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Renfrewshire Council · 15 November 2022
Back to Local Review Body. — 15 November 2022 and its agenda

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Page 1

PLANNING
AUTHORITY’S
SUBMISSIONS

Page 2

Chief Executive's Service
Renfrewshire House
Cotton Street, Paisley, PA1 1WB
//www.renfrewshire.gov.uk
My Ref: 
Contact: James Weir
Telephone: 07483 370666
Email: dc@renfrewshire.gov.uk
Date: 12 July 2022 
Stephen Govan 
Proposal: Erection of dwellinghouse with associated access (in principle)
Location: Site On Western Boundary Of Marypark, Marypark Road, Langbank, , 
Application Type: Planning Permission in Principle
Application No: 22/0125/PP 
Dear Sir/Madam, 
NOTIFICATION OF REFUSAL OF CONSENT 
The Council has decided to refuse your application, details of which are given above. I enclose
a Decision Notice which provides details of the reasons for refusal. I also enclose a copy of your
submitted plans duly endorsed. 
You have the right to appeal against this decision to the Local Review Body and notes on how
to appeal are attached. 
Yours faithfully,
Alasdair Morrison
Head of Economy and Development

Page 3

Page 1 of 3 
Chief Executive's Service
Renfrewshire House
Cotton Street, Paisley, PA1 1WB
//www.renfrewshire.gov.uk
REFUSE Consent subject to the reasons 
Ref.  22/0125/PP     
DECISION NOTICE 
Town and Country Planning (Scotland) Act 1997
Planning etc. (Scotland) Act 2006
Town and Country Planning (Development Management Procedure) (Scotland) Regulations 2013     
TO
Mr Arthur MacMillan
Finlaystone House
Finlaystone Estate
Langbank
Port Glasgow
PA14 6TJ 
With reference to your application registered on 22 February 2022 for Planning Consent for the
following development:- 
PROPOSAL
Erection of dwellinghouse with associated access (in principle) 
LOCATION
Site On Western Boundary Of Marypark, Marypark Road, Langbank, 
DECISION
The Council in exercise of their powers under the above Acts and Orders, having considered
the above proposal, the plans endorsed as relating to it and the particulars given in the above
application hereby:- 
REFUSE Consent subject to the reasons listed on the reverse/paper apart. 
PLANS AND DRAWINGS
The plans and drawings relative to this refusal are those identified in the Schedule of
Plans/Drawings attached as a paper apart and forming part of this Decision Notice. 
Dated: 8 July 2022 
Signed ......................................................
Appointed Officer
on behalf of Renfrewshire Council

Page 4

Page 2 of 3 
Ref. 22/0125/PP 
REASON FOR REFUSAL 
PAPER APART 
TERMS AND CONDITIONS 
Reason for Decision 
1. The proposed development does not comply with Policy ENV1 of the Adopted
Renfrewshire Local Development Plan 2021 and the draft New Development
Supplementary Guidance, Green Belt Development Criteria and Housing in the Green
Belt as it has not been demonstrated that there is a specific locational need for a
dwellinghouse and the development has the potential to have an adverse effect on the
integrity of the Site of Importance for Nature Conservation (SINC) and the ancient
woodland. 
2. The proposed development does not comply with Policy ENV2 of the Adopted
Renfrewshire Local Development Plan 2021 and the draft New Development
Supplementary Guidance, Trees, Woodland and Forestry and Local Designations as the
development has the potential to have an adverse effect on the integrity of the Site of
Importance for Nature Conservation (SINC) and the ancient woodland.

Page 5

Page 3 of 3 
TOWN AND COUNTRY PLANNING (SCOTLAND) ACT 1997 
1. If the applicant is aggrieved by the decision to refuse permission for or approval required by a
condition in respect of the proposed development, or to grant permission or approval subject to
conditions, the applicant may require the planning authority to review the case under section
43A of the Town and Country Planning Act (Scotland) Act 1997 within three months beginning
with the date of this notice. The notice of review should be addressed to Head of Legal and
Democratic Services, Renfrewshire House, Cotton Street, Paisley PA1 1PR. 
2. If permission to develop land is refused or granted subject to conditions and the owner of the
land claims that the land has become incapable of reasonably beneficial use in its existing state
and cannot be rendered capable of reasonably beneficial use by the carrying out of any
development which has been or would be permitted, the owner of the land may serve on the
planning authority a purchase notice requiring the purchase of the owner of the land's interest in
the land in accordance with Part 5 of the Town and Country Planning (Scotland) Act 1997.

Page 6

Appendix 1 
RENFREWSHIRE COUNCIL  Application No: 22/0125/PP
CHIEF EXECUTIVE’S SERVICE
RECOMMENDATION OF PLANNING APPLICATION
Regd:22 February 2022  
Applicant Agent
Mr Arthur MacMillan
Finlaystone House
Finlaystone Estate
Langbank
Port Glasgow
PA14 6TJ 
Stephen Govan
Ingram Architecture & Design
227 Ingram Street
Glasgow
G1 1DA 
Nature of Proposals
Erection of dwellinghouse with associated access (in principle) 
Site
Site On Western Boundary Of Marypark, Marypark Road, Langbank, 
Description 
This application seeks planning permission in principle for the erection of a dwellinghouse on a
site to the west of Marypark House in Langbank. The site is accessed from Marypark Road which
is a private single track road serving nine houses. Marypark Road is accessed from the A8 trunk
road to the west of the site. 
The application site extends to approx. 700 square metres. It is situated in an area of woodland,
with rising ground and a rocky outcrop to the west and south. To the east is another development
plot on which planning permission in principle for a dwellinghouse was granted in 2019. The
proposed house and the consented house would share the same access. Beyond the
development plot to the east is Marypark House. Marypark Road bounds the site to the north with
the A8 beyond. 
History 
Application No: 19/0516/PP
Description: Erection of dwellinghouse and formation of access (planning consent in principle)
Decision: Grant subject to conditions 
Policy and Material Considerations 
Adopted Renfrewshire Local Development Plan 2021
Policy ENV1 – Green Belt
Policy ENV2 – Natural Heritage
Policy P1 – Renfrewshire’s Places
Policy I1 – Connecting Places
Policy I3 – Flooding and Drainage 
Draft New Development Supplementary Guidance
Delivering the Environment Strategy – Green Belt Development Criteria, Housing in the Green

Page 7

Belt, Local Designations and Trees, Woodlands and Forestry
Delivering the Places Strategy – Creating Places
Delivering the Infrastructure Strategy – Connecting Places, Flooding and Drainage 
Material Considerations
Renfrewshire’s Places Residential Design Guide 
Publicity 
The Council has undertaken neighbour notification in accordance with the requirements of
legislation. 
An Advert was placed on the press on 9 March 2022 for the following reasons;
Neighbour Notification. 
Objections/Representation 
None received. 
Consultations 
Environment & Infrastructure Services - (Roads) – No comments. 
Communities & Housing Services - (Environmental Protection Team) – Advisory note
requested should ground disturbance uncover any contamination or unusual materials. 
Transport Scotland – No objections. 
Glasgow Airport Safeguarding – No comments. 
Applicants Supporting Information 
Tree Survey – Trees within the site are entirely self seeded surviving among areas of invasive
rhododendron. There are fourteen low quality trees and one medium quality cherry tree. The
overall biological value of the plot is considered low. 
Ecological Constraints Survey – Proposed development may impact the integrity of the Site of
Importance for Nature Conservation (SINC) and the ancient woodland. However, the effects are
likely to be short term and mainly during construction works. 
If development is kept to the open area of the site, then it is likely that only limited limbing and
felling of young trees would be required. The open area has previously been cleared and is now
dominated by rhododendron. 
The site has suitable habitat for badgers and nesting birds. However, no evidence of badgers was
identified on the site. Two trees were found to be suitable for roosting bats. However again there
is no evidence that they are being used by bats. 
Various recommendations are made with respect to the development of the site. These include
vegetation clearance outwith the bird nesting season, retention of the vegetation line along the

Page 8

northern edge of the site, and timing of works on site to avoid disturbance to foraging or
commuting bats. 
Flood Risk Assessment – The site is at medium to high risk of flooding from fluvial sources and
failure of drainage infrastructure. Mitigation measures include forming a maintenance wayleave
along the eastern boundary of the site, raising ground levels to mimic those along the eastern
boundary, a 200mm freeboard, and confirming responsibility for maintenance of a culvert. The
development will not increase the flood risk at neighbouring properties and is in general
accordance with the principles set out in Scottish Planning Policy. 
Assessment 
The application site is covered by both Policy P1 and Policy ENV1 designations within the
adopted Renfrewshire Local Development Plan 2021. The Policy P1 area relates to the proposed
access which would be shared between the proposed dwellinghouse and the dwellinghouse
approved on the plot to the east. Most of the site, including the area on which the dwellinghouse
will be sited, is covered by Policy ENV1. 
As most of the site area is covered by Policy ENV1, it is considered that assessment against this
policy should take precedence. 
Policy ENV1 states that development within the green belt will be considered appropriate in
principle where it is a housing land shortfall remedy which satisfies Policy 8 of Clydeplan or is in
support of certain uses. It also states that development within the green belt will only be
considered acceptable where it can be demonstrated that it is compatible with the provisions of
the New Development Supplementary Guidance. 
A housing land shortfall has not been identified. Therefore, the proposal requires to be assessed
against the other criteria that allow development of this type to come forward and the criteria
within the draft New Development Supplementary Guidance (SG). 
The SG states that development can be acceptable in principle where it is for a purpose in support
of acceptable green belt uses. Green Belt Development Criteria provides a set of guidance that all
development require to meet, including that traffic and access infrastructure can be sensitively
accommodated and that it has been demonstrated that there has been careful consideration of the
siting, design, scale and grouping of any buildings and infrastructure. Further to this guidance
Housing in the Green Belt states residential development proposals require to be assessed
against the following criteria. 
Development is required to maintain and support an established activity 
The development is not required to maintain or support an established activity that is suitable in
the green belt. 
There is a need for the residential use to be located outwith the settlement   
It has not been demonstrated that there is a need for the development to be located outwith the
settlement. 
Buildings which have special architectural, traditional or historic character may be converted for
residential use

Page 9

The development does not involve the conversion of an existing building. 
The proposal demonstrates outstanding quality of design, is of an appropriate scale within its
setting, and makes a positive contribution to the site and surrounding area 
As the application is in principle only no design details have been provided. The applicant has
provided a site plan which shows a dwellinghouse could be accommodated on the plot with
respect to its dimensions. There is not any significant tree coverage on this part of the site, and
only self-seeded trees of low quality would have to be removed to accommodate the development.
The topographical constraints are acknowledged, and the submitted levels plan shows that most
of the rear curtilage would be on steeply sloping ground. Whilst it is noted that a similar
topographical relationship was accepted at the neighbouring plot it is also noted that the
ecological survey submitted has indicated that this proposal may impact the integrity of the SINC
and the ancient woodland that the site is located within. 
The proposal integrates with, complements and enhances the established character of the area 
As the application is in principle only no design details have been provided. However, as the plot
is enclosed by sloping ground and tree coverage to the south, east and west and the A8 trunk
road to the north it is unlikely that development would be overly visible. However, it has the
potential to have an adverse impact on the SINC and the ancient woodland. 
Replacement dwellings should reflect the specific character of the location, fit well with the
surrounding landscape and achieve a high design standard 
The proposed development does not constitute a replacement dwellinghouse. 
It is noted that the applicant has submitted survey work relating to trees, ecology, topography, and
flood risk which determines that the site’s constraints could potentially be overcome. However, the
proposal does not meet the criteria required in assessment of this type of development for the
above reasons. 
The development must also be assessed against the green belt development criteria. 
There is no loss of prime quality agricultural land associated with the proposals. It is also not
anticipated that the development poses a significant pollution risk with respect to public water
supply and water courses. 
There is no requirement to provide access to open space. 
Whilst it is noted that an argument has been made that the development can be accommodated
with limited impact on identified nature conservation interests there is potential that the
development may impact the integrity of the SINC and the ancient woodland that the site is
located within. 
The northern boundary of the site is defined by a stone wall. Removing part of the wall to form an
access has already been accepted through the approval of application 19/0516/PP. Both the
proposed dwellinghouse and the previously approved dwellinghouse would share the same
access.

Page 10

It is unlikely that the development would have a significant adverse impact on landscape character
given the characteristics of the site. The proposed development continues the ribbon style of
residential development along the southern side of Marypark Road. Further development to the
south and west of the site wouldn’t be possible given the topography and tree coverage which
encloses the site. 
The applicant has advised that a connection could be made to the public water supply and
drainage network. Further details regarding the disposal of foul and surface water could be
controlled via condition. 
Policy ENV2 states that development proposals must consider the potential impact on natural
heritage. Further guidance is provided in the SG on Trees, Woodlands and Forestry and Local
Designations. 
The ecology report and tree survey submitted with the application conclude that the site is of low
natural heritage value despite its location within an ancient woodland and SINC. It is notable from
the site visit that the site has been cleared of trees in the past, and invasive rhododendron is now
present. The trees which are present are self-seeded, with the tree survey noting that the majority
are of low quality. The ecology report advises that the development may impact the integrity of the
SINC and the ancient woodland but that the effects are likely to be short term and mainly during
construction works. Whilst it is recognised that the applicant seeks consent in principle for the
erection of a dwellinghouse it is considered that to allow any development to be formed
substantial works would be required and that there is insufficient information to demonstrate that
the development would not affect the integrity of the ancient woodland and SINC has not been
established. 
Policy P1 states that within Renfrewshire’s Places there will be a general presumption in favour of
a continuance of the built form. As noted above the principal assessment has been undertaken
against policy ENV1 as the bulk of the site is covered by this designation. However, Policy P1 is
still considered to be relevant with respect to matters of amenity and compatibility. 
The Environmental Protection team have raised no concerns with respect to statutory nuisances
such as noise affecting the site. The indicative site plan also demonstrates that the relationship
between the proposed dwellinghouse and the neighbouring plot is likely to be acceptable with
respect to maintaining sufficient levels of privacy and daylight. 
Policy I1 states that all development proposals require to ensure appropriate provision for
accessibility. 
In this instance the Environment and Infrastructure Service (Road) has not offered any formal
comments as the development falls outwith their jurisdiction (the site is serviced from a private
road which connects to a trunk road). However, they have recommended that any development is
undertaken in accordance with the standards set out within the National Roads Development
Guide. 
It is noted that Transport Scotland have not objected to the proposals. 
With respect to Policy I3, the Flood Risk Assessment confirms that the presence of a culvert to the
southeast of the site is not a barrier to development subject to the incorporation of some
recommendations. The development will not increase the flood risk at neighbouring properties and
is in general accordance with the principles set out in Scottish Planning Policy.

Page 11

In conclusion, the applicant has demonstrated the principle that the development plot could
accommodate a dwellinghouse. A continuation of the existing development pattern along the
southern side of Marypark Road is not considered to be undesirable. The topography and
woodland coverage to the south and west largely screens the site from external vantage points. 
However, the proposal does not comply with the adopted Renfrewshire Local Development Plan
or the draft New Development Supplementary Guidance as it has not been demonstrated that
there is a specific locational need for a dwellinghouse in this green belt location and the details
provided of the development are such that it has not been fully demonstrated that the
development would not have an adverse impact on the integrity of the SINC or the ancient
woodland given the works required to form such a development. It is therefore considered that the
application must be refused. 
Index of Photographs
A site visit has been undertaken on 13 December 2021, and photographs relevant to the
application have been archived. 
RECOMMENDATION 
Refuse. 
Reason for Decision 
1. The proposed development does not comply with Policy ENV1 of the Adopted
Renfrewshire Local Development Plan 2021 and the draft New Development
Supplementary Guidance, Green Belt Development Criteria and Housing in the Green Belt
as it has not been demonstrated that there is a specific locational need for a dwellinghouse
and the development has the potential to have an adverse effect on the integrity of the Site
of Importance for Nature Conservation (SINC) and the ancient woodland. 
2. The proposed development does not comply with Policy ENV2 of the Adopted
Renfrewshire Local Development Plan 2021 and the draft New Development
Supplementary Guidance, Trees, Woodland and Forestry and Local Designations as the
development has the potential to have an adverse effect on the integrity of the Site of
Importance for Nature Conservation (SINC) and the ancient woodland.

