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St Mary Redcliffe Project 450 RIBA 2 Stage End Report

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2 Method<br />

2.8 A list of other species considered during the Extended Phase 1 Habitat Survey are listed below:<br />

• Badger<br />

• Dormice<br />

• Great Crested Newt (GCN)<br />

2.1 The methods adopted in the survey throughout the assessment are outlined below. They accord<br />

with the good practice guidance documents for ecological survey and assessment produced by the<br />

Chartered Institute of Ecology and Environmental Management 1 and the British <strong>St</strong>andards<br />

Institute 2 .<br />

Desk <strong>St</strong>udy<br />

2.2 To provide additional background information to the report, and to highlight any potential habitat<br />

and/or species that may be influenced over the proposed changes to the Site, an evaluation of<br />

pre-existing biological records was undertaken. A data search for statutory designated sites within<br />

a 5km of the Site was undertaken as well as a data search for non-statutory designated sites, bat<br />

records and other notable species groups within 2km of the Site.<br />

2.3 Data was both requested and collated from the following sources:<br />

• Bristol Regional Environmental Records Centre (BRERC); and<br />

• Multi-Agency Geographical Information for the Countryside (MAGIC).<br />

2.4 Absence of species records within the desk study from the biological records does not equate to<br />

absence in reality. Species distributions were interpreted with caution as they may reflect surveyreporting<br />

effort rather than actual distributions.<br />

Extended Phase 1 Habitat Survey<br />

2.5 A Phase 1 Habitat Survey was undertaken. This survey is a rapid, standardised approach to<br />

categorising different habitat types within any given terrestrial site, and was carried out within the<br />

Site boundary.<br />

2.6 A DAFOR scale was applied to the species listed within each habitat type. A DAFOR scale assigns a<br />

letter to a species based on how prominent they are within that particular habitat, it is at the<br />

discretion of the surveyor to decide what label to assign to a particular species. DAFOR translates<br />

as:<br />

• D – Dominant<br />

• A – Abundant<br />

• F – Frequent<br />

• O – Occasional<br />

• R – Rare<br />

2.7 The survey was ‘extended’ by considering the suitability of the Site for notable or protected fauna<br />

and flora. Species considered included those identified within the desk study, or those considered<br />

appropriate by the surveyor whilst on Site. The survey was conducted by Greg Nightingale BSc,<br />

ACIEEM and Isaac Hogan BSc, MSc, QCIEEM on 12 th August 2019. Weather conditions were sunny<br />

and dry.<br />

• Nesting Birds<br />

• Reptiles<br />

Bats<br />

2.9 Several different bat surveys were carried out as to assess the Site’s suitability to support bat<br />

roosts. The following surveys were undertaken: Preliminary Roost Assessment, Preliminary<br />

Hibernation Assessment, Ground Level Assessment (GLA) and <strong>End</strong>oscope Surveys.<br />

2.10 All features were examined using a torch (CB2-L1) Clubman Deluxe Li-Ion 12V 8.8 AH and<br />

binoculars (Pentax Papilio ll 5x21)). The search took place on the 12 th August 2019, conducted by<br />

Greg Nightingale (Class 2 Bat Licence holder) and Isaac Hogan. The survey methods used is in<br />

accordance with Bat Conservation Trust (BCT) guidelines 3 .<br />

2.11 Only the areas of the Site to be affected by the proposals were assessed (i.e. a complete survey<br />

of the church was not carried out as the church would largely be unaffected by the proposals).<br />

Information gathered was then used to evaluate the Bat Roost Potential (BRP, for designation see<br />

Table 2.1) of each feature.<br />

Preliminary Roost Assessment (PRA)<br />

2.12 A PRA of the exterior of the church was undertaken to determine if the building had the potential<br />

to support bat roosts. The PRA on Site included inspecting the north-east and south-east church<br />

walls up to one storey high from the courtyard area only, as these were the areas to be affected<br />

by the proposals. In addition, and external and internal survey of a small outbuilding, located to<br />

the south-east of the church, was undertaken. This is the first step towards establishing whether<br />

there are roosts present in, or access points available on structures or buildings. Features<br />

searched for included: gaps in brickwork/stonework, lifting damaged rendering on walls and lifted,<br />

or under tiles and slates. A thorough search for actual and potential signs, including bats,<br />

droppings, urine splashes ect, were searched for.<br />

Preliminary Hibernation Survey Assessment<br />

2.13 Proposals include below ground work, as a result preliminary hibernation surveys were conducted<br />

in underground spaces beneath the church and northern lawn, including the cellar; the vault; and<br />

a third underground space, to evaluate the suitability for use by bats over winter. A thorough<br />

search for actual and potential signs, including bats, droppings, urine splashes ect, were searched<br />

looked for as well as potential access points into the underground area. including all vents, ducts,<br />

and surfaces.<br />

Ground Level Assessment (GLA)<br />

2.14 All trees within the Site underwent a GLA. This included all trees found within the southern lawn.<br />

The assessment involved a detailed inspection of a tree from ground level to identify any Potential<br />

Roost Features (PRFs) that could be used by bats to roost. PRF searched for included: woodpecker<br />

holes, loose bark, hollow trunks, cavities, splits and cracks along branches, and dense ivy lattices.<br />

<strong>End</strong>oscope Survey<br />

2.15 PRFs found during the GLA, which were within close proximity to the proposed works was subject<br />

to an endoscope survey (Video Borescope N85NH). This enabled a detailed review of the potential<br />

for the PRF to support a bat roost. Evidence such as: droppings, grease marks and staining,<br />

1 Survey guidance is available at http://www.cieem.net/sources-of-survey-methods-sosm- and appraisal guidance is available at<br />

http://www.cieem.net/guidance-on-preliminary-ecological-appraisal-gpea-<br />

3 Collins, J. (ed.) (2016) Bat Surveys for Professional Ecologists: Good Practice Guidelines (3rd ed). The Bat Conservation Trust,<br />

London.<br />

2 British <strong>St</strong>andards Institute (2013). BS42020:2013 Biodiversity – Code of Practice for Planning and Development. BSI, London.<br />

Ecological Impact Assessment for <strong>St</strong>.<strong>Mary</strong>s Church, <strong>Redcliffe</strong> 8 September 2019<br />

Ecological Impact Assessment for <strong>St</strong>.<strong>Mary</strong>s Church, <strong>Redcliffe</strong> 7 September 2019

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