East Dunbartonshire Main Issues Report 2013 Background Report 5
Making the Most of Our Environment East Dunbartonshire Council Local Development Plan 2013 MIR Background Report 5: Making the Most of Our Environment
Overview
This background report provides background information on three areas of policy including:
Green Network Opportunities – This section includes a cover report and Annex 1- a copy of the ‘East Dunbartonshire Green Network Opportunities Mapping’ report prepared with the Glasgow and Clyde Valley Green Network Partnership to identify the most effective opportunities for improving the green network.
Wind Farm Policy and Spatial Framework – This section defines onshore wind energy developments, sets out the national, strategic and current local planning policy context for these and other sources of information. It also sets out the planning considerations for a spatial framework for wind energy development in the East Dunbartonshire Local Development Plan, as required by emerging Scottish Planning Policy.
Local Nature Conservation Sites Review – This Review of Local Nature Conservation Sites was carried out in 2009. The review recommends a range of sites for designation as Local Nature Conservation Sites, see Annex 2. The designation of these sites has been included in the Main Issues Report as a preferred option.
Green Network Opportunities
Introduction
A green network is a strategic network of green infrastructure components such as woodland, wetlands, grasslands, active travel (walking and cycling) routes, greenspace links, open space, watercourses and waterways. The Council wishes to protect, promote, enhance and extend the green network in order to improve the living environment, provide an attractive setting for business and tourism, enhance biodiversity networks, provide opportunities for healthy living and active travel, opportunities to plant woodland for biomass fuel and integrate the urban and rural areas of East Dunbartonshire with the wider city region. The green network in East Dunbartonshire links and integrates with the Glasgow and Clyde Valley Green Network and therefore the wider Central Scotland Green Network. More information can be found in the Monitoring Statement.
New development can have significant benefits in facilitating the development of the green network through developers providing new and enhanced green infrastructure components. Therefore, in order to inform the Main Issues Report, the Glasgow and Clyde Valley Green Network Partnership carried out analysis of East Dunbartonshire to identify areas where green network opportunities could be delivered through new development.
Glasgow and the Clyde Valley Green Network Partnership Green Network Opportunities Mapping
Together with the Glasgow and the Clyde Valley Green Network Partnership the Council has developed a Geographical Information Systems approach to identifying opportunities for
East Dunbartonshire Council Local Development Plan 2013 MIR Background Report 5: Making the Most of Our Environment the delivery of the green network in East Dunbartonshire. More detail can be found in the Opportunities Mapping report, See Annex 1.
The following list sets out the opportunities identified in the Opportunities Mapping report that can be found in the Main Issues Report. These opportunities have been selected because they can be delivered through development sites identified in the Main Issues Report.
Opportunity Settlement Jellyhill Bishopbriggs Westerhill Bishopbriggs Craigton/Tambowie Milngavie The Allander/Auchenhowie Road and Kilmardinny Bearsden / Milngavie North Baljaffrey/Mains Plantation Bearsden / Milngavie Kessington/Templehill Wood Bearsden Glazert Water, Broomhill and Broomhill Kirkintilloch Cleddans and North Hillhead Kirkintilloch Kirkintilloch Gateway/Woodilee Road Kirkintilloch Woodilee Lenzie Gartshore Park Twechar High Park/Balgrochan Marsh and Balgrochan Lennoxtown Station Road/Glazert and Glazert Water Lennoxtown Redhills Lennoxtown Redmoss Grasslands Milton of Campsie
Note: The varying scenarios used in the green network opportunities mapping results in similar locations being shown in multiple scenarios. These locations have been combined in the table above where they overlap. In addition to those sites identified above through the Green Networks Opportunities Mapping, the Council also suggests Cairnhill Woods, Bearsden as a priority area.
East Dunbartonshire Council Local Development Plan 2013 MIR Background Report 5: Making the Most of Our Environment
Wind Farm Policy and Spatial Framework
Introduction
This section defines onshore wind energy developments, sets out the national, strategic and current local planning policy context for these and other sources of information. It also sets out the planning considerations for a spatial framework for wind energy development in the East Dunbartonshire Local Development Plan, as required by emerging Scottish Planning Policy.
Definition of Onshore Wind Energy Developments
A wind farm is a group of wind turbines in the same location used to produce energy. The Strategic Development Plan 2012 addresses wind farms with a generating capacity of 20MW or more, the scale of proposal classed as a major development. Any applications for wind farm developments with output capacity exceeding 50MW are determined by the Scottish Government under s.36 of the Electricity Act 1989. The Council is a statutory consultee on this scale of proposal, submitted to the Scottish Government.
The emerging draft SPP requires wind farms, and wind turbines of all scales to be considered under the Spatial Framework. Wind farm development proposals can be categorised as: . Small Scale Turbines – 15 to 30m, to blade tip . Community Scale Turbines – 30 to 50m, to blade tip . Medium Scale Turbines – 50 to 80m, to blade tip . Larger Scale – 80m to150m, to blade tip . Extensions to Wind farms – All scales and potential for repowering.
Single or small wind turbine proposals are domestic or community in scale, rather than commercial. This type of proposal can be taken as up to 3 turbines and below 70 metres in height (base to blade tip). Appendix 2 sets out the range of wind energy proposal identified in the Supplementary Planning Guidance of adjacent planning authorities.
Draft Scottish Planning Policy (SPP) 2013
Draft SPP requires local development plans to clearly set out the potential for wind turbine and wind farm development of all scales as part of the spatial framework. It also sets the policy for development in green belts, which applies to East Dunbartonshire’s lowland countryside areas.
Paragraph 218 of the Draft SPP identifies the planning considerations that should be considered in a spatial framework. It identifies four groups and notes that, except for those in group 1, the existence of planning considerations does not impose a blanket restriction on wind farm development. The groups include: 1. Areas where wind farms will not be acceptable 2. Areas of significant protection 3. Areas where planning constraints are less significant, where opportunities for wind farm development can be realised through good design or mitigation
East Dunbartonshire Council Local Development Plan 2013 MIR Background Report 5: Making the Most of Our Environment
4. Areas where wind farm proposals are likely to be supported subject to detailed consideration against identified policy criteria
The Draft SPP notes that local development plans should describe the types and scales of development which would be appropriate within a green belt. It states that this can include development meeting a national requirement or established need, if no other suitable site is available. It does not however mention renewable energy directly as an appropriate development in the green belt. Neither does it identify green belt as a planning consideration for the spatial framework for wind energy.
Strategic Development Plan (SDP)
Glasgow & Clyde Valley SDP, 2012, Strategy Support Measure 9 notes that “Low carbon economic growth requires that indigenous supplies of natural resources continue to be developed and that, where feasible, a phased programme of development be established through the life of the plan. Broad areas of search for wind energy have been outlined in the Spatial Development Strategy and it will be for Local Development Plans to take forward the refinement of these areas to establish their long term potential.”
The SDP reflects the context of a low carbon future and protects important natural environments by defining search areas for wind farm developments of 20 Megawatts (MW) generating capacity, see Diagram 16. Background Report 11 Wind Energy Search Areas sets out the methodology for this. This uses a three stage method, as advised by Scottish Government, to identify:
1. Areas of significant protection - international and national designations, wind farms of 20MW or over; existing, consented or at planning application stage. The Green Belt, Cumulative Impact, Landscape Capacity and Visual Impact are to be addressed at local level by local authorities.
2. Other constraints and policy criteria suggestions – It is recognised that the identification of a constraint does not lead to a blanket restriction on development, these include: . Regional and local heritage designations - Regional Scenic Areas (Kilpatrick Hills, Campsie Fells and Kilsyth Hills) are relevant in the Strategic planning context and were considered. . Historic environment – These include World Heritage Sites, Scheduled Ancient Monuments and Conservation Areas . Tourism and recreation – criteria are suggested . Communities – It uses a separation distance of up to 2km between areas of search and the edge of settlements to guide development to the most appropriate sites and to limit visual impact. However it notes that this is not a blanket restriction on development. . Aviation and defence - applications will be judged on a case by case basis . Broadcasting installations - applications will be judged on a case by case basis.
3. Remaining areas of no significant constraint - the broad areas of search at the regional level. It is recognised that within these areas of search sites may be further constraints such as landscape capacity and cumulative impact, other natural heritage
East Dunbartonshire Council Local Development Plan 2013 MIR Background Report 5: Making the Most of Our Environment
interests, project viability, including wind speed, site access, ground suitability and other environmental factors; and grid capacity and that these are more appropriately dealt with at local authority level.
4. Broad Areas of Search – there are none in East Dunbartonshire. The SDP does not identify any wind energy broad area of search in East Dunbartonshire. In their refinement of this strategy, local authorities are required, among other things, to distinguish those areas outwith the broad areas of search which require significant protection from those with potential constraints.
East Dunbartonshire, Local Plan 2
The following local policies apply. There is no supplementary planning guidance on the subject.
DQ8 – Renewable Energy Developments The Council will generally support proposals for all types of renewable energy developments except: a) where there would be an adverse impact on historic and natural environment resources defined in this Plan b) where there would be an adverse impact on the landscape quality of the Green Belt, Campsie Fells and Kilpatrick Hills Regional Scenic Area c) where there would be an adverse impact on local amenity through traffic, noise and visual impact d) wind farm development in the Campsie Fells and Kilpatrick Hills Regional Scenic Area
DQ13 - Safeguard Consultation Zones and Pipeline Consultation Corridors Development Proposals within the safeguard consultation zones and Pipeline Consultation Corridors identified in Appendix 5 will be determined in consultation with the Heath and Safety Executive and the facilities operators/ owners.
Within the Airport Safeguarding Zone (see Appendix 5) around Glasgow Airport, development which adversely affects the operation, integrity or safety of the airport will not normally be permitted.
GB2K – Telecommunications and Renewable Energy Certain telecommunications and renewable energy proposals may be considered appropriate for green belt locations, subject to compliance with relevant development management design guidance and where there is no alternative location out with the green belt.
Local Development Plan
The Local Development Plan will need to set out a spatial framework for wind energy developments, in line with Draft SPP, and include a policy map. The current policy will also need to be revised to reflect all the planning considerations for developments set out in the Draft SPP, in particular cumulative impact. The spatial framework will consider the following categories which are explained further below: . Areas where wind farms will not be acceptable - there are none in this area, as they only apply to National Scenic Areas or National Parks.
East Dunbartonshire Council Local Development Plan 2013 MIR Background Report 5: Making the Most of Our Environment
. Areas of significant protection – there are areas which fall into this category in East Dunbartonshire . Areas where planning constraints are less significant, where opportunities for wind farm development can be realised through good design or mitigation – there are areas which fall into this category in East Dunbartonshire . Areas where wind farm proposals are likely to be supported subject to detailed consideration against identified policy criteria – due to the planning considerations in the area there is not likely to be an area in this category in East Dunbartonshire.
Areas of significant protection The following planning considerations in East Dunbartonshire require significant protection: . Roman Frontiers World Heritage Site (Antonine Wall) and its buffer zone protected by Local Plan 2 Policies HE1A & HE1B . SSSIs - because of their national nature conservation interest. There are six in East Dunbartonshire, protected by Local Plan 2 Policy NE1A. . Scheduled Ancient Monuments, in particular the extensive Forth and Clyde canal, protected by Local Plan 2 Policy HE4. . Conservation Areas out with settlements at Baldernock, Bardowie, Cadder and Milngavie Reservoirs, protected by Local Plan 2 Policy HE3A . Community separation of up to 2.5km between wind farms and the edge of towns, cities and villages, to reduce visual impact. This separation distance is a guide not a rule and decisions on individual developments should take into account specific local circumstances and geography. This applies to most of the lowland part of East Dunbartonshire. . Civil aviation consultation zones, this includes the one for Glasgow Airport, to the west of Bearsden and Milngavie . Flood risk areas, with an annual probability of flooding greater than 0.5%, including adjacent to the Allander Water, Glazert Water, Luggie Water and River Kelvin. . High quality unaltered peat, such as Lenzie Moss. . Areas where cumulative impact limits further development. There are no planning permissions for wind farms in East Dunbartonshire. However development in neighbouring areas could have a cumulative impact on landscape character in East Dunbartonshire. Cumulative impacts occur when two or more wind turbines are visible either in combination, in succession or sequentially. Where proposals would result in two or more wind turbine developments within close proximity (around 15km or less), their cumulative impact requires to be fully evaluated. Wind energy developments currently existing or with planning permission adjacent to this area include: single turbines in North Lanarkshire, wind farms north of the Carron Reservoir, Stirling and Whitelee Wind Farm in East Renfrewshire. Cumulative impact is likely to change through time and will need to be reconsidered for every application that takes place.
Areas where planning constraints are less significant, where opportunities for wind farm development can be realised through good design or mitigation There are four key planning considerations of this type in East Dunbartonshire: Local Nature Reserves, Local Nature Conservation designations, Local Landscape Areas and Areas with High or Medium Sensitivity in terms of Landscape Capacity. A background report providing more detail on the landscape capacity of the East Dunbartonshire for
East Dunbartonshire Council Local Development Plan 2013 MIR Background Report 5: Making the Most of Our Environment wind energy development should form part of the preparation for the Local Development Plan, Proposed Plan.
Local Nature Conservation Designations The three Local Nature Reserves and sixty six Local Nature Conservation Sites are safeguarded by Local Plan 2 Policies NE1B and NE1C.
Local Landscape Areas The Regional Scenic Areas (RSA) will be identified as Local Landscape Areas in the Local Development Plan, Proposed Plan. The approach to considering the capacity of the landscape character types in the RSA, outlined below, is consistent with adjacent North Lanarkshire.
The Kilpatrick Hills RSA in the West Dunbartonshire Council area extends into East Dunbartonshire and is designated in both areas. The Campsie Fells RSA is connected to the north to the Campsies which is part of a Local Landscape Area, in Stirling Council area, and in the east to the Kilsyth Hills RSA, in North Lanarkshire. The Kilpatrick Hills and Campsies are also part of the rugged moorland hills landscape character type.
The rugged moorland hills landscape character type has high sensitivity to wind energy developments due to its landscape capacity. It is visually prominent in the Clyde Valley area, form part of the setting of Glasgow and its surrounding towns, are of high scenic quality and development in them could have a potential cumulative impact with other existing and consented wind energy developments visible nearby.
Areas with High or Medium Sensitivity in terms of Landscape Capacity The following consideration of the landscape capacity for wind farms in East Dunbartonshire is consistent to the one applied by North Lanarkshire Council, which shares three of the four landscape character types in this area. The lowland areas of East Dunbartonshire are made up of three distinct landscape character types: Broad Valley Lowland, Rolling Farmland and Drumlin Foothills which have attractive qualities and high or medium landscape sensitivity.
Broad Valley Lowland includes the Kelvin Valley which extends into North Lanarkshire and Glasgow (small area south east of Bearsden) and forms an important communication corridor. This low lying area is considered to have a medium to high scenic quality, whilst possessing features of high landscape value.
Rolling Farmland is around Kirkintilloch and extends into Glasgow (small area west of Bishopbriggs) and North Lanarkshire (at Cumbernauld). This has attractive qualities and high sensitivity as it forms a countryside setting for Kirkintilloch and Lenzie and is highly visible from the main line railway and M80.
Drumlin Foothills, in the Milngavie to Torrance area, also extends into West Dunbartonshire (small area west of Milngavie). This is a prominent area of landscape that forms a low range of hills in front of the RSA of the Campsies and part of the setting of settlements, in particular Kirkintilloch, Torrance, Balmore and Milngavie. The local landscape importance of this area has been recognised by the designation of most of this area as a Special Landscape Area in a Planning Guidance Note.
East Dunbartonshire Council Local Development Plan 2013 MIR Background Report 5: Making the Most of Our Environment
Other Sources of Information
Renewable UK advise that wind turbines start operating at 4 to 5 m/s and reach maximum power at 15 m/s. Annual mean wind speed data, at 25 metres above ground level, in East Dunbartonshire includes the following approximate wind speeds: 7 to greater than 10 metres per second (m/s) in the Campsies and Kilpatrick Hills and 5 to 7 m/s in the Green Belt (see ETSU for DTI 1999). These approximations were applied at one kilometre grid square resolution and take no account of local/ small scale variables. This data can only be used as a guide and should be refined by on site wind speed measurements. Other sources of information from public and private bodies are identified in Appendix 2.
Appendix 1 – The Range of Turbines Identified in the Supplementary Planning Guidance of Adjacent Planning Authorities
South Lanarkshire Council’s Supplementary Planning Guidance for renewable energy categorises proposals by number of turbines and height. . Single/ small wind turbine applications: up to 3 turbines and below 70 metres in height (base to blade tip). This is a notional threshold between domestic/ community and commercial scale operations. . Wind turbine developments: Between 1 and 3 turbines and 70 metres in height (base to blade tip) or above . Small wind farm applications: Between 4 and 6 turbines or 70 metres in height (base to blade tip) or above . Medium wind farm applications: Between 7 and 15 turbines or less than 50MW . Large wind farm applications: More than 15 turbines or more than 50MW.
North Lanarkshire Council’s Supplementary Planning Guidance for wind turbine developments categorises wind turbine heights as follows: The categories of wind farm development scenarios are: . High - Large Extent (18MW+) 6 or more turbines taller than 100m . High - Small Extent (6-15MW) 2-5 turbines taller than 100m . High - Single (3MW) 1 turbine taller than 100m . Medium - Large Extent (12MW+) 6 or more turbines, 40-100m high . Medium – Small Extent (4-10MW) 2-5 turbines, 40-100m high . Medium – Single (2MW) 1 turbine, 40-100m high . Low - Large Extent (6 MW+) 6 or more turbines less than 40m . Low - Small Extent (2-5MW) 2-5 turbines less than 40m . Low - Single (1MW) 1 turbine less than 40m high
Stirling Council, Supplementary Planning Guidance – Policy & Guidance for wind turbines identifies the following size ranges of turbines: . Micro (see General Permitted Development Order Review) . Small = up to 25m, medium = 25 to 50m, . Medium to large = 50 to 80, large = 80 to 110m, . Very large = greater than 110m.
East Dunbartonshire Council Local Development Plan 2013 MIR Background Report 5: Making the Most of Our Environment
Appendix 2: Other Sources of Information
BWEA, UK Wind Speed: Database http://www.bwea.com/noabl/index.html Glasgow & Clyde Valley Strategic Development Plan 2012 NATS (en-route) plc (NERL), pre-planning consultancy service: http://www.nats.co.uk/environment/windfarms Noble Environmental Power/ Noble, Wind Maps. North Lanarkshire Council, Supplementary Planning Guidance: http://www.northlanarkshire.gov.uk/CHttpHandler.ashx?id=7542&p=0 Scottish Government, Draft Scottish Planning Policy 2013 Scottish Government, Specific Advice Sheet for Onshore Wind Turbines: http://www.scotland.gov.uk/Topics/Built-Environment/planning/National-Planning- Policy/themes/renewables/Onshore Scottish Government, Process for preparing spatial frameworks for wind farms: http://www.scotland.gov.uk/Resource/0039/00399098.pdf Scottish Government, Carbon Savings from Wind Farms on Scottish Peatland – A New Approach, 2008: http://www.scotland.gov.uk Scottish Government, Scottish Planning Circular 2/2003: Safeguarding of Aerodromes, Technical Sites and Military Explosives Storage Areas Scottish Government, Renewables Action Plans: http://www.scotland.gov.uk/Topics/Built-Environment/planning/ National-Planning-Policy/themes/renewables Scottish Natural Heritage Guidance on Siting and Designing Windfarms: www.snh.org.uk/pdfs/strategy/renewables/Guidance_Siting_Designing_...windfarms.pd f Scottish Natural Heritage, Onshore Wind Farms in Scotland, August 2012: http://www.snh.gov.uk/docs/A763435.pdf Scottish Power, Electricity Transmission Network in Central and Southern Scotland: http://www.spenergynetworks.co.uk/connecting_to_our_network/ Scottish Renewables - Information on the demand for and technologies for Onshore Wind: http://www.scottishrenewables.com/technologies/onshore-wind/ SEPA Planning Advice Note 4 on Windfarm Developments: http://www.sepa.org.uk/planning.aspx#Guidance_ Notes South Lanarkshire Council, Supplementary Planning Guidance: https://www.southlanarkshire.gov.uk/downloads/file/7619/wind_energy_supplementary_g uidance_may_2013 Stirling Council, Supplementary Planning Guidance:http://www.stirling.gov.uk/services/business-and-trade/planning-and- building-standards/local-and-statutory-development-plans/supplementary-planning- guidance/wind-farms
East Dunbartonshire Council Local Development Plan 2013 MIR Background Report 5: Making the Most of Our Environment
Annex 1: Glasgow and the Clyde Valley Green Network Partnership, East Dunbartonshire Green Network Opportunities Mapping
East Dunbartonshire Green Network Opportunities Mapping
gcv green network Contents Page
1 Summary ...... 1
2 Introduction ...... 6
2.1 What is the Green Network? 7 2.2 What Comprises the Green Network? 7 2.3 Policy Context and Rationale 9 2.4 The Role of Planning in Delivery 12 2.5 Key Principles for Planning the Green Network 12
3 Methodology ...... 14
3.1 Approach 15 3.2 Analysis Outputs 18
4 Interpretation of Analysis ...... 20
4.1 Overview 21
5 Analysis of Individual Datasets ...... 30
5.1 EDC Wide Access Priorities 33 5.2 MIR Settlement Clusters Access Priorities 34
6 Conclusions ...... 36
6.1 East Dunbartonshire Wide Green Network Opportunities 37 6.2 MIR Settlement Clusters Green Network Opportunities 38 6.3 East Dunbartonshire Green Network Expansion Priorities 40 6.4 Future Applications of Outputs 40
7 Appendices ...... 44
www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk
1 Summary
The Central Scotland Green Network is a National Development as identified in National Planning Framework 2 and as such its delivery must be considered and planned for at regional and local authority levels when producing planning policy and in development management decision making.
