Theoretical Background: 2.1 Landslide Processes 2.1.1 Definitions and Classifications
Theoretical Background: 2.1 Landslide Processes 2.1.1 Definitions and Classifications
Theoretical Background: 2.1 Landslide Processes 2.1.1 Definitions and Classifications
Theoretical Background
A very basic but widely accepted and used definition for landslide was established
by Cruden (1991) and Cruden and Varnes (1996) and defines a landslide as
‘‘the movement of a mass of rock, debris or earth down a slope’’. However, the
term can be confusing if the parts of the word are considered. Cruden and Varnes
(1996) note that it describes all kinds of mass movements and is not limited to
granular soil (as land might suggest) or a sliding movement process. The term
landslide is well established in the research community and will therefore also be
used in this thesis as an overarching term referring to all movement types and
material properties. Further on, the term mass movement is used interchangeably
with landslide.
The most common classification for landslides is based on material properties
and process types (Table 2.1). Besides the main types of movement processes
there is one complex class which contains movement processes with two or more
different processes acting together along with downslope movement of the land-
slide mass.
A second widely acknowledged classification of landslides is based on move-
ment velocity (Cruden and Varnes 1996), which ranges from extremely fast to
extremely slow (Table 2.2). Moreover, landslides can be distinguished regarding
their state of activity. Cruden and Varnes (1996) established eight groups, namely
active, suspended, reactivated, inactive, dormant, abandoned, stabilized and relict
mass movements. Further on, single, multiple and successive movements are
distinguished. Other differentiations can be based on, for example, the water
content of involved materials (Cruden and Varnes 1996).
The term creep, which was used to describe continuous and imperceptible slow
movements of the ground (e.g., Terzaghi 1950, 1961) was omitted due to various
definitions and interpretations. Cruden and Varnes (1996) propose to not use the
Table 2.1 Mass movement classification based on process type and material (Cruden and Varnes
1996; Dikau et al. 1996)
Process type Type of material
Rock Debris Earth
Topple Rock topple Debris topple Earth topple
Fall Rock fall Debris fall Earth fall
Slide Translational Rock slide Debris slide Earth slide
Rotational
Flow Rock flow Debris flow Earth flow
Spread Rock spread Debris spread Earth spread
Complex e.g., rock avalanche e.g., flow slide e.g., slump-earthflow
term creep and to replace it with the appropriate descriptors of their classification.
However, the term creep may still be applied in a simple mechanical way to
describe deformation that continues under constant stress (Cruden and Varnes
1996; Terzaghi et al. 1996).
Landslides are a sign of slope instability which is defined as the ‘‘propensity for a
slope to undergo morphologically and structurally disruptive landslide processes’’
(Glade and Crozier 2005b, p. 43). Glade and Crozier (2005b) visualise slope
stability as a dynamic spectrum (Fig. 2.1). On one end, there is a stable slope
2.1 Landslide Processes 9
Fig. 2.1 Stability states and destabilising factors (after Crozier 1989; Glade and Crozier 2005b)
In theory, a slope is stable as long as the FoS is greater than one and slope
movement commences if the FoS is 1.0 or smaller. However, Glade and Crozier
(2005b) stress the point that the FoS is only a relative measure of stability as it
gives no information on the magnitude of destabilisation that is needed until slope
failure occurs. Moreover, some authors describe the onset of movements even
before the FoS becomes lower than 1.0 (Petley et al. 2002, 2005b, c) which they
2.1 Landslide Processes 11
Fig. 2.3 Idealized stress–strain curves for brittle (a) and ductile (b) deformation (Petley and
Allison 1997)
During this phase shear zone contraction or dilation may occur which affects pore
pressures and therefore strain rates (Iverson 2005). Thereafter, strains primarily
occur as displacement along the shear surface.
Ductile behaviour can be observed at high effective stresses prevalent in very
deep-seated landslides and in materials with little or no inter-particle bonding like
weathered clays (Petley and Allison 1997). The initial phases of elastic and
elastic–plastic strain are similar to the brittle failure regime. However, due to the
high confining stress no shear surface can develop. Increased load results in purely
plastic deformation at constant stresses as the material reforms. Moreover, a
transition between ductile and brittle behaviour was observed by Petley and
Allison (1997) at very high pressures, which are present in very deep-seated
landslides.
As mentioned above the term creep does not describe a certain landslide type but
refers to the mechanical behaviour of geological materials to constant stress. Some
creep takes place in almost all steep earth and rock slopes and may concentrate along
pre-existing or potential slip surfaces or distribute evenly across the landslide profile
(Fang 1990). Creep movements in landslide can be continuous or may vary sea-
sonally with hydrological conditions (Petley and Allison 1997). Creep can be
maintained for long periods, however, creep gradually decreases shear strength and a
slope’s margin of stability (Fang 1990) and eventually the slope may fail.
A widely acknowledged concept of creep distinguishes between the phases of
creep movement (Okamoto et al. 2004; Petley et al. 2005b, c, 2008). When con-
stant stress lower than peak strength is applied to a soil mass subsequent strains are
time-dependant and can be visualised as displacement versus time plot (Fig. 2.4).