Page 12

Applicant:   Mr Arthur MacMillan  Ref. No: 22/0125/PP
Site:           Site On Western Boundary Of
Marypark
Marypark Road
Langbank 
Officer:    James Weir 
Documents 
Document Document Attached
(Admin)

Document Attached
and Signed

Decision Letter  
Decision Notice  
Appendix 1 – Report of Handling    
Plans to be stamped 
Drawing Number Drawing Title Checked
Paper/DMS 
(Officer)

Stamped
DMS
(BS)

1720(2-)01 A Site Plan as Existing  
1720(2-)02 B Site Plan as Proposed  
1720(2-)03 Existing and Proposed Block Plan  
AP1579/Topo/01 Topographical Survey  
1720(2-)00 Location Plan                                   
Officers Initials: JW   Business Support Initials: __DM_____

Page 13

Notes:
1. This drawing is the property of
Ingram Architecture & Design
Limited and must not be disclosed,
loaned or copied without the written
permission of Ingram Architecture
& Design
2. All sizes in  millimetres
3. Do not scale from drawings
4. Any discrepancies to be notified
to client/architect immediately
5. All sizes to be checked on site
revision
1:500@A3 Mar 17
A
Site Plan
Arthur Macmillan
Marypark Road
Proposed Housing
1720(2-)01
As Existing
drawing
scale
project
client
date
revnumber
INGRAM
A r c h i t e c t u r e  &  D e s i g n
227 Ingram Street Glasgow
G1 1DA       0141 221 5191
getus@ingramarchitecture.co.uk
www.ingramarchitecture.co.uk
NORTH
Marypark
House
Woodview
Cottage Briarwood
MARYPARK ROAD
GREENOCK ROAD
A Planning 17.02.22
0 10 20 50 METRES

Page 14

8.93
Notes:
1. This drawing is the property of
Ingram Architecture & Design
Limited and must not be disclosed,
loaned or copied without the written
permission of Ingram Architecture
& Design
2. All sizes in  millimetres
3. Do not scale from drawings
4. Any discrepancies to be notified
to client/architect immediately
5. All sizes to be checked on site
revision
1:500@A3 Mar 17
B
Site Plan
Arthur Macmillan
Marypark Road
Proposed Housing
1720(2-)02
As Proposed
drawing
scale
project
client
date
revnumber
INGRAM
A r c h i t e c t u r e  &  D e s i g n
227 Ingram Street Glasgow
G1 1DA       0141 221 5191
getus@ingramarchitecture.co.uk
www.ingramarchitecture.co.uk
new opening
in wall
NORTH
Marypark
House
Woodview
Cottage Briarwood
MARYPARK ROAD
GREENOCK ROAD
Plot 1
Plot 2
existing
water
course
A Design Development 17.11.17
B Planning 17.02.22
0 10 20 50 METRES
Plot 1
previously
granted
Permission in
Principle
19/0516/PP

Page 15

LP
LP
TP
AP2
6.610
AP1
6.879
AP3
11.592
AP4
10.928
9.54
9.18
9.40
9.15
9.12
8.96
8.81
8.78
8.64
8.61
7.08
6.98
7.09
7.11
7.02
7.29
6.99
6.78
6.80
6.74
6.70
6.65
6.68
6.59
6.57
6.62
6.64
6.72
6.68
6.96
6.74
6.73
6.72
6.68
6.64
6.63
7.37
7.04
11.68
9.83
9.38
8.93
8.74
9.18
9.47
9.95
10.28
10.21
10.21
9.51
9.77
10.33
11.45
10.67
11.89
13.87
17.03
14.45
17.18
12.22
12.85
11.61
10.51
12.46
11.49
13.22
13.32
14.15
13.79
14.96
15.50
17.06
18.42
9.62
9.41
9.75
10.11
10.16
11.17
12.70
14.87
11.19
10.46
13.61
15.29
19.79
12.17
14.39
16.53
18.12
15.76
14.11
13.92
12.76
11.69
11.58
13.2614.23
13.38 13.61
15.01
15.74
15.37
12.56
10.23
9.19
8.45
8.33
8.11
8.24
8.83
8.22
8.15
8.56
9.29
10.41
9.23
9.57
10.31
10.73
10.28
10.59
10.67 10.81
14.91
13.98
11.70
12.25
12.67
14.88
14.09
18.87
19.39
19.43
18.47
16.61
15.5017.58
13.70
12.43
11.22
10.52
9.99
9.57
9.05
8.76
12.00
10.93
13.66
14.29
8.03
8.23
9.43
8.97
8.74
8.33
9.85
9.65
10.21
Marypark Road
Trees
Trees
Trees
Trees
Trees
Trees
Stone Wall 1.2m
Stone Wall 1.2m
Stn : AP1
E : 237565.876
N : 673477.898
Z : 6.879
Stn : AP2
E : 237545.414
N : 673469.159
Z : 6.610
Stn : AP3
E : 237556.899
N : 673453.231
Z : 11.592
Property
Boundary Marker
Property
Boundary Marker
900MM DIA
1300MM DIA
Stn : AP4
E : 237590.425
N : 673451.715
Z : 10.928
Rock Face
Rock Face
Rock Face
Rock Face
Post and Wire Fencing 1.1m
Overhead Line
Dilapidated
Metal Railing
1.1m
Trees
Trees
Grass
Grass
GrassLP
LP
TP
AP2
6.610
AP1
6.879
AP3
11.592
AP4
10.928
9.54
9.18
9.40
9.15
9.12
8.96
8.81
8.78
8.64
8.61
7.08
6.98
7.09
7.11
7.02
7.29
6.99
6.78
6.80
6.74
6.70
6.65
6.68
6.59
6.57
6.62
6.64
6.72
6.68
6.94
6.96
6.74
6.73
6.72
6.68
6.64
6.63
7.37
7.04
6.98
11.68
9.83
9.38
8.93
8.74
9.18
9.47
9.95
10.28
10.21
10.21
9.51
9.77
10.33
11.45
10.67
11.89
13.87
17.03
14.45
17.18
12.22
12.85
11.61
10.51
12.46
11.49
13.22
13.32
14.15
13.79
14.96
15.50
17.06
18.42
9.62
9.41
9.75
10.11
10.16
11.17
12.70
14.87
11.19
10.46
13.61
15.29
19.79
12.17
14.39
16.53
18.12
15.76
14.11
13.92
12.76
11.69
11.58
13.2614.23
13.38 13.61
15.01
15.74
15.37
12.56
10.23
9.19
8.45
8.33
8.11
8.24
8.83
8.22
8.15
8.56
9.29
10.41
9.23
9.57
10.31
10.73
10.28
10.59
10.67 10.81
14.91
13.98
11.70
12.25
12.67
14.88
14.09
18.87
19.39
19.43
18.47
16.61
15.5017.58
13.70
12.43
11.22
10.52
9.99
9.57
9.05
8.76
12.00
10.93
13.66
14.29
8.03
8.23
9.43
8.97
8.74
8.33
9.85
9.65
10.21
Marypark Road
Trees
Trees
Trees
Trees
Trees
Trees
Dense Vegetation
Post
and
Wire
Fencing
1.1m
Stone Wall 1.2m
Stone Wall 1.2m
Stn : AP1
E : 237565.876
N : 673477.898
Z : 6.879
Stn : AP2
E : 237545.414
N : 673469.159
Z : 6.610
Stn : AP3
E : 237556.899
N : 673453.231
Z : 11.592
Property
Boundary Marker
Property
Boundary Marker
900MM DIA
1300MM DIA
Stn : AP4
E : 237590.425
N : 673451.715
Z : 10.928
Rock Face
Rock Face
Rock Face
Rock Face
Post and Wire Fencing 1.1m
Overhead Line
Dilapidated
Metal Railing
1.1m
Dilapidated
Metal
Railing
1.1m
Trees
Trees
Grass
Grass
Grass
new opening
in wall
NORTH
Marypark
House
shared
access
bins
Notes:
1. This drawing is the property of
Ingram Architecture & Design
Limited and must not be disclosed,
loaned or copied without the written
permission of Ingram Architecture
& Design
2. All sizes in  millimetres
3. Do not scale from drawings
4. Any discrepancies to be notified
to client/architect immediately
5. All sizes to be checked on site
Feb 221:200@A1
-
Existing & Proposed
Arthur Macmillan
Marypark Road
1720(2-)03
Block Plan
revision
INGRAM
A r c h i t e c t u r e  &  D e s i g n
drawing
scale
project
client
date
revnumber
227 Ingram Street Glasgow
G1 1DA       0141 221 5191
getus@ingramarchitecture.co.uk
www.ingramarchitecture.co.uk
A - -
0 1
Proposed Housing
bins
2 3 4 5 10 25 METRES
SITEPLAN AS EXISTING 1:200
SITEPLAN AS PROPOSED 1:200
Plot 1
previously
granted
Permission in
Principle
19/0516/PP

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International House,
Hamilton International Park,
Stanley Boulevard,
Hamilton,
G72 0BN 
www.terrenus.co.uk
Directors:  William Hume       Company Reg. No. SC464672 
MARYPARK ROAD, LANGBANK
FLOOD RISK ASSESSMENT
FOR
ARTHUR MACMILLAN
Report No.: 1800-200 Version: FINAL
Revision: - Issue Date: 24th September 2019
Authors: RA/WH

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MARYPARK ROAD, LANGBANK
FLOOD RISK ASSESSMENT
FOR
ARTHUR MACMILLAN 
SITE SUMMARY INFORMATION 
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Name of Site: Marypark Road, Langbank
Ordnance Survey Grid Reference: NS 37598 73469
Site Address: Marypark Road, Langbank, Renfrewshire    
PA14 6UT
Local Authority: Renfrewshire Council
Current Site Use: Wooded overgrown land
Proposed Site Use: Residential Development 
Area (hectares): 0.1 ha approx.
On site buildings: No current buildings
Type of Investigation: Level 2 Flood Risk Assessment

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MARYPARK ROAD, LANGBANK
FLOOD RISK ASSESSMENT
FOR
ARTHUR MACMILLAN 
TABLE OF CONTENTS 
SECTION          PAGE 
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1 INTRODUCTION .................................................................................................................................... 1
1.1 BACKGROUND ............................................................................................................................ 1
1.2 OBJECTIVES OF INVESTIGATION ........................................................................................ 1
1.3 SCOPE OF STUDY ....................................................................................................................... 1
1.4 PROPOSED SITE END-USE ....................................................................................................... 1
1.5 LIMITATIONS OF REPORT ...................................................................................................... 1
2 SITE DETAILS ......................................................................................................................................... 2
2.1 DATA SOURCES .......................................................................................................................... 2
2.2 SITE LOCATION & DESCRIPTION ......................................................................................... 2
2.3 SITE NEIGHBOURS .................................................................................................................... 3
2.4 GEOLOGICAL SETTING ........................................................................................................... 3
2.5 HYDROLOGY AND DRAINAGE............................................................................................... 3
2.5.1 SEPA Flood Map ............................................................................................................................ 4
2.6 RIVER CLYDE FLOOD MODELLING .................................................................................... 5
2.7 GROUNDWATER ......................................................................................................................... 5
3 FLOOD RISK ASSESSMENT ................................................................................................................ 6
3.1 GENERAL ...................................................................................................................................... 6
3.2 FLUVIAL FLOOD RISK .............................................................................................................. 6
3.3 SURFACE WATER ....................................................................................................................... 6
3.4 LOCAL DRAINAGE ..................................................................................................................... 6
3.5 COASTAL FLOODING ............................................................................................................... 7
3.6 GROUNDWATER RISE .............................................................................................................. 7
4 DISCUSSION AND RECOMMENDATIONS ....................................................................................... 8
4.1 GENERAL CONCLUSIONS........................................................................................................ 8
4.2 DEVELOPMENT AND POSSIBLE MITIGATION MEASURES .......................................... 8
4.3 EFFECTS ON SITE NEIGHBOURS .......................................................................................... 8
4.4 OVERALL FLOOD RISK ASSESSMENT CONCLUSION .................................................... 8

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MARYPARK ROAD, LANGBANK
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ARTHUR MACMILLAN 
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Figures
Fig 1 - Site Location 
Fig 2 – Additional Survey Works
Fig 3 – Overland Flow Pathways
Fig 4 –Catchment Analysis
Photographic Plates

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MARYPARK ROAD, LANGBANK
FLOOD RISK ASSESSMENT
FOR
ARTHUR MACMILLAN 
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1 INTRODUCTION
1.1 BACKGROUND
The development of a parcel of land at the eastern extent of Finlaystone House Estate, south of
Marypark Road, Langbank is currently under consideration by Arthur MacMillan.
In order to meet the requirements of the Planning process, Terrenus Land & Water Ltd were
approached by Arthur MacMillan, to undertake a flood risk assessment for the site.
1.2 OBJECTIVES OF INVESTIGATION
The principal aim of the assessment is to develop an understanding of the flood risk to the site and the
proposed development. Consideration of feasible mitigation measures if required also forms part of
the investigation. 
1.3 SCOPE OF STUDY
The following tasks were undertaken during the course of this investigation:
 Collation of data;
 Site walkover inspection;
 Assessment of data;
 Undertake a qualitative assessment of the potential impacts of and constraints to the proposed
layout; and
 Production of an Interpretative Report.
1.4 PROPOSED SITE END-USE
It is understood that the proposed development will entail the construction of a single residential
dwelling with access off Marypark Road. Proposed layout plans were not available at the time of
writing this report.
1.5 LIMITATIONS OF REPORT
Terrenus Land & Water Ltd. has prepared this report for the sole use of the Client, in accordance with
generally accepted consulting practice and for the intended purpose as stated in the related contract
agreement. No other warranty, expressed or implied, is made as to the professional advice included in
this report. Should any third party wish to use or rely upon the contents of the report, written approval
must be sought from Terrenus Land & Water Ltd; a charge may be levied against such approval.
To the best of our knowledge, information contained in this report is accurate at the date of issue.
There may be conditions pertaining at the site not disclosed by the study, which might have a bearing
on the recommendations provided if such conditions were known. We have, however, used our
professional judgement in attempting to limit this during the assessment.
It is important therefore that these implications be clearly recognised when the findings of this study
are being interpreted. In addition, this should be borne in mind if this report is used without further
confirmatory investigation after a significant delay.

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2 SITE DETAILS
2.1 DATA SOURCES
The following data sources were consulted during the course of the Flood Risk Assessment:
 Client supplied information;
 SEPA Flood Maps;
 British Geological Survey Interactive Map (Geology of Britain Viewer);
 Publicly available on-line aerial imagery and mapping;
 Publicly available on-line historic maps; 
 River Clyde Flood Management Strategy, Hydrodynamic Modelling Report- Halcrow
/Fairhurst; and
 Available additional information including site specific topographic survey of salient points.
2.2 SITE LOCATION & DESCRIPTION
The site is centred around National Grid Reference (NGR) NS 37598 73469 and is shown on Figure 1
in the Appendix. 
Publicly available local maps and site specific topographic survey information were combined with
information obtained during the site walkover to form the basis of the understanding of the site
topography and surrounding area. 
A site walkover inspection was undertaken on the 17th September 2019 and forms the basis of the
following description. A photographic record of the site visit is included in the Appendix to this
report.
The site forms an irregular shaped plot of land covering approximately 0.1ha of land to the south of
Langbank Road in the west of Langbank, Renfrewshire. 
The site is bound to the north by a stonewall along Marypark Road, to the east by a stonewall and
fence to the adjacent property of Marypark House, to the west by a dilapidated metal fence and to the
south is constrained by a steep rock outcrop.
The site slopes down to the north from the base of the rocky outcrop towards Marypark Road. The
area is heavily overgrown with many mature trees and rhododendron bushes (photo 1 and 2). The site
forms the eastern extent of Finlaystone House Estate which lies 1km to the west. There is some
rubble and metal sheeting present at the site which may be associated with the former building that
occupied the site. There is a gap in the stone wall located on the northern boundary that has a wooden
fence across and was formerly a gateway.
Due to the dense tree cover at the site it was difficult to carry out a comprehensive topographic survey
at the site. The relevant salient points that were able to be determined are shown on Fig 2 included in
the Appendix. The topographic survey information together with Ordnance Survey information has
been used to provide information on ground levels in the vicinity of the site.
There is a rocky outcrop located on the southern boundary of the site which is approximately 10m
high. The ground levels at the top of this outcrop are around 25mOD and at the base are
approximately 15mOD. At the southern corner of the site there is a cleft in the cliff face where a
watercourse is present discharging from the ground above. At the base of the cliff the watercourse
enters an old stone culvert.

