Eaglestone Local Park Management Plan 2011‐2015

Neighbourhood Management

Milton Keynes Council Eaglestone Local Park

www.milton‐keynes.gov.uk/parks‐and‐open‐space/

Eaglestone Local Park – Green Flag Management Plan

Version Control

Version Number Purpose / Changes Author Date 1 Original M. Barnes 24/1/11 1.1 Updates to: M. Barnes 10/1/12 p.7 - Council Plan p.8 - Social Atlas p.9 – Para 5 (enquiries) p.11 – Para.4 p.12 – Para. 8 & 9. p. 23 – Para. 3 p. 29 – Interpretation p.32 – Footpath reconstruction Appendix 6 - Updated 1.2 Updates to: M. Barnes 5/12/12 Document re-page numbered. p.9 Council corporate plan p.10 Social Atlas p.11 para 4 (dynamic play space) p.20 para 2 (planting “was” undertaken) p.25 para 3 Appendix 6 - Updated

2 Contents

Page 1. Forward 5 2. Introduction 5 3. History and description of the local area 7 4. Location of Eaglestone Local Park and site context 7 5. Eaglestone Local Park Vision Statement 8 6. Aims and purposes of the site 8 7. Community 10 8. Ecology 14 9. Facility and visitor management 23 10. Interpretation and publicity 27 11. Development of Eaglestone Local Park 34

Appendices Introduction to Milton Keynes council 0 Site Plan of Eaglestone Local Park 1 Meadow Development Plan 2 Play Area audit 3 Eaglestone Park Survey 4 Tree Survey & Assessment 5 Events 2007-12 and Attendance Figures 6 Risk Assesments and DDA Survey 7 Annual programme 8 Local Plan Framework 9 Landscape Management Framework 10 Management Specifications 11 Highway Footpath Reconstruction 12

Management Plan

Eaglestone Local Park

1. Forward The Eaglestone Local Park Management and Development Plan has been produced in order to set out a vision for the park. The plan includes information about the local context, history, nature and make up of the site.

This plan has been prepared with the input of Milton Keynes Council staff, particularly the Neighbourhood Management team as well as Woughton Community Council, Thames Valley Police, Falconhurst School and local residents, both individually and through the Residents Association. The plan is designed to ensure a coordinated approach so that future development is in line with Milton Keynes council policies to preserve and enhance the flora and fauna and meets the aspirations of the local community. In addition, the plan informs the local community, user groups, contractors and any one else with an interest about management, maintenance and future development issues.

The plan has been guided by both Green Flag advice and CABE Space (Commission for Architecture and the Built Environment) guidelines for excellence in design and management of parks.

2. Introduction

Eaglestone Local Park is a large informal area of just over 4 hectares. It is located within the Parish of Woughton. The area was originally farm pasture; remnant hedgerows (which contain supplementary planting undertaken as part of the development of the Eaglestone) are a visual reminder of this.

Woughton is not deficient in terms of the quantity of open space of recreational value and therefore it is important that facilities in the area compliment each other, rather than duplicate provision.

Eaglestone Local Park is designated as a local park in the Milton Keynes hierarchy of parks and open space and provides a range of outdoor recreational pursuits which accommodate:

• A contribution to landscape structure. • Sufficient mown grassed area to provide for informal recreational use. • Equipped play provision. • Some youth provision. • Areas to promote and enhance biodiversity. • Space for public art development.

The park has links with the Peartree Lane Wildlife Corridor and other neighbourhood open spaces within Eaglestone. These are accessible by visitors along the city’s Redways, suitable for both pedestrians and cyclists and via neighbourhood pathways. Growth in the area is likely to increase the strategic importance of the park for recreation.

3. History & Descriptions of the Local Area In 1927 "The Victoria History of the Counties of England: Buckinghamshire" states with regard to the Woughton-on-the-Green parish, as it then was:

The parish of Woughton has an area of 1,224. acres, of which 333 acres are arable land and 806 permanent grass. The soil is various, mostly clay, and the subsoil clay and gravel. The principal crops grown are wheat, beans and barley. The parish is watered by the River Ouzel, which forms its eastern boundary. The slope of the land is from 345 ft. above ordnance datum in the west to 216 ft. above ordnance datum in the east, where the Ouzel is liable to overflow its banks. Until the end of the 18th century the river here was crossed by a bridge, known as Monxton's Bridge, connecting Walton and Woughton parishes.

From: A History of the County of Buckingham: Volume 4 (1927), pp. 515-519.

The area that makes up the Park was previously farmland with original hedgerows and ditch lines still extant. This has been verified from parish records and early OS maps. The park was developed during the construction phase of Eaglestone between 1970 and the mid 1980’s as part of the new town of Milton Keynes with the addition of the two play areas and the adjacent local centre. The principal architect of Eaglestone was Ralph Erskine, responsible for notable developments such as the Byker Wall estate in Newcastle and the Greenwich Millennium Village in London. Milton Keynes Council manages around half of the parks and open spaces within the borough (the Parks Trust being responsible for the linear parks within the new city development). Eaglestone Local Park is one of approximately 161 parks varying in size and location which are managed by the council.

Figure 1. Aerial view of Eaglestone Local Park.

In the above image, the park dominates the centre of Eaglestone, the remnants of the field boundary system can be clearly seen. Golden Drive snakes round the area to the South East and the local centre and Falconhurst School can be seen to the North West. The housing stock in the South of Eaglestone is predominately owner-occupier; the Everglades sheltered housing complex on Great Denson to the West of the park and significant

6 levels of tenanted properties to the North. A Redway runs North to South through the park providing a safe through route for cyclists and pedestrians away from the roads. This Redway links to the centre of Milton Keynes 1km to the North and to the Peartree Lane wildlife corridor to the South providing a gateway to all areas of the city by foot or by bike along the 273km of Redway routes.

4. Location of Eaglestone Local Park and Site Context

Eaglestone Local Park is located within the grid square of Eaglestone south of the centre of Milton Keynes. The site is the largest open space in Eaglestone and dominates the centre of the estate. The site is bordered by Golden Drive to the East and is overlooked by residences on other sides. There is no public motor vehicle access. Access for pedestrians is via footpaths at 20 locations around the parks 2km perimeter and by the Redway (cycle path) from the North by the local centre and from the South via Kite Hill, Golden Drive and Peartree Lane.

Legend Woodland Shrub bed Amenity grass Street light Wet Ditch Play area Meadow grass Bench Tree Redway route

Status Grid reference Local Park SP 866 376 GB

Area Access 3.8 hectares Open throughout the year. 9.3 acres

Figure 2. Layout of Eaglestone Local Park (See Appendix 1 for larger version)

5. Eaglestone Local Park Vision Statement

In 2005 a service charter was created to outline Milton Keynes Council’s commitment to parks and open spaces. The charter sets out the standards the public should expect and the services the council provides:

• Attractive open spaces that encourage pride in locality. o Provide information on and promote parks and open spaces as a community resource.

o Assess parks and open spaces to ensure equal access for all members of the community.

o Encourage the involvement of members of the community, who represent as many green space users as possible, in the service.

• Functional parks & open spaces that provide opportunities for recreation. o Manage and inspect parks and open spaces on a programmed basis, against national standards, to ensue that they are clean, well maintained, healthy, safe and secure places for all members of the public to use.

• Sustainable parks and open spaces for current and future generations in a modern growing city. o Conserve natural features, flora and fauna and structural features of merit.

o Maintain the park to available resources, using environmentally sound methods, relying on best practises available to current knowledge.

6. Aims and Purposes of the Site

Milton Keynes Council recognises that parks and green spaces make a valuable contribution towards its priorities of economic generation and prosperity, social inclusion and environmental protection. These aspirations are borne out in:

• The Community Strategy “Our handbook for change” 2004 – 2034 o Conserve the greenness of Milton Keynes o Well-designed green spaces, of a suitable size and in the right location o Local identity / sense of place

• Waste Strategy (Approved 20/12/05) o The Council will install recycling facilities in all Council buildings for the recycling of paper and other materials. o The Council will encourage and educate to minimise waste and continue to promote waste minimisation in its activities.

• Council Corporate Plan 2012-16 o Living in MK. o Visiting MK. o Cleaner, Greener, Healthier, Safer MK

• Capital Strategy 2010/11 to 2014/15 o Contributes to the community vision, the community strategy and the council’s vision, values, strategic objectives and council priorities.

• Milton Keynes Open Space Strategy 2007-2027 o The Strategy’s vision is to achieve: “The best possible standard of provision, integration and quality of accessible open space within the Borough of Milton Keynes, serving the needs of the growing Milton Keynes community, ensuring that local people are involved and that open space is valued by all and managed in a sustainable manner for future generations”.

• Milton Keynes Local Area Agreement - Closing the Gap o Empower local people to have a greater influence over local decision-making (Outcome 1.5). o Increase the number of people volunteering (Outcome 1.5).

• Public Art Strategy 2010-2014 o To promote and build on the public arts collection, interpreting and caring for it for future generations. o To empower and involve communities in public art development to enhance and celebrate the sense of place.

6.1 Local Plan The local plan sets out the requirements of planning to meet the needs of the community. The emphasis of Policy L3 and the standards outlined below is on meeting the specific local needs in a flexible manner, providing a wide range of quality facilities. (See Appendix 9).

“A fixed proportion of development sites be reserved for open space.” They may need to fulfil more than just an area for recreation – e.g. on aesthetic or nature conservation grounds.

The strategic plan for provision identifies that Eaglestone Local Park should offer the following range of quality open space facilities to local households within approximately a 500-metre radius:

• Large open area of grassland to accommodate informal recreation • Form part of the wildlife corridor • Children’s play area (Neighbourhood level provision). • Teenage provision • Community Events Area • Areas of wildlife interest

Eaglestone Local Park provides the local community with an area of aesthetically pleasing naturalised open space; it offers free access with opportunities to pursue a range of outdoor leisure and social activities. There are provisions for local people of all ages and levels to have the ability to meet, walk, sit, play and enjoy.

7. Community The 2012 Milton Keynes Social Atlas provides a comprehensive update of demographic information for Milton Keynes.

Key

Shading indicates a value between the average value and 50% above the average.

Shading indicates a value 50% above the average value.

Statistical highlights

• Population 2450 • Higher rate of reported Violent Crime, Burglary, Fires and Criminal Damage. • High %age of older people.

Figure 3. Eaglestone Social Atlas 2012 analysis.

The park offers a varied, accessible, no cost leisure facility to the community which can be enjoyed by all.

There are numerous health benefits to the local community. Trees act to absorb noise and pollution from the air. Open spaces provide locations for informal play and sport. The provision of modular play equipment allows younger members of the community to develop mobility and social skills. The peaceful surroundings provide an area which helps to reduce stress through interaction with the natural world. Redways offer links for cyclists and pedestrians to all areas of the city with minimal confrontation with motorised vehicles. The majority of park users from the locality are fortunate in that they can access the park without having to cross roads. 7.1 Report a Problem? The Council Web pages allow members of the public to report problems directly over the net. User-friendly interactive graphics allow the user to access information about council services and report problems in their area. Each scene contains a number of themed “hot spot” areas, which are “doorways” to service menus

The themes covered in the Street Scene interactive graphic include;

Transport, Highway Repair, Pavement Maintenance, Waste and Recycling, Residential, Retail, Street Lighting, Drainage, Crossings and Road Safety, Trees and Scrub Maintenance and Animals on Highways,

http://www.mkweb.co.uk/street-care/

Figure 4. STREETCARE website graphic

The public are also able to report a problem via the Environmental Services Helpline on (01908) 252592. Calls are logged and reports are collated highlighting problem areas for particular landscape types, vandalism etc.

During 2008-12, nineteen enquiries were received by Milton Keynes council in relation to this park. Four of these were related to the management of the play areas (reporting damaged equipment or litter). Seven were regarding tree related management (trees obstructing satellite signals, fallen or damaged limbs - Policies regarding the management of trees in general in Milton Keynes can be found on the Parks and Open Spaces website). Other enquiries relate to missing bollards, footway defects, and flooding. http://www.milton-keynes.gov.uk/parks-and-open-space/

7.2 Involvement The council is committed to involving the local community and providing opportunities for local people to participate and feed in to the management decision-making process including;

• Members of the public are provided with opportunities to feedback through the Parish council and residents association.

• Park user survey carried out in 2007-8 and 2011-12 (see Appendix 4) to assess local community needs and use within parks. • Local school involved with wild flower and spring bulb planting in 2007 and 2008. • A programme of events throughout the year aimed at the whole community (see Appendix 6).

Figure 5. Falconhurst School planting spring flowering bulbs.

7.3 Community Outreach Although many local people already use the park, the aim of the various initiatives is to widen the appeal. Talks are offered to local groups, as are guided walks, such as the Bat and History Open Day walks. By working with other agencies in the area it has been possible to engage young people through the holiday play schemes and through the youth centre.

The Safer Communities wardens, part of the Neighbourhood Management team at Milton Keynes Council provide a simple package which enables groups at middle schools to:

• Identify problems like graffiti and vandalism in their area. • Utilise the STREETCARE website so that youngsters and their families can report problems at any time. • Shows how these problems are resolved.

This simple exercise not only helps youngsters to take control of their environment but also provides a vehicle for literacy, IT and citizenship within the schools' programmes.

Wardens also talk to schools regarding personal safety, awareness of issues around Halloween and firework safety.

The team also have access to a environmental toolkit comprising a range of pickers, brushes, wipes and other items to enable local groups to embark on a “Tidy up” in their area. These have been supplied free of charge by the councils cleansing contractor, Serco.

7.4 Parish liaison A close working relationship with the parish is fostered through regular meetings and the support of the Councils own parish partnership department. The site is jointly visited by Neighbourhood Management staff and members of the community council to ascertain the issues and requirements for the park to meet the needs of the local community. Neighbourhood Managers and council officers regularly attend parish meetings as well as Neighbourhood Action Groups (NAGs) which work closely with Thames Valley Police and residents to identify the top three concerns for residents and act to eliminate anti-social behaviour and improve community safety. http://www.milton-keynes.gov.uk/safermk_safer_neighbourhoods/

Eaglestone has an active Residents Association which meets on a monthly basis. Regularly attended by council neighbourhood engagement officers; it serves as a point of contact to gauge satisfaction with service delivery and as a sounding board for proposed improvements and events. Additionally, it allows the officers to engage local interest and promote the park as a local resource for leisure and recreation. As the park has many physical neighbours with the properties which surround it, maintaining a working rapport with the community is of high importance.

Falconhurst School has been enthusiastic in encouraging its pupils to engage with the development of the park. For example, they assessed and suggested improvements to play facilities within the area which were then put forward with support for MKC and the residents association into a successful bid for funding from GrantScape in 2006. The school has further aided in the development by replanting native wildflower species to the pond area with the aid of the council ecologist and in planting some 4000 spring flowering bulbs over the last 2 years. In total, this has encompassed the involvement of over 300 pupils across 4 year groups during 2006-8. The school has additionally had input into the users survey to gauge user satisfaction and to highlight areas for improvement / development opportunities within the park. From their comments, the climbing wall was devised and developed in 2008.

Eaglestone Youth Group, along with residents at Everglades and the residents association are currently involved in a project to provide opportunities for exercise within the park with a “park gym” (installed) and dynamic play space. Subject to third party funding from Community Spaces the dynamic play space was installed with additional gym equipment and funding for facilitator support in 2012.

Figure 6. Looking East along a woodland edge.

8. Ecology

8.1 Existing Situation

8.1.1 Habitats within the Park The existing habitat structure, shown in Appendix 1 is extremely simple, as follows:

a) Trees and shrubs The park is well-endowed with six early-mature tree-belts following ditches or the park boundary. These were almost entirely planted c.1970s, the only older trees being several Ash along the southern boundary of the eastern (Merlin Walk) section. Species diversity is limited: Crack Willow and White Poplar clearly dominate with Italian Alder, Norway Maple, Cherry, Horse Chestnut and other exotics.

An amount of enrichment planting was recently performed with local volunteers, and there was some local bramble clearance.

The early-mature tree stock has few or no cavities suitable for hole-nesting birds or roosting bats, though some trees have ivy cover.

The under storey includes a range of native and exotic shrubs with stump or seedling regeneration of canopy species. Shrubs include Hazel, Field Maple, Holm Oak, Garden Privet, Hawthorn, Sloe, Elder, Portuguese Laurel. The structure is generally open but with dense Bramble thickets offering some nest cover to common birds e.g. Blackbird, Dunnock, Wren.

Ground-flora is largely absent, with few or no indicators of long-established woodland.

Throughout the park, but especially near the edges, incidental trees and shrub-beds, mostly of exotic species. Some which are poorly sited may now be removed without affecting the main woodland structure.

b) Amenity grass swards The majority of the grass area is a fertile, sown amenity sward of perennial rye-grass and white clover with few other herbs. Despite the steep topography and locally impeded drainage, there is no significant variation and no areas of botanical interest.

Several grass areas have been re-seeded, totaling 2600m2 sown with wild flower seed (Emorsgate mix EM1) in October 2007. A further 2400m2 expansion of the transitional areas between short amenity sward and the woodlands has been implemented during 2009 with the intention of reducing the fertility to allow for further native wildflower planting.

c) Water features In the western section, shallow ditches, now quite dry, follow the two tree- lines, converging at a small (3 x 10m) pond, little more than a sump at the ditch junction.