In the primary creep stage strains are initially high due to elastic deformation but
decrease with time. During the secondary creep phase the material suffers diffuse
damage but strains are generally slow or almost steady (Okamoto et al. 2004), or
may even stop altogether (Petley et al. 2008). When diffuse micro-cracks start to
interact to form a shear surface, the critical point into the tertiary phase is reached
(Reches and Lockner 1994; Main 2000). This phase is characterized by a rapid
acceleration of displacement until final failure.
The increasing displacement rates associated with rupture growth and micro-
crack interactions during the tertiary creep stage have been subject to research for
2.1 Landslide Processes 13
a long time in order to predict final failure (Saito 1965; Bjerrum 1967; Saito 1969;
Voight 1989; Fukuzono 1990) and volcanic eruptions (Voight 1988). The concept
is frequently termed progressive failure analysis and usually employs examination
of movement patterns by plotting movement in K t space, where K ¼ 1=v (v is
velocity and t is time) (Petley et al. 2002).
It has been observed in many shear experiments and real landslides that linear
trends in acceleration occur if failure is imminent. This was the case for first-time
failures and for failures in which brittle behaviour was dominant in the basal shear
zone. However, reactivated landslides and failures where ductile deformation is
dominant display asymptotic trend in K t space which has been observed in several
landslides, e.g., in Italy, New Zealand, California, Japan and the UK (Petley et al.
2002; Carey et al. 2007).
The potential for prediction and early warning of landslide failures has been
showed by several case studies. Kilburn and Petley (2003) and Petley and Petley
(2006) analysed displacement data from the famous Vaiont reservoir rockslide in
Northern Italy, which caused a flood wave that killed around 2000 people in 1963.
The result of the analysis was that at 30 days before final failure a transition to a
linear trend in movement acceleration was visible and final failure was therefore
predictable. Moreover, in the case of the artificial landslide experiment at the
Selford slide (Selford Cutting Slope Experiment) final failure could be predicted
50 days in advance (Petley et al. 2002).
Despite its potential, progressive failure analysis has not been integrated into an
early warning system yet. A test application to the slope under investigation in this
study failed because of slow movement rates and insufficient acceleration phases
(Thiebes et al. 2010).
Slow active landslides are widespread in many geomorphological contexts and
materials, and can display steady movements over long periods of time, often
along completely developed shear zones (Picarelli and Russo 2004). Changes in
displacement rates of slow or extremely slow landslides is in many cases related to
varying pore water pressures (Leroueil 2004) and movements can be continuous or
intermittent. Especially in landslides of moderate depths pore pressures primarily
drive displacements, while in deeper landslides creep and erosion, as other phe-
nomena of stress relief, are the main influential factors (Picarelli and Russo 2004).
While pore pressures control landslide movement on short and medium time-
scales, erosion, weathering, progressive weakening due to strain are influencing on
a larger time-scale (Picarelli and Russo 2004).
Seasonal variations of pore pressures close to surface are not necessarily
reflected by deeper layers if materials are rich in clay (Leroueil 2004). Moreover,
clays also influence infiltration and slope stability by their swelling and drying
behaviour. Very dry clay may develop cracks which allow for quick percolation
into depth along preferential flow paths. Preferential flow paths can have a
positive effect on slope stability by allowing quick drainage of potentially
unstable areas, but can also have an adverse effect by contributing additional
water to areas where shear surfaces may develop (Uchida et al. 2001). Infiltra-
tion in unsaturated materials is a complex process (Leroueil 2004) and strongly
14 2 Theoretical Background
Fig. 2.5 Effects of external perturbations on a geomorphological system (after Bull 1991)
Landslides are the results of complex interaction within the natural environment, and
if human intervention is present, the interactions and feedbacks become even more
complex (Armbruster 2002). A widely acknowledged approach in physical geog-
raphy was laid out by Chorley and Kennedy (1971) and aimed to provide a theoretical
framework which allows for analysis of form, material, and processes, as well as
interaction and feedbacks (Dikau 2005). Moreover, the conceptual approach com-
prises variable space and time-scales of system evolution and external system con-
trol, as well as early approaches to non-linear system response (Slaymaker 1991).
Four types of systems can be distinguished: morphological systems, cascading sys-
tems, process-response systems and control systems (Chorley and Kennedy 1971).
2.1 Landslide Processes 15
Following Glade (1997) morphological systems can be used to describe the interac-
tion between landslide-prone regions and potentially landslide-triggering rainfall
events. Bell (2007) notes, that if research focuses on, for example, landsliding of
periglacial strata cascading systems may be more appropriate. Research on factors
controlling landslide behaviour can benefit from a process-response system point of
view, while control systems are important in geomorphological hazard research
where direct human manipulation of material parameters aims to decrease risks
(Dikau 2005). The effects of external perturbation on a geomorphological system are
exemplified for alluvial deposits in Fig. 2.5.
Reaction time is important within landslide research and illustrates how fast a
slope reacts to external perturbation, such as rainfall, snow melting or earthquakes.
Relaxation time describes the velocity of movement until all energy is depleted
and may range from slow creeping movements to sudden failure. During persis-
tence time a slope is stable until further perturbation impacts trigger further system
response.