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The ground surface of the site falls approximately 8m from the base of the cliff face towards
Marypark Road which lies at around 6.8mOD in the vicinity of the site. The central part of the site is
relatively flat lying where the former building occupied the site. 
Marypark Road falls gently to the east and west from the site and lies approximately 2 to 3m above
the adjacent A8 dual carriageway. The duel carriageway itself lies at around 4mOD in the vicinity of
the site.
A review of on-line historic maps shows that on the first edition Ordnance Survey sheet dated 1858
the site comprises land belonging to Finlaystone House Estate with the eastern boundary identified
and the cliff face on the southern boundary of the site. A railway line located to the north of the site.
The 1897 edition records Marypark House being constructed together with Marypark Road. A well is
identified at the base of the cliff 75m to the east of the site.
The 1914 edition identifies the boundaries of the site being a separate parcel of land. A watercourse is
identified ‘rising’ 150m south of the site and flowing towards the cliff face where it terminates. A
well is recorded adjacent to Marypark House at the base of the cliff.
The 1958 edition records little change however the 1968 edition records an alteration in the layout of
the A8 and Marypark Road with a new crossing point beneath the railway line further to the south. A
building is shown present on the southern part of the site which is again recorded on the 1971 edition.
The 1977 edition records the building at the site to be no longer present with the adjacent A8 widened
into a dual carriageway with little change shown on the most recent 1994 edition.
2.3 SITE NEIGHBOURS
To the south and west the site is bordered by open ground, which in the west comprises woodland
belonging to the Finlaystone House Estate. To the north is Marypark Road and an embankment down
to the A8 dual carriageway beyond which lies a railway line and the southern banks of the River
Clyde estuary. To the east is Marypark House and other dwellings located along Marypark Road.
2.4 GEOLOGICAL SETTING
The superficial deposits are likely to be thin or absent beneath the site due to the steeply sloping
nature of the topography of the site.
A southwest to northeast trending geological fault crosses the southern part of the site along the line
of the cliff face present in the southern part of the site. North of this fault the bedrock comprises
sedimentary units of the Inverclyde Group which are Carboniferous in age. South of the fault there is
igneous bedrock, also of the Carboniferous. 
2.5 HYDROLOGY AND DRAINAGE
The Ordnance Survey sheet records an unnamed watercourse terminating at the southern boundary of
the site which rises some 150m to the south of the site. A well is also indicated behind Marypark
House. The watercourse was identified on the Ordnance Survey sheets at the same time as the
building of Marypark House; the culvert at the base of the cliff into which the watercourse sinks may
have been constructed at this time.
During the site walkover there was no defined channel noted in the land above the cliff face (plate 3),
only a boggy area was noted with a change of vegetation approximately 100m south of the site (plate
4). A small amount of water was noted to be flowing down a cleft in the cliff face (plate 5) and
entering the culvert located on the southern boundary of the site at the base of the cliff (plate 6). At
the location of the culvert there is an old stone trough approximately 900mm wide and 1500mm long
(3 foot by 5 foot) surrounding the culvert. The culvert inlet is located in the base of the trough at the
northern end and is 230mm in diameter and has an opening on both the vertical and horizontal face
(plate 8). The culvert is protected by an metal grill as is the top of the southern wall of the trough and
also over the inlet of the culvert.

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Immediately downstream and on the west side of the stone trough, there is a low wall approximately
200mm high and the trace of a fenceline (plates 9 and 10). This relict feature appears to follow the
original land boundary and extends between the northwest corner of the trough and the existing
boundary fence to the neighbouring property. This indicates that the stone trough and culvert are
located on and to the east of the site boundary and not as far west as shown on the current Ordnance
Survey map. In addition, the line of the watercourse recorded on the Ordnance sheet is not considered
representative.
Downstream of the stone trough a 400mm high concrete wall topped with angular cobbles has been
more recently constructed to the rear of Marypark House (plate 11). This wall is orientated northwest
to southeast and appears to have been constructed to prevent any water entering the rear garden of
Marypark House in the event of a blockage of the culvert and overtopping of the stone trough. The
gardens of Marypark House generally lie at a lower level than that of the site itself and without this
cut off wall overland flow would preferentially flow through the neighbour’s garden of Marypark
House.
Anecdotal evidence indicates that Scotland Transerv periodically clear out the culvert and
surrounding area and a pile of angular gravel was noted adjacent to the culvert during the site
walkover (plate 12). During the site walkover large blocks of rock were noted in the base of the cleft
which had fallen from the cliff face and a large tree had fallen across the top of the cleft (plate 13).
The outfall of the culvert was not determined during the site walkover however it is considered likely
that it is connected with drainage infrastructure within Marypark Road or discharges directly into the
River Clyde.
During the site walkover no other seepages were noted along the base of the cliff within the site. The
ground surface of the site is dry and firm. Slight seepages were noted issuing from the base of the
embankment to the north of Marypark Road issuing onto the lower lying ground on adjacent
footpaths (plates 14 and 15).
Along the northern edge of Marypark Road, small channels at the sides of the road have been made
(plates 16 and 17) to assist the drainage of Marypark Road. Limited drainage gulleys were noted
along Marypark Road with a gulley located in front of Woodside View appearing to have been
recently maintained (plate 18).
Limited drainage gulleys were noted along the southern edge of the A8 dual carriageway, however
several gulleys were noted adjacent to the central reservation located along the low point of the
roadway beneath the railway bridge.
2.5.1 SEPA Flood Map
The SEPA flood map does not show any likelihood of fluvial or coastal flooding within the site,
however, surface water and coastal flooding potential is noted over the A8 to the north of the site.
Furthermore, the minor watercourse to the south of the site has a catchment which is too small to be
assessed fluvially by SEPA and is shown as a surface water flood potential along the eastern
boundary of the site.
SEPA makes the following statement about the Flood Map:
“The river flood map was developed using a nationally consistent approach to producing flood
hazard information, such as depth of water and speed of flow arising from river flooding. It is
based on a two-dimensional flood modelling method applied across Scotland to all catchments
greater than 3km2. The river flood map includes hydraulic structures and defences such as
bridges, culverts and flood storage areas where appropriate information was available.

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and
The surface water flood map combines information on rainfall and sewer model outputs. It
incorporates data from a national surface water study, a regional surface water study with
increased resolution in selected areas and a Scottish Water sewer flooding assessment.”
The flood map should be treated with caution and SEPA makes the following general comment:
“The flood maps are designed to provide a community level assessment of flooding and its
impacts. They model flooding at a national scale. As with any approach of this scale, there are
limitations and assumptions made to enable modelling and a consistent approach to be applied
across Scotland. Limitations arise from the data used to create the maps, the modelling
techniques applied and the ability to incorporate datasets from local studies into a national
approach.” 
Additional background details of the SEPA flood map can be found on the SEPA website:
http://www.sepa.org.uk/flooding/flood_maps.aspx
2.6 RIVER CLYDE FLOOD MODELLING
The River Clyde Flood Management Strategy- Hydrodynamic Modelling Report – Flood Defence
Levels for Design prepared by Halcrow and Fairhurst predicts water levels at ISIS cross sections
that are taken along the route of the River Clyde. The relevant cross section contained within the
report (SEC_117) is located close to the eastern boundary of the site. At this location the 1 in 200
year predicted water levels is 4.26mOD. The 1 in 200 year predicted water levels identify the
Functional Flood Plain and the design level given in the report is + 20% Climate change and +0.7m
freeboard. This gives a design level of 5.27mOD in this area of the River Clyde.
2.7 GROUNDWATER
Local and Regional groundwater flow will be in line with the general landform to the north towards
the River Clyde Estuary. 
Local groundwater will be perched and is likely to lie at the interface of the superficial deposits and
the bedrock.
A review of the SEPA River Basin Management Plan Interactive Map shows the regional
groundwater body immediately to the south of the site to be the Langbank Groundwater Body and
beneath the site itself to be the Greenock Groundwater Body.  Groundwater flows and levels and
groundwater quality in both these bodies are noted to be Good, with an overall classification of Good.

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3 FLOOD RISK ASSESSMENT
3.1 GENERAL
Flooding occurs when the amount of water arriving on land exceeds the capacity of the land to
discharge that water (by infiltration, overland flow, groundwater rise or a failed drainage system). It
can occur on any level or near-level areas of land but the main concern in inland areas is with land
adjacent to watercourses (fluvial flooding) and the possibility of overland flow (surface water
flooding). 
3.2 FLUVIAL FLOOD RISK 
The site walkover has confirmed that the watercourse identified on the Ordnance Survey map is not a
clearly defined channel and does not exist in the location shown on the map. In the vicinity of the
southern extent of the site there is a cleft in the rockface that forms a conduit for water to flow from
the higher ground above the site to the south over the rock face. At the base of this cleft there is a
stone trough that collects the water and it is then culverted down the hillside. The line and extent of
this culvert is not known. This culvert is protected by a metal grill to prevent blockages and it is
understood that debris is periodically removed from the stone trough by Scotland Transerv. 
The minor watercourse has a catchment which is too small to be assessed fluvially by SEPA and is
shown as a surface water flood potential along the eastern boundary of the site. 
A review of the Flood Estimation Handbook Web Service (FEH13) indicates that the catchment for
the watercourse located to the south of the site is less than 0.5km2 and is therefore not recorded.
Following the site walkover and a review of available topographic information and utilising the
overland flow pathways, the catchment was determined. The extent of this catchment is interpreted to
be 0.18km2 and is shown on Fig 4 included in the Appendix. An outline estimation for the minor
watercourse indicates a peak flow of between 400l/s and 700l/s. The watercourse culvert is likely to
be steeply sloping and has been calculated to have a capacity in the order of 200l/s and is thus
undersized for the potential 200 year storm event. 
During the design storm overland flow will occur at the culvert in the south of the site, leading to a
Medium to High risk of fluvial flooding at the site. Consideration of the overland flow route through
the site is considered in Section 3.4 below.
3.3 SURFACE WATER 
A review of the SEPA Flood Map indicates a risk of surface water flooding along the A8 and also
down the eastern boundary of the site. 
Potential surface water flow was assessed by utilising available topographic information,
supplemented by the site walkover. The interpreted flow pathways are shown on Fig 3 included in the
Appendix which indicates that surface water runoff within the site will generally be to the north
towards Marypark Road, thereafter, will be to the west and east along Marypark Road and to the
north down the embankment towards the A8 dual carriageway. 
The local landform indicates that the risk of surface water flooding within the site is Low to Medium
according to Scottish Planning Policy (SPP). 
3.4 LOCAL DRAINAGE
During the site walkover, limited road drainage gullies were noted to be present in the vicinity of the
site and rudimental drainage channels had been cut along the northern edge of Marypark Road. In
addition, seepages were noted to be issuing from the embankment in front of the site down towards
the A8.

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A failure of the local road drainage system may lead to flood routing along Marypark Road and the
A8 but the local topography indicates that any overland flow will be to the east and west and away
from the site. Such a failure in road drainage will not impact the site and the site is considered to be at
Little or No Risk of flooding from a failure in the local road drainage infrastructure.
A failure of the watercourse culvert in the south of the site will lead to overtopping of the stone
trough which would have historically flowed to the east and through the gardens of Marypark House.
As noted in Section 2.5 above a low wall has been constructed to redirect any overland flow to the
southwest and to the west of the eastern site boundary, through the site and onto Marypark Road. 
Given the current modification to the overland flow pathway the risk to the site from a failure of this
culvert is considered to be Medium to High.
3.5 COASTAL FLOODING
A review of the SEPA flood map shows that the site lies in close proximity to the flood plain of the
River Clyde. 
The River Clyde Flood Management Strategy recommends a design level of 5.27mOD in this area of
the River Clyde. Marypark Road at the site entrance lies at 6.8mOD with the site itself lying above
this level. The site therefore lies in excess of 2.5m above the peak 1 in 200 year water level. 
Whilst it is noted that the RCFMS hydraulic model is currently being updated which may result in
alterations to the estimated peak water level, the site entails a significant freeboard so that coastal
flood risk is assessed to be Little to None according to Scottish Planning Policy (SPP). 
3.6 GROUNDWATER RISE
The underlying superficial deposits are likely to be thin or absent beneath the site and shallow
groundwater may be present. No springs or seepages were noted along the base of the rockface.
The local landform indicates that there is Little to No Risk of isolated ground water rise within the
site.

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4 DISCUSSION AND RECOMMENDATIONS
4.1 GENERAL CONCLUSIONS 
For new developments, the acceptable risk of flooding should take into account various factors
including risk to human health and the direct and indirect financial losses relating to flooding.
For the proposed re-development of the site, the following general conclusions can be made:
 The site is at Medium to High risk of flooding from fluvial sources.
 There is Low to Medium risk of flooding as a result of surface water.
 There is Medium to High risk of flooding as a result of a failure in drainage infrastructure.
 The site is at Little or No risk from coastal flooding.
 There is Little or No risk of isolated groundwater rise occurring at the site.
 Dry pedestrian access and egress is maintained throughout the design storm event from
Marypark Road.
 Emergency vehicular access along Marypark Road, should be possible throughout the design
storm event. 
4.2 DEVELOPMENT AND POSSIBLE MITIGATION MEASURES
Consideration should be given in the proposed layout to include a maintenance wayleave along the
eastern boundary of the site in order to enable the existing maintenance of the culvert to continue and
maintain the existing overland flow route. Such a wayleave should be in the order of 2m wide and at
least 0.5m deep. The bed should be vegetated in order to mimic the existing slope and prevent
additional sheet flow.
It is recommended that the existing ground level be raised within the central part of the site to mimic
the ground levels along the eastern boundary. Final Floor Levels should be set at least 200mm above
the final ground level.
Discussions should be held at the earliest opportunity with Scotland Transerv in order to confirm the
responsibilities for maintaining the culvert.
The possibility of shallow perched groundwater below the site should be considered as part of the
development. 
4.3 EFFECTS ON SITE NEIGHBOURS
The proposed development will have a neutral impact on any flooding and will not increase the flood
risk to any site neighbours.
4.4 OVERALL FLOOD RISK ASSESSMENT CONCLUSION
The Scottish Planning Policy notes that new developments should be free from significant
flood risk from any source and that such development should not:
 materially increase the probability of flooding elsewhere;
 add to the area of land which requires protection by flood prevention measures;
 affect the ability of the functional flood plain to attenuate the effects of flooding by
storing flood water;
 interfere detrimentally with the flow of water in the flood plain; or

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 compromise options for future river management.
With the proposed wayleave constructed to maintain the existing overland flow pathways and the
land raising at the site the proposed development will be at Little or No risk from flooding according
to the SPP flood framework. 
Dry emergency pedestrian and emergency vehicular access is available to the site throughout the
design storm event. 
It is concluded that the proposed development is feasible and is in broad accordance with the
principles of the Scottish Planning Policy. 
-oo000oo-
Terrenus Land & Water Ltd wishes to thank Arthur MacMillan for the opportunity to prepare this
report and trust that it meets with your requirements. However, should you wish to discuss the
contents of the report then please do not hesitate to contact the undersigned. 
Signed for and on behalf of
Terrenus Land & Water Ltd 
William Hume
Director

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APPENDIX

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FIGURES

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©2019 Microsoft. Image courtesy of Ordnance Survey
Client: 
Arthur MacMillan
Drawing Title: 
Site Location Plan 
International House,
Hamilton International Park,
Stanley Boulevard,
Hamilton,
G72 0BN 
www.terrenus.co.uk
Project:
Marypark Road, Langbank
Date:19/09/2019   
Figure 1 Grid Ref: 
NS 37598 73469
SCALE: N.T.S. DO NOT SCALE 
Site centred on 
NS 37598 73469

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Copyright: Imagery ©2019 Google, Imagery ©2019 Getmapping plc, Infoterra Ltd & Bluesky, Maxar Technologies, Map data ©2019  United Kingdom
Client: 
Arthur MacMillan
Figure Title: 
Additional Survey Works 
International House,
Hamilton International Park,
Stanley Boulevard,
Hamilton,
G72 0BN 
www.terrenus.co.uk 
Project:
Marypark Road, Langbank
Date: 18/09/2019 
Figure 2 Grid Ref: NS 37598 73469
SCALE: N.T.S. DO NOT SCALE

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Copyright: Imagery ©2019 Google, Imagery ©2019 Getmapping plc, Infoterra Ltd & Bluesky, Maxar Technologies, Map data ©2019  United Kingdom
Client: 
Arthur MacMillan
Figure Title: 
Overland Flow Pathways 
International House,
Hamilton International Park,
Stanley Boulevard,
Hamilton,
G72 0BN 
www.terrenus.co.uk 
Project:
Marypark Road, Langbank
Date: 18/09/2019 
Figure 3 Grid Ref: NS 37598 73469
SCALE: N.T.S. DO NOT SCALE

Page 40

Copyright: Imagery ©2019 Google, Imagery ©2019 Getmapping plc, Infoterra Ltd & Bluesky, Maxar Technologies, Map data ©2019  United Kingdom
Client: 
Arthur MacMillan
Figure Title: 
Catchment Analysis 
International House,
Hamilton International Park,
Stanley Boulevard,
Hamilton,
G72 0BN 
www.terrenus.co.uk 
Project:
Marypark Road, Langbank
Date: 18/09/2019 
Figure 4 Grid Ref: NS 37598 73469
SCALE: N.T.S. DO NOT SCALE

Page 41

MARYPARK ROAD, LANGBANK
FLOOD RISK ASSESSMENT
FOR
ARTHUR MACMILLAN 
Z:\Jobs\Jobs L&W\1800-1899\1800 - Arthur MacMillan\1800-200 - Marypark Road FRA\7 - Reports\1800-200 - Marypark Road, Langbank FRA Report.doc
PHOTOGRAPHIC PLATES

Page 42

MARYPARK ROAD, LANGBANK
FLOOD RISK ASSESSMENT
FOR
ARTHUR MACMILLAN 
Plate 1 – General view of site looking east from base of cliff. 
Plate 2 – General view of site looking north from base of cliff.

