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On geometrical scaling of Cayley trees and river networks
Peter Molnar*
Institute of Hydromechanics and Water Resources Management, Swiss Federal Institute of Technology,
ETH Hoenggerberg, 8093 Zurich, Switzerland
Received 18 February 2004; revised 26 October 2004; accepted 8 February 2005
Abstract
Geometrical scaling properties of rooted Cayley trees generated by percolation on the Bethe lattice are analysed. Statistical
scaling relations between the characteristic topological length and width dimensions and cluster size as a function of the lattice
occupation probability are identified analytically and by simulation. Cayley trees generated with a constant occupation
probability exhibit statistical self-affinity at small scales, but approach self-similarity with increasing size, similar to Markov
branching models under random topology postulates. The position of the peak of the topological width function is
asymptotically invariant with regard to cluster size. However, Cayley trees grown with a constant occupation probability are
generally too elongated. A numerical experiment in which the occupation probability on the Bethe lattice decreased
systematically on unbranched links as the cluster grew provided average length to width ratios more comparable to river
network data. Although the occupation probability uniquely determines the probability of termination, continuation and
branching, it is difficult to meaningfully connect it to physical processes involved in river network evolution.
q 2005 Elsevier B.V. All rights reserved.
Keywords: Cayley trees; Percolation; Scaling; River networks
1. Introduction
This study analyses topological properties of
hierarchical branching structures called rooted Cayley
trees, generated by percolation on the Bethe lattice—a
structure commonly used to simulated phase tran-
sitions in physics (e.g. Stauffer and Aharony, 1994).
Special attention is devoted to branching and
geometrical scaling properties of clusters grown on
the Bethe lattice, for example, the relations between
cluster diameter, width and size, as a function of
0022-1694/$ - see front matter q 2005 Elsevier B.V. All rights reserved.
doi:10.1016/j.jhydrol.2005.02.035
* Tel.: C41 1 6332958; fax: C41 1 6331061.
E-mail address: [email protected].
the lattice occupation probability. The Bethe lattice in
which each site has three neighbours is considered, in
this way the simulated trees are topologically
analogous to river networks. There is also a physical
resemblance in that rooted Cayley trees expand by
headward growth, much like natural drainage systems
eroding the landscape do.
The topological structure of river networks has
been studied extensively since the development of the
notion of topological randomness by Shreve (1967)
and later works (see Smart, 1972, for a review).
Shreve (1974) also investigated the geometrical
scaling of river networks, and assuming topological
randomness and the statistical independence of
Journal of Hydrology 322 (2006) 199–210
www.elsevier.com/locate/jhydrol
P. Molnar / Journal of Hydrology 322 (2006) 199–210200
interior and exterior links and drainage areas, he
determined the relation between the expected topolo-
gical mainstream length l of networks with a given
magnitude m (lfmh). This, and subsequent studies
showed that in topological terms random river
networks approach a self-similar configuration as
they grow in size (h/0.5) (e.g. Mesa and Gupta,
1987; Troutman and Karlinger, 1989; Agnese et al.,
1998).
However, observations of the geometrical scaling
of natural river networks showed a tendency for h to
be generally larger than 0.5, this became known as
Hack’s law (Hack, 1957). There are basically two
reasons why hO0.5: (a) the mainstream length is
itself a function of scale and has a fractal dimension
larger than 1; (b) river basins are self-affine structures
and elongate with increasing size. In fact a combi-
nation of these two factors likely leads to Hack’s law
in natural river networks (Rigon et al., 1996). Here I
focus on the second aspect, that is the self-affinity of
river networks in the context of their topological
structure. This study builds on many previous
analyses of the scaling invariance properties of natural
river networks, and those simulated using versions of
the random topological postulates and by lattice
percolation (e.g. Jarvis and Sham, 1981; Meakin
et al., 1991; Nikora and Sapozhnikov, 1993; Maritan
et al., 1996; Rigon et al., 1996; Costa-Cabral and
Burges, 1997; Dodds and Rothman, 2000; Niemann
et al., 2001; Veitzer and Gupta, 2001). These
investigations have contributed considerably to our
understanding of the signature of randomness in river
network formation, and to the possible connections
between the geomorphological structure and hydro-
logical response.