The pond now holds little water. No reason is known for this failure of supply. This typically occurs with development, when sewers replace former agricultural ditch systems. However, here, extensive grass slopes draining into the ditches should generate sufficient run-off to fill this small pond, at least in winter. Water abstraction by Poplars and Willows may be one explanation.

The pond until scraped out in October 2007 was dominated by emergent plants, chiefly a large Sedge. This will return, but in the meantime a range of wild flower species (500 plants) have been planted by local schoolchildren.

Below the pond, a deep ditch, flowing in parts but in stretches culverted, follows the woodland belt along the southern edge of the park.

Great crested newt: see 9.1.3c, below.

d) Soils

The Geological Survey shows the upper flanks of the park on chalky boulder- clay with Head (a glacial deposit) in the valley. The underlying Oxford clay is exposed in the easternmost part of the park. However, the entire park could be covered with imported topsoil, abundant during the development of Milton Keynes.

8.1.2 Surrounding habitats

The park is surrounded by mostly small houses and gardens with which it makes a very long (1800m) edge. Some houses directly front the park, whilst other boundaries have front or back gardens with fences, shrub or hedge planting.

On the east, plantation woodland along the V8 Marlborough St dual- carriageway almost touches the park. To the south, but beyond 200m of housing, is the wooded Peartree Lane. Both are designated Wildlife Corridors receiving some protection in the Milton Keynes Local Plan.

Eastward 250m, but across Marlborough St, extensive parkland follows the Grand Union Canal, also a designated as Wildlife Corridor.

8.1.3 Protected or notable species

Although not yet surveyed, the following animals may use the park or its surroundings. No protected plants occur in Milton Keynes.

a) Bats (all UK species and any roost sites protected) There are few or no potential roost-sites in the park, most trees being too young for suitable cavities. However the sheltered tree-lines and adjacent gardens should attract foraging bats, and surrounding houses could hold roosts of Pipistrelles and possibly Brown long-eareds. Two public “bat walks” were held, when Common Pipistrelles were seen foraging at scattered points.

A number of bat (and bird) boxes were made by volunteers and placed in trees.

b) Badger (animals and setts protected) and other mammals

Although setts (burrows) are unlikely, badgers are still in the area (evidenced by occasional roadkills on Marlborough St.) and could forage in the park.

Fox and Muntjac deer are likely to occur. Grey squirrel is abundant, and may suppress bird breeding.

c) Great Crested Newt (animals, ponds and surrounding terrestrial habitat protected)

A single juvenile was found beneath debris in June 2001. Around the pond, decayed timber revetments may offer some shelter for this and other amphibians. The pond is no longer considered viable for Great Crested Newt to breed. It could persist in nearby garden ponds, though none are known and they are generally poor habitat. Wood piles are being re-introduced as part of the woodland thinning process, currently ongoing.

d) Reptiles (protected against deliberate killing or injuring)

There is a small chance of grass snake or even common lizard, but suitable habitat hardly exists.

e) Breeding birds (nests, eggs and young protected)

Hedges and shrub-beds offer nest-sites for e.g. Blackbird, Dunnock, Wren. However most trees are too young to hold nest-holes and hole-nesters e.g. Tits or House sparrows are likely to depend on garden nest-boxes or buildings. Additional nesting boxes were installed in the park in 2008-9.

Grey squirrels, cats, crows (incl. Magpie) and possibly Great spotted woodpecker are likely to seriously depress breeding by other birds.

Several common birds are “Red” or “Amber”-listed by the conservation bodies due to rapid declines, or are priority species in Biodiversity Action Plans1. Those known or likely to occur here include House sparrow, Starling, Song thrush, Bullfinch, Dunnock and Green woodpecker.

f) Insects

The encapsulated hedgerows and ditches within the park along with the recently established wildflower meadows offer a diverse and beneficial environment. Minimisation of herbicide use to allow the growth of food sources for adult and larval stages (such as Stinging Nettles and Spear Thistles). Adjoining gardens offer a source of non-native food plants. Allowing dead wood to lie where it is safe to do so provides habitat for

1 UK Biodiversity Action Plan; Bucks & Milton Keynes Biodiversity Action Plan 2000 – 2010.

16 woodlice. Hollow stemmed plant species such as hogweed provide a refuge during winter months.

Additional native grassland replacement of 0.3ha added in 2008 has encouraged species of dragonfly and damselflies to the park. Further expansion of woodland transition areas in 2009, once fertility is reduced will provide further suitable habitat for wildflower planting.

8.1.4 Summary evaluation

The existing wildlife value of the park is LOW, and the potential only LOW- MODERATE for the following reasons:

• Woodland belts are narrow and heavily disturbed, with early-mature trees of planted and mainly exotic species. There is a particular lack of cavities for birds to nest or bats to roost. • Pond and ditches are of very limited extent and virtually dry. • Grass is extensively fertile perennial rye-grass sward of no botanic interest. 2600m2 was replaced with wildflower meadow in 2008 with additional transition areas added in spring 2009. • Pets and Grey squirrels are encouraged by nearby housing. • Public usage, e.g. for dog-walking or informal play, causes heavy disturbance.

More positively:

• Surrounding houses and gardens, may provide nesting, roosting or feeding for birds or bats, and nectar sources for insects, complementing habitats in the park. • The linked tree-belts may provide some food for birds and sheltered foraging or commuting corridors for bats. Complemented in 2008 with under planting of maturing woodland with diverse shrub layer species and occasional notable trees. • Support from Woughton Parish Council and Falconhurst School. • Existing deficiencies offer clear scope for enhancements with potential to engage local residents. • The community centre adjoining the park offers a base for activities. • The low baseline offers scope for enhancements with potential to engage local residents in surveys and planting. • The large number of residents immediately surrounding the park provides a pool of potential enthusiasts.

8.2 Proposals

Appendix 2 offers a realistic vision for wildlife enhancements which, if carefully carried out, will also have significant public benefits, creating a more diverse and naturalistic, but still “safe” experience.

Figure 7.

Meadowland Flowers in Eaglestone Local Park

(Clockwise from top Left)

Hedge Woundwort Ragged Robin Cut-leaved Cranesbill Forget-me-Not Ox-eye Daisy

Management changes

• Continue to diversify mowing regimes where possible. However, with the existing botanically poor sward, the benefits would be “structural” rather than visual or ecological, breaking up large expanses of grass, pulling together fragmented islands of planting and providing a transition at woodland “edges”. At least two cuts per year are required to prevent the fertile Perennial rye-grass sward looking merely unkempt. Further wildflower seeding or “pictorial meadows” are preferable.

Selective pollarding and thinning in woodland areas to diversify structure, remove some “leggy” or defective trees, open views and reduce shading along paths. Retain deadwood, stacked (where practicable) otherwise chipped. Begun during the winter of 2008, woodland thinning works and replanting undertaken with local volunteers

Continue with “herbicide minimisation”.

Coppicing (“stooling”) rather than profile pruning where shrub growth hems in paths.

8.3 Wildlife enhancements

Possible enhancements (with scope to engage local residents) include:

• Further seeding either of wild-flower meadows of wild bird food strips (e.g. sunflowers). See Appendix 2. Once the transition strips around the woodland have been established and fertility reduced, it is proposed to enhance them with plug planted native wildflowers.

• Bulb-planting, in grassland or woodland, has great social value and can be used to justify reduced mowing frequencies. Begun in 2007, this has now been expanded to over 100m2.

• Tree-planting to enrich existing belts with wildlife-friendly or attractive species. An ideal community event for National Tree Week. Undertaken during the 2008 National Tree Week with local volunteers, 200 were new trees planted within the woodlands.

• Planting wildlife-friendly (flowering or fruiting) shrubs, either native species along woodland edges, or exotics e.g. Buddlejas nearer houses. The existing shrub area to the North of Everglades was replanted in winter 2008-9 with forsythias and buddleja.

• Community orchard, offering fruit for wildlife as well as people. Appendix 2 identifies a possible site. However vandalism can be a problem and maintenance requirement is high. Some flowering crab apples were added as part of woodland enhancement work in winter 2008-9.

• Bird or bat boxes, made in the community. The park could absorb scores of these to compensate for the relatively young, cavity-free tree stock.

Over two dozen boxes were erected in 2008-10 following community workshops, with a further workshop undertaken in February 2011.

Figure 8. Bird and bat box event - Eaglestone Activity Centre.

• Bird-feeding and observation area. To be investigated further following the re-establishment of shrub areas planted in 2008. • Amphibian refuge construction, near the pond. • Restore water to the ditches and ponds. A longer-term project which, however, preliminary investigation suggests may be unfeasible.

Pond

As the pond does not retain a volume of open water is has been rapidly colonised by wetland plant species, notably sedges. By the introduction of a more diverse range in the autumn of 2007, this established during 2008 and it is hoped that this will quickly increase the wildlife value of the park and support a wider range of fauna. It will also enhance the aesthetic appeal as well as the educational potential of the park.

The intention is to provide a graded habitat running through trees, then on down to the shrub level and to wetland vegetation. Maintain a natural appearance, which will be enhanced over time as the area matures. Interpretation will be incorporated once re-establishment around the pond area has settled.

Trees

Disease of horse chestnut (Aesculus hippocastanum) is a potential issue as is the prospect of global warming for all trees in the park. Some thinning and formative pruning has been carried out over the past three years. Grass is to be left uncut under trees (not saplings) this prevents damage from machines and provides an important microhabitat for insects.

Trees are healthy at present but continued vigilance will need to be adhered to stop the spread of disease if detected. The Tree Survey in 2007 highlighted some remedial work to be carried out during the winter months which provided opportunities for planned enhancement of the tree cover (see Woodlands). This work was carried out during 2008. The 2008 Tree Survey (See Appendix 5) did not identify any further remedial action necessary to individual trees, however previously identified works were actioned (highlighted red on the survey). Following summer inspection it was agreed to remove a further line of trees from the north of Everglades to improve visibility and provide an opportunity to replant the shrubs. This was done with the support and input from Everglades residents.

A recent (2010) structural survey of properties in Down Dean, Everglades and Great Denson has highlighted issues allegedly caused as a result of root desiccation of the sub-soil. As a result of this survey, a plan is now in place to carry out replanting of a number of trees in this area following selective felling, coppicing and pollarding to reduce any associated risk. This is a further opportunity to undertake planting as desired in the woodland management plan above. Affected tree are indicated in Appendix 5.

Planting of specimen trees to provide a visual focal point and meeting point for the community will be a valuable event to involve local residents, there has been an indication from some residents to develop a community orchard either within or close to the park. Further discussions will be undertaken following a review of the 2010-11 user survey.

Woodlands

Beginning in 2008, woodland areas A-D, G-I and P (See Appendix 5) will be progressively rejuvenated with native and non-native species to provide the area with enhanced ecological and amenity value.

Each year asub-section of each woodland area will be thinned of poor standing timber, undesirable ground cover and weak growth. This will then be repopulated with more desirable species. By tackling each area a section at a time it will prevent excessive disturbance of the indigenous wildlife.

It is anticipated that the range of species once enhancement is complete should be a split of 80%-20% deciduous-evergreen and will provide a varied and visually stimulating experience. See Fig. 31.1 and 31.2.

Species will be chosen from but not limited to the list below, which contains a mix of native and non-native species of diverse form, colour and structure.

• Quercus • Cedrus • Thuja • Davidia • Sorbus • Malus

• Betula • Populus • Arbutus • Pinus • Tillia • Crataegus • Prunus

By protecting the less robust and slower growing species with under planting of thorny species we hope to prevent the need for visually intrusive protective fencing whilst the trees establish. During 2008 areas D and P were thinned to create the desired planting pockets and 216 new trees have been planted as part of National Tree Week with the help of local residents. Additional transitional areas of meadow were added for the 2009 season between the woodlands and amenity grass.

During Spring 2011 as part of the launch of the Milton Keynes “In Bloom” further planting was undertaken with trees supplied by the Woodland Trust.

Uniform Age of Stock

Monoculture Canopy

Poor Shrub Diversity No Meadow “Edge”

Figure 9.1 – Current Structure.

Canopy of Diverse Age and Species

Diverse Shrub Layer Habitat Rich Meadow Transition

Figure 9.2 –Enhanced Structure (10 years following establishment). Wildlife surveys suitable for volunteers

• Visual monitoring of bird & bat-boxes2. • Recording birds at feeding area or bird-seeded strip. A pretext for public bird-walks or popular “garden bird” surveys may provide a lead in. • Walking checks for bat roosts in adjacent housing and bat flight activity in the park (requires basic training and electronic bat detectors). Undertaken as a public event in July 2009, this found evidence of Pipistrelle activity. • Butterfly census to monitor benefits of wild-flower seeding and management changes (needs basic training).

Public events

The foregoing projects suggest a range of public events including: (those undertaken since 2007 are indicated √ )

• Bird and bat box making √ • Willow coppicing or willow weaving/sculpture√ • Tree or shrub planting √ • Hay-raking in wild-flower seeded areas instead of contract maintenance • Bulb-planting in grass or woodland √ • Bird feeding station construction • Amphibian refuge construction √ • Community orchard planting and aftercare • Bird walk or observation training √ • Bat walk or observation training √ • Bug or “minibeast” hunts √ (By Falconhurst School) • Trails, quizzes and games to include a wildlife element (as part of the Easter egg hunt)√ • Longer walks / cycling or “health walks” to include the canal and Woughton area √

9. Facility and Visitor Management

9.1 Health and safety All operations carried out at Eaglestone Local Park have been risk assessed (see Appendix 7) and are reviewed on a regular basis, whenever any operations or activities are planned. Details of contractor’s responsibilities are covered in the General Service Requirements which are available on request.

Notices alerting the public to areas of risk, such as deep water are routinely inspected. The issue of water safety has lead to detailed discussions with RoSPA and water safety packs are sent out to all neighbouring schools. The

2 Opening bat-boxes (once used) needs a Natural England licence for which substantial training is required. For bird-boxes in particular annual cleaning or maintenance is desirable. Both these activities require ladder work which may be unsuited to volunteers.

23 department also offers talks to schools on the issue of water safety throughout Milton Keynes. The pond area in the park does not retain a large volume of water and levels vary from under 30cm in winter to nil in summer.

9.2 Play Areas

Legend

DEAP Doorstep Equipped Area for Play >5 Items of equipment. (In line 60m walk > 5 minutes)

LEAP Local Equipped Area for Play <5 items of equipment. (In line 240m walk 5 minutes)

NEAP Neighbourhood Equipped Area for Play <8 items of equipment. (In line 600m walk 15 minutes)

Park Outline

Figure 10. Play area accessibility

The FIT (Fields in Trust, formally the NPFA) guidance The 6-acre Standard outlines the realistic catchment area of play areas based on the level of provision.

As can be seen in Fig. 12 the Local Area for Play (LEAP) represented by the green circles has a catchment area which covers much of the immediate area around the park. The Neighbourhood Area for play (NEAP) represented by the blue area covers a much greater distance.

Although it is unlikely children would access it from neighbouring estates on a casual basis, the play areas are connected by a Redway and footpaths, the major linking routes for pedestrians and cyclists in Milton Keynes. This gives the park a greater potential for use as a destination play area or as a stop off point on a recreational route as they are clearly marked on the city map.

The play areas in the park are subject to a weekly inspection to cleanse and inspect the operation of the equipment. All maintenance and cleansing staff (part of the MK Fix-It team) are trained to undertake these inspections and have followed a relevant course e.g. the ILAM Playground Inspecting and Reporting Course. Recent interventions by the councils continuous improvement unit has led to a change in working practices resulting in faster response times and a more cost efficient service.

The park has two play areas that provide for a range of abilities and ages. Improvements in the park have taken place in the last 5 years in partnership with the parish, school and the residents association. These have included

24 the replacement of one area and the repainting of one modular unit with the replacement of the safety surfacing from bark to “grass tiles” and the installation of the bespoke climbing wall “traverse” with associated grass tile safety surfacing.

Figure 11. Construction of the Climbing Wall Traverse.

An annual independent inspection is also carried out to ensure the council standard is maintained. In 2009 a more complete survey was commissioned to include play value of the range and quality of the equipment in addition to a brief development programme. The sites are considered to offer basic play value and to be in generally good condition. Recommendations have been followed where budget has allowed with future improvement projects are being planned with the input from local groups (subject to available funding). Copies of the inspection are in Appendix 3.

New play area signs have been produced using the MK Council branding guidelines with an anti-graffiti coating (Appendix 3). The signs display the general rules of play areas in Milton Keynes, using both words and symbols in a positive and non-prohibitive way.

Following extensive consultation with the community, a plan is now in place to provide an additional resource in the park suited to older (12+) children and adults comprising a more dynamic range of equipment and a multi location park gym. Phase one of this is now in place. Phase 2 was completed in the summer of 2012 (plan in Appendix 3).

9.3 Access Footpaths within the park are adopted as part of the highway network. They are inspected annually and repair or resurfacing is carried out where the surfacing falls below a set standard. Some areas of the park have received resurfacing works, notably to the south of Great Denson and along Merlin Walk, around the pond. Work continues on this project. A Disability Discrimination Assessment was carried out during 2008, finding the need for a suitable seat along Merlin Walk Redway. Following consultation on design and location, this was installed during early 2009.