The GCV Green Network Partnership developed a GIS based approach to identify strategic regional opportunities for delivery of the Green Network in the Glasgow and Clyde Valley (GCV) Strategic Development Plan. The analysis uses a range of Green Network related datasets to identify strategic locations where the planning process and the targeting of resources can deliver multiple Green Network benefits.
The approach was recognised by East Dunbartonshire Council as having the potential to identify Green Network Opportunities at the local authority and settlement scales providing data which could inform the production of the their Main Issues Report (MIR) and subsequent Local Development Plan (LDP). To this end the methodology and the datasets used were refined and adapted to reflect East Dunbartonshire’s particular circumstances.
Four sets of outputs were produced to cover a range of potential scenarios.These were:
1 East Dunbartonshire wide analysis using all known development opportunities identified in Local Plan 2;
2 Outputs for each of the four MIR settlement clusters using all known development opportunities identified in Local Plan 2;
3 East Dunbartonshire wide analysis using development sites identified through the MIR consultation process; and
4 Outputs for each of the four MIR settlement clusters using development sites identified through the MIR consultation process.
Note: A more detailed rationale for developing four separate outputs is given at the end of the Summary.
Each iteration of the analysis identified geographical locations which represent an opportunity to deliver multiple Green Network benefits through the targeting of the planning process or resources. These were:
1 East Dunbartonshire wide - all known development
1 North Baljaffrey/Mains Plantation 2 The Allander/Auchenhowie Road 3 Glazert Water, Lennoxtown 4 High Park/Balgrochan Marsh 5 Redmoss Grasslands 6 Galzert Water, Broomhill 7 Southbank/Park Burn 8 Twechar 9 Woodilee 10 Wester Cleddans www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 1 Green Network Opportunities Mapping
2 Main Issues Report Settlement Clusters – All known development (local plan 2)
i Bearsden and Milngavie
1 Kilmardinny 2 Academy Gardens site 3 Pendicle Road Area 4 Canniesburn 5 Switchback
ii Bishopbriggs, Balmore, Bardowie and Torrance
1 Westerhill 2 Woodhill Park 3 Auchinairn Road 4 Wester Cleddans
iii Kirkintilloch, Lenzie and Twechar
1 North Hillhead 2 Broomhill 3 Park Burn/The Greens 4 Woodilee 5 Shirva Glen 6 Gartshore Park
iv Lennoxtown, Clachan of Campsie, Haughhead and Milton of Campsie
1 Balgrochan 2 Station Road/Glazert 3 Redhills
3 East Dunbartonshire wide – pre-MIR development sites
1 North Baljaffrey/Mains Plantation 2 Glazert Water, Lennoxtown 3 High Park/Balgrochan Marsh 4 Redmoss Grasslands 5 Galzert Water, Broomhill 6 Twechar 7 Woodilee, Kirkintilloch
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4 Main Issues Report Settlement Clusters – pre-MIR development sites
i Bearsden and Milngavie
1 Craigton/Tambowie 2 Mains 3 Pendicle Road Area 4 Drymen Road Corridor 5 Switchback 6 Kessington/Templehill Wood
ii Bishopbriggs, Balmore, Bardowie and Torrance
1 Bishopbriggs North/Cadder 2 Jellyhill 3 Bishopbriggs Town Centre 4 Woodhill 5 Huntershill 6 Auchinairn Road Corridor 7 Wester Cleddans
iii Kirkintilloch, Lenzie and Twechar
1 Shirva Glen 2 Gartshore Park 3 Cleddans 4 Kirkintilloch Gateway/Woodilee Road 5 Crosshill/Boghead Road
iv Lennoxtown, Clachan of Campsie, Haughhead and Milton of Campsie
1 Balgrochan 2 Station Road/Glazert 3 Redhills
This following report describes in detail the approach applied and interprets the specific opportunities associated with the geographical locations listed. A series of recommendations are also made which can be summarised as:
The Report should be used to:
• Develop robust and defensible Green Network policies for the Local Development Plan
• Target limited resources and planning gain effectively
• Inform masterplanning and development management decisions
• Develop Green Network Strategies for opportunity areas identified through analysis
www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 3 Green Network Opportunities Mapping
• Inform Strategies which support the Local Development Plan e.g. Open Space, Biodiversity and Access Strategies
• Set Single Outcome Agreement Targets and measures
Note: The purpose of the Main Issues Report is to generate options and not to act as a draft plan. As a result, new developments sites are not certain to be carried forward to the proposed plan at this stage. Part of the Green Network analysis relies on assessing development or regeneration opportunities as a criterion for delivering any identifies opportunities.
For that reason, the analysis was run twice. Firstly, all known development opportunities (i.e. those currently identified in LP2) were used to assess existing green network opportunities. The analysis was then run again, this time using all proposed development sites submitted during the call for sites. This allowed the Council to identify green network opportunities to include in the Main Issues Report for a variety of options depending on if any new development options were included as an option.
The structure of the Main Issues Report looks at the area wide issues for East Dunbartonshire and then breaks these issues down to assess the spatial implications for individual communities. Green Network opportunities were therefore identified at a Council-wide scale and then at a local level in order to identifying priority sites for each level. The results do contain some differences, largely due to the habitat and access layers. In the Council-wide analysis the top circa 30% of priorities were used for both the habitat and access datasets i.e. the 30% highest priorities across the whole of the council area. When the datasets were divided into the four settlement clusters the top circa 30% of priorities were recalculated for each of the areas and, although there is some correlation with the Council-wide priorities, the second analysis identified local priorities.
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www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 5 introduction
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2 Introduction
2.1 What is the Green Network?
The Green Network is a large scale and ambitious initiative that will, through planned and co-ordinated local action which delivers a strategic vision, transform Central Scotland by improving local communities, promoting healthier lifestyles, connecting and enhancing natural habitats, transforming perceptions and by attracting and retaining investment in the area.
The Green Network will deliver a range of outcomes including:
Enterprise Development
The economy will benefit from the Green Network because it provides:
• attractive locations in which existing businesses will wish to remain as they develop and grow • vibrant communities that will attract new business investment, and encourage staff recruitment and retention • new opportunities for innovative enterprises to help manage the Green Network
Health Improvement
People will benefit from the Green Network because it will provide:
• attractive locations in which to exercise or relax • safe spaces that encourage well-being and community spirit • cleaner living environments of which local people can be proud
Stronger Communities
Communities will benefit from the Green Network because it will:
• provide well-designed, sustainable places in which to live • empower local communities to take ownership and help create the safe, attractive places that they want • provide spaces that people can be proud of and which will help develop a community spirit
Biodiversity and the Environment
People, wildlife and environment will benefit from the Green Network because it:
• provides robust diverse habitats, linking across the metropolitan area • reduces human impact on the environment • reduces the impact of climate change on the urban population
2.2 What Comprises the Green Network?
The Green Network is a network of high quality connected green and open space which delivers a range of multiple benefits as described above and is designed and maintained to deliver these benefits now and into the future. www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 7 Green Network Opportunities Mapping
The form, size and function of its individual elements will vary significantly, however, the combination of these individual elements is what will create the Network.
In thinking about the development of the Green Network, it is helpful to distinguish between:
Green Network Cores/Hubs
– large areas of existing or new greenspace which already deliver a wide range of Green Network benefits. The aim should be to protect and expand these areas, to create new cores/hubs, create visual connections and, critically, to develop corridors to link them;
Green Network Corridors and Links
– continuous corridors of greenspace along rivers, disused railways, paths and cycleways and existing railways and roads which serve to connect Green Network Cores/Hubs. Many of these corridors are incomplete, or provide a limited number of functions, so a key aim is to increase the number, continuity, visual interaction and functionality of these corridors;
Green Network Stepping Stones
– it may not always be necessary or appropriate to create a continuous corridor of greenspace. Many plant and animal species, for example, are able to move short distances between areas of habitat. Historically suburbs had regular public and private squares set amongst densely developed terraces. The development of Green Network Stepping Stones can provide incomplete corridors linking larger areas of greenspace. This could include the planting of street trees, improved roadside verges or garden improvement.
Isolated Greenspaces
- it is likely that there will always be some isolated greenspaces which are difficult to connect to the wider Green Network. While the functions of such spaces are likely to be more limited, they still have potential to provide considerable benefits to local communities.
Green Network Cores/Hubs, Corridors and Links, and Stepping Stones may be comprised of any number of types of greenspace as defined in PAN 65 ‘Planning and Open Space’.
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2.3 Policy Context and Rationale
This document assists with the interpretation of national policy and guidance into local policy and guidance, and more importantly into delivery on the ground in the form of quality places in which people will want to live, work and enjoy in their free time. It therefore sets out locally derived and sensitive Green Network priorities which help to deliver the GCV Green Network - a regional component of the Central Scotland Green Network (a National Development) as set out in National Planning Framework 2.
The hierarchy of policy context within which this will be achieved is outlined below.
2.3.1 Scottish Policy Framework
Scottish Planning Policy (SPP)
Scottish Planning Policy (SPP) is the statement of the Scottish Government’s policy on nationally important land use planning matters and supersedes the previous individual documents.
Of particular relevance to the delivery of the Green Network are the sections relating to the preparation of Development Plans, Development Management and a number of the individual subject policies including:
Open Space and Physical Activity
“Green networks which provide opportunities for physical activity and access to the outdoors, and increase accessibility within settlements and to the surrounding countryside, should be promoted and safeguarded through the development plan”
Landscape and Natural Heritage
“A strategic approach to natural heritage...linked together in integrated habitat networks can make an important contribution to...biodiversity”
“Planning Authorities should seek to prevent further fragmentation and isolation... and identify opportunities to restore links”
Flooding and Drainage
“Water courses should not be culverted as part of a new development…and exiting culverts should be opened where possible. In all cases opportunities for habitat restoration or enhancement should be sought.”
National Planning Framework 2 (NPF 2)
NPF2 lays out the spatial development of Scotland to 2030. It recognises that Strategic Planning for the city regions:
“provides the opportunity to develop extensive green networks connecting our inner urban areas with their surrounding rural environments, providing a wide range of social, health and environmental benefits”.
It identifies the Central Scotland Green Network as one of fourteen “National Developments” in recognition that its delivery “offers the opportunity to effect a step change in environmental quality, woodland cover and recreational opportunities. It will make Central Scotland a more www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 9 Green Network Opportunities Mapping
attractive place to live and do business, help to absorb CO2 and promote healthier, more active lifestyles”.
NPF2 recognises that the Glasgow and Clyde Valley Green Network Partnership is delivering this National Development in the west Central Belt by “taking forward a programme of greenspace enhancement designed to promote healthier lifestyles, better environments, greater biodiversity, stronger communities and economic opportunity.”
Other National Policy and Strategy and Documents
Other national policy and strategic documents of particular relevance to the GN Programme include:
• Designing Places (Scottish Government 2008) • Designing Streets (Scottish Government 2010) • People and Places : Regeneration Policy; (Scottish Government 2006) • Closing the Opportunity Gaps; (Scottish Government 2007) • Scottish Forestry Strategy; (Forestry Commission Scotland 2006) • Scottish Biodiversity Strategy; (Scottish Government 2004) • Smart, Successful Scotland; (Scottish Government 2001) • Green Jobs Strategy. (Scottish Government 2005) • Equally Well (Scottish Government 2008) • Good Places, Better Health (Scottish Government 2008)
2.3.2 Regional Policy Framework
GCV Joint Structure Plan (2006)
The 2006 GCV Structure Plan identified the creation of a high quality Green Network as a key success factor in delivering a successful City Region.
This concept of a Green Network provides a regional framework for the development of sites of many different types, delivered and managed on the ground by many different organisations. The aim is to achieve a quantum shift in the scope, scale and quality of greenspace work taking place across the area, giving priority to:
• greenspace associated with the living and working environment of local communities; • greenspace supporting key strategic objectives, such as economic development, regeneration, biodiversity, sustainable development and environmental education; and • greenspace linked to flagship development initiatives.
2012 Strategic Development Plan and Main Issues Report
Supporting the Strategic Community Plan, the GCV Strategic Development Plan (SDP) provides an overarching planning framework for the development of infrastructure across the region. The SDP supersedes the Joint Structure Plan and is a much more focussed document representing priorities and opportunities spatially. As with the earlier Joint Structure Plan delivery of the GCV Green Network remains a cornerstone of the SDP.
The initial stage of delivering the SDP for the GCV area is the production of a Main Issues Report (MIR) which has a strategic focus and explores the key issues and spatial options at a strategic level.
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The MIR, and the subsequent adopted 2012 SDP, identifiy 14 geographical areas across the GCV where strategic opportunities exist to deliver the Green Network. These 14 “hotspots” will in due course require to be reflected in the eight respective GCV Local Development Plans.
The development of this report with East Dunbartonshire Council will apply the SDP methodology to the local authority scale in order to identify local Green Network Opportunities.
2.3.3 Local Policy Framework
In line with new planning policy, East Dunbartonshire Council (EDC) has to prepare a Local Development Plan (LDP) which reflects the priorities identified in the SDP. The starting point for this process is the gathering of evidence, preparation of the Monitoring Statement and the identification of the key issues, priorities and opportunities in a Main Issues Report.
The new style LDP will therefore require to incorporate policies which seek to ensure a robust and defensible Green Network. This document will inform the development of those policies.
www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 11 Green Network Opportunities Mapping
2.4 The Role of Planning in Delivery
The planning system is one of the most important means of realising the Green Network vision. It can ensure that development respects and enhances the Green Network. It can provide the broader spatial perspective to co-ordinate individual actions in order to create quality places in which to live and work.
It can help ensure that the right Green Network components, of the right quality, are created in the right place, and that the widest possible range of benefits result.
2.5 Key Principles for Planning the Green Network
The following principles should be considered by planners to help ensure that development of the Green Network is embedded within Glasgow and the Clyde Valley’s planning system.
1 The Green Network should be integrated into the design process for all developments
All development presents an opportunity to deliver the Green Network. The greatest Green Network benefits are likely to be achieved if Green Network design elements (i.e. surface water management, habitat networks, access networks, green and open space and stewardship) are considered as an integral part of the development design process, rather than dealt with as an afterthought once other elements of the scheme have become ‘fixed’. For major developments the opportunities to deliver the Green Network should feature in a design brief.
2 Planning for the Green Network must be based on spatial analysis
It is vital that the planning process looks beyond the boundaries of individual development sites, however large, to consider the broader spatial context; helping to create a more coordinated and joined up network. It needs to consider two dimensions of the Green Network. Firstly, how does a given site relate to the wider Green Network? Secondly, what kinds of Green Network benefits are most appropriate in that location? Aims and objectives defined in local authority Open Space Strategies should be a key consideration.
3 The quality and function of greenspace and how it will be sustained should be considered from the outset
The Green Network can deliver a range of benefits. In order to deliver the required mix of benefits and to sustain delivery there is a need to focus on ensuring that high quality open space of the right kind is delivered in the right place. Many of the problems associated with existing open spaces reflect a shortage of funding for effective management of green infrastructure. The planning process should encourage solutions which take future management and maintenance issues into account, and use planning conditions and agreements to facilitate ongoing site management.
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3 Methodology
The methodology which has been applied to the identification of Green Network Opportunities Mapping in East Dunbartonshire was originally developed in response to guidance from planners for the need to represent strategic Green Network opportunities spatially and graphically within the GCV Strategic Development Plan (SDP) Main Issues Report (MIR).
Although originally conceived to identify strategic opportunities across the Glasgow metropolitan region it was recognised from the outset that the resultant data could also be interrogated at a finer resolution for more localised opportunities.
Additionally, by replacing regionally based datasets with East Dunbartonshire specific datasets, outputs which were more relevant and useful to the local authority context could be produced. The resultant outputs will be used by East Dunbartonshire Council in two ways:
a To identify local priorities for action and what that action might be to deliver maximum and multiple benefit.
b To inform the development of LDP Green Network policies and supporting technical documentation and, if required, supplementary planning guidance.
3.1 Approach
The development of the methodology began by seeking to address the following questions:
1 What Green Network resource currently exists and where are the opportunities to improve it?
2 Where are the priority areas to expand the Green Network for?
a Biodiversity habitat networks?
b Public access to greenspace?
3 Where are the major areas of land use change and social need?
A series of datasets were identified which could provide answers to these questions both at the regional scale for the SDP and at a local scale for East Dunbartonshire.
www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 15 Green Network Opportunities Mapping
3.1.1 Datasets
The GIS based analysis considered four data layers which collectively spatially represent the GCV Green Network, key strategic locations where future land use change present opportunities for delivery and where opportunities exist for the expansion of connectivity for people and wildlife. The data layers were:
Layer 1 Existing Greenspace Provision, Path Network and Potential for Enhancement
SDP East Dunbartonshire
GCV wide greenspace dataset based on PAN ED Open Space Audit qualitative scores 65 typologies produced in 2006 (2003)
Core Path Plans from each of the eight GCV ED Core Path Plan local authorities. Datasets weighted to reflect potential for improvement.
Layer 2 Strategic Biodiversity and Access Priorities
SDP East Dunbartonshire
GCV wide Integrated Habitat Network ED wide Integrated Habitat Network priorities modelling priorities modelling
Layer 3 Strategic Access Priorities
SDP East Dunbartonshire
Strategic Outdoor Recreation and Active Travel Opportunities dataset produced by ED wide Network for People priorities Central Scotland Green Network showing modelling supply mapped against demand and need.
Level 4 Strategic Development Opportunities, Land Use Change Opportunities and Areas of Social Need
SDP East Dunbartonshire
Flagship Regeneration Areas and Community ED Development and Regeneration Sites Growth Areas across the GCV
Social Indices of Multiple Deprivation N/A
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3.1.2 Weighting of Datasets
In order to rank and prioritise the GN opportunities identified by each of the datasets, and to aid the GIS analysis, a system of weighting was applied. The weightings, and the rationale for them, as applied to the East Dunbartonshire datasets are detailed below:
Existing Greenspace and Core Paths
The Green Network is in essence a range of types of green and open space and the paths and links which connect them. In 2003 East Dunbartonshire Council undertook a comprehensive Open Space Audit which detailed the quantity and quality of its greenspace resource according to their PAN 65 typology. When combined with the local authority’s Core Path Plans, these two datasets can be taken as a good representation of the current Green Network.
However, not all greenspace presents the same opportunity for enhancement or increased functionality and therefore delivery of the Green Network. Weighting was therefore applied to the Open Space Audit qualitative scores to reflect the differing potentials as follows:
Sites scoring a qualitative score of less than 65% were taken as a high opportunity for enhancement and weighted as 3 in the analysis.
Core paths were taken as having limited ability to deliver more to the GN and therefore weighted as 1 (although it is recognised that some paths may fall short of a desirable quality).
Strategic Biodiversity Opportunities
The Integrated Habitat Network (IHN) Model uses GIS to spatially represent grassland, wetland and woodland habitats and the ability of species to move between habitats and through the adjacent landscape.
The IHN Model represents the current status of habitats and how they are ‘functionally connected’. However, it doesn’t show where best effort and resources should be targeted to increase the size and number of habitat networks.
To address this new software was developed which uses the IHN model data as a baseline but delivers outputs which identified priority areas for habitat creation.
The analysis employs a series of assessment criteria applied to a 100m grid of cells covering East Dunbartonshire. The output from this analysis was used in the final Green Network Opportunities Mapping analysis.
The top 30% of cells identified as habitat creation priorities were taken as a high opportunity and weighted as 3 in the analysis.
Strategic Access Opportunities
New work was commissioned by the GCV Green Network Partnership which would use a similar approach to habitat opportunity modelling but would instead analyse the urban environment in terms of its permeability for human accessibility from homes to greenspace and path networks.
Firstly, a Networks for People (N4P) model was developed which uses GIS to accurately map the distances people have to travel from their houses to either greenspace or a core path. Any household which is modelled as being further than 250m is considered to be disconnected from the Green Network. www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 17 Green Network Opportunities Mapping
Secondly, as for strategic habitat opportunities modelling, software applied a series of assessment criteria to 100m cell grid of cells covering East Dunbartonshire and those hexagons which consistently scored lowly in terms of adjacency and connectivity to greenspace and path networks were identified as high opportunity to improve the network.
The lowest scoring 10%, 11-20% and 21-30% of assessment cells were weighted as 3, 2 and 1 respectively in the final analysis.
Strategic Development Opportunities & Areas of Need
In consultation with East Dunbartonshire Council Officers, a series of development and regeneration sites were identified as having the potential to deliver the Green Network.
These sites were weighted as 3 in the final analysis i.e. they offered a high potential for delivery.
Note:n discussion I with East Dunbartonshire Council Officers it was agreed that the analysis should focus purely on the physical aspects of the Green Network and not include SIMD as had been done for the SDP. It was felt that analysis of the correlation between the Green Network Opportunities outputs and SIMD, as well as other health, social and economic factors, could be carried out independently at a later date for specific purposes.
3.1.3 Analysis and Outputs
GIS analysis was employed to overlay the weighted datasets detailed above and to identify geographical locations across East Dunbartonshire where there was strong correlation between them. These areas of correlation were taken as locations where opportunities exist to deliver multiple Green Network benefits through the targeting of effort and resources.
The output from the analysis was a map based spatial representation of the three highest scoring clusters of 100m cells across East Dunbartonshire.
3.2 Analysis Outputs
The outputs from the GIS analysis are:
1 Individual GIS layers showing:
a The top 10, 20 and 30% priorities for habitat creation (for combined and individual habitat types)
b The top 10, 20 and 30% priorities for access enhancement
c Weighted development/regeneration opportunities
2 Combined analysis of the above layers identifying areas of greatest opportunity to deliver multiple Green Network benefits.
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www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 19 interpretation of analysis EDC wide
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4 Interpretation of Analysis
4.1 Overview
The analysis was undertaken in four phases to:
1 Identify East Dunbartonshire wide strategic Green Network opportunities using all known development sites identified in Local Plan 2 (LP2);
2 Identify localised Green Network opportunities for each of the four settlement clusters used for the Main Issues Report using all known development sites identified in LP 2;
3 Identify East Dunbartonshire wide strategic Green Network opportunities using development sites identified through the MIR process;
4 Identify localised Green Network opportunities for each of the four settlement clusters used for the Main Issues Report development sites identified through the MIR process.