The main questions in this simulation study
address the geometrical scaling properties of random
clusters (e.g. characteristic width, length, width
function) grown on the Bethe lattice. For example,
do the resulting trees exhibit self-similarity or
-affinity; how do they differ from the standard Markov
birth–death branching process; and is the observed
statistical scaling behaviour substantially different
from that of natural river networks? What this
simulation study does not address is the causal aspect
of river network formation, i.e. the thesis that both
chance and necessity in the form of energy optimality
act together to shape river network topology
(e.g. Rodriguez-Iturbe and Rinaldo, 1997; Rinaldo
et al., 1998).
Of the numerous simulation studies of river
networks conducted in the past, this numerical
experiment is most similar to studies of the random
topological model of Shreve (1967) by the discrete or
continuous Markov process (e.g. Mesa and Gupta,
1987; Troutman and Karlinger, 1989; Agnese et al.,
1998) and the topological headward growth model of
Howard (1971). Here river links on the Cayley tree
cluster have a length, which is a function of the
occupation probability of the lattice (assumptions are
not made a priori on the link length distributions). The
Bethe lattice is not a constrained two-dimensional
structure, unlike the lattice models used for random
walk simulations of river networks (e.g. Leopold and
Langbein, 1962; Scheidegger, 1967; Meakin et al.,
1991; Nikora and Sapozhnikov, 1993). The occu-
pation probability uniquely determines the probability
of termination, continuation and branching. These
probabilities are fundamental for river network
topology (e.g. Howard, 1971; Stark, 1991) and are
investigated in detail.
The paper is organised as follows. Section 2
reviews the basic properties of rooted Cayley trees
and their simulation. Section 3 focuses on the issue of
topological self-affinity in generated clusters. Section
4 discusses the statistical scaling properties of the
topological width function. Section 5 gives some
comparisons of scaling results with river network
data, and Section 6 summarizes the main conclusions.
2. Rooted Cayley trees
Rooted Cayley trees are generated here by
percolation on the Bethe lattice, i.e. a lattice
consisting of sites and bonds in which every site has
z neighbours which are occupied with an occupation
probability p. For the river network analogue of
Cayley trees the branching number zZ3, as every site
in a river network has one downstream link and a
maximum of two upstream links. If an occupied site
has only one occupied neighbour it is a surface site, if
two neighbours are occupied it is a midstream site,
and if all three neighbours are occupied it is a junction
site. The bonds of a cluster between two junction sites
constitute a link. The connected structure of occupied
P. Molnar / Journal of Hydrology 322 (2006) 199–210 201
sites is called a cluster, or tree. In the generation of a
rooted Cayley tree, an arbitrary (occupied) site is
chosen as the origin of a cluster, and one of its bonds
is assigned to lead to another occupied site called the
root. The growth of the cluster proceeds in a random
manner upstream from the root until only surface sites
are left. The size of a cluster n (the total number of
occupied sites it contains) increases with the occu-
pation probability p. At a critical probability pZpc(percolation threshold), a nonzero probability exists
that an infinite cluster spanning the entire lattice is
generated. This critical probability is pcZ1/(zK1),
that is pcZ1/2 for the Bethe lattice with zZ3 (see
Stauffer and Aharony, 1994, p. 28). The behaviour
just below the percolation threshold, where large
clusters are generated, is the focus of this study. In
branching theory, this is equivalent to the statement
that the probability of extinction is equal to 1 if and
only if the mean number of offspring per site S is less
than 1. On the Bethe lattice SZ2p, so p!1/2 (see
Karlin, 1966, p. 291).
If we think of rooted Cayley trees as topological
equivalents of river networks, and assume that sites
and bonds have on the average constant drainage areas
contributing to them (we force the trees into two-
dimensional space), we can identify a length and
width dimension of the trees similarly as we would for
a river network (e.g. Troutman and Karlinger, 1989;
Agnese et al., 1998). Let us define k as the stage
of development of a tree in percolation, see Fig. 1
Fig. 1. Example of a generated rooted Cayley tree with nZ30,
kmaxZ9, jmaxZ5.