The classic systems approach by Chorley and Kennedy (1971) is essentially
based on the concept of thermo-dynamic equilibrium which means that a system
will return to a steady-state by negative feeback effects after external perturbations
(Dikau 2006). In recent years, however, research shifted more to the analyis of
non-equilibrium systems and non-linear relationships (Dikau 2005). Nonlinearity
implies that ‘‘outputs or responses of a system are not proportional to inputs or
forcings across the entire range of the latter’’ (Phillips 2006, p. 110), which is
dominant in geomorphic systems. Sources of nonlinearity in nature are summa-
rized by Phillips (2003) and comprise thresholds, storage effects, saturation and
depletion, self-reinforcing positive feedbacks, self-limitation, competitive rela-
tionships, multiple modes of adjustment, self-organisation and hysteresis. Non-
linear system analysis provides, according to Dearing (2004), new insights and
aids to understand system behaviour. Novel concepts developed in this area of
research include complexity, self-organisation, deterministic chaos and are
reviewed and discussed in detail elsewhere (Phillips 1992a, b, 2003; Richards
2002; Favis-Mortlock and De Boer 2003; Dikau 2006).
There is no single, precise definition of complexity (Favis-Mortlock and De
Boer 2003). However, complexity may loosely be delineated as the fact that
systems cannot be described by the properties of its parts (Gallagher and
Appenzeller 1999). According to Phillips (1992a) complexity can arise from
cumulative process-response mechanisms which are far too numerous to be
accounted for in individual details, or due to multiple controls over process–response
relationships that operate over a range of spatial and temporal scales.
The studies of Bak et al. (1988) on sand-pile models provided some insights on
complex systems. In these models grains were dropped onto a sand pyramid. This
resulted either in no changes, or in landslides of various sizes. The landslide sizes
were found to follow a power-law distribution, but it was, however, not possible to
predict the size of the next landslide. The fact that the system drove itself to a
critical state was referred to as self-organised criticality, a concept that has been
16 2 Theoretical Background
Even though landslides can occur without the impact of external factors, generally
their occurrence is connected to some kind of triggering event. Many factors can
act as triggers for landslides. The most common natural triggers are either related
to geological events, such as seismic shaking due to volcanic eruptions or earth-
quakes, or hydrological events such as intense rainfall, rapid snow melt or water
level changes in rivers or lakes at the foot of slopes (Wieczorek 1996). Moreover,
human interaction in the form of loading or slope cutting can trigger landslide
events. The most important trigger, however, in both shallow and deep-seated
landslides is intense rainfall (Crosta and Frattini 2008). Infiltrating rain percolates
within the soil, thus increasing pore pressures at hydrologic boundaries, which
subsequently decreases shear strength. Positive pore water pressure may occur
directly caused by infiltration and percolation (saturation from above), or may be
the result of perched groundwater tables (saturation from below) (Terlien 1998).
Important factors determining the evolution of saturation are soil permeability and
2.1 Landslide Processes 17
thresholds (Reid 1994; Crosta 1998; Terlien 1998; Ekanayake and Phillips 1999;
Iverson 2000; Frattini et al. 2009).
Coupled hydrology and stability models have been widely applied to predict the
effects of rain storms, and to define critical situations. Examples for local scale
(Buma 2000; Brooks et al. 2004; Berardi et al. 2005; Pagano et al. 2008), and
regional scale (Dhakal et al. 2002; Crosta and Frattini 2003) approaches can be
found in the respective literature.
reviews (Franklin 1984; Keaton and DeGraff 1996; McGuffey et al. 1996;
Mikkelsen 1996; Soeters and Van Westen 1996; Turner and McGuffey 1996;
Olalla 2004; Van Westen 2007; Liu and Wang 2008). No self-contained review on
existing monitoring systems will be given as many examples of monitoring sys-
tems are presented in the review on early warning systems (Sect 1.4). It is however
important to mention that many landslide monitoring systems employ several
different techniques, such as methods for measuring landslide movement and
hydrology.
Regarding monitoring it should be made clear, that there is no obvious
threshold that determines what time intervals between repeated measurements are
necessary for it to be classed as monitoring. Olalla (2004) points out that moni-
toring can range from, for example, inclinometer measurements carried out once in
a year, or automatic measurements in intervals of seconds. Therefore, every
repeated measurement could be defined as monitoring. Automatic monitoring
systems are however more convenient than manual measurements as they do not
require humans to regularly go to study sites which may be remote or difficult to
access. Another advantage of automated monitoring systems is the ability to
control measures by time intervals, thresholds or user input. Besides this, questions
of data storage, transmission and security arise with such automatic systems.
Moreover, data should automatically be processed and checked to prevent
inconsistencies (Olalla 2004). However, issues of managing automatic monitoring
systems will not be discussed here.
or to take undisturbed material samples. Generally, pits and trenches can only be
established on shallow movements. Examples are given by Bromhead et al.
(2000), Clark et al. (2000) and Topal and Akin (2008). Penetration tests can also
be performed to investigate stiffness of subsurface materials. More often, drillings
are utilised to investigate landslide bodies. An ample variety of drilling devices is
available on the market from simple handheld sounding poles to truck-sized rotary
drilling machines. Besides the advantage of directly probing the landslide body
and having the opportunity to take core samples, sensors can be applied within the
boreholes to further investigate subsurface movement and hydrological processes.
