TILIA'S PHYSICAL DIMENSIONS OVER TIME
by Flemming Kjølstad Larsen1 and Palle
Kristoffersen2
Abstract. Tree height, trunk height, trunk diameter,
crown base, and crown radius were measured on 331 trees
growing in urban environments (Tilia cordata, T. europaea, T.
euclora, and T. platyphyllos). Regression analyses revealed
quadratic correlation between age and size for all relationships.
Growth formulas and growth rates were derived and growth
curves compiled. The results can be used for forecasting
Tilia's physical dimensions as functions of time and
environment and with it for planning and assessing the consequences
of Tilia tree-planting schemes in urban environments.
When implemented as a computer-aided design (CAD)
application, these relationships can form the basis for dynamic
illustration of a project.
Key Words. Tilia; computer-aided design; urban
trees; tree growth.
All architectural uses of trees must fulfill spatial
and aesthetic functions. The visual impression is vital
because first impressions are based on what we see,
with size and form as the dominant factors. Purposeful
work with design of urban tree schemes demands a
thorough knowledge of individual species' growth potential
in relation to the given growing environment.
This study describes and determines the
relationships between age and tree height, age and
trunk height, age and trunk diameter, age and crown
base, age and crown radius, and for unshaded trees
and trees with their crowns affected by shading,
when their crowns are growing together.
The purpose of this study is to make it possible
at any given time to forecast the dimensions of the
trees as functions of age. It should be possible to use
this tool to estimate the consequences of planting
grids, and in landscape design, to provide the
information needed for better, more realistic planting plans.
When implemented as a computer-aided design (CAD)
application, these relationships can form the basis
for the dynamic illustration of a project.
MATERIALS AND METHODS
The data were recorded in Copenhagen, Denmark,
55° 42' N, 12° 35' E. Copenhagen is characterized by
a coastal climate. All measurements were carried out
on trees that seemed undamaged and unrestricted by wind.
The data were recorded during the period
February through April 1997. It covers 331
Tilia (T. cordata, T. europaea, T.
euclora, and T. platyphyllos), which were
distributed as 251 trees at 25 locations in rows
along streets, supplemented by measurements taken from
80 trees in nurseries (Table 1). All were chosen in light
of age, with a view toward describing growth
throughout the chosen period of 0 to 100 years.
The ages of the plantations were calculated
from park administrations' plant records. If tree size at
the time of establishment was not known, then 10
years, which corresponds to a trunk circumference of 18
to 20 cm (7 to 8 in.), was added to the age.
A number of trees representative of each
plantation were chosen and measured (Table 1). The choices
were made on the basis of the visual impression of the
trees' dimensions. Extremes were excluded (e.g.,
extremely small trees, damaged trees). The distances
between rows and plants were measured with a tape
measure and were specified as the average of at least three
measurements, rounded off to the nearest 5 cm (2 in.).
Tree height, trunk height (from the ground to the bottom
of the first influential branch), and crown base
height (from the ground to underneath of the crown)
were measured by clinometric triangulation and rounded
off to the nearest 5 cm. Trunk diameters were
calculated from the external trunk circumference, as
measured with a tape measure at a height of 1 m (3.3 ft)
(relating them to Danish commercial sizes) and rounded off
to the nearest whole centimeter. Crown radii were
measured along the ground surface with a tape
measure from the center of the trunk to the tip of the most
remote downward-projecting shoot, rounded off to
the nearest 5 cm.
Table 1. Age and size measurements of four
Tilia species.
