The Urban Forestry Organisation Limited 

Tree Constraints Plan Relating to the Site for Proposed Community Centre, Fontley Road, Titchfield, Hampshire, PO15 6QR

 

 

 

 

 

 

 

 

Commissioned by Alykhan Tejani of Better Prepared Ltd

and compiled by Chris Rose B.Sc (For). MICF. CEnv 

 

 

 

                                          Contents

 

 

INTRODUCTION.................................................................................................... 3

TERMS AND DEFINITIONS.................................................................................. 4

BACKGROUND...................................................................................................... 5

   PROPOSALS FOR TREE RETENTION……………………………………...6

REVISED TREE REPORT FORMS...................................................................... 7

LOCATION DRAWING TREE RETENTION AND REMOVAL............................. 8

THE ROOT PROTECTION AREA (RPA).............................................................. 9

ROOT PROTECTION AREA DRAWING.............................................................. 10

THE TREE CONSTRAINTS PLAN (TCP)............................................................ 11

TREE SHADOW PLOT.......................................................................................... 14

SHADING PERCENTAGES................................................................................... 15

 

 

  

 

 

 

Introduction

 

These plans, assessments and statements have been compiled by Chris Rose, the Managing Director of the Urban Forestry Organisation Limited. Chris obtained a degree in forestry from Aberdeen University in 1969. He became a member of the Institute of Chartered Foresters in 1982 and currently acts as a mentor for candidates wishing to take their Part II entry examinations, in the arboriculture specialism, for membership of that Institute. He is also a member of the Confederation of Forest Industries and the Royal Forestry Society. Chris has worked in both the private and public sector gaining a wealth of experience in Arboriculture, Forestry and Landscape Management. He has over thirty years experience working with trees in Milton Keynes and has received two Centre of Excellence Awards from the Forestry Authority for his arboricultural and landscape work in that town.

 

This work which was undertaken following instructions from Alykhan Tejani of Better Prepared Ltd, involves the preparation of a Tree Constraints Plan (TCP), an Arboricultural Implications Assessment, (AIA), an Arboricultural Method Statement (AMS) and a Tree Protection Plan, (TPP) relating to the trees which may be affected by the development of the proposed Community Centre at Fontley Road, Titchfield, Hants.

      This current task is underpinned by our Tree Condition Report of 17 September 2010.

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

 

Definitions

 

From British Standard 5837:2005

 

Root Protection Area (RPA)

A layout design tool indicating the area surrounding a tree that contains sufficient rooting volume to ensure the survival of the tree, shown in plan form in square metres.

 

Tree Constraints Plan (TCP)

A plan prepared by an arboriculturalist for the purposes of layout design showing the RPA and representing the effect that the mature height and spread of retained trees will have on layouts through shade.

 

Construction Exclusion Zone (CEZ)

An area based on the RPA, identified by an arboriculturalist, to be protected during development including demolition and construction work, by the use of barriers and/or ground protection fit for purpose to ensure the successful long term retention of a tree.

 

Tree Protection Plan (TPP)

A scale drawing prepared by an arboriculturalist showing the finalised layout proposals, tree retention and tree and landscape protection measures detailed within the Arboricultural method statement (AMS), which can be shown graphically.

 

Arboricultural Implications Assessment (AIA)

A study, undertaken by an arboriculturalist, to identify, evaluate and possibly mitigate the extent of direct and indirect impacts on existing trees that may arise as a result of the implementation of any site layout.

 

Arboricultural Method Statement (AMS)

A methodology for the implementation of any aspect of development that has the potential to result in loss of or damage to a tree.

 

 

 

 

 

 

 

 

  

 

Background   (Extract from previous Tree Condition Report)

 

 

The subject site carries very little in terms of trees with its boundaries and those trees are of poor quality and not worthy of retention if they create a significant constraint on the development proposals.

 

In fact, if the bungalow and its garden area are to be retained there are only two trees on the development area. These are a small squat Ash and a multistemmed Goat Willow.

The hedge on the eastern boundary of the development area adjacent to the horse paddock comprises Hawthorn and Blackthorn and again is of poor quality. There is a patch of scrubby Buddleia, Bramble and small fruit trees, next to a barn in the centre of the site, none of this is worthy of retention.

 

The perimeter hedges and woodland to the site are a completely different matter. They consist of some very old trees with a fairly wide range of species and provide excellent screening and wildlife habitat. They will need to be protected during the development process. The southern roadside hedge consists of Oak, Field Maple, Hawthorn, Blackthorn and Elder.  The northern and eastern woodland boundaries have some very large Oak with Ash, Field Maple and Goat Willow. On the boundary with Fontley Road the internal plants are tall straggling hawthorn. These could be layered to prolong their life and to create a stock proof barrier.

 

There are four trees within the grounds of the bungalow. The multistemmed Hazel would benefit from coppicing. The rather old apple is in poor condition but is still producing fruit.

The Norway Spruce at the gable end of the bungalow is considered to be too close to the structure of the building and is likely to conflict with the foundations of the property. It should be removed. The Silver Birch adjacent to the retaining wall to the access road appears to have damaged the structure of that wall. It too should be removed.

