a framework for street tree planning in urban areas in israel
TRANSCRIPT
Landscape and Urban Planning, 19 ( 1990) 203-2 12 Elsevier Science Publishers B.V.. Amsterdam - Printed in The Netherlands
203
A Framework for Street Tree Planning in Urban Areas in Israel
S. AMIR and A. MISGAV
Technion-Israel Institute of Technology, Faculty ofArchitecture and Town Planning, Haifa 32000 (Israel)
(Accepted for publication 18 January 1990)
ABSTRACT
Amir, S. and Misgav, A., 1990. A frameworkfor street tree planning in urban areas in Israel. Landscape Urban Plann., 19: 203-212.
This article presents the methodological as- pects of a proposed planning process for an ur- ban street tree system. The process specifies goals and objectives for street tree planning, cri- teria for evaluation of process output, develop ment stages in the preparation of conceptual and detail planting plans and a case study for dem- onstrating the use of an analysis method to de-
termine the suitability of site/tree projile of a given street.
Based on the use of subjective and objective data sources, the process could be adapted for use in the planning of other urban vegetation areas. The contribution of such a process to de- cision making depends on availability of data on site conditions and on species selection choices that are provided by the list being used.
INTRODUCTION
The increased intensity in development of urban areas often creates environmental con- ditions which will not support the continuous existence of street trees (Hubbes, 1975 ) . Past studies often show that there is a need for a conscious planning policy and management of street trees to prevent the persistent and ongo- ing destruction of this resource.
Clark ( 1978) indicates that trees generally have a low priority among decision makers. Public authorities often view tree planting
largely as a visual enhancement effort. They often do not take into consideration the broader environmental and functional roles that such trees possess (Rousakis, 1978).
Several studies have examined the functions of urban trees (Brown, 1983; Yahav, 1986) and Robinette ( 1972) classified the functions of trees as architectural, functional, engineering, climatic and aesthetic. Economic values were studied by Payne ( 1978) and Johnson et al. ( 1982) analysed their social and psychological functions. Pitt et al. ( 1979) dealt with climatic and engineering functions, while Appleyard
0169-2046/90/$03.50 0 1990 Elsevier Science Publishers B.V.
204 S. AMIR AND A. MISGAV
AND OBJECTIVES
EVELOPHENT kF ti ONCEPNAL
*n?!=r Tll!TF
\i EVRL~PHENT F ETAILED PLAN
J PHySICAL/ VISUAL CHARACTER OF ME STRREET
CLIMATE CONTROL NOISE ABATEMENT AIR POLLUTION
E
lwxhr.A‘I”N F TReET \I REES r, DETEF.~~INEc I
I
ELECTION ‘F REE SPECIES
EFINE PREPERRED LIMATE. NOISE, ISUAL CONTROL
SPECIES VARIETY SPECIES IN ONE
Fig. 1. Street tree planning process.
URBAN STREET TREE PLANNING IN ISRAEL 205
( 1978) investigated trees as an aesthetic as- pect of the urban environment. Environmen- tal functions of trees were studied by Rich ( 1970) for air pollution and amelioration, and by Schiller ( 1984) for noise control.
Street tree resource management has lacked a long-range and coordinated approach that would ensure the biological needs of trees. Un- like most of the urban infrastructure, trees are living units and are the concern of many professionals. Andresen ( 1975 ) indicated that in many cities management tools that go be- yond the day-to-day problem-solving type are lacking. Growth and the enduring viability of trees require a management system that can assess the impact of daily actions on the con- tinuous existence of a tree population. What is often lacking is a clear and predetermined pol- icy that identifies urban trees as a living re- source and one that fulfils multiple functions. Such a policy necessitates an ongoing planning and management system whose goal is to en- sure the existence of trees and their develop- ment over time.
This article presents the content and stages of a proposed planning process for an urban street tree system in Israel.
