SITE CONTENT & KEY ISSUES SWOT ANALYSIS
Middlewood Park
Salford is primarily urban. Around 1/3 of the city consists of rural open space, and relatively, the west side of Salford city is highly industrialised and densely populated. On the other side of the railway is Manchester city centre where it is mainly commercial with some residential pockets and various use high-rise buildings.
Middlewood Park is a 6-hectare site located at the very right side of the city of Salford, adjacent to the Manchester city centre and River Irwell.
of Salford
Important historical featureCathedral Church of St. John
Vegetation
The site is dominated by grassland. Shrubs and woodland edge species are only found on the slope of the north margin.
Topography
The site is mainly flat with a small hill about 5m in height next to the canal.
Manchester, Bolton & Bury Canal
Now derelict. Part of the canal that runs through the site has been restored and kept as a historical heritage and a feature of the site.
Brief history of the site:
It was a storage and transport area back in 1890s. There used to be warehouses, good sheds, mills and train tracks on site.
Railway Viaduct
The site is sorely isolated from both city centres by the viaduct which is 8m height difference.
CONCEPT
VISION & AIMS
A sustainable urban woodland for escaping city life and reconnecting with nature.
To establish an exciting woodland in the urban fabric that provides a sense of escape for busy urbanites from the hustles of city life. The park offers a higher quality of “close-to-nature experience” by featuring various types of woodland and aims to enhance the biodiversity in the urban area.
When it comes to facing global warming and extreme climate change in the future, some of the native vegetation will be replaced by adaptable exotic plants. Having a mix of native and exotic vegetation improves the resilience of the park. On a larger scale, the urban woodland also acts as a piece in the ecological stepping stone system in the Greater Manchester area, connecting the rural regions of Salford to the city centre of Manchester.
Narrow and interdict car excess on E Ordsall Ln to lessen the distinction between the two sides and by applying a woodland framework to unite the site as one.
Limited access of quality green space in high density area
Isolated/ Unwelcome
Propose Solution
Urban Woodland Park for local and serve as a stepping stone system in the wider context connecting Manchester and Salford
On the left, the woodland in front of the residential area is neat and uniform to match the urban style. The woodland character becomes more organic, en closed, and similar to natural woodland while moving closer to the rail viaduct on the right.
To provide a high quality and inclusive “urban green space” that encourages people to contact with nature to improve well-being.
Woodland Interior
The interior rooms are crucial to creating an attractive woodland: The change of light and shade Autumn leaf carpets Woodland herb and perennials.
MANAGEMENT
An adaptable and exciting urban woodland for many generations.
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To provide a long-lasting, exciting, and attractive woodland park that presents distinctive experiences throughout the year—using various approaches to maintain the unique character of areas.
Adaptive and Resilient
Extend vegetation living years through suitable management approaches. Use exotic vegetation mixes to experiment with the adaptation to future climate change.
Maintain Woodland Character Maximise Biodiversity
Improve wildlife’s living environment and maintain diversity through maintenance techniques and yearly surveys to support habitat conservation.
Advisor
Assign Project Manager and employ management team to take care of the park.
Full funding for the project through Establishing Years (Year 1-5), and funding for long-term management.
Project Manager is in charge of the major decision making of the management of the park.
partnerships provide trained staff or volunteers, while others deliver guidelines and advice for associated aspects of managing Middlewood Park.
MANAGEMENT METHOD
Middlewood Park has a main woodland as the framework and various character woodland areas. The management tasks are tailored to each zone in order to reach a high-quality and suitable management plan.
Main Woodland Woodland Core
Woodland Edge A Woodland Edge B Woodland Edge C
Wet Woodland Wet Woodland Edge Wet Woodland Core
Mash Area
Floral Meadow Pond Canal Cherry Grove Hazel Grove Lawn Collective Tree Garden
Orchard
Woodland Development Model
Provide professional insight of horticultural technique.
Responsibility
of Management Team: Park, Woodland and orchard management, canal and pond maintenance, operation of cafe and paddling boat rental.
Manchester City of Trees RSPB RHS Volunteers Skilled
paid staffs
Commission Partnerships
Source
volunteers
Bene ts for the organisation: Raise of awareness of the issues and the organisation Potential of increased membership
Bene ts for the project: Source of funding and grants for the project Provide guidance and professional advice Partnership supports Bene ts for the organisation: Increased project awareness to implement elsewhere
Middlewood Park is a newly planted woodland that needs extra care and attention during the first few years. Weed control is essential to ensure the young trees establish well and form the canopy sooner. After a continued canopy is developed, thinning and felling unwanted trees is vital for the ecosystem and the final proposed woodland structure.