 

 

 

 

 

 

Proposals for Tree Retention, Tree Removal and Tree Replacement

 

In our previous work and in accord with British Standard 5837 Trees in Relation to Construction we made the following recommendations in relation to the retention or otherwise of the various category gradings:

 

Category A Trees – Those of high quality and value: in such a condition as to be able to make a substantial contribution for a minimum of 40 years.

Recommendation: To be retained.

 

Category B Trees – Those of moderate quality and value: in such a condition as to make a significant contribution for a minimum of 20 years.

Recommendation: To be retained if at all possible.

 

Category C Trees – Those of low quality and value: currently in adequate condition to remain until new planting can be established or will be deemed not worthy of retention where they impose a significant constraint on the development or redevelopment of the subject site.

Recommendation: Retain or remove according to individual circumstances.

 

Category R Trees – Those in such a condition that any existing value would be lost within 10 years and those which in the current context should be removed for reasons of sound arboricultural management (includes dead, dying, disfigured, dangerous and significantly diseased trees)

Recommendation: Fell and remove.

 

 

Having studied the development proposals we have consolidated our views on tree retention and removal as follows:

 

It is clear that the woodlands and hedges on the outer boundaries of the site need to be conserved and protected during the development phase as they are mature, of good quality, and provide valuable screening and wildlife habitat.

 

The two internal trees, tree numbers 4 and 8 and the hedge between the development area and the horse paddock are all of poor quality and should be removed.

 

The following pages give the detail of the revisions in the format of Tree Survey Report Forms and a site layout drawing showing the trees which are to be removed.

 

 

Trees to be retained or removed can be summarised as:

 

Tree

Number

1

2

3

4

5

6

7

8

9

10

11

12

13

Retain

Y

Y

Y

 

Y

Y

Y

 

Y

Y

Y

Y

Y

Remove

 

 

 

Y

 

 

 

Y

 

 

 

 

 


 

 

The Urban Forestry Organisation Limited

Revised Tree Survey Report Form (as BS 5837:2005)

 

Location:  Site for Community Centre, Fontley Road, Titchfield, Hants    Date: 24 April 2010                                              Surveyor: Chris Rose

                 

 

Tree No.

Species

Height (Metres)

Stem Diameter (mms)

No

Stems

Crown Spread

 

 

North

South

East

West

 

Height of Crown Clearance (metres)

Age Class

Physiolo-gical Condition

Structural Condition

Preliminary Management Recommendations

ERC

Years

Category Grading

1

Quercus robur

13.01

0.48

S

9.45

8.56

10.71

9.79

3.91

M

Fair

Crown rather thin. Significant deadwood in crown. Ivy on main stem has been cut and clings there dead.

None

40+

A

2

Quercus robur

10.13

0.30

S

6.94

6.84

6.88

6.82

1.27

MA

Good

Reasonably good tree. Form is moderate.

None

40+

A

3

Acer campestre

9.14

0.24

S

5.94

6.15

5.92

5.90

2.20

MA

Good

Group of four Field Maples. Form only moderate.

None

40+

A

4

Fraxinus excelsior

6.02

0.18

S

4.37

3.90

4.28

4.37

2.76

Y

Poor

Small poor quality tree, Poor form with large secondary stem from near base.

Fell and remove

10-20

R

5

Fraxinus excelsior

9.20

0.24

S

7.13

7.11

7.12

7.12

2.88

MA

Fair

Crown rather thin.

None

40+

A

6

Quercus robur

17.21

0.51

S

12.89

12.82

12.88

12.94

2.38

OM

Poor

Three main stems. Cavity and decay at base. Significant deadwood in large spreading crown.

None

20-40

B

7

Quercus robur

18.86

0.63

S

12.17

11.89

12.18

12.44

2.1    0

OM

Fair

Minor stem to north with cavity and decay at junction with main stem which breaks to three at four metres with probability of water pocket. Deadwood in crown.

None

40+

A

8

Salix caprea

6.18

0.19

MS

6.18

6.38

5.99

5.99

1.82

MA

Fair

Four stems from base with weak forks.

Fell and remove

20-40

R

9

Quercus robur

10.79

0.37

S

9.71

10.00

9.74

9.89

1.42

OM

Fair

Adjacent to Fontley Road, leaning over road. Ivy covered main stem. Main stem breaks to two at four metres. Deadwood in crown. Category subject to result of climbing inspection.

Climbing inspection to assess safety of main fork.

40+

A

10

Corylus avellana

6.53

0.09

MS

5.46

5.19

5.24

5.18

1.49

MA

Fair

Multiple stems from base, from coppice origin.

Coppice if to be retained.

10-20

C

11

Malus spp

5.23

0.19

S

5.62

5.61

5.60

5.61

1.20

M

Fair

Heavy side branch at half metre. Poor shape and poor form.

None

10-20

C

12

Picea abies

6.14

0.21

S

2.55

2.47

2.47

2.48

0.25

Y

Good

Very close to gable end of bungalow, prospect of conflict with foundations.