(kZ0 at the root). At every stage, there are iZ2kK1
possible sites to be occupied, and j of these sites in the
cluster are occupied with probability p. Let us denote
the maximum stage of development of a tree by kmax,
and consider it to be a characteristic length scale of the
tree (the topological diameter of the river network).
Similarly, let us consider that the maximum number
of occupied sites at a stage in a tree jmax represents the
characteristic width scale of the tree (the topological
peak of the width function of the river network).
These two topological quantities can be used to
identify the self-affinity of generated trees, and be
compared to known results of river networks. An
example of a rooted Cayley tree is shown in Fig. 1.
The mean cluster size hni of a rooted tree is
dependent on the occupation probability, and can be
estimated from the following reasoning. Let us define
the mean number of sites that belong to one branch
from the origin as T. Since sub-branches are
statistically equivalent to branches, then TZp(1C2T), which gives TZp/(1–2p). The mean cluster
size (to which the origin belongs) is equal to the
origin, the root, and the mean size of the two upstream
branches, i.e. hniZ2C2T. This gives the following
relation between the mean cluster size and the
occupation probability below the critical probability
p!pc:
hniZ 2ð1KpÞ=ð1K2pÞ (1)
or in the scaling field pc–p:
hniZ ð1KpÞ=ðpc KpÞ (2)
Therefore the mean cluster size of a rooted Cayley
tree scales as
hnif ðpc KpÞKg (3)
with scaling exponent gZ1 (e.g. Stauffer and
Aharony, 1994). An example from a sequence of
generated trees with different p values is shown in
Fig. 2.
The random topological model (RTM) of Shreve
(1967) assumes that the probabilities of branching and
termination in a random river network tree are
independent and equal to 0.5. On the other hand,
trees generated on a Bethe lattice allow for a link to
continue without branching. On a Bethe lattice with
zZ3 the probabilities of termination p0, continuation
Fig. 2. The scaling of mean rooted cluster size hni in the field pcKp.
Each point is the mean from 10,000 generated trees with occupation
probability p. The line represents the theoretical relationship for hni
from Eq. (1).
P. Molnar / Journal of Hydrology 322 (2006) 199–210202
p1, and branching p2 are:
p0 Z ð1KpÞ2; p1 Z 2pð1KpÞ; p2 Z p2 (4)
These relations are shown in Fig. 3. Note that at the
percolation threshold pZpcZ1/2, p1Z0.5 and p0Zp2Z0.25. So compared to the RTM and its Markov
model applications, branching is less promoted on the
Bethe lattice.
A river link on a Cayley tree can consist of one or
more bonds, and thus has a length dimension. The link
lengths of a cluster are discrete and geometrically
distributed with a probability mass function:
PrðLZ kÞZ pkK11 ð1Kp1ÞZ pkK1
1 ðp0 Cp2Þ;
kZ 1; 2;.; kmax
(5)
Fig. 3. Probability of termination p0, continuation p1, and branching p2 (lef
(right) as a function of the occupation probability p on the Bethe lattice w
Note that both the probability of termination and of
branching add to the overall probability mass, the
former are external links and the latter are internal
links in the cluster. Fig. 4 shows that for pZpcZ0.5
external and internal links are equally likely to occur.
However, for p!pc external links are more likely.
The mean link length
hLiZ 1=ð1Kp1ÞZ 1=ðp0 Cp1Þ (6)
varies between 1 and 2 as a function of the occupation
probability, see Fig. 3. At pZpcZ0.5, the mean link
length reaches a maximum of 2. Below and above the
percolation threshold the mean link length decreases
to 1, because either termination or branching
dominates cluster growth. Also shown in Fig. 3 is
the coefficient of variation of L, which is equal to
CVðLÞZffiffiffiffiffi
p1p
, and reaches a maximum at pZpc. The
geometric probability mass function (and its expo-
nential continuous counterpart) for the link lengths is
convenient because it can be used to derive asympto-
tic results for the length and width scales of river
networks (e.g. Mesa and Gupta, 1987; Troutman and
Karlinger, 1989).
3. Self-affinity of clusters
The first geometrical scaling property of Cayley
trees that is investigated is topological self-affinity. A
statistically self-affine object is one that is anisotropic,
and in two-dimensional space grows disproportio-
nately in both directions. It has been argued that river
t); and mean link length E(L) and the coefficient of variation CV(L)
ith zZ3.