The MIR settlement clusters used in the analysis were:
I Bearsden and Milngavie II Bishopbriggs, Torrance and Balmore III Kirkintilloch, Lenzie and Twechar IV Lennoxtown, Milton of Campsie, Clachan of Campsie and Haughead
The purpose of using this combined approach was:
1 To enable strategic, authority wide policy to be developed which addresses broad thematic issues which emerge through the analysis; and
2 To support the development of local policy reflecting local issues and the effective targeting of on the ground action.
3 To build in flexibility which allows for uncertainty over inclusion of some development in the Local Development Plan.
Each of the four analysis iterations identifies locations where the opportunity exists to deliver multiple Green Network benefits through the planning process and/or the targeting of resources.
Note: The EDC wide analysis was run using the four datasets described fully in Section 3:
• Open space quality • Habitat priorities • Access priorities • Development opportunity to deliver the GN
For the localised analysis the four datasets were separated into the MIR settlement cluster boundaries and local priorities recalculated for each. The opportunities mapping analysis was then rerun for each of the four MIR settlement clusters.
Since the outputs are based on correlation of priorities between the datasets, and the priorities are different at authority wide and local levels, there may be differences in the geographical locations identified at the two scales. www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 21 Green Network Opportunities Mapping
4.1.1 EDC Wide Analysis – All Known Development (LP2) The locations identified through the analysis as being strategically important for delivery of the Green Network, based on Local Plan 2 development sites are: Figure 1 below (included as Appendix 1) shows East Dunbartonshire wide strategic Green Network opportunities using all known development sites identified in Local Plan 2 which have the 1 North Baljaffrey/Mains Plantation potential to deliver maximum, multiple benefits for the investment of effort and resources and 2 Kilmardinny, Bearsden targeting of the planning process. 3 Glazert Water, Lennoxtown 4 High Park/Balgrochan Marsh Appendix 1 - Strategic Green Network Opportunities - Local Plan 2 Sites 5 Redmoss Grasslands 6 Galzert Water, Broomhill
4 7 Southbank/Park Burn 8 Twechar 3 9 Woodlilee, Kirkintilloch 10 Wester Cleddans, Bishopbriggs 5
6 8 Additionally, single very high and high scoring cells, which do not correlate with significant clusters are distributed throughout East Dunbartonshire. These cells still represent 7 1 2 significant opportunity for delivery, particularly when adjacency of high scoring baseline layer cells is considered, and should be considered when dealing with planning 9 applications, geographically targeted resources or funding applications.
10 The specific Green Network Opportunities which relate to each of the ten identified
Legend clusters are: Very high opportunity
High opportunity Strategic Opportunities - All Development
This map is reproduced from Ordnance Survey material with the permission of Ordnance Survey on behalf of the Controller of Her Majesty's Stationery Office © Crown Copyright. Unauthorised reproduction infringes Crown copyright 00.5 1 2 3 4 and may lead to prosecution or civil proceedings. Glasgow & The Clyde Valley Strategic Development Kilometres Planning Authority 100032510 2012. O 1 North Baljaffrey/Mains Plantation, Milngavie
Figure 1 - Strategic Green Network Opportunities • Open space enhancement combined with creation or expansion of woodland, grassland, wetland habitat mosaic Note: For the 100m x 100m cells upon which the analysis is based to score in the highest • Potential for enhancement of core path opportunity band (shown in red), they must have at least maximum scoring correlation between two of the datasets plus one other score i.e. a score of 7 and above. These will be referred to as very high opportunities. For the cells to score in the high band (shown in orange) they must have 2 Kilmardinny, Bearsden a maximum scoring of 3 in at least two cells i.e. a total score of 6. • Opportunity for broadleaved woodland habitat creation associated with As the analysis focuses on the potential for people to access and use the Green Network, and is development strongly associated with delivery through development and regeneration, the identified opportunities correlate with population centres rather than rural areas. 3 Glazert Water, Lennoxtown Areas where there are clusterings of cells can be taken to be geographical locations where the opportunity exists to deliver multiple Green Network benefits. • Open space enhancement combined with creation or expansion of woodland habitat • Development opportunity to deliver creation or expansion of woodland habitat • Potential for enhancement of core path
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The locations identified through the analysis as being strategically important for delivery of the Green Network, based on Local Plan 2 development sites are:
1 North Baljaffrey/Mains Plantation 2 Kilmardinny, Bearsden 3 Glazert Water, Lennoxtown 4 High Park/Balgrochan Marsh 5 Redmoss Grasslands 6 Galzert Water, Broomhill 7 Southbank/Park Burn 8 Twechar 9 Woodlilee, Kirkintilloch 10 Wester Cleddans, Bishopbriggs
Additionally, single very high and high scoring cells, which do not correlate with significant clusters are distributed throughout East Dunbartonshire. These cells still represent significant opportunity for delivery, particularly when adjacency of high scoring baseline layer cells is considered, and should be considered when dealing with planning applications, geographically targeted resources or funding applications.
The specific Green Network Opportunities which relate to each of the ten identified clusters are:
1 North Baljaffrey/Mains Plantation, Milngavie
• Open space enhancement combined with creation or expansion of woodland, grassland, wetland habitat mosaic • Potential for enhancement of core path
2 Kilmardinny, Bearsden
• Opportunity for broadleaved woodland habitat creation associated with development
3 Glazert Water, Lennoxtown
• Open space enhancement combined with creation or expansion of woodland habitat • Development opportunity to deliver creation or expansion of woodland habitat • Potential for enhancement of core path
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4 High Park/Balgrochan Marsh
• Open space enhancement combined with creation or expansion of primarily wetland habitat with neutral grassland and some peripheral woodland • Potential for enhancement of core path
5 Redmoss Grasslands
• Open space enhancement combined with creation, expansion or management of grassland habitat and some woodland expansion
6 Galzert Water, Broomhill
• Open space enhancement combined with creation or expansion of woodland habitat with some wetland • Development opportunity to deliver creation or expansion of wetland habitat with some woodland
7 Southbank/Park Burn, Kirkintilloch
• Open space enhancement combined with creation or expansion of woodland and wetland habitat • Development opportunity to deliver open space enhancement with creation or expansion of woodland habitat • Potential for enhancement of core path
8 Twechar
• Development opportunity to deliver access enhancement and creation or expansion of wetland and woodland habitat • Open space enhancement combined with creation and expansion of wetland and woodland habitat • Potential for enhancement of core path
9 Woodilee, Kirkintilloch
• Development opportunity to deliver open space enhancement with creation or expansion of woodland and wetland habitat • Potential for enhancement of core path
10 Wester Cleddans, Bishopbriggs
• Opportunity for broadleaved woodland and wetland habitat mosaic creation • Some access to open space enhancement associated with development
Note: Where core path enhancement is suggested above it is acknowledged that no qualitative path data was included in the analysis and the potential may not exist if the core path is currently of a high quality.
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4.1.2 MIR Settlement Cluster Findings – All Known Development (LP2)
i Bearsden and Milngavie (Appendix 2)
1 Kilmardinny - Opportunity for broadleaved woodland habitat creation associated with development.
2 Academy Gardens Site - Opportunity for access to open space enhancement associated with development either through creation of new open space or improved access routes to existing space.
3 Pendicle Road Area - Opportunity for broadleaved woodland habitat creation associated with low quality open space enhancement and open space enhancement associated with development.
4 Canniesburn - Opportunity for broadleaved woodland habitat creation and possible enhancement of core path associated with development.
5 Switchback - Opportunity for broadleaved woodland habitat creation and access to open space enhancement opportunity with possible core path improvements.
ii Bishopbriggs, Balmore, Bardowie and Torrance (Appendix 3)
1 Westerhill - Opportunity for broadleaved woodland habitat creation and some access to open space enhancement associated with development.
2 Woodhill Park - Opportunity for broadleaved woodland habitat creation associated with low quality open space enhancement.
3 Auchinairn Road - Opportunity for broadleaved woodland, neutral grassland and wetland habitat mosaic creation associated with development.
4 Wester Cleddans - Opportunity for broadleaved woodland and wetland habitat mosaic creation and some access to open space enhancement associated with development
iii Kirkintilloch, Lenzie and Twechar (Appendix 4)
1 North Hillhead - Opportunity for broadleaved woodland habitat creation associated with low quality open space enhancement.
2 Broomhill - Major opportunity to deliver, through development, broadleaved woodland and wetland habitat creation and access to open space enhancement through the creation of new space. Possible opportunity for core path enhancement through development.
3 Park Burn/The Greens - Opportunity for broadleaved woodland and wetland habitat mosaic creation and associated with development. Possible opportunity for core path enhancement through development.
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4 Woodilee - Major opportunity to deliver, through development, broadleaved woodland and wetland habitat creation and access to open space enhancement through the creation of new space. Possible opportunity for core path enhancement through development.
5 Shirva Glen - Opportunity for broadleaved woodland and wetland habitat mosaic creation associated with low quality open space enhancement. Possible opportunity for core path enhancement through development.
6 Gartshore Park - Opportunity for broadleaved woodland and wetland habitat mosaic creation associated with low quality open space enhancement. Opportunity to deliver both through development at the site.
iv Lennoxtown, Clachan of Campsie, Haughhead and Milton of Campsie (Appendix 5)
1 Balgrochan - Opportunity for broadleaved woodland, neutral grassland and wetland habitat creation associated with low quality open space enhancement and development.
2 Station Road/Glazert - Opportunity for broadleaved woodland habitat creation and some access enhancement associated with low quality open space enhancement and development.
3 Redhills - Opportunity for broadleaved woodland and neutral grassland habitat creation associated with low quality open space enhancement.
4.1.3 EDC Wide Findings – Pre-MIR Development Sites
The locations identified through the analysis as being strategically important for delivery of the Green Network, based on pre-MIR development sites are:
1 North Baljaffrey/Mains Plantation 2 Glazert Water, Lennoxtown 3 High Park/Balgrochan Marsh 4 Redmoss Grasslands 5 Galzert Water, Broomhill 6 Twechar 7 Woodilee, Kirkintilloch
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The sites are shown in Figure 2 below and in Appendix 6. The specific Green Network Opportunities which relate to each of the seven identified clusters are:
Appendix 6- Strategic Green Network Opportunities - Pre-MIR Development Sites
3
2
4
6 5
1
7
Legend
Very high opportunity
High opportunity
Strategic Opportunities - Pre-MIR Housing
This map is reproduced from Ordnance Survey material with the permission of Ordnance Survey on behalf of the Controller of Her Majesty's Stationery Office © Crown Copyright. Unauthorised reproduction infringes 00.5 1 2 3 4 Crown copyright and may lead to prosecution or civil proceedings. Glasgow & The Clyde Valley Kilometres Strategic Development Planning Authority 100032510 2012. O
Figure 2 - Strategic Green Network Opportunities
1 North Baljaffrey/Mains Plantation, Milngavie
• Open space enhancement combined with creation or expansion of woodland grassland, wetland habitat mosaic • Potential for enhancement of core path
2 Glazert Water, Lennoxtown
• Open space enhancement combined with creation or expansion of woodland habitat • Development opportunity to deliver creation or expansion of woodland habitat • Potential for enhancement of core path
3 High Park/Balgrochan Marsh
• Open space enhancement combined with creation or expansion of primarily wetland habitat with neutral grassland and some peripheral woodland • Potential for enhancement of core path
4 Redmoss Grasslands
• Open space enhancement combined with creation, expansion or management of grassland habitat and some woodland expansion
www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 27 Green Network Opportunities Mapping
• Development opportunity to deliver creation or expansion of woodland habitat
5 Galzert Water, Broomhill
• Open space enhancement combined with creation or expansion of woodland habitat with some wetland • Development opportunity to deliver creation or expansion of wetland habitat with some woodland
6 Twechar
• Development opportunity to deliver access enhancement and creation or expansion of wetland and woodland habitat • Open space enhancement combined with creation and expansion of wetland and woodland habitat • Potential for enhancement of core path
7 Woodilee, Kirkintilloch
• Development opportunity to deliver open space enhancement with creation or expansion of woodland and wetland habitat • Potential for enhancement of core path
4.1.4 MIR Settlement Cluster Findings – Pre-MIR Development Sites
I Bearsden and Milngavie (Appendix 7)
1 Craigton/Tambowie - Opportunity for broadleaved woodland and wetland habitat creation and access/core path enhancement associated with Tambowie Farm, Craigton Woods and Craigton Road developments.
2 Mains - Opportunity for broadleaved woodland and neutral grassland habitat creation and access/core path enhancement associated with Mains Plantation improvements which is identified as a having the potential to deliver more in the greenspace audit.
3 Pendicle Road Area - Opportunity for broadleaved woodland habitat creation associated with low quality open space enhancement.
4 Drymen Road Corridor - Opportunity for broadleaved woodland and wetland habitat creation and access enhancement. Opportunities not associated with development or low quality open space enhancement.
5 Switchback - Opportunity for broadleaved woodland habitat creation and access to open space enhancement. Potential for core path improvements.
6 Kessington/Templehill Wood - Opportunity for broadleaved woodland habitat creation associated Templehill Wood improvements which is identified as having the potential to deliver more in the greenspace audit.
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II Bishopbriggs, Balmore, Bardowie and Torrance (Appendix 8)
1 Bishopbriggs North/Cadder - Opportunity for broadleaved woodland habitat creation and access/core path enhancement associated with North Bishopbriggs and Cadder developments.
2 Jellyhill - Opportunity for broadleaved woodland habitat creation and access/core path enhancement associated with Jellyhill development.
3 Bishopbriggs Town Centre- Opportunity for broadleaved woodland habitat creation and access enhancements. Opportunities not associated with development or low quality open space enhancement.
4 Woodhill - Opportunity for broadleaved woodland habitat creation and core path enhancement associated with improvements to low quality open space improvements.
5 Huntershill - Opportunity for broadleaved woodland and neutral grassland habitat creation associated with Huntershill development.
6 Auchinairn Road Corridor - Opportunity for broadleaved woodland and neutral grassland habitat creation. Key opportunity for access to open space enhancement as area currently shown to have poor provision. Opportunities not associated with development or low quality open space enhancement.
7 Wester Cleddans - Opportunity for broadleaved woodland and wetland habitat creation and access to open space enhancement associated with Wester Lumloch development.
III Kirkintilloch, Lenzie and Twechar (Appendix 9)
1 Shirva Glen - Opportunity for broadleaved woodland and wetland habitat creation associated with low quality open space enhancement. Potential opportunity for core path enhancement.
2 Gartshore Park - Opportunity for broadleaved woodland and wetland habitat mosaic creation associated with low quality open space enhancement.
3 Cleddans - Opportunity for broadleaved woodland habitat creation and low quality open space enhancement associated with Cleddans Playing Fields development.
4 Kirkintilloch Gateway/Woodilee Road - Opportunity for broadleaved woodland and wetland habitat creation associated with low quality open space enhancement at McGavigan’s Grassland and through development at Kirkintilloch Gateway.
5 Crosshill/Boghead Road - Opportunity for broadleaved woodland and wetland habitat creation and low quality open space enhancement associated with Crosshill Road development.
www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 29 Green Network Opportunities Mapping
IV Lennoxtown, Clachan of Campsie, Haughhead and Milton of Campsie (Appendix 10)
1 Balgrochan - Opportunity for broadleaved woodland, neutral grassland and wetland habitat creation associated with low quality open space enhancement. Potential opportunity for core path enhancement on edge of site.
2 Station Road/Glazert - Opportunity for broadleaved woodland habitat creation and access enhancement associated with low quality open space enhancement at Station Road Playing Fields and the Stewart Farms, Well Lane and Campsie View developments.
3 Redhills - Opportunity for broadleaved woodland and neutral grassland habitat creation associated with low quality open space enhancement at Redhills.
Notes:
1 Where core path enhancement is suggested above it is acknowledged that no qualitative path data was included in the analysis and the potential may not exist if the core path is currently of a high quality.
2 In addition to the cell clusters, single very high and high scoring cells, which do not correlate with significant clusters, are distributed throughout East Dunbartonshire. These cells still represent significant opportunity for delivery, particularly when adjacency of high scoring cells in the individual layers is considered. Individual cells should be considered as important opportunities for delivery of the Green Network when dealing with planning applications, geographically targeted resources or funding applications.
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www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 31 analysis of individual datasets
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5 EDC Wide Analysis of Individual Datasets
The previous analysis describes the outputs as an aggregation of the 4 baseline datasets. The constituent datasets can however provide valuable decision support when viewed individually.
In particular the Networks for People and Integrated Habitat Network datasets should be used to inform decisions on habitat creation and access enhancement at the strategic local authority, settlement scale and site scales.
Note: The Integrated Habitat Network outputs are too complex to describe fully in this report, however, the Partnership can provide assistance and further analysis on request.
The Networks for People outputs are described in more detail below.
5.1 EDC wide Access Priorities
The Networks for People datasets when viewed singly can be used to inform access enhancement decisions at local authority, settlement and site scales.
Figure 3 below shows an extract from the dataset with the full map, included as Appendix 12, showing the top 30% of access enhancement priorities for East Dunbartonshire.
Figure 3 – Access Priorities Bishopbriggs Extract
www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 33 Green Network Opportunities Mapping
The shaded hexagons represent the communities in East Dunbartonshire which are the most disconnected from the Green Network. The network analysis applied has identified the shaded hexagons as being 250m or more from an open space identified in East Dunbartonshire’s Greenspace Strategy or from a core path.
This output should be used to guide the targeting of development opportunity, planning gain or resources towards these areas to, wherever possible, connect them to the Green Network.
It is recognised that in some areas the opportunity won’t exist to create new greenspace or path networks to connect communities. In such circumstances it is important to ensure that the spaces which are closest to those communities are of a sufficient quality that people would be willing to walk or cycle further to reach them. Consideration could also be given to “greening” the on-road journey to the spaces by adopting a Designing Streets (Scottish Government 2010) approach using measures such as street trees, cycle lanes and signage and prioritising pedestrian movement. These measures would make the local environment more permeable for non-vehicular movement.
5.2 MIR Settlement Clusters Access Priorities
The Networks for People analysis was rerun for the four MIR settlement clusters to identify local access priorities. The analysis also highlighted where open spaces were failing qualitatively as assessed in the EDC Greenspace Audit (2003).
Spaces shaded green were rated at a 65% and above qualitative score and are considered of an acceptable or good standard, although opportunities to improve these spaces should still be considered. Spaces shaded red were rated below 65% and are considered below an acceptable standard and should be actively targeted for enhancement.
The outputs are shown in Appendices 11-14
Note: A revision of the Audit is planned for the summer 2012 and, when available, the new data should replace the 2003 data, however, it is likely that the majority of the spaces considered will not have changed significantly.
The orange hexagons represent the 30% of 100m cells within the considered settlements which are most disconnected from the Green Network i.e. open spaces and core paths.
a Bearsden and Milngavie (Appendix 11)
Significant areas of Milngavie and particularly Bearsden are shown in the analysis as being disconnected from the Green Network.
Generally there are three ways in which this under provision of access to open space can be addressed:
1 New space or access links can be created, perhaps as part of new development, however, given the fairly dense urban form in many settlements this often isn’t possible.
2 Access to existing spaces can be enhanced by the implementation of Designing Streets (Scottish Government, 2010) approaches making the urban environment more permeable for people and encouraging them to travel further to open spaces.
3 The nearest open spaces to disconnected areas can be enhanced to provide levels of multifunctionality and a high quality visitor experience so people are again willing to travel further to access them.
34 www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk
The vast majority of open spaces within Milngavie and Bearsden score above a 65% qualitative score. Thirteen sites within the two settlements score less than 65% and these should be a priority for enhancement through the planning process or the targeting of resources.
More detailed investigation of the site assessment sheets, held within the Greenspace Team, will reveal the particular aspects of the five key assessment themes the sites failed on and which require to be addressed.
Note: A significant feature of Milngavie and Bearsden is the high proportion of private garden ownership which, while not a substitute for high quality publically accessible open space, should be taken into consideration when allocating limited resources across EDC.
b Bishopbriggs, Balmore, Bardowie and Torrance (Appendix 12)
Significant areas of Bishopbriggs and Torrance are shown in the analysis as being disconnected from the Green Network and the principles outlines in a) above should also be applied here.
Seven spaces in Bishopbriggs and Torrance are identified as failing qualitatively and should be targeted as a priority for enhancement.
c Kirkintilloch, Lenzie and Twechar (Appendix 13)
Significant areas of central Lenzie, and some other smaller areas throughout Kirkintilloch and Twechar, are shown in the analysis as being disconnected from the Green Network and the principles outlines in a) above should also be applied here.
There are a significant number of sites identified as failing qualitatively across the area. Some of these are relatively small pocket sites and the range of functions they could offer may be limited to a very localised usage.
Woodilee is also shown as failing qualitatively but development of the site has commenced since the 2003 Audit and is likely to result in the provision of high quality open space provision and improved public access throughout the area.
The vast majority of open space within Twechar is shown as failing qualitatively and this should be seen as a priority for the village.
d Lennoxtown, Clachan of Campsie, Haughhead and Milton of Campsie (Appendix 14)
A limited area of Lennoxtown, north of the Main Street, is shown in the analysis as being disconnected from the Green Network and the principles outlines in a) above should also be applied here.
There are a significant number of large scale sites identified as failing qualitatively across the area and which have the potential to offer a range of functions through the targeting of planning gain or resources.
www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 35 conclusions
www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk
6 Conclusions
6.1 East Dunbartonshire Wide Green Network Opportunities
The GIS based analysis used to identify EDC Green Network Opportunities was originally developed for, and applied to, the Glasgow and Clyde Valley Strategic Development Plan. Subsequent modification for application to Local Development Plans has resulted in a robust and powerful decision support tool.