Year 1-5 //Establishing Years
Year 10-15 //Canopy Developed
Introduce lower ground layer vegetation once the woodland has formed a continued canopy. Thinning is required when fast-growing species establish a canopy and start to suppress smaller trees and ground layer species.
Year 15+ //After Thinning
The thinning process allows the ecosystem to renew and grow to reach its balance, and also gives the slow-growing tree species space to develop into maturity and a period of time for ground layer species to thrive.
Lawn Field
Required regulary mowing retain cerntain grass height. Fre quency based on growth rate.
Year 20+ //Long-term
Thinning and coppice are required for the long-term management of a healthy woodland. Monitor and collect woodland data to support the management approaches. Regular health and safety checks to ensure park safety.
Regularly water surface clearance Waterway clearance in small sections where necessary Monitor and remove dominating species Periodic cutting of margin plants duing winter vagetation replacement De-silting pond if necessary Swamp Cypress Wet Woodland CC’ Section
to FreGrove
Cafe & paddling boat rental
Paddling in the canal alongside the cherry tree grove is one of the highlight in Middlewood Park.
Rotational Coppice
Coppicing is a traditional approach to woodland management that allows some tree species to put out new shoots from their stump or roots in the following spring if cut down during winter. Corylus avellana (Hazel) is a typical species that respond well to coppicing.
Hazel Playground
A natural playground for kids. Corylus avellana (Hazel) planted sparse apart with bark chip flooring. Rotational coppice in coupes required and bark chip maintence.
Management Aim
To maintain a diverse mosaic of habitat and vegetation types, and to prevent fragmentation
Wet woodland Management
Rotational coppice shrub layer
Pruning edge trees to control shade of the pond
Regular thinning and felling where necessary
Mowing ground layer if necessary
Replace die out trees
Retain veteran trees and standing dead wood
Marsh area
This area is consisted of two distinctive speices: Taxodium distichum (Swamp cypress) and the undergrowth of Lysichiton camtschatcensis (Skunk cabbage). Taxodium distichum shows stunning yellow autumn colour and Lysichiton camtschatcensis provide vivid yellow and white colour in spring.
Management Aim
To create a UK native light woodland experience with special interest in spring
Establishing Year Management Tasks
Weed control durinig growing season
Thinning to provide space for slow-growth spp.
Introduce woodland herbs and climbers after the canopy is developed
Woodland Core Management
Regular thinning
Assess woodland climbers and herbs
Selective pruning
Coppicing and felling
Retain veteran trees and dead wood
Maintain glade margin
Regular health and safety check
Create small log piles for creature’s benefit
Glade Increases edge habitat within the wood and ensure light reaches the woodland floor. Glade management requires ragularly cut back of the ground layer after flower season, shurb cut back and coppicing of woodland edge species.
Flora Meadow Management Aim
To create a vibrant visual interest and provide habitat for pollinators
Specimen Tree Quercus pubescens
1. MANAGEMENT VISION & AIMS
1.1 VISION
An adaptable and exciting urban woodland for many generations
To provide a long-lasting, exciting, and attractive woodland park that presents distinctive experiences throughout the year—using various approaches to maintain the unique character of areas. The major management approach aims to maximise the site’s contribution to the area’s wildlife, increase the biodiversity of species wherever feasible, and manage the site to stop areas from becoming species-poor. Management should aim to compromise between visitors’ use and protection of the site wildlife (e.g., rotation access and zoning).
1.2 AIMS
Adaptive and Resilient
Extend vegetation living years through suitable management approaches. Use exotic vegetation mixes to experiment with the adaptation to future climate change.
Maximise Biodiversity
Improve wildlife’s living environment and maintain diversity through maintenance techniques and yearly surveys to support habitat conservation.
Maintain Woodland Character
Manage and maintain the unique character of the woodlands to present their best condition all year round in order to attract visitors.
The management plan of Middlewood Park can be separated into two parts with different goals the areas aim to achieve: Woodland and Habitats , and the Recreational Areas . This management report is focused on the first part of the management method and tasks: Woodland and Habitats.
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MANAGEMENT FRAMEWORK
2.1 STRUCTURE OF PARTNERSHIP AND OTHER PARTICIPANTS
RSPB RHS
Information about wild birds protection and habitat conservation.
Provide professional insight of horticultural technique.
Responsibility of Management Team: Park, Woodland and orchard management, canal and pond maintenance, operation of cafe and paddling boat rental.
• •
Responsible for the management of Middlewood Park.
Assign Project Manager and employ management team to take care of the park. Full funding for the project through Establishing Years (Year 1-5), and funding for long-term management.
Project Manager is in charge of the major decision making of the management of the park.