In many cases inclinometers are used to determine subsurface movement of
landslides (Borgatti et al. 2006; Bonnard et al. 2008; Bressani et al. 2008;
Jongmans et al. 2008; Mihalinec and Ortolan 2008; Yin et al. 2008). General remarks
on the use of inclinometers for landslides research are provided by Stark and Choi
(2008). Inclinometers consist of a flexible drilled pipe which is placed vertically into
a drilled borehole. A high-precision probe is inserted and the inclination of the pipe is
measured in even distances, for example, every e.g., 50 cm. Repeated measurements
give information of the occurred inclination changes in downslope and horizontal
direction for the entire length of the pipe. However, it is important that inclinometers
are fixed into the stable ground beneath the shear surface to prevent data bias.
Automated inclinometer s are commercially available and usually consist of several
inclinometer probes connected to each other to a chain, or automatic systems where
the probe automatically moves within the pipe. Within landslide monitoring the use
of automatic inclinometer and inclinometer chains has been described by for
example, Lollino et al. (2002) and Olalla (2004), Volkmann and Schubert (2005) and
Wienhöfer and Lindenmaier (2009). However, inclinometers can only withstand a
certain amount of displacement before pipes break. This makes them especially
applicable for monitoring of slow moving landslides, but also for detection of shear
processes in faster moving landslides.
A more recent method for the detection of subsurface movements and defor-
mation is Time Domain Reflectometry (TDR). Barendse and Machan (2009) note
that inclinometers can determine the magnitude and direction of ground deforma-
tion, while TDR is primarily used to identify depths of active shearing. The TDR
method has initially been developed in the 1950s for locating discontinuities in
power transmission cables (Pasuto et al. 2000). TDR has first been used within
landslide research in the 1980s in underground coal mine monitoring (Olalla 2004)
and since then applied to several other case studies (Pasuto et al. 2000; Barendse
and Machan 2009; Singer et al. 2009; Yin et al. 2010a). The principle of TDR is
based on an electric signal sent through a coaxial cable. Shear movements deform
the cable which creates a spike in cable signature and depth can be detected from
the signal. Laboratory tests of TDR method for detection of shear processes have
been performed by Baek et al. (2004) and Blackburn and Dowding (2004). Pasuto
et al. (2000) compared TDR cables to inclinometer measurements and extensom-
eters. Their result was that TDR cables are less sensitive to deformations but can
withstand a larger displacement than usual inclinometers. The higher stability of
24 2 Theoretical Background
TDR cables make them a good choice for monitoring faster moving processes like
the Gschliefgraben flowslide in Austria (Marschallinger et al. 2009).
Wire or rod extensometers are used to monitor the distance between two points
and are frequently utilised in surface movement investigations (Furuya et al. 2000;
Angerer et al. 2004; Barla et al. 2004; Willenberg et al. 2004; Wu et al. 2008).
Extensometers are in most cases applied to investigate surface movements but can
also be installed within boreholes (Bloyet et al. 1989; Krauter et al. 2007).
Accuracy of extensometers depends on the length measured and usually is in the
sub-mm range.
Tiltmeters are able to give high resolution information on inclination and have
been applied to several landslide monitoring systems (Clark et al. 1996; Meidal
and Moore 1996; Barton and McCosker 2000; Blikra 2008; García et al. 2010).
Crackmeters are used to monitor displacements in the sub-mm range at joints
and cracks in rocks, buildings and other structures. The application of crackmeters
has been described by several authors (e.g., Keaton and DeGraff 1996; Greif et al.
2004; Olalla 2004; Vlcko 2004; Moore et al. 2010).
The mentioned field based methods only give information on ground dis-
placements for points or along lines. However, spatial methods are also available
that give information on displacement for entire slopes.
In recent years many studies utilised Terrestrial Laser Scanning (TLS) for
monitoring of geomorphological processes. The technique is similar to LiDAR,
but ground-based. In contrast to LiDAR it is appropriate for steep cliffs and rock
faces as the scanner can be placed in front of it. TLS scans are used to create three
dimensional DTM which can further be analysed quantitatively within GIS or
CAD environments to assess e.g., the volume of displaced material between
measurements. Precision of TLS is heavily dependent on distance to the target and
ranges from centimetres to mm, as well as environmental conditions such as rain
or vegetation. General remarks on TLS and its usage for monitoring geomor-
phological processes are provided by Prokop and Panholzer (2009) and Schaefer
and Inkpen (2010). Many case studies applied TLS for landslide monitoring (e.g.,
Mikoš et al. 2005; Rosser et al. 2005; Rosser and Petley 2008; Avian et al. 2009;
Baldo et al. 2009; Oppikofer et al. 2009; Abellán et al. 2010).
SAR methods can also be applied in ground-based studies, which are frequently
termed Slope Stability Radar (SSR) (Van Westen 2007). The major advantages of
this method are that they provide high precision data in sub-millimetre range
without being affected by weather conditions and without the need to install
reflectors or ground marks. However, vegetation drastically decreases accuracy.
