brian g. crane 2013 initial results from a long term study of the effects of root damage on street...

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brian g. crane 2013 INITIAL RESULTS FROM A LONG TERM STUDY OF THE EFFECTS OF ROOT DAMAGE ON STREET TREES European Conference of Arboriculture Planning the green city: relationships between trees and infrastructures Turin 26th-28th May 2014 brian g. crane 2014

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Page 1: Brian g. crane 2013 INITIAL RESULTS FROM A LONG TERM STUDY OF THE EFFECTS OF ROOT DAMAGE ON STREET TREES European Conference of Arboriculture Planning

brian g. crane 2013

INITIAL RESULTS

FROM A LONG TERM STUDY

OF THE EFFECTS OF

ROOT DAMAGE ON

STREET TREES

European Conference of Arboriculture

Planning the green city: relationships between trees and

infrastructures

Turin 26th-28th May 2014

brian g. crane 2014

Page 2: Brian g. crane 2013 INITIAL RESULTS FROM A LONG TERM STUDY OF THE EFFECTS OF ROOT DAMAGE ON STREET TREES European Conference of Arboriculture Planning

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A THOUGHT

A layman, a mathematician and a scientist are driving through Wales. They see a black sheep:

‘Look’, says the layman, ‘the sheep in Wales are black’

‘No’, says the mathematician, ‘in Wales there is one black sheep’

‘Not so’, says the scientist ‘in Wales, there is a sheep – we know half of it is black’

?

Page 3: Brian g. crane 2013 INITIAL RESULTS FROM A LONG TERM STUDY OF THE EFFECTS OF ROOT DAMAGE ON STREET TREES European Conference of Arboriculture Planning

THE ARBORICULTURIST’S BIG QUESTION

But what’s happening here?

We know a lot about how the aerial parts function – because we can see them working and measure what’s happening

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HEALTH WARNING!!!

The data in this presentation has been checked, but further validation is required

before finalisation and publication.

Due to the large database, any amendments and the effect they have on figures

is likely to be limited

RESULTS NOT YET FORMALLY PUBLISHED

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Project Outline and Timings

1994 Record root damage to street trees in the London Borough of Havering

2000/1 Follow-up visit collecting limited data – 1994/2001 data transferred to MS Excel spreadsheet

2013 Full re-survey of aerial parts. Analysis of data

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IMPORTANT BECAUSE:

Thought to be the largest assessment of its kind ever carried out:

Over the longest period of time

Trees are mature

Subject to urban pressures

Large study population

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FIGURES

1994 – 1,168 trees assessed.

2001 – re-survey – results overtaken by 2013 survey

2013 - 1,061 trees assessed.

Period of Time: early 1994 to June/July 2013.

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Approximately 100 trees removed.

Cable installation company paid £250,000 GBP compensation

.....and agreed planting of 3 trees for every one removed

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SOIL !!!!

Yum!!!!

Pore

spaces

Moisture

Tree soil Minerals

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To the (Urban) Landscape

Below Ground!!!!!!

Welcome!

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LONDON BOROUGH OF HAVERING

Outer London Borough

Main period of development in surveyed areas – inter-war

Main areas surveyed:

RomfordHornchurchHarold HillElm Park

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Original trenches generally about 500 -

650 millimetres deep (350 + millimetres

cover, 100 millimetres pipe diameter

and 100 + millimetres granular levelling

fill).

Re-excavated trenches between 1.4 and

3 metres long

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Rooting depth‘...from numerous studies involving comprehensive root

excavations the indication is that typically as much as 90% of the tree root length occurs in the upper metre of soil’. (Roberts, R., Jackson, N. and Smith, M. 2006 Tree Roots in the Built Environment)

‘Overall temperate broadleaved trees have 82% of their roots in the upper 50 centimetres of soil...’ (Jackson, R.B., Canadell, J., Ehleringer, J.R., Mooney H.A., Sala, O.E. and Schultz, E.D. 1996. A global analysis of root distribution for terrestrial biomes. Oecologica, 389-411).

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Dated: 2003

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1994

SURVEY

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Necessary to upload tree location data without GPS locations and add these later

Crown condition. Almost all the crowns

of existing trees were in good condition.

This was assessed on leaf cover, leaf

size and extension growth.

Almost all the trees had been managed

by heavy crown reduction on a regular

basis. Heavy crown reduction was

assessed as existing when a tree

showed reduction back to cuts of 150

millimetres or more.

Assessment of suitability for

follow-up survey with ground-

searching radar – if woody

plants near enough for roots to

confuse radar, site not selected.

In 46% of eligible sites the street

tree was the only significant

vegetation.

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2013 SURVEY

Applies to both tree AND each

root

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Remarks 1994 Root diameter

Distance from trunk

Depth Root Severed Y/N

Root matrix value

Total weighting

Phone pole adjacent-wires in crown. Adjacent to cross over - Large surface buttress roots.

18 210 15 Y 2 2

             

Adjacent to cross over - Water pipe between tree street lamp adjacent and Encom trench.