Consider removal in order to safeguard structure of bungalow.

20-40

C

13

Betula pendula

9.05

0.20

S

4.80

4.53

4.25

4.30

1.63

Y

Fair

Heavy side branch on north side. Tree situated very close to retaining wall which is showing signs of cracking.

Consider removal in order to safeguard structure of wall.

20-40

C

 

 

 

1


The Root Protection Area (RPA)

 

The RPA refers to underground constraints and is the minimum area in square metres which should be left undisturbed around the tree during the construction works.

 

The RPA can be calculated as an area equivalent to a circle with a radius twelve times the stem diameter of each tree as follows:

 

RPA (m2) =  ( stem diameter mm @1.5 m x 12 )2      x     3.142

                                           1000                         

 

 

The Root Protection Areas for trees on the boundaries of the development area (and excluding those trees which are within the demise of the bungalow) are given in the following table and are shown on a following drawing by means of red circles which also indicate the position of any required tree protection fencing. (subject to modification of terms given later).

 

 

Tree No

Species

Height

Diameter

RPA

 

 

Metres

MM

Sq Metres

1

Quercus robur

13.01

0.48

104

2

Quercus robur

10.13

0.30

40

3

Acer campestre

9.14

0.24

26

5

Fraxinus excelsior

9.20

0.24

26

6

Quercus robur

17.21

0.51

117

7

Quercus robur

18.86

0.63

180

9

Quercus robur

10.79

0.37

62

 

 

Normally the Root Protection Area should be centred on the stem of each tree unless there is something to suggest that the root plate of the tree is not symmetrical.  There is no evidence to lead us to believe that any of the root plates of the trees to be retained are not symmetrical.

 

The drawing on the following page shows the BS 5837 calculated root protection areas for the individual sample trees in the woodland and hedgerows on the boundaries of the site.

 

It will be noted that the recommended calculation places the Root Protection Area for all trees inside the crown spread of the tree, (because the trees have a relatively thin stem and a large, in comparison, crown spread).  Our own personal and professional view in relation to this situation is that it is preferable to consider the extent of the Root Protection Area to be equivalent to the crown spread of the tree.  We have accommodated this within the positioning of the tree protection fencing as defined in the Tree Protection Plan.


 

1

 

 

 

 

The Tree Constraints Plan (TCP)

 

 

 

The TCP considers both underground and above ground constraints.

 

The above detail relating to the RPA for the retained trees covers the extent of the underground constraints.

 

 

In terms of the above ground constraints we have considered the current and ultimate height and spread of the retained trees in our deliberations. These matters are important in terms of the size of the trees in relation to potential development, the dominance of the trees and their movement at times of high wind.

 

We have used as base data that given in The National House Building Councils Standards, effective from September 2008 and amended the figures to suit the particular soil and climate conditions relevant to the Fontley Road site. Our findings are given on the following pages. 

 

The trees, woodland and hedgerows to be retained are on the boundaries of the site and consist mostly of mature specimens which will not increase in height and spread to any great extent in the forthcoming years. Therefore we expect that the continued growth of the retained trees will have no significant impact on the Community Centre in the future.

 

 

 

 

 

 


 

The Urban Forestry Organisation Limited

(Tree Height and Crown Spread)

 

Location:  Community Centre Site, Fontley Road, Titchfield, Hants

 

Tree No.

Species

Height (Metres)

NHBC Max

Height

ms

Site

Specific Max Height

ms

Existing Crown Spread

 

 

North

South

East

West

 

Potential

Max Crown

(radius)

ms

1

Quercus robur

13.01

20.00

19.00

9.45

8.56

10.71

9.79

13.00

2

Quercus robur

10.13

20.00

19.00

6.94

6.84

6.88

6.82

13.00

3

Acer campestre

9.14

15.00

14.00

5.94

6.15

5.92

5.90

8.00

5

Fraxinus excelsior

9.20

23.00

22.00

7.13

7.11

7.12

7.12

10.00

6

Quercus robur

17.21

20.00

19.00

12.89

12.82

12.88

12.94

13.00

7

Quercus robur

18.86

20.00

19.00

12.17

11.89

12.18

12.44

13.00

9

Quercus robur

10.79

20.00

19.00

9.71

10.00

9.74

9.89

13.00


 

 

 

Other Matters Relating to The Tree Constraints Plan (TCP)

 

The other matter of above ground constraints concerns shade cast by the retained trees. This issue is of more importance when dealing with housing developments and is a little consequence in relation to the proposed Community Centre as the development is proposed for the centre of the site and the retained trees and hedges are all on the site boundaries. However we have included an example of a tree shade diagram for completeness on the next page of this report. The drawing relates to a mature Oak tree in the southern hedgerow and shows in purple hatching the shade which would be cast by such a tree at 12.00 noon on 22 October in any year.

 

 

 

 

 

 

 

Tree Shadow Diagram

 


 

Graphs showing shading of an area within the proposed development using data relating to a mature Oak tree