Volunteers Skilled paid staffs
Bene ts for the project: Source of funding for the project Local volunteers Workshops and training Skilled workers
Bene ts for the organisation: Raise of awareness of the issues and the organisation Potential of increased membership
Middlewood Park aims to present a unique neighbourhood nature park that can be enjoyed in all seasons. In order to achieve that, high maintenance is required. As the park’s owner, Salford City Council is responsible for maintaining the park after construction is completed. A project manager is required due to the high level of upkeep demanded.
Partnerships
Some partnerships provide trained staff or volunteers, while others deliver guidelines and advice for associated aspects of managing Middlewood Park.
Advicery/ Guidelines
Bene ts for the project: Source of funding and grants for the project Provide guidance and professional advice Partnership supports
Bene ts for the organisation: Increased project awareness to implement elsewhere
Bene ts for the project: Local volunteers Local community has a sense of place keeping
Bene ts for the community: Provide close to nature environment Better scenery
2.2 FUNDING SOURCES AND SCHEME
Funding & Income Source Year 1 10 15 5
Short term
The Woodland Trust
MOREwoods Funding Scheme
Forestry Commission
Woodland Creation and Maintenance part of Countryside Stewardship
Long term
Salford City Council
Maintenance budget
Forestry Commission
Woodland Carbon Guarantee
Cafe and shop
Paddling boat rental Orchard events
MANAGEMENT YEARLY TASKS AND EVENTS
EVENTS/ FEATURE Winter
Summer Autumn
Volunteer hazel coppicing: assist skill staffs with rotational coppicing
Perennials cut back Coppicing
Tree felling if necessary
Spring
EVENTS/ FEATURE
Spring bulbs
Cherry blossom
Wild flower Paddling boat
MANAGEMENT
Planning winter work
EVENTS/ FEATURE MANAGEMENT MANAGEMENT
Vegetation survey Species survey
Harvest fruit Autumn colour
EVENTS/ FEATURE MANAGEMENT
Plant new vegetation if necessary Pond clearance if necessary
4. MANAGEMENT OF THE WOODLANDS AND HABITATS
MANAGEMENT APPROACH
The Middlewood Park has a main woodland as its framework that is composed of various character woodland areas to provide biodiversity and seasonal interest. The management tasks are tailored to each zone in order to reach a high-quality and suitable management plan, which will be demonstrated by orders (fig 4-1).
The general tasks of maintaining the main woodland area are divided into two stages: the Establishing Years (fig 4-2) and the Long-term Management (table 4-1).
figure 4-1 Management zoning plan
table 4-1 Main woodland management tasks
Main Woodland Woodland Core
Wet Woodland
Wet Woodland Core
Wet Woodland Edge
Woodland Edge A Woodland Edge B Woodland Edge C Mash Area Orchard
Floral Meadow Pond / Canal Cherry Grove Hazel Grove Lawn Collective Tree Garden
Detail Why Time Frequency Where Other Participants Tasks
Establish Years (Year 1-5)
1 Weed control
Use foliar acting herbicides to keep 1m squared around each tree weed free during growing season.
2 Ragular Grass/weed cutting Cut back grass and keep weeds of semi-shade like nettles and brambles in check.
To eliminate weed competition for young trees. Year 1-3 mid Apr-Sep If weed coverage exceed approximately 50% of the area Ground layer -
Main Woodland Woodland Core Wet Woodland
To reduce competition for young establishing trees. Year 1-5 Jul Annual Ground layer -
3 Thinning Remove 25% of trees on first thinning operations; 15% removal after 5 years. Gives trees more space to establish a fully growth Year 5 Nov-Feb Twice Tree layer
Longterm Management
Woodland trust, Local volunteers
4 Replace die out trees Replace plant to suitable species if a lot of them die out. To place the gap and find our what are the suitable species. Oct-Mar If necessary Tree layer Local volunteers
Wet Woodland Edge Wet Woodland Core
Woodland Edge A Woodland Edge B Woodland Edge C Mash Area
1 Plan out management goals/ tasks Discuss management approach of the year. To set out management plans according to the current situation.
3 Create small log piles
Apr-Aug Annual Whole site Other advisory partnerships
2 Monitor and mapping species Annual inspection of gerenal growth of the woodland. To keep track on invasion and specie domination. Apr-Aug Annual Whole site Wildlife trust, Woodland trust
Leave some small cut timber in the wood to create habitat piles. To provide shelter to the small animal and insects.
Orchard
Floral Meadow Pond / Canal Cherry Grove Hazel Grove Lawn Collective Tree Garden
After cutting, thining or coppiceWoodland Ground layer Volunteers
4 Coppicing and pollard Plan out the cutting cycle to create a mixed aged coppice on 15 years rotation. Extend shrub life and increase biodiversity by opening up ground layer. Depends on spp. Nov-Feb 15 years rotation Woodland Edge Volunteers
5 Health and safty check
Regular monitor and document tree health and condition. If safety concerns rises responsible actions are required.