| Number | Age | Tree height (m) | Trunk height (m) | Trunk diameter (cm) |
Species/location | of trees | year | Average | SDz | Average | SDz | Average | SDz |
T. cordata |
Bellahoejparken | 10 | 32 | 9.23 | 0.85 | 6.62 | 0.70 | 21.77 | 1.93 |
Irlandsvej II | 10 | 20 | 8.62 | 1.37 | 5.94 | 0.86 | 14.39 | 2.65 |
Landgreven | 10 | 48 | 12.44 | 1.73 | 9.24 | 1.59 | 26.87 | 2.72 |
Birkholmx | 10 | 8 | 3.89 | 0.47 | 2.06 | 0.15 | 5.35 | 0.39 |
T. euchlora |
Borgervænget I | 10 | 95 | 16.46 | 1.95 | 12.22 | 1.74 | 57.52 | 4.24 |
Borgervænget II | 10 | 33 | 7.28 | 0.64 | 4.77 | 0.58 | 14.01 | 1.06 |
T. europaea |
Allersgade | 10 | 24 | 9.55 | 0.53 | 7.18 | 0.61 | 19.19 | 3.70 |
Allersgd.-Thorsgd. | 10 | 24 | 7.63 | 0.60 | 5.00 | 0.80 | 14.77 | 1.31 |
Blaagrd. Plads | 10 | 108 | 17.52 | 2.05 | 13.31 | 2.57 | 49.37 | 3.53 |
Femte Juni Plads | 10 | 92 | 17.98 | 1.53 | 13.68 | 1.28 | 51.85 | 4.89 |
GarnisionsKirkegrd. | 10 | 17 | 6.67 | 0.43 | 4.68 | 0.36 | 11.08 | 1.10
|
Irlandsvej I | 10 | 77 | 17.10 | 1.73 | 12.47 | 2.24 | 44.15 | 5.86
|
Kastrup Fort | 10 | 25 | 10.11 | 0.57 | 7.07 | 0.72 | 25.69 | 2.94
|
Noerre Allé | 10 | 17 | 8.50 | 0.84 | 5.51 | 0.80 | 19.70 | 4.06
|
Noerrebroparken | 10 | 65 | 18.92 | 0.95 | 15.27 | 1.66 | 51.73 | 3.53
|
Remiseparken | 12 | 40 | 9.42 | 0.60 | 6.80 | 0.68 | 24.14 | 3.42
|
Ryvang Allé | 10 | 105 | 17.81 | 1.26 | 13.64 | 1.17 | 53.32 | 4.99
|
Roedkilde Plads | 10 | 82 | 20.53 | 0.69 | 16.00 | 0.96 | 50.58 | 4.40
|
Roedovre Raadhus | 8 | 51 | 11.27 | 0.44 | 8.65 | 0.63 | 27.22 | 4.37
|
Stengade | 10 | 26 | 9.89 | 0.82 | 7.72 | 0.92 | 18.75 | 1.62
|
Soendermarken | 10 | 39 | 15.21 | 0.98 | 11.86 | 0.91 | 33.30 | 2.21
|
Ulrich Birks Allé | 10 | 107 | 18.39 | 1.67 | 14.85 | 1.82 | 63.44 | 7.44
|
Vestre Kirkegaard | 12 | 112 | 25.09 | 1.67 | 20.62 | 2.28 | 53.58 | 17.33
|
Birkholmx | 29 | 2 | 1.64 | 0.36 | - | - | 0.76 | 0.28
|
Birkholmx | 5 | 4 | 2.79 | 0.56 | 1.80 | 0.06 | 3.44 | 0.42
|
Birkholmx | 10 | 5 | 3.18 | 0.23 | - | - | 3.34 | 0.43
|
Birkholmx | 10 | 7 | 3.51 | 0.26 | 2.05 | 0.16 | 4.11 | 0.35
|
Birkholmx | 10 | 8 | 3.89 | 0.47 | 2.06 | 0.15 | 5.35 | 0.39
|
Birkholmx | 9 | 9 | 4.53 | 0.40 | 2.79 | 0.41 | 6.44 | 0.84
|
Birkholmx | 7 | 12 | 5.80 | 0.77 | 3.84 | 0.69 | 9.50 | 1.77
|
Birkholmx | 10 | 25 | 11.84 | 0.87 | 9.35 | 0.80 | 27.82 | 2.14
|
T. platyphyllos
|
Fælledparken | 10 | 31 | 9.56 | 1.88 | 7.20 | 1.89 | 26.04 | 5.16
|
Hulgaards Plads | 9 | 60 | 14.94 | 1.78 | 12.05 | 1.62 | 49.06 | 6.11
|
Lyngbyvej | 10 | 31 | 9.09 | 1.05 | 6.17 | 1.14 | 22.00 | 1.71
|
zStandard deviation.
|
xTrees in nurseries.
|
Table 2. Growth rates of Tilia cordata, T.
europaea, and T. platyphyllos.
Y* | b1 | b2
|
Tree height | 0.3846 | -0.0038
|
Trunk height | 0.1061 | -0.0012
|
Trunk diameter | 0.8778 | -0.0066
|
Crown base | 0.0891 | -0.0010
|
Crown radius, unshaded | 0.1257 | -0.0010
|
Crown radius, shaded | 0.1358 | -0.0016
|
*Y = b1d + b2d; d = age.
|
Table 3. Growth formulas of Tilia cordata, T.
euro-paea, and T. platyphyllos.