Past studies have suggested various contents and structures for street tree management sys- tems and the means for their implementation. Grey and Deneke ( 1986), International City Management Association ( 1982)) Howard and Hudson ( 1984), Tate ( 1984), Johnson et al. ( 1982 ) all identified the importance of includ- ing the following three elements as a part of any management system: inventory of the re- source, plan for new planting and a strategy for resource maintenance. In addition to such professional elements, several administrative aspects have been suggested for inclusion such as long-range planning for manpower, and budget, as management tools which indirectly impact the well-being of the resource.
The process described below is one of three issues that emerged in the original study, (see Fig. 1): ( 1) development of methods for in-
ventory of the street tree population; (2) de- sign of a planning process and of its update for planting street trees; (3) development of a maintenance program for urban trees. Details of the descriptive model and proposed main- tenance program are not included here, but are described in Amir and Misgav ( 1988 ).
In preparing the plan, we followed a four- stage process: ( 1) specification of the problem through the identification of goals and objec- tives; (2) development of evaluation criteria needed to assess the quality of the results; (3) generation of development and detailed street tree plans; (4) demonstration of the use of the process in a case study.
GOALS AND OBJECTIVES FOR URBAN STREET TREE PLAN
This stage provided the conceptual basis of the plan that is based on preference by deci- sion makers, on past studies and on research generated from case studies. This stage was di- vided into four elements: goals, objectives, means and criteria. The subjects divided into three groups (spatial-visual, function and bi- ological-physiological aspects) and are pre- sented in Fig. 2 in an hierarchical order, from the general to the specific.
Goals and objectives are concerned with two uses: ( 1) as a broad and general system which is relevant to any city-scale street tree planting plan; (2 ) as a framework that defines the con- tent of a specific plan prepared for smaller areas such as a neighbourhood or the individual street. The goals-objectives framework relates to specific characteristics of a site and its conditions.
The proposed street tree plan has four major goals. The most important goal is the selection of tree species with the greatest suitability for a given location. The second goal deals with the achievement of a major function of trees in cit- ies as providers of a green living environment. Trees give special landscape character to a place. A third concerns trees’ contribution to
.L
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REE
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AL
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ITY
SUIT
ABIL
ITY
Fig.
2. G
oals,
obj
ectiv
es,
mea
ns a
nd c
riter
ia fo
r th
e pla
nning
st
reet
tre
e sy
stem
TABL
E 1
Crite
ria
and
mea
sure
s fo
r sit
e ev
aluat
ion
and
tree
spec
ies
sele
ctio
n
Crite
ria
Type
Cr
iteria
M
easu
res
Leve
l 1
Leve
l 2
Leve
l 3
Visu
al an
d sp
atia
l
Tree
Tree
Tr
ee
Tree
Tree
Bo
th
Both
Si
te
Site
Si
te
Site
Phys
ical
and
biolog
ical
Both
Tree
Tr
ee
Tree
Tr
ee
Tree
Func
tiona
l Bo
th
Both
Bo
th
Site
Si
te
Tree
size
: Cro
wn
Heig
ht
Tree
for
m
Tree
tex
ture
Tr
ee c
olou
r: Le
aves
Bl
osso
m
Crow
n de
nsity
Pl
antin
g de
nsity
Pl
antin
g ar
rang
emen
t Co
nstru
ctio
n de
tails
St
reet
fur
nitur
e Fo
regr
ound
vie
ws
Plan
t va
riety
Clim
atic
regio
n
Grow
th
rate
to:
Life
expe
ctan
cy
Decid
uous
/eve
rgre
en
Form
of g
rowt
h Nu
isanc
es
Envir
onm
enta
l se
nsiti
vity
Regu
lation
of
m
icroc
limat
e Sc
reen
ing a
bility
No
ise a
bsor
ption
Tr
affic
co
ntro
l Do
min
ant
land
use
Narro
w:
< 5
M
Low:
<8