9.4 Furniture Benches were one of the most requested improvements from the 2007-8 survey. As part of a drive to re-use and recycle materials where possible, seven benches were constructed using materials from tree thinning operations within the city. These have been located at strategic points around the park to provide perch or rest points at key locations. This is in addition to the bench installed to fulfil the requirements of the DDA inspection. Their condition is inspected regularly to asses how they are wearing with any remedial action being taken by the maintenance team. Other items such as fencing or the bridge structure are inspected by the area officer on an annual basis.

Figure 12. Bench constructed from recycled timber.

9.5 Community safety The public can contact Milton Keynes Council through the web page or the environmental services help desk number, both of these are widely advertised on council publicity, vehicles and signage. Council staff are often at the park, they can easily be identified through liveried vehicles and uniforms. This presence, although not formally used as a deterrent to antisocial behaviour, can have a positive effect on safety in the park.

The Parish Community Wardens patrol the parks on a regular basis and provide feedback from the community to the Park Supervisor. The Wardens play a key role in networking with local people, dealing with local environmental issues or acting as a conduit to other agencies. They are also additionally supported by the Police Community Support Officers (PCSOs) based at the parish offices in Netherfield, they patrol the park twice daily. Anti- social behaviour orders including drinking controls and dispersal orders have reduced the perceived level of crime and antisocial behaviour in the park. Events such as the Bat Walk encouraged people who would not normally use the park in the evening due to these perceived problems to get out into the park. The event passed without incident! The councils Environmental Enforcement Team can be called upon to issue penalties for actions that undermine park management, such as fly tipping and dog waste that can lead to a feeling of neglect and loss of security. They patrol regularly and educate dog owners about responsible ownership, providing free poop-scoop bags, information leaflets and installing signage.

10. Interpretation and Publicity At present there are several ways the Neighbourhood Management interpret Eaglestone Local Park. These are as follows:

10.1 Community survey During December 2007 and January 2008 Milton Keynes council conducted a series of consultations with differing demographic user groups to identify priorities and needs. This included the Eaglestone Residents Association, Falconhurst School, and Everglades sheltered housing complex. From this we were able to identify priorities for the park which are included within the Action Plan at the end of this document. The full results of the survey can be found in Appendix 4.

A further survey was undertaken in 2011 which provided information on current performance and future objectives.

10.2 Events Programme Neighbourhood Management provides events in the parks it manages for a variety of reasons:

• A way of communicating with public, what are their thoughts about the parks, what would they like to see? • A chance to put a face to a name and open up channels of communication. • A method to involve the public in the management of their parks, to start or encourage friends groups. • Broaden the knowledge or skills of the community in using parks. • Show the range of uses or activities that can take place in parks. • Strengthen and act as a focus for the community. • Provide a wide range of activities for different age groups. • Provide activities for the whole family. • Offer opportunities of leisure at low or no cost.

10.3 Notice Boards for public information: As a focus for visitors, informing them of current initiatives, issues and events in the park. It also allows for seasonal variations, interpretation of features, wildlife or particular plants to be highlighted. It is hoped that the local community will use the board to convey messages and therefore contribute to the parks function as a means of facilitation.

Environment

Eaglestone Local Park -Spring ½ Term Event

Bi rd b ox Maki ng 16th Feb ruary 10:00am-12noon Eaglestone Activity Centre

Come and construct birdbox kits for use by our feathered friends in Eaglestone local Park.

Or make one to take home for a small fee.

Children should be accompanied by a responsible adult, all equipment supplied.

www.milton-keynes.gov.uk/parks

For further details please contact: Landscape Services Helpline (01908) 252592

Landscape Services, Synergy Park, Ch esn ey Wol d , Bl eak Hal l , Milton Keynes MK6 1LY

Figure 13. A typical seasonal events poster.

10.4 Internet Articles are added to the Milton Keynes Council web site and the web address promoted in all other advertisement and promotion. Sections on the web page include descriptions of the park, “What’s on?” And who to contact if there are issues. http://www.milton-keynes.gov.uk/parks-and-open- space/displayarticle.asp?id=20697

10.5 Media Media coverage is sought for most high profile activities and events (see Appendix 6). Articles are written for the Parish newsletter, Residents Association Newsletter and events are advertised in the local newspapers (MK News and Citizen).

PR:135 FOR RELEASE: Immediately Pupils spring into action to bring colour to local park.

On Friday morning 2,000 white daffodils were planted by 50 pupils from Falconhurst School in Eaglestone Local Park.

For the 2nd year running the pupils and teachers joined with the Landscape Services staff from Milton Keynes Council to enjoy a morning learning how to plant the bulbs and look after the surrounding area.

The planting, by Year 5 and Year 6 pupils, is part of the ongoing development of the park and its application for a Green Flag Award, the national standard for parks and green spaces, which it hopes to gain in the coming year.

Maurice Barnes, Landscape Streetcare Officer, said: “By getting involved in the ongoing management and development of their local park, not only do the children achieve a sense of ownership of their local environment, it also serves to educate and inform them in the work required to manage quality public spaces. Their efforts on Friday will be seen for many years to come.”

Caroline Key, Deputy Head of Falconhurst School added: “The planting was a fantastic activity for the children. For many of them it was a new and very muddy experience and they are very much looking forward to seeing the results of their hard work in the spring.”

In addition to the bulbs being planted in Eaglestone park, pupils and teachers from Southwood School took part in the seeding of wild flowers in Conniburrow hoping to establish a wild flower meadow.

Continuing there efforts and as part of National Tree Week on the 29th November, there is a community planting day to enhance the diversity, habitat and look of the tree cover in Eaglestone Local Park. Meet in the park at 10am, all welcome.

- End -

Figure 14. Press release highlighting local involvement

10.6 Friends group The Eaglestone Residents Association forms the basis of our friends group, with input from the Youth club based at Eaglestone Activity Centre (now managed as a community business) and Woughton Community Council, Thames Valley Police and Falconhurst School. This allows for a more coordinated approach to managing the park and greater democracy. In time the group will bring additional benefits such as events run for the local community, greater awareness of issues and ownership of the park and as already realised, avenues to funding opportunities. Regular meetings take place between the interested parties to co-ordinate events, funding applications, initiatives and to take the park forward with the involvement of the community.

Figure 15. Pond Replanting with Local School

Pupils from Falconhurst School along with Neighbourhood Management and Woughton Community Council staff establishing a variety of native flora around the pond area following re-modelling work. This will provide a valuable habitat for invertebrates once established. Part of the wildflower meadow can be seen in the background shortly following seeding.

10.7 Marketing Events are set out at the start of each year following a review of the previous year’s take-up.

An events calendar is linked to an Event Delivery Plan for each event which details the responsible officer, requirements, partner organisations and delivery timeline (see Appendix 6)

To promote the park, Milton Keynes council Neighbourhood Management utilises the expertise of the council communications team to develop press

30 releases for print and broadcast media. Events are also promoted in house via the council’s parks website.

Notice boards at each of the parks offer an opportunity to advertise the events for the year ahead with more prominent posters nearer the event date.

Local schools are supplied with advertising materials for events to encourage participation, as are community centres, libraries, residents groups and sheltered housing sites.

Primary contacts for Eaglestone Local Park event promotion:

MKC Communications Team - LiveMK - Heart Radio - MK News - MK Citizen - MK Web MKC Parks website Woughton Parish council Eaglestone Residents Association Falconhurst School Previous Event Attendees (letter or e-mail)

Partner organisations also play a big part in delivering events and drawing in residents to Milton Keynes parks. These include:

BTCV (Now The Conservation Volunteers) MK Play Association MK Play Rangers MK Lions (Basketball) MK Dons (Football)

Partner organisations offer expertise and event experience as well as acting as a “draw” to encourage participation.

Griffin good as new after lick of paint.

From MK News – Sept 2007.

One of the city's famous pieces of urban artwork has been restored with a lick of paint.

The Griffin, in Eaglestone has been made as good as new as part of a pilot project called ARTiFACTS.

The project gives students and residents the chance to learn from professional conservators and artists the techniques and processes used to conserve aspects of Milton Keynes' cultural heritage.

The project covers some of the public sculptures in the city as well as environmental artworks and plantings managed by Milton Keynes Parks Trust.

ARTiFACTS project leader Justin Neal said: "Our cultural heritage collection is very important to us here in Milton Keynes. It's a collection going back over 30 years from the first concrete and play sculpture created by artists such as Liz Leyh and Bill Billings and Lesley Bonner in the 1970s.

"Famous pieces like the Concrete Cows at Bradwell, the Tin Man on Beanhill, and the Griffin on Eaglestone all form part of a social history of the city." The 12ft long and 6ft high Griffin was produced by city artist Lesley Bonner in 1983.

ARTiFACTS is a joint project between Milton Keynes Parks Trust, MK Council's Culture Team, MK Community Futures Group, thecentre:mk, students from MK College and Eaglestone residents.

Figure 16. Publicising Park Involvement (Public Art Restoration).

Figure 17. The Restored Griffin and (insert) before restoration.

11. Development of Eaglestone Local Park

Over the past 5 years, Eaglestone Local Park has undergone changes to improve the facilities, environment and community involvement. The sections below show how the park has developed in line with the Green Flag criteria. From this we have identified the parks Strengths, Weaknesses, Opportunities and Threats and how we can enhance the park for the future based on input from the community, partner organisations within a work delivery plan.

The process of preparing Eaglestone Local Park for Green Flag submission has enabled Neighbourhood Management to revisit working methods and standards. This has been hugely beneficial not only for the park and its present users but also for the department and the wider community.

The development of the park over the past five years was community led from the start. The grant application for the replacement of the play area adjacent to the Griffin statue rolled forward with the restoration of the Griffin, the establishment of the wildflower meadows and the involvement of the community in planning the way forward with the park user survey. This has led on to the replacement of the bridge by the pond, the introduction of seating and the climbing wall installation. Aesthetically, there have been rejuvenation of areas of shrub planting and woodland which will continue in future years with the input and help of volunteers. Education of and participation by the community has led to an increased feeling of local ownership in the park. Falconhurst School has been active in the use of the park as an educational resource and continues to play active role in the development of planting and in the consultation of younger residents. Most recently, they have been involved in the design of a new seating area to remove issues of congestion on the Redway in the afternoon by the school gates. Projects currently in the planning stage envisage the provision of an outdoor gym and adventurous play area for over 12’s as well as a feature bridge structure through the lower tree canopy in one area of woodland.

The range of improvements identified, both physical and developmental have been acted upon where budget and season have allowed. Other improvements and modifications to the structure and management of the park to enhance the facilities, opportunities for involvement and landscape have been also been identified as part of a continuous improvement programme in conjunction with consultation with local residents, the school and parish council.

• A Welcoming Place o Direction signs indicating the location of the park form the local centre as well as from Peartree Lane and Golden Drive. o Signs at major entrances to the park indicating facilities, ownership, who to contact and how. o Vehicular access restricted to council vehicles. o Benches installed through the park to provide rest spots (DDA compliant where required) as requested in the user survey. o Seasonal information displayed on the notice board. o New Play Area signage.

Strengths Weaknesses Signage in and to the park. Limited interpretation of ecological Central location within Eaglestone. benefits. Links to the Redway network. Walking route times and benefits. Access away from roads. DDA Assessed site.

Opportunities Threats Proximity to the Local Centre and Anti-social behaviour. School. New seating area adjacent to school gate.

Work Plan delivery:

Seasonal Information Who MKC Neighbourhood Management When Seasonally How Posters, fliers and local press (RA and Parish news) Outputs Information detailing seasonal activity

Biodiversity Interpretation Who Neighbourhood Management When 2012 How Provision of signage and seasonal information on species and lifecycles. Outputs Information detailing importance of habitats and lifecycles.

• Healthy, Safe and Secure o Provision of a modern, new play site for the under 10’s offering a wide play value in a limited space. o Redesign of planting along walkways and entrances to provide better sightlines and remove potential obstructions. o Footways resurfaced - ongoing. o Community Council provides free poop-scoop bags at the activity centre and dog bins within the park. o Replacement of walkway across pond. o Improvements to safer surfacing in play sites. o Night-time bat walks help to reduce perception of the site as a no-go area at night. o Provision of climbing wall as response to survey feedback.

Strengths Weaknesses Risk assessments undertaken. No full time on-site staff Modern play facilities regularly inspected. Dog fouling enforcement undertaken. Opportunities Threats Climbing wall interpretation to Anti-social behaviour. encourage use. Vandalism. Provision of water fountain. Fly-tipping of garden waste. Provision of fitness circuit. Incidents of dog fouling Closer ties to nearby hospital. Further education and enforcement on waste issues.

Work Plan delivery: Dog Fouling & Waste Education. Who MKC Environmental Services When Ongoing How On-site education and enforcement activity. Outputs Reduction in incidents of fouling

Footpath Reconstruction. (Appendix 12) Who MKC Neighbourhood Management When Ongoing – as budget allows. How Funding from Local Transport Plan Capital fund. Outputs Reconstruction and repair of park footways as surveyed.

Fitness Area and Water Fountain provision, Climbing Wall signage. Who Eaglestone Residents Association When Pending securing of funding source How Grant funding and match funding from Woughton Community Council. Outputs Provision of fitness trail and dynamic play through the park.

• Well Maintained and Clean o Provision of 3 new waste separating bins. o Restriction of herbicide use to hard surfaces only. o Footpath reconstruction underway. o Replanting of the area to the north of Everglades to open sightlines and improve planting.

Strengths Weaknesses Dog and litter/recycling bins in Footway degradation to be addressed. prominent locations. Brash chipped on-site and used as mulch. Timber re-used as benches or habitat piles. Opportunities Threats Education on waste and litter issues. Fly tipping of garden waste. Replanting of woodland areas to add Litter. colour and form.

Work Plan delivery: Seating area at rear of Falconhurst School Who MKC Neighbourhood Management When January 2011 How Installation of seating area and bike racks. Outputs Provide space for waiting parents off Redway.

Waste Education Programme Who MKC Neighbourhood Management / waste education. When Ongoing How Various communication programmes. Outputs Education on waste issues leading to a cleaner environment.

Community Orchard Who Residents Association When 2011-2015 How Funding bid to “The Big Tree Plant” scheme. Outputs Provision of community mixed fruit orchard.

• Sustainability o Waste timber used to make benches. o Small timber used to construct winter shelters (hibernacula) for fauna. o Development of transitional woodland edge meadows and perennial flower meadows. o Woodland tree stock thinned or coppiced and diversified with new planting – ongoing. o Drainage channels cleared of obstructions. o Replanted pond area. o Bird and bat box installation. o Updated “peat-free” statement from plant stock supplier.

Strengths Weaknesses Meadows establishing new habitat. Lack of diversity in woodlands.

Opportunities Threats Increase biodiversity in transitional Pressure from recreational use. meadows. Fly tipping. Community planting days. Interpretation walks. Community led species surveys.

Work Plan delivery: Woodlands Who MKC Neighbourhood Management When Ongoing thinning and replanting programme. How Revenue budgeted works for replanting based on tree survey. Woodland Trust free tree scheme as part of “In Bloom” 2011. Outputs Balanced diverse woodland with a range of species, form and habitat.

• Conservation and Heritage o Heritage walk to show how Eaglestone grew around the park. o Improvements to the management of the woodland areas and grassland. o Re-profiling of the pond with the replacement of the bridges. o Development of 5000m2 of perennial meadow. o Renovation of the “Griffin” statue.

Strengths Weaknesses “Griffin” is prominent popular local Slow take up of wildlife surveying by feature. users. Meadows providing an increase in Low diversity in transitional grassland. local biodiversity.

Opportunities Threats Interpretation of local ecology. Fly tipping. School use as outdoor classroom. Mass bulb planting for spring colour. Bird feeding stations. Plug planting wildflowers. Use of Griffin as focal point for activities.

Work Plan delivery: Meadow diversity Who MKC Neighbourhood Management When Ongoing How Increase in diverse broadleaved perennials though seeding and plug planting (as appropriate). Outputs Increase in plant biodiversity

Wildlife Surveys Who Community When Ongoing How Use of iSpot and other wildlife reporting methods Outputs Identify species indicators within the park.

Griffin Refresh Who Make A Difference When Competition Autumn 2010 – Painting Spring 2011 (Weather dependent) How Community Design competition and re-painting of “Griffin”. Outputs Community engagement in the Arts.

• Community Involvement o Involved Falconhurst School in projects such as play development, planting of bulbs and native flowers. o Developed links with the Residents Association, Activity Centre and Everglades Sheltered housing. o Identified opportunities for improvement through user survey. o Encouraged conservation activities with bird/bat box making and planting days. o Heritage Open Day walk to discover the development of Eaglestone. o Development of community led funding bids for additional recreational activities. o Summer fun days arranged by Woughton Community Council. o Regular opportunities to get feedback through the residents association.

Strengths Weaknesses Residents and youth group actively Low take up of volunteering involved in decision making. opportunities. Linked to local centre and pedestrian/cycle routes. Active and passive leisure activities. Opportunities Threats Follow up on 2008 survey to gauge Competition from other leisure activities. changes in use/perception or issues. Funding for future projects.

Work Plan delivery: User / Resident survey Who MKC Neighbourhood Management When Bi-annually How Through school and residents association. Outputs Identify needs, challenges, and issues and identify barriers to use.

• Marketing o Dedicated website for management information. o Event delivery procedure implemented. o Positive publicity gained through local media. o “What’s On” guide in local newspapers and on council website o Promotion of events through on site notices.