Luzi et al. (2005) used a ground-based DinSAR system to monitor displacement on
the Italian Tessina landslide and compared the measurements to regular theodolite
surveys. Based on comparable displacement results by both methods they conclude
that InSAR is also applicable for landslide early warning systems. Several other
research projects installed SSR systems to monitor displacements of landslides
(Canuti et al. 2002; Antonello et al. 2004; Casagali et al. 2004; Eberhardt et al.
2008; Bozzano et al. 2010; Casagli et al. 2010).
2.2 Landslide Investigation and Monitoring 25
Another method that has increasingly been used in recent years is Brillouin
Optical Time-Domain Reflectometry (BOTDR). These optical fibres can be used
for measurement of ground deformations along profiles. The principle of this
method is based on an interaction of pulsed beam and photons that are thermally
excited within the light propagation medium (Wang et al. 2008a), which are
affected by temperature and strains. Laboratory simulations to test the applicability
of BOTDR (Dai et al. 2008; Wang et al. 2008a), as well as field applications
(Higuchi et al. 2007; Dai et al. 2008; Shi et al. 2008a, b; Moore et al. 2010) have
been described.
Given the great importance of rainfall and slope hydrology for landslide triggering,
these factors are frequently analysed and monitored within landslide research.
Climatic factors such as rain, snowfall, temperature and wind are usually measured
at climate stations, which are commercially available or in many cases provided by
meteorological agencies. Measurement of ground-water conditions such as pore
pressures and soil water suction is usually accomplished by using piezometers and
tensiometers. An overview on different types of these sensors can be found in
Kneale (1987). Piezometers are probably the most common hydrological sensor
utilised for landslide research (e.g., Wu et al. 2008; Yin et al. 2008; Calvello et al.
2008; Ching-Chuan et al. 2009; Yin et al. 2010a) and come as simple standpipe or
more advanced vibrating wire piezometers. Piezometers measure the pressure of
water in saturated soils and therefore give information on the height of the
groundwater table within a soil. Tensiometers measure matrix potentials and are
frequently utilised to assess the soil suction in the vadose zone (Li et al. 2004;
Rinaldi et al. 2004; Montrasio and Valentino 2007; Greco et al. 2010). Piezometers
and tensiometers are usually installed within boreholes or directly into the soil at
trenches.
In recent years Time Domain Reflectometry (TDR) has also been applied to
measure volumetric soil water contents. Greco et al. (2010) compared TDR sen-
sors with tensiometers and concluded that TDR might be more useful for landslide
monitoring and early warning since TDR measurements of soil water content
change smoothly, while soil suction showed abrupt steep fronts. More examples of
TDR application for assessing soil water are presented by e.g., Hennrich (2000),
Tohari et al. (2004) and Kim (2008).
The chemical properties of ground and pore water have a widely acknowledged
effect on shear strength and affect slope stability (Di Maio and Onorati 2000;
Angeli et al. 2004) by for example, influencing the mechanical behaviour of clays
(Leroueil 2004). However, monitoring of ground water composition is only rarely
included in landslide monitoring systems (Sakai and Tarumi 2000; Montety et al.
2007; Sakai 2008).
26 2 Theoretical Background
Several methods from geophysics have been utilised for landslide research, mainly
for prospection of landslide bodies and for investigation of hydrological processes
acting within landslides. However, wider application of geophysics in landslide
research have been hindered for two reasons (Jongmans and Garambois 2007):
geophysical methods provide images of geophysical parameters which are not
directly linked to geological parameters required by geotechnical engineers and
geomorphologists; and the overestimation of the quality and reliability of results
among some geophysicists. The main advantages of geophysical methods com-
pared to standard geotechnical approaches are that they are non-invasive and can
be applied to large areas for a low cost. However, the main disadvantages are the
decrease of resolution with depth, the non-uniqueness of solutions for data
inversion and interpretation, and the in-direct information (Jongmans and
Garambois 2007). Generally, geophysical methods are used for prospection of
landslide bodies, detection of discontinuities and shear surfaces, as well as for
investigation of hydrological regimes. Measurements are usually short-term and
only a few long-term monitoring exist (Supper and Römer 2003; Lebourg et al.
2005). Geophysical methods will only briefly be presented here, more detailed
reviews on geophysical application are provided by many introductive textbooks
(Telford et al. 1990; McGuffey et al. 1996; Parasnis 1997; Reynolds 1997; Kearey
et al. 2002; Milsom 2003; Schrott et al. 2003; Knödel et al. 2005).
Seismic methods are based on the velocity measurements of seismic waves in
subsurface materials. Generally, denser material causes faster wave propagation.
At layer interfaces waves are partly reflected, but also partly transferred into depth
due to refraction. In geomorphological applications seismic signal is usually
induced by a sledge hammer that is pounded on a steel plate. Penetration depths of
more than 30 m can be reached by more powerful sources e.g., drop weights or
explosives) (Schrott and Sass 2008). Measurements are taken by geophones which
are located at even distances along a profile. A number of different seismic
techniques have been established, of which seismic reflection, seismic refraction
and seismic tomography are the most common. Although seismic methods proved
to be suitable for many geomorphological studies which require definition of
subsurface properties (Hecht 2001), such as determination of active layer in per-
mafrost or volumes of sediment bodies, problems may occur if low velocity layers
are sandwiched in high velocity layers (Schrott and Sass 2008). Examples of
dedicated landslide subsurface characterisation applying seismic methods are
provided by several authors (Schmutz et al. 2000; Willenberg et al. 2002; Meric
et al. 2004; Meric et al. 2005; Heincke et al. 2006, 2010).