To keep track on vegetation health and make sure it's a safe environment for visitors. Apr-Aug Annual Whole site Woodland trust
WOODLAND DEVELOPMENT MODEL
Middlewood Park is a newly planted woodland that needs extra care and attention during the first few years. Weed control is ess ential to ensure the young trees establish well and form the canopy sooner. After a continued canopy is developed, thinning and felling unwanted tre es is vital for the ecosystem and the final proposed woodland structure.
Year 1-5 //Establishing Years Year 10-15 //Canopy Developed
Plant fast-growing species to form canopy and establish woodland character. Bulbs are planted in a mass to create interest in spring, while young trees develop for the first 5 years.
Introduce lower ground layer vegetation once the woodland has formed a continued canopy. Thinning is required when fast-growing species establish a canopy and start to suppress smaller trees and ground layer species.
Year 15+ //After Thinning Year 20+ //Long-term
The thinning process allows the ecosystem to renew and grow to reach its balance, and also gives the slow-growing tree species space to develop into maturity and a period of time for ground layer species to thrive.
figure 4-2 Woodland development model
Thinning and coppice are required for the long-term management of a healthy woodland. Monitor and collect woodland data to support the management approaches. Regular health and safety checks to ensure park safety.
Woodland Character
Oak-Birch light high woodland with early spring woodland herbs.
Plant at 2m centre in group
Planting density: 25 trees per 100 m 2 Ratio of trees to shrubs : 80:20 (roughly)
Management Aim
To create a ‘‘UK native-like’’ light woodland experience with special interest in spring and focusing on habitat conservation.
Species Choice
Woodland Core Mix
Betula pendula
Ilex aquifolium
Populus tremula
Quercus falcata
Quercus pubescens
Silver birch Holly Aspen Spanish oak Downey oak
Woodland Climbers
Typical species for woodland ground cover (mix A)
Alliaria petiolata
Blechnum spicant
Convallaria majus Digitalis purpurea
Established Woodland Management
Hedera canariensis
Lonicera japonica Algerian ivy Japanese honeysuckle
Hyacinthoides non-scripta Narcissus pseudonarcissus Oxalis acetosella Primula vulgaris Ranunculus acris Teucrium scorodonia Viola odorata
Garlic mustard Deer fern Lily of the Valley Wild foxglove Bluebells
Wild Daffodil Wood-sorrel Primrose Buttercup Wood sage Sweet violet
Woodland Core Management Tasks
The management of the woodland core is mainly low after the establishing years. The most important and frequent long-term management work will be monitoring vegetation health and growth rate. These data lead to the decision-making of when and what approach should be used in maintaining the balance of this complex habitat to present its best character set in the design phase.
Table 4-2 only shows the additional tasks for the woodland core area from the general management tasks listed above (table 4-1)
table
4-2
Woodland core management tasks
Glade Management
Glades are crucial to the woodland habitat. It increases the edge area within the wood and ensures light reaches the woodland floor, which provides excellent opportunities for under-story species to thrive. The glade maintenance requires regular cut back and coppicing of shrubs and other woodland edge species, as well as ground layer cut back after flower season. This approach can ensure the glade maintains its margin and function without letting natural succession happen.
Main Woodland Woodland Core
Detail Why Time Frequency Where Other Participants Tasks
Establish Years (Year 1-5)
1 Introduce woodland herbs Once the woodland has formed a continued canopy, add in woodland herb mix. To increase biodiversity at ground level.
Woodland Edge A Woodland Edge B Woodland Edge C
Wet Woodland Wet Woodland Edge Wet Woodland Core
Year 5+ Oct-Nov Once Woodland Ground layer Local volunteers
Longterm Management
1 Regular thinning
Start time depend on species growth rate and if understorey plants are suppressed by the canopy shading.
Mash Area Orchard
Floral Meadow Pond / Canal Cherry Grove Hazel Grove Lawn Collective Tree Garden
2 Introduce climbers Once the upper layer is strong and tall enough, add in some climbers into the branches. To increase biodiversity vertically. Year 5+ Oct-Nov Once Tree layer -
To remain woodland stucture and increase light for understorey plants. Nov-Feb 10 years rotation Tree layer Volunteers
2 Assess woodland climbers Add or remove/ reduce depend on growing situation. See if it has successfully developed/ supressing the tree. Apr-Aug Annual Tree layer -
3 Assess woodland herbs Add/ replant during planing season according to planting plan if necessary. See if it has successfully developed Mar-Apr Annual Woodland Ground layer -
4 Perennial cut back Cut back ground floor perennials.
5 Grassland cut back Cut after the flowering season.
6 Selective pruning Trim back overgrowing canopy and cut down lower branches to maintain glade margin as neccessary.
7 Coppicing and pollard Plan out the cutting cycle to create a mixed aged coppice on 15 years rotation.
8 Retain veteran trees and standing dead wood Make sure they're not unsafe. Retain dead wood for small animals as shelters.