Fig. 4. The probability mass functions for link lengths on the Bethe lattice with occupation probability pZ0.5 (left) and pZ0.3 (right). The
contributions of external and internal links to the overall probability Pr(LZk) are indicated.
P. Molnar / Journal of Hydrology 322 (2006) 199–210 203
basins exhibit self-affinity at some scales. To explore
the self-affine behaviour of clusters grown on the
Bethe lattice, let us define the following scaling
relationships between mean characteristic length and
width scales conditioned on the cluster size n (e.g.
Nikora and Sapozhnikov, 1993):
hkmaxjnifnl; hjmaxjnifnt (7)
The exponents l and t describe the geometrical
scaling behaviour of the trees (lCtZ1 is indica-
tive of tree compactness). Furthermore, if trees are
geometrically self-similar, then lZtZ1/D, where
D is the fractal dimension of the tree (e.g.
Peckham, 1995). The fractal dimension of a
network that covers the entire drainage area is
nearly space filling, so D/2 (e.g. Tarboton et al.,
1988). For self-affine trees, lst, and both
exponents are needed to fully describe the geo-
metrical scaling of the cluster. The Hurst coefficient
may be used to quantify self-affinity:
H Z t=l (8)
For self-similar trees HZ1 and for self-affine
trees H!1 (e.g. Nikora and Sapozhnikov, 1993;
Rigon et al., 1996).
In river network analyses, the scaling of main-
stream length with drainage area is known as Hack’s
law: LfAh, with the exponent h generally larger than
0.5 (Hack, 1957). This fact had been shown to be due
to a combined effect of the sinuosity (fractality) of the
streams and the self-affinity (elongation) of the basins
(Rigon et al., 1996). With the scaling described in
Eq. (7) we can test the self-affine interpretation of
Hack’s law for Cayley trees. Assuming that cluster
size scales as nfkmax jmax, we get:
hkmaxjnifnl=ðlCtÞ or hkmaxjnifn1=ð1CHÞ (9)
So the self-affine topological interpretation of
Hack’s law leads to (e.g. Nikora and Sapozhnikov,
1993; Rigon et al., 1996):
hZ l=ðlCtÞZ 1=ð1CHÞ (10)
For the self-similar case, HZ1 and hZ0.5, while
for the self-affine case H!1 and hO0.5. In the
topological interpretation we do not consider the
fractal dimension of the main stream. For an
explanation of the effect of the mainstream fractal
dimension of real river networks on h, see Rigon et al.
(1996) and Maritan et al. (1996).
To test the above scaling behaviour, 10,000 rooted
Cayley trees were generated on a Bethe lattice with a
range of occupation probabilities p. To eliminate the
confounding effect of very small clusters on the
statistics, only trees which contained more than three
junctions were considered in the analysis. The scaling
relationships of Eq. (7) are shown in Fig. 5. The
exponents l and t were determined by least squares
linear regression on log-transformed data; then H was
computed from (8) and h was computed from (10).
The results for l, H and h are shown in Fig. 6. The
main conclusion is that Cayley trees approach self-
similarity with increasing size; smaller trees are
generally self-affine with H!1, while self-similarity
is approached as n increases. It is also evident that
Fig. 5. Topological length and width scaling of generated Cayley trees (pZ0.499). Data points represent averages over exponentially distributed
integer classes of n (with NO30). Altogether 10,000 trees were generated, the largest tree had nZ434,199, kmaxZ2371, jmaxZ581. The
minimum and maximum bounds for the topological length come from basic considerations of cluster growth on the Bethe lattice: K0Zlog2 n
and K1ZnK2.
P. Molnar / Journal of Hydrology 322 (2006) 199–210204
the self-affine topological interpretation of Hack’s
exponent h is substantially different from the scaling
exponent l for smaller trees, which confirms that
affinity plays an important role in the geometrical
scaling of clusters. Results from a simulation by a
discrete Markov branching process under RTM
postulates also shows asymptotic self-similarity in
Fig. 6. That h approaches 0.5 with increasing network
size has been derived analytically for the RTM
Fig. 6. The scaling exponents l, h and H of generated Caley trees (left) an
squares linear regression on log-transformed data in classes of 50 points f
assuming exponential link lengths by Mesa and
Gupta (1987), see Fig. 6.