M
Irreg
ular
Ellip
tical
Fine
Da
rk g
reen
, lig
ht g
reen
, gre
y gr
een
Med
ium
: 5-
l 0
M
Wid
e:
10 M
+ M
ediu
m:
8- 1
2 M
High
: 12
M+
Pyra
mida
l Ro
und
Colu
mna
r, pa
lm,
weep
ing
Med
ium
Co
arse
Ye
llow
gree
n, r
ed g
reen
Br
own
Othe
r
Back
grou
nd
is tra
nspa
rent
Tr
unk
is tra
nspa
rent
Ov
erlap
ping
Spac
e is
narro
wer
than
cro
wn
Regu
lar,
geom
etric
Irr
egula
r (W
idth
, fo
rm a
nd m
ater
ial
of p
ath,
roa
d an
d st
ruct
ure)
(In
vent
ory
of e
xistin
g st
reet
furn
iture
)
(Cha
ract
erist
ics
of e
xistin
g sh
ort
dist
ance
vie
ws)
(Num
ber
of s
pecie
s an
d th
eir s
patia
l ar
rang
emen
ts)
Not
trans
pare
nt
Broa
der
spac
e Co
mbin
ation
of
bot
h
Jord
an
Valle
y, i
nter
nal
valle
y
l-4
year
s Up
to
50 y
ears
De
ciduo
us
Excu
rrent
Coas
tal
zone
, 30
0-60
0 M
, ab
ove
sea l
evel
1 O-8
yea
rs
50-
100
year
s Se
mi-d
ecidu
ous
Decu
rrent
500
M+
up to
15
year
s 10
0 + y
ears
Ev
ergr
een
Sens
itivity
to
dise
ases
Ag
gres
sive
root
s, s
hoot
s, s
mel
l, all
ergy
, br
ittle
, at
tract
s,
inse
cts,
thor
ny,
poiso
nous
Fr
ost,
wind
, he
ath,
dro
ught
, ra
inst
orm
, air
poll
ution
Leve
ls of
tre
es’ a
bility
to
reg
ulate
tem
pera
ture
, ex
posu
re w
as b
ased
also
on
form
, de
nsity
, te
xtur
e an
d co
lour
of c
rown
Sc
reen
ing f
unct
ion
of tr
ees
depe
nds
on t
heir
crow
ns’
text
ure
and
size,
tree
for
m a
nd p
lantin
g de
nsity
Ab
sorp
tion
depe
nds
large
ly on
text
ure
of c
rown
and
den
sity
of p
lantin
g Ac
hievin
g sa
fety
for
pede
strian
an
d dr
iver
by b
ette
r pla
nting
M
ajor
land
uses
wer
e cla
ssifie
d to
hou
sing,
com
mer
cial,
majo
r tra
nspo
rtatio
n st
reet
208 S. AMIR AND A. MISGAV
the aesthetic, climatic, environmental, traffic and safety qualities of the city. The fourth goal concerns the contribution of trees to the reduc- tion of conflict between conditions needed for their long-range survival and human activities in their immediate environment (Fig. 2).
Six objectives were identified that provide a basis for management (Fig. 2 ) . They are in- tended to achieve maximum suitability be- tween trees and their site environment in three areas: the spatial-visual, biological-physical and the functional. The objective of the pro- cess is to arrive at an optimum among these areas. To make the framework operational, a set of criteria and means was developed. Cri- teria were used to evaluate the degree to which a given street tree design achieved the stated objectives.
Three sets of criteria were developed to re- late to two types of tree planning tasks. The first is concerned with tree selection, the second with site suitability, the third with both tasks. Visual-spatial criteria are intended for use in the evaluation of the degree to which a tree is suitable for a site with a given visual quality. The second group is concerned with evalua- tion of tree suitability for a site with a given growth and physical constraint. The third type evaluates the degree to which a tree is likely to fulfil a function that would ameliorate the cli- matic or other environmental conditions. Cri- teria and measures for the evaluation of trees and sites, or both, are identified by subject and type of task in Table 1.
PROCESS FOR GENERATING A CONCEPTUAL STREET TREE PLAN
The plan-making process is based on the content developed in the goals-objective stage. This includes the preparation of two plans: one for general guidelines and another for detailed street planting.
The conceptual stage includes design guide- lines and the preparation of a city-wide plan. An important function of the latter is to pro-
vide a comprehensive decision-making frame- work. It makes the implementation of design guidelines in local plans feasible. One of the plan’s objectives is to develop agreeable visual and landscape identities for various parts of the city. It is intended to secure a given visual and spatial form in the organization of new planting.