To present a tidy sence.
To present a tidy sence.
Nov-Dec Annual Woodland & Glade Ground layer -
Oct-Mar Annual Glade Ground layer -
To provide increased edge habitat within the wood and ensure light reaches the woodland floor. Nov-Feb 10 years
Glade Shurb Layer -
Extend shrub life and increase biodiversity by opening up ground layer. Nov-Mar 15 years rotation Glade Woodland trust Volunteers
Dead wood is a valuable resource for some species. If there is no safety concern, it's better for the ecosystem to keep them. - - Tree layer Woodland trust
WOODLAND EDGE A
Woodland Character
Oak-Birch light high woodland edge with early spring woodland herbs.
Plant at 2m centre in group
Planting density: 25 trees per 100 m 2 Ratio of trees to shrubs : 50:50 (roughly)
Management Aim
To create a similar UK native woodland semi-open edge, and to maximise the biodiversity value of the habitat while preventing fragmentation.
Species Choice
Woodland Edge Mix A
Betula utilis jacquemontii
Crataegus monogyna
Corylus avellana Corylus colurna
Prunus spinosa Sorbus aria
Birch(multi stemmed) Hawthorn Hazel Turkish Hazel Blackthorn Whitebeam
Typical species for ground cover
Alliaria petiolata Blechnum spicant Convallaria majus Digitalis purpurea Hyacinthoides non-scripta Narcissus pseudonarcissus Oxalis acetosella Primula vulgaris Ranunculus acris Teucrium scorodonia Viola odorata
Garlic mustard Deer fern Lily of the Valley Wild foxglove Bluebells Wild Daffodil Wood-sorrel Primrose Buttercup Wood sage Sweet violet
figure 4-5 Woodland edge mix A image
table 4-3 Woodland edge mix A management tasks
Detail Why Time Frequency Where Other Participants Tasks
1 Coppicing
Coppicing 'Crataegus monogyna ' and 'Corylus avellana ' in small coupe on 10 years rotation.
Extend shrub life and increase biodiversity by opening up ground layer. Nov-Feb 2 years Shurb Layer Volunteers, Woodland trust
2 Perennials cut back Cut back according to species requirements. To encourage flora generation next year. Feb-Mar Annual Woodland Ground layer -
3 Maintain woodland edge margin Cut back self-seeding woodland core tree species. To keep to the design plan and prevent natural succession dominating the whole area. Nov-Feb 3 years Woodland Edge Volunteers
4 Cut back/ pruning shrubs Check out under storey shrubs growth see if cut back is required. To prevent shrubs overgrowing suppressing other species. Nov-Feb 2 years Shurb layer -
5 Maitain margins of Vegetations Keep the margin of different areas according to design plan by cutting back. To keep to the design plan.
Nov-Feb Annual Woodland Edge -
6 Invasion control Remove/ reduce 'Rubus fruticosus ' and other fast growing or invasive species that might come along the woodland edge. To prevent unwanted, competitive vegetations. Nov-Feb Annual Woodland Edge -
Woodland Character
Red and pink colour theme vibrant seasonal woodland edge.
Plant at 2m centre in group
Planting density: 25 trees per 100 m 2
Ratio of trees to shrubs : 40:60 (roughly)
Management Aim
To create a visual abundant, neat woodland edge.
Species Choice
Woodland Edge Mix B
Acer campestre
Malus sylvestris
Prunus avium
Prunus serrulata
Rosa canina Sorbus aucuparia
Taxus baccata
Field maple Crabapple Wild cherry Japanese cherry Dog rose Rowan Yew
Typical species for ground cover
Campanula trachelium
Geranium pratense Geranium robertianum
Luzula sylvatica Narcissus pseudonarcissus Salvia verbenaca Sanguisorba officinalis Silene dioica Stachys officinalis Teucrium scorodonia Torilis japonica
Woodland Edge B Management Tasks
table 4-4 Woodland edge mix B management tasks
Tasks
Longterm Management
Detail Why
Bell flower Meadow geranium Herb robert
Greater wood-rush Wild daffodil Great burnet Red campion Common hedgenettle Devil’s-bit scabious Wood sage Upright hedge parsley
figure 4-6 Seasonal image of woodland edge mix B
Nov-Feb Annual Shurb layer -
4 Cut back Check out under storey shrubs growth see if cut back is required. To prevent shrubs overgrowing suppressing other species. Nov-Feb 2 years Shurb layer -
5 Maitain margins of Vegetations Keep the margin of different areas according to design plan by cutting back. To keep to the design plan.