The East Dunbartonshire outputs demonstrate extensive scope for delivery of strategic Green Network priorities through the planning process and the targeting of resources. The analysis identified, across East Dunbartonshire, ten locations using the Local Plan 2 development dataset and seven locations using the MIR development dataset, where intervention has a high potential to deliver multiple Green Network benefits.
These EDC wide strategic opportunity areas are:
Local Plan 2 Development Data
1 North Baljaffrey/Mains Plantation 2 Kilmardinny, Bearsden 3 Glazert Water, Lennoxtown 4 High Park/Balgrochan Marsh 5 Redmoss Grasslands 6 Galzert Water, Broomhill 7 Southbank/Park Burn 8 Twechar 9 Woodilee, Kirkintilloch 10 Wester Cleddans, Bishopbriggs
Pre-MIR Development Data
1 North Baljaffrey/Mains Plantation 2 Glazert Water, Lennoxtown 3 High Park/Balgrochan Marsh 4 Redmoss Grasslands 5 Galzert Water, Broomhill 6 Twechar 7 Woodilee, Kirkintilloch
There is a large degree of correlation between the two sets of opportunities. The fact that there are ten locations in the first list and seven in the second is a function of the Local Plan 2 Development Dataset containing more sites and therefore increasing the chances of correlation with other datasets.
www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 37 Green Network Opportunities Mapping
6.2 MIR Settlement Clusters Green Network Opportunities
The strategic Green Network locations identified for the MIR settlement clusters are:
Local Plan 2 Development Data
i Bearsden and Milngavie
a Kilmardinny b Academy Gardens Site c Pendicle Road Area d Canniesburn e Switchback
ii Bishopbriggs, Balmore, Bardowie and Torrance
a Westerhill b Woodhill Park c Auchinairn Road d Wester Cleddans
iii Kirkintilloch, Lenzie and Twechar
a North Hillhead b Broomhill c Park Burn/The Greens d Woodilee e Shirva Glen f Gartshore Park
iv Lennoxtown, Clachan of Campsie, Haughhead and Milton of Campsie
a Balgrochan b Station Road/Glazert c Redhills
38 www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk
Pre-Development Data
i Bearsden and Milngavie
1 Craigton/Tambowie 2 Mains 3 Pendicle Road Area 4 Drymen Road Corridor 5 Switchback 6 Kessington/Templehill Wood
ii Bishopbriggs, Balmore, Bardowie and Torrance
1 Bishopbriggs North/Cadder 2 Jellyhill 3 Bishopbriggs Town Centre 4 Woodhill 5 Huntershill 6 Auchinairn Road Corridor 7 Wester Cleddans
iii Kirkintilloch, Lenzie and Twechar
1 Shirva Glen 2 Gartshore Park 3 Cleddans 4 Kirkintilloch Gateway/Woodilee Road 5 Crosshill/Boghead Road
iv Lennoxtown, Clachan of Campsie, Haughhead and Milton of Campsie
1 Balgrochan 2 Station Road/Glazert 3 Redhills
There is a significant degree of correlation between the two sets of locations although not as strong as in the EDC wide analysis. The specific opportunities for each of the areas are detailed in Chapter 4 of the Report and from these can be drawn a strong underlying theme of woodland, wetland and grassland habitat mosaic creation or expansion associated with open space enhancement and particularly within development and regeneration locations.
Given the strong association of the identified opportunities with development and regeneration the planning process can be utilised and robustly applied, through masterplanning and development management, to ensure the particular open space, access or habitat benefits are fully realised in proposals and seen through to delivery.
www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 39 Green Network Opportunities Mapping
Recommendation 1
Use outputs from Green Network Opportunities Mapping to inform the delivery of Green Network benefits through the planning process across East Dunbartonshire
6.3 East Dunbartonshire Green Network Expansion Priorities
Sections 5.1 and 5.2 of the Report illustrate the value of using the individual datasets to inform expansion of the Green Network in terms of habitat and access.
The Integrated Habitat Network Priorities and Networks for People Priorities outputs can be interrogated at a range of scales: local authority wide, settlement wide or on a site by site basis and should be used to inform the work of Biodiversity, Access and Greenspace Officers as well as Policy and Development Management Planners.
Findings of this report can be used to integrate the Green Network into:
1 Complimentary strategies e.g. Open Space, Access and Biodiversity Strategies,
2 Land management decisions e.g. the design and maintenance of open space,
3 Funding applications e.g. Scottish Rural Development Programme, Central Scotland Green Network Development Fund
Recommendation 2
Further analysis and application of the Integrated Habitat Network and Networks for People Priorities Outputs to inform delivery of the Green Network in East Dunbartonshire.
6.4 Future Applications of Outputs
6.4.1 Local Development Plan
The Central Scotland Green Network is a National Development identified in National Planning Framework 2 and as such its delivery has to be addressed in Local Development Plans.
This report will inform the East Dunbartonshire Main Issues Report (MIR), the first stage in the replacement of the current Local Plan, which will be a consultative document which sets out a Vision for future development across the local authority area.
The Green Network Opportunities Mapping outputs should be used to inform issues relating to the Green Network and subsequently the writing of Local Development Plan policies which define, protect, expand and enhance East Dunbartonshire’s Green Network, both as a valuable local resource and as part of the Central Scotland Green Network. 40 www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk
Recommendation 3
Use outputs From Green Network Opportunities Mapping and supporting datasets to develop robust and defensible Local Development Plan Green Network Policies.
6.4.2 Masterplanning and Development Proposals
The integration of Green Infrastructure into masterplans and development proposals should be considered at the outset of the development process. The Green Network Opportunities Mapping and the Expansion Priorities outputs can be used in the early stages to ensure delivery of the Green Network is put on a comparable footing with other developmental considerations.
It is important to emphasise that the outputs should not be viewed as constraints to the development planning process but rather decision support tools which can assist in finding an optimal solution for built and green infrastructure.
Recommendation 4
Use outputs from IHN and N4P Priorities Mapping to inform the early stages of masterplanning and development proposals
6.4.3 Development Management
When considering planning applications Development Management planners have a range of issues to consider and ensure are reflected in site proposals. GIS datasets play an important supporting role in the process often in the form of “constraints” maps. The Central Scotland Green Network is now a National Development identified in National Planning Framework 2, and therefore its delivery must also be considered when appraising planning applications.
The outputs from the Green Network Opportunities Mapping, and the individual datasets which underlie the analysis, can be used to inform Development Management decision making and the targeting of planning gain. However, unlike other planning considerations, their use can highlight opportunities for delivery of the Green Network through development and not be viewed as a constraint to development.
To facilitate use in Development Management decisions, the output layers should, as part of the Proposed Plan proposals map, be accessible to planners through East Dunbartonshire’s GIS system.
www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 41 Green Network Opportunities Mapping
Recommendation 5
Mainstream the use of Green Network Opportunities Mapping and supporting dataset outputs in Development Management to identify Green Network opportunities and the targeting of planning gain
6.4.4 Green Network Strategy Development
The Green Network Partnership has produced Green Network Strategies for a range of locations across the Glasgow and Clyde Valley area. The purpose of the Strategies is to develop a detailed understanding of spatial, social and economic interactions of a given area and to produce a strategic Green Network response which seeks to address those factors.
The East Dunbartonshire analysis identified eight strategic locations across the local authority area for delivery of the Green Network. The production of Green Network Strategies for these locations would ensure that the full range of potential benefits would be delivered. As well as addressing the delivery of Green Network infrastructure, Strategies would integrate the health, social and economic agendas into proposals.
Recommendation 6
Develop Green Network Strategies for the Opportunities Areas identified through the Green Network Opportunities Mapping
6.4.5 Targeting of Resources
Public bodies have an obligation to deliver value for money and are increasingly expected to deliver an improving service with decreasing budgets. The effective targeting of resources therefore is more important than ever.
The Green Network Opportunities Mapping outputs provide a tool to target those limited resources effectively and for maximum return on investment. The outputs can be used to inform prioritised action planning and budget allocation for delivery of Green Network priorities.
Recommendation 7
Use Green Network Opportunities Mapping and Habitat and Access Expansion Priorities outputs to inform the targeting of budgets and action on the ground
42 www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk
6.4.6 Single Outcome Agreements
Single Outcome Agreements (SOA) set out the key outcomes and targets that local authorities and their partners commit to achieving in agreement with The Scottish Government.
It can be difficult to identify appropriate targets in moving towards Outcomes and ways in which to measure whether the targets have been achieved.
The Integrated Habitat Network (IHN) Model provided detailed and measurable data on ecological connectivity, a cornerstone of sustainable management of the natural environment and mitigation against species ability to adapt to the effects of climate change. The model should be utilised to set and measure the success of meeting SOA targets on management of the natural environment.
The Networks for People (N4P) Model also has the potential to be used in setting accessibility targets for access to open space and natural environments and should be investigated more fully.
Recommendation 8
Use IHN Model to set and monitor SOA targets and investigate use of N4P model to set accessibility targets
The GCV Green Network Partnership Executive Team would welcome the opportunity to work with East Dunbartonshire Council in the future to offer advice and technical support for all of the above.
www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 43 Green Network Opportunities Mapping
8 Appendices
Appendix 1 EDC Wide Green Network Opportunities (Local Plan 2 Development)
Appendix 2 Bearsden and Milngavie Green Network Opportunities (Local Plan 2 Development)
Appendix 3 Bishopbriggs, Balmore, Bardowie and Torrance Green Network Opportunities (Local Plan 2 Development)
Appendix 4 Kirkintilloch, Lenzie and Twechar Green Network Opportunities (Local Plan 2 Development)
Appendix 5 Lennoxtown, Clachan of Campsie, Haughead and Milton of Campsie Green Network Opportunities (Local Plan 2 Development)
Appendix 6 EDC Wide Green Network Opportunities (Pre-MIR Development)
Appendix 7 Bearsden and Milngavie Green Network Opportunities (Pre-MIR Development)
Appendix 8 Bishopbriggs, Balmore, Bardowie and Torrance Green Network Opportunities (Pre-MIR Development)
Appendix 9 Kirkintilloch, Lenzie and Twechar Green Network Opportunities (Pre-MIR Development)
Appendix 10 Lennoxtown, Clachan of Campsie, Haughead and Milton of Campsie Green Network Opportunities (Pre-MIR Development)
Appendix 11 Bearsden and Milngavie Access Priorities
Appendix 12 Bishopbriggs, Balmore, Bardowie and Torrance Access Priorities
Appendix 13 Kirkintilloch, Lenzie and Twechar Access Priorities
Appendix 14 Lennoxtown, Clachan of Campsie, Haughead, Milton of Campsie Access Priorities
44 www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 8 O Kilometres 9 6 7 5 0.5 4 0 1 2 3 4 10 3
2 1 High opportunity High All Development Opportunities- Strategic Very high opportunityhigh Very Legend Appendix 1 - Local Plan 2 Sites 1 - GreenOpportunities Network Strategic Appendix This mapisreproduced from Ordnance Survey materialwith the permission of Ordnance Survey on behalf theof Controllerof Her Majesty'sStationery Office © Crown Copyright. Unauthorisedreproduction infringes Crowncopyright mayand lead to prosecution civilor proceedings. Glasgow &The ClydeStrategic Valley Development AuthorityPlanning 100032510 2012. 1 Appendix www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 45 Appendix 2 - Bearsden and Milngavie - Local Plan 2 Sites
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48 www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk Appendix 5 - Lennoxtown, M of C, Haughhead, Campsie - Local Plan 2 Sites
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5 Appendix O www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 49 50 Appendix 6
Appendix 6- Strategic Green Network Opportunities - Pre-MIR Development Sites
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Access to Open Space Bearsden et al Access to OS
. Top 30% GreenspaceAudit Acceptable/good quality Failing quality
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54 www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk 55 Appendix 12 - Bishopbriggs Torrance Balmore Bardowie - Access to OS
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56 www.gcvgreennetwork.gov.uk www.gcvgreennetwork.gov.uk Appendix 12 - Bishopbriggs Torrance Balmore Bardowie - Access to OS Appendix 13 - Kirkintilloch Lenzie Twechar - Access to OS
Legend Legend Bishopbriggs et al Access to OS Kirkintilloch et al Access to OS
. 30% . 30% Greenspace Audit Greenspace Audit Acceptable/good quality Acceptable/good quality Failing quality Failing quality
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East Dunbartonshire Green Network Opportunities Mapping Interim Report
Ally Corbett Development Officer Glasgow & Clyde Valley Green Network Partnership 0141 956 6222, www.anderson-marketing.co.uk tel. AMC by and produced designed
tel. 0141 229 7746 fax. 0141 221 4518 email. [email protected] web. www.gcvgreennetwork.gov.uk Annex 2: East Dunbartonshire Council, 2009, Review of Local Nature Conservation Sites - Ecology
East Dunbartonshire Council
Review of Local Nature Conservation Sites - Ecology
Prepared by: Checked by: Dr Jonathan Fairbairn Joanna Loughrey 7 Clairmont Gardens Glasgow G3 7LW
Tel: 0141 332 0373 Fax: 0141 332 3182 Email www.rpsgroup.com
Planning & Development Ltd
East Dunbartonshire Council November 2009
This report has been prepared within the RPS Group Quality Management System to British Standard EN ISO 9001 : 2000
STATUS: DRAFT
DATE: 3rd November 2009
PROJECT MANAGER: Dr Jonathan Fairbairn
PROJECT REVIEWER: Dr Simon Zisman
Review of Local Nature Conservation Sites - Ecology RPS Planning & Development Ltd SGP6044/JF/SZ DRAFT East Dunbartonshire Council November 2009
Contents
1. Introduction ...... 1
1.1 Background ...... 1 1.2 Scope of review ...... 1 1.3 Assessment Methodology ...... 2 1.4 Management Prescriptions ...... 4
2. Review of Local Nature Conservation Sites (LNCS) .... 5
3. Survey Results ...... 6
3.1 Barraston Grasslands NS 847 640 ...... 6 3.2 Almeel Burn NS 595 813 ...... 10 3.3 Geelong Gardens Wetlands NS 595 821 ...... 13 3.4 Easterton Woods NS 689 748 ...... 17 3.5 Fin Glen NS 603 794 ...... 22 3.6 Castle Hill Grasslands NS 525 727 ...... 25 3.7 Spouthead NS 655 779 ...... 29 3.8 Woodburn Reservoir and Glen NS 672 677 ...... 33 3.9 Meikle Reive NS 640 789 ...... 38 3.10 Birdston Meadows NS 655 758 ...... 41 3.11 Wilderness Woods NS 592 714 and NS 601 722 ...... 44
Review of Local Nature Conservation Sites - Ecology RPS Planning & Development Ltd SGP6044/JF/SZ DRAFT East Dunbartonshire Council November 2009
1. Introduction
1.1 Background
This report presents the results of a review of Local Nature Conservation Sites in East Dunbartonshire Council (EDC) area. The review was required to take into account Local Nature Conservation Sites (LNCS) and Important Wildlife Corridors (IWCs) in relation to the emerging Local Plan. In total, 31 LNCS were surveyed to Phase 1 standard in order to provide an updated record of the nature conservation value of the habitats present. Additionally, the main IWCs were surveyed to provide information on their capacity to act as viable wildlife corridors.
The list of sites was drawn up by East Dunbartonshire Council and represents sites under pressure from development in the Local Plan. Updated surveys and assessments of these areas were considered necessary in order for the Council to determine what level of protection or management should be afforded to each.
This report also provides a functionality measure for IWCs. There are no widely accepted methods for assessing functionality and grading importance of wildlife corridors. Many theories exist, although empirical evidence based methods are few. These are also generally site and species specific. IWCs are considered to be important for a wide variety of species (i.e. plants, mammals, invertebrates, reptiles and amphibians) and there is added complexity due to the interactions between corridors and island populations. A quantitative assessment of the relative merits of wildlife corridors for each species group is difficult without wider, detailed survey and therefore the measure of functionality is a qualitative one. The methods used to reach these assessments are presented in the report.
It is recommended that the Council adopt all IWCs as LNCS and afford them similar levels of protection. They should be assessed according to separate criteria, reflecting their differing value for conservation and wildlife. However, corridors represent an important resource which when lost can lead to a decline in conservation value of disparate sites greater than the magnitude of the apparent loss.
1.2 Scope of review
The report is structured as follows:
Review of LNCS and associated surveys
For each site a map of the current LNCS boundary and a phase 1 habitat map are provided. There is then a brief description of the site which includes information provided by consultees. The relative value of the site for its ecological resources is assessed and protective measures are prescribed where necessary in order to safeguard the ecological interests of the site. These measures are commensurate with the value of the resources present.
Target notes provide additional information from the phase 1 survey. Due to constraints of time, detailed species lists were not compiled. The Scottish Wildlife Trust (SWT) hold species lists for some LNCSs, but these were not made available to RPS.
Review of Local Nature Conservation Sites - Ecology 1 RPS Planning & Development Ltd SGP6044/JF/SZ FINAL East Dunbartonshire Council November 2009
1.3 Assessment Methodology
The assessment of LNCSs combined two approaches. The SNH Guidance on Establishing and Managing Local Nature Conservation Site Systems in Scotland (2000) provides brief descriptions of methods which should be reproduced for all systems throughout Scotland. This enables the establishment of a generic system for the conservation of LNCSs whilst enabling individual council areas to adopt area- specific approaches at the local level. More detailed information on the classification system adopted here includes the SNH guidance as well as an adapted SWT Assessment of Candidate Wildlife Sites. An extract of this document was kindly provided by the author, D.C. Shenton. Whilst the SWT assessment incorporates a scoring system, this is not directly transferable to some elements of the assessment.
The relative values of each site are thereby assessed for the following criteria:
Rarity of habitats This is a comparative assessment of the rarity of habitats in the local and national context. Habitats that are nationally rare are assessed to be of high conservation value. The degree to which similar habitat exists elsewhere in the local area (defined here as East Dunbartonshire Council area) define the value of the individual sites. For example, a habitat that is common throughout the local area gains a lower score than one which is rare in the local area. This is determined from the local biodiversity action plan (LBAP) as well as local knowledge of the council area. Additional information used to determine habitat rarity is the UK biodiversity action plan (UKBAP) and Scottish Biodiversity List (SBL). Whilst these lists do not determine rarity per se they recognise habitats that are either decreasing in extent or integrity in the national context, or else vulnerable due to their limited spatial extent. A scoring system is used for this element, where:
Habitat not rare = 0 Habitat rarer than average = 1 Locally rare habitat = 2 Nationally rare habitat = 3
Diversity of species This is a comparative assessment of that might be expected to occur within the site, for the types of habitats present. This is based on expert knowledge of Scottish habitats and the diversity of species they can support. This allows appropriate consideration of habitats that may be expected to be species poor, with those that would be species rich. In addition, where one habitat scores more highly than other habitats which may have depleted diversity, the higher score is used. A scoring system is used for this element, where:
Lower than expected = 0 Average = 1 Higher than expected = 2 Considerably higher than expected = 3
Rarity of species This is a measure determining species that are rare, endangered or vulnerable in the national or local context. These classifications are partly based on UKBAP, Scottish BAP and LBAPs. Whilst these lists do not determine rarity per se they recognise species that are either in decline or else of conservation concern.
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A scoring system is used for this element, where:
No rarities = 0 A few local rarities = 1 Many local rarities = 2 Nationally rare species present = 3
Habitat naturalness This is a measure of the degree of current or historic human intervention. Un- improved habitats are generally rare in Scotland, although appreciation should be given to habitats such as quarries or bings, where habitats would not exist without the intervention of human activities. A scoring system exists for this element, although the case for wholly or partially artificial habitats can be made, where they represent rare habitats of local importance.
Wholly artificial = 0 Partially natural = 1 Mainly natural = 2 Known to be natural or semi-natural = 3
Habitat extent This is a measure of the amount of habitat on the site relative to the total present in the local area. This allows the relative importance of the LNCS to be judged against similar habitats elsewhere in the locale. A scoring system is applied to this measure, taking a lead from the SNH guidance rather than the SWT criteria:
Less than 1% of this type of habitat in the local area = 0 1-4% of this type of habitat in the local area = 1 5-19% of this type or habitat in the local area = 2 >20% of this type of habitat in the local area = 3
Connectivity This is a measure of the physical links between broadly similar habitats on the site and in the surrounding area. This measure allows the assessment for potential new links to be formed through off-site management to improve the connectivity. A scoring system is proposed for this element:
Unconnected to similar habitats with no potential to create links to habitats within 1km = 0 Unconnected to similar habitat with potential to create links to habitats within 1km = 1 Limited connection to similar habitat with no potential to create additional links to unconnected habitats within 1km = 2 Limited connection to similar habitat with potential to create additional links to unconnected habitats within 1km or forming a stepping stone within an important network = 3 Extensive connection to similar habitat within 1km or forming a key part of important network = 4
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Assessment based on total score Scoring 0/22 to 5/19: The site is in very poor condition and should no longer be classified as an LNCS. Alternatively, it may represent an important open space that could be managed for the benefit of the community. Such sites may be open spaces within inner cities that can be planted for community woodlands, or as wild flower meadows. Whilst these are likely to represent wholly artificial habitats for the foreseeable future, naturalisation may eventually lead to them becoming valuable islands for wildlife in the wider landscape.
Scoring 6/19 to 8/19: If the site is: seriously vulnerable to known threats, represents significant amenity or educational value, or if the site does or potentially could link similar habitats to create a mosaic of similarly vulnerable habitat.
The site is assessed to be in poor condition but should be subject to management to increase the condition of the site.
Scoring 9/19 to 15/19: The site is assessed to be in moderate or good condition, but should be subject to ongoing management where this is required to conserve the condition or improve it.
Scoring 16/19 or higher: The site is in very good condition. Management prescriptions may be considered to conserve the condition of the site, and it should be protected from negative impacts that may occur from neighbouring land use.
1.4 Management Prescriptions
Brief recommendations are made where LNCS sites require management in order to protect or enhance their nature conservation value. Where invasive alien species were recorded, control measures are recommended. The LNCS boundaries were also assessed, and measures are put forward where these should be altered either to include neighbouring habitat or exclude low value habitats.