A variation of seismic method is applied to record fracture signals produced by
deformation within landslides, and to locate fracture both in space and time. These
methods can be distinguished as micro-seismic, nano-seismic and passive seismic
(Joswig 2008). Instead of creating a seismic signal by e.g., a sledge hammer, these
methods use the acoustic signals emitted by deformation processes by ‘‘listening’’
2.2 Landslide Investigation and Monitoring 27
Soeters and Van Westen (1996) distinguish between four distinct approaches
for regional landslide hazard analysis, i.e. inventory-based, heuristic, statistic and
deterministic approaches.
Landslide inventories allow for detailed analyses of landslide distribution and
in case of multi-temporal inventories activity patterns and form the basis for
regional modelling of landslide susceptibility, hazard and risk.
Heuristic methods integrate the knowledge and experience of geomorphological
and geotechnical experts to derive a regional map of landslide susceptibility and
hazard. Soeters and Van Westen (1996) distinguish between geomorphological
analysis (Kienholz et al. 1984; Cardinali et al. 2002; Reichenbach et al. 2005) and
weighted combination of thematic maps (Pachauri et al. 1998; Nagarajan et al.
2000; Dikau and Glade 2003; Moreiras 2005; Petley et al. 2005a).
Statistical methods are the most frequently applied method to model regional
landslide susceptibility and hazard, and to predict future slope failures (Armbruster
2002). Herein, a statistical relationship between possible landslide causative fac-
tors and the presence of existing landslides is established, and used for prediction
of future landslide by spatial interpolation. A vast range of different methods has
been developed. Bell (2007) provides a extensive list of statistical methods, of
which the most frequently applied are bivariate regression (Ayalew et al. 2004;
Süzen and Doyuran 2004), multiple regression (Carrara 1983; Chung et al. 1995),
discriminant analyses (Ardizzone et al. 2002; Carrara et al. 2003; Guzzetti et al.
2006), logistic regression (Atkinson et al. 1998; Ohlmacher and Davis 2003; Süzen
and Doyuran 2004; Brenning 2005), neural networks (Fernández-Steeger et al.
2002; Lee et al. 2003; Catani et al. 2005), support vector (Brenning 2005),
bayesian statistic (Chung and Fabbri 1999; Lee et al. 2002; Neuhäuser 2005),
fuzzy logic (Tangestani 2003; Dewitte et al. 2006; Lee 2006) and likelihood ratio
(Chung et al. 1995; Chung 2006; Demoulin and Chung 2007).
Regional deterministic models apply physically-based simulations to assess
landslide susceptibility expressed chiefly as FoS, and provide useful insights into
landslide causes (Carrara et al. 1992). The most frequently applied methodology for
regional deterministic modelling is based on distributed hydrological modelling and
stability calculation using a simplified approach, i.e. the infinite-slope model.
Hydrological modelling is essentially based on topographical flow routing and the
simulated development of soil saturation above an impermeable layer (O’Callaghan
and Mark 1984; Fairfield and Leymarie 1991; Freeman 1991; Quinn et al. 1991; Lea
1992; Costa-Cabral and Burges 1994; Terlien et al. 1995; Tarboton 1997). Calcu-
lation of slope stability utilises geotechnical parameters such as cohesion and internal
friction, which can be measured in the field or laboratory (Soeters and Van Westen
1996; van Westen et al. 1997). The infinite-slope model estimates stability for single
grid-cells of a DTM and neglects any effects of neighbouring areas. Moreover,
deterministic methods are only applicable when geomorphic and geologic conditions
are fairly homogenous over the entire study area and landslide types are simple
(Soeters and Van Westen 1996). Due to these limitations, regional deterministic
models are only suitable for simple landslide processes, such as shallow translational
landslides. The most widely used models for regional deterministic analyses are
30 2 Theoretical Background
TOPMODEL (Montgomery and Dietrich 1994; Casadei et al. 2003; Meisina and
Scarabelli 2007), SHALSTAB (Dietrich et al. 1998; Morrissey et al. 2001; Huang Jr
et al. 2006), and SINMAP (Pack et al. 1998, 2001, 2005; Zaitchik and van Es 2003;
Pack and Tarboton 2004; Kreja and Terhorst 2005; Thiebes 2006; Deb and El-Kadi
2009), but similar studies have also been performed by other authors (Hammond
et al. 1992; Terlien et al. 1995; Wu and Sidle 1995; van Westen et al. 1997; Wu and
Sidle 1997; Sidle and Wu 1999; Xie et al. 2004; Claessens et al. 2005).
Models for the analysis of single slope failures, i.e. local models, have a long
tradition in geotechnical slope stability practice. These models have frequently
been applied to assess the stability of human-made or natural slopes, and the
design of slopes, such as embankments, road cuts, open-pit mines etc. Moreover,
physically-based models for single slopes allow detailed investigation of failure
processes, assessment effects of triggering events, and assessment of the effec-
tiveness of remedial measures and stabilisation works.
