Passed Awaiting metadata descriptionPassed Awaiting metadata description

1 Present (Count) Passed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata description

2‐3 Present (Count) Passed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata description

1 Present (Count) Passed Awaiting metadata description1 Present (Count) Passed Awaiting metadata description

Passed Awaiting metadata descriptionPassed Awaiting metadata description

4 Present (Count) Passed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata description


Passed Awaiting metadata description1 Present (Count) Passed Awaiting metadata description

Passed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata description

3 Present (Count) Passed Awaiting metadata description2 Present (Count) Passed Awaiting metadata description1 Present (Count) Passed Awaiting metadata description2 Present (Count) Passed Awaiting metadata description

Passed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata description


4‐6 Present (Count) Passed Awaiting metadata description2 Present (Count) Passed Awaiting metadata description2‐3 Present (Count) Passed Awaiting metadata description


Passed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata descriptionPassed Awaiting metadata description


Passed Awaiting metadata descriptionPassed Awaiting metadata description

3‐4 Present (Count) Passed Awaiting metadata descriptionPassed Awaiting metadata description


5 Present (Count) Passed Awaiting metadata description2 Present (Count) Passed Awaiting metadata description4‐5 Present (Count) Passed Awaiting metadata description1‐2 Present (Count) Passed Awaiting metadata description


Passed Awaiting metadata description3‐4 Present (Count) Passed Awaiting metadata description1 Present (Count) Passed Awaiting metadata description1 Present (Count) Passed Awaiting metadata description3‐4 Present (Count) Passed Awaiting metadata description1‐2 Present (Count) Passed Awaiting metadata description2 Present (Count) Passed Awaiting metadata description

Passed Awaiting metadata description1 Present (Count) Passed Awaiting metadata description2 Present (Count) Passed Awaiting metadata description2 Present (Count) Passed Awaiting metadata description2 Present (Count) Passed Awaiting metadata description

Passed Awaiting metadata description3 Present (Count) Passed Awaiting metadata description2 Present (Count) Passed Awaiting metadata description

Passed Awaiting metadata descriptionBern3, Sect.41, Sect.42, UKBAP Passed SR000351000000DLBern3, Sect.41, Sect.42, UKBAP Passed SR000351000000DLBern3, Sect.41, Sect.42, UKBAP Passed SR000351000000DLBern3, Sect.41, Sect.42, UKBAP Passed SR000351000000DLBern3, Sect.41, Sect.42, UKBAP Passed SR000351000000DLBern3, Sect.41, Sect.42, UKBAP Passed SR000351000000DLBern3, Sect.41, Sect.42, UKBAP Passed SR000351000000DLBern3, Sect.41, Sect.42, UKBAP Passed SR000351000000DL

1 Present (Count) Bern3, Sect.41, Sect.42, UKBAP Passed Awaiting metadata description1 Adult (Count) Bern3, Sect.41, Sect.42, UKBAP Passed Awaiting metadata description

Bern3, Sect.41, Sect.42, UKBAP Pending Awaiting metadata descriptionBern3, Sect.41, Sect.42, UKBAP Pending Awaiting metadata description

1 Adult (Count) Bern3, Sect.41, Sect.42, UKBAP Passed Awaiting metadata description1 Adult (Count) Bern3, Sect.41, Sect.42, UKBAP Passed Awaiting metadata description

Bern3, Sect.41, Sect.42, UKBAP Pending Awaiting metadata descriptionBern3, Sect.41, Sect.42, UKBAP Pending Awaiting metadata description

1 Adult (Count) Bern3, Sect.41, Sect.42, UKBAP Passed Awaiting metadata description4 Adult (Count) Bern3, Sect.41, Sect.42, UKBAP Passed Awaiting metadata description2 Adult (Count) Bern3, Sect.41, Sect.42, UKBAP Passed Awaiting metadata description1 Adult (Count) Bern3, Sect.41, Sect.42, UKBAP Passed Awaiting metadata description

FEP7/2, LBAP:2, ScotBL, Sect.41, Sect.42, UKBAP Passed SR000351000000DLFEP7/2, LBAP:2, ScotBL, Sect.41, Sect.42, UKBAP Passed SR000351000000DL

FEP7/2, LBAP:2, ScotBL, Sect.41, Sect.42, UKBAP Passed SR000351000000DLFEP7/2, LBAP:2, ScotBL, Sect.41, Sect.42, UKBAP Passed SR000351000000DLFEP7/2, LBAP:2, ScotBL, Sect.41, Sect.42, UKBAP Passed SR000351000000DLFEP7/2, LBAP:2, ScotBL, Sect.41, Sect.42, UKBAP Passed SR000351000000DLFEP7/2, LBAP:2, ScotBL, Sect.41, Sect.42, UKBAP Passed SR000351000000DLFEP7/2, LBAP:2, ScotBL, Sect.41, Sect.42, UKBAP Passed SR000351000000DL

1 Present (Count) FEP7/2, LBAP:2, ScotBL, Sect.41, Sect.42, UKBAP Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, ScotBL, Sect.41, Sect.42, UKBAP Pending Awaiting metadata description2 Adult (Count) FEP7/2, LBAP:2, ScotBL, Sect.41, Sect.42, UKBAP Passed Awaiting metadata description1 Dead (Count) FEP7/2, LBAP:2, ScotBL, Sect.41, Sect.42, UKBAP Pending Awaiting metadata description1 Present (Count) FEP7/2, LBAP:2, ScotBL, Sect.41, Sect.42, UKBAP Pending Awaiting metadata description