Y* | b1 | b2 | r2 | P | n
|
Tree height | 0.3846 | -0.0019 | 0.9703 | 0.0001 | 299 |
Trunk height | 0.1061 | -0.0006 | 0.9272 | 0.0001 | 227
|
Trunk diameter | 0.8778 | -0.0033 | 0.9725 | 0.0001 | 288
|
Crown base | 0.0891 | -0.0005 | 0.9152 | 0.0001 | 229
|
Crown radius, |
|
unshaded | 0.1257 | -0.0005 | 0.9461 | 0.0001 | 601
|
Crown radius, |
|
shaded | 0.1358 | -0.0008 | 0.9356 | 0.0001 | 463
|
*Y = b1 + b2d2; d = age.
|
The variability for each plantation was
examined and considered homogeneous. The statistical
analyses were carried out using SAS.
Analyses of variance for all four species (T. cordata,
T. euchlora, T. europaea, and T.
platyphyllos) and for a group that included
T. cordata, T. europaea, and T.
platyphyllos revealed a significant species-related effect on
dimensions. As representatives of the Tilia family in
the environment in question, T. cordata, T.
europaea, and T. platyphyllos can be treated in common.
T. euchlora, which is differentiated by its lower growth rate (Table 1),
is ignored in the data set and then in further analysis.
Regression analyses were conducted for T. cordata,
T. europaea, and T. platyphyllo, collectively, to
determine whether the relationships between age and 1)
tree height, 2) trunk height, 3) trunk diameter, 4)
crown base, and 5) crown radius of both unshaded trees
and shaded trees (in avenues and rows) were linear
(Y = b1d) or quadratic
(Y = b1x +
b2d2).
[Y is the examined parameter (tree height, trunk diameter, etc.),
d is age, and b1 and
b2 are constants.] Growth rate guides
(Table 2) were obtained by differentiating the
relationships found through regression analysis.
RESULTS AND DISCUSSION
The regression analyses revealed quadratic
correlations for all relationships both for trees affected
by shade and for unshaded trees (Table 3 and Figure 1).
The correlation between age and tree height
(r2 = 0.97, P = 0.0001) showed that height increases
with age, to 19.5 m (64 ft) at an age of 101 years. Thus,
in an urban growing environment, the height curve
gives a reasonably certain picture of Tilia's height as a
function of age in the interval 0 to 100 years.
The tree heights given by the relationships of
this study were lower than those in the literature. For
in
stance, Johnson (1975) states that Tilia
europaea attains a height of about 10 m (33 ft) at the age of 20
years and that the tree can attain a height of up to 40 m
(132 ft). This study shows that, in the urban
environment, Tilia attains a height of only about 7 m (23 ft) after
20 years and a maximum height of about 20 m (66
ft) after 100 years.
Growth in height decreased steadily as age
increased. According to the calculations,
Tilia grows to about 5 m (16 ft) during the first 15 years, whereas the height
increase from 85 to 100 years is only about 0.5 m (20 in.).
The correlation between age and trunk diameter
(r2 = 0.97, P = 0.0001) shows that the expected
trunk diameter after 100 years is about 55 cm (22 in.).
The correlation between age and trunk height
(r2 = 0.97, P = 0.0001) shows that trunk height
increases with age. The correlation between age and crown
base shows that the crown base increases marginally
with age (r2 = 0.92, P = 0.0001). These values are
expected in both cases, because the branching height and
crown base are regulated by pruning of the lowest
branches. In urban locations, these lowest branches frequently
interfere with traffic; thus, they are often removed.
Further crown lifting often occurs for aesthetic reasons.
The correlations between age and crown radius
for both unshaded trees and shaded trees show that
crown diameter increases with age. The
r2 assumed values of 0.95 and 0.94, respectively. The coefficients of
correlation largely coincide up to the age of about 45 years,
at which time the growth rate of the crown radii of
trees affected by shade flattens out. From that point
on, shade (the effects of which depend on the
distances between rows and plants) exerts a strong influence
on crown radius, which, thereafter, only increases
very slowly.
TREE HEIGHT
CROWN BASE
TRUNK HEIGHT
TRUNK DIAMETER
CROWN RADIUS, SHADED
CROWN RADIUS, UNSHADED
Figure 1. Tree age versus size parameters of
Tilia cordata, T. europaea, and T.
platyphyllos.
CONCLUSION
In this study, we have described Tilia's growth from
0 to 100 years, with primary emphasis on the
younger years because that is when planners traditionally
attempt to forecast its growth.
The duration of the period for which it is
actually possible to plan in urban environments presents
us with a new problem. Many studies have shown
that the average life span of urban trees is very short
and can be as low as 10 to 15 years (Foster and
Blaine 1978; Gilbertson and Bradshaw 1990; Nowak et
al. 1990; Miller and Miller 1991). This study shows
that within the actual life span of urban trees, it will
be difficult to obtain the expected architectural and
aesthetic function.