An additional test of asymptotical self-similarity
in Cayley trees can be obtained by looking at
higher order conditional moments of the scaling
relationships between kmax, jmax and cluster size n.
For example, under the simple scaling hypothesis
hk2maxjnifn2l hj2maxjnifn2t (11)
d the RTM (right). The exponents l and t were determined by least
rom Fig. 5 moving across the whole range of n.
Fig. 7. Coefficient of variation of kmax and jmax (top), the mean position of the peak of the width function k (center), and the mean
length/width ratio m (bottom) of generated Cayley trees and the discrete RTM as a function of cluster size n (Cayley trees were generated
with pZ0.499).
P. Molnar / Journal of Hydrology 322 (2006) 199–210 205
the coefficient of variation of kmax should obey:
CVðkmaxÞZ hk2maxjni0:5=hkmaxjniZ constant (12)
and the same should be true for CV(jmax) (e.g.
Rigon et al., 1996). Fig. 7 (top) confirms this
behaviour for the generated clusters on the Bethe
lattice and the RTM, where both coefficients of
variation are reasonably independent of n over a
large range of scales.
4. Scaling of the width function
The second investigated geometrical scaling prop-
erty of Cayley trees is the relative position of the peak
of the topological width function k defined as:
kZ kp=kmax (13)
where
kp Zminfk : jZ jmaxg (14)
is the stage k at which jZjmax in a single cluster; k is
constrained by (0,1]. The scaling of the mean of k
conditioned on cluster size n, hkjni, was found to
P. Molnar / Journal of Hydrology 322 (2006) 199–210206
asymptotically approach 0.5 for the RTM (e.g.
Troutman and Karlinger, 1989; Agnese et al., 1998).
Although Cayley trees differ from the RTM postu-
lates, hkjni is also asymptotically scale invariant with
n and approaches 0.5, see Fig. 7 (center).
However, Cayley trees and RTM trees differ
substantially if one looks at the characteristic
topological length/width ratio defined as:
mZ kmax=jmax (15)
The scaling of the mean of m conditioned on cluster
size n, hmjni, is shown in Fig. 7 (bottom). Troutman
and Karlinger (1989) show that under RTM postulates
the length/width ratio should asymptotically be equal
hkmaxjni=hjmaxjniZ2hLi, where hLi is mean link length
(exponentially distributed). For the discrete RTM
with hLiZ1, this leads to hmjniZ2. For clusters
generated on the Bethe lattice near the percolation
threshold pZpc, this leads to:
hmjniZ 2=ð1Kp1ÞZ 4 (16)
assymptotically for large n, as can be seen in Fig. 7. So
Cayley trees are more elongated than RTM trees.
So far in the analysis, the occupation probability p
was kept constant. It is interesting to explore whether
a variable p would better represent the landscape
variability in which river networks form. Two
experiments were conducted along this line: (1) p
was treated as a Beta distributed random variable with
mean equal pc and a given variance; and (2) p was
made functionally dependent on the stage since the
last bifurcation. The first test led to the same general
mean behaviour and will not be discussed in
more detail here. The second test assumed that p
Fig. 8. Variable occupation probability p as a function of k and d, accordi
function k of generated Cayley trees with dZ0.01 and dZ1. Basic statist
decreases exponentially with the stage of the cluster
development k for links that continue without
branching:
pZ p0 eKdk (17)
With increasing d and increasing cluster diameter
k, it becomes increasingly difficult for single branches
(links) to continue to percolate, see Fig. 8 and Table 1.
Below pZ1/3, links are more likely to terminate than
to continue branched or unbranched (see Fig. 3). This
may be thought of as a river network growing in a
headward manner into a less erodible environment.
To test the impacts of a variable p, 10,000 Cayley
trees were again generated with p 0Z0.499 and d
varying from 0 to 1. The impact on the geometrical
scaling of the generated clusters is illustrated in Fig. 9
and summarised in Table 1 in terms of hmi and hki and
compared to a constant occupation probability p. The
results show that p and d do not influence the position
of the peak of the topological width function hki
strongly, but there is a substantial impact on the
‘shape’ of the clusters, i.e. their length/width ratio hmi.