Page 43

MARYPARK ROAD, LANGBANK
FLOOD RISK ASSESSMENT
FOR
ARTHUR MACMILLAN 
Plate 3 – General view looking north towards site. 
Plate 4 – Boggy area to south of site above cliff.

Page 44

MARYPARK ROAD, LANGBANK
FLOOD RISK ASSESSMENT
FOR
ARTHUR MACMILLAN 
Plate 5 – View south of cleft in cliff face. 
Plate 6– Culvert at base of cliff.

Page 45

MARYPARK ROAD, LANGBANK
FLOOD RISK ASSESSMENT
FOR
ARTHUR MACMILLAN 
Plate 7 – Culvert at base of cliff looking north. 
Plate 8 – Looking down on culvert located at northern end of stone trough.

Page 46

MARYPARK ROAD, LANGBANK
FLOOD RISK ASSESSMENT
FOR
ARTHUR MACMILLAN 
Plate 9 – Looking north along relict fenceline located between stone trough and boundary
with Marypark House. 
Plate 10 – Relict stonewall and fenceline.

Page 47

MARYPARK ROAD, LANGBANK
FLOOD RISK ASSESSMENT
FOR
ARTHUR MACMILLAN 
Plate 11 – Concrete wall constructed to rear of Marypark House to deflect water flow in case
of blockage. 
Plate 12 – Mound of stones assumed to be removed during clearance of culvert.

Page 48

MARYPARK ROAD, LANGBANK
FLOOD RISK ASSESSMENT
FOR
ARTHUR MACMILLAN 
Plate 13 – Fallen rocks and tree in vicinity of cleft. 
Plate 14 – Seepage from embankment onto footpath adjacent to A8.

Page 49

MARYPARK ROAD, LANGBANK
FLOOD RISK ASSESSMENT
FOR
ARTHUR MACMILLAN 
Plate 15 – Seepage from embankment onto footpath adjacent to A8. 
Plate 16– Pathway cut into northern side of Marypark Road to assist drainage down the
embankment.

Page 50

MARYPARK ROAD, LANGBANK
FLOOD RISK ASSESSMENT
FOR
ARTHUR MACMILLAN 
Plate 17– Pathway cut into northern side of Marypark Road to assist drainage down the
embankment. 
Plate 18 – Area cleared around manhole located in Marypark Road.

Page 51

Tree Survey  
BS 5837:2012 Trees in Relation to Design, 
Demolition and Construction-Recommendations 
Land to the South of Marypark Road
Finlaystone Estate 
29th January 2022 
Prepared for 
Finlaystone Estate 
Prepared by
C. A. Calvey, P.T.I., Tech.Cert (Arbor.A), Cert.Arb (RFS), BA Hons.
Principle Arboricultural Consultant
Ayrshire Tree Surgeons Ltd

Page 52

CONTENTS
Introduction & Survey Findings Summary     Page 1 
Map: Site Location Plan (Scale 1: 2500)      Page 2
Map: Tree Positions Plan (Scale 1:250)      Page 3
Photographs         Page 4
Tree Schedule          Pages 5 - 7
Tree Survey Assessment criteria       Pages 8 - 9
Report Limitations        Pages 10 - 11 
Appendix 1: Project Contact Details      Page 12 
Appendix 2: References        Page 13

Page 53

Page 1
Introduction
Finlaystone Estate instructed the Arboricultural survey conducted on 25th January 2022 for a small plot of
land to the south of Marypark Road, Finlaystone Estate. Trees were assessed in accordance with
BS5837:2012 Trees in Relation to Design, Demolition and Construction-Recommendations. Christopher
Calvey is an independent arboriculturist and the report presents an impartial assessment of the tree stock.   
The report is based on visual inspections conducted from ground level for the purpose of categorizing trees
in relation to design, demolition and construction and does not provide reliable data on tree safety. This
report is not, nor should it be taken to be, a full or thorough assessment of the health and safety of trees on
or adjacent to the site, and therefore it is recommended that detailed tree inspections of retained trees are
undertaken on a regular basis with the express purpose of complying with the landowner’s duty of care and
satisfying health and safety requirements. Please refer to Report Limitations on pages 10-11. The authority
of this report ceases within one year from the date of the survey or following severe weather occurrences
which supersede the current validity of the report. 
Survey Findings
The survey area is within an unused corner of the estate and trees are entirely self-seeded specimens
surviving amongst areas of invasive rhododendron. The plot falls within the SINC (non-statutory ‘Site of
Importance for Nature Conservation’) which covers the wider Estate. Due to natural degradation and
colonisation by non-native invasive species the biological value of the plot is very low. 
There are eleven ‘C’ low quality trees within the site boundary and one ‘B’ moderate quality young
cherry tree.  Trees neighbouring the site to the east and south are included in the tree survey to measure
their root protection areas in proximity to the site boundary. Trees 836, 837 and 838 will cause structural
damage to the stone boundary wall if left in situ and recommended for removal irrespective of any future
proposals for the site.  Rhododendron ponticum is recommended for eradication. Mature Ash tree 835 is at
stage 3 of Chalara Ash dieback disease and in terminal decline. 
Using the Report
Trees are identified by a numbered metal tree tag attached to the tree which corresponds to the site plan
and tree schedule. Tree maps show the position of trees, crown spread and maximum rooting zone
illustrated by grey dodecagons. The crown spread of a tree is identified by a coloured circle and illustrates: 
1. Green for ‘A’ (High quality trees) – not applicable
2. Mid blue for ‘B’ (Moderate quality trees) 
3. Grey for ‘C’ (Low quality trees) 
4. Dark Red for ‘U’ (trees ‘Unsuitable’ for retention in the current land use).

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Page 2

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Page 3

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Page 4   
Tree 824 Suppressed with extensive bark
wounds
Tree 827 Basal wounding and bleeding
canker. Very low quality
Tree 836  threatens wall Trees 830 -832 south boundary 
Hazel Shrub 829  Tree 828

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Page 5

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Page 6

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Page 7

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Page 8
Tree Survey Assessment Criteria
The tree survey is undertaken in accordance with a range of criteria listed in BS 5837:2012 Trees in
Relation to Design, Demolition and Construction-Recommendations. 
Quality Category 
Category A: (HIGH quality, trees with particular merit with an estimated remaining life expectancy of
at least 40 years). 
Category B: (MODERATE quality with an estimated remaining life expectancy of at least 20 years). 
Category C: (LOW quality with an estimated remaining life expectancy of at least 10 years). 
Category U: (UNSUITABLE quality, in such condition that they cannot realistically be retained as living
trees in the context of the current land use. Life expectancy less than 10 years).
Sub Categories: The BS 5837 subcategories: 1 - mainly Arboricultural Qualities, 2  - mainly landscape
qualities, 3  - Cultural qualities. 
Tree Condition
Defects or diseases and relevant observations have been recorded under condition of Crown, Stem,
Basal area and Physiological condition. It is important to appreciate that in BS5837 criteria only basic
condition categories are recorded and the inspection process does not constitute a tree safety
survey. 
The overall condition of a tree has been referred to as one of the following:
• Good: A sound tree needing little if any attention at the time of survey.
• Fair: A tree with minor but rectifiable defects or in the early stages of stress, from which
it may recover. The tree may have structural weaknesses which might result in failure.
• Poor: A tree with clear and obvious major structural and or physiological defects or
stressed such that it would be expensive to retain and necessarily requires to be
inspected on a regular basis for safety purposes.
• Decline: Irreversible with death inevitable in the short term.
• Dead. To be removed unless stated to the contrary.
Age Class 
Age Class and Life Expectancy are clearly related but the distinction is necessary due to the variation
among tree species.  Knowledge of the longevity of individual species has been applied to determine
the relative age and life expectancy categories in which trees are placed. 
Age class is classified as:
• Y: Young trees up to 15 years of age. 
• SM: Semi-mature trees less than 1/3rd life expectancy. 
• EM: Early Mature trees between 1/3rd and ½ of life expectancy.
• M: Mature trees between ½ and 2/3rd of life expectancy. 
• LM: Late mature - A senescent or moribund specimen with a limited safe useful life
expectancy. 
• V: Veteran status – a tree of significant age and character such that even in poor condition
the tree has a value for retention for arboricultural or ecological reasons.

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Page 9
Safe Useful Life Expectancy (SULE)
The survey schedule identifies a Safe Useful Life Expectancy (SULE) for each tree. This is a subjective
assessment of the number of years that the tree can be expected to survive without deteriorating to
the extent that safety is compromised. The estimated remaining contribution is given in ranges of
years (<10, 10 to 20, 20 to 40, >40). 
It is important to note that SULE does not in any way suggest that regular inspection and remedial
work can be ignored. SULE does not take into account routine management that will be required to
deal with minor structural or cultural problems, or damage that may arise from climatic or other
physical intervention. The SULE value given for each tree reflects the following opinion based on
current tree condition and environmental considerations: 
<10 years. The tree has very limited prospects, due to terminal decline or major structural problems.
Its removal should be planned within the next 10 years, unless immediate removal is recommended
for safety reasons. 
10-20 years. The tree has obvious structural or physiological problems that cannot be rectified, and
decline is likely to continue. Removal or major tree surgery work may be necessary, or the species is
approaching its normal life expectancy and decline due to senescence can be expected within this
timeframe. 
20-40 years. Relatively minor defects may exist that are likely to increase safety risks or general tree
health over a longer period of time. At this stage it is not possible to fully predict the impact of such
defects. Or the species is approaching its normal life expectancy and due to senescence decline can
be expected within this timeframe. 
>40.  There is currently no health or structural problems evident, and the tree can be expected to
survive safely for 40 or more years.

Page 62

Page 10
Report limitations
1. The survey is only concerned with the arboriculture aspects of the site.
2. The report is based on visual inspections conducted from ground level with the purpose of
categorising trees in relation to design, demolition and construction and does not provide
reliable data on tree safety. This report is not, nor should it be taken to be, a full or thorough
assessment of the health and safety of trees on or adjacent to the site, and therefore it is
recommended that detailed tree inspections of retained trees are undertaken on a regular basis
with the express purpose of complying with the landowner’s duty of care and satisfying health
and safety requirements.
3. The statements made in this report do not take account of the effects of extremes of climate,
vandalism, or accident, whether physical, chemical or fire. 
4. The authority of this report ceases within one year from the date of the survey or when any site
conditions change, soil levels are altered near trees, tree work undertaken, or following severe
weather occurrences which supersede the current validity of the report.   
5. The validity, accuracy and findings of this report will be directly related to the accuracy of the
information made available prior to and during the inspection process. No checking of
independent third-party data will be undertaken. 
6. Any observations that are made in regard to the condition of built structures and hydrology are
from a laypersons view. The legal property on which the trees stand is not assessed. 
7. The report contains Visual Tree Inspections undertaken from ground level. Visual inspections
relate only to those parts of the tree which are visible. Roots are not inspected and during
summer when trees are in leaf parts of the canopy may not be visible. Where a tree or parts of a
tree could not be inspected due to epicormic growth, ivy or restricted access, liability is not
accepted. Only the visible pathogens are recorded; this does not confirm the absence of other
pathogens but that no fungal fruiting bodies, or other signs, were visible at the time of the
survey. 
Ayrshire Tree Surgeons cannot accept any liability in connection with the following: 
I. A tree which has not been subject to a full and thorough inspection. 
II. For any part of a tree that is not visible from the ground near the tree. 
III. Where excavations have taken place within the rooting area of a tree. 
IV. Branch or limb failure resulting from conditions associated with Summer Branch Drop. 
V. The effect of extreme weather events, climate, vandalism or accident, whether physical,
chemical or fire.

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Page 11 
VI. Where tree surgery work is not carried out in accordance with current good practice
8. Felling licenses are the responsibility of the tree owner. The Forestry Commission controls tree
felling by issuing felling licences. In any calendar quarter, you may fell up to 5 cubic metres
without a licence if no more than two cubic metres are sold. Timber volumes are not assessed. 
9. Planning restrictions applying to tree works remain the responsibility of the tree owners.
10. No failsafe guarantees can be given regarding tree safety because the lightweight construction
principles of nature dictate a natural failure rate of intact trees. Trees are living organisms and
can decline in health rapidly due to biotic and abiotic influences. Therefore, failure of intact trees
can never be ruled out due to the laws and forces of nature. 
11. This report has been prepared exclusively by the Ayrshire Tree Surgeons Ltd for the ‘Client’ and
no responsibility can be accepted for actions taken by any third party arising from their
interpretation of the information contained in this document. No other party may rely on the
report and if they do, then they rely upon it at their own risk.
Christopher Calvey - Ayrshire Tree Surgeons Ltd

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Page 12
Appendix 1: Project Contact Details 
Arthur MacMillan
Finlaystone Country Estate
PA14 6TJ 
arthur@finlaystone.com
Tel. 07802 254056 
Project Arboriculturalist 
Christopher Calvey, 
Ayrshire Tree Surgeons Ltd 
North Hourat Farm, 
Kilbirnie, Ayrshire 
KA25 7LJ 
Tel. 01505 681898 
Mobile: Mo. 07920 763132 
E-mail: chris@ayrshiretreesurgeons.co.uk

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Page 13
Appendix 2: References
British Standards Institute.  (2012). Trees in Relation to Design, Demolition and Construction –
Recommendations BS5837:2012BSI, London. 
British Standards Institute.  (2010). Recommendations for Tree Work BS 3998:2010 BSI, London. 
Tree Preservation Orders, A Guide to the Law and Good Practice (2005). Department for
Communities and Local Government 
Lonsdale D.  (1999). Research for Amenity Trees No 7:  Principles of Tree Hazard Assessment and
Management, HMSO, London. 
Mattheck & Breloer H. (1994). Research for Amenity Trees No.4: The Body Language of Trees,
HMSO, London. 
NHBC Standards (2007) Chapter 4.2 ‘Building Near Trees’. National House-Building Council. 
NJUG 4 Guidelines for the planning, installation and maintenance of utility apparatus in proximity to
trees. Issued 16 November 2007. 
STROUTS R.G. & WINTER T.G. (1984), Diagnosis of ill health in trees, HMSO Publications, London
SHIGO A.L. (1991), Modern Arboriculture, Shigo and Trees Associates
Hazards from Trees – A General Guide ISBN 0-85538-514-6
Tree Felling – Getting Permission. Forestry Commission and free to download from their website
www.forestry.gov.uk
Trees and the Law ISBN 0-900978-15-5 Published by the Arboricultural Association Tel: 01794 68717
Institute of Chartered Foresters Tel: 0121 225 2705

Page 66

www.wildsurveys.co.uk 
St James Business Centre, Linwood Road, Paisley, PA3 3AT
Telephone 0141 887 2770   Mobile 07788 826 480   Fax 0871 5030923 
Ecological Constraints Survey
& Aerial Tree Survey 
Finlaystone, Langbank 
For 
Arthur MacMillan 
FINAL 
11th January 2022

Page 67

ii www.wildsurveys.co.uk                                                 
OP08-01-20-V2 
Quality Management 
Project No: WS3608.21
Prepared by: Chloe Rossi-Easto 11/01/22 Signed by:
Reviewed by: Morna McBean 3/02/22 Signed by: 
Version
No. Date Comments / Changes Changed by
2 10/02/22 As per requested by the client, amendments have been made within
the report. 
CR
3 16/02/22 As per requested by the client, amendments have been made within
the report.
CR 
00/00/00   
Contacts
Chloe Rossi-Easto  E: 
M: 0
NatureScot Caspian House
Mariner Court
Clydebank Business Park
Clydebank
G81 2NR
T:0131 314 6750
www.nature.scot 
The report is confidential to the Client and Wild Surveys Ltd accepts no responsibility of whatever nature
to third parties to whom this report may be made known. The material in this report has been produced
for the exclusive use of the Client and shall not be distributed or made available to any other company
or person without the knowledge and written consent of the Client.
The report has been prepared by Wild Surveys Ltd. No individual is personally liable in connection with
the preparation of this report.  By receiving this report and acting on it, the client or any other person
accepts that no individual is personally liable whether in contract, tort, for breach of statutory duty or
otherwise.