In the preparation of the conceptual plan, decisions were based on three design elements: spatial arrangements of trees, their size and form. Three types of spatial arrangement were identified for use: the formal arrangement, non-formal and a combination of the two (see Table 1). Tree size is concerned with the di- mension of the diameter of the crown and the height of the tree. For planning objectives, trees were divided into three groups: small, medium and large. The third design element is tree form which defines the space of streets, the type of care that is needed by the tree and the func- tions that a tree could fulfil.
As shown in Fig. 1, the first stage in plan preparation is specification of measures, as de- fined in Table 1. The three elements are used in the following sequence: arrangement, size and form. To develop a tree profile, the ele- ments are combined through two matrices, ar- rangement/size, with the resulting combina- tions brought together with form. This results in the specification of a wide range of tree pro- files. Each profile with its characteristics con- stitutes the basis for evaluation of the suitabil- ity of trees for various site conditions.
The profile data are used with a set of pre- determined design principles to develop a gen- eral planting plan, as is demonstrated for the case study below. The final product, at this stage, does not name tree species, but specifies design principles and tree profiles to be ap plied in each street. It is intended that the con- ceptual stage will provide sufficient flexibility to enable the completion of detailed design for various sites. Such design could take into con- sideration additional tree-specific and site-re- lated aesthetic and functional factors.
URBAN STREET TREE PLANNING IN ISRAEL 209
DETAILED STREET PLANTING PLAN
Once tree arrangement, size and form for a given street type are specified, it is possible to complete the preparation of a detailed street planting plan. This stage includes detailed studies of site characteristics and the selection of tree species. Site evaluation is made on the basis of three groups of criteria: spatial-visual, biological and functional (Table 1). Site suit- abilities and limitations on tree growth and function were identified. This information was then used as a basis for the selection of species suitable for a site. The tree species selection process includes three stages: ( 1) develop- ment of a street tree list; (2) selection criteria ordering; (3) selection of species.
A general tree list was based on existing lists and on other written sources that helped verify the suitability of species as street trees. Data describing the trees in the list were classified according to size and to four groups of site characteristics: physical, tree growth condi- tions, site maintenance factors and site aes- thetic qualities. Table 2 presents a sample tree profile.
Criteria classification provided a basis for the description of trees in the general list (Ta- ble 1). The use of the list for the selection of the most suitable tree for a site required the or- dering of criteria according to importance.
Criteria were classified into those of pri- mary and secondary importance (Table 2). The first included all those that are mandatory for the continuous existence of a street tree. The second group were considered not mandatory. Ten types of criteria were used in the case study. The primary upper, the more important group, are concerned with visual, bio-physical, and maintenance subject, and the secondary with visual and functional criteria. Criteria were also ordered within the group as indicated by the numbers l-3 (Table 2 ) .
Street trees were selected from a general list through a two-stage elimination process. In the first stage, a list of potential tree selections for
a street is evaluated according to the primary criteria. Only those trees that satisfied all the primary criteria were retained on the list. The new list is then evaluated using the secondary criteria. In this stage, the less suitable trees are not dropped from the list, but are placed in a less preferable position. This order provides the designer with greater flexibility in making choices among trees.
SELECTION OF A TREE FOR A SITE - A CASE STUDY
The selection of the most suitable tree spe- cies for a place is based on site and tree suita- bility characteristics. These are detailed in the lower part of Fig. 1 where site evaluation and tree species selection factors are presented. Each factor is detailed by selected characteris- tics of a site or trees to describe the nature of suitability.
The content and sequence of tree species screening involves five succeeding matrices (Table 2 ). Each matrix concerns different combinations of site/tree characteristics. The first three matrices are concerned with pri- mary criteria, the latter two with secondary criteria.