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2. Review of Local Nature Conservation Sites (LNCS)
In total, an assessment was made of 11 sites in the East Dunbartonshire Council area.
1) Barraston Grasslands (Score = 10) 2) Almeel Burn (Score = 15) 3) Geelong Gardens Wetlands (Score = 10) 4) Easterton Woods (Score = 11) 5) Fin Glen (Score = 13) 6) Castle Hill Grasslands (Score = 12) 7) Spouthead (Score = 15) 8) Woodburn Reservoir and Glen (Score = 14) 9) Meikle Reive (Score = 15) 10) Birdston Meadows (Score = 10) 11) Wilderness Woodlands (Score = 8)
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3. Survey Results
3.1 Barraston Grasslands NS 847 640 Surveyed by Andrew Matthews, 21st July 2009
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Barraston Grassland covers the southern flanks of the wooded hilltop by the Acre Valley road with woodland on the northern slopes. The main habitats are semi- improved neutral grassland and marshy grassland in the south with scattered scrub and semi-natural broadleaved woodland in the north. The grassland is slightly impoverished in terms of species due to improvement likely to be associated with historical grazing. There are field boundaries comprising mainly common hawthorn, Crataegus monogyna, with scattered Crataegus monogyna throughout some areas of the grassland.
The woodland is dominated by ash, Fraxinus excelsior, beech, Fagus sylvatica and sycamore, Acer pseudoplatanus, with the occasional sessile oak Quercus petraea. The low lying nature of the area means that is may be subject to seasonal flooding and provides suitable habitat for wintering bird species
The abundance of rosebay willowherb, Chamerion angustifolium, with bramble, Rubus fruticosus, in large thickets on this site makes these areas almost impenetrable to walkers and botanically very depauperate. However the flowers do provide significant resources to pollinating insects especially bees and the Rubus sp and Crataegus monogyna, fruits are a significant resource for frugivorus birds and small mammals.
The major habitats of interest are the semi-improved neutral grassland and broadleaved woodland. Inundated marshy grassland may provide occasional breeding locations for amphibians as well as rich invertebrate food resources for some bird species.
Condition Assessment and Site Score
Rarity of habitats: Whilst there are other examples of semi-improved neutral grassland in the local area, this habitat has not been subject to intensive agricultural improvement and provides a suitable habitat for restoration. It is therefore of conservation interest. Score = 2
Diversity of species: Due to the semi-improved nature of the grasslands they are, by definition, of lower diversity than unimproved grasslands. Given the national rarity of unimproved neutral grassland, the diversity of species is assessed to be average. Score = 1
Rarity of species: Although no locally rare species were recorded, it is likely that the site supports a wide range of breeding birds and foraging bat species. Some mature trees within the woodland may support roosting bats, although no bat survey was completed at the site. Score = 0
Habitat naturalness: Barraston Grasslands represent abandoned agricultural land, demarcated by hedgerows and fencing. The woodland in the north of the site is semi-natural. Score = 1
Habitat extent: Barraston Grasslands is likely to represent more than 5% of the neutral grassland in the local area. Score = 3
Habitat connectivity: The site is not linked to other similar habitats, although the LNCS Torrance marsh supports seasonally flooded grassland. Score = 3
The LNCS is assessed to score 10.
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Management Prescriptions
Several foot paths in the north of the site clearly seen in aerial photos are now totally overgrown by Chamerion angustifolium and Rubus fruticosus. It is likely that both historical management (draining the lower field) and more recent changes (in grazing regime in the upper three fields) combine to reduce the conservation value of the site overall. Managed inundation of the lower field and early grazing of the upper three fields could improve the condition of these habitats through simultaneously reducing the dominance and continuing spread of Chamerion angustifolium. Ultimately this action would be beneficial, improving access to the site and increasing its biodiversity. This strategy may best be persued early on, in concert with spraying and cutting.
A small stand of Japanese knotweed, Fallopia japonica, should be sprayed with herbicide to prevent the spread of this invasive plant.
Target Notes Barraston Grasslands Target note number Description 1 Semi natural broadleaved woodland canopy is Fagus sylvatica dominated with Fraxinus excelsior, Acer pseudoplatanus and occasionally Quercus petraea. Ground cover under the canopy is mostly bare leaf litter with Dryopteroid ferns and Rubus fruticosus with occasional Viburnum opulus close to NVC W14. Tracks in path evidence frequent use by mountain bikes and dog walkers. 2 (NS 84736 64053) large fire site with dumped timber shed panels & garden tools. The scorching and wilting of canopy evidence recent burning. 3 Planted Larix eurolepis and spreading Fraxinus excelsior saplings at northern access from woodland path on to Barraston grasslands. Here also are large stands of garden escapee Rubus idaeus at the back of Drum farmhouse and tall ruderal habitat community dominated by Chamerion angustifolium which is heavily overgrowing the paths. Vegetation also includes Rubus fruticosus, Urtica dioica, Cirsium arvense, Arrhenatherum elatius, Holcus mollis and Heracleum sphondylium. 4 Scrub habitat dominated by Crataegus monogyna with Acer pseudoplatanus and Fraxinus excelsior saplings present. 5 Mosaic of habitats. Semi-improved neutral grassland and tall ruderal dominated by Chamerion angustifolium. Other species include; Cynosurus cristatus, Agrostis stolonifera, Lolium perenne, Plantago lanceolata, Arrhenatherum elatius, Senecio jacobaea, Centaurea nigra, Cirsium arvense, Calluna vulgaris, Prunella vulgaris and Trifolium repens. 6 Semi improved neutral grassland in field opposite front elevation of Drum farmhouse. Vegetation is dominated by Arrhenatherum elatius var bulbosum, Deschampsia cespitosa, Holcus mollis, Senecio jacobaea, Rumex acetosella, Lotus corniculatus. 7 Northern hedge dominated by Ligustrum vulgare, Sambucus nigra, with Acer pseudoplatanus and Crataegus monogyna. Eastern hedge of Cupressus leylandii with a large solitary Populus sp at its centre. Following the line of the hedge is an area of enrichment marked by a stand of Urtica dioica. 8 Wet hollow with Valeriana officinalis, Ranunculus repens and Agrostis stolonifera. 9 Tall ruderal stands dominated by Chamerion angustifolium spreading in to the lower end of the field. 10 Gap in long Crataegus monogyna dominated hedge opening on to the largest lower field. The northern side of this hedge has a strip of enrichment. The southern side runs parallel with a ditched drain with a broader strip of marshy grassland including Filipendula ulmaria, Cirsium arvense, Urtica dioica and Ranunculus repens. 11 Semi-improved neutral grassland in lower field. Sward is a mixture of Arrhenatherum elatius var bulbosum, Deschampsia flexuosa, D. cespitosa, Dactylis glomerata, Holcus mollis, Tall ruderal, Chamerion angustifolium dominated vegetation is present in the NW corner and an isolated patch is centrally located however invasion is considerably limited in this wetter field.
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Barraston Grasslands Target note number Description The eastern and southern parts of this field are conspicuously wetter with patchy areas of marshy grassland noted as carpets of Ranunculus repens, Cirsium palustre, Juncus conglomeratus tussocks and Alopecurus geniculatus. 12 Wet margin under mature Fraxinus excelsior and Crataegus monogyna at southern site boundary. Species include Phalaris arundinacea, Calystegia sepium, Urtica dioica, Rumex acetosa. Other herbs at the margin of this field include Lysimachia vulgaris and Stachys sylvatica 13 Small solitary stand of Fallopia japonica 14 Tall ruderal community dominated by Chamerion angustifolium with Rubus fruticosus. A strimmed verge with Dactylis glomerata, Holcus lanatus and Campanula latifolia gives way to a very overgrown slope uphill of the drive access to drum farm house. Backing on to the wooded hilltop, Fraxinus excelsior, Acer pseudoplatanus, Crataegus monogyna and Betula pubescens are all regenerating and closing canopy over former grassland.
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3.2 Almeel Burn NS 595 813 Surveyed by Andrew Matthews, 12th August 2009
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Almeel Burn is situated in north west region of the Campsie Fells and can be reached on foot by following Knowehead Road, which runs over the Kirk Burn and out to Knowehead farm. Due north of the farm steadings at the rear of the adjoining field is a rough track running west hugging a contour at about 300m. This track leads to, and crosses, the Almeel Burn at its lowest run of waterfalls. The site lying immediately north of this track begins with a steep bank rising another 200m with dense tall stands of continuous bracken, Pteridium aquilinum. The site leads to a plateau on the fells dominated by a mosaic of, wet modified bog with acid grassland on drier areas. In small gullies and numerous hollows, acid/neutral flushes occur. As the slope plateaus at approximately 500m a transitional area of wet heath/acid grassland mosaic grades in to wet dwarf shrub heath which extends to the north of the site.
Almeel Burn itself begins draining from an area of basin mire. It is flanked by a steep sided narrow valley. The habitats found along the burn are quite different from those dominating the fells plateau as the immediate area is relatively sheltered from the elements and, until recently, grazed by sheep. The vegetation here consists of a neutral grassland sward with shaded wet areas in and around the burn, bare rock and exposed peat providing numerous microhabitats. On these slopes and down the course of the burn scattered individual rowan Sorbus aucuparia, and grey willow, Salix cinerea, are present, frequently growing on difficult to access ledges near to waterfalls. Extending south of the site between a reworked track and the Finglen Burn a grazed mosaic of habitat Pteridium aquilinum and semi-improved neutral grassland has been planted out with Scots pine, Pinus sylvestris, in tree tubes.
RPS have records of skylark and wheatear from the site. No signs of otter were recorded, although it is highly likely that the resident population utilise this burn for foraging.
Condition Assessment and Site Score
Rarity of habitats: The LBAP has a habitat action plan for Rivers, Burns and Marginal Habitats. Wet heath/ acid grassland represent the rarest of the habitats on the site. Upland heath is a UKBAP priority habitat, however this example is not considered to be an example of a habitat in favourable condition. Score = 2
Diversity of species: The species diversity is higher than average, due to the remnant woodland plants existing within the grassland sward along the burn. Score = 2.
Rarity of species: Skylark is a UKBAP species and is red listed species of conservation concern. Wheater is an amber listed species of conservation concern. Score = 3.
Habitat naturalness: The majority of the site is considered to be of natural origin, although the lower slopes of the burn corridor were historically wooded. Grazing is likely to have prevented the recolonisation of this woodland with lone standing trees restricted to rocky outcrops. Score = 3
Habitat extent: The habitats on the site are considered to represent less than 5% of similar habitats within the council area. Score = 1
Habitat connectivity: The main interests of the LNCS are the flowing water and wet heath/acid grassland, which are directly linked to similar habitats. Score = 4
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The Almeel Burn LNCS is assessed to score 15.
Management Prescriptions
A full set of management prescriptions should be created with the land owners, and should include re-forestation of the lower reaches of the site and the banks of the Almeel Burn. The species mix should aim to recreate the woodland likely to have existed previously, with native broadleaves forming the majority of the canopy. Grazing management should form an integral part of this plan, including sheep stocking plans and deer control.
Pteridium aquilinum control should be considered, including cut and spray where large stands of continuous Pteridium aquilinum exist.
Target Notes Almeel Burn Target Note Number Description 1 (NS 59532 81291) Two large patches of Luzula sylvatica each 15m2. Acid moorland species such as Agrostis capillaris dominate the site and incongruous woodland ground flora relicts such as the wood rush which is present elsewhere with Viola riviana and Oxalis acetosella are probably remnants of a woodland ground flora. 2 (NS 59527 81998) Wet heath/acid grassland mosaic, consisting of Molinia caerulea, Juncus effusus, Chamerion angustifolium and Calluna vulgaris. 3 (NS 59512 82142) Peat hagging with bare exposed peat. Narthecium ossifragum, Cladonia sp and moss sp. 4 (NS 59592 81794) Vegetation on east face of gorge moss and fern rich with Salix cinerea saplings colonising it. 5 (NS 59592 81588) Old Sorbus aucuparia with large corvid nest. 6 (NS 59657 81334) Sorbus aucuparia with patch of Chamerion angustifolium. 7 Almeel Burn has a rocky bottom dominated by a thick carpet of liverwort Scapania undulata. 8 (NS 59639 81304) Acid/neutral flush on hanging gully on east flank of Almeel Burn. Vegetation includes; Chrysosplenium oppositifolium moss, liverwort and fern species with Pinguicula vulgaris. 9 (NS 59653 81227) to (59650 81210) Approximately 20m of old dry stone wall running north south and retaining the bottom of the eastern slope of the Almeel Burn gully to a height of about 1-1.5m particularly rich in lichens and mosses. 10 (NS 59607 81098) to (59558 81005) Most northerly extent of Pteridium aquilinum on the western side of Almeel Burn gully. This island of Pteridium aquilinum is advanced beyond the main stand 11 (NS 84006 63806) to (59574 80930) Pteridium aquilinum on the eastern flank of Almeel Burn gully, an island of Pteridium aquilinum advanced beyond the main stand. 12 (NS 59578 80947) Point 10-20m due east of 2 large Sorbus aucuparia trees and one Salix cinerea on both sides of burn at the head of the first and largest waterfall which is covered by ferns and has many wet microhabitats. 13 (NS 59555 80670) Area extending south of site between track and river is a mosaic of Pteridium aquilinum and semi-improved acid grassland with weeds of enrichment such as Cirsium arvense and Urtica dioica. Much of this area is planted with Pinus sylvestris in tree tubes and grazed by sheep.
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3.3 Geelong Gardens Wetlands NS 595 821 Surveyed by Andrew Matthews, 2nd September 2009
The site centres on a wetland adjacent to Geelong Gardens, a residential street lying to the west of the site. Due north of Lennoxtown’s main school the wetland is
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bordered in the north by the Campsie golf course. There are no well used paths crossing the wetland and as a result it is relatively undisturbed. The vegetation of the weltand consists of marhy grassland with areas of scattered scrub and a small area of semi-natural woodland.
Gardens of several residential properties and the golf course back on to the site, and there is some evidence of garden escapes and tipping of garden waste on the periphery of the site.
Condition Assessment and Site Score
Rarity of habitats: Marshy grassland is a relatively widespread habitat in the local area, although it is often found in small extents associated with standing and running water. This habitat is therefore relatively rare in the context of the surrounding improved land (agricultural and golf course) and built up area. Score = 2.
Diversity of species: The marshy grassland areas are relatively species rich, showing no signs of impoverishment. Score = 2.
Rarity of species: European hedgehog is a priority species on the UKBAP. No other nationally or locally rare species were recorded. Score = 1.
Habitat naturalness: The habitat is mostly natural, with no signs of artificial drainage or improvement. It is likely that the area was once wooded with trees cleared to make way for rough grazing. However, the site has a recent history of little or no management. Score = 3.
Habitat extent: Geelong Gardens Wetlands represent less than 5% of the marshy grassland in the local area. Score = 1.
Habitat connectivity: The site is not directly linked to any similar habitats and none are present within 1km of the site. Score = 1
The LNCS is assessed to score 10.
Management Prescriptions
The north western fringe of the wetland is particularly prone to dumping and may require management to remove the waste. Monitoring should be maintained to ensure that the site remains rubbish-free in the longer term. Biological indicators suggest this wetland is in relatively good condition given its proximity to a busy town centre. The spread of invasive and garden plants, Fallopia japonica and conifers does pose a threat and should be checked by cutting and spraying where appropriate.
The scattered Salix cinerea dominated scrub is of interest, especially for breeding and wintering passerine birds although its extent should be monitored as it is prone to spreading and too much cover may not represent a positive trajectory to the sites overall ecological interest.
Consideration could be given to developing a plan for the maintenance of this habitat, including 3-4 yearly operations to clear channels of vegetation.
Target Notes
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Geelong Gardens Wetland Target Note Number Description 1 Expanse of marshy grassland dominated by Filipendula ulmaria, Deschampsia cespitosa and Juncus effusus growing over a carpet of mosses and Ranunculus repens. Patchy vegetation grading from very wet areas close to the stream marked by Iris pseudacorus and Valeriana officinalis; to drier areas with more meadow grasses Holcus lanatus and Phleum pretense. Other frequently encountered species are Lysimachia vulgaris, Phalaris arundinacea, Equisetum palustre, Equisetum arvense, Rumex acetosa, Rumex acetosella, Galium aparine, Angelica sylvestris, Viburnum opulus, Urtica dioica, Centaurea nigra, Alchemilla mollis, Agrostis stolonifera, Deschampsia flexuosa, Rubus fruticosus and Epilobium palustre. 2 Alnus glutinosa and Salix caprea are common in wetlands such as this and are semi natural often self-seeded or as is likely with the stand of Alnus glutinosa in the north of this wetland, planted. Salix caprea, Alnus glutinosa and Betula pubescens make up the majority of the canopy cover over the wetland however Salix cinerea, Crataegus monogyna and Sorbus aucuparia are also present as scattered scrub. Deer grazed Fraxinus excelsior seedlings and saplings are occasional and probably seeded from the large mature trees at the wetland margins. 3 (NS 59512 82142) Incongruous non natives include some hybrid poplars, four Picea alba and a Pinus sylvestris. The conifers are probably long forgotten planted out Christmas trees and they correlate with patches of acid indicators Deschampsia flexuosa and Achillea ptarmica. 4 (NS 59592 81794) Grassy hillock with owl pellets surrounded by marshy area with numerous small toads and frogs. Vegetation includes Crataegus monogyna, Cirsium palustre, Plantago lanceolata and Carex hirta. 5 (NS 59592 81588) Largest hybrid poplar with garden escapee spirea x pseudosalicifolia. 6 (NS 59624 81588) Carex ovalis, Ranunculus acris, Dactylorhiza maculata and Equisetum pratense patch. 7 (NS 59624 81572) Garden escapes Lonicera nitida, and Salix sp with probable deliberate transplantations Camellia sp and Cornus stolonifera. 8 (NS 59648 81456) Disturbed and drier area in the north west corner of wetland. Dominant grasses include Arrhenatherum elatius and Alopecurus pratense with stands of Rubus fruticosus and carpets of Potentilla anserina. The northern and western boundary hedges include Fagus sylvatica and Cupressus leylandii in the west. Sambucus nigra, Ilex aquifolium and Symphoricarpos albus in the north west corner becoming a patch of Picea sp with Acer pseudoplatanus, Sorbus aucuparia and Crataegus monogyna farther east. 9 (NS 59642 81404) Dumped area of garden waste, largely thinnings and brash with some imported invasives and exotics including Spiraea x pseudosalicifolia, Crocosmia x crocosmiiflora, Aster novi-belgii, Calystegia sepium, Phalaris arundinacea var. picta and Aegopodium podagraria. Other waste includes brick rubble, ton bags, vehicle parts and oil cans. 10 (NS 59657 81334) Northern boundary with Campsie golf course drainage ditch with stream flowing west to east between and parallel with a path and the boundary hedge. Vegetation cover comprises Arrhenatherum elatius, Filipendula ulmaria, Dryopteris filix-mas, Rumex acetosa and Urtica dioica. 11 Semi-natural broadleaved woodland at sharp right angled bend in stream with path continuing over low railway sleeper bridge. A dense stand of Alnus glutinosa stabalises the ground where the stream flows from a culvert out into the wetland. The ditched watercourse meanders and becomes more diffuse in the south of the wetland. Inundation here is frequent and ground cover consists of bare earth with Ranunculus repens and Agrostis stolonifera. 12 (NS 59639 81304) Area of concrete foundation carpeted in Pleurzsium schreberi and with more owl pellets. Path sides dominated by Dactylis glomerata and Heracleum sphondylium. 13 (NS 59653 81227) Semi-improved neutral grassland sward is dominated by Arrhenatherum elatius, Dactylis glomerata, Cynosurus cristatus, Lolium perenne, Holcus mollis, Festuca rubra and Anthoxanthum odoratum. Common herbs include Plantago lanceolata, Ranunculus acris, Centaurea nigra, Cirsium arvense, Cirsium vulgare, Hypochaeris radicata, Senecio jacobaea, Vicia sepium, Trifolium pratense, Rumex acetosa and R. acetosella. The trees surrounding the site include Fagus sylvatica, Crataegus monogyna, Acer pseudoplatanus and Crataegus monogyna. 14 (NS 59607 81098) Wet corner of amenity grassland under mature Fraxinus excelsior mostly comprising Ranunculus repens, Bellis perennis, Taraxacum officinale backing onto poured concrete drainage channel with Glyceria fluitans and Myosotis
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Geelong Gardens Wetland Target Note Number Description scorpioides. The understory includes Fallopia japonica and Calystegia sepium 15 (NS 84006 63806) Tall ruderal community dominated by Chamerion angustifolium. 16 (NS 59578 80947). Alien population of 3-4 plants of Polemonium caeruleum probably garden escapes.
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3.4 Easterton Woods NS 689 748 Surveyed by Andrew Matthews, 4th September 2009
The site consists of two separate areas of broadleaved semi natural woodland surrounded by fields of both arable and improved grassland. Other habitats include marshy grassland, scattered scrub, dry heath, tall ruderal, inundation vegetation, standing and open water.
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The site is bordered in the north by the Forth and Clyde canal and in the south by the B 8048. Access is gained to both sites from St Flanan Road.
The northernmost woodland is dominated by goat willow, Salix caprea, woodland which is a semi natural late succession community established on a steep sided bing of soft shale and coal finings. The ruins of St Flannan’s colliery buildings provide interesting habitats within the eastern leg of this woodland. This colliery was in operation after 1896 and closed prior to 19331, since when successional habitats have encroached on the bing. The bing is an artificial landscape feature consisting of a steep sided mound of coal finings. Scottish Natural Heritage regard bings as important for conservation primarily due to their unusual soils. These are typically; free draining, nutrient poor, changed in mineral content and often in an unstable and exposed heap. This is often a habitat which supports species that thrive on this unusual soil type but are largely underrepresented in the broader landscape. The woodland, now well established on the bing, is dominated by Salix caprea, it is linked to the Forth and Clyde canal, an important wildlife corridor which extends to other woodlands in the east and west. This bing, especially its unstable flanks, represents an important island of suitable habitat for pioneer species, which characterise scree and open habitats in an otherwise predominantly agricultural landscape. There are signs that the bing is well used by walkers and cyclists. Some unvegetated slopes have become unstable where rain runoff has eroded the slopes.