The new tools presented here make it possible
to obtain a dynamic picture of the varying
dimensions and visual impression of the trees over time.
With these functions, applications for dynamic
illustrations can be made more realistically in
urban environments using tools such as AutoCAD.
We described the Tilia species commonly
used (except for T. euchlora) to prepare a simple
planning tool for the most popular genus of urban tree in
Denmark. The species-related differences encountered
in the plantations were only minor and lacked
significance in this context.
LITERATURE CITED
Foster, R.S., and J. Blaine. 1978. Urban tree survival: Trees
in the sidewalk. J. Arboric. 4(1):14-17.
Gilbertson P., and A.D. Bradshaw. 1990. The survival of
newly planted trees in inner cities. Arboric. J. 14: 287-309.
Johnson, H. 1975. The International Book of Trees
(Danish version: Traernes Bog). Editor Aa. Andresan.
Lademann 1975: 174-175, 287-288.
Miller, R.H., and R.W. Miller. 1991. Planting survival
of selected street tree taxa. J. Arboric. 17(7):185-191.
Nowak, D.J., J.R. McBride, and R.A. Beatty. 1990.
Newly planted street tree growth and mortality. J.
Arboric. 16(5):124-129.
Acknowledgments. We thank Copenhagen's park
districts, the Park Departments of Frederiksberg and
Roedovre Local Council, the Danish Palaces and Properties Agency,
Palaces and Properties Agency, Garnisons Cemetery, Vestre
Cemetery, and the public building society, Socialt Boligbyggeri,
for the great courtesy and helpfulness they showed when
we were trying to obtain planting plans.
1*Landscape Architect
Praestebakken 16
DK-2610 Roedovre
Denmark
2Ph.D., Research Landscape Architect
Danish Forest and Landscape Research Institute
Hoersholm Kongevej 11
DK-2970 Hoersholm
Denmark
*Corresponding author.
Résumé. Sur 331 arbres-Tilia cordata, T. europea, T.
euclora et T. platyphyllos-localisés en environnement urbain, on a mesuré
la hauteur de l'arbre, la hauteur du tronc, le diamètre du tronc,
le diamètre de la couronne et le rayon de cime. Les analyses
de régression ont révélé une corrélation quadratique entre l'âge
et la dimension dans toutes les relations. Une formule
de croissance ainsi que des taux de croissance ont été dérivées,
et des courbes de croissance compilées. Les résultats peuvent
être utilisés pour prévoir les dimensions physiques du tilleul
en fonction du temps et de l'environnement, et aussi pour
planifier et évaluer les conséquences de la plantation du tilleul sur
le schéma de l'environnement urbain. Lorsque implantées
dans une application de type CAD, ces relations peuvent fournir
une base pour l'illustration dynamique d'un projet.
Zusammenfassung. Von 331 Bäumen aus urbanen
Gebieten (Tilia cordata, europaea, euclora,
platyphyllos) wurde die totale Höhe, Stammhöhe, Stammdurchmesser, Kronenbasis und
-radius gemessen. Die Regressionsanalyse enthüllte
quadratische Korrelationen zwischen Alter und Größe für alle
Beziehungen. Wachstumsschemata und Wachstumsraten wurden und
Wachs-tumskurven erstellt. Die Ergebnisse können zur Vorhersage
der
physikalischen Dimension von Tilia als Funktion über die
Zeit und Umwelt genutzt werden und damit auch für Planung
und Untersuchung der Auswirkungen von Lindenpflanzungen
in urbanen Gebieten. Wenn diese Beziehungen als CAD
Anwend-ung implementiert werden, können sie die Basis für
eine Dynamische Illustration eines Projektes bilden.
Resumen. Se midió en 331
árboles (Tilia cordata, T. europaea,
T. euclora, y T. platyphyllos) que crecen en ambientes urbanos,
la altura del árbol, altura del tronco, diámetro del tronco, base de
la corona y radio de corona. Los análisis de regresión
revelaron correlación cuadrática entre la edad y el tamaño para todas
las relaciones. Fueron derivadas las fórmulas de crecimiento y las
tasas de crecimiento y de allí se compilaron curvas de
crecimiento. Estos resultados pueden ser usados para pronosticar
las dimensiones físicas de los Tilia, como funciones de tiempo
y ambiente y con ello para la planeación y evaluación de
las consecuencias de plantaciones con árboles de
Tilia en ambientes urbanos. Cuando se implementan como una aplicación en
Diseño Asistido por Computadora (CAD), estas relaciones pueden
formar las bases para la ilustración dinámica de un proyecto.