To demonstrate the screening process, we used a general list of 14 different trees indi- cated by number from 1 to 14 (Table 2 ) . Tree names are indicated in footnotes. Trees were put on the list after pre-screening of a larger list for proper sizes and forms. The ( - ) symbol in- dicates that the tree does not satisfy the re- quired level of a mandatory criterion specified in the corresponding row and that the tree is not suitable for the site in question. In the sec- ond phase, screening continues with the sec- ondary criteria.
To demonstrate the screening process, we chose a street in the study area. Its main func- tion is transportation within a residential area. Street characteristics and functions were used to design the preferred profile. Tree and site
TABL
E 2
Tree
list
scr
eenin
g pr
oces
s -
a ca
se st
udy
Type
of
Orde
r Tr
ee/s
ite
decis
ion
Tree
cha
rac-
Ex
istin
g Pr
efer
red
leve
ls Tr
ee s
pecie
s lis
t’ cr
iteria
fa
ctor
s m
atric
es
teris
tic
site
for
tree
in st
reet
co
nditio
ns
1 2
3 4
5 6
7 8
9 10
11
12
13
14
Prim
ary
I cr
iteria
2
Tree
size
an
d fo
rm/-
site
phys
ical
limita
tion
Site
gro
wth
cond
itions
/- tre
e en
viron
men
t su
itabi
lity
3 Tr
ee
main
tena
nce
requ
irem
ents
/- sit
e ph
ysica
l- sp
atia
l ch
arac
teris
tics
Seco
ndar
y 1
crite
ria
Tree
ae
sthe
tics
2 Tr
ee
cont
ribut
ion
to e
nviro
nmen
t/-
site
fimct
iona
l pr
oblem
s
Size
Form
Extre
me
tem
pera
ture
Vu
lnera
bility
to
air
pollu
tion
Decid
uous
/- ev
ergr
een
Grow
th
patte
rn
Root
Br
owth
Gr
owth
ra
te
Life
expe
ctan
cy
Crow
n de
nsity
Co
lour
Text
ure
Parti
cles
abso
rptio
n
Noise
ins
ulatio
n
Narro
w M
ediu
m
(The
list
was
pre
-scr
eene
d fo
r siz
e an
d fo
rm)
sidew
alk
size
Elec
tric
A+B
lines
gr
oups
2 M
ount
ain
Low
mou
ntain
a3
.
clim
ate
clim
ate
Pollu
ted
Resis
tanc
e to
air
air
poll
ution
’
Expo
sed
site
Narro
w pa
ssag
e Pa
ved
sidew
alk
Norm
al
Ever
gree
n .
0 l
Decu
rrent
Not
aggr
essiv
e ro
ot
Med
ium
l
.
.
Norm
al
Med
ium-lo
ng
l 0
.
Not
appli
cable
No
t ap
plica
ble
Not
appli
cable
Ai
r po
llutio
n
Mini
ma1
Grey
or
dark
gre
en
Med
ium
Data
not
av
ailab
le’
Tran
spor
t Da
ta n
ot
avail
able
0 .
l
‘List
of
14 m
ediu
m-s
ized
trees
: 1.
Acac
ia d
ealab
aita;
2.
Ace
r ob
tusif
oliu
m;
3. A
kctry
on
tom
enta
sum
; 4.
Albi
zzia
julibr
issin;
5.
Cel
tis a
ustra
liq
6. C
eltis
ges
her
aziv;
7. E
ryth
rina
cora
ioak
mod
rum
; 8.
Gra
villea
ru
bust
a; 9
. Jun
eper
us;
10. L
oges
trom
ia sp
ecio
sa;
11. O
lea e
urop
aea;
12
. Que
rcus
ilex
, 13
. Sch
inus
tere
binth
i- fo
liw,
14. T
amar
ix ar
ticul
ata
‘Pre
ferre
d tre
e fo
rms:
A =
roun
d ty
pe;
B =
colum
nar
and
palm
s.
‘* in
dica
tes
the
tree
is no
t su
itable
for
the
pre
ferre
d cr
iteria
. ‘L
ack
of v
alida
ted
data
on
thes
e fa
ctor
s in
the
case
stu
dy m
ade
their
inc
lusion
in
the
evalu
ation
im
poss
ible
.