Today, a wide range of computer calculation programs are available for
numerical slope stability assessment. Despite the development of more sophisti-
cated numerical models, limit-equilibrium methodology is still widely applied
(Abramson 2002). In the following a short overview of local landslide modelling
methods and techniques is presented. It is beyond the scope to review the theo-
retical background and mathematical and mechanical derivation of local stability
calculation. These can be found in the literature sources provided or in various
textbooks (Chandler 1991; Bromhead 1998; Abramson 2002; Aysen 2002;
Eberhardt 2003a; Ortigão and Sayao 2004; Duncan and Wright 2005; Gitirana Jr
2005; Cheng and Lau 2008).
Limit-equilibrium methods provide a mathematical procedure to determine the
forces within a slope that drive and resist movement. The factors included in the
2.3 Landslide Modelling 31
2008), and 3DEC (Cheng et al. 2006; Ming-Gao et al. 2006; Lato et al. 2007; Bai
et al. 2008).
may be due to a false sense of security and building of higher value infrastructure
in potentially hazardous areas.
Uncertainties always prevail in hazard prediction and are also a major challenge
for early warning (UNISDR 2004b). Storms may change their track, or lose their
strength over time, earthquakes may be expected for a large area, but no exact
location can be determined. For many hazard events, only statistical forecasts,
such as an El Niño event probability for the next year of 60% can be made. In
addition, uncertainties within the social components complicate the prediction of
the hazard consequences. These include the reaction of the population to warnings
and hazardous events, and the functioning of evacuation plans and general disaster
management. Baum and Godt (2009) provide interesting examples where people
were moving into warning areas on purpose to secure their homes or save pets.
Others misunderstand the warning and believe that if a warning is issued by for
example the Department of Forestry it only relates to areas with actual logging
activities.
Moreover, the costs of unnecessary evacuations due to false alarms are a major
concern for decision makers. False alarms are a problem of early warning systems
as they can substantially compromise the credibility of early warning systems
(Larsen 2008). In 1982 the United States Geological Survey (USGS) issued a
warning for the Mammoth Lakes Area because of an expected volcanic eruption
potentially threatening a ski resort on the slopes of the volcano. After the eruption
did not occur the USGS was mocked as the US Guessing Society (Die Zeit 2010).
However, Sorensen (2000) argues, that false alarms do not necessarily diminish
the trust in early warning systems if the reason for the false alarm is understood.
The number of false alarms can be reduced by pursuing a conservative strategy and
by issuing generalised warnings. However, the use of generalised warnings
decreases with the size of the geographic area (Larsen 2008).
An interesting example of consequences of false warning took place in Italy in
2009 were a scientist had been measuring the emissions of radon gases which are
associated with earthquakes. Based on his measurements he was expecting a major
earthquake for the city of Sulmona two days before the devastating L’Aquila
earthquake (5.8 magnitude on Richter scale) which is located 70 km north-west.
As his prediction did not turn out to be accurate he was accused for creating panic
but later absolved (Die Zeit 2010).
On the other hand a group of seven Italian earthquake scientists who were
assessing the seismic activity in the L’Aquila region were accused of gross neg-
ligent manslaughter as they failed to predict the disaster. Only days before the
earthquake they had stated at a meeting with city officials that there were no
grounds for believing a major quake was on the way despite some smaller quakes
in the previous days (Cartlidge 2010). The allegations gained much attention in the
scientific community as well as from general public, and a petition to end the
investigations had been signed by over 5000 scientists. In this open letter it was
stated that at the moment there are no scientific method to predict earthquake
timing and that therefore, there is no ground for the allegations (Die Zeit 2010).
Warner Marzocchi, chief scientist at the Italian National Institute for Geophysics
2.4 Landslide Early Warning Systems 39
and Vulcanology commented that ‘‘as scientists, we have to focus on giving the
best kind of scientific information’’ and that the decisions of what actions need to
be taken ‘‘is down to others to decide’’ (Cartlidge 2010). Thomas Jordan, earth
scientists who had also been working in the L’Aquila region added that the costs of
false alarms are too high compared to the low probabilities of an earthquake
occurring, so that there was no basis to initiate actions such as mass evacuations
(Cartlidge 2010).
A similar case happened in the Italian community of Sarno, which was hit by
devastating landslides and a debris flood in 1998. Before the disaster event the
mayor had told the people to stay calm and to stay at home even though there were
already heavy rainfall and landslides occurring in the vicinity of the town (Die Zeit
2010). After the event he was accused for negligent manslaughter but later
absolved because the event could not have been foreseen.
The previous examples clearly illustrate some of the problems and challenges
of early warning systems, arising from both natural and social components.
Besides technical difficulties of natural hazard prediction, legal, social and polit-
ical dimensions add to the complexity of early warning. Effective early warning
systems must therefore be carefully planned. Resulting from the work of the
Integrative Landslide Early Warning Systems (ILEWS) project, issues have been
identified that need to be addressed when early warning systems are to be installed
(Bell et al. 2010). Important factors to be accounted for include the process (flood,
volcanic eruptions, landslides), time (slowly developing or rapidly initiating
hazards), forewarn time needed to provide useful warning, financial aspects (pri-
vate or public investments), communication of warning (unidirectional, bidirec-
tional), threatened human lives and infrastructure (cost-effectiveness) and
stakeholders to be warned (governmental agencies, emergency services). Thus,
early warning systems have to be demand-orientated and adapted to local condi-
tions (Twigg 2003). In addition, it is important that early warning systems are
embedded into the local community to increase acceptance of warnings (Mileti
1999; Greiving and Glade 2011).