With decreasing cluster size and especially with an
increasing probability of termination upstream, gen-
erated Cayley trees become more compact, hmiz2.
5. Some comparisons with river networks
The scaling behaviour of Cayley trees is different
from other statistical models of river
network evolution, for example Scheidegger’s
(1967) directed random walk model (hZ2/3, HZ0.5). Other simple tree structures such as Peano’s
ng to Eq. (17). Histograms of the position of the peak of the width
ics are listed in Table 1.
Table 1
Statistics of generated Cayley trees for selected cases of constant and variable occupation probability p shown in Fig. 9, and of selected natural
river networks
Constant p Variable p River networks
pZ0.499 pZp 0 eKdk (dZ0.01) pZp 0 eKdk (dZ1) H!1500 m HO1500 m
hni 1787.7 89.6 22.7 – –
hkmaxi 61.7 22.9 8.6 – –
hjmaxi 15.6 6.8 4.5 – –
hmi 4 3.7 2 2.42 1.96
sm 1.77 1.57 0.67 0.74 0.58
hki 0.52 0.53 0.55 0.65 0.59
sk 0.19 0.19 0.15 0.16 0.16
p 0Z0.499, h i denotes the mean, s is standard deviation. Statistics are computed from 10,000 generated trees. Also listed are statistics for hmiZhl/wi and hki for 150 Swiss basins divided into two classes based on mean altitude H.
P. Molnar / Journal of Hydrology 322 (2006) 199–210 207
network have a self-similar character like assympto-
tical Cayley trees (hZ0.5, HZ1), but unrealistic
scaling of topological length and width properties
(kZ1, and m!1) (e.g. Marani et al., 1991; Colaiori
et al., 1997). However, this does not mean that Cayley
trees and the studied topological descriptors here
represent natural river networks well.
Keeping in mind the topological constraints of the
simulation, Fig. 9 shows hl/wi and hki computed from
Fig. 9. The position of the peak of the topological width function hki and
occupation probability p (upper panels) and variable p (lower panels) acco
G1 standard deviation. Square symbols are data from 150 river networ
(!1500 m), white are high basins (O1500 m). Note that the river netwo
associated p or d.
width functions derived from actual topography of
150 river basins in Switzerland for comparison. The
basins were divided into two classes by mean altitude,
those above (62 basins) and those below 1500 m
(88 basins). The drainage areas of the basins ranged
from 6 to 913 km2. The river networks were extracted
using the standard D8 method on a DEM with a 25-m
resolution; the width functions were determined;
and k and l/w were computed for each basin. Note
the length/width ratio hmi for generated Cayley trees with constant
rding to Eq. (17). Symbols denote the mean, bars indicate the range
ks across Switzerland classified by altitude: black are low basins
rk data are plotted for comparison purposes, they do not have an
P. Molnar / Journal of Hydrology 322 (2006) 199–210208
that the basins at lower altitude have a consistently
higher k and larger l/w ratio, i.e. they are more
elongated with maximum incremental drainage area
further upstream than basins at higher altitude. The
basic statistics are listed in Table 1.
There are similarities and discrepancies with
generated Cayley trees as Fig. 9 and Table 1 show.
For example, the random nature of percolation and
cluster development results in the position of the
peak of the width function hkiz0.5, while the river
networks show consistently hkiO0.5. The distri-
butions of k are also quite different, rather
symmetrical for Cayley trees, but negatively
skewed for the studied river networks, although
variability is of the same order. In terms of the
length/width ratio, clusters grown with a constant
occupation probability are too elongated. However,
when growth of single links is suppressed as the
cluster expands, the topological length/width ratio
of Cayley trees becomes quite similar to that of the
river networks. It was also found that the length/
width ratio of the studied Swiss basins clearly
defines an envelope curve for flood peaks with high
return periods observed at the basin outlets. In this
sense the shape of the river basin and the structure
of the river network are fundamental features for
flood production.