Page 68

iii www.wildsurveys.co.uk                                                 
OP08-01-20-V2 
Table of Contents
Introduction 1
1.1 Project Objectives 1
1.2 Site Location 1
Methodology 2
2.1 Desk Study 2
Planning Policies 2
2.2 Ecological Constraints 2
2.3 Protected Species 3
2.4 Limitations 6
Results 7
3.1 Desk study 7
3.2 Ecological Constraints Survey 7
Discussion and Recommendations 9
4.1 Discussion 9
4.2 Recommendations 9
References 11
Appendix 1 – Site Location and Photographs 12
Appendix 2 – Summary of Relevant Policy and Legislation 21
Appendix 3 - European Protected Species and the Law 23
Appendix 4 – Wildlife and Countryside Act Species and the Law 25
Appendix 5 – Badgers and the Law 26
Appendix 6 – Birds and the Law 27
Appendix 7 – Guidance on Optimal Survey Periods 28
Appendix 8 - Desk Study Search Results 29
Appendix 9 – Constraints Plan 33

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Ecological Constraints Survey and Preliminary Roost Assessment – Finlaystone, Marypark Road, Finlaystone   
iv www.wildsurveys.co.uk                                                 
OP08-01-20-V2 
Executive Summary
Wild Surveys Ltd was commissioned by Author MacMillan to undertake an ecological constraints survey
and desk study at Finlaystone, Marypark Road (National Grid reference NS3759273466).  The aim of the
survey was to describe the broad habitats on site and to identify any potential ecological constraints
within or adjacent to the survey area and provide mitigation and recommendations for further survey
as appropriate in order to inform planning prior to the development of residential houses on the site.
A desk study was undertaken to review information available within the public domain. Publicly
available databases, local wildlife groups and our own internal records were consulted for historical
evidence of protected species in and around the site.  In addition, a walkover survey was carried out on
11th January 2022 by experienced ecologists to identify the broad habitat types present as well as any
field signs of protected or notable species.  An aerial tree survey was then carried out on the 25th January
2022 to inspect suitable features for roosting bats within trees on the site. 
From the desk study it was found that there are four Sites of Importance for Nature Conservation found
within 2km of the site boundary. The site lies on the extreme edge of The Finlaystone Estate,
immediately adjacent to the village of Langbank. There are 15 woodlands listed within the Ancient
Woodland Inventory which lie within 2km of the site boundary. The closest ancient woodland is located
within the site boundary, Wood ID: 26708. The Inner Clyde is a Site of Special Scientific Interest, a Special
Protection Area, a Ramsar as well as a RSPB Reserve, which located 80m north of the site, with a main
road and railway line separating the designated sites from the site boundary. Brucehill-Inland Cliff is a
Local Nature Conservation Site which is located approximately 1.6km north of the site boundary. 
There are records of soprano pipistrelle, brown long eared and hedgehog found within 2km of the site
boundary.
The survey area has habitat suitable for badger, nesting birds and foraging, commuting and roosting
bats. No field signs of any protected species was found during the survey.
Two trees were found to be suitable for use by roosting bats. As there was no current or historical
evidence of use by bats these features were soft blocked with organic material.

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Ecological Constraints Survey and Preliminary Roost Assessment – Finlaystone, Marypark Road, Finlaystone   
Project number: WS3608.21 1 www.wildsurveys.co.uk
11 January 2022                                                 OP08-01-20-V4 
1 Introduction
1.1 Project Objectives
1.1.1 Wild Surveys Ltd (WSL) was commissioned by Arthur MacMillan to undertake an ecological
constraints survey, an aerial tree survey and desk study at Finlaystone, (hereafter referred to
as ‘the site’), Marypark Road, Langbank (National Grid Reference NS3759273466). This report
presents the results of the survey carried out. The survey area included the area within the
site boundary and an additional 30m buffer around the site boundary. Site location can be
found within Appendix 1.
1.1.2 The aim of the survey was to provide a broad description of the existing habitat types within
the survey area and to determine the presence and location of any ecologically valuable areas
and habitat types with the potential to support protected species in order to inform planning
prior to the development of a residential property. 
1.1.3 Following the ecological constraints survey which was undertaken on the 11th January 2022,
an aerial tree survey was carried out on two trees which were identified as having suitable
features for use by roosting bats on the 25th January 2022.
1.1.4 This report will therefore identify any ecological constraints with regards to potential
development and highlight the need for further survey work and mitigation measures, where
appropriate.
1.2 Site Location
1.2.1 The site is located adjacent to the village of Langbank, east of Port Glasgow. The site is located
within the extreme edge of the Finlaystone Country Park. With ancient woodland directly
south of the site. Further south is agricultural land with areas of woodland. Gleddoch Golf
course is located to the southeast of the site. The River Clyde is located north of the site.  The
location of the survey and photographs are shown in Appendix 1.

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Ecological Constraints Survey and Preliminary Roost Assessment – Finlaystone, Marypark Road, Finlaystone   
Project number: WS3608.21 2 www.wildsurveys.co.uk
11 January 2022                                                 OP08-01-20-V4 
2 Methodology
2.1 Desk Study
2.1.1 A data search was undertaken by WSL to review information available within the public
domain. Publicly available databases, local wildlife groups and our own internal records were
consulted for historical evidence of protected species in and around the site. Listings in
Scottish Biodiversity List (SBL) and Local BAP was also checked. This information was gathered
to identify the status of these protected species within 2 km of the site.  
2.1.2 A search using NatureScot sitelink, the Renfrewshire Local Development Plan was carried out
to discover any statutory or non-statutory designated sites within 2 km. These would include:
▪ Local Nature Reserve (LNR);
▪ Local Authority designated site, e.g. Site of Importance for Nature Conservation (SINC);
▪ Wildlife Nature Reserve (Scottish Wildlife Trust, Royal Society for the Protection of Birds,
etc.);
▪ Ancient Woodland Inventory (AWI);
▪ Site of Special Scientific Interest (SSSI);
▪ Special Area for Conservation (SAC); and,
▪ Special Protection Area (SPA).
2.1.3 This information was gathered to identify the status of protected species within 2 km of the
site, determine the Zone of Influence (ZoI) (survey area) that may be required for further
surveys. In addition, the information was used to identify potential impacts on bats which may
result from the proposed redevelopment.
Planning Policies 
2.1.4 The policies set out below are those relevant to nature conservation and include those from
the Local Development Plan. The Local Development Plan was adopted by Renfrewshire
Council on 2021 and is the land use plan which sets out the policies and proposals which the
Council wishes to use to guide development across the area up to date and beyond.
2.1.5 In respect to the above, regard has been made to the following policies: 
▪ Scottish Planning Policy (SPP) 2014 (Scottish Government, 2014); 
▪ Planning Advice Note 60: Planning for Natural Heritage (Scottish Government, 2000);
and,
▪ Renfrewshire Local Development Plan (2021):
- Policy ENV1: Greenbelt; and
- Policy ENV2: Natural Heritage.
2.2 Ecological Constraints
2.2.1 An ecological constraints survey was carried out on the 11 January 2022 to establish broad
habitat types and their ecological importance. The survey also aimed to identify suitability for
a number of protected species in order to make recommendations for avoidance, mitigation

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Ecological Constraints Survey and Preliminary Roost Assessment – Finlaystone, Marypark Road, Finlaystone   
Project number: WS3608.21 3 www.wildsurveys.co.uk
11 January 2022                                                 OP08-01-20-V4 
and for any further survey effort, if required. A summary of relevant policy and guidance in
Scotland can be found in Appendix 2, with the legal context in relation to protected species
and habitats found in Appendix 3 - 6. The survey area included the area within the site
boundary and an additional 30m buffer around the site boundary.
2.2.2 Habitats on site consists of an area of semi improved grassland and rhododendron
(Rhododendron sp.) with broadleaved woodland and a steep rocky incline to the south of the
site.  Given the habitat types on site particular attention was given to the potential presence
of the following species; bats (Chiroptera), badger (Meles meles) and habitat suitable for use
by nesting birds.  Methodologies are detailed below for each of these species. There is no
habitat within the survey area suitable for otter (Lutra lutra), great crested newt (Triturus
cristatus), red squirrel (Sciurus vulgaris), pine marten (Martes martes), water vole (Arvicola
amphibius), reptiles (Squamata), or wildcat (Felis silvestris) and these species are not discussed
further.
2.3 Protected Species
Bats
2.3.1 A daytime assessment was carried out to identify habitat with the potential to support roosting
or foraging and commuting bats within and adjacent to the site (including habitat suitable for
roosting such as buildings and trees).  The survey area Zone of Influence (ZOI) where all
development activities will be located is shown in Appendix 1. Further information on the legal
protection afforded to bats can be found in Appendix 3.
2.3.2 All trees were inspected from the ground and climbed for an aerial inspection where required
on the 25th January 2022 to identify signs of current and historical bat use and to assess the
trees’ potential to support bats. Any features which were suitable for supporting bats were
noted and, if necessary, trees were climbed and cavities inspected internally using Rigid CA-
150 SeeSnake inspection cameras.
2.3.3 The habitat assessment was carried out in accordance with the Bat Conservation Trust’s Bat
Survey Guidelines (Collins, J. 2016).
2.3.4 The location of the trees inspected can be found in Appendix 9.  The assessment aimed to
identify the following:
▪ Roosts and potential for roosts within the ZoI determined by the area affected by the
proposed activities within the site and data collected during the desk study;
▪ Bat activity / field signs of bats;
▪ Evaluate the suitability of any habitat within the ZoI which may support roosting,
foraging or commuting bats;
▪ Determine any potential impacts on bats within the ZoI;
▪ Any requirement for further survey work or for section 44 licensing; and,
▪ Determine the scope and survey area for any further survey work.
2.3.5 The ZoI was inspected in accordance with current best practice guidance from the Bat
Conservation Trust 3rd Edition (Collins, J. 2016) in order to identify the suitability of the ZoI to
support roosting, commuting and foraging bats. Guidelines for determining suitability of
habitat features for bats is presented in the following table:

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Ecological Constraints Survey and Preliminary Roost Assessment – Finlaystone, Marypark Road, Finlaystone   
Project number: WS3608.21 4 www.wildsurveys.co.uk
11 January 2022                                                 OP08-01-20-V4 
Table 1: Guidelines for assessing the potential suitability of proposed development sites for bats,
based on the presence of habitat features within the landscape (to be applied using professional
judgement) (adapted from Table 4.1 on Page 35 of current BCT, 2016):
Suitability Description Roosting habitats Commuting and foraging
habitats
Negligible
Negligible habitat features on
site likely to be used by
roosting bats.
Negligible habitat features
on site likely to be used by
commuting or foraging
bats.
Low
A structure with one or more
potential roost sites that could
be used by individual bats
opportunistically.
However, these potential roost
sites do not provide enough
space, shelter, protection,
appropriate conditions and/or
suitable surrounding habitat to
be used on a regular basis or
by larger numbers of bats (i.e.
unlikely to be suitable for
maternity or hibernation).
A tree of sufficient size and age
to contain Potential Roost
Features (PRFs) but with none
seen from the ground or
features seen with only very
limited roosting potential.
Habitat that could be used
by small numbers of
commuting bats such as a
gappy hedgerow or
unvegetated stream, but
isolated, i.e. not very well
connected to the
surrounding landscape by
other habitat.
Suitable, but isolated
habitat that could be used
by small numbers of
foraging bats such as a lone
tree (not in a parkland
situation) or a patch of
scrub.
Moderate
A structure or tree with one or
more potential roost sites that
could be used by bats due to
their size, shelter, protection,
conditions and surrounding
habitat but unlikely to support
a roost of high conservation
status (with respect to roost
type only – the assessments in
this table are made
irrespective of species
conservation status, which is
established after presence is
confirmed).
Continuous habitat
connected to the wider
landscape that could be
used by bats for commuting
such as lines of trees and
scrub or linked back
gardens.
Habitat that is connected to
the wider landscape that
could be used by bats for
foraging such as trees,
scrub, grassland or water.

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High
A structure or tree with one or
more potential roost sites that
are obviously suitable for use
by larger numbers of bats on a
more regular basis and
potentially for longer periods of
time due to their size, shelter,
protection, conditions and
surrounding.
Continuous, high-quality
habitat that is well
connected to the wider
landscape that is likely to be
used regularly by
commuting bats such as
river valleys, streams,
hedgerows, lines of trees
and woodland edge.
High-quality habitat that is
well connected to the wider
landscape that is likely to be
used regularly by foraging
bats such as broadleaved
woodland, tree-lined
watercourses and grazed
parkland.
Site is close to and
connected to known roosts. 
Badger
2.3.6 The survey included searching for field signs of badgers, including: 
▪ Presence of holes with evidence of badgers such as footprints, discarded hairs; etc.;
▪ Presence of dung pits or latrines;
▪ Presence of well-used runs with subsidiary evidence of badger activity; and
▪ Presence of other indications of badger activity such as signs of foraging, snuffle marks
and footprints.
2.3.7 In addition, any mammal holes which were either dug by badger or could be used by badger
(known as setts) were also noted.  Setts were examined for evidence of current use including:
▪ Identifiable badger hairs present within sett entrances or spoil heaps;
▪ Badger prints present within sett entrances or spoil heaps;
▪ Well-worn paths connecting the sett with other known setts, badger latrines or dung
pits; 
▪ Recent digging when associated with other evidence of badger; or
▪ Bedding present at sett entrances or recently buried within spoil heaps.
2.3.8 Day nests comprised of collections of bedding above ground were also noted if present.
2.3.9 Badger surveys can be carried out at any time of the year.  However, the optimum period is
between November and March when vegetation has died back, and signs can be more easily
seen. Information on the legal protection afforded to badger can be found in Appendix 5.

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Nesting Birds
2.3.10 The habitats within the survey area were evaluated for their suitability to support notable bird
species and, in particular, nesting birds.  Information on the legal protection afforded to birds
can be found in Appendix 6.
Invasive Non-native Species
2.3.11 Particularly common, invasive non-native species, such as giant hogweed (Heracleum
mantegazzianum), Japanese knotweed (Fallopia japonica), and Himalayan balsam (Impatiens
glandulifera) will have been noted, where found.  
Other Notable Species or Habitats
2.3.12 Any suitable habitat for and field signs of SBL species brown hare (Lepus europaeus), hedgehog
(Erinaceus europaeus) and common toad (Bufo bufo) will be recorded where present. No
survey was undertaken specifically for SBL invertebrates or bird species, however, species
were recorded where incidentally observed during the survey.
2.4 Limitations
Physical Limitations
2.4.1 No physical limitations occurred during the survey.
Seasonal Limitations
2.4.2 Ecological surveys provide a snapshot of the broad habitats and species present within the
survey area at the time the survey is undertaken. Faunal species are transient in nature and
can move in and out of an area. A lack of field signs of any particular species does not confirm
absence, only that no field signs were present at the time of survey. Suitability for protected
species and variation in use of the site by protected species on a seasonal basis has been
considered based on the broad habitat types present.
2.4.3 There are seasonal limitations to all species and habitats surveys.  A table of optimal survey
periods can be found in Appendix 7.

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3 Results
3.1 Desk study 
3.1.1 The following designated sites were located within 2km of the proposed site:                                                                                                                                                                                                                                                                                                                                                                                                                                                                                                                                                                                                                                                                                                                                                                                               
▪ Brucehill - Inland Cliff, Local Nature Conservation Site (LNCS), approximately 1.6 km from
the site; 
▪ Inner Clyde, SSSI, SPA, Ramsar and RSPB Reserve, approximately 80m from the site; 
▪ 15 AWIs, closest being Wood ID:26708 , located within the site; and, 
▪ Four SINCs, the closest being Finlaystone Estate found within the site boundary,
Barscube Hill, approximately 950m from the site, Knockmountain Wood, approximately
1.7km, Ferryhill Plantation, approximately 1.8km from the site.
3.1.2 From the desk study it has been found that the following bat species are known to be found
within Renfrewshire: common pipistrelle (Pipistrellus pipistrellus), soprano pipistrelle (P.
pygmaeus), Daubenton’s (Myotis daubentonii), Natterer’s (Myotis nattereri), Leisler’s
(Nyctalus leisleri), noctule (Nyctalus noctula) and brown long-eared bat (Plecotus auritus). 
There are records of soprano pipistrelle bats found approximately 300m from the site. Brown
long-eared bat has been recorded within 1km of the site.
3.1.3 Within the Renfrewshire Local Development Plan, policy ENV1: Greenbelt and ENV2: Natural
Heritage are both relevant to the site.
3.1.4 One record of hedgehog (Erinaceus europaeus) was recorded approximately 420m from the
site.
3.1.5 The full desk study results can be found in Appendix 8.
3.2 Ecological Constraints Survey
3.2.1 All ecological constraints identified within the site can be viewed in Appendix 9.
Habitat 
3.2.2 The site is found within a woodland setting, dominated by rhododendron and an open area of
semi improved grassland with broadleaved woodland, including beech (Fagus sylvatica), ash
(Fraxinus excelsior), sycamore (Acer pseudoplatanus), goat willow (Salix caprea). The south of
the site is a steep rock face. 
Protected Species
Bats 
3.2.3 As the site is surrounded by ancient woodland, the site and areas surrounding the site has
suitable foraging and commuting habitat for bats. The vegetation line, stone wall and road to
the north of the site provides a suitable commuting corridor for foraging and commuting bats.
Therefore, site was classed as having moderate suitability for foraging and commuting bats.
3.2.4 One mature ash tree to the far west of the site contains two knot holes and one tear out which
were inspected by endoscope for signs of roosting bats. No field signs of bats were found
within any of the features. Two knot holes approximately 7m up, south facing and north facing
had negligible suitability for roosting bats. The limb tear out had high suitability for roosting

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bats with a depth of approximately 0.5m and a diameter of 3/4cm. All features were soft
blocked with vegetation.
3.2.5 A sycamore tree located to the far east of the site contains a tear out located on the main stem
approximately 1m up. This feature was endoscoped and no field signs of bats were found
within it. The feature had low suitability for roosting bats and was soft blocked with
vegetation. 
3.2.6 The locations of the trees can be seen in Appendix 9.
Badger
3.2.7 The site has suitable habitat for badger within the woodland area of the site. No field signs
were recorded during the survey.
Nesting Birds
3.2.8 The trees and shrubs within the site have suitable habitat within the site for nesting birds. No
nests were noted on site. During the survey calls of long-tailed tits (Aegithalos caudatus), blue
tits (Cyaniste caeruleus), magpie (Pica pica), blackbird (Turdus merula), and robin (Erithacus
rubecula) were recorded. 
Invasive, Non-native Species
3.2.9 Rhododendron was recorded to the east of the site.
Other Notable Species or Habitats
3.2.10 No other species were recorded.