Strengths Weaknesses Access to a broad range of media. Officer time to organise events. Events organised with parish and resident involvement. Opportunities Threats Increase the range of activities Limited MKC budget to arrange events. available. Promote the park through the hospital.

Work Plan delivery: Community Events Who R.A., Woughton CC, MKC Neighbourhood Management When Ongoing How Community focused events as a response to need Outputs Community engagement in Bio-diversity, Recreation and Social networks.

• Management o Develop Green Flag management practices. o Closer working within the council to remove barriers between departments. o Restructuring of Environmental Services to an area based service.

Strengths Weaknesses Reorganisation of services to remove Specialist officer knowledge needs service silo barriers. development.

Opportunities Threats More customer focused service Reduction in revenue funding. provision. Cross-working, shadowing and knowledge sharing to increase officer skills.

Work Plan delivery: Neighbourhood Engagement Officer Development Who MKC Neighbourhood Management When Ongoing How In-house training Outputs Increase skill set of the officers.

Appendix 0

Introduction to Milton Keynes Council.

About Milton Keynes Council

Milton Keynes is situated 50miles from London, Oxford and Cambridge and 80miles from Birmingham. The council provides over two hundred services to more than 230,000 people in Britain’s fastest growing city and manages over 1200 hectares of Parks & Open Spaces.

As one of the key locations for growth in the United Kingdom Milton Keynes is set to grow further over the next thirty years, and probably beyond that. The new development will create 28,100 new homes in MK by 2011 and 71,000 dwellings by 2031 giving a projected population increase of approx 110,000. 4,500 of these homes will be in Central Milton Keynes.

This increase in development will generate: • A greater number of houses per hectare (higher density). • Regenerate existing areas of MK i.e. Wolverton and Bletchley. • Create new areas of sustainable living and working. • Bring enhanced public transport systems and interchanges.

Alongside the growth agenda, the Council has the important task of delivering quality services to the people of Milton Keynes.

We still have considerable challenges, not least from those services that are not yet above average. Not everybody has a universally positive experience using our services, and we can constantly improve. Making sure that growth brings real advantages, rather than under funded or overstretched services, remains a high priority.

Open Space Strategy.

The purpose of the Open Space Strategy for Milton Keynes is to guide the thinking and direction of open space provision, management, accessibility, integration and use over the next 10 years; whilst acknowledging that implementation will affect open space planning for at least the next 25 years as population of the Borough more than doubles from the 1991 census figure of 178,270 to over 380,000 residents.

The Vision for this Strategy is:

To achieve the best possible level of provision, integration and variety of accessible open space within the Borough of Milton Keynes to serve the needs of the growing Milton Keynes community, and ensure that open space is managed in a sustainable manner for future generations.

Achieving the Vision will require a holistic and co-ordinated approach to:

• Maximise the quality, performance and benefits of existing open spaces for the community.

• Increase the level of public access, awareness and usage of the Borough of Milton Keynes open space by 25% by 2014.

• Create and develop a framework for ensuring high quality, accessible, sustainable, and appropriately resourced open spaces that are an integral part of the Milton Keynes council area focusing on integrated planning for the existing rural and urban areas as well as the proposed growth areas.

• Ensure accountability at all levels for the development and management of open space and an active community involvement.

• Creating clean, safe, attractive, varied, welcoming and interesting open space environments.

Measuring Performance

Milton Keynes Council is independently inspected as part of the CAA (Comprehensive Area Assessment) and Communities and Local Government Place Survey, undertaken across all local authority areas.

Full details of Milton Keynes’ performance can be found on the Oneplace website at:

http://oneplace.direct.gov.uk

Related highlights from the 2008-9 Milton Keynes assessment include:

• Percentage of residents who have used parks and open spaces at any time within the last six months - In the top 5% nationally.

• Percentage of residents who have used parks and open spaces at any time within the last year. - In the top 5 councils nationally.

• N199 Children and young people's satisfaction with parks and play areas. - Above the national average.

• Percentage of residents who identify parks and open spaces as something important in making somewhere a good place to live. - In the top 5% nationally.

• Percentage of residents who think local public services are working to make the area cleaner and greener. - Above the national average.

• NI 197 Improved local biodiversity - proportion of local sites where positive conservation management has been or is being implemented. - Above the national average.

• NI 195a Improved street and environmental cleanliness - levels of litter. - In the best third nationally.

Neighbourhood Management

Neighbourhood Management manages over 1200 hectares (ha.) of parks and spaces (equivalent to 1800 football pitches). This includes 550 play areas, 880ha of grass, 110ha of shrubs, 110,000 trees and 60ha of woodland.

Parks and open spaces provide individual, community, environmental and economic benefits for all ages and abilities. We aim to maximise these benefits for the community by maintaining

1. Attractive open spaces that encourage pride in locality.

2. Functional parks & open spaces that provide opportunities for recreation, exercise, community events, conservation and

3. Sustainable parks and open spaces for current & future generations in a modern growing city to enhance their quality of life, health and well-being by promoting a healthy lifestyle and absorbing pollution.

Environmental Services

Neighbourhood Management “The vision for more cost effective and flexible services”

Neighbourhood Management provides localised neighbourhood management and service delivery, working closely with local bodies to meet locally determined priorities to improve quality of life.

Neighbourhood Managers will be responsible for liaising with members, communities, other agencies and stakeholders, to determine how local needs, preferences and priorities are addressed.

Each of the Neighbourhood Managers, as well as being responsible for their Neighbourhood Management Team, will be responsible for a cross cutting service area:

A reactive task force carrying out repairs and maintenance to the streets, Fix-it MK play areas and illuminated furniture. Creating an attractive environment whilst managing, developing and Landscape protecting the expanse of open space and countryside in Milton Keynes. Delivering highway and general street maintenance to our highway Highways network. Cohesion & Dealing with our statutory obligations associated with environmental crime, Partnerships anti social behaviour and other community issues. Delivering the statutorily cleaning function and engaging communities in My Street MK the delivery of this. Enable the Directorate to bring together key communications messages and to ensure Parish Councils and CMK also have a consistent approach Communications to messages. Neighbourhood Management will bring together the local community and service providers at a neighbourhood level to tackle problems through influencing mainstream service provision.

What are the key benefits?

Physical improvement to the environment

People feeling safer and safety is the first priority

Improved communications with a single point of contact

Smarter ways of working

Consistent approach to working with partners

Medium – long term: greater efficiencies will result

Communities will have a say in local priorities

Our Service Standards

We will:

1. Manage and inspect parks and open spaces on a programmed basis, against national standards, to ensure that they are clean, well maintained, healthy, safe and secure places for all members of the public to use.

2. Maintain parks & open spaces, to available resources, using environmentally sound methods, relying on best practices available according to current knowledge.

3. Conserve natural features, flora and fauna and structural features of merit.

4. Encourage the involvement of members’ of the community, who represent as many green space users as possible, in the service.

5. Assess parks and open spaces to ensure equal access for all members of the community.

6. Provide information on and promote parks and open spaces as a community resource.

7. Respond to all emergency situations, e.g. fallen branches, damaged play equipment, within 24 hours.

8. Answer all telephone calls within 5 rings (helpline).

9. Answer all correspondence within 10 working days. Where detailed investigation is necessary we will acknowledge your letter within this timescale and respond in detail as soon as possible.

Environmental sustainability Milton Keynes is an expanding area and is increasingly having to meet the challenges of this. The Local Plan for Development is a continually reviewed strategy which sets out Milton Keynes aims for the continued expansion for the borough. http://www.milton- keynes.gov.uk/local%5Fplan%5Freview/DisplayArticle.asp?ID=29610

To combat the excesses of poor development a number of strategies and partnerships have been developed, which include:

• Milton Keynes Environmental Partnership The partnership is made up of key players in the area with a necessarily broad theme. These encompass issues of environmental protection and pollution, planning and design, energy and climate change. It also impacts on key issues developed in the Community Strategy and MK Local Agenda 21. • Milton Keynes Local Agenda 21 Strategy

Following the UN Conference on Environment and Development (“Earth Summit”) held in Rio in 1992 Agenda 21 was endorsed and this document sets out how we can work towards sustainable development. In 2002 Milton Keynes Council made a positive commitment to establishing a working party to work towards the goals of Agenda 21 with the production of, Milton Keynes Local Agenda 21 Strategy. http://www.miltonkeynes.gov.uk/mklowcarbonliving/

• Herbicides

The use of herbicides is kept to a minimum. Alternative methods of weed control are employed wherever possible (see “Weed Control”). However in some circumstances such as hard surface areas in play areas the removal of algae, moss and some weeds through the use of herbicide or algaecide is required to maintain safety standards.

• Pesticide use

The policy with regard to pesticides is contained in the General Service Requirements.

The Operations team record all use of pesticide within the park and copies of records are retained by both the contractor and council for forty years for the purposes of exposure and health monitoring.

• Horticultural peat

Horticultural peat is not used at all by Milton Keynes Council or on any land controlled by them. The majority of our plants are supplied bare rooted. All suppliers of plant materials must certify that any container grown stock is grown stock is grown in peat free media. We do not purchase ericaceous species which must be grown in peat as these plants are not suitable for the soils in Milton Keynes. Our plant supplier’s policy on peat usage is included in their environmental statement at the end of this document.

• Waste plant material

All waste plant material produced is re-used through the creation of habitat piles, mulching, off-site composting or temporary path maintainace.

• Climate change impacts: The council recognises the impact of climate change throughout its operations; recent strategy has included the zero emission strategy for new homes. The strategy includes the design of planting to shelter properties to ameliorate the impact of high summer temperatures and cooling winter winds.

• Vehicles The council is changing the vehicle fleet to reduce carbon emissions; so far there are 21 LPG (Liquefied Petroleum Gas) powered vehicles and all new vehicles are selected for low emissions. Programmed maintenance to manufacturers’ guidelines optimises the efficiency of the fleet. Waste oils and fluids from vehicles and machines are collected and returned to the supplier for re-processing.

Milton Keynes is part of a national pilot, called Plugged in Places. This will see the installation of charging bays, beginning in Central Milton Keynes, paving the way for the introduction of electric vehicles.

• Street Lighting Milton Keynes council has since 2003 sourced 100% of its electricity needs for streetlights from renewable sources (Scottish Hydro). The council is currently rolling out across the borough new, low energy lighting columns which consume less power, have greater longevity and cause less light pollution. It is also possible to monitor the condition and change the luminescence of these lights remotely to gain further efficiency savings. http://www.milton-keynes.gov.uk/street_lighting/home.asp?r=11576

Depots and Offices All council buildings are now provided with electrical power from a minimum of 88% renewable sources. http://www.milton-keynes.gov.uk/sustainable-living/documents/SIP4.doc

The landscape department appreciates that global warming will have a profound effect on how it manages the open space. One area that appears to be having an effect already is the warmer winters that allow for pest species to survive and/or increase in number. This has in particular impacted on tree species, to combat this; trials of resistant species planting are being undertaken.

Works on a wider strategy to deal with the impacts of global warming are underway throughout the council.

Environmental Sustainability Measures in Eaglestone Local Park

Within this park we:

• Use no herbicide except for weed control within hard surfaces. All beds are hand weeded and edging to hard surfaces is carried out manually. Play area safety surfaces are pressure washed (where applicable) to remove moss and algae. • Bring no plants onto site which are grown in horticultural peat. Wherever possible, bare rooted plants are specified. • Send all meadow arisings to the main borough composting site in nearby Haversham which also processes household garden waste. • Reuse other waste plant materials on site by chipping/mulching. Larger tree surgery arisings are left in situ as habitat piles. Where it is impractical or unsafe to do this the arisings are left in the woodland areas along the brook and behind the pond.

Over: Environmental Statement from our landscape contractors’ preferred nursery stock supplier.

55 Appendix 1

Eaglestone Local Park Plan

Appendix 3 – Eaglestone Local Park Play Areas

Play Area Signage.

This signage replaces the previously used design to incorporate a less prohibitive message (removing the red slashed circles) whilst promoting a responsible attitude to play area use. The sign is also in line with the councils corporate branding guidelines.

Proposed Fitness and Dynamic Play Area

iii Name of Play Area: Local Park - North End (EAGL 20)

Date: 30/7/09 Inspector: IM

General Comments

The play area is a local sized facility, sited in a park.

Weather: Sunny Time of Inspection: 12:52

Design

The play area has been designed for children aged 2+.

The following have been inspected and found to be in good order:

Orientation Minimum Space Design Age Traffic (Movement) Clashes

Ancillary Items

The following have been inspected and found to be in good order:

Access/Pathways – Bitmac Fencing – Bow Top General Surfacing - Wetpour Planting Ownership/Information Sign Access/Maintenance Gates Litter Bin

Work required: Install a seat. (Comment- Seating incorporated into retaining wall,additional benches provided)

Equipment

(1) Basket Swing

Lappset The item meets the requirements of BSEN 1176 where this may be tested on site without dismantling or destruction. The item is in good condition and no work is required at this time.

Surfacing Wetpour The surfacing meets the dimensional requirements of BSEN 1176.

(2) Multi-Play Unit

Lappset The item meets the requirements of BSEN 1176 where this may be tested on site without dismantling or destruction. The item is in good condition and no work is required at this time.

Surfacing Wetpour The surfacing meets the dimensional requirements of BSEN 1176.

(3) Spring Seesaw

Lappset The item meets the requirements of BSEN 1176 where this may be tested on site without dismantling or destruction. The item is in good condition and no work is required at this time.

Surfacing Wetpour The surfacing meets the dimensional requirements of BSEN 1176.

(4) 4 Seat Rocker

Lappset The item fails to meet the requirements of BSEN 1176 in the following respect: One hand grip missing from the item – replace.

Surfacing Wetpour The surfacing meets the dimensional requirements of BSEN 1176.

(5) Bridge

Lappset The item meets the requirements of BSEN 1176 where this may be tested on site without dismantling or destruction. The item is in good condition and no work is required at this time.

Surfacing Bark The surfacing meets the dimensional requirements of BSEN 1176.

(6) MUGA

Base The item fails to meet the requirements of EN 15312 in the following respect: Damage evident to the mesh fencing and loose panels – repair.

Surfacing Bitmac Trip hazards at entrance – PCC edging to surrounding bitmac – improve levels. Risk Assessment

Ancillary Items and Environment /Other Hazards

Ancillary Item Risk Score Comment Action or Control Fencing 6 See Report Access/Maintenance 2 See Report Gates Planting 2 See Report Access/Pathways 2 See Report Cleanliness 2 See Report General Surfacing 2 See Report Litter Bin 2 See Report Ownership/Information 2 See Report Sign

Environmental/ Risk Score Comment Action or Control Other Hazards Minimum Space 2 See Report Traffic (Movement) 2 See Report Clashes Design Defects 2 See Report Adjacent Roads 2 See Report Informal Supervision 6 See Report

Equipment

No. Equipment Item Surfacing Risk Score Action, Control or Comment 1 Basket Swing Wetpour 6 See Report 2 Junior Multi-Play Unit Wetpour 6 See Report 3 Spring Seesaw Wetpour 4 See Report 4 4 Seat Rocker Wetpour 6 See Report 5 Bridge Bark 4 6 MUGA Bitmac 8 See Report

THE ASSESSED LEVEL OF RISK FOR THE PLAYGROUND AT THE TIME OF THE INSPECTION IS – MEDIUM. ______

2009 Milton Keynes BC Yes/No Comments/Description Play Area Evaluation

North Ridge (Front of 11)

Type: LEAP

Local Plan compliant in terms of type, area, distance from dwellings and basic content

Context /Suitability: High Density (Urban) Medium Density (Urban) X Low Density (Urban) Sub-Urban Rural

Constraints : Covenants, TPO, Unknown easements, reserved site

Physical Quality Score out of 5 All site installations and equipment 5 well maintained Soft and/or hard landscape well 5 maintained High quality setting - hard and soft 3 landscape and features/equipment Play value to intended level - 3 existing interest Scope and opportunities for 3 improvement Serviceable lifespan in years of >10 (5) existing site Is site quality capable of economic 3 improvement Total Score: 27/35

Inherent Qualities Score out Positive Scores of 5 Favourable aspect, light, open and 2 good visibility Does the play area have natural 5 shade Good relationship with built 5 environment and local dwellings Good level of surveillance from 5 adjacent dwellings and paths Total Score: 17/20

Inherent Defects Score out Negative scores of 5 Poor, out-dated or inappropriate 1 design Poor quality of build or now 1 deemed economically unserviceable Poor maintenance or not 1 maintainable to appropriate standard, Poor / inappropriate relationship 1 with local dwellings

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Is there evidence of crime, 1 vandalism and/or significant misuse Total Score: 5/25

Usage/Performance How well does the play area / site serve its intended area :- Immediate area [LAP/LEAP] Yes Neighbourhood [LEAP/NEAP] No Wider area [NEAP] No Is the play area part of a larger No public open space. Does the play area cater for Yes intended ages group [ LAP<6 - LEAP<8/9 - NEAP<12/13 ] Does the site provide significant or Significant adequate play value in accordance with type Do site constraints mitigate against No continued use as a viable play area

Accessibility /Security Is the site DDA / Access for All Yes compliant [surfaces, gradients, path widths] To what extent is equipment DDA Partially compliant Is there good access/connectivity Yes with the locality and to other play facilities Is there good access for all within Yes the wider site Are public routes to the site Yes overlooked / good surveillance

Local Public Views Discussion / questioning must be structured and focused to enable comparative evaluation Is the play area valued by local Unknown people Is there a significant difference of Unknown opinion locally on the value of the play area What is the local Town/ Parish Unknown council view

Opportunities Does the site have unused play Yes potential or capacity for significant improvement Is the location, size, access and No capacity suitable for consideration as a Strategic Neighbourhood Play Area. (SNPA) Is the site providing or Yes

viii economically able to provide a significant play opportunity for its locality Can access be improved : [a] A easily; [b] with some difficulty; [c] with great difficulty [d] cannot be improved

Possible Alternative Uses [For further consider on completion of wider area evaluations, for sites lacking the capacity for reasonable level of a play service delivery or not capable of significant improvement]

______

DEVELOPMENT PROGRAMME

Initial Views

The play area is a local sized facility, sited on an open space. It provides good play value and activity.