Nov-Feb Annual Woodland Edge -
6 Invasion control Remove/ reduce 'Rubus fruticosus ' and other fast growing or invasive species that might come along the woodland edge. To prevent unwanted, competitive vegetations. Nov-Feb Annual Woodland Edge -
Woodland Character
Fruity, shruby and wild woodland edge.
Plant at 2m centre in group
Planting density: 25 trees per 100 m 2
Ratio of trees to shrubs : 60:60 (roughly)
Management Aim
To create a habitat that attract wild bird and small animals and high in biodiversity value.
Species Choice
Woodland Edge Mix C
Ilex aquifolium
Malus sylvestris
Olea europaea
Prunus padus
Prunus spinosa Rubus fruticosus
Sambucus nigra Sorbus aucuparia Vaccinium myrtillus
Holly Crabapple European olive Bird cherry Blackthorn Bramble Elder Rowan European blueberry
table 4-5 Woodland edge mix C management tasks
Typical species for ground cover
Campanula trachelium
Geranium pratense
Geranium robertianum
Luzula sylvatica
Narcissus pseudonarcissus Salvia verbenaca
Sanguisorba officinalis Silene dioica
Stachys officinalis Teucrium scorodonia Torilis japonica
Bell flower Meadow geranium Herb robert Greater wood-rush Wild daffodil Great burnet Red campion Common hedgenettle Devil’s-bit scabious Wood sage Upright hedge parsley
Rotational Coppice
Coppicing is a traditional approach to woodland management that allows some tree species to put out new shoots from their stump or roots in the following spring if cut down during winter. ‘ Corylus avellana ’ (Hazel) is a typical species that respond well to coppicing.
1 Coppicing Coppicing 'Crataegus monogyna ' and 'Corylus avellana ' in small coupe on 10 years rotation. Extend shrub life and increase biodiversity by opening up ground layer. Nov-Feb 2 years Shurb Layer Volunteers, Woodland trust 2 Perennials cut back Cut back according to species requirements. To encourage flora generation next year. Feb-Mar Annual Woodland Ground layer -
3 Place bird house Place bird house and bug hotels on trees and ground. To encourage wild bird to visit and nest. Jul-Aug Replace if necessary Woodland Edge RSPB, Wildlife trust, Volunteers
4 Cut back/ pruning shrubs Check out under storey shrubs growth see if cut back is required. To prevent shrubs overgrowing suppressing other species and improve the shape and character of a tree whilst maintaining health. Nov-Feb 2 years Shurb layer -
5 Maitain margins of Vegetations Keep the margin of different areas according to design plan by cutting back. To keep to the design plan. Nov-Feb Annual Woodland Edge -
6 Invasion control Remove/ reduce 'Rubus fruticosus ' and other fast growing or invasive species that might come along the woodland edge. To prevent unwanted, competitive vegetations. Nov-Feb Annual Woodland Edge -
7 Collect data of wild birds Monitor nesting rate and wild bird visiting frequency. To have a better understandind of wild bird habitat conservation. - very 3 months
Woodland Edge RSPB, Wildlife trust
HAZEL GROVE
Woodland Character
Fruity, shruby and wild woodland edge.
Plant at 5m centre apart
Planting density: 10 trees per 100 m 2
Management Aim
To create a beautiful, aestethic hazel coppice with gentel carpet ground layer species.
Species Choice
Hazel Grove
Corylus avellana
Corylus colurna ellana Hazel Italian hazel
Typical species for ground cover
Alliaria petiolata
Narcissus pseudonarcissus
Ranunculus acris
Primula vulgaris
Prunella vulgaris
Silene dioica
Tulipa sylvestris
Tulipa tarda
Garlic mustard Wild daffodil Buttercup Primerose Self-heal Red campion Wild tulip Late tulip
Hazel Grove Management Tasks
table 4-6 Hazel grove management tasks
Tasks
Longterm Management
1 Raguler coppice
figure 4-8 Hazel grove section
figure 4-7 Sissinghurst Castle Garden. Image of hazel coppiced grove with lovely ground cover.
Sissinghurst Castle Garden. https://www.ntprints.com/image/1056200/jonathan-buckley-the-nuttery-inspring-at-sissinghurst-castle-garden-near-cranbrook-kent 0 1 5 10 20m
Coppice of 'Corylus avellana' and 'Corylus colurna ellana ' on 5-10 years rotation in coupes: 1/3 of the trees in the system at a time. Extend shrub life and to form a coppided glade. Nov-Feb 5-10 years, depends on growing condition Shrub layer Woodland trust
2 Mow path Mowing height: 6cm. To keep the footpath accessible and tidy. - As required Ground layer -
3 Perennials cut back Cut back according to species requirements. To encourage flora generation next year. Feb-Mar Annual Ground layer -
4 Clean up coppiced cut Pile the small cut in other areas where necessary. Keep the ground neat. To present a clean and aesthetic image. After cutting, thining or coppice - Ground layer -
Woodland Character
Dominated by swamp cypress, shows dramatic autumn colour.