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Ecological Constraints Survey and Preliminary Roost Assessment – Finlaystone, Marypark Road, Finlaystone   
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4 Discussion and Recommendations
4.1 Discussion
4.1.1 As the site is found on the extreme edge of the Finlaystone Estate SINC and within an ancient
woodland, the proposed development may affect the integrity of these designated site,
however if recommendations are followed, there may be short term indirect effects to these
sites, during construction works.
4.1.2 The woodland within the site is an ancient woodland which is listed within the Scottish
biodiversity list. It is WSL understanding that the proposed plans will be restricted to an open
area which has previously been cleared in the distant past and is now dominated by
rhododendron with limited tree limbing and removal of young trees only, therefore avoiding
any direct impact to the ancient woodland.
4.1.3 Within the Renfrewshire Local Development Plan, policy ENV1 and ENV2 are both relevant to
the site. 
4.1.4 The site has suitable habitat for badger and nesting birds, however no field signs of badger
were found during the survey. There is a large area of rhododendron which is an invasive non-
native species found within the site. 
4.1.5 As the surrounding habitat to the site is ancient woodland, there are other opportunities for
foraging and commuting bats in the nearby woodland, beyond the site boundary. 
4.1.6 Two trees were found to be suitable for use by roosting bats. As there was no current of
historical evidence of use by bats these features were soft blocked with organic material. 
4.2 Recommendations
Licensing Requirements 
4.2.1 No licence is currently required but may be required following further survey work.
4.2.2 A summary of relevant policy can be found in Appendix 2, with the legal position in relation to
protected species is contained within Appendix 3 - 6. 
Avoidance / Retention 
4.2.3 WSL understands that the ash tree to the west of the site is to be retained within the project
plans. If the tree is to be removed it is recommended that the tree undergoes a pre-fell check
for bats prior to removal. 
4.2.4 It is recommended that any vegetation clearance should be carried outside the nesting bird
season (typically March-September). 
4.2.5 It is recommended that where possible, the vegetation line which borders the north of the site
should be retained along with the stone wall to avoid disturbance to foraging and commuting
bats.
4.2.6 It is recommended that all works stop an hour before sunset and not commence again until
an hour after sunrise to avoid disturbance to any foraging and commuting bats.
4.2.7 As the rhododendron is an invasive non-native species, it should not be allowed to spread from
the site, if they must be removed advice should be sought from a specialist prior to removal.

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Further Survey 
4.2.8 The blocking of features in our experience can remain in place up to three months, therefore
the work should be carried out as soon as possible. If the proposed works extends beyond
three months from the point of survey, an ecologist should be contacted for further advice.
4.2.9 Should avoidance of the nesting bird season (March-September) not be possible, a nesting
bird survey should be undertaken no more than 48 hours prior to any work being undertaken
on site by a suitability experienced ecologist.
4.2.10 A pre-construction survey for badger should be carried out within eight weeks of works
commencing due to the high mobility of wildlife.
4.2.11 Due to the high mobility of wildlife and to re-establish the ecological baseline, if the proposed
works have not commenced within 12 months then the project ecologist should be contacted
to determine the requirement for repeat ecological surveys. The bat survey is valid for up to
18 months from the date of survey (CIEEM, 2019). 
Enhancement Measures
4.2.12 The Local Development Plan contains policies ENV1 and ENV2 which focus on the natural
environment and details how new developments can enhance habitats/biodiversity including
through creating, enhancing and better linking habitats and ecosystems. 
4.2.13 The policies state that new development should aim to enhance biodiversity where possible.
For redevelopment of the site, consultation should be undertaken with the individual
responsible for biodiversity at the Local Planning Authority and bespoke enhancement
measures designed for the site.

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5  References 
Bang, P. & Dahlstrom, P., 2001, Animal Tracks and Signs, Oxford University Press, Oxford 
CIEEM, 2019, Advice Note on the Lifespan of Ecological Reports & Surveys, April 2019
https://cieem.net/wp-content/uploads/2019/04/Advice-Note.pdf- 
Collins, J. (Ed), 2016, Bat Surveys for Professional Ecologists: Good Practice Guidelines (3rd Edition), Bat
Conservation Trust, London 
Entwistle, A.C., et al., 2001, Habitat Management for Bats – A guide for land managers, landowners and
their advisors, JNCC, Peterborough 
Forestry Commission and The Bat Conservation Trust, 2005, Guidance Note: Woodland Management for
Bats, Forestry Commission, Wetherby 
IEMA - Institute of Environmental Management and Assessment (1997) Guidelines for Baseline Ecological
Assessment, Taylor & Francis, London 
JNCC Joint Nature Conservation Committee, 2005, Handbook for Phase I Habitat Survey: A Technique for
Environmental Audit, JNCC, Peterborough 
JNCC, 2003, Extended Phase 1 Habitat Survey, England Field Unit, Nature Conservancy Council,
Peterborough 
Mitchell-Jones, A.J and McLeish, A.P, 2004, The Bat Workers Manual. JNCC, Peterborough. 
Renfrewshire Biodiversity Action Plan 2018 – 2022:
https://www.renfrewshire.gov.uk/media/6303/Renfrewshire-Biodiversity-Action-Plan-2018-
2022/pdf/Biodiversity_Action_Plan_FINAL.pdf?m=1527000856037 
Renfrewshire Local Development Plan 2021: 
https://www.renfrewshire.gov.uk/media/14133/Renfrewshire-Local-Development-Plan-
2021/pdf/Renfrewshire_Local_Development_Plan_2021.pdf?m=1638892760710 
Roper, Timothy J., 2010, Badger, Collins, London 
Rose, F. & O’Reilly, C., 2006, The Wild Flower Key (revised edition), Frederick Warne, London 
Scottish Biodiversity Forum, 2012, www.biodiversityscotland.gov.uk     
Scottish Natural Heritage, 2001, Scottish Wildlife – Badgers and development, SNH, Battleby 
Scottish Natural Heritage, 2014, Licensing Guidance – What is a Badger Sett?, SNH, Inverness 
The UK Biodiversity Action Plan (UK BAP), 2012, http://jncc.defra.gov.uk/page-5155

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Appendix 1 – Site Location and Photographs

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Photographs 
Image 1: Proposed site area 
Image 2: Rhododendron on site. Target note 1.

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Image 3: Ash tree with features suitable for roosting bats. No field signs of bats noted.

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Image 4: Stone wall along the northern boundary of the site. 
Image 5: Sloping area to the south of the site.

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Image 6: Site view looking to the north of the site.

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Image 7: Knot holes on ash tree which has suitability for roosting bats. Target note 2.

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Image 8: Limb tear out on ash tree. Target note 2.

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Image 9: Knot hole which has suitable features for roosting bats. Target note 2.

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Image 10: Tear out on sycamore tree, feature suitable for roosting bats.  No field signs of
bats were found. Target note 3.

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Appendix 2 – Summary of Relevant Policy and Legislation 
Policy and Guidance in Scotland
This section briefly summarises the policy, guidance and related issues in Scotland that are relevant to the main
text of the report. The following text does not constitute legal or planning advice. 
Scottish Planning Policy (SPP) (Scottish Government, 2014)1
The SPP sets out planning policies including those that relate to the protection of biodiversity. Planning authorities,
and all public bodies, have a duty under the Nature Conservation (Scotland) Act 2004 to further the conservation
of biodiversity Policy Principles. The SPP states the planning system should: 
▪ Facilitate positive change while maintaining and enhancing distinctive landscape character; 
▪ Conserve and enhance protected sites and species, taking account of the need to maintain healthy
ecosystems and work with the natural processes which provide important services to communities; 
▪ Promote protection and improvement of the water environment, including rivers, lochs, estuaries,
wetlands, coastal waters and groundwater, in a sustainable and coordinated way; 
▪ Seek to protect soils from damage such as erosion or compaction; 
▪ Protect and enhance ancient semi-natural woodland as an important and irreplaceable resource,
together with other native or long-established woods, hedgerows and individual trees with high nature
conservation or landscape value; 
▪ Seek benefits for biodiversity from new development where possible, including the restoration of
degraded habitats and the avoidance of further fragmentation or isolation of habitats; and 
▪ Support opportunities for enjoying and learning about the natural environment. 
National Planning Framework 3 (Scottish Government, 2014)2 
The National Planning Framework, sets out a long-term vision for development and investment across Scotland
over the next 20 to 30 years.
Paragraph 4.5 states “Biodiversity in Scotland is rich and varied. We have numerous internationally and nationally
important habitats and species with a diverse network of protected sites, concentrated particularly in the north
and west of Scotland, along our coasts and estuaries and in our upland areas. However, biodiversity is not just
confined to our rural areas - our built environment, key infrastructure corridors and the greenspaces within our
cities and towns also provide important habitats, and can together contribute to a wider national ecological
network. Our marine wildlife is rich and varied. Geodiversity underpins our landscapes and provides important
ecosystem services.” 
Paragraph 4.10 states “The 2020 Challenge for Scotland's Biodiversity aims to promote and enhance Scotland's
nature, and to better connect people with the natural world. Maintaining our natural capacity to provide services
makes economic sense - to help achieve this, biodiversity in Scotland needs to be viewed at a landscape scale.” The
2020 Challenge for Scotland's Biodiversity is part of the Scottish Biodiversity Strategy as described below.
UK Biodiversity Action Plan (UKBAP), (JNCC, 1994)3
The United Kingdom Biodiversity Action Plan (UK BAP) was published in 1994. It was the UK Government’s
response to the Convention on Biological Diversity (CBD), which the UK signed up to in 1992 at the Earth Summit
in Rio de Janeiro. The UK BAP describes the biological resources of the UK and provides detailed plans for
conservation of these resources. 
1 https://www.gov.scot/publications/scottish-planning-policy/
2 https://www.gov.scot/publications/national-planning-framework-3/
3 https://jncc.gov.uk/our-work/uk-bap/

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Scottish Biodiversity Strategy4
In Scotland, the Scottish Biodiversity Group was formed and identified national priorities and targets for species
and habitats in conjunction with local authorities, non-governmental organisations and local communities, with
the production of the Scottish Biodiversity Strategy (including the Scottish Biodiversity List5. The Scottish
Biodiversity List is a list of animals, plants and habitats that Scottish Ministers consider to be of principal
importance for biodiversity conservation in Scotland.
Planning and Development: Protected Animals, Protected Areas NatureScot (Formerly SNH)6
NatureScot states that the presence, or potential presence, of any protected species is a “material consideration
in planning application decisions”.
If there is reasonable evidence that a protected species is present on site or may be affected by a proposal, its
presence must be assessed and measures proposed to avoid impacts, as necessary. 
Early surveys and comprehensive protection plans will help to progress a development proposal that may affect a
protected animal.
Proposals requiring the most careful scrutiny include those that may impact on:
▪ European protected species – e.g. bats, otter and great crested newt;
▪ Species on Schedule 5 of the Wildlife and Countryside Act 1981 (as amended) – e.g. red squirrel and water
vole; and
▪ Badger – protected under the Protection of Badgers Act 1992. 
You may need to apply to NatureScot for a licence for any activity that has the potential to disturb a protected
species. This includes disturbance of the species for the purpose of the development and/or survey work.
The “Planning and Development -Protected Areas” document highlights the importance of protected areas in
Scotland. A Habitats Regulations Appraisal must be conducted for any development proposal that requires
planning permission or other consent and might affect a Natura site.
Guidance on European Protected Species, development sites and the planning system (Scottish Government
2006)7
This document highlights the importance of completing all surveys for European Protected Species prior to seeking
planning permission. 
It warns against the use of suspensive conditions in planning permissions instead of fully ascertaining, prior to the
determination of the planning application, whether a European Protected Species (EPS) is present on a site. 
Therefore, to ensure that all decisions are compliant with the Habitats Directive and the Regulations and the above
mentioned Guidance, planning authorities should fully ascertain whether protected species are on site and what
the implications of this might be before considering whether to approve an application or not. 
Therefore, it is recommended that ecological surveys for EPS are carried out prior to seeking planning
permission.   
4 https://www.nature.scot/scotlands-biodiversity/scottish-biodiversity-strategy
5 https://www.nature.scot/scotlands-biodiversity/scottish-biodiversity-strategy/scottish-biodiversity-list
6 https://www.nature.scot/professional-advice/planning-and-development/planning-and-development-
advice/planning-and-development-protected-species and https://www.nature.scot/professional-
advice/planning-and-development/advice-planners-and-developers/planning-and-development-protected-areas
7 https://www.gov.scot/publications/european-protected-species-chief-planner-letter/

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Appendix 3 - European Protected Species and the Law
Bats, otters, great crested newts, natterjack toad, wildcat, cetaceans, and several other animals are protected
under European law, in Annexes II and IV of Council Directive 92/43/EEC of 21 May 1992 on the conservation of
natural habitats and of wild fauna and flora (The Habitats Directive 1992). The Habitats Directive is translated into
Scots law under the Conservation (Natural Habitats, &c.) Regulations 1994 (as amended in Scotland), often
referred to as the Habitats Regulations, with these species being classified as European protected species.  Under
these regulations it is an offence to: 
▪ Damage or destroy a breeding site or resting place of such an animal; and to, 
deliberately or recklessly:
▪ Capture, injure or kill a wild animal of a European protected species;
▪ Harass a wild animal or group of wild animals of a European protected species;
▪ Disturb such an animal while it is occupying a structure or place which it uses for shelter or protection;
▪ Disturb such an animal while it is rearing or otherwise caring for its young;
▪ Obstruct access to a breeding site or resting place of such an animal, or otherwise to deny the animal use
of the breeding site or resting place;
▪ Disturb such an animal in a manner that is, or in circumstances which are, likely to significantly affect the
local distribution or abundance of the species to which it belongs; and,
▪ Disturb such an animal in a manner that is, or in circumstances which are, likely to impair its ability to
survive, breed or reproduce, or rear or otherwise care for its young. 
There are also several plant, fungi, and lichen species protected under this legislation.  EPS animals can potentially
return to the same resting site every year; therefore, bat roosts, otter holts, etc. are protected even if there are
no animals there all year round.  These laws are not designed to prevent work, but to minimize its impact on the
long-term survival of EPS.  As such, some activities affecting EPS or their places of shelter may need to be done
under and in accordance with the terms of a licence issued by the licensing authority, NatureScot allow certain
otherwise illegal actions to be undertaken legitimately.  Such activities might include: 
▪ Blocking, filling or installing grilles over old mines or tunnels;
▪ Building, alteration or maintenance work;
▪ Getting rid of unwanted bat colonies;
▪ Tree felling;
▪ Re-roofing;
▪ Remedial timber treatment;
▪ Rewiring or plumbing in roofs;  
▪ Demolition;
▪ Maintenance or construction of watercourse crossings (e.g. culverts under roads, bridges);
▪ Vegetation clearance along riparian corridors; 
▪ Any disturbing (e.g. loud or night works) within proximity to watercourses;
▪ Dewatering or infilling ponds;
▪ Removal of woodpiles and debris near waterbodies; and,
▪ Translocation of species. 
If a licence is required: 
Further survey will be required in order to gain sufficient information in order to supply a sufficient baseline
and to inform the necessary mitigation plan required to support a licence application.
Application forms can be found on the NatureScot website along with guidance:
https://www.nature.scot/professional-advice/protected-areas-and-species/licensing/species-licensing-z-
guide/bats/bats-licences-development 
Please note the need to provide clear justifications as to the purpose of the licence and any alternatives
which may have been considered. Supporting information will be required to specifically support an
application and depending on the findings of this survey, further survey work may be required, along with
a detailed mitigation plan specific to the bat interest on this site and to the works proposed.  NatureScot

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also generally require that all other consents, such as planning permission and historic building consent,
are in place before a licence will be considered. 
A Habitats Regulations licence may be granted by NatureScot if the following three tests are met:
1. That the licence application must demonstrably relate to one of the purposes specified in Regulation
44(2) of the Habitats Regulations.  These purposes include, among others:
▪ Preserving public health or public safety;
▪ Other imperative reasons of overriding public interest, including those of a social or economic
nature and beneficial consequences of primary importance for the environment; or,
▪ Preventing serious damage to livestock, foodstuffs for livestock, crops, vegetables, fruit,
growing timber or any other form of property, or to fisheries.
2. That there is no satisfactory alternative; and
3. That the development will not be detrimental to maintenance of the populations of the species at a
favourable conservation status. 
If an EPS is found during the period of development:
The project ecologist should be contacted immediately for advice before proceeding with works. Advice from
NatureScot may be required; the project ecologist should be able to determine this.