DEVELOPMENT PROGRAMME

Initial Views

The play area is a local sized facility, sited in a park. It provides good play value and activity.

Long Term Proposals

Monitor, maintain and inspect.

Ensure any future development of the site in terms of equipment, ancillaries and access embraces the ethos of the DDA and allows accessibility for all.

Cost Implications (Ballpark Figures)

Low to medium.

Milton Keynes BC Comments: Seating incorporated in retaining wall around play area. MUGA not part of this facility.

Trip hazard on access will be addressed by 15th January 2010.

Appendix 4 Eaglestone Local Park User Survey. 2007-08 & 2010-11(Partial)

During autumn and winter 2007-08 Milton Keynes council undertook an exercise in engaging the local community in the development of the local park.

This took the form of a short questionnaire base on the BVPI questions used in the 2006 survey but going further into assessing the views of the users on topics which have been high on the list of priorities for residents from informal discussion.

The sample was taken form local residents attending the association meeting, residents of the Everglade sheltered housing unit and a class year 6 children at Falconhurst School. Where we have responded to opinions highlighted in the survey the details are included below.

The survey has been repeated during December 2010 and January 2011, included below is detail on how the perception and impression of the park has altered during this time. Some questionnaires were still to be included at January 27th 2011.

Q.1 How often do you visit the park?

The majority of respondents were daily or weekly users, reinforcing the parks use as a thoroughfare with good access from all parts of the estate.

2011 – Majority are still regular users, increase in daily use respondents.

Drop in usage frequency indicated by maturing younger respondents from the school finding other diversionary activities.

Q.2 Why do you visit the park?

Respondents were clear that the main reasons for visiting the park were for play, dog walking, relaxation, exercise and wildlife.

2011 – Dog walking and play are the key activities, renovated Griffin play area has been a popular improvement.

Q.3 What attracts you to the Park?

The range of answers highlights the high level of responses from younger people. Respondents are attracted to the park as a place for play, relaxation, wildlife and exercise.

2011 – Attraction of the renovated Griffin statue has increased visitor focus on the arts. “Play” and “Fun” opportunities are also key.

Q.4 How satisfied are you with the park as a whole?

The vast majority were either satisfied or very satisfied with the overall condition of the park.

2011 – Overall satisfaction has improved.

Q.5 How satisfied are you with the cleanliness of the park (Litter)?

Although levels of littering on the site are low, respondents felt that there was a need for more provision of litter bins and enforcement.

2011 – Increase in bin provision (3 recycling bins) at key littering points has begun to improve perception of littering as an issue.

Q.6 How satisfied are you with the cleanliness of the park (dog fouling)?

The park is well provisioned with dog waste bins (4 in total), however there is still a perception that owners are not being responsible for their dogs.

2011 – Dog fouling issues have been addressed with regular enforcement and education activities. Perceptions of an issue in the park may be as a result of a recent “Dog poo fairy” campaign to encourage continued improvement.

Q.7 How satisfied are you with personal safety?

From the responses we received, the majority of users feel safe within the park. From informal questioning, this is due to being overlooked by private residences, open pathways and good lighting. Those who were unsatisfied stated a perceived fear of crime.

2011 – Feelings over personal safety in the park have improved.

Q.8 How satisfied are you with the condition of the footpaths?

Respondents stated that the paths were on occasion uneven and have stated that leaves and detritus have made some paths slippery.

2011 – Path improvements have made an impact on satisfaction in the park.

Q.9 How satisfied are you with the condition of the planting?

From the information received, respondents were satisfied with the planting provided within the park. Professional observation however has concluded that this could be sympathetically developed to provide a more ecologically beneficial site with grater aesthetic appeal. Modifications to the planting have taken place during the winter of 2008.

2011 – Alterations and rejuvenation of the planting has inevitably led to some immaturity in the planting which is reflected in a slight decrease in planting satisfaction.

Q.10 How satisfied are you with the maintenance of play areas?

Satisfaction in the maintenance of play areas is high which reflects well on current management practices. Recent development of the play facilities has been well received locally.

2011- Satisfaction with play area management remains good.

Q.11 Have you attended an event?

Event attendance from survey respondents outside of the schools was low; this is possibly due to timing of the events during weekdays. Events planned for 2008 onwards are focusing more on school holidays, weekends and evenings. As a result attendance figures were up on the previous year although poor weather did affect attendance at the bird watching walks and tree week events.

2011 – Responses were received from a number of event goers.

Q.12 Suggestions for improvements…

Residents felt there was a need for improved seating and litter control as a priority. Seating is to be addressed with the installation of informal seating options within the park utilising reclaimed timber from forestry operations within the city. These will take the form of shaped and contoured limbs, trunks and stumps. Following the DDA audit in 2008, a compliant seat was installed for 2009. There was a desire for the installation of a climbing wall within the park which was installed during July 2008. From the school, there was a request for a tree house and play road area. Trees within the park were not considered suitable for such a structure; however this may form part of future play provision such as an elevated shelter as part of a scheme for older children. Play track / road options are limited for this site due to the proximity to properties and land contours. Some provision may be possible within the courts of the activity centre to the north of the park. From Everglade sheltered housing complex, there was a request for bird feeding stations, this would tie in with rejuvenation planting within the planting to the north of that site, possibly as an event for the autumn to construct feeders. This is now planned for autumn 2009 following the rejuvenation of the planting in 2008. Further suggestions such as the teen area / tree house, picnic area, water fountain and goals will need further local consultation on location and design with the residents association and parish.

2011 – The focus on a healthier lifestyle has focused a desire for a water fountain in the park. This will be investigated as part of the proposal for exercise improvements. Family use for barbeques and picnics can

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additionally be looked into as part of further consultation. The popularity of community events on the site has indicated a desire for “more of the same”.

What was the best improvement?

Play and the griffin were highlighted as the biggest improvements in the park over the last 3 years.

Other comments received from the 2011 survey:

“It’s a pleasant place to come across, a joy.”

“Always clean and good for small children.”

“It looks like a botanical garden.”

“It’s a lot better than before and I feel more involved in the environment.”

“The trees are like a forest.”

“The Griffin makes it special.”

“…if you go there it just makes me special.”

“It’s a fun place to make new friends”.

“Every kid that plays there has fun.”

“There are lots of friendly people.”

Eaglestone Local Park Community Survey

How Often Do You Use Eaglestone Local Park?

Daily Weekly Monthly 6Months Year Never 2008 17 13 3 3 3 11 2011 14 5 6 7 3 5

How Often Do you use Eaglestone Local How Often Do You Use Eaglestone Local Park 2008? Park 2011?

Daily Daily Weekly Weekly Monthly Monthly 6Months 6Months Year Year Nev er Nev er

Never- Why? 2008 2011 Poor mobility 2 Use changed in last 3 years (2011)? Nothing for the elderly 1 About the same 16 Poor Sight 1 Visit more 9 Play area is for Visit less 14 babies 1 No Response 1 Too busy 2 Live out of area 3 1 Too far 1 Not colourful 1 getting boring 1 No response 3

Why do you visit the park?

Play Dog No Areas walking Wildlife Sports Relaxation Exercise Other Socialise Transit Response 2008 19 13 12 3 14 16 1 1 3 2011 22 6 3 3 3 5 1 3 1

Why do you visit the park 2008?

Play Areas

Dog w alking

Wildlife Sports Relax ation

Exercise Other Socialise

Why do you visit the park 2011?

Play Areas Dog w alking Wildlife Sports Relax ation Exercise Other

Socialise

Transit

What attracts you to the park? 20 2008 2011 Play 19 10 Wildlife 8 18 Friends 3 2 Green 3 2 16 walking 3 Trees 2 2 fields 2 14 Space 2 1 Art 2 8 12 Quiet 1 Unspoilt 1 2008 10 Commuting 1 2011 No roads 1 Safety 1 1 8 Local 1 2 Family activity 1 6 Convenient 1 realxing 1 Clean 3 4 Pleasant place 1 Fun 5 2 Its special 3

0 y e rt t t g n ife en c A iet l g ds n e l ds e lds in ivity en Fu Pla lking e a t ni lxi ild en Gr a Trees fi Qu ut Safety Local e Clean W Spa m t plac Fri w Unspoi nv rea special No ro o an Its Com C Family ac Pleas

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How Satisfied are you with… The Park as a whole?

Very No Unsatisfied Unsatisfied Satisfied Very Satisfied response 2008 2 5 26 12 4 2011 1 3 22 13 1

How satisfied are you...with the park as a whole?

30 25

20 2008 15 2011 10 5

0 Very Unsatisfied Satisfied Very No Unsatisfied Satisfied response

How satisfied are you… With the cleanliness of the park (Litter)?

Very Very No Unsatisfied Unsatisfied Satisfied Satisfied Response 2008 10 19 15 2 2 2011 9 14 13 3 1

How satisfied are you...with the cleanliness of the park (Litter)?

15 2008 10 2011 5

fied fied fied fied is tis is tis sa sponse nsat n Sat U y Sa Re U r o ry Ve N Ve

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How satisfied are you… With the cleanliness of the park (Dog fouling)?

Very No Very Unsatisfied Unsatisfied Satisfied Satisfied Response 2008 9 15 15 6 4 2011 8 17 13 1

How satisfied are you...With the cleanliness of the park (Dog fouling)?

18 16 14 12 10 8 6 4 2 0

Very Unsatisfied Satisfied Very No Response Unsatisfied Satisfied

How satisfied are you… Personal safety?

Very No Very Unsatisfied Unsatisfied Satisfied Satisfied Response 2008 19 17 9 3 2011 4 5 18 13

How satisfied are you with...Personal Safety?

20 18 16 14 12 10 8 6 4 2 0 Very Unsatisfied Satisfied Very Satisfied No Response Unsatisfied

How satisfied are you… With the condition of the footpaths?

Very No Very Unsatisfied Unsatisfied Satisfied Satisfied Response 2008 8 19 13 8 1 2011 7 3 14 8 7

How satisfied are you with...the condition of the footpaths?

20 18 16 14 12 2008 10 8 2011 6 4 2 0 Very Unsatisfied Satisfied Very Satisfied No Response Unsatisfied

How satisfied are you… With the condition of the planted areas?

Very Very No Unsatisfied Unsatisfied Satisfied Satisfied Response 2008 1 5 21 19 4 2011 10 18 5 7

How satisfied are you with...The condition of the planted areas?

25 20 15 2008

10 2011 5 0

d ied ie ied sf sfied onse i tisf isf sat sp nsati n Sa U U o Re Very Sat N Very

How satisfied are you… With the maintenance of the play areas?

Very Very No Unsatisfied Unsatisfied Satisfied Satisfied Response 2008 2 8 17 16 7 2011 2 1 25 4 8

How satisfied are you with.. the maintenance of

the play areas?

30 25

20 2008 15 2011 10

5 0

Very Unsatisfied Satisfied Very No

Unsatisfied Satisfied Response

Have you attended an event? 2008 2011 Bulb planting 9 6 Wetland Planting 6 2 At work 1 Bat Walk 6 Paint Griffin 1 Play Assoc. 6 Bird/Bat boxes 1 Tidy up day 1 Flag Raising 1 No 16 12 no response 18 9

20 18 16 14 12 10 8 6 4 2 0 g g k lk c. s ay g o tin tin or iffin e d in N w is t Wa Gr a lan t box p Plan A y Asso a R lb d Bat aint a dy up P Ti ag Bu Pl Fl no response Bird/B Wetlan xi

What is the biggest improvement made to the park What could we have done better? in the last 3 years? Nothing 2 2011 Exercise machines 2 Play Area 18 reduce stinging nettles 1 Griffin 7 make more secure 2 No response 5 Table Tennis 1 Bridge/Pond 3 Water Fountain 1 Don’t Know 3 Re-paint griffin 2 Plants 2 Keep an eye on it 1 Events 2 More play facilities 3 Bulbs 2 More colour 1 Signage 1 More interesting 1 Green Flag 1 less litter 1 Benches 1 no dogs 1 Bat Boxes 1 General change 1

What is the biggest improvement made in the park in the last 3 years?

10 2011

a s s e se w t b ag s g e n o n l l e n n a a Griffin /Pond K Pl Bu nch h ay Ar spo e Events en F e c l Signage re B P Bat Boxes ral Don’t G e No re Bridg n e G

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Suggested Improvements

18 16

12 2008 10 2011 8

6 4

0 l . l t s r b y a t y t g s t e p e t g k e a n s s s s a a r s d t k h e s m s s n s a c n i e t i h a e t s c g e i i n i t u n s t n b m e e a e l r n n c c z e n i e a l s i l n i l r A g k i n o n t r u u o n e e i t a o u r t l r r i t n i a i l s i l l o W r i o n p o a e l a n q t n d i t e B u a a P a ic n p a r o u o b a t o A n C ic n s p t v t w o a r o g a h p b e l i r s n w c M t c E c e p a e / t u r n d t S a e g t a n H c s l T t n Q l e p s e A T i i o l e g b a D C d o e o S i a e g d S S t e io o n P t k n e m d e n / a t i B u t d n y B n i l n b F i n t a t n i p Z g r s h t a c b i N s g n i D i i t a u g e r a r a B P e a B n F b e r m o r i t L u S n l n o i e c r i n e s / i a B a r u a T o l r i P e o p i l t l e p b t r T t r l c u H i o c d o S c h P e M p e C y a a a x i x Y e e F i g l h m H a n e e S l n c e i t E e W c a m g / P e o i L W S l F g n o a i s i e o P o l a d s C r r T g o i D T o a F B e D m S i r T

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Appendix 5: Eaglestone Local Park Tree Survey 2011

Inspected MK East Jan 2011 Girth - cm Height - m Area No. Street Location Species Girth/Height Nos. Faults Management Prescription Eaglestone Sectional clearance of Pk Woodland A Ivy bramble/scrub and replant Eaglestone Sectional clearance of Pk Woodland B bramble/scrub and replant. Eaglestone Sectional clearance of Pk Woodland C Ivy bramble/scrub and replant

Eaglestone Pk Woodland D OK Ivy Woodland E Removed Eaglestone Pk Woodland F OK Cavity in Ash trunk Eaglestone Pk Woodland G OK Eaglestone Sectional clearance of Pk Woodland H bramble/scrub and replant Eaglestone Sectional clearance of Pk Woodland I Willow bramble/scrub and replant Eaglestone Pk Woodland J OK Eaglestone Pk Woodland K OK Large Willows to be pollarded, poor Eaglestone formed Chestnuts, and Willow to be Pk Woodland L OK removed.