URBAN STREET TREE PLANNING IN ISRAEL 211
characteristics were evaluated with preferred measures. The measures indicate levels in each criterion that were preferred in the street tree screening process.
Screening was carried out in five levels. (a) The primary physical conditions of the site, with narrow sidewalks and overhead power lines, limited the type of arrangement, size and form of the trees that could be considered to those of medium size and of the round and col- umnar form groups. For the same reason, the proposed formal arrangement type was cho- sen. (b) In the second matrix, the lack of suit- able growth conditions in the site eliminated four trees ( 1, 7, 13, 14). They were not suita- ble to the mountain climate prevailing on the site. (c) In the last level of primary criteria screening, unsuitable visual and functional characteristics eliminated an additional eight species. Levels (d) and (e) dealt with second- ary evaluation criteria. There were no limita- tions on the use of the remaining two species because visual-functional characteristics and environmental problems were non-mandatory requirements.
Two species, Nos. 2 and 11, Acer obtusifol- ium and Olea europaea, respectively, satisfied the required profile for the chosen site. The analysis indicated that the two species were equally preferred, both satisfied the secondary aesthetic factors in the fourth matrix and data on site/tree environmental constraints were not available. Data on the last two matrices would have shown differences in suitability, the species that would satisfy criteria of higher im- portance would be selected.
DISCUSSION AND CONCLUSIONS
This article deals with methodological as- pects of the street tree planning process, but not with those aspects which are related to the de- velopment of resource description, and inven- tory and tree management processes.
A strong relationship exists among the three parts of the whole process, in content, reason-
ing and in the method of analysis. However partial description of one stage, as in this pa- per, could not provide a full explanation or sufficient details to consider the many solu- tions presented in the planning stage. This pre- sentation provides a description of the ideas and the skeleton of a process for making deci- sions rather than fully documenting a “how to do it” process.
The methods for data processing described above apply objective data, particularly con- cerned with site characteristics. On the other hand, content dealing with visual-design as- pects of the environment is largely subjective in nature. Regardless of the degree of data ob- jectivity, implementation processes will be highly influenced by ideas and design concepts chosen by various decision makers during planning and implementation. They will deter- mine the final quality and degree of objectivity of the plan. The processes and content sug- gested above should be seen as subjective/ob- jective bases on which the final plan will be produced.
The process is described as a static condi- tion, but in reality the development of a street tree plan is a dynamic endeavour which con- tinues for many years and in ever-changing en- vironments. In the future, it will be important to adopt decision-making processes to changes in site conditions. This could be done either through re-evaluation of the suitability of cri- teria and measures, or by reconsideration of the levels of importance and re-evaluation of the effect of implementation of a given planning stage in the future.
The process is suitable for implementation in cities of different scales. Several changes could be made in the type and intensity of the inventory to suit the size, lay-out and a given combination of characteristics. A city with a large existing street tree system, but with no new trees to be planted, would be likely to in- vest its resources in planning for maintenance. A new location which is expecting additional physical growth would invest more in the de-
212 S. AMIR AND A. MISGAV
velopment of a plan for new planting. The pro- posed process could be adapted to suit differ- ent scales and characteristics of various systems.
The process could also be used for managing other vegetation resources found in public parks, private yards and other urban green open spaces. This would require some adjust- ment of the descriptive model and criteria, and resources to suit vegetation dispersal patterns in the open spaces.
The experience with the case study has shown that for the process to be fully taken ad- vantage of, it is important to improve data availability for a site for which a plan is being prepared. It is important to develop data on the functional-environmental characteristics of the site. In our case, data were not available on air pollution and noise levels. Also needed is a broader tree list that contains a variety of spe- cies. Such additional data will help justify the detailed list of criteria provided for in the process.
Clearly, where data are not available and the number of criteria that could be used is re- stricted, the level of details that a planting plan could arrive at would be confined and the po- tential contributions of the overall process will be limited.
ACKNOWLEDGEMENTS
This research was funded partly by the KKL Forestry Department, to which the researchers are grateful.
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