Given the variety of hazards for which early warning systems have been
installed it is difficult to define clear categories. Some basic distinction, however,
can be made (Bell et al. 2010):
– Monitoring systems are primarily installed to increase the understanding of
natural processes but can also be utilised to plan further actions. These moni-
toring systems differ by technologies applied, time intervals between mea-
surements and degree of automation.
– Expert- or control systems provide information on potentially hazardous events
and are chiefly implemented to gain information on critical developments and
with the aim to guide scientists and decision makers.
– Alarm systems are based on monitoring systems and provoke an automatic
warning if, for example, a predefined threshold is exceeded. Further differen-
tiation of alarm systems can be made between pre- and post event systems and
the forewarn time provided by the system. Moreover, these systems differ in
40 2 Theoretical Background
A regional early warning system for shallow landslides is implemented for the
Seattle Area, USA since 2002 (Baum et al. 2005a; Baum and Godt 2009) and is
jointly managed by NWS, USGS and the city of Seattle. The technical system
comprises a total number of 17 automatic rain gauges with an average distance of
2–5 km between them and quantitative weather forecasts. In addition, a test slope
was instrumented to improve understanding of pore water pressure development
and landslide triggering. Furthermore, landslide mapping and probabilistic regio-
nal hazard modelling were performed (Baum et al. 2005b). Detailed examination
of rainfall data led to the establishment of a minimum threshold for landslide
triggering based on intensity and duration analysis and an antecedent water index
calculated from cumulative rainfall of 3 days, and rain within the previous 15 days
(Chleborad 2000, 2003, 2006). For the assignment of alert levels thresholds are
used for both, intensity-duration and antecedent water index. Rainfall exceeding
intensity-duration thresholds triggers a warning status at high antecedent water
status. Watch level is issued, in the occurrence of medium antecedent rainfall
index values and observed or forecasted rainfalls above thresholds. Outlook level
is activated if any of the rainfall threshold is exceeded. In other cases the alert is
null. In addition, warnings are only provided if thresholds are exceeded for at least
three gauges relating to an expected number of three or more landslide events
(Baum and Godt 2009). Warning thresholds performed satisfactory in back-anal-
ysis with data from the 1978 to 2003 period; only eight storms caused landslides
without previous threshold exceedance (Godt et al. 2006). Forty per cent of all
warnings were followed by landslides events and 85% off all landslides were
triggered by rainfall above thresholds values. To increase the acceptance of the
early warning system and improve risk awareness of the local residents, USGS
provides educational material and information (USGS 2006).
In the USA, USGS is responsible for allocation of warnings related to geo-
logical events, including landslides. To increase interoperability of warning sys-
tems and ensure smooth warning communication a common alerting protocol
(CAP) was created (Highland and Gori 2008). This data format is the same for
many different kinds of warnings including also man-made hazards and terrorism.
Today it is widely used by state agencies in the USA. Landslide related CAP
warning have been adopted for all study areas, for which reliable rainfall thresh-
olds have been established, i.e. Seattle, San Francisco Bay Area and burned areas
and parts of the Appalachian mountain areas of the eastern US. All alerts,
including archived warnings, are presented on USGS website. To increase the
populations’ awareness of landslide hazards and the potential outcomes of land-
slide events, a documentary movie was produced, which is also planned for school
education (Highland and Gori 2008). Moreover, a wide range of fact sheets, reports
and other information on landslide hazards, consequences and warnings is pro-
duced by USGS.
The most advanced and successful landslide early warning system may be that
installed in Hong Kong, China (Schuster and Highland 2007). Hong Kong is
densely populated by seven million inhabitants and very prone to landslides
occurrences and damage consequences. The terrain is rugged, with hills rising up
2.4 Landslide Early Warning Systems 43
Fig. 2.8 Number of landslide fatalities in Hong Kong (after Wong and Ho 2000)
steeply, and less than 30% of the densely populated areas are flat (0–5) (Brand
et al. 1984). The limited availability of favourable land means that geotechnical
slope construction works including design of cut and fill slopes and slope stabi-
lisation are frequently required. Moreover, strong rainfalls with hourly intensities
exceeding 150 mm occur along with tropical cyclones and low pressure. After two
catastrophic landslide events in 1972 and 1976 which together caused more than
100 fatalities, the Geotechnical Control Office was established to reduce landslide
consequences (Malone 1997). Later, the agency was renamed the Geotechnical
Engineering Office (GEO). GEO has many responsibilities, such as establishing
instructions and guidelines for slope design, slope stabilisation, quantitative risk
management and early warning (Chan 2007). Moreover, education programs for
the general population and homeowners aim to raise awareness of landslides and
related risks. Radio and television features, a telephone hotline and a website
provide a wide range of information and advice