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Eaglestone Pk Woodland M OK Eaglestone Pk Woodland N OK Eaglestone Pk Woodland O Eaglestone Sectional clearance of Pk Woodland P bramble/scrub and replant Eaglestone Pk Woodland Q Thin Eaglestone Pk Woodland R OK Eaglestone Pk Woodland S OK 1x decay in Cherry Eaglestone Pk Woodland T OK Eaglestone Pk From Merlin Walk 1 Cherry 30/8 1 removed Eaglestone Pk From Merlin Walk 2 Cherry 20/4 1 Dead poplar Felled Eaglestone Pk From Merlin Walk 3 Ash 35/12 1 Eaglestone Pk From Merlin Walk 4 Cherry 30/9 1 Eaglestone Pk From Merlin Walk 5 Cherry 30/9 1 Eaglestone Pk From Merlin Walk 6 Ash 30/12 1 Eaglestone Pk From Merlin Walk 7 Ash 30/13 1 Eaglestone Pk From Merlin Walk 8 Ash 30/14 1 Eaglestone Pk From Merlin Walk 9 Ash 30/15 1

Eaglestone Pk From Merlin Walk 10 Ash 30/16 1 Eaglestone Pk From Merlin Walk 11 Cherry 20/4 1 Scars Eaglestone Pk From Merlin Walk 12 Ash 40/12 1 Eaglestone Pk From Merlin Walk 13 Alder 20/6 1 Eaglestone Pk From Merlin Walk 14 Willow 50/14 1 Eaglestone Pk From Merlin Walk 15 Maple 30/10 1 Growing towards house Eaglestone Pk From Merlin Walk 15a Alder 30/10 1 Eaglestone Pk From Merlin Walk 16 Alder 50/14 1 Eaglestone Pk From Merlin Walk 16a Maple 50/12 1 Eaglestone Pk From Merlin Walk 16b Birch 30/15 1 Eaglestone Pk From Merlin Walk 17 Thorn 25/4 1 Eaglestone Pk By pond 18 Ash 60/16 1 Eaglestone Pk By pond 19 Willow 30/16 1 Eaglestone Pk By pond 20 Willow 30/14 1 By pond 20a Willow 30/14 1 By pond 20b Willow 30/14 1 By pond 20c Willow 30/14 1 By pond 20d Willow 30/14 1 By pond 20e Willow 30/14 1 Eaglestone Kite Hill 21 Acer 30/8 1 Scars

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Pk Eaglestone Pk Kite Hill 21a Maple 30/8 1 Bark damage Felled Eaglestone Pk Kite Hill 21b Willow 40/10 1 Eaglestone Pk Kite Hill 21c Willow 40/10 1 Eaglestone Pk By play area 22 Cherry 30/10 1 Base damage Eaglestone Pk By play area 23 Willow 35/9 1 Old pollard Eaglestone Pk By play area 24 Willow 40/16 1 Eaglestone Pk By play area 25 Cherry 25/7 1 Felled - Dead Eaglestone Pk By play area 26 Horse Chest 30/10 1 Eaglestone Pk By play area 27 Willow 30/14 1 Eaglestone Pk By play area 28 Willow 55/16 1 Eaglestone Pk By play area 29 Willow 30/14 1 Eaglestone Pk By play area 30 Willow 30/14 1 Eaglestone Pk By play area 31 Willow 60/18 1 Base damage Eaglestone Pk By play area 32 Willow 55/18 1 Eaglestone Pk By play area 33 Cherry 25/6 1 Rot in base Eaglestone Pk By play area 34 Willow 60/18 1 Eaglestone Pk Rear Condor Close 35 Acer 30/9 1

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Eaglestone Pk Rear Condor Close 36 Acer 30/9 1 Eaglestone Pk Rear Condor Close 37 Acer 30/9 1 Eaglestone Pk Rear Condor Close 38 Sorbus 20/5 1 Rot In trunk Felled Eaglestone Pk Rear Condor Close 39 Ash 30/8 1 Eaglestone Pk Rear Condor Close 40 Ash 25/7 1 Eaglestone Pk Rear Condor Close 41 Ash 30/8 1 Eaglestone Pk Rear Condor Close 42 Sorbus 20/5 1 Eaglestone Pk Rear Great Denson 43 Oak 15/5 1 Eaglestone Pk Rear Great Denson 44 Oak 15/5 1 Eaglestone Pk Rear Great Denson 45 Alder 20/7 1 Eaglestone Pk Rear Great Denson 46 Alder 10/4 1 Eaglestone Pk Rear Great Denson 47 Alder 15/4 1 Eaglestone Pk Rear Great Denson 48 Cherry 20/4 1 Eaglestone Pk Rear Great Denson 49 Birch 20/7 1 Eaglestone Pk Rear Great Denson 50 Alder 20/6 1 Eaglestone Pk Rear Great Denson 51 Willow 90/20 1 Pollarded to 5m, to be re-pollarded Eaglestone Pk Rear Great Denson 52 Horse Chest 25/7 1 Eaglestone Rear Great Denson 53 Horse Chest 25/7 1 Ripped Limb Tidy

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Pk Eaglestone Pk Rear Great Denson 54 Horse Chest 25/7 1 Eaglestone Pk Rear Great Denson 55 Willow 70/20 1 Hanging Limb To be pollarded Eaglestone Pk Rear Great Denson 56 Horse Chest 25/7 1 Scars & rot Felled Eaglestone Pk Rear Great Denson 57 Willow 100/20 1 To be pollarded Eaglestone Pk Rear Great Denson 58 Willow 90/20 1 Hanging Limb To be pollarded Eaglestone Pk Rear Great Denson 59 Horse Chest 30/7 1 Eaglestone Pk Rear Great Denson 60 Horse Chest 30/7 1 Eaglestone Pk Rear Great Denson 61 Willow 60/20 1 Split trunk Felled Eaglestone Pk Rear Great Denson 62 Willow 30/20 1 To be removed Eaglestone Pk Rear Great Denson 63 Horse Chest 20/6 1 Eaglestone Pk Rear Great Denson 64 Willow 45/20 1 Eaglestone Pk Rear Great Denson 65 Horse Chest 30/9 1 Felled Eaglestone Pk Rear Great Denson 66 Willow 45/20 1 coppiced Eaglestone Pk Rear Great Denson 67 Horse Chest 25/8 1 Eaglestone Pk Rear Great Denson 68 Willow 60/20 1 To be removed Eaglestone Pk Rear Great Denson 69 Willow 70/20 1 To be pollarded Eaglestone Pk Rear Great Denson 70 Willow 70/20 1 To be pollarded

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Eaglestone Pk Rear Great Denson 71 Willow 25/16 1 To be removed Eaglestone Pk Rear Great Denson 72 Willow 45/20 1 To be removed Eaglestone Pk Rear Great Denson 73 Horse Chest 30/12 1 Eaglestone Pk Rear Great Denson 74 Horse Chest 25/7 1 Eaglestone Pk Rear Great Denson 75 Willow 30/16 1 To be removed Eaglestone Pk Rear Great Denson 76 Horse Chest 30/12 1 Eaglestone Pk Rear Great Denson 77 Willow 50/20 1 To be removed Eaglestone Pk Rear Great Denson 78 Horse Chest 25/7 1 Eaglestone Pk Rear Great Denson 79 Horse Chest 25/9 1 Eaglestone Pk Rear Great Denson 80 Horse Chest 25/9 1 Eaglestone Pk Rear Great Denson 81 Horse Chest 25/9 1 Eaglestone Pk Rear Great Denson 82 Horse Chest 25/9 1 Eaglestone Pk Rear Great Denson 83 Willow 25/935/14 1 To be removed Eaglestone Pk Rear Great Denson 84 Willow 160/20 1 To be pollarded Eaglestone Pk Rear Great Denson 85 Cherry 35/9 1 Eaglestone Pk Rear Great Denson 86 Cherry 35/9 1 Eaglestone Pk Rear Great Denson 87 Cherry 25/8 1 Eaglestone Rear Great Denson 88 Alder 20/6 1 Felled

Pk Eaglestone Pk Rear Great Denson 89 Alder 20/6 1 Felled Eaglestone Pk Rear Great Denson 90 Birch 25/9 1 Eaglestone Pk Rear Great Denson 91 Alder 15/5 1 Felled Eaglestone Pk Rear Great Denson 92 Alder 15/6 1 Eaglestone Pk Rear Broad Dean 93 Cherry 40/8 1 Rot in base Eaglestone Pk Rear Broad Dean 94 Acer 40/8 1 Rot in base Eaglestone Pk Rear Broad Dean 95 Cherry 40/8 1 Rot in base Eaglestone Pk Rear Broad Dean 96 Cherry 65/8 1 Rot In trunk Eaglestone Pk Rear of Everglade 97 Willow 140/25 1 Eaglestone Pk Rear of Everglade 98 Willow 40/15 1 Dead crown Felled Eaglestone Pk Rear of Everglade 99 Willow 40/18 1 Eaglestone Pk Rear of Everglade 100 Willow 40/25 1 Eaglestone Pk Rear of Everglade 101 Willow 60/20 1 Eaglestone Pk Rear of Everglade 102 Willow 60/20 1 Eaglestone Pk Rear of Everglade 103 Willow 60/20 1 Eaglestone Pk Rear of Everglade 104 Acer 20/10 1 Eaglestone Pk Rear of Everglade 105 Poplar 25/12 1

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Eaglestone Pk Rear of Everglade 106 Willow 50/20 1 Eaglestone Pk Rear of Everglade 107 Willow 35/18 1 Dead Felled Eaglestone Pk Rear of Everglade 108 Willow 50/20 1 Eaglestone Pk Rear of Everglade 109 Poplar 35/20 1 Eaglestone Pk Rear of Everglade 110 Poplar 25/14 1 Eaglestone Pk Rear of Everglade 111 Willow 35/20 1 Eaglestone Pk Rear of Everglade 112 Willow 50/20 1 Eaglestone Pk Rear of Everglade 113 Willow 35/20 1 Eaglestone Pk Rear of Everglade 114 Willow 60/20 1 Eaglestone Pk Rear of Everglade 115 Willow 60/20 1 Eaglestone Removed for new seating area Jan Pk By Ball Courts 116 Acer 25/7 1 Bark damage 2011 Eaglestone Removed for new seating area Jan Pk By Ball Courts 117 Acer 25/7 1 2011 Eaglestone Pk By Ball Courts 118 Acer 25/7 1 Eaglestone Pk By Ball Courts 119 Accacia 25/8 1 Eaglestone Pk By Ball Courts 120 Accacia 45/11 1 Dead wood Felled Eaglestone Pk By Ball Courts 121 Alder 30/11 1 Eaglestone Pk By Ball Courts 122 Alder 30/11 1

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Eaglestone Pk By Ball Courts 123 Alder 30/11 1 Eaglestone Pk By Ball Courts 124 Accacia 45/10 1 Dead wood Eaglestone Pk By Ball Courts 125 Sorbus 15/4 1 Rot In trunk Felled Eaglestone Pk By Ball Courts 126 Acer 35/12 1 Eaglestone Pk By Ball Courts 127 Acer 40/12 1 Eaglestone Pk By Woodland T 128 Acer 35/12 1 ` Eaglestone Pk By Woodland T 129 Acer 30/12 1 Eaglestone Pk By Woodland T 130 Acer 35/12 1 Eaglestone Pk By Woodland T 131 Sorbus 15/5 1 Eaglestone Pk By Woodland T 132 Sorbus 15/5 1 Felled -Weak Eaglestone Pk By Woodland T 133 Sorbus 15/5 1 Eaglestone Pk By Woodland T 134 Sorbus 15/5 1 Eaglestone Pk By Woodland T 135 Sorbus 15/5 1 Eaglestone Pk By Woodland T 136 Sorbus 15/5 1 Eaglestone Pk By Woodland T 137 Horse Chest 35/10 1 Eaglestone Pk By Woodland T 138 Horse Chest 40/11 1 Eaglestone Pk By Woodland T 139 Horse Chest 35/10 1 Bark damage Fell. Eaglestone By Woodland T 140 Horse Chest 35/10 1

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Pk Eaglestone Pk By Woodland T 141 Alder 35/10 1 Rot In trunk Eaglestone Pk By Woodland T 142 Acer 35/10 1 Eaglestone Pk By Woodland T 143 Acer 25/10 1 Eaglestone Pk By Woodland T 144 Acer 35/10 1 Eaglestone Pk By Woodland T 145 Accacia 25/10 1 Felled Eaglestone Pk By Woodland T 146 Horse Chest 25/9 1 Eaglestone Pk By Woodland T 147 Cherry 25/9 1 Eaglestone Pk By Woodland T 148 Thorn 15/5 1 Coppiced Eaglestone Pk By Woodland T 149 Birch 15/7 1 Coppiced Eaglestone Pk By Woodland T 150 Thorn 25/8 1 Eaglestone Pk By Woodland T 151 Thorn 25/6 1 Eaglestone Pk By Woodland T 152 Birch 15/6 1 Overhanging gardens Coppiced to hedge winter 07 Eaglestone Pk By Woodland T 153 Thorn 25/6 1 Eaglestone Pk By Woodland T 154 Thorn 25/6 1

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Appendix 6: Events at Eaglestone Local Park 2007-12

10-13th September 2007 ARTiFACTS restoration of Griffin public artwork.

18th October 2007 Bulb planting with Falconhurst School (Years 2-3) 120 Children over 3 hours in groups of 20. Two staff from Falconhurst School, Two Streetcare staff.

9th November 2007 Bulb and Wildflower planting with Falconhurst School and local residents. 120 Children (years 5-6) in groups of 20 over 3 hours. No residents attended. Two staff from Falconhurst School, Three Streetcare staff plus one parish warden.

13th December 2007 Residents Association consultation evening (Eaglestone Activity Centre). 41 residents attended with 2 councillors over three hours (evening event). One Streetcare officer.

3rd January 2008 Everglade Sheltered housing complex consultation morning. 8 residents attended over 1 hour, one Streetcare officer.

15th January 2008 Falconhurst School, consultation with year 6 pupils on park development.

24th January 2008 Residents association meeting highlighting suggestions from survey and development opportunities.

21st February 2008 Living Willow Art and Bird / Bat Box Making (Eaglestone Activity Centre and Local Park). Attendance of 12 residents.

21st March 2008 Easter Egg Hunt. Wildlife quiz, puzzles and games around the park. 12 Attendees.

22nd March 2008 No Eagles…but Songbirds Aplenty – Bird watching walk in Eaglestone local park.

10th June 2008 Youth group development meeting for future projects.

26th June 2008Residents association meeting – Update on progress of Green Flag application and future development opportunities.

2nd July 2008

Everglades Coffee Morning – discussion of use and future opportunities in Eaglestone Local Park.

17th July 2008 Bat Walk through Eaglestone Local Park to Peartree Bridge and the Grand Union Canal. – 20 residents attended.

4th August 2008 Eaglestone Community Clean-Up Day. 20 attendees, plus assistance from TVP, Probation Service, cleansing and Safer Communities Unit.

7th August Everyday Activity bike ride

21st August Everyday Activity bike ride

4th September Everyday Activity bike ride

13th September 2008 Heritage Open Day – Tour of the area highlighting how Eaglestone was developed. Play Association also attended. 43 Residents attended.

18th September Everyday Activity bike ride

25th September 2008 Residents Association meeting – Ongoing development update.

2nd October. Everyday Activity bike ride

23rd October 2008 Residents Association meeting – Ongoing development update.

14th November 2008 Spring bulb planting with Falconhurst School.

25th November 2008 Senior Youth group meeting to develop proposals and engage with prospective users.

29th November 2008 Tree Council - National Tree Week planting event – 3 attendees.

19th February 2009 Bird and Bat box making. 23 Attendees. (Eaglestone Activity Centre).

10th July 2009

Bat Watching Walk – Summer evening walk with bat detectors and ecologist – 18 attendees.

September 2009 Bird Feeder making – 10 attendees (Eaglestone Activity Centre)

February 2010 Bird and Bat box making. 15 Attendees. (Eaglestone Activity Centre).

March 2011 Britain in Bloom Launch event with Falconhurst School

April 2011 Woughton Community Council Easter Activities

May-August 2011 Streetgames sessions (Wednesday evenings) 18 sessions.

July 2011 Make a Difference repaint Griffin with Falconhurst School

August 2011 Consultation on Phase 2 of dynamic play area

September 2011 Bat Walk (With use of QR Codes on advertising posters to link to Bat sounds)

November 2011 Tree planting with Eaglestone Pre-School (30 trees donated by Sainsbury’s)

August 2012 Opening of Dynamic Play space (Phase 2). – Eaglestone Olympics. Doggy PitStop (Advice and information session). Summer Activity Sessions

December 2012 Consultation event to discuss future development plans.

(Planned play sessions earlier in the year cancelled due to dynamic play installation, later sessions cancelled due to poor ground conditions/weather).

Planned for 2013

Activity sessions Pond Tidy –Up Doggy Pit Stop Gym Sessions

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Environment

Eaglestone Local Park

– Summer Event

Bat Walk

th 10 July 2009

9:15pm‐11pm

Join officers of the Landscape and Countryside section on this informative walk through Chepstow Local Park. Meet by the Flagpole.

Bat detectors will be provided.

Children should be accompanied by a responsible adult, please do not bring torches.

www.milton‐keynes.gov.uk/parks

For further details please contact: Landscape Services Helpline (01908) 252592

Landscape Services, Synergy Park,

Chesney Wold, Bleak Hall, Milton Keynes MK6 1LY vi

Event Delivery Plan

Date: Time: Title: Risk Assessment

Marketing Lead Officer Participant Register Reserve Officer(s) Pictures

Partners (Agencies or individuals, inc. contact details)

Timeline Who Task Due

Budget

Requirements (Tools, Display, Materials, Forms).

Planned Outcome:

Notes:

What was Achieved? Nos. Adults -

Nos. Children -

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Eaglestone Local Park.

DDA Assessment

Date: 4/11/2008

Assessor: Christine Jeckley

The park was traversed by a wheelchair user, no obstructions were found to wheelchair use.

Some minor undulations were found in the path surfacing, there is evidence of resurfacing of some path sections.

The bridge structure over pond area is not fully compliant. Access is available around pond on both sides.

Play areas are accessible by wheelchair users.

Installed seating provides some rest opportunities but its design does not offer back or arm support.

Reccomendations:

Addition of compliant seating. – (Installed January 2009)

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Appendix 9 - Local Plan Framework

Appendix 10 Landscape Management Framework Examples of how the service is Service What you can expect delivered Pruning, mowing, weed control Healthy trees, shrubs and uniform and mulching of shrub beds. Parks and Management cover of grass Open of vegetation Hedge laying Spaces Conservation of remnant vegetation. Annual tree inspections. Britain in Bloom entry

Clean, attractive and interesting Tree and shrub planting. landscape setting. Design and construction of park Diverse horticultural and play improvements features. Provision and Inspection and reporting of litter maintenance of Linear and variable scale planting. for cleansing landscape settings Simple functional landscape. Street trees. Green corridors

Informal, semi natural landscape. Native tree planting

Formal setting for organised sport Replacement of ageing planting

Line marking of pitches

Protection and Control of more vigorous species. Diverse planting that encourages enhancement wildlife of biodiversity Management Plan Shredding of prunings and mulching of beds. Maintenance practices that minimise Protection and pollution and are sustainable. Monitoring herbicide usage. enhancement of environment. Tree planting to absorb pollutants. Woodland belt, street trees.