The surrounding improved grassland which is cattle grazed is bordered by fences and defunct Crataegus monogyna dominated hedges. Some tree lines are present comprising mature specimens that may harbour roosting bats. In the south is a low lying and wet field margin backing on to a wedge of sparse downy birch, Betula pubescens, on waterlogged peat with a ground layer of wet heath.
Easterton plantation is otherwise known as Easterton Moss and is a remnant raised bog, encroached with semi natural broadleaved woodland dominated by Betula pubescens. There is evidence of articial drainage around the slopes of the bog which have resulted in a drying effect that has allowed trees and woodland flora to colonise the higher slopes. At the southern edge of the Easterton plantation is a pond with marginal vegetation.
Condition Assessment and Site Score
Rarity of habitats: The bing provides one of the only remaining mining spoil habitat in the local area. Scottish Natural Heritage consider bings to be important features for conservation due to their mineral content. This is often a habitat which supports species that thrive on this soil type but are outcompeted in other habitats. Raised bog is a local priority habitat and Easterton Moss is one of only seven such habitat types within the local area and represents a UKBAP and LBAP priority habitat. Score = 3.
Diversity of species: Species diversity on the bing is no greater than the average that would be expected. Species diversity is lower than expected for an active moss, probably due to the encroachment of Betula pubescens resulting in shading out of large areas. Score = 1.
Rarity of species: No nationally or locally rare species were identified. The bing site is believed to provide potential for colonising species that require the mining spoil
1 http://www.dmm.org.uk/company/b1021.htm
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habitat present. The moss may once have supported round-leaved sundew, an LBAP species. However, the near total encroachment of the habitat by trees may have resulted in this species being lost from the site. Score = 0.
Habitat naturalness: The habitat of the bing was originally entirely artificial. Natural colonisation has occurred on the slopes. Much of the bog is natural habitat, although the encroachment of the Moss by trees and presence of artificial drainage has altered its naturalness. Score = 3.
Habitat extent: The LNCS represents one of a few examples of bing habitat in the local area. There are approximately 140ha of raised bog in the council area. Easterton Moss represents 3.5% of this total. Score = 2.
Habitat connectivity: The broadleaved woodland of the bing habitat is linked to nearby woodland by narrow strips of woodland bordering the Forth and Clyde canal. The raised lowland bog is not linked to any similar habitat within 1km. There is no potential for creating habitat links to similar habitats as raised bog formation is a very long-term process. Score = 2
The LNCS is assessed to score 11.
Management Prescriptions In the north the bing is an area of interest which may merit some management to limit the effects of a number of threats to its associated habitats. These include dumping, casual felling, excavation of spoil material and its removal. Priority should be given to ceasing the removal of spoil from the bing along with damage and loss of the trees stabilising it. Controlling the access along the canal and from the south by St Flannan road with bollards or gates would limit these threats.
As the majority of the disturbance seems to be associated with a trail bike circuit it could be worth monitoring the extent of this circuit and controlling its use.
A management plan should be created for the raised moss in the south. This should include prescriptive felling and removal of trees and the blocking of drainage channels. A protective buffer zone could be fenced off to exclude the moss and surrounding aquatic habitats from farming activities.
Target Notes
Easterton Woodlands Target Note Number Description 1 Broad field boundary between improved grassland grazed by cattle and an arable field of barley. The strip of vegetation consists of a mature line of Fagus sylvatica, with occasional Fraxinus excelsior, Quercus sp. and Crataegus monogyna. The ground layer is neutral grassland which is variable in character over the rise of the hill. There are wetter elements and species including Deschampsia cespitosa, Agrostis capillaries, Anthoxanthum odoratum, Festuca ovina, Juncus effusus, Succisa pratensis, Gallium saxatile, Potentilla erecta, Dryopteris filix-mas, Equisetum arvense, Vaccinium myrtillus, Chamerion angustifolium and Cantharellus cibarius. 2 Bare ground and steep slopes at the site of an excavation of soft shale and coal finings from the north of the bing. Short ephemeral vegetation is scattered, often associating with Salix caprea and Betula pubescens saplings and low scrub. This pioneer community is on unstable ground rooting in to thin soil carpeted with Pleurozium shreberii. The ground layer is species poor with Agrostis stolonifera, Tussilago farfara, Deschampsia cespitosa, Hypochaeris radicata, Ranunculus repens, Senecio jacobaea, Rubus fruticosus, Centaurea nigra, Plantago lanceolata,
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Easterton Woodlands Target Note Number Description Sagina procumbens, Tanacetum vulgare, Prunella vulgaris, Fragaria vesca, Euphrasia nemorosa, Epilobium hirsutum and Lycoperdon perlatum. 3 The area of broadleaved semi-natural woodland habitat surrounding these earthworks is undermined and eroded, appearing in parts more like scrub in stature. There is an opening to the canal tow path in the north. 4 Dense, shady woodland established on the top of the bing dominated by Salix caprea with occasional Betula pubescens, Fraxinus excelsior, Fagus sylvatica, Crataegus monogyna, Acer pseudoplatanus and Taxus sp. The ground layer is dominated by dryopteroid ferns with carpets of moss and Ranunculus repens. The eastern side of the woodland is in better condition than the west. Considerable casual felling, landscaping, burning and dumping have thinned the canopy and disturbed the ground layer in the west. At NS 68996 74850 a fire site and trails bike circuit converge. Vegetation here includes Rubus fruticosus, Urtica dioica, Sambucus nigra, Dactylis glomerata, Geum urbanum, Cerastium myosotis sp., Rubus idaeus and Lycopersicon esculentum. 5 On the lower slopes of the north western flank of the bing a small clearing (20m2 bare ground) partially dissects the western leg of woodland on lower rambling spoil heaps from that on the main bing. Fringing this clearing and associated with the nearby ruined brick buildings is short ephemeral vegetation with Cirsium arvense, Juncus conglomeratus, Urtica dioica, Holcus mollis, Phalaris arundinacea, Medicago lupulina, Senecio jacobaea, Chamerion angustifolium, Deschampsia cespitosa, Rumex obtusifolia, Hypochaeris radicata, Heracleum sphondylium, Agrostis stolonifera, Matricaria discoidea, Sonchus asper, Artemisia vulgaris, Trifolium dubium, Trifolium repens, Rubus fruticosus, Ranunculus repens, Plantago lanceolata and Centaurea nigra. Due to access from the tow path the fringes of the clearing have been used for fly tipping. As well as household waste, car parts, a cooker, a fridge and carpet are also dumped. Garden escapes probably transplanted in dumped garden waste include Crocosmia x crocosmifolia and Fuchsia magellanica. 6 Western leg of woodland is more evenly mixed in composition with Fraxinus excelsior, Betula pubescens, Salix caprea, Acer pseudoplatanus, Sambucus nigra and Crataegus monogyna forming a dense canopy and casting deep shade in hollows between the banks and heaps of spoil. The ground layer includes carpets of Ranunculus and moss with Geum urbanum, Geranium robertianum, Rubus fruticosus and Dryopteris sp. with occasional Pteridium aquilinum in the clearings. The series of low brick outbuildings running parallel to the tow path is very overgrown. The mortar hosts a calcicole fern and moss community dominated by Phylitus scolopendrium and Adiantum trichomanies. 7 Dry heath on crest of spoil heap with occasional Crataegus monogyna and Betula pubescens over Calluna vulgaris, Vaccinium myrtillus, Deschampsia flexuosa, Peltigera canina, Cladonia arbuscula and Cladonia macilenta. The unstable shale bank to the south is dominated by colonising Hypochaeris radicata. 8 Improved neutral grassland grazed by cattle. The sward includes Lolium perenne, Festulolium loliaceum, Cynosurus cristatus, Ranunculus acris, Rumex acetosa, Juncus effusus and Alopecurus geniculatus. 9 Fork in canal tow path becomes St Flannan’s road. The vegetation in the fork includes damp neutral grassland dominated by Arrhenatherum elatius, Dactylis glomerata and Cirsium arvense with some Cirsium palustre and Juncus articulatus with occasional Fraxinus excelsior seedlings. Also present are Centaurea nigra, Heracleum sphondylium, Digitalis purpurea, Scrophularia nodosa, Rhinanthus minor and Teucrium sp. Turning vehicles have rutted the path sides and the disturbed ground has Trifolium dubium and Prunella vulgaris with Agrostis stolonifera. A large stand of tall ruderal vegetation habitat dominated by Chamerion lies due west of this and snowberry is spreading in the adjacent hedgerow. 10 Defunct hedgerows and verges of St Flannan’s road include Crataegus monogyna, Rosa canina, Alopecurus pratensis, Cynosurus cristatus, Dactylis glomerata, Deschampsia cespitosa, Phleum pretense, Myrrhis odorata, Stachys officinalis, Ranunculus acris, Cirsium vulgaris, and Odontites verna. 11 Pooling standing water with large draw down zone of inundation vegetation dominated by Juncus effusus, Ranunculus repens, Polygonum aviculare and Alopecurus geniculatus. 12 Very sparse, borderline scattered scrub habitat of wizened Betula pubescens. An area of hagging peat reveals it is more than 0.5 m deep. The ground layer vegetation is wet heath/ acid grassland mosaic with Molinia coerulea, Calluna vulgaris, Vaccinium myrtillus, Deschampsia flexuosa, Potentilla erecta, Gallium
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Easterton Woodlands Target Note Number Description saxatile and occasional Eriophorum angustifolium and Erica tetralix. Sphagnum species and Cladonia lichens are also present. Fruiting fungi include Boletus edulus, Russula claroflava and Piptoporus betulinus. 13 Easterton plantation is covered in semi-natural broadleaved woodland dominated by Betula spp with occasional Sorbus aucuparia, Crataegus monogyna and some Quercus petraea. The lower slopes are very wet supporting wizened Betula spp with shallow root plates rafting on waterlogged peat. Old overgrown drainage ditches run perpendicular to the contours of the hill and cushions of Sphagnum fringed by Carex hirta and Carex strigosa prevent effective drainage in some places. The raised ground in-between is covered by Hylocomium splendens, Deschampsia flexuosa, Galium saxatile, Potentilla erecta, occasional Vaccinium myrtillus and Calluna vulgaris. As the slope increases and the ground dries, a Dryopteroid dominated vegetation develops under a higher shadier canopy. Due south of the top of the hill a north facing rock outcrop provides a microhabitat for ferns and mosses. The mature Quercus spp that crown the summit back on to a small clearing on the western flank with Ulex europaeus and Pteridium aquilinum. 14 The east of the woodland has Betula spp markedly grander in stature as they have developed sheltered from the prevailing wind in the lee of the hill. The Dryopteroid ground layer thins giving way to Brachypodium sylvaticum, Oxalis acetosella and Rubus fruticosus with tinder fungus on dead wood. 15 Landscaped field margin with south eastern part of the woodland has formed a small pond and island. Surrounded by improved grassland the ponds vegetation includes Potamogeton natans, Sparganium erectum, Typha latifolia Iris pseudacorus, Lemna minor, Juncus and Carex sp. 16 Wet field margin dominated by Juncus effusus with a poached fringe and small cluster of emergent Salix caprea scrub forming.
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3.5 Fin Glen NS 603 794 Surveyed by Frazer MacFarlane, 10th August 2009
Fin Glen is a relatively remote upland valley leading from the Campsie Fells. The Finglen Burn, a tributary of the Glazert Water flows down the steep-sided glen. In the
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lower reaches it forms a rich semi-natural broadleaved woodland remnant in a gorge consisting of mature Quercus robur, Fagus sylvatica, Fraxinus excelsior, Acer pseudoplatanus and alder, Alnus glutinosa, with understorey of Crataegus monogyna, hazel, Corylus avellana, and Sorbus aucuparia and rich ground flora of ferns, grasses and bryophytes. In the mid to upper reaches it gives way to abundant open unenclosed upland acid / wet valley grassland, tall ruderals and Pteridium aquilinum typical of several glens of the basalt Campsie Fells.
The Finglen Burn is a relatively high energy burn which flows over a steep gradient. The substrate is boulders and bedrock with several pools and falls. Otter spraints were recorded on in-stream boulders and it is likely that this forms part of an otter territory. No resting up sites were recorded, although it is considered likely that there are some present within the LNCS boundary.
A female hen harrier was recorded foraging over open ground in the north of the site.
Rarity of habitats: The Fin Glen comprises semi-natural broadleaved woodland in the lower section of the river valley, with a rich under storey. The LBAP has a habitat action plan for Rivers, Burns and Marginal Habitats. Whilst wet heath and grassland mosaic contains some areas of upland heath vegetation, it bears more in common with blanket bog, being devoid of dwarf shrub and occurring over deep peat. The habitats are therefore considered locally rare. Score = 2
Diversity of species: The diversity of plant species within the wooded habitats was higher than expected, due to the steep slopes preventing modification of this habitat. Heavy grazing of the higher reaches of the site has resulted in a grass-dominated mosaic, with fewer heath species than expected. Score = 2
Rarity of species: Hen Harrier is a nationally rare species, red listed on the UK birds of conservation concern. Otter are a priority species, listed on the UKBAP. Score = 3
Habitat naturalness: The habitats on the site are almost totally natural, although the semi-improved grassland has been modified by grazing and areas of woodland planting have been undertaken. Score = 2
Habitat extent: None of the habitats within the LNCS constitute significant amounts of similar habitat found elsewhere in the local area. Score = 0.
Habitat connectivity: The wet heath/acid grassland mosaic is linked to extensive heath habitat, whilst the river corridor and woodland extends south to the Glazert and River Kelvin corridor. Score = 4
Total Score = 13.
Management Prescriptions
A full set of management prescriptions should be created with the land owners, and should include re-forestation of the lower reaches of the site and the banks of the Fin Burn. This should be tied into the management for the Almeel Burn. The species mix should aim to recreate the woodland likely to have existed previously, with native broadleaves forming the majority of the canopy. Grazing management should form an integral part of this plan, including sheep stocking plans and deer control.
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Pteridium aquilinum control should be considered, including cut and spray where large stands of continuous Pteridium aquilinum exist.
Target Notes
Fin Glen Target Note Number Description 1 Semi-natural broadleaved woodland (NS 600 799). Remnant Native Wooded Gorge. Quercus robur, Fagus sylvatica, Fraxinus excelsior, Acer pseudoplatanus and Alnus spp with understory of Crataegus monogyna, Corylus avellana and Sorbus aucuparia and rich ground flora of ferns, grasses and bryophytes. To north, dominant banks of Pteridium aquilinum and young broadleaved sapling plantings (in aesthetically diminishing plastic tubes). 2 White Spout Waterfall (NS 599 799) Hydrological/Geological feature. Near vertical waterfall. Offering high potential scenic value. Good potential for Otters. 3 Horse Craig (NS NS 58827 80864) Upland species-rich ledge. Rock outcrop and side tributary. Semi-natural, with Fraxinus excelsior, Sorbus aucuparia, Salix alba. Understory of Heather and Vaccinium myrtillus patches and Dryopteris filix-mas by burn. 4 Marshy grassland. Juncus beds and wet grasses at burn sides as upper reaches of Fin Burn narrows and widens from steep sided valley of lower and mid sections of Glen.
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3.6 Castle Hill Grasslands NS 525 727 Surveyed by Andrew Matthews on 23rd and 24th July 2009.
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The area surveyed covers five fields on a hill due east of Bearsden. The site is delimited by the A810 to the north, Peel Glen Road to the west and a golf course and farm access road to the east. Running approximately east to west across the middle of the site are the remains of the Antonine wall and at its centre the site of a roman hill fort. Still prominent under a mature Crataegus monogyna hedge down the west flank of castle hill heading south west towards Hutchinson hill is an overgrown ditch and embankment marking the course of the ancient defensive earthworks.
The majority of the vegetation is neutral grassland bordered by Crataegus monogyna dominated hedges with long thin strips of enrichment identified by the presence of herb species. Patches of wetter communities characterised by tussocks of soft rush, Juncus effusus, are found especially on the western flanks of the hill. In the southern fields tall oat-grass, Arrhenatherum elatius var bulbosum, is dominant with patches of scattered scrub, closing on denser scrub towards the bottom of the slope. Other habitats present include broadleaved woodland.
The site is managed by Historic Scotland and Bearsden and Milngavie District Council. The Antonine Wall was designated a World Heritage Site in 2008.
There is evidence of vandalism and burning of several of the mature trees within the central mound on the site.
Rarity of habitats: Neutral grassland is a nationally rare habitat with most examples having been impoverished by agricultural improvement. Whilst this habitat is species rich, it has been subject to some improvement in the past and is therefore considered to constitue the UKBAP priority habitat Lowland Meadows. Hedgerows are a UKBAP priority habitat. Score = 3
Diversity of species: The diversity of plant species within the grassland is higher than expected for enclosed grasslands. The species rich hedgerows are relatively diverse when compared to similar habitats in the local area. Score = 2
Rarity of species: No nationally or locally rare species were recorded. Score = 0
Habitat naturalness: The habitats on the site are not natural, having been former enclosed pasture. However, the grasslands are likely to have been present at this site for a long period of time, as reflected in the high species diversity. Score = 1
Habitat extent: Castle Hill Grasslands represents relatively large extent of the neutral grassland in the council area. Score = 2
Habitat connectivity: The grasslands are connected to similar habitats in West Dunbartonshire and Glasgow City council areas. Score = 4
Total Score = 12.
Management Prescriptions
The condition of the habitats on this site raises concern. Firstly the condition of the ring of trees at castle hills summit is poor. Now mature, the amenity value of these trees in terms of their addition to the complexity of the landscape should not be underestimated. Probably originally planted as a wind break and shelter for grazing stock animals the trees continue this service for visitors taking in the view. Their position makes them particularly exposed and vulnerable. Many of the Acer pseudoplatanus are heavily set with tar spot Rhytisma acerinum and many of the
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Fagus sylvatica have parasitic growths of artist’s conk, Ganoderma applanatum. Secondly and less concerning is the almost total fungal loading of the grassland by rusts, smuts and ergots, Claviceps purpurea. This is unusual and probably due to the exposed aspect and high traffic of walkers.
Stopping further losses from the ring of 97 trees makes protection of mature trees and seedlings a priority. A longer term solution is desirable and may require tackling the immediate vandalism problem, better signposting and local community involvement. Directly reducing access to the trunks of these trees may be achieved by planting thorny scrub of gorse, Ulex europaeus, or by using large galvanised steel tree guards. Given the potential for archaeological disturbance, Historic Scotland who also care for the site should work alongside conservation groups to identify the most appropriate solution.
Future management of the grasslands could include grazing or mowing and sowing of yellow rattle, Rhinanthus minor, to break the dominance of the grass Arrhenatherum elatius. This would create a more diverse grassland community with greater biodiversity value.
Target Notes
Castle Hill Grasslands Target Note Number Description 1 (NS 52520 72721) Defunct hedge of Crataegus monogyna with occasional Sambucus nigra and larger trees; Acer pseudoplatanus. The hedge rises in height as it approaches the ring of trees at the summit of castle hill. Running parallel with the northern side of this hedge is a strip of shaded enrichment marked by Urtica dioica, Rumex acetosa, Heracleum sphondylium and Myrrhis odorata. 2 (NS 52488 72751) Semi-improved neutral grassland habitat. This is the common habitat across this site. Species composition and dominance is locally changeable but generally the sward in the northern half of the site is more species rich, with: Holcus mollis, Phleum pratense, Dactylis glomerata, Agrostis stolonifera, Cynosurus cristatus, Festuca rubra, Deschampsia cespitosa in the tall sward and Lolium perenne frequent on well trodden and rabbit grazed paths. The most common herbs include Rumex acetosa, Cirsium arvense, Centaurea nigra, Senecio jacobaea, Ranunculus acris, Trifolium repens, Trifolium pratense, Lotus corniculatus and Galium aparine. 3 (NS 52368 72651) Wet patches are frequent and too small to map. They are especially common on the western flank of castle hill. The vegetation cover is characterised by Juncus effusus, Ranunculus repens, Equisetum arvense, Dryopteris filix-mas, Cirsium palustre and often fringed by Rumex acetosa, Urtica dioica and Veronica chamaedrys. 4 (NS 52351 72625) On western flank, disturbed areas of heavier acid soil are marked out by small patches of Achillea ptarmica. Also present are scrambling patches of Rubus fruticosus and occasional Rosa canina. 5 (NS 52386 72697) Ring of mature trees at summit of castle hill dominated by Fagus sylvatica (65 trees) with Acer pseudoplatanus (25 trees) and Quercus robur and Aesculus hippocastanum (3 trees each). The fragmented canopy overtops semi- improved neutral grassland with Anthoxanthum odoratum, Deschampsia flexuosa, Cynosurus cristatus, Hypochaeris radicata, Cerastium arvense. There are 5 wind- thrown trees and 1 standing dead. 6 (NS 52398 72634) Dactylorhiza maculata, Potentilla erecta and Succisa pratensis next to mature wind-thrown Fagus sylvatica. 7 Grassland on summit enclosed by ring of trees. Species include Agrostis capillaris, Poa trivialis, Deschampsia cespitosa, Holcus mollis and Dactylis glomerata. Prominent herbs include Cirsium arvense and Rumex acetosa. 8 Crataegus monogyna scrub in south of site provides cover and food for birds and abuts on to a mixed broadleaved woodland comprising Salix cinerea, Salix caprea, Crataegus monogyna, Fraxinus excelsior, Quercus robur, Betula pubescens, Sorbus aucuparia with Lonicera sp. and Hedera helix as scramblers.