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Appendix 4 – Wildlife and Countryside Act Species and
the Law 
Red squirrel, pine marten, water vole, freshwater pearl mussel, as well as some species of fish and other
invertebrates protected under national legislation, the Wildlife and Countryside Act (1981) (as amended in
Scotland) Schedule 5.  Several plants are also protected under this piece of legislation under Schedule 8.  Species
such as pine marten and red squirrel are fully protected, making it an offence to intentionally or recklessly: 
▪ Kill, injure, or take any wild animal included in Schedule 5;
▪ Damage or destroy any structure or place which any wild animal specified in Schedule 5 uses for shelter
or protection; 
▪ Disturb any such animal while it is occupying a structure or place which it uses for shelter or protection;
and
▪ Obstruct access to any structure or place which any such animal uses for shelter or protection. 
The water vole, though in sharp decline in the UK, and is listed on Schedule 5 in respect of section 9(4) only, i.e.
their habitat is protected but the animals themselves are not, except while they are in their shelters. So while it is
not an offence to kill, injure or take a water vole in Scotland, the other offences regarding damage to shelter and
disturbance still apply.  Although water voles are not currently protected from killing or taking in Scotland, England
and Wales gave water vole full protection in April 2008, and they are expected to receive full protection in Scotland
in the near future. 
If a licence is required: 
The recent Wildlife and Natural Environment (Scotland) Act 2012 provided a new licensing purpose to apply to
Schedules 5 and 8 species listed in the Wildlife and Countryside Act.  The new purpose is designed to mimic the
tests required for EPS species.  Therefore, there is still a need to provide clear justifications as to the purpose of
the licence and any alternatives which may have been considered. Supporting information will be required to
specifically support an application and depending on the findings of this survey, further survey work may be
required, along with a detailed mitigation plan specific to the Schedule 5 interest on this site and to the works
proposed.  NatureScot also generally require that all other consents, such as planning permission and historic
building consent, are in place before a licence will be considered.   
The relevant purposes for which a licence can be granted include: 
▪ Preserving public health or public safety;
▪ Preventing serious damage to livestock, foodstuffs for livestock, crops, vegetables, fruit, growing timber,
or any other form of property or to fisheries; or
▪ For any other social, economic or environmental purpose; provided that
a. Undertaking the conduct authorized by the licence will give rise to or contribute towards the
achievement of, a significant social, economic or environmental benefit; and,
b. There is no other satisfactory solution. 
Application forms can be found on the NatureScot website along with guidance:
https://www.nature.scot/professional-advice/protected-areas-and-species/licensing/licensing-forms-and-
guidance 
If a Schedule 5 species is found during the period of development:
The project ecologist should be contacted immediately for advice before proceeding with works. Advice
from NatureScot may be required; the project ecologist should be able to determine this.

Page 95

Appendix 5 – Badgers and the Law
Badgers are protected by the Protection of Badgers Act 1992 (as amended in Scotland).
The purpose of the Act is to protect the animals from deliberate cruelty and from the incidental effect of lawful
activities which could cause them harm. Under this legislation it is an offence to deliberately or recklessly: 
▪ Kill, injure, take, possess or cruelly ill-treat a badger or attempt to do so;
▪ Damaging or destroying it;
▪ Obstruct access to, or any entrance of, a badger sett; and,
▪ Disturb a badger whilst it is occupying a sett. 
If a licence is required: 
Application forms can be found on the NatureScot website along with guidance:
https://www.nature.scot/badgers-licence-forms-and-guidance-documents 
Please note supporting information will be required to specifically support an application and depending on the
findings of this survey, further survey work may be required, along with a detailed mitigation plan specific to the
badger interest on this site and to the works proposed.  NatureScot also generally require that planning permission
is in place before a licence will be considered. 
If a badger is found during the period of development:
The project ecologist should be contacted immediately for advice before proceeding with works. Advice from
NatureScot may be required; the project ecologist should be able to determine this.

Page 96

Appendix 6 – Birds and the Law
All species of wild bird and their nests are also protected under the Wildlife and Countryside Act 1981 (as amended
in Scotland), which makes it illegal to deliberately or recklessly: 
▪ kill, injure or take any wild bird;
▪ take, damage or destroy the nest of any wild bird while that nest is in use or being built;
▪ At any other time takes, damages, destroys or otherwise interferes with any nest habitually used by any
wild bird included in Schedule A1;
▪ Obstructs or prevents any wild bird from using its nest; and,
▪ take or destroy an egg of any wild bird. 
There are also further offences for birds listed on Schedule 1 of the Act which includes deliberately or recklessly:
▪ Disturbing any wild Schedule 1 bird while it is building a nest or is in, on or near a nest containing eggs or
young; and,
▪ Disturbing dependent young of such a bird. 
You should note that there is no licensable purpose of development for birds. 
Should there be a risk of one of the above offences it is strongly advised that works are either micro-sited to avoid
the nests or timed to avoid the nesting season (1 March to 31 August), depending on the species and type of work. 
If live nests are found:
The project ecologist should be contacted immediately for advice before proceeding with works. Advice from
NatureScot may be required; the project ecologist should be able to determine this.

Page 97

Appendix 7 – Guidance on Optimal Survey Periods
Protected
Species Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec
Habitats &
Vegetation
Recommended time to surveys mosses
and lichens only Recommended time to undertake Phase 1 habitat surveys Recommended time to surveys mosses
and lichens only
Badgers Best time for field surveys Surveys possible, but sub-optimal Best time for field surveys
Bats Inspection of hibernation, tree and
building roosts
Activity
surveys
only;
invasive
surveys to
be avoided
Activity surveys and inspection of building roosts.
Emergence counts.
Activity
surveys
only;
invasive
surveys to
be avoided
Inspection of
hibernation, tree and
building roosts
Birds Winter birds Breeding birds/migrant species Breeding birds Breeding birds/migrant species Winter birds
Otters Year-round surveying, though wet
weather can limit visibility.
Surveys for otters can potentially be conducted all year round, preferably when weather
condition are stable, though dense vegetation cover can be limiting
Year-round surveying,
though wet weather can
limit visibility.
Pine Martens
Surveys can be carried
out at any time of year,
though better in spring
and summer
Survey for breeding dens Optimal survey period is spring to
summer
Surveys can be carried out at any time of year, though
better in spring and summer
Red Squirrels Survey at any time of year, breeding
females
Survey at any time of year weather permitting, optimal in spring and summer. 
Breeding females can be surveyed December to September
Survey at any time of
year
Breeding
females
Water Voles Reduced WV
activity
Initial
surveys Best time to survey Surveys possible, but vegetation cover & weather
conditions can be limiting
Initial
surveys
Reduced WV
activity
Great Crested
Newt
No surveys as newts in
hibernation
Pond Surveys for adults: mid-March to mid-June. 
Surveys must include visits undertaken between
mid-April and mid-May.  Egg surveys April to mid-
June.  Larvae surveys from mid-May Terrestrial
habitat surveys
Larvae surveys to mid-
August Terrestrial
habitat surveys
Terrestrial habitat
surveys
No Surveys – newts in
hibernation

Page 98

Appendix 8 - Desk Study Search Results 
Location Finalystone,
Marypark Road OS Grid Squares NS37587734
60
Date of
Search 05/11/2022
Wild Surveys Data
Bat Species
No of Records within
2 km
Approximate
distance in km Site name/Grid Ref Date
Soprano pipistrelle 1 390m south NS3788373105 Sep 2013
Wild Surveys Data
Protected Species
No of Records within
2 km
Approximate
distance in km Site name/Grid Ref Date
No Data    
NBN Bat Species
Data
No of Records within
2 km
Approximate
distance in km Site name/Grid Ref Date Data
Licence
Soprano pipistrelle 4 1km west NS3649173501 June
208 –
Jue
2019
CC-BY Bat
Conservati
on Trust
Brown long eared 24 1km west NS3649173501 June
2007 –
June
2019
CC-BY Bat
Conservati
on Trust
NBN Species
Protected Species
No of Records within
2 km
Approximate
distance in km Site name/Grid Ref Date Data
Licence
Hedgehog 1 420m east NS3804373448 August
2019
The
Conservati
on
Volunteer
LOCAL BAT GROUP
Bat Species Data
No of Records within
2 km
Approximate
distance in km Site name/Grid Ref  Date 
No Data     
Renfrewshire Biodiversity Action Plan (2018 – 2022)

Page 99

Species action plans with relevance to the site / survey area:
▪ Juniper
▪ Orchids
▪ Red and amber list bird species
▪ Lesser whitethroat
▪ Invasive, non-native species 
Habitat action plans with relevance to the site / survey area:
• Mixed deciduous woodlands
• Upland oakwood
• Upland birchwood
• Wet Woodland
• Blanket bogs
• Meadows
• Heathland 
Bat species known to be present within the LBAP area:
▪ Soprano pipistrelle
▪ Common pipistrelle
▪ Daubenton’s bat
▪ Whiskered bat
▪ Leisler’s bat
▪ Natterer’s bat
▪ Brown long eared bat
▪ Nathusius pipistrelle
Designated Site Search- Statutory, Non-statutory and Local Nature Reserves within 2 km
Site name & Grid
Reference Designation Features  Distance
Brucehill- Inland Cliff LNCS
Inland sandstone cliffs with
dripping water which
supports various ferns and
bryophytes.
1.6km north
Inner Clyde
SSSI & SPA &
RAMSAR &
RSPB Reserve
Inner clyde encompasses
the interidal zone of the
Clyde estuary which is
important habitat for
wintering birds, especially
waders. Estuarine saltmarsh
and mudflats. 
80m north
15 AWI AWI
15 AWI found within 2km of
the site boundary. The
closest being within the site,
Wood ID: 26708 which is of
semi-natural origin.
Within the site – 2km

Page 100

Finlaystone Estate SINC 
Broad leaved woodland with
extensive conifer
plantations.  Within in the site.
Barscube Hill SINC
Semi-improved pasture on a
lope with several prominent
ridges and depressions. 
950m south
Knockmountain Wood SINC Woodland, Grassland and
Marshland. 1.7km southwest
Ferryhill Plantation SINC
Woodland mainly downy
and silver birch with ancient
woodland.
1.8km east 
Data Licenses
Open Government License (OGL). OGL license information can be found at: 
http://www.nationalarchives.gov.uk/doc/open-government-licence/version/2/
Creative Commons license with attribution (CC-BY).  CC-BY license information can be found at:
https://www.creativecommons.org/licenses/by/4.0

Page 101

Designated Sites Map

Page 102

Appendix 9 – Constraints Plan 
Ecological Constraints Map
Finlaystone Estate,
Marypark Road, Langbank,
PA14 6UT

Page 103

Target
Note Grid Reference Notes
1 NS3757573462 Rhododendron approximately 3m x 7m.
2 NS3755573450 Mature ash tree. Three knot holes and one tear out located on tree. 
3 NS3758773453
Sycamore tree. Tear out on the main steam approximately 1m up, south
facing. 
Tree
No.
Grid
Reference
Species Feature BCT
Suitability 
Field
Signs
Recommendations
2
NS3755573450
Ash 2 knot
holes
1 limb
tear out
Low 
High
NA Works within site be
carried out within
three months.
3
NS3758773453
Sycamore Tear out
on main
stem
~1m high
Negligible NA NA

Page 104

Registered Address
Room 41, 
St James Business Centre, 
Linwood Road, 
+44 (0) 141 887 2770 
j

Page 105

MEMORANDUM 
Communities and Housing 
Director: Mary Crearie 
Tel: 07768988028 Fax: 0141 618 7500
My Ref: CH/KMcI/LC
Your Ref: 22/0125/PP
Ask For: Karen McIndoe
Date: 9 March 2022   
To: Sharon Marklow, Strategy and Place Manager 
From:  Head of Communities & Public Protection 
Application Number:   22/0125/PP 
LOCATION:    Site On Western Boundary Of Marypark, 
Marypark Road, Langbank 
While the site does not appear to have a long history of previous use, historical map
information suggests a building (unknown use) was formerly present onsite c1970s.
While there is no requirement for action at this stage, should ground disturbance
uncover any evidence of contamination or unusual materials (e.g. membranes, relict
structures, materials with unusual colour/texture/odour, staining/sheens etc) during
the proposed works, all work should cease immediately. The applicant should then
seek professional advice regarding the ground conditions at the site, and their
implications for the proposed development, and notify the Building Standards section
of the Council in the first instance. 
Karen McIndoe
Environmental Health Officer

Page 106

Page 1 of 7
Renfrewshire House Cotton Street Paisley PA1 1JD  Tel: 0300 3000 144  Fax: 0141 618 7935  Email: dc@renfrewshire.gov.uk
Applications cannot be validated until all the necessary documentation has been submitted and the required fee has been paid.
Thank you for completing this application form:
ONLINE REFERENCE 100538106-001
The online reference is the unique reference for your online form only. The  Planning Authority will allocate an Application Number when
your form is validated. Please quote this reference if you need to contact the planning Authority about this application.
Type of Application
What is this application for? Please select one of the following: *
  Application for planning permission (including changes of use and surface  mineral working).
  Application for planning permission in principle.
  Further application, (including renewal of planning permission, modification, variation or removal of a planning condition etc)
  Application for Approval of Matters specified in conditions.
Description of Proposal
Please describe the proposal including any change of use: *  (Max 500 characters)
Is this a temporary permission? *  Yes   No
If a change of use is to be included in the proposal has it already taken place?  Yes   No
(Answer ‘No’ if there is no change of use.) *
Has the work already been started and/or completed? *
 No   Yes – Started   Yes - Completed
Applicant or Agent Details
Are you an applicant or an agent? * (An agent is an architect, consultant or someone else acting
on behalf of the applicant in connection with this application)  Applicant  Agent
Application for Permission in Principle for new Dwelling House

Page 107

Page 2 of 7
Agent Details
Please enter Agent details
Company/Organisation:
Ref. Number: You must enter a Building Name or Number, or both: *
First Name: * Building Name:
Last Name: * Building Number:
Address 1
Telephone Number: * (Street): *
Extension Number: Address 2:
Mobile Number: Town/City: *
Fax Number: Country: *
Postcode: *
Email Address: *
Is the applicant an individual or an organisation/corporate entity? *
  Individual    Organisation/Corporate entity
Applicant Details
Please enter Applicant details
Title: You must enter a Building Name or Number, or both: *
Other Title: Building Name:
First Name: * Building Number:
Address 1
Last Name: * (Street): *
Company/Organisation Address 2:
Telephone Number: * Town/City: *
Extension Number: Country: *
Mobile Number: Postcode: *
Fax Number:
Email Address: *
Ingram Architecture & Design
Mr
Stephen
Arthur
Govan
MacMillan
Ingram Street
Finlaystone Estate
227
Finlaystone House
07900 882 495
G1 1DA
PA14 6TJ
UK
UK
Glasgow
Port Glasgow
Langbank
07802 254 056
s.govan@ingramarchitecture.co.uk
arthurmacmillan10@me.com

Page 108

Page 3 of 7
Site Address Details
Planning Authority:
Full postal address of the site (including postcode where available):
Address 1: 
Address 2:
Address 3:
Address 4:
Address 5:
Town/City/Settlement:
Post Code:
Please identify/describe the location of the site or sites
Northing Easting
Pre-Application Discussion
Have you discussed your proposal with the planning authority? *  Yes   No
Pre-Application Discussion Details Cont.
In what format was the feedback given? *
 Meeting  Telephone  Letter  Email
Please provide a description of the feedback you were given and the name of the officer who provided this feedback. If a processing
agreement [note 1] is currently in place or if you are currently discussing a processing agreement with the planning authority, please
provide details of this. (This will help the authority to deal with this application more efficiently.) * (max 500 characters)
Title: Other title:
First Name: Last Name:
Correspondence Reference Date (dd/mm/yyyy):
Number:
Note 1. A Processing agreement involves setting out the key stages involved in determining a planning application, identifying what
information is required and from whom and setting timescales for the delivery of various stages of the process.
Email correspondence with advice given to provide information on the developable footprint, Tyree protection, ecology,
topography and flooding
Mr
Renfrewshire Council
James Weir
02/12/2021
SIte adjacent to Marypark House, Marypark Road, Langbank
673465 237577

Page 109

Page 4 of 7
Site Area
Please state the site area:
Please state the measurement type used:  Hectares (ha)   Square Metres (sq.m)
Existing Use
Please describe the current or most recent use: *  (Max 500 characters)
Access and Parking
Are you proposing a new altered vehicle access to or from a public road? *  Yes   No
If Yes please describe and show on your drawings the position of any existing. Altered or new access points, highlighting the changes
you propose to make. You should also show existing footpaths and note if there will be any impact on these.
Are you proposing any change to public paths, public rights of way or affecting any public right of access? *  Yes   No
If Yes please show on your drawings the position of any affected areas highlighting the changes you propose to make, including
arrangements for continuing or alternative public access.
Water Supply and Drainage Arrangements
Will your proposal require new or altered water supply or drainage arrangements? *  Yes   No
Are you proposing to connect to the public drainage network (eg. to an existing sewer)? *
  Yes – connecting to public drainage network
  No – proposing to make private drainage arrangements
  Not Applicable – only arrangements for water supply required
Do your proposals make provision for sustainable drainage of surface water?? *  Yes   No
(e.g. SUDS arrangements) *
Note:-
Please include details of SUDS arrangements on your plans
Selecting ‘No’ to the above question means that you could be in breach of Environmental legislation.
Are you proposing to connect to the public water supply network? *
  Yes
  No, using a private water supply
  No connection required
If No, using a private water supply, please show on plans the supply and all works needed to provide it (on or off site).
719.60
Vacant Land

Page 110

Page 5 of 7
Assessment of Flood Risk
Is the site within an area of known risk of flooding? *  Yes    No   Don’t Know
If the site is within an area of known risk of flooding you may need to submit a Flood Risk Assessment before your application can be
determined. You may wish to contact your Planning Authority or SEPA for advice on what information may be required.
Do you think your proposal may increase the flood risk elsewhere? *  Yes    No   Don’t Know
Trees
Are there any trees on or adjacent to the application site? *  Yes   No
If Yes, please mark on your drawings any trees, known protected trees and their canopy spread close to the proposal site and indicate if
any are to be cut back or felled.
All Types of Non Housing Development – Proposed New Floorspace
Does your proposal alter or create non-residential floorspace? *  Yes   No
Schedule 3 Development
Does the proposal involve a form of development listed in Schedule 3 of the Town and Country  Yes   No   Don’t Know
Planning (Development Management Procedure (Scotland) Regulations 2013 *
If yes, your proposal will additionally have to be advertised in a newspaper circulating in the area of the development. Your planning
authority will do this on your behalf but will charge you a fee. Please check the planning authority’s website for advice on the additional
fee and add this to your planning fee.
If you are unsure whether your proposal involves a form of development listed in Schedule 3, please check the Help Text and Guidance
notes before contacting your planning authority.
Planning Service Employee/Elected Member Interest
Is the applicant, or the applicant’s spouse/partner, either a member of staff within the planning service or an  Yes    No
elected member of the planning authority? *
Certificates and Notices
CERTIFICATE AND NOTICE UNDER REGULATION 15 – TOWN AND COUNTRY PLANNING (DEVELOPMENT MANAGEMENT
PROCEDURE) (SCOTLAND) REGULATION 2013
One Certificate must be completed and submitted along with the application form. This is most usually Certificate A, Form 1,
Certificate B, Certificate C or Certificate E.
Are you/the applicant the sole owner of ALL the land? *  Yes    No
Is any of the land part of an agricultural holding? *  Yes    No
Certificate Required
The following Land Ownership Certificate is required to complete this section of the proposal:
Certificate A

Page 111

Page 6 of 7
Land Ownership Certificate
Certificate and Notice under Regulation 15 of the Town and Country Planning (Development Management Procedure) (Scotland)
Regulations 2013
Certificate A
I hereby certify that –
(1) - No person other than myself/the applicant was an owner (Any person who, in respect of any part of the land, is the owner or is the
lessee under a lease thereof of which not less than 7 years remain unexpired.) of any part of the land to which the application relates at
the beginning of the period of 21 days ending with the date of the accompanying application.
(2) - None of the land to which the application relates constitutes or forms part of an agricultural holding
Signed: Stephen Govan
On behalf of: Mr Arthur MacMillan
Date: 21/02/2022
 Please tick here to certify this Certificate. *
Checklist – Application for Planning Permission
Town and Country Planning (Scotland) Act 1997
The Town and Country Planning (Development Management Procedure) (Scotland) Regulations 2013
Please take a few moments to complete the following checklist in order to ensure that you have provided all the necessary information
in support of your application. Failure to submit sufficient information with your application may result in your application being deemed
invalid. The planning authority will not start processing your application until it is valid.
a) If this is a further application where there is a variation of conditions attached to a previous consent, have you provided a statement to
that effect? *
 Yes   No   Not applicable to this application
b) If this is an application for planning permission or planning permission in principal where there is a crown interest in the land, have
you provided a statement to that effect? *
 Yes   No   Not applicable to this application
c) If this is an application for planning permission, planning permission in principle or a further application and the application is for
development belonging to the categories of national or major development (other than one under Section 42 of the planning Act), have
you provided a Pre-Application Consultation Report? *
 Yes   No   Not applicable to this application
Town and Country Planning (Scotland) Act 1997
The Town and Country Planning (Development Management Procedure) (Scotland) Regulations 2013
d) If this is an application for planning permission and the application relates to development belonging to the categories of national or
major developments and you do not benefit from exemption under Regulation 13 of The Town and Country Planning (Development
Management Procedure) (Scotland) Regulations 2013, have you provided a Design and Access Statement? *
 Yes   No   Not applicable to this application
e) If this is an application for planning permission and relates to development belonging to the category of local developments (subject
to regulation 13. (2) and (3) of the Development Management Procedure (Scotland) Regulations 2013) have you provided a Design
Statement? *
 Yes   No   Not applicable to this application
f) If your application relates to installation of an antenna to be employed in an electronic communication network, have you provided an
ICNIRP Declaration? *
 Yes   No   Not applicable to this application

Page 112

Page 7 of 7
g) If this is an application for planning permission, planning permission in principle, an application for approval of matters specified in
conditions or an application for mineral development, have you provided any other plans or drawings as necessary:
  Site Layout Plan or Block plan.
  Elevations.
  Floor plans.
  Cross sections.
  Roof plan.
  Master Plan/Framework Plan.
  Landscape plan.
  Photographs and/or photomontages.
  Other.
If Other, please specify: *  (Max 500 characters)
Provide copies of the following documents if applicable:
A copy of an Environmental Statement. *  Yes   N/A
A Design Statement or Design and Access Statement. *  Yes   N/A
A Flood Risk Assessment. *  Yes   N/A
A Drainage Impact Assessment (including proposals for Sustainable Drainage Systems). *  Yes   N/A
Drainage/SUDS layout. *  Yes   N/A
A Transport Assessment or Travel Plan  Yes   N/A
Contaminated Land Assessment. *  Yes   N/A
Habitat Survey. *  Yes   N/A
A Processing Agreement. *  Yes   N/A
Other Statements (please specify). (Max 500 characters)
Declare – For Application to Planning Authority
I, the applicant/agent certify that this is an application to the planning authority as described in this form. The accompanying
Plans/drawings and additional information are provided as a part of this application.
Declaration Name: Mr Stephen Govan
Declaration Date: 21/02/2022
Payment Details
Online payment: 413702
Payment date: 21/02/2022 11:56:53
Created: 21/02/2022 11:56
Flood Risk Assessment, Ecological Report, Tree Survey, Topographic Survey
Ecological Report, Tree Survey

Page 113

Transport Scotland
Roads Directorate
Network Operations - Development Management
Response On Development Affecting Trunk Roads and Special Roads
The Town and Country Planning (Scotland) Act 1997
The Town and Country Planning (Development Management Procedure)
(Scotland) Regulations 2013 S.I.2013 No 155 (S.25)
Town and Country Planning (Notification of Applications) (Scotland) Direction 2009
To Renfrewshire Council
Chief Executive's Service Renfrewshire House Cotton
Street, Paisley, PA1 1WB
Council Reference:- 22/0125/PP
TS TRBO Reference:- NSW/29/2022
Application made by Mr Arthur MacMillan per Stephen Govan, Ingram Architecture & Design 227 Ingram Street Glasgow G1
1DA and received by Transport Scotland on 02 March 2022 for planning permission for erection of dwellinghouse with
associated access (in principle) located at Site On Western Boundary Of Marypark, Marypark Road, Langbank affecting the A8
Trunk Road.
Director, Roads Advice
The Director does not propose to advise against the granting of permission1.
2. The Director advises that planning permission be refused (see overleaf for reasons).
3. The Director advises that the conditions shown overleaf be attached to any permission the council may give
(see overleaf for reasons).
To obtain permission to work within the trunk road boundary, contact the Area Manager through the general contact number
below. The Operating Company has responsibility for co-ordination and supervision of works and after permission has been
granted it is the developer's contractor's responsibility to liaise with the Operating Company during the construction period to
ensure all necessary permissions are obtained.
ü
Operating Company:-
Address:-
Telephone Number:-
e-mail address:- OCCR.SWSCOTLAND@amey.co.uk
TS Contact:- Area Manager (A8)
0141 272 7100
NEW SOUTH WEST
Buchanan House, 58 Port Dundas Road, Glasgow, G4 0HF
150 Polmadie Road, Glasgow
Page 1 of 2

Page 114

Transport Scotland Response Date:- 09-Mar-2022
Roads - Development Management
Buchanan House, 58 Port Dundas Road, Glasgow, G4 0HF
Telephone Number:
e-mail: development_management@transport.gov.scot
Transport Scotland Contact:-
Transport Scotland Contact Details:-
Iain Clement
NB - Planning etc. (Scotland) Act 2006
Planning Authorities are requested to provide Transport Scotland, Roads Directorate, Network Operations - Development Management with a copy of the
decision notice, and notify Transport Scotland, Trunk Roads Network Management Directorate if the recommended advice is not accepted.
Page 2 of 2

Page 115

1
James Weir
From: Stephen Boyle
Sent: 10 March 2022 10:24
To: James Weir
Subject: RE: Consultation Letter for Planning Application Ref:22/0125/PP
Hi James, 
Yes, as it is a private road it would be recommended the access is constructed as per the national roads
development guide ( width, surfacing, drainage, sightlines etc). No surface water should discharge onto the private
road. 
I have not been sent the drive thru application, so either John has it or its been missed. It’s a difficult one as on first
glance I thought it would not be acceptable. However, I'm struggling to see a reason why. 
Doesn’t appear to have any impact on sightlines for the Glenburn Rd/ Caplethill Rd junction, if there was a
restriction then it would be resolved by ensuring no parking takes place on space No1. There is no pedestrian
provision but that could be conditioned and maybe get a footway provided on Glenburn Rd between where the
footway stops and the access to this development. Parking could be considered limited and when car wash is
opened could cause issues. The access off Caplethill Rd would be better closed up and all movements concentrated
on Glenburn Rd, but this would have implications for the car wash. 
I would say if there was a reason to refuse it would be for the increased movements for an access in close proximity
to a junction. There is a lot going on here with a car wash, tyre place and a barbers. There is three access points and
it is hard to determine the impact the development will have on vehicle trips and parking. 
I know that maybe doesn’t help as its quite conflicting but its an awkward one. 
Let me know if you want to discuss further. 
Thanks
Stephen 
-----Original Message-----
From: James Weir <james.weir@renfrewshire.gov.uk> 
Sent: 10 March 2022 09:25
To: Stephen Boyle <stephen.boyle@renfrewshire.gov.uk>
Subject: RE: Consultation Letter for Planning Application Ref:22/0125/PP 
Hi Stephen, 
Yes it looks like private road accessed from trunk road as you say so no problem to not provide comments. An FRA
has been done and we will condition drainage as standard if it gets approved. And we have consulted TS regards the
trunk road. If they ask for a roads authority update I will just say outwith jurisdiction but recommended to follow
national roads development guide or something if that sounds ok? 
Can I ask a favour about another application 21/0057/PP. Not sure who has been allocated it but I am wondering if
you guys will find it acceptable or not? I have attached a block plan. Basically it's at the junction of Glenburn Road
and Caplethill Road, and we have received several objections on road safety. There are also cllr's involved, and its
been called to board. I think we will be recommending refusal anyway, but would be grateful for roads input as well
as if you have concerns as well it would add weight to our decision. 
Hope that’s ok, let me know if you want to discuss further.

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2
Thanks again,   
________________________________
James Weir
Planner, Development Management
Renfrewshire House, Cotton Street, Paisley, PA1 1JD
Phone: 07483370666
Email: dc@renfrewshire.gov.uk
Web: Renfrewshire Council Website 
Please consider the environment before printing this email 
I am currently working from home so have no access to my phone line. Please contact me by email and I will
respond as soon as possible. 
Due to the ongoing issues related to the Coronavirus, unfortunately the Planning Authority are suspending the drop
in duty planning officer service. Please contact Planning via email – dc@renfrewshire.gov.uk 
Please note if you submitted your application via the eDevelopment portal all additional supporting documentation
in relation to your application should be submitted in the same manner as the original application.  Supporting
Documentation should not be sent to the Case Officers email address or to the Council’s dc@renfrewshire.gov.uk
mailbox.  If you have any queries with this process please contact 0300 3000 144. 
-----Original Message-----
From: Stephen Boyle <stephen.boyle@renfrewshire.gov.uk> 
Sent: 09 March 2022 15:55
To: James Weir <james.weir@renfrewshire.gov.uk>
Subject: FW: Consultation Letter for Planning Application Ref:22/0125/PP 
Hi James, 
Mark had sent this to John which has made its way to me as John is still off sick. 
Looking at this application, it is a private road and is served off the trunk road. Is that correct? Not 100% sure we
want or need to comment on this one? I know we had not been consulted on the 19/0516/PP application, 
Let me know your thoughts, slightly reluctant to comment on it as any issues (construction, flooding, surface water
onto the trunk road etc) may come back to us but it is private. 
Thanks
Stephen 
-----Original Message-----
From: Mark Higginbotham <mark.higginbotham@renfrewshire.gov.uk> 
Sent: 08 March 2022 10:36
To: Stephen Boyle <stephen.boyle@renfrewshire.gov.uk>
Cc: John Everett <john.everett@renfrewshire.gov.uk>
Subject: FW: Consultation Letter for Planning Application Ref:22/0125/PP 
Stephen
Can you do while John is off 
Mark Higginbotham
Transportation & Development Manager
Environment & Infrastructure, Renfrewshire Council, Cotton Street, Paisley, PA1 1BR Mob 07432 105694

Page 117

3
-----Original Message-----
From: Mark Higginbotham
Sent: 03 March 2022 12:03
To: John Everett <john.everett@renfrewshire.gov.uk>
Subject: FW: Consultation Letter for Planning Application Ref:22/0125/PP 
For you John 
Mark Higginbotham
Transportation & Development Manager
Environment & Infrastructure, Renfrewshire Council, Cotton Street, Paisley, PA1 1BR Mob 07432 105694 
-----Original Message-----
From: dc@renfrewshire.gov.uk <dc@renfrewshire.gov.uk>
Sent: 02 March 2022 14:49
To: Mark Higginbotham <mark.higginbotham@renfrewshire.gov.uk>
Subject: Consultation Letter for Planning Application Ref:22/0125/PP 
Dear Mark Higginbotham 
Please find attached important information from Renfrewshire Council with regards to the planning application
submitted on 22 February 2022. 
The documentation relating to the application can be reviewed online through the Council's Public Access web site,
if you have registered as a Consultee on the system you directly input your comments to the case through this web
site. 
Kind regards 
Renfrewshire Council
Renfrewshire House, Cotton Street, Paisley, PA1 1JD

Page 118

1
James Weir
From: Kirsteen Macdonald <Kirsteen.Macdonald@agsairports.co.uk>
Sent: 28 March 2022 10:37
To: James Weir
Subject: 22/0125/PP
Hi James 
22/0125/PP 
This application is below consultation height for us so we have no comment. 
Kind regards 
Kirsteen 
Aberdeen | Glasgow | Southampton
Kirsteen Macdonald
Safeguarding Manager
Glasgow Airport   
M +44 (0)7808 115 881    
kirsteen.macdonald@agsairports.co.uk  
www.agsairports.co.uk  
Glasgow Airport, Erskine Court, St Andrews Drive, Paisley, PA3 2TJ        
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