Tree Preservation Orders Park signs Information available from Milton Provision of People Keynes Council on parks and open Internet website information spaces, their benefits and operations Leaflets Barriers to vehicles Absence of inappropriate uses

Regulation of Monitoring by Area Supervisors Control of illegal dumping. use Reporting of illegal activities to Control of encroachment police Intimate scale settings for passive Provision and maintenance of Provision and use by workers and shoppers. seating, paths, playground maintenance of equipment, water features and opportunities Large open spaces for community vegetation. for informal events and recreation by families, recreation social groups and individuals. Bonfire night firework displays.

Opportunities for outdoor exercise Eg 'Folk on the Green, music and socialising. festival’

Opportunities for safe play by children.

Opportunities for supervising adults to relax in outdoor setting.

Everyday use by people for walking, cycling, jogging etc Opportunities to observe flora and Provision of fauna. Maintenance of woodland, ponds opportunities and their access.

for natural Diverse environment. discovery Website, leaflets Information on biodiversity. Access audits.

Provision of Maintenance of paths. Easy cycle, pedestrian and disabled open space for person movement along footpaths access and and roads. Encroachment pruning. movement Overhanging vegetation notices issued to offending properties Provision of opportunities Playing surfaces suitable for Maintenance of football pitches,

for organised organised sport goal posts etc sport An accessible Management Plan Management that describes sites specifies Management Preparation of management plans planning objectives, issues and future work programmes. Community consultation on levels of Customer enquiry handling. service, management plans. Customer and Customer surveys. community Community gardens. involvement Facilitation and support for Gardens competition. 'Community Gardens'.

A system that ensures long-term Condition surveys. Asset maintenance and replacement of site

management features (shrubs, trees, benches, bridges, pergolas, play equipment). Annual tree inspections

Commissioning Maintenance agreements that Maintenance contracts and of maintenance achieve best value. specifications. services

Monitoring of Site inspections. Maintenance done to specified maintenance quality and on time. services Work schedules No unsafe working practices. Health Site visits to ensure compliance and with health and safety Safety Maintain safe environment, tree requirements. Risk assessments stock.

Appendix 11 Management Specifications

Management of the park is carried out as per the contract specification; the full contract is available on request. All relevant details for day-to-day operations are included; both the full contract and the designated Council Neighbourhood Engagement officer will need to be consulted on an ad hoc basis.

Although these specifications cover normal foreseeable aspects of maintenance, there are occasions when extra works need to be instigated such as clearing away fallen trees after high winds. A dayworks record is filled in and issued to the maintenance team. Usually hours are agreed with the Supervisor in advance. Relevant pricing details are recorded and when work is completed the Supervisor will sign the sheet to indicate satisfactory completion of the works.

Introduction

The following management prescriptions have been ascribed after careful consideration of the data from the flora and fauna surveys, physical factors and the needs of the park visitors. Vegetation types can be seen on the management plan in Appendix 1.

The proposals take into account the relative importance of recreational needs and those of nature conservation and attempt to attain a good balance in accordance with the management objectives.

The following section is composed of a list of habitat and recreation management tasks, which describe:

1 The area of which management is required. 2 The type of management to be carried out. 3 The time in the year at which management should be carried out. 4 The equipment required.

Prescriptions for the main landscape / habitat types in the park are shown in the following sections and can be referred to on the site plan in Appendix 1. Timings for the maintenance of differing landscape types through the year can be found in the annual programme (Appendix 8).

Where method modification is required to facilitate landscape improvements training is carried out by in house specialists or those with prior experience with the method required or though outside agencies such NPTC. For example, our contractors’ operatives have been trained in traditional hedge laying techniques by an outside specialist.

Litter Collection, Graffiti, Fly Posting and Fly Tipping. Co-ordinated by Milton Keynes council Cleansing Department, these operations are managed under service level agreements.

Litter - The site is litter picked on a weekly cycle in summer and every two weeks in winter. Any recyclable waste is separated out and processed at the materials recycling facility. Bins are emptied each day during the working week. The location of bins is regularly

monitored and adjusted as necessary. The council is in the process of rolling out separated bins for waste and recyclables. Cleansing also operates the sweeper service on highways and redways to remove surface detritus on a four week schedule. Play areas are litter picked on a weekly basis at the same time as a safety check. Incidents of glass litter or hypodermic needles are responded to on an emergency call out basis. Monitored under NI 195a-b.

Graffiti – Graffiti is removed from the site on an annual cycle. Any incidents of offensive graffiti of a sexual or racist nature are removed within 24 hours. Monitored under NI 195c.

Fly Posting – Removed as and where reported. Where possible, offenders are pursued by our enforcement team and several prosecutions have taken place. Monitored under NI 195c.

Fly Tipping – Removed as and when reported with 10 working days. Again, enforcement action may be taken where the offender can be identified. The council has had several successful prosecutions. Monitored under NI 196.

Dog Waste Bins

These are provided and managed by the local parish. Bins are emptied weekly. Dog waste causing a hazard within the park is responded to by the council’s cleansing department on a rapid response basis within 2 hours and as part of the litter picking cycle.

13.1 Play Areas

The play area inspections are mandatory and have to be recorded; these are carried out once a week. Inspections are recorded on small hand held PDAs. At the end of each day they are downloaded and work allocated, this also allows for records to be stored and accessed more conveniently. Any emergency work is phoned straight to the maintenance team from the inspectors / cleaners.

Once per year, each play area is inspected by a certified organisation such as The Royal Society for the Prevention of Accidents (RoSPA) and The National Playing Fields Association (NPFA). The results are recorded electronically by them and sent to us on a CD ROM.

Example inspection reports are included as Appendix 4.

Location Plan of Grassland

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15. Grassland As stated in the primary objective grass can have an important effect on how the park is conceived. Areas bordering sections of woodland or groups of trees are cut twice yearly (See Appendix 1 & 2) to grade in a naturalistic manner. These transition areas have the potential to offer significant biodiversity potential over that of single habitat type. A similar treatment is allowed for pond margins and areas away from high usage.

15.1 Present state Areas of short rotation or formal grass are in good condition. Twice yearly areas have been recently introduced along with a suitably varied, native sourced, wildflower mix. Establishment is ongoing to harmonize with the woodland areas and add variety. Transitional areas between woodlands and the amenity sward were established in 2009 with the intention to colonise with wildflower plugs.

15.2 Desired state Twice yearly mown areas to have greater species diversity provide greater visual amenity and ecological value. Amenity sward areas should have good coverage and allow for informal sport and play. Grass areas shall be maintained to the desired number of cuts or target growth limits.

15.3 Management required Continue with present regime on amenity swards. Continued cut and collect on meadow areas will reduce soil fertility over time and favour less competitive herb species. Introduction of wildflower species has been carried out but further planting may be of benefit. Alternatively a chain harrow and reseeding could be tried if the former prescription has no effect. Mowing around woodland areas has been “relaxed” to allow a more naturalistic aspect and provide a transition between amenity grassland and woodland. It is intended to spot plant these areas with wildflowers.

Where there are spring bulb plantings within amenity grassland, these are not mown until 6 weeks after flowering to allow regeneration of the storage organ for the following year. Close mown amenity grassland to be monitored for wear where it is used for informal sports use and renovated as required.

15.4 Calendar Amenity grassland areas 12 times a year, meadow areas twice a year with path cut through where necessary.

15.5 Equipment Grassland is mown, where terrain allows, with ride on cylinder type cut machine, otherwise with rotary machine or in the case of meadow areas with flail machines, strimmers and rakes.

15.6 Performance Defects (What we look for) • Grass growth impeding the safe and appropriate recreational uses of parks and open spaces and creating an unsightly appearance to open space users. • Grass cuttings left in piles or on hard surfaces. • Grass cutting in excessively inclement weather damaging surface through rutting. • Grass cut to incorrect height. • Uneven cutting. • Litter cut up by grass cutting operations.

Figure 21. Categories of grass area and required management

Open Space Standards Type Height of cut No cuts. (Approx. Compulsory Intervention Level period cut.) Public Open 25mm 12 cuts/annum (3 Space, & week cycle) Highway verges Amenity 18mm 25mm grass Drainage 100mm As directed ditches + embankment Local Wildlife Unless For this purpose, Exception: where there are hard Site ponds & otherwise where water level edges or “public access point” is watercourses specified, an fluctuates (as in most shown on plans, mowing shall be unmown ponds), the “edge” is closer if required to give public fringe min. the upper (winter) access to or views of the water. 2m wide shall level, as revealed by be left around distinctive wetland ponds and vegetation (e.g. along sedges or rushes) watercourses and mowing shall be . no closer to than 2m to that edge.

Local Wildlife Where shown on the drawings, the Contractor shall leave an unmown strip Site hedge & 2.0m wide along hedges or woodland edges. woodland When directed by the SO, the Contractor shall mow this strip to a height of edges 150mm and remove arisings. This operation shall normally take place in September of each year. Arisings shall be normally be disposed within the LWS where directed by the SO. Local Wildlife Where shown on the drawings, the Contractor shall leave meadow areas Site unmown until directed to top them by the SO. Meadows When directed by the SO, the Contractor shall mow the area to a height of 150mm and remove arisings. This operation shall normally take place between July and September of each year. Where possible this operation shall take place during daytime and in dry weather when amphibians are least likely to be present. Arisings shall normally be removed from site unless otherwise directed by the SO.

Rotation CUT ROTATION GRASSLAND TO 100mm AS DIRECTED AND REMOVE ARISINGS grass land On each occasion of mowing, the Contractor shall cut up to 30% of the area. The parcels to be cut and the commencement of cutting are wholly at the discretion of the Landscape Services Manager. Not more than two weeks after completion of mowing, arisings shall be removed by raking and disposed on site (normally within 200m) as directed. Rotation-mown areas may be rough or steep, and the material to be mown and removed may include bramble or re-growth from stumps cut previously.

16. EDGING Present Edging maintains a neat appearance to the periphery of grass areas and adjacent planted beds. It prevents damage by the vegetation to the adjacent hard surface and allows safe transit along footpaths. Herbicide reduction has taken place in recent years to remove the requirement to utilise pesticides between grass and shrub beds. Manual control by hoeing or strimming being more favoured.

16.1 Desired state Edges cut on same day as grass cutting and the growth is consistent with adjacent grass areas. Grass does not encroach onto footpaths.

16.2 Calendar

LOCATION EDGING Grass edges to The hard surface shall be cleared of all soil and vegetation overlap. The hard surfaces. cutting back and control shall be undertaken once per year during the periods January- March and October-December. Grass edges to Growth shall be maintained up to the periphery of the shrubs to the shrub beds. lengths specified on the adjacent grassed area. It shall be carried out on the same day as the grass cutting. Grass edges to The Contractor shall maintain edging in a sharp, tightly cut, neat and formal borders. vertical condition with all arisings removed off site. It shall be carried out on the same day as the adjacent grass cutting. Grass edges to The Contractor shall leave a strip as directed by the supervising officer Woodland. adjacent to the woodland as a buffer zone to be cut twice annually in April and September.

16.3 Equipment

LOCATION TYPE OF METHOD OF CONTROL GROWTH Grass/Hard Grass growth Herbicide application surface. through tarmac

Grass/Hard Grass only Strimming or chemical. Chemical application must not surface. overlap: encroach more than 50mm into the grass. Grass/Hard Soil and grass Cut back using approved equipment, such as a spinning surface. overlap: disc cutter, and remove arisings from site.

Grass/ Grass Strimming of the edge shall precede grass mowing so Shrub bed. that the mowing machine removes any clippings. Where plants overlap grass border edges growth shall be maintained to allow free passage to mowing machines. Grass/Formal Grass A line is to be used in order to ensure a true straight line border. is maintained. All curves shall be smooth with soil drawn e.g. bedding back from the edges.

16.4 Performance defects (What do we look for?) • Grass growth and soil overlapping hard surfaces. • Grass not maintained or ill defined up to bed edges. • Jagged edges to grass areas. • Edging arisings not removed from site. • Excessive pesticide use.

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Location Plan of Shrub areas.

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17. Shrub beds Shrub beds perform a number of purposes among these being: -

• Separation between areas. • Softening the built environment. • Link areas. • Aesthetically enhance areas. • Provide habitat and cover for birds, insects and amphibians.

17.1 Present state Shrub areas within the park are maintained as per the current contract specification. Where funds have allowed, replanting has taken place as areas have begun to tire and plant density has been lost due to natural wastage, wear or abuse. Some small shrub areas have been removed and returned to amenity grassland where appropriate. Those areas which have been replanted have been done so with species which have an ecological as well as aesthetic quality where appropriate.

17.2 Desired state A healthy and attractive shrub bed, free of weeds and litter, that provides an all year round interest. The main reason for pruning is to maintain the habit and character of the plant and to keep it within acceptable size limits in support of this. We are developing new plantings in aesthetically deficient areas to enhance the park experience.

To carry out an effective management regime to contain the planting it is important to appreciate the shrub growth forms which exist and the objectives for their pruning: -

Sprawling & groundcover shrubs.

• Maintain form and texture of the plant • Keep canopy dense • Maintain a cover of healthy young growth

Bushy shrubs growing from a stool or a main stem.

• Maintain the habit of the shrub • Maintain form and surface texture • Maintain shoot and foliage density • Enhance seasonal effects

Specimen shrubs.

• Keep and enhance the individual character and form of the shrub • Maintain healthy growth • Enhance seasonal interest

17.3 Management required Some areas of shrubbery have been identified for removal to improve sight lines and vigilance. This has also had the effect of simplifying management and allow for a better use of resources. Pruning promotes new healthy growth and maintains the balance of species. At all times pruning must prevent encroachment onto roads, paths, cycleways, the obstruction of sight lines (with particular attention to all junctions), road signs, name plates, manhole covers and the base of lamp columns, and to prevent the obstruction of light to windows.

A swathe one metre wide, minimum, shall be kept clear from the Highway to and around lamp columns to allow access for maintenance staff. Shrubs adjacent to roads, cycle ways and paths shall be cut back at an acute angle of 60 degrees from the ground into the plants to prevent re-growth into the path.

Following winter pruning in 2008, areas which have become thin due to natural losses were replanted with species to provide colour, winter cover for fauna and to encourage desirable insects, these included Buddleja, Forsythia, Ilex, Lingustrum, Cornus, Rosa and Berberis.

These areas included the rear of Everglades, beds to the south of Great Denson and in beds on approach to the park entrances along Great Denson around the northern most play area and along Merlin Walk.

17.4 Calendar Maintenance pruning shall be carried out during the periods January to March and November/ December unless otherwise indicated and according to the methods and species as shown below:

Sprawling & groundcover shrubs. • Light pruning to contain height and spread • Heavy pruning to reduce vigour and keep habit and form • Coppice for complete regeneration when plant is of poor quality or needs containing

Bushy shrubs growing from a stool or a stem • Light prune to keep with desired limits • Heavy prune to remain form of plant • Coppice when plants are overgrown and branch framework needs renewing or to maintain aesthetic qualities

Specimen shrubs. • Keep and enhance the individual character and form of the shrub • Maintain healthy growth • Enhance seasonal interest

Plant pruning method and frequency

PLANT ANNUAL PRUNING METHOD LONGER TERM METHOD Berberis (deciduous) Coppice to 200-300mm every 5 years Berberis (evergreen) Lightly prune surface annually Buddleia species (except Prune hard back, annually, to lowest globosa) growing points forming a stool about 300-450mm high Cornus species Coppice 33 – 50% plants Coppice to 150mm every 2-3 years Cotoneaster (groundcover Lightly prune whole surface annually type) Cotoneaster (shrub type) Prune hard back every 5 years to a basic framework about 450mm high Crataegus monogyna (shrub) Prune hard back, every 4 years, to lowest growing points forming a stool about 300-450mm high Cytisus Lightly prune whole surface after flowering removing two thirds of annual growth. Do not cut into old wood. Eleagnus species Prune hard back, every 4 years, to form about 300-450mm high Forsythia species Coppice 25% plants Coppice to 300mm every 4 years Hedera helix (climber) Cut down to 600mm every 4years or p prevent interference with building feat eaves, windows Hypericum (groundcover type) Prune hard back entire plant annually Ligustrum species Prune hard back, every 4 years, to lowest growing points forming a stool about 300-450mm high Lonicera (groundcover type) Lightly prune whole surface annually Mahonia aquifolium Heavy prune 20% of the old stems each year Philadelphus species Coppice 20% of plants Coppice to 150mm every 5 years Potentilla species Lightly prune whole surface annually Prunus laurocerasus Heavy prune to 300 – 450mm framework every 3-4 years (Laurel) Prunus lusitanica Heavy prune to 300 – 450mm framework every 3-4 years (Portugal Laurel) Pyracantha species Heavy prune to 300 – 450mm framework every 3-4 years Ribes sanguineum (Flowering Heavy prune to 150mm every 5 currant) years Rubus cockburnianus Coppice 50% of plants Coppice to 150mm every 2 years Roses (shrub) Coppice to 100-150mm every 5 years Salix species Coppice to 150-200mm every 2 years Sambucus species Heavy prune every 2 years, to lowest growing points forming a stool about 150-200mm high Symphoricarpos (groundcover Lightly prune whole surface annually to type) contain the shrub Symphoricarpos (shrubby Coppice to 150mm every 4 years types) Viburnum tinus Heavy prune to 300 – 450mm every 5 years Large, Small-flowered, English Large and small flowered roses in formal beds shall be pruned twice a year, to roses an outward pointing bud, using sharp instruments, trimming any ragged edges and removing any dead wood. In autumn the plants are to be reduced by one third in height to alleviate winter windblow and in early spring pruned to encourage basal growth and keep the plant in a balanced and compact habit. Small-flowered and English roses shall be pruned to an outward facing bud at about 450mm in height. Herbaceous plants Herbaceous plants are to be trimmed after flowering so as to remove seed heads, and subsequently cut back when the foliage has died back in winter. All arisings and trimmings shall be removed off site.