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Castle Hill Grasslands Target Note Number Description 9 Extensive vandalism of mature ring of trees approximately 70% affected. Damage includes removal of large areas of bark, carving of graffiti in trunks and laying of fires at their bases. This damage contributes to disease and weakening which increases the likelihood of wind throw. The potential threat of wind throw is twofold; firstly, disturbance or damage to the underlying archaeological interests through large root plates being overturned. Secondly, the less likely risk to the public from falling trees or boughs. Camping (evidenced by a discarded tent), littering and fires are prohibited by the Bearsden and Milngavie rules for the management and regulation of the site. However the sign outlining these is in disrepair and a considerable distance from the site. Given the difficulty policing these rules other strategies should be pursued. 10 (NS 52465 72573) Area of neutral grassland very different in species composition from that on the north facing flanks. The species poor sward is dominated by Arrhenatherum elatius var. bulbosum with Plantago lanceolata, Achillea milfolium, Angelica sylvestris, Rumex acetosa and Cirsium arvense. 11 (NS 52492 72635) Area of enrichment dominated by Urtica dioica and Rubus fruticosus. Zone of overgrazed ground from adjacent field pasture grazed by horses. Margin includes Lolium perenne, Rumex acetosa, Prunella vulgaris and Veronica chamaedrys. 12 (NS 52489 72704) Fraxinus excelsior, Acer pseudoplatanus regeneration and Silene dioica around large wind thrown Fagus sylvatica with many bracts of the fungus Ganoderma applanatum.
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3.7 Spouthead NS 655 779 Surveyed by Andrew Matthews on 15th September 2009
This extensive site follows the Spoutburn and its adjacent habitats from Cowies Glen to the steep slopes of Campsie fells. There are a wide range of habitats associated
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with the Campsie fells at the Forking Burn becoming the Spouthead Burn and finally the Waltry Burn. The habitats include native broadleaved woodland, dense scrub, scattered scrub, improved grassland, semi-improved neutral grassland, marshy grassland, acid grassland, neutral flushes, Pteridium aquilinum, and waterfall microhabitats.
The main habitats of value are those associated with the burns, including microhabitats at waterfalls. These areas are rich in bryophytes due to the high energy nature of the falls spraying the banksides with water.
Directly observed species include roe deer and buzzard. Evidence of mole, mice, shrew, owl and possibly badger was noted. Anecdotal records include tawny owl, barn owl, peregrine, sparrow hawk, kestrel, bullfinch, greenfinch, linnet and dipper (pers.com. M. Mc Kenna shields cottage).
Rarity of habitats: The Spoutburn represents a headwater, part of the UKBAP Rivers priority habitat. Score = 3
Diversity of species: The diversity of plant species within steep sided gorges and falls of the Spouthead Burn are high in diversity. The degraded woodland margins contain lower species diversity than would be expected due to the influence of grazing livestock. Score = 2
Rarity of species: Linnet and Bullfinch are UKBAP priority species with associated action plans. Score = 3
Habitat naturalness: The main habitats of interest on the site are natural, although the woodland surrounding the burn is much reduced in extent than historically would have been the case. Score = 2
Habitat extent: Spouthead represents a relatively large extent of the high energy waterfalls in the council area. Score = 2
Habitat connectivity: The burn is connected to similar habitats downstream, although the woodland cover along this habitat is discontinuous and patchy downstream of the site. Score = 3
Total Score = 15.
Management Prescriptions
The fragmented corridor of woodland, scrub and other riparian habitats associated with the watercourses on this site would benefit from management. Fencing off these areas from the adjacent pasture will prevent poaching and grazing which is detrimental to the vegetation, especially the ground layer in the woodland to the south of the site. The burn in the middle of the site, although not wooded and without marginal vegetation, has a similar problem marked by its badly eroded sides. The rutted tracks trodden by sheep have cut furrows along the crest of bank of the burn in places, which have subsided when undermined and washed away by the burn. This problem is most evident in the field by target note 12. Broadleaved native trees could be planted in a fenced enclosure to stabilise the bank using suitable species such as Salix caprea, Betula pubescens and Fraxinus excelsior. Areas of encroaching Pteridium aquilinum especially in the north of the site should be cut and sprayed to control their spread. Changing the grazing regime may also help in removing Pteridium aquilinum from the rough pasture in the north.
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Spouthead Target Note Number Description 1 Marshy grassland habitat: Juncus effusus, Juncus conglomeratus, Juncus squarrosus, Juncus articulatus, Juncus tenuis, Molinia caerulea, Deschampsia cespitosa, Carex nigra, Carex pulicaris, Carex viridula ssp oedocarpa, Potentilla erecta, Galium saxatile, Galium verum, Luzula campestris, Stachys palustris, Digitalis purpurea. Very sparse heath species Calluna vulgaris, Vaccinium myrtillus also present Festuca ovina, Anthoxanthum odoratum, Rubus fruticosus, Epilobium palustre, deer grazed Betula pubescens and Salix caprea seedlings. Closer to the burn Ulex europaeus and Equisetum fluviatile are growing. 2 Area of semi-natural broadleaved woodland with a prominent browse line. The canopy is dominated by Betula pubescens with occasional Sorbus aucuparia, Salix caprea and Crataegus monogyna. Sparse Pteridium aquilinum is present at the southern field boundary. The ground layer includes Agrostis capillaris, Holcus mollis, Poa nemoralis, Holcus lanatus tussocks of Molinia caerulea and Deschampsia cespitosa, Carex elata, Luzula campestris, Potentilla erecta and occasional Juncus effusus. 3 Improved grassland sheep grazed sward is closely cropped. Lolium perenne is the dominant grass with Trifolium repens and Ranunculus acris throughout. Wetter margins include Ranunculus repens, Juncus sp, Alopecurus geniculatus and Glyceria declinata 4 Semi-improved grassland with lower grazing pressure encouraging a taller and more mixed sward with Phleum pratense, Holcus mollis, Dactylis glomerata, Festulolium loliaceae, Lolium perenne, Ranunculus acris, Alopecurus pratensis, Ranunculus repens, Polygonum persicaria, Lotus corniculatus, Trifolium repens, Trifolium pratense, Agrostis stolonifera and Agrostis capillaris. 5 Cowies glen with semi-natural broadleaved woodland. Canopy species include Fagus sylvatica, Acer pseudoplatanus, Fraxinus excelsior, Ulmus glabra, Alnus glutinosa, Crataegus monogyna, Sorbus aucuparia, Crataegus monogyna, and coppiced Corylus avellana. The steep slopes are heavily poached on accessible very wet areas and have a ground layer which includes Ranunculus repens, Filipendula ulmaria, Chrysosplenium oppositifolium, Dryopteris filix-mas, and Geranium robertianum. 6 The ungrazed and unpoached sections of the same stretch of woodland are in better condition. The canopy is similar but with more Salix caprea. The intact ground layer includes all the species noted in target note 5 as well as Deschampsia cespitosa, Dactylis glomerata, Poa nemoralis, Viola riviniana, Ajuga reptans and Rubus fruticosus. 7 Deep gorge with damp shady waterfall habitats and neutral flushes down slopes Ranunculus repens, Chrysosplenium oppositifolium and Dryopteris dilatata present. Mosses include Mnium hornum, Conocephalum conicum, Plagiothecium undulatum and Scapania undulate. 8 Extensive reappointment of drainage replacing the mapped ditches with buried perforated pipe and gravel. 9 Extensive Pteridium aquilinum. 10 Erosion of banks exacerbated by livestock. It is likely that the course of the burn has been altered. It seems to be straitened from the meandering course mapped on Ordinance Survey. 11 Mature Fraxinus excelsior at the gates and cattle grids at the entrances to Shields Farm and Spouthead Farm. The burn passes through a large concrete culvert under the track. The improved fields due west of this have tall luxuriant swards probably mown for silage. 12 Semi-natural broad-leaved woodland with Fraxinus excelsior, Quercus robur, Prunus spinosa, Corylus avellana and Ulmus glabra, growing in a steeply sided gulley. The heavily shaded ground cover is sparse and Dryopteroid dominated. The brighter upper slopes are overgrown with Pteridium aquilinum, Rubus fruticosus and Heracleum sphondylium. The leg of scrub following the burn to the east comprises Sorbus aucuparia, Alnus glutinosa and Betula pubescens. 13 A heavily poached area at the back of the cattle shed with Juncus sp.
14 Continuous dense scrub dominated by Prunus spinosa. Running the length of the field north from Spouthead Farm this scrub follows the burn and is too dense to walk through. Other woody species include Crataegus monogyna, Sorbus aucuparia and
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Spouthead Target Note Number Description Ulex europaeus. The ground layer includes Rosa canina, Filipendula ulmaria, Oxalis acetosella, Equisetum arvense and Rubus fruticosus. The cover and fruit are important resources for passerine birds. 15 Recently ploughed field, very sparse vegetation includes; Polygonum aviculare, Myosotis arvensis, Fumaria officinalis, Capsella bursa-pastoris and Stellaria media. 16 Semi improved acid grassland. The sward is dominated by Deschampsia cespitosa, Agrostis capillaris, Deschampsia flexuosa, Molinia caerulea, Juncus squarrosus, gallium saxatile, Festuca ovina and Anthoxanthum odoratum. 17 Small patch of Luzula sylvatica and Fraxinus excelsior by waterfall. Semi-improved acid grassland is extensive across the face of the hills however very occasionally small precipitous ledges and very steep gradients have caused some areas, less accessible to sheep, to retain pockets of ericoid heath. Species include Vaccinium myrtillus, Calluna vulgaris and Thymus serpyllum.
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3.8 Woodburn Reservoir and Glen NS 672 677 Surveyed by Caroline Boffey on the 18th June 2009 and Andrew Matthews on 6th September 2009.
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Woodburn reservoir situated in the north west of the site is fed by an un-named burn rises in the Campsie fells to the north. The Woodburn burn that leaves the reservoir winds its way over the site flowing south east in to a woodland at the south east corner of the site. The habitats found include improved and semi improved neutral grassland, marshy grassland, semi-natural broad-leaved woodland, conifer plantation, scattered scrub, neutral flush and open water. The improved and semi- improved neutral grassland habitats account for much of the site and are actively managed for grazing sheep and cattle. The other habitats are largely marginal and associated with the watercourse. Running west to east from an area of marshy grassland to the woodland approximately through the middle of the site is a planted windbreak dominated by mature Quercus robur. Field boundaries are mostly dry stone walls with a few fences and defunct hedges.
Woodburn Glen is a semi-natural woodland with some plantation woodland mixes. The woodland is partially cleared in the south, with a number of private residential properties situated within the glen.
Fauna observed on site included roe deer, buzzard, kestrel, mallard, tufted duck, black-headed gull, rook, pheasant, stickleback, brown trout, toad, hare and shrew. Signs of rabbit were observed and it is likely frogs are also present. The sticklebacks in Woodburn reservoir had a population boom this summer and are very abundant. The brown trout which were transplanted as fry from the nearby Birken burn a year ago are now approximately 1-2 lbs. Further unsubstantiated records include sparrowhawk, dipper, cormorant, osprey and goldeneye duck (pers comm. J Curtis, Campsie outdoor centre).
Rarity of habitats: Whilst there are other examples of standing water habitat within the local area, eutrophic standing water is nationally scarce and this habitat is considered nationally important for wildlife. Score = 3
Diversity of species: The site is generally managed for agricultural and water protection measures, resulting in some habitats that are relatively impoverished. The fauna that has been recorded are no more diverse than would be expected in these types of habitat. Score = 1
Rarity of species: Brown trout are a priority species listed on the UKBAP. Several locally rare species have been recorded by the Campsie outdoor centre including osprey and goldeneye. Black-headed gull, kestrel, goldeneye, Osprey and tufted duck are amber listed birds of conservation concern. Score = 3
Habitat naturalness: Woodburn reservoir is a man-made feature, with ongoing management in place within the standing water and some areas of the shoreline. Although modified upstream, the Wood Burn is a natural habitat. The habitats bordering the burn are modified through clearance of trees and grazing. Score = 1
Habitat extent: Woodburn Reservoir represents less than 5% of the standing water in the local area. Score = 1
Habitat connectivity: The LNCS is not linked to other similar habitats, and there are none within 1km. However, it does form an important stepping stone within the disparate network of standing water (especially for otter and waterfowl). Score = 3
The LNCS is assessed to score 14.
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Management Prescriptions
Water quality in woodburn reservoir is good but poaching and enrichment adversely affect the quality in the burn downstream. Where possible, access to the burn by livestock should be limited.
Pteridium aquilinum stands in the woodland at the north of Woodburn Glen should be cut and sprayed to control it. Overall Pteridium aquilinum is rare and anecdotally the current grazing regime is partly responsible.
Planting woodland cover between the glen and the reservoir would enhance the ecological value of the site, allowing dispersal of species between these habitats. Native riparian trees could be planted along the length of the Wood Burn, with species including Fraxinus excelsior, Alnus glutinosa, Betula spp. and Crataegus monogyna. This would also reduce the likelihood of poaching of the burn.
Ecology of the Woodburn Glen is under pressure due to the presence of residential properties. Trees have been felled to make room for these developments and garden species are at risk of escaping into the surrounding woodland.
Woodburn Reservoir and Glen Target Note Number Description 1 Mature broadleaved woodland mainly non-native. Fagus sylvatica and Acer pseudoplatanus with some Fraxinus excelsior, Ulmus glabra, Quercus petraea. Ungrazed grassy ground flora in the field with species including: Dactylis glomerata, Arrhenatherum elatius. 2 Garden pond with much Lemna sp., Typha latifolia, Glyceria. Possible habitat for amphibians. 3 Mature semi-natural broadleaved woodland with an open canopy in some places. Quercus robur dominates, with other species including: Acer pseudoplatanus, Corylus avellana, Sorbus aucuparia, Chamaecyparis lawsoniana, Betula pubescens, Fagus sylvatica, Fraxinus excelsior, Tilia cordata, Aesculus hippocastanum, Quercus cerris. Patches of Rhododendrum ponticum. Young Tilia cordata and Salix pentandra planted alongside the road. Grassy understory, damp in places with species including: Holus lanatus, Deschampsia cespitose, Ranunculus repens, Juncus effusus, Rumex obtusifolius, Dactylis glomerata, Poa trivialis, Urtica dioica, Hyacinthoides no n-scripta and Rubus fruticosus. 4 Patch of mature conifer plantation, mainly Larix eurolepis with Picea sitchensis. Grassy understorey with species including: Holcus lanatus, Anthoxanthum odoratum, Urtica dioica, Oxalis acetosella, Digitalis purpurea, Hyacynthoides non-scripta, Poa trivialis, Rhytidiadelphus squarrosus, Rubus fruticosus, Pteridium aquilinum. 5 Wetter semi-natural broadleaved woodland. Alnus glutinosa canopy with Corylus avellana and Betula pubescens. Damp grassy ground flora with species including: Holcus lanatus, Ranunculus repens, Juncus effusus, Urtica dioica, Rumex obtusifolius, Stachys sylvatica, some Pteridium aquilinum, Arrhenatherum elatius. Alnus glutinosa regeneration into grassy area. 6 Marshy area along ditch with species additional to area described in target note 5 including: Caltha palustris, Valeriana officinalis, Iris pseudocorus, Chrysosplenium oppositifolium, Phalaris arundinacea, Filipendula ulmaria, Poa trivialis, Geranium robertianum, Alnus glutinosa and Salix caprea.
7 Dense, semi natural thicket of Betula pubescens at pole stage. A few conifers around the edge mainly Pinus sylvestris and Picea abies with Sorbus aucuparia also present. Ground flora includes: Pteridium aquilinum, Hyacynthoides non-scripta, Dryopteris dilatata, Oxalis acetosella, Rubus fruticosus, Potentilla erecta. Mossy with Rhytidiadelphus squarrosus and R. loreus, Atrichum undulatum, Thuidium tamariscinum, Plagiothecium undulatum. Patch of Rhododendrum ponticum. 8 Open gravely area with regeneration of species including: Betula pubescens seedlings, Juncus effusus. Small open ditches which are possible habitats for amphibians.
9 Small strip of Pinus sylvestris.
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Woodburn Reservoir and Glen Target Note Number Description 10 Mature semi-natural oak woodland. Quercus ssp wood. Quercus robur predominates with Betula pubescens, Acer pseudoplatanus, Corylus avellana, Sorbus aucuparia, Crataegus monogyna, Fagus sylvatica, Fraxinus excelsior. Ground flora of Pteridium aquilinum Hyacynthoides non-scripta, Dactylis glomerata, Ranunculus repens, Rumex acetosa, Urtica dioica, Circaea lutetiana, Geranium robertianum, Oxalis acetosella, Stellaria holostea, Ajuga reptans, Stachys sylvatica, Poa trivialis, Galium aparine, Rubus fruticosus, Geum urbanum, clump of Rhododendron ponticum, Mnium hornum, Luzula sylvatica, Silene dioica, Holcus lanatus. Damp areas with Alnus glutinosa; Chrysosplenium oppositifolium, Ranunculus repens, Lysimachia nemorum, Geranium robertianum, Carex remota, Deschampsia cespitosa and Poa trivialis. 11 Mature semi-natural broadleaved woodland. Towards the top part of the wood the canopy the wood becomes mainly non-native as Acer pseudoplatanus predominates with scattered Quercus robur and Sorbus aucuparia, Fraxinus excelsior, Betula pubescens, Corylus avellana, Fagus sylvatica, and veteran hollow Betula pubescens. The grassy/bluebell ground flora has some Pteridium aquilinum. Other species include: Holcus mollis, Silene dioica, Circaea lutetiana, Dryopteroid ferns, Oxalis acetosella, Rubus fruticosus, Veronica montana, Stachys sylvatica and Stellaria holostea. 12 Area of mature Fagus sylvatica wood with some large trees. Also Acer pseudoplatanus and Quercus robur. Ground flora included Pteridium aquilinum, Hyacynthoides non- scripta, Oxalis acetosella and Holcus mollis. 13 Semi-natural mature broadleaved wood of Acer pseudoplatanus and Quercus robur with Fraxinus excelsior, Betula pubescens, Sorbus aucuparia, Corylus avellana and Fagus sylvatica. The grass ground flora contained Hyacynthoides non-scripta, Pteridium aquilinum, and fern dominated areas. Other species present included: Holcus mollis, Stellaria holostea, Geranium robertianum, Oxalis acetosella, Poa trivialis, Circaea lutetiana, Stachys sylvatica, Geum urbanum, Dryopteroid ferns, Deschampsia caespitosa, Ranunculus repens, Ajuga reptans, Anemone nemorosa, Thuidium tamariscinum, Atrichum undulatum. Mostly dry but with some damper area wih Chrysosplenium oppositifolium, Lysimachia nemorum. 14 Open mown grassy area, one Dactylorhiza fuchsia plant seen. 15 Woodburn reservoir. Aquatic plants noted were Potamogeton natans, P. crispa and Chara sp 16 Vegetation around Woodburn reservoir forms three distinct areas. In the north a thin strip of scrub dominated by Salix caprea with occasional Salix cinerea and Betula pubescens in the east. Growing at the waters edge are Carex sp., Juncus effusus and Sparganium erectum. 17 In the south west the landscaped upslope bank consists of a neutral grass land dominated by Deschampsia cespitosa, Rubus fruticosus, Urtica dioica, Centaurea nigra, Ulex europaeus, Crataegus monogyna and Cirsium arvense. The crest of this bank is mown and semi-improved with Holcus lanatus, Lolium perenne, Juncus articulatus, Plantago lanceolata, Trifolium pratense, Ranunculus repens, Carex viridula spp oedocarpa, Achillea millfolium, Aegopodium podagraria, Cerastium Fontana, Equisetum arvense, Rumex obtusifolius and R. acetosella. The down slope forming the bowl of the reservoir is lined with stone sets and has been colonised by moss and lichens with sparse vegetation rooting through the deep gaps. Species include Pleurozium schreberi, Grimmia pulvinata, Cladonia arbuscula, Peltigera canina, Holcus mollis, Hypochaeris radicata, Dryopteris dilatata and Geranium robertianum. 18 The south eastern edge of the reservoir is shallower and grades from marginal vegetation to marshy grassland. Triglochin palustre, Iris pseudacorus, Sparganium erectum, Phalaris arundinacea, Phragmites australis, Eleocharis palustre and Carex sp. The marshy grassland has a carpet of Rhytidiadelphus triquetris with Deschampsia cespitosa, Dactylis glomerata, Arrhenatherum elatius, Holcus mollis, Agrostis stolonifera, Gallium verum, G. saxatile, Succisa pratensis, Potentilla erecta, Filipendula ulmaria, Centaurea nigra, Angelica sylvestris, Medicago lupulina and Dryopteris affinis overtopped by a few low individuals of Crataegus monogyna, Ulex europaeus and occasional Betula pubescens seedlings. 19 Ruin of Drumairn farm. Spreading around this part of the field especially to the north is wetter and less palatable vegetation dominated by established tussocks of Juncus effusus with occasional Deschampsia cespitosa, Cirsium arvense and Senecio jacobaea. Also present are Fraxinus excelsior and Sorbus aucuparia seedlings with larger individuals of Crataegus monogyna amongst the ruin. Polypodium vulgare and common epipetric mosses and lichens have colonised the remaining walls and rubble. 20 Improved grassland is dominated by Lolium perenne with Cynosurus cristatus, Trifolium dubium, Bellis perennis and Rumex acetosella with Juncus effusus tussocks and
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Woodburn Reservoir and Glen Target Note Number Description Alopecurus geniculatus in wetter areas. 21 Gully and small disused quarry due to east of ruin. Scattered scrub of Crataegus monogyna, Sambucus nigra, Ulex europaeus over topping a stream with Pteridium aquilinum, poached ground and marginal wet flushes including Chrysosplenium oppositifolium, Petasites hybridus, Urtica dioica, Ranunculus repens, Prunella vulgaris and Geranium robertianum. Stream bottom with Scapania undulata. 22 Woodland dominated by mature Fagus sylvatica with Acer pseudoplatanus, Quercus robur, Ulmus glabra, Sorbus aucuparia, Fraxinus excelsior and Crataegus monogyna at fringes and occasionally in the understory. Ground layer consists of Brachypodium sylvaticum, Poa nemoralis, Oxalis acetosella and Hylocomium splendens in the drier parts and Pteridium aquilinum, Rubus fruticosus and Deschampsia cespitosa in brighter clearings. 23 The Wood Burn enters a steep sided shady gorge in the woodland and wet marginal vegetation includes Carex remota. The confluence with another unnamed burn results in a large flush dominated by Chrysosplenium oppositifolium. The steep rocky outcrop adjacent to this is carpeted in Blechnum spicant, Mnium hornum, Conocephalum conicum and Plagiothecium undulatum. 24 Marshy grassland of Juncus effusus and Deschampsia cespitos, with J. squarrosus, J. acutiflorus, J. conglomeratus, J. bufonius, Luzula campestris, Galium saxatile, and Potentilla erecta.