Plant at 2m centre in group
Planting density: 25 trees per 100 m 2 Ratio of trees to shrubs : 90:10 (roughly)
Management Aim
To maintain a diversee mosaic of habitat and vegetation types, and to prevent fragmentation.
Species Choice
Wet Woodland Core Mix
Betula pubescens Populus alba Populus tremula Taxodium distichum
Wet Woodland Edge Mix
Alnus glutinosa Alnus cordata Crataegus monogyna Frangula alnus Salix alba Salix caprea Salix cinerea
Marsh Area
Lysichiton camtschatcensis Taxodium distichum
Downey birch White poplar Aspen Swamp cypress
Typical species for arquatic margin plants
Alder Italian alder Hawthorn Alder buckthorn White willow Goat willow Grey sallow
Skunk cabbage Swamp cypress
Achillea ptarmica Butomus umbellatus Caltha palustris Carex pendula Filipendula ulmaria Iris pseudacorus Juncus effusus
Lychnis flos-cuculi Lythrum salicaria Myosotis scorpioides Prunella vulgaris Stachys palustris Succisa pratensis Vicia cracca
Sneezewort
Flowering rush Marsh marigold Sedges Meadowsweet Yellow-flag iris Soft rush Ragged robin Purple loosestrife Water forget-me-not Self-heal Marsh woundwort Devil’s-bit scabious
https://www.bigstockphoto.com/image-332453302/stock-photoiris-marsh-on-a-pond%2C-a-pond-with-yellow-flowers%2C-yellow-iris%2C-marsh-vegetation
figure 4-9 Aquatic marginal plant featuring ‘ Iris pseudacorus’ (yellow-flag iris). This species spreads quickly, maintaining by digging out the unwanted ones to prevent species domination.
figure 4-10 Marsh area featuring ‘ Taxodium distichum ’ (Swamp cypress) and the undergrowth of ‘ Lysichiton camtschatcensis ’ (Skunk cabbage).
figure 4-11 Wet woodland section
Wet Woodland & Pond Management Tasks
The management of the wet woodland is similar to the main woodland mentioned above, with regular thinning to open up canopy and rotational coppicing to dense under-storey growth.
Ponds do not require much maintenance aside from removing any litter or organic matters and inspecting the pond for pollution or invasive or dominating species. Other than those above, controlling algal blooms is essential to a diverse pond habitat. Algal bloom is caused by a release of nutrients during soil disturbance and should reduce naturally over time.
table
4-6
Hazel grove management tasks
If it densely covers the water surface and prevents the light and oxygen from getting into the water, then clearing and treatment are required. To control algal blooms ideally is to remove the source of nutrients coming into the water; if it’s not possible, clearing by hand and treating with barley straw are the options. Barley straw is most effective if applied twice a year. Better results when applied in early spring before algal growth begins and again in autumn. Rotting tree bark can be just as good as barley straw at getting rid of algae which is a good reason for leaving some fallen branches in the water. (The Mersey Forest pond management guide)
Detail Why Time Frequency Where Other Participants Tasks
Longterm Management
1 Waterway clearance
Remove trash, excess mud silt and organic matter where necessary in small sections. Regular cleaning helps prevent serious cloggage of the pond. Oct-Dec Annual Waterway Fresh water habitat trust
2 De-silting pond Clearing of bottom muck. De-silt centre part of the waterbody only. To maintain biodiversity. (Wildlife needs deeper water) Nov-Feb 2 years
Bottom of pond Fresh water habitat trust
3 Water surface clearance Remove trash and organic matter floating on the water. To maintain a clean and beautiful environment. If necesseray Fortnightly Water Surface Fresh water habitat trust
4 Monitor pond vegitations
Map out vegetation plans to monitor plant growth, expansion or invasion. To collect data of plant growing rate in order to identify fast growing species and species domination. - Monthly record
Pond and margin area Wildlife trust, Woodland trust
5 Remove dominating species Cut back or remove dominating and quick growing species as required. To prevent dominating species taking over the whole area and smothering other plants, decreasing biodiversity. Oct-Dec At least once a year (depends on spp.) Pond and margin area Local volunteers
6 Periodic cutting Reeds, wet grassland and other aquatic vegetations required cut back or mowed. To maintain a neat and sense of care environment. Nov-Mar Annual Pond and margin area -
7 Shade control Retain vegetation on the northern side of the pond and clear only the southern edges. To ensure sunlight for aquatic plants to carry out photosynthesis. Nov-Mar If shade coverage exceed approximately 40% of the area
8 Remove cuttings
9 Vegetation replacement
Place cleared vegetation on the bank, close to the water for 24hr to allow trapped wildlife to escape back into the water. The removal can be used as compost for the orchard.