6. Conclusions
This study reports a numerical analysis of the
geometrical scaling properties of rooted Cayley trees
simulated by percolation on the Bethe lattice (with
zZ3 neighbours and occupation probability p),
discusses the resulting statistical scaling behaviour
of the generated random clusters, and compares the
results to river networks.
First, the analysis shows that Cayley trees
generated with a constant occupation probability,
like trees grown under the RTM postulates by
Markov branching models, are self-affine (hO0.5,
H!1) but approach self-similarity asymptotically
with increasing size (hZ0.5, HZ1). Natural river
basins also exhibit some degree of self-affinity
(e.g. Rigon et al., 1996; Rinaldo et al., 1998).
There are indeed physical reasons for this posed by
the threshold of channelization in the natural
landscape (e.g. Montgomery and Dietrich, 1992).
Second, the position of the peak of the topological
width function k is slightly greater than 0.5 but
asymptotically approaches kZ0.5 for Cayley and
RTM trees alike. However, the ratio between the
characteristic length and width scales m shows that
asymptotically for large n Cayley trees are more
elongated (hmjniz4) than RTM networks (hmjniz2),
because the probability of branching p2 is always
lower than that of termination p0 or continuation p1 on
the Bethe lattice, regardless of the occupation
probability. In comparison, natural river networks
studied here have hkiz0.6, and a length/width ratio
hl/wiz2.
Third, the numerical experiments in which the
occupation probability p was not kept constant but
was allowed to decrease systematically upstream on
unbranched links lead to a small increase in k and
more pronounced decrease in m, and gave values
more comparable to the river network data
presented here. This experiment was intended to
simulate a condition of substrate heterogeneity,
where a river network grows into a less erodible
environment. Similar experiments were carried out
by the invasion percolation experiments of Stark
(1991) where random strengths were assigned to
the lattice bonds and headward growth persisted
along the weakest bonds on the lattice, and network
simulations of Howard (1971) and Smart and
Moruzzi (1971), where arbitrary probabilities were
replaced by ones which presumably reflected the
processes involved in network growth. A variable
occupation probability may better reflect the
competition for drainage area and erodibility of
the landscape, which play a fundamental role in the
geometrical scaling of river basins. However, it
remains doubtful whether p in simple percolation
models, such as the one studied here, can mean-
ingfully be related to actual physical mechanisms
or processes taking place in river network evolution
(e.g. Rinaldo et al., 1998).
The geometrical scaling behaviour of Cayley trees
provides some interesting insight into the role of the
occupation probability on the Bethe lattice and the
assymptotic behaviour of scaling exponents and self-
similarity of generated trees. Nevertheless, when
comparing the results to natural river networks, it is
P. Molnar / Journal of Hydrology 322 (2006) 199–210 209
important to keep some fundamental limitations in
mind. For example, one has to be aware of the
constraints imposed by the topological nature of the
analysis. Cayley trees are purely topological struc-
tures and it is only assumed that cluster size and link
length are synonymous of drainage area and river
reach length. It has also been noted that simple
topological measures, such as k and m here, may be
too lenient descriptors of river network structure. For
instance, they ignore the vertical dimension which is
fundamental for river basin dynamics (e.g. Rinaldo
et al., 1998). Also the fact that most random tree
generation models give roughly equivalent results in
terms of diameter–size relations suggests that the
connection between random river network trees and
natural river networks may be hard to find (e.g.
Howard, 1971; Smart, 1972).
Recent studies of the scaling properties of land-
scapes illustrate that the evolution dynamics driven by
erosion and uplift lead to robust river basin scaling
laws, and that randomness together with efficiency act
in shaping the landscape (e.g. Rodriguez-Iturbe and
Rinaldo, 1997; Veneziano and Niemann, 2000;
Banavar et al., 2001). It is certain that randomness
plays an important role in natural river network
development, and therefore studies of randomly
generated tree-like structures will likely continue to
play an important role in our understanding of natural
river network variability.
Acknowledgements
Thanks are due to an anonymous reviewer and
Andrea Rinaldo for their thoughtful comments on the
manuscript and on more substantial questions of river
network evolution. Digital elevation data used in this
study were provided under an agreement between the
Swiss Federal Office for Topography and ETH Zurich
(Swisstopo DHM25 Level 1).
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