32 250 15 Y 2 2

             

  75 190 20 Y 6 11

  16 190 20 Y 2  

  19 190 15 Y 2  

  8 190 15 Y 1  

  8 200 20 Y 0  

  4 200 5 N 0  

             

Link ID

Road Location Date of Inspection

Species Height Trunk diameter at 1.5 metres

Crown radius

Age

1 Alan Gardens O/S 6/8 18/10/1994 Acer pseudoplatanus

10 44 6 M

                 

2 Alan Gardens O/S 4/2 18/10/1994 Platanus x hispanica

10 80 6 M

                 

3 Alan Gardens Flank of No 1 18/10/1994 Platanus x hispanica

12 55 8 M

3                

3                

3                

3                

3                

                 

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ROOT DAMAGE MATRIX

Complete spreadsheet 4414 lines, 67 columns

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Root diameter

Distance from trunk

Depth Root Severed Y/N

Root matrix value

Total weighting

Weighting class

18 210 15 Y 2 2 VL

             

32 250 15 Y 2 2 VL

             

75 190 20 Y 6 11 H

16 190 20 Y 2    

19 190 15 Y 2    

8 190 15 Y 1    

8 200 20 Y 0    

4 200 5 N 0    

             

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ROOT DAMAGE MATRIX

Root size (diameter

at cut end)

Overall severed root diameter or numbers

Weighting Total weighting

Weighting class<1

metres from trunk

1 to 1.5 metres from trunk

>1.5 metres from trunk

<9 millimetres

Less than 100 millimetres in total *

1 1 1 1, 2 Very low

<9 millimetres

Between 100 and 500 millimetres in total*

2 4 4 3 to 5 Low

<9 millimetres

Over 500 millimetres in total*

4 2 1 6 to 7 Moderate

10 to 24 millimetres

Per root 3 2 2 8 to 11 High

25 to 49 millimetres

Per root 6 4 2 12 - 21 Very high

50 to 79 millimetres

Per root 10 8 6 >21 Extremely high

80 to 99 millimetres

Per root 12 10 8 C1 if roots present C2 if no roots

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DATA HANDLING

Remove invalid entries (unlocated or misidentified trees, data entries which appeared to be incomplete)

Develop single-line entry for each tree using root damage matrix

Merge spreadsheets

Check continuity of entries

Interrogate data

Sample re-check data with GIS entries

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Tilia x europaea planted in

mid 1800s. Roots cut down to about 1 metre

depth in 1970s. Tree still growing

with good vigour

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AcerAesculusAilanthusBetulaCarpinusCrataegusFagusFraxinusLaburnumMalusPinusPlatanusPrunusPyrusQuercusRobiniaSorbusTilia

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Tilia

Acer

SPECIES BREAKDOWN

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Control 1 (only unsevered roots found)

Control 2 (no roots found)

Extremely heavy

Very heavy

Heavy

Moderate

Light

Very light

7.5%

27.6%

13.8%18.5%

9%

6.2%

10.3%

7.1%

TO SHOW DEGREES OF DAMAGE RECORDED

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THIS BOROUGH DOES NOT HAVE A PUBLISHED TREE OR

URBAN FORESTRY STRATEGY

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FACTORS AFFECTING STREET TREE LOSSES IN URBAN

AREAS

Changing fashions (e.g. replacement of larger species with smaller)

Disease outbreaks – particularly common in monocultures)

Pressure from individual householders

Subsidence claims

Removal of declining stock (overmaturity)

Cost of management

Highway and utility works

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Mature Acer pseudoplatanus. Roots cut

down to about 1 metre

depth for theatre car-parking in

1970s. Tree still growing with good

vigour

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Trees remainingMissing trees (ad-justed)Vehicle crossoversAbiotic removals

Class Number Percentage of total

Trees remaining 696 65.6Missing trees (adjusted)

284 26.7

Vehicle crossovers 77 7.3Abiotic removals 4 0.4

Overall results – Missing trees have been adjusted to show effects of vehicle crossovers and ‘abiotic’ removals

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0

100

200

300

400

500

600

700

800

900

1000

Series1

Class No %

Small trees original population 117

Missing small trees 65 55.6

Large trees original population 935

Missing large trees 286 30.1

Differences in losses between smaller, short-lived and larger, longer-lived genera

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0

10

20

30

40

50

60

Series1

TO SHOW AVERAGE d.b.h. INCREASE BETWEEN 1994 AND 2013

d.b.

h. c

entim

etre

s

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0

100

200

300

400

500

600

700

800

Series1

Class Number PercentageControl trees 363Control trees missing 102 22.9Control trees crossovers 19Non-control trees 698Non-control trees missing 286 32.2Non-control trees crossovers 61

Control/non-control tree survival – adjusted by subtracting ‘crossovers’ from ‘missing’ totals.

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To show losses expressed as % age of each damage grouping

Perc

enta

ge

0

5

10

15

20

25

30

35

40

45

50

Series1

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Average %age loss over all damage

ranges %age loss - control trees

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Extremely heavy damage

Very heavy damage

Heavy damage

Moderate damage

Light damage

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WHERE NOW?

Try to establish reasons for tree removals in localised areas using Freedom of Information Act

Re-check data – interrogate using Access database – increase parameters

Prepare, peer-review and publish full paper

Examine funding for ground-searching radar analysis of selected sites – first attempt to secure funding was unsuccessful

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My sincere thanks to:

David Cutler Professor of Plant Science and Research Fellow, Royal Botanic Gardens, Kew

Francesco Ferrini Professore di Arboricoltura urbana e di Parchi e Giardini, Dipartimento di Ortoflorofrutticoltura - Università di Firenze , Italy

Edward F Gilman Professor, University of Florida, Environmental Horticulture Dept

Tom Smiley Arboricultural Researcher, Bartlett Tree Research Lab, Charlotte NC

Gary Watson Senior Research Scientist Morton Arboretum Adjunct Professor, University of Illinois

Jeremy Barrell Registered Consultant, Arboricultural Association, Chartered Arboriculturist, UK

Dave Shandley Mobile GIS Services, UK

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THE ENDThank you for your attention

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