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3.9 Meikle Reive NS 640 789 Surveyed by Andrew Matthews on 20th September 2009.
The site at the edge of the Campsie fells consists of a diverse range of habitats over a steep topographical gradient. Habitats include; acid grassland, semi and improved
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grasslands, arable land, semi-natural broadleaved woodland, scattered scrub, Pteridium aquilinum, marginal inundation, scree and cliff. The archaeological feature at the centre of the site is the remains of a mott and bailey castle. These defensive earthworks are still prominent in the north and west but encroaching Pteridium aquilinum threatens to obscure them in the south and east.
Due east of the archaeological site is a track which loops around a dozen bee hives. This apiculture is small scale as only half of the hives appear to be active and is probably seasonally dependent on the flowering of ericoid heath species higher in the Campsie fells. The arable land immediately to the east is planted to supplement these bee colonies.
A single peregrine was noted roosting on a small cliff-face during the survey, although no signs of nesting were recorded.
Rarity of habitats: Cliff, scree and acid grassland represent the main habitats of interest at the site. These support lichens and heath species that are free from grazing. Inland Rock Outcrop and Scree is a UKBAP priority habitat. Score = 3
Diversity of species: The diversity of habitats within the site results in a higher than average diversity of species, especially lichens and bryohpytes associated with scree and waterfalls. Score = 2
Rarity of species: No nationally or locally rare species were recorded. Score = 3
Habitat naturalness: The habitats are mostly natural, with the exception of the semi- improved neutral grassland and extensive earthworks associated with the old fort. Score = 3
Habitat extent: The scree and cliff habitats are likely to represent less than 5% of this type of habitat within the local area. Score = 1
Habitat connectivity: The habitats are extensively linked to similar scree, cliff and acid grassland along the slopes of the Campsie fells. Score = 3
The LNCS is assessed to score 15.
Management Prescriptions
The extensive and spreading stands of Pteridium aquilinum are the primary threat to the site. These stands are encroaching on the rarer and botanically more interesting drier slopes and ledges as well as the scree and boulder landscape. The Pteridium aquilinum also poses a conspicuous threat to future appreciation of the sites archaeological interest in two key ways. Firstly it reduces access, as the tall stands of Pteridium aquilinum are difficult to walk through. Secondly it damages the visual impact of the site, as the height and density of Pteridium aquilinum obscures the definition and detail of the earthworks that differentiate this castle’s footprint from any other hill. In the shorter term the Pteridium aquilinum can be managed by cutting and spraying together with a change in the grazing regime although in the longer term broad leaved tree plantation should be considered to control and exclude the Pteridium aquilinum. The areas of coniferous plantation in the south of the site comprise Picea sitchensis and may need to be thinned. Future plantings should consider native broadleaved species instead. The trees planted on the near by Campsie golf course include Sorbus aucuparia, Fraxinus excelsior and Betula pubescens. It may be that as these trees mature the connectivity of the wildlife
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corridor extending west will increase although this is primarily dependant on the future management of the golf course.
Meikle Reive Target Note Number Description 1 Junction of fenced enclosures is the northern most tractable point of the burn. The plateau of the fell from which it drains is much wetter with areas of hagging peat revealing the underlying soil type. The marshy grassland extending north is dominated by Juncus sp with Deschampsia cespitosa, Molinia caerulea and Carex hirta. The boundary with the acid grassland which dominates the steep slope running south follows more or less the fencing east to west. The sward on this slope is dominated by Agrostis capillaris, Deschampsia cespitosa, Deschampsia flexuosa, Gallium saxatile, Gallium verum and Potentilla erecta. Down in the burn Carex nigra, Cirsium arvense, Juncus effusus, Valeriana officinalis and Heracleum sphondylium are present. 2 Waterfall microhabitat with scrambling curtain of Alchemilla vulgaris. 3 Salix cinerea subsp. oleifolia standing over the waterfall rocky outcrop with another scrambling curtain of Alchemilla vulgaris, Thymus serpyllum and Cladonia sp. 4 Very steep slopes and inaccessible ledges are dryer and receive less attention from grazers, consequently the vegetation is different in composition. Species include; Calluna vulgaris, Erica tetralix, Vaccinium myrtillus, Cladonia arbuscula, Antennaria dioica, Aira praecox, Saxifraga hypnoides, Thymus serpyllum, Campanula rotundifolia, Achillea millfolium and lichens; Cladonia arbuscula and Peltigera canina. 5 Boulders and rocky outcrops with crustose lichens Racomitrium lanugenosum, Grimmia pulvinata, Polysticum aculeatum and scattered Pteridium aquilinum. 6 A rough track serving a dozen honey bee hives. Approximately half of these seem to have active colonies. There is very limited disturbance associated with this apiculture and it is likely a good use of the site as other uses are restricted because of its archaeological interest. 7 The former castle has characteristic concentric rings of defensive ditches and banks. Water has pooled in a small hollow on the eastern flank of the man made hill and marginal vegetation includes Typha latifolia, Phalaris arundinacea and Deschampsia cespitosa. 8 Unidentified legume crop probably planted as field cover for game birds. The surrounding semi improved grassland has been limed and sown with Lolium perenne in the past although it is now dominated by Cynosurus cristatus, Dactylis glomerata, Arrhenatherum elatius and Festuca sp. 9 Rolling hills and hollows covered by a tall ungrazed sward dominated by Agrostis capillaris and Deschampsia cespitosa with occasional Ulex europaeus scrub. 10 Sheer cliff faces with scrambling and epipetric vegetation rooting into fissures and ledges. Hedera helix and Sambucus nigra are visible. A resting peregrine was observed, only very slight liming suggests this is a commonly used promontory rather than a nesting site. 11 Ulex europaeus with occasional Crataegus monogyna scrub in the south and east of the site. 12 Semi-natural broadleaved woodland in the south west corner of the site is dominated by Fraxinus excelsior with Fagus sylvatica and Acer pseudoplatanus. The ground layer includes stands of Rubus fruticosus with occasional Geum urbanum and Poa nemoralis. Deer observed moving through the wood.
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3.10 Birdston Meadows NS 655 758
Surveyed by Caroline Boffey on the 18th June 2009.
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The site is largely broadleaved plantation over damp meadows with tall herb communities, with marshy areas and vegetation-filled ditches. The trees were planted within the last 10 years, and provide cover for deer and small mammals. Species present within the plantation include Acer pseudoplatanus, Fraxinus excelsior, wild cherry, Prunus avium, Crataegus monogyna, Betula spp. and Quercus robur. Mown paths are maintained across the site to allow access for walkers.
Although the woodland is young, it provides excellent nesting and foraging habitat for passerine birds. The ditches and marshy areas may provide habitat for invertebrates and amphibians
Rarity of habitats: Broadleaved plantation is not rare in the local scale, although the extent of the wooded area and the diversity of the species make this site relatively unique in the local area. Score = 1
Diversity of species: The species mix used in the plantation, in combination with the marshy grassland and hedgerows results in a larger than expected diversity of species for this habitat type. Score = 2
Rarity of species: No nationally or locally rare species were recorded during the survey. Score = 1
Habitat naturalness: The habitat is not natural, comprising plantation woodland over drained marshy flood plain. Score = 1
Habitat extent: There are several broadleaved woodlands in East Dunbartonshire, and this habitat represents a small percentage of the total habitat in the area. However, as an area of newly planted woodland, it represents a relatively extensive amount of new woodland habitat in the area. Score = 1
Habitat connectivity: The habitat is connected to similar woodland habitat and marshy grassland along the River Kelvin corridor. The southern boundary of Milton of Campsie supports several woodland areas, both mature and immature plantation. Score = 4
The LNCS is assessed to score 10.
Management Prescriptions
The main management prescriptions for the woodland are continued monitoring of the trees as they grow and appropriate thinning when the canopy begins to close. The paths should be maintained in order to allow the use and enjoyment of the site by local residents.
A small patch of Fallopia japonica was recorded on the site. The River Kelvin in this area has large stands of this invasive plant, and control by spraying should be considered both in the site boundary and beyond.
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Birdston Meadows Target Note Number Description 1 Semi-improved neutral grassland dominated by Elytrigia repens. Deschampsia cespitosa, Poa trivialis and Alopecuris pratensis. 2 Young plantation over neutral grassland and tall herb vegetation. A mixture of tree species is dominated by Acer pseudoplatanus. Also present: Fraxinus excelsior, Crataegus monogyna, Crataegus monogyna, Betula pubescens, Quercus robur, Sorbus aucuparia, Picea sitchensis, Alnus rubra, Alnus glutinosa, Prunus padus, Salix caprea, Corylus avellana, Pinus sylvestris, Aesculus hippocastanum, Popullus tremula, Fagus sylvatica, whitebeam and poplar. The ground flora includes: Holcus lanatus, Rannunculus repens, Rumex obtusifolius, Poa trivialis, Chamerion angustifolim, Heracleum sphondylium, Urtica diocia, Dactyluis glomerata, Arrhenatherum elatius, Rubus fruticosus, Cirsium arvense 3 Semi-improved neutral grassland. This is an area of tall grass, Arrhenatherum elatius dominated, with Cirsium arvense and some Chamerion angustifolium and Holcus lanatus. 4 Defunct hedge comprising Crataegus monogyna grown out to between 3 and 5 metres high. 5 Marginal vegetation. Wet ditch covered by vegetation, species including: Rorippa nasturtium-aquatica, Juncus effusus, Myosotis scorpioides, Epilobum hirsutum, Rannunculus repens, Poa trivialis, Urtica dioica, Valeriana officinalis, Phalaris arundinacea, Glyceria fluitans, Stachys sylvatica. Slow moving water is present in the ditch with aquatic invertebrates present. This habitat is suitable for amphibians, although none were noted. 6 Marsh with Juncus effusus, Ranunculus repens, Valeriana officinalis, Galium palustre, Myosotis scorpioides, Stellaria alsine, Alopecuris geniculatus, Agrostis stolonifera, Deschampsia cespitosa, Holcus lanatus, Poa trivialis, Glyceria fluitans, and Persicaria lapathifolia. 7 Broadleaved plantation woodland planted over grassy vegetation with Holcus lanatus, Arrhenatherum elatius, Heracleum sphondylium, Cirsium arvense, Poa trivialis, Chamerion angustifolium, Alopecuris pratensis, Rannunculus repens, Deschampsia cespitosa and Rubus idaeus. At the edge of the young plantation are mature trees of Salix caprea, Crataegus monogyna, Fraxinus excelsior, Acer pseudoplatanus, Sambucus nigra, Aesculus hippocastanum, Fagus sylvatica, Crataegus monogyna, Tilia sp. and Prunus avium. A small patch of Fallopia japonica is present within the plantation. 8 Vegetation-filled damp ditch with marshy plants such as Phalaris arundinacea, Valeriana officinalis, Epilobium hirsutum, Urtica dioica, Juncus effusus, Poa trivialis, Deschampsia cespitosa, Veronica beccabunga and Myosotis scorpioides. Marginal vegetation includes Glyceria fluitans, Rnanunculus repens, Juncus effusus, Mentha aquatica, Veronica beccabunga, Arrhenatherum elatius, Deschampsia caespitose, Filipendula ulmaria and Epilobium hirsutum. 9 Broadleaved plantation woodland at pole stage dominated by Alnus glutinosa. Tall grassy/ tall herb vegetation underneath of Holcus lanatus, Arrhenatherum elatius, Ranunculus repens, Chamerion angustifolium, Veronica chamaedrys, Poa trivialis, Urtica dioica, Rumex obtusifolius and Alopecuris pratensis. An area of tall hebs is present at the edge of the plantation dominated by C. angustifolium and Arrhenatherum elatius. 10 Tall herb/ grass with Dactylis glomerata, Holcus lanatus, Chamerion angustifolium, Urtica dioica, Ranunculus repens, Galium aparine, Cirsium arvense and Rubus fruticosus.
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3.11 Wilderness Woods NS 592 714 and NS 601 722
Surveyed by Andrew Matthews on 21st July 2009
Review of Local Nature Conservation Sites - Ecology 44 RPS Planning & Development Ltd SGP6044/JF/SZ FINAL East Dunbartonshire Council November 2009
The area surveyed consists of two sites abutting a SSSI woodland just north west of Bishopbriggs. The northernmost site is a Glasgow City Council land fill site comprising grassland and scrub. .It is separated from the SSSI by the Balmuildy road and in the west it meets the Buchley ECO Centres compost, recycling depot and a bonds free warehouse. The southernmost site is largely wooded and is bordered to the north by the Balmuildy road, and to the east by an access road to a kennels and the Bishopbriggs recycling depot. The area extends as a tapering leg of woodland between marshy grassland in the east and agricultural land in the west. Part of this LNCS borders the Rookery Plantation LNCS in the south. The combination of the Wilderness Woods LNCS, Wilderness Plantation SSSI, Buckley Sand Pit LNCS and Rookery Plantation LNCS create a block of terrestrial semi- natural and natural habitats linking the River Kelvin and the Forth and Clyde Canal.
Accessed from the Bishopbriggs recycling depot the site is centred on a woodland dominated by Fagus sylvatica and Betula pubescens with occasional Quercus robur. Some of the mature trees have preservation number tags. The woodland continues as a tapering leg of woodland and grades to Salix caprea and Crataegus monogyna scrub at its margins. This leg of woodland lies between marshy grassland developing over landfill in the east and arable land in the west. It meets in the south the Forth and Clyde canal, with the Bishopbriggs Golf Club on the opposite bank. In the north the site boundary is marked by the Balmuildy road. Running down its eastern edge an access road to a kennels and the Bishopbriggs recycling depot marks the survey boundary with the SSSI woodland.
The recycling depot is closed at night and is frequently subject to petty arson and vandalism. The Bishopbriggs and Buchley police have keys to the main gate in order to attend the recycling depot, the isolated kennels and occasionally recover burnt out vehicles driven on to the marshy grassland and abandoned. The woodland receives low levels of associated disturbance; littering, fire laying and camping.
Rarity of habitats: No nationally or locally rare habitats were identified on the site. Score = 0
Diversity of species: The diversity of species is relatively high in areas of disturbed ground where ruderal vegetation exists. Score = 2
Rarity of species: Skylark are a UKBAP priority species and were noted breeding on the northern part of the site. No nationally or locally rare species were noted on the main part of the site. Score = 1
Habitat naturalness: The habitat is not natural, comprising plantation woodland over restored ground. Score = 1
Habitat extent: There are several broadleaved woodlands in East Dunbartonshire, and this habitat represents a small percentage of the total habitat in the area. Score = 0
Habitat connectivity: The habitat is connected to similar woodland habitat and marshy grassland along the River Kelvin corridor. The southern boundary of Milton of Campsie supports several woodland areas, both mature and immature plantation. Score = 4
The LNCS is assessed to score 8.
Review of Local Nature Conservation Sites - Ecology 45 RPS Planning & Development Ltd SGP6044/JF/SZ FINAL East Dunbartonshire Council November 2009
Management Prescriptions The foremost threats to this site are associated with unmonitored vehicle access. The misuse of the derelict house and dumping thought the site would be significantly limited by the placement of a gate at the junction with the balmuildy road. Removing the dumped waste and demolishing the burnt out house should be prioritised.
Melilotus alba and Buddleia davidii are alien plants that although potentially beneficial for pollinator diversity may spread and become invasive. Therefore they should be removed by cutting and spraying whilst their extent is relatively limited.
The main body of woodland in this survey is functionally contiguous with the SSSI woodland to the east and is very similar in character and composition. The access road that separates them is gated and locked at the junction with the Balmuidy road from 7pm every night. It is only single track tarmac with passing places and as a result is not particularly busy. Given that some areas of the canopy are closed over this access road, the western leg of woodland may as well be included in the SSSI. As this decision is likely to depend on other criteria a further assessment may be needed.
Throughout the marshy grassland many tree seedlings particularly Salix caprea are growing. These are heavily browsed by deer especially close to the cover of the wood and away from the exposure and disturbance of the depot. The extent of emerging scrub should be monitored as areas of significant regeneration will begin to emerge over this habitat if not controlled. Much of marshy grassland is very open and some cover may represent a positive trajectory in the sites development.
Wilderness Woods Target Note Number Description 1 Pioneer community on waste ground disturbed by heavy vehicles with fire sites and compacted heavy soils forming shallow pools of water. Short ephemeral habitat, vegetation includes: Trifolium dubium, Prunella vulgaris, Juncus bufonius, Juncus conglomeratus, Persecaria maculosa, Polygonum aviculare, Bellis perennis, Agrostis stolonifera, Poa annua, Cynosurus cristatus, Rumex obtusifolius, Ranunculus repens, Epilobium montanum, green filamentous alga, Ajuga reptans, Carex viridula ssp oedocarpa, Salix caprea seedlings, Plantago major, Cerastium fontanum, Sagina procumbens and Pleurozium schreberi. 2 The landfill site adjacent to the wilderness woodland is mapped as marshy grassland but it is a highly variable assemblage reflected by its diversity. Species include: Deschampsia cespitosa and Juncus effusus as co-dominants throughout. Equisetum arvense and carpets of Pleurozium schreberi correspond with nutrient poor gravely soil. Others species include Medicago lupulina, Anthoxanthum odoratum, Alopecurus pratensis, Trifolium dubium, lotus corniculatus, Trifolium repens, Trifolium pratense, Vicia sepium, Urtica dioica, Artemisia vulgaris, Stellaria media, Cerastium arvense, Ranunculus repens, Ranunculus acris, Achillea millfolium, Stellaria hollostea, Rumex obtusifolius, Rumex acetosa, Odontites verna, Prunella vulgaris, Senecio jacobaea, Plantago lanceolata, Galium aparine, Centaurea nigra, Cirsium arvense, Phalaris arundinacea, Valeriana officinalis, Tussilago farfara, Torilis japonica, Alchemilla vulgaris, Mentha aquatica, Scutellaria galericulata, Rhinanthus minor, Carex ovalis, Carex elata, Carex nigra, Carex hirta, Carex viridula subsp oedocarpa, and Eriophorum angustifolium. 3 The waste ground around the recycling centre has several ruderal and non-native shrubs including a Salix sp, Cotoneaster sp, and Hypericum androsaemum. Other species include Salix caprea, Polygonum bistorta, Lapsana communis, Cirsium arvense, Artemisia vulgaris and Dipsacus fullonum. 4 Main body of woodland surrounding an area of semi-improved neutral grassland habitat. At this particular site the canopy has been thinned the felled Fagus sylvatica have been limbed and stacked in a pile approximately five meters squared. Other canopy species include Betula pendula, Betula pubescens, Acer pseudoplatanus, Sorbus aucuparia and Quercus robur. The ground layer species include; Rubus fruticosus, Poa nemoralis, Carex remota, Oxalis acetosella, Dryopteris filix-mas,
Review of Local Nature Conservation Sites - Ecology 46 RPS Planning & Development Ltd SGP6044/JF/SZ FINAL East Dunbartonshire Council November 2009
Wilderness Woods Target Note Number Description Dryopteris afinis and sparse Pteridium aquilinum. 5 Small clearing with the sward in a damp hollow dominated by meadow grasses especially Agrostis capillaris, Deschampsia cespitosa, Juncus effusus, Rubus fruticosus, Rubus saxatile, Urtica dioica, Digitalis purpurea and Dactylorhiza maculata. 6 The majority of the woodlands ground flora is dominated by Dryopteroid ferns, Poa nemoralis, leaf litter, Oxalis acetosella, and Anemone nemorosa. A gully varying in depth travels most of the length of the woodland. In this area, vegetation includes cushions of Polytrichum commune, Carex remota and Blechnum spicant. 7 Long line of mature Fagus sylvatica with gnarled roots protruding from an embankment with sparse Deschampsia flexuosa and moss sp. 8 A hollow of marshy grassland dominated by Deschampsia cespitosa, Juncus effusus, Angelica sylvestris and Valeriana officinalis. 9 Dumping in woodland more prevalent in the extreme east corner close to the recycling depot. Waste includes old bikes and scrap metal, car batteries etc. 10 Thin leg of woodland becomes lower in stature with more Salix caprea and Salix cinerea. 11 Under the closed Salix caprea dominated scrub, the patchy ground layer includes Urtica dioica, Rubus fruticosus, Ranunculus repens, Poa nemoralis, Phalaris arundinacea, Juncus sp, Viburnum opulus, and Potentilla palustris. 12 Derelict house at junction with Balmuidy Road and access road to compost depot. Site of considerable vandalism fire and drug abuse. The garden is stacked high with dumped rubbish probably encouraging further fly tipping. The vegetation due east of the hose is very wet, Juncus effusus, Valeriana officinalis dominated with Stachys sylvatica, Carex pendula, Alnus glutinosa, and Betula pubescens scrub screening it from the road. Many garden escapes including Aster novi-belgii, Antirrhinum majus, Buddleja davidii, Spiraea pseudosalicifolia and Symphytum x uplandicum.
Review of Local Nature Conservation Sites - Ecology 47 RPS Planning & Development Ltd SGP6044/JF/SZ FINAL East Dunbartonshire Main Issues Report 2013 Background Report 5
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