To prevent smothering the waterway and lessen habitat damage. After cutting -
Wet woodland edge -
Pond and margin area Volunteers
Replace die out plant with suitable species under yearly monitor. To place the gap and find our what are the suitable species. Oct-Dec Annual Pond and margin area -
10 Pollution of water Clear out the pond in sections. To ensure solving the pollution entirely. Oct-Dec If necesseray Pond Fresh water habitat trust
11 Coppicing and pollard
12 Regular thinning
Coppicing 'Alnus glutinosa ' and Alnus cordata ' in small coupe on 15 years rotation.
To dense the under-storey layer and increase biodiversity by opening up ground layer. Nov-Feb 3 years
Wet woodland edge Volunteers, Woodland trust
Start time depend on species growth rate and if understorey plants are suppressed by the canopy shading. To remain woodland stucture and increase light for understorey plants. Nov-Feb 10 years rotation Tree layer Volunteers
13 Regular mowing Mowing required when under storey grass reach over 40cm To keep the wet woodland edge and the bank neat. -
When under storey grass reach over 40cm Wet woodland edge -
Management Aim
Enhance community participation and increase wildlife abundance through food production.
Species Choice
Orchard
Malus domestica ‘Greensleeves’
Malus domestica ‘Saturn’
Pyrus communis ‘Concorde’
Pyrus communis ‘Winter Nelis’
Festuca longifolia
Apple Apple Pear Pear Grass
The Orchard Management Tasks
Established Years (1-10 years)
Many young trees fail to grow or die before maturity due to neg ligence. Aftercare should focus on watering, weed and pest con trol,and firming in. Keep an area of 1m 2 around the base of each tree weed free to exliminate the competition with weeds. Always water the trees and maintain the watering programme during the establishment phase.
Long-term
Pruning is essential when it comes to managing an orchard. It’s an approach to improve the shape and character of a tree whilist maintaining health. By removing unwanted growth, crossbranch es and deadwood can restore health and vigour of the tree.
table 4-7 The orchard management tasks
Detail Why Time Tasks
Establish Years (Year 1-5)
1 Weed control Use foliar acting herbicides to keep 1m squared around each tree weed free during growing season. To eliminate weed competition for young trees. Year 1-3 mid Apr-Sep
If weed coverage exceed approximately 50% of the area Ground layer -
2 Ragular Grass/weed cutting and mowing Cut back grass and keep weeds of semi-shade like nettles and brambles in check. To reduce competition for young establishing trees. Year 1-5 Jul If grass height exceed 40 cm Ground layer -
3 Path mowing Regular mowing foot path at 60mm. To keep the footpath visible and accessible.
Year 1-5 Jul If grass height exceed 10 cm Ground layer -
4 Fertilise fruit tree When and what kind of fertiliser is required differ on the growing condition and nutrients it lacks. To producing better fruits and increase production. Year 1-5 Depend on growth conditioin. - Under the tree -
5 Replace die out trees Replace plant to suitable species if a lot of them die out. To place the gap and find our what are the suitable species. Oct-Mar If necessary Tree layer Local volunteers
Longterm Management
1 Hold Fruit Harvest Event Fruit picking event for visitors as a funing source. As one of the funding source of park management. Oct-Feb Monthly Orchard Volunteers/ Locals
2 Fruit harvest Rest of the fruit goes to food bank or charity. Bad ones goes to compost on site. - Oct-Feb Monthly Fruit tree Volunteers
3 Regular Pruning
4 Regular cutting back
5 Mow grass
To remove cross branches. Pruning Pyrus communis 'Concorde' and Pyrus communis 'Winter Nelis' as required.
Cutting back Malus domestica 'Greensleeves' and Malus domestica 'Saturn' as required
To encourage fruiting for next year and improve the shape and character of a tree whilst maintaining health Nov-Jan Anunal Fruit tree -
To encourage fruiting for next year. Oct-Nov Anunal Fruit tree -
Left 1m from the centre of tree unmowed. Mowing height: 30cm. Footpath mowing height: 6cm. To keep the footpath accessible and tidy. - As required Orchard footpath -
6 Monitor tree diseases Yearly check and document tree health. To make sure trees are desease-free and get treatment when needed. Sep Anunal Fruit tree -
‘‘A sustainable urban woodland for escaping from daily city life and reconnecting with nature.’’