FEP7/2, LBAP:2, ScotBL, Sect.41, Sect.42, UKBAP Pending Awaiting metadata description2 Adult (Count) FEP7/2, LBAP:2, ScotBL, Sect.41, Sect.42, UKBAP Passed Awaiting metadata description1 Adult (Count) FEP7/2, LBAP:2, ScotBL, Sect.41, Sect.42, UKBAP Passed Awaiting metadata description1 Present (Count) Bern3, PBA, ScotBL, WO5 Passed Awaiting metadata description

Bern3, PBA, ScotBL, WO5 Pending Awaiting metadata description1 Present (Count) Bern3, PBA, ScotBL, WO5 Pending Awaiting metadata description1 Present (Count) Bern3, PBA, ScotBL, WO5 Passed Awaiting metadata descriptionPresent Adult (Count) Sect.41, Sect.42, UKBAP Passed Awaiting metadata description3 Present (Count) Bern2, CMS_A2, CMS_EUROBATS‐A1, FEP7/2, HabRegs2, HSD4, LBAP:2, LBAP:3, ScotBL, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description1 Present (Count) CMS_A2, HabRegs2, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description1 Present (Count) CMS_A2, HabRegs2, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description1 Present (Count) CMS_A2, HabRegs2, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description

CMS_A2, HabRegs2, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata descriptionCMS_A2, HabRegs2, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata descriptionCMS_A2, HabRegs2, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description

1 Adult Female (Count) CMS_A2, HabRegs2, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description1 Present (Count) CMS_A2, HabRegs2, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description

CMS_A2, HabRegs2, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description1 Juvenile Female (Count) CMS_A2, HabRegs2, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description1 Adult Male (Count) CMS_A2, HabRegs2, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description1 Adult Male (Count) CMS_A2, HabRegs2, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description1 Male (Count) CMS_A2, HabRegs2, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description1 Adult Female (Count) CMS_A2, HabRegs2, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description1 Adult Male (Count) CMS_A2, HabRegs2, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description

Bern2, Bern3, CMS_A2, CMS_EUROBATS‐A1, FEP7/2, HabRegs2, HSD4, LBAP:2, ScotBL, Sect.42, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description500 Present (Count) Bern2, Bern3, CMS_A2, CMS_EUROBATS‐A1, FEP7/2, HabRegs2, HSD4, LBAP:2, ScotBL, Sect.42, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description

Bern2, Bern3, CMS_A2, CMS_EUROBATS‐A1, FEP7/2, HabRegs2, HSD4, LBAP:2, ScotBL, Sect.42, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description1 Female (Count) Bern2, Bern3, CMS_A2, CMS_EUROBATS‐A1, FEP7/2, HabRegs2, HSD4, LBAP:2, ScotBL, Sect.42, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description6 Present (Count) Bern2, Bern3, CMS_A2, CMS_EUROBATS‐A1, FEP7/2, HabRegs2, HSD4, LBAP:2, ScotBL, Sect.42, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description4 Present (Count) Bern2, Bern3, CMS_A2, CMS_EUROBATS‐A1, FEP7/2, HabRegs2, HSD4, LBAP:2, ScotBL, Sect.42, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description1 Present (Count) Bern2, Bern3, CMS_A2, CMS_EUROBATS‐A1, FEP7/2, HabRegs2, HSD4, LBAP:2, ScotBL, Sect.42, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description

Bern2, Bern3, CMS_A2, CMS_EUROBATS‐A1, FEP7/2, HabRegs2, HSD4, LBAP:2, ScotBL, Sect.42, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata descriptionBern2, Bern3, CMS_A2, CMS_EUROBATS‐A1, FEP7/2, HabRegs2, HSD4, LBAP:2, ScotBL, Sect.42, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata descriptionBern2, Bern3, CMS_A2, CMS_EUROBATS‐A1, FEP7/2, HabRegs2, HSD4, LBAP:2, ScotBL, Sect.42, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata descriptionBern2, Bern3, CMS_A2, CMS_EUROBATS‐A1, FEP7/2, HabRegs2, HSD4, LBAP:2, ScotBL, Sect.42, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata descriptionBern2, Bern3, CMS_A2, CMS_EUROBATS‐A1, FEP7/2, HabRegs2, HSD4, LBAP:2, LBAP:3, ScotBL, Sect.42, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description

1 Juvenile Female (Count) Bern2, Bern3, CMS_A2, CMS_EUROBATS‐A1, FEP7/2, HabRegs2, HSD4, LBAP:2, LBAP:3, ScotBL, Sect.42, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description30 Present (Count) Bern2, Bern3, CMS_A2, CMS_EUROBATS‐A1, FEP7/2, HabRegs2, HSD4, LBAP:2, LBAP:3, ScotBL, Sect.42, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5b Passed Awaiting metadata description

Bern2, Bern3, CMS_A2, CMS_EUROBATS‐A1, FEP7/2, HabRegs2, HSD4, LBAP:2, LBAP:3, ScotBL, Sect.41, Sect.42, UKBAP, WCA5/9.4b, WCA5/9.4c, WCA5/9.5a, WCA5/9.5 Passed Awaiting metadata description

Appendix

IV

Appendix IV


Target Notes

Target Note 1 Single hole badger sett in northern bank of dry ditch. Disused.

Target Note 2 Three hole badger sett, cobwebbed. One hole had collapsed.

Additional two hole sett, signs of rabbit. Dung pit opposite in field.

Target Note 3 Two badger dung pits.

Appendix

V

Appendix V


Tytton Lane Development, South of Boston Delta-Simons Project No. 13-0525.02

Photograph 1 – Broadleaved plantation at eastern extent of Site 2

Photograph 2 – Dense scrub – Site 3


Photograph 3 – Wet ditch with overhanging vegetation

Photograph 4 – Recolonising arable field


Photograph 5 – Dry ditch

Photograph 6 – Cycle/footpath Site 2

extended phase 1 habitat survey south of tytton lane east...

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