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Other species shall be pruned if required in accordance with the guidelines as laid out in ‘The Pruning of Trees, Shrubs and Conifers’ by George E. Brown, 2nd edition, 15th February 2005. Where plants overlap hard areas, growth shall be maintained so as not to restrict use of that area.

Some areas of shrubs not specifically specified in the annual pruning method nor the Bill of Quantities are pruned on a rotational basis and thus will only be pruned twice during the life of the Contract namely in the second and fifth years. At the end of the growing season all plants shall be checked and all dead, diseased, damaged or crossing branches shall be cut off.

All arisings shall be chipped or shredded, with the appropriate machinery according to their size, on site. The resulting residue shall then be returned as mulch, no greater than 75mm deep, to the shrub bed or another near suitable shrub bed, being spread around the base of shrubs without covering them.

17.8 Performance defects (What do we look for)

• Pruning out of season when birds are nesting. • Overgrown shrubs. • Shrubs encroaching on highways and hard surfaces. • Inappropriate cutting with hedge trimmers destroying the character. • Shreddings in the crown of the shrub. • Piles of shreddings greater than 75mm deep except on Local Wildlife Sites where agreed.

17.9 Equipment

Pruning, is to be carried out using sharp clean instruments to give a clean cut and may involve the use of clearing saws and pruning saws for thicker stems (>25mm) but only loppers or secateurs for lighter stems (<25mm). Light pruning may be done with hedge trimmers.

Coppicing can be carried out with reciprocating blades, circular saws and pruning saws. It may be feasible to carry out part of the work by mechanised flailing providing manual pruning follows this up.

18. WEED CONTROL

The control of weeds in areas designated as shrub beds and woodland. Any plant growing ‘out of context’ shall be deemed a ‘weed’.

• Weeds are controlled to maintain the neat appearance of shrub beds, to reduce competition and encourage a desired range of plants. • The control of weeds in woodland is purely to restrict growth of invasive weeds that exclude native ground flora species. • The total control of weeds in hard surfaces is to prevent damage to these surfaces and prevent accidents such as tripping or slipping.

18.1 Management

The control of weeds by environmentally sensitive methods such as mulching, hoeing or mechanical removal or by the planting of groundcover is preferred to a broad spectrum herbicide control (Glyphosate based herbicide). Where herbicide application is used, it is targeted to those areas which would otherwise not receive sufficient control from other methods.

Weed control methods

LOCATION WEED CONTROL Garden areas, The Contractor shall hoe and hand weed the area with all arisings summer & winter removed from site. bedding. Hedge bases Base to be strimmed annually in August Local Wildlife Sites After coppicing/stooling of non-native shrubs, weed control may be applied during the first growing season where necessary to prevent weeds (including bramble) smothering the regrowth. Herbicides may be used for this purpose. For this purpose “non-native” means beds containing a majority of horticultural varieties or species. Hard surfaces Keep area 100% free of vegetation, moss and algae Woodland Restrict growth of invasive weeds such as bramble, pervasive tree seedlings such as Norway Maple, Sycamore and Ash. Weeding shall be by mowing, strimming, hand-pulling or herbicide spot-treatment only. Overall herbicide treatment is not permitted.

18.2 Performance defects (What do we look for)

• Lack of warning signs. • Herbicides being applied in inclement weather conditions. • Excessive weed coverage. • Weeds above 100mm. • Weeds not eradicated/removed. • Overuse of herbicide resulting in unsightly and excessive dead vegetation/bare ground. • Herbicide damage to plants evidenced by distortion to leaves or dieback.

Location plan of Hedges.

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19. HEDGE

Hedges provide separation between areas; define lines, form spaces and pleasing patterns by providing sculptural and pleasing structures. Many also serve conservation purposes by acting as habits to additional flora and fauna. Hedge cutting maintains a neat appearance, density of plant growth and functional habit.

19.1 Desired state

Pruning operations are carried out in order to maintain hedges in a neat, tidy and pleasing appearance, at a height between 1.5m and 2.1m unless otherwise instructed by the Landscape Services Manager. They should be managed as to maintain a strong framework, with the appropriate shape and width in relation to its height.

19.2 Management required

Rural hedge (Mixed species types) shall only be cut on the highway side to a triangular shape (wide at the base, narrow at the top) to encourage wildlife. Non-rural hedges shall be maintained perpendicular, with the top level and at a right angle to the sides. Variegated or other uncharacteristic growth shall be pruned using approved methods suitable to maintain a high quality finish and appearance. All arisings shall be removed from site.

Carry out pruning to prevent encroachment onto roads, paths and cycleways, so that growth does not extend more than 150mm over these surfaces. Such pruning shall also be undertaken to prevent the obstruction of sight lines and the base of lamp columns, and to prevent the obstruction of light to windows.

Unless it is absolutely necessary operations should avoid pruning hedges in the bird- nesting season between 1st April and 30th June. The type of hedge plant material shall determine the timing of pruning:

Hedge plant type and cutting frequency

HEDGE PLANT TIME OF CUTTING Buxus sempervirens: Pruned twice per year, once in July and once in September. Berberis: Pruned once per year after flowering or in winter after fruiting Carpinus betulus: Pruned once per year between August and September. Crataegus monogyna: Pruned once per year in August. Cupressocyparis Leylandii: Pruned twice per year, once in April and once August. Fagus sylvatica: Pruned once per year between August and September Ilex aquifolium: Pruned once per year between August and September Ligustrum ovalifolium Pruned twice per year, once in July and once in September. Prunus laurocerasus Pruned once per year in April. Prunus spinosa: Pruned once per year in August. Taxus baccata: Pruned once per year between July and September Mixed field hedges Pruned once per year between August and November. The hedgerow adjacent to 47 Forest Rise was restricting the amount of light

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onto the footpath at one of the entrances to the park. This was reduced in height during winter 2007-8 and inter-planted with native hedgerow whips to promote rejuvenation.

19.3 Performance defects (What do we look for?)

• Hedges overhanging footpaths and other hard surfaces preventing safe usage. • Hedges unsightly in appearance not cut to a consistent profile. • Hedge cutting during bird nesting season.

19.4 Equipment

Coppicing can be carried out with reciprocating blades, circular saws and pruning saws. It may be feasible to carry out part of the work by flailing providing manual pruning follows this up.

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Location Plan of Woodlands.

20. Woodlands

Milton Keynes Council recognises that there are many benefits of trees: -

• A source of beauty in our environment. • A conditioner of the air by absorbing CO2 and pollutants from it, etc. • A contributor to biodiversity. • Screen unattractive views. • Reducer of urban noise. • A teaching environment.

It also recognises that uncontrolled issues can arise and therefore management needs to maintain a balance to provide the advantages of trees but ensure people have unimpeded access along footpaths and roadways and that streetlamps in Milton Keynes council’s care are not impeded by foliage from trees or shrubs.

20.1 Present state Selected canopy species are thinned or coppiced to maintain species diversity and promote lower growth glades or at margins.

20.2 Desired state Mixed age stands of diverse native and exotic trees with well developed under story of herbs, shrubs and climbers. Restrict growth of invasive weeds such as bramble, pervasive tree seedlings such as Norway Maple, Sycamore and Ash. Weeding shall be by mowing, strimming, hand-pulling or herbicide spot-treatment only. Overall herbicide treatment is not permitted. Present management regime to be followed, standing dead wood to be left if it posses no risk to the public to provide habitat. Develop areas of increased diversity to provide an aesthetic mix of native and exotic species which will additionally benefit the park ecology. Removing some trees when they are overcrowded will allow more sunlight to lower levels promoting growth in the lower woody and herbaceous layers. The remaining climax tree cover will have a more balanced well-clothed crown. This will therefore create more space for those trees remaining, creating a flourishing woodland with greater biodiversity and amenity value.

Woodland maintenance priorities.

Work Type Requirement List of Priorities Thinning Remove 50 % of all Trees that contain; trees, leaving a flat 1. Splits in main stem, surface less than 50mm 2. Decay in main stem, from surrounding soil 3. Compressive junctions in main stem, level 4. Included bark in main stem, 5. Excessive deadwood in main stem 6. Other trees to achieve 50% of original leaving an even spread of trees Pruning On retained trees, Defective Branches that contain; remove all defective 1. Decay & disease branches, observing 2. Compressive junctions correct angle of cut. 3. Included bark 4. Excessive dead wood

20.3 Performance defects (What do we look for?)

• Branches not target pruned to branch collar or side shoot. • Cuts left torn or uneven. • Stumps left too tall or uneven. • Defective branches left on the tree. • Defective trees remaining (except where dead trees pose no hazard).

20.4 Prescriptive Woodland management following 2007 Tree and Woodland Survey.

Over the next 6 years, woodland areas A-D, G-I and P (See Appendix 5) will be progressively rejuvenated with native and non-native species to provide the area with enhanced ecological and amenity value. Those works highlighted in the survey have been completed.

Each year a 40m sub-section of each woodland area will be thinned of poor standing timber, undesirable ground cover and weak growth. This will then be repopulated with more desirable species. By tackling each area a section at a time it will prevent excessive disturbance of the indigenous wildlife.

Species will be chosen from but not limited to the list below, which contains a mix of native and non-native species of diverse form, colour and structure.

• Quercus • Cedrus • Thuja • Davidia • Sorbus • Malus • Betula • Populus • Arbutus • Pinus • Tillia • Crataegus • Prunus

By protecting the less robust and slower growing species with under planting of thorny species we hope to prevent the need for visually intrusive protective fencing whilst the trees establish.

During 2008 areas D and P have been thinned to create the desired planting pockets and 216 new trees have been planted as part of National Tree Week with the help of local residents. Additional transitional areas of meadow have been added for the 2009 season between the woodlands and amenity grass.

Uniform Age of Stock

Monoculture Canopy

Poor Shrub Diversity

No Meadow “Edge”

Current Structure.

Canopy of Diverse Age and Species

Diverse Shrub Layer Habitat Rich Meadow Transition

Enhanced Structure (10 years following establishment).

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Location Plan of Trees (See appendix 5 for detail).

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21. Trees

21.1 Present state

21.2 Desired state

Good mix of specimen trees which are visually stimulating and ecologically beneficial.

21.3 Management required

Following the 2007 tree survey it is intended to continue to crown lift and dead wood as necessary. Pollarding is to continue on those trees which are currently maintained in this manner. This provides an important habitat, creates visual stimuli and prevents excessive leaf fall and shading of the pond.

Pruning of trees allows for the removal of damaged branches that can be dangerous to the public but could allow disease to enter the tree. Pollarding is long established woodland practice that has over the centuries associated itself with a specific wildlife profile.

Planting of specimen trees to provide a visual focal point and meeting point for the community will be a valuable event to involve local residents

Tree maintenance procedures.

Work type Required Prune broken Any branches hanging below 5 metres over a carriageway to be pruned to allow and/or clearance to that height. Cut off all branches to clear roadway that can be safely dangerous reached from ground level. Report all branches not reachable from ground level to the branches. Landscape Services Manager.

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Work type Required Branches over Cut off all branches up to 2 metres, using hand tools from ground level. Allowance to be footpath made for snow and rain loading. Branches over Cut off all branches up to 3 metres, using hand tools from ground level. Allowance to be redway, made for snow and rain loading. bridleway Epicormic Cut all epicormic growth to a height of 4 metres, using secateurs hand saws and long growth handled pruners Dangerous Any broken or partly broken branches hanging within the tree that can be reached from branches ground level are to be removed and the stumps to be pruned back to the branch collar as described in BS3998: 1989. Contractor is also to deal with any small broken or dangerous branches on instruction from the Landscape Services Manager or when discovered by the Contractor. Proximity to Any branches coming into contact with overhead services or buildings to be pruned to services or give a clearance of at least 1.5 metres. buildings All branches impeding street lamps throw to an angle of 45 degrees from the perpendicular to be pruned to allow clearance to that angle. Branches impeding streetlamp, not reachable from ground level. Report to Landscape Services Manager. Prune to lift The Contractor shall prune branches to a specified height above ground level (specified crown in the Schedule) but the crown MUST be balanced all around. Allowances must also be made for the sway of branches caused by winds and local turbulence, and the droop of fully leaved branches caused by rain. Pruning cuts outside collar. Specification applies to a height reachable from ground level, beyond that report to the Landscape Services Manager. Pollard tree The Contractor shall prune back all branches to the bole to encourage leafy growth and to obtain a specific shape. This should ideally be done on young trees of less than 5m in height. On larger trees the pruning of the large branches back to the bole shall be accompanied by fertilization. The Contractor shall prune back all branches on previously pollarded trees, to the pollard point every season to maintain the pollard shape. Pruning cuts to be such that a stub of young wood containing live or dormant buds is to be left attached and no wound treatment shall be applied. Cut back to pollard joints Stumps of 30-60mm to be left on pollard bolling. Pollard willow The Contractor shall cut off upper section of tree at a height of between 2.4 metres and 3.6 metres as directed. Timber of 100mm diameter and above shall be cut into 2m lengths and stacked. Timber 50mm to 100mm diameter shall be cut into 2m lengths and stacked separately. All brushwood and timber less than 50mm diameter to be removed from site. The Pollarding is to be carried out each year between October/November as directed. Coppice The coppicing shall be at a height not above 200mm and shall require timber to be willlow disposed of as in 047090. Pollard maiden The period of this operation shall be November-February inclusive. trees The Contractor shall cut off the upper section of the tree at height 2.4-3.6m. There shall be a single transverse cut, sloped not more than 1:3 to shed water. To deter climbing, all side branches below the pollarding cut shall be pruned flush with the trunk. Timber larger than 100mm diameter shall be removed from the site and disposed of by the Contractor at his discretion. A record of the quantity removed shall be provided. Material less than 100mm diameter shall (unless otherwise directed) be chipped on site and heaped where directed by the Authorised Officer’s Representative.

Thin marked The Contractor shall fell and remove trees marked with an "X" in tree paint. Felling of trees these trees shall be done in such a way so as not to damage remaining trees. In the case of softwoods stumps shall be treated against infection by Fomes (Heterobasidion) annosum. Clear felled The Contractor shall fell marked trees "in one" using either power saw or manually trees operated winch. Remove The Contractor shall remove stumps of trees indicated by approved methods. The area stumps about the stumps shall be excavated by hand digging and the main stump axed through. The stumps shall then be lifted from their locations and removed using approved methods. The empty pits shall be made good with topsoil or other suitable material. Specification applies irrespective of the size of the stump. Kill stump The Contractor shall kill stumps indicated by application of approved chemical poisons. Chemicals shall be applied to 25mm diameter by 50mm deep holes drilled into the sapwood area of the stump at 50-100mm intervals. Chemicals to be applied as powder or in supersaturated solutions. The Contractor shall ensure that seepage of the Chemical into the soil is avoided and that protective clothing recommended by the manufacturer or by the Control of Pesticide Regulations 1986, is worn. Chip stump The Contractor shall chip stumps indicated to a minimum of 150mm below ground level using approved machine. All arisings to be removed off site. Soil level shall be restored by backfilling with topsoil or other suitable material. Specification applies irrespective of size of stump.

21.4 Performance defects (What do we look for?)

General. all situations. • Branches not cut to branch collar or side shoot. • Cuts left torn or uneven. • Broken branches. • Arisings not removed. • Trees pruned unnecessarily in proximity to nesting birds.

Prune broken, dangerous branches etc. • Branches hanging below 2 metres over footpaths. • Branches hanging below 5 metres over a roadway and not reported. • Broken branches left within tree • Epicormic growth below 4 metres

Prune to clear streetlamps. • Branches impeding streetlamp and not reported • Cuts left torn or uneven

Pollard tree • Cuts in pollard bolling due to stumps being cut back too far • Stumps left too long • Areas not pollarded

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21.5 Calendar

Tree work to be carried out after leaf fall and before substantial new leaf formation. Approx October to March.

21.6 Equipment

Chain saw, PPE, bow saw and shredder

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Location of Watercourses and Pond.

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22 Wetlands

The pond is a valuable habitat particularly for invertebrates. Due to the shallow nature and poor water retention properties of the pond it is liable to siltation. Original watercourses have become redundant since the development of the estate but still exist within the woodland belts and provide interception of surface water, preventing flooding.

22.1 Present state

22.2 Desired state

Provide a graded habitat running through trees, then on down to the shrub level and to wetland vegetation. Maintain a natural appearance, which will be enhanced over time as the area matures. Interpretation will be incorporated once re-establishment around the pond area has settled.

22.3 Management required

Pruning of other trees if over shadowing water bodies or excessive leaf fall is entering the water. Dredging as a last measure when required. Annual clearance of decaying matter to prevent stagnation and reduce fertility to provide a more diverse flora.

22.4 Calendar

Tree work to be carried out after leaf fall, approx October to March. Dredging as and when required.

22.5 Equipment

Tree work - Chain saw, PPE, bow saw and shredder. Dredging by mechanised means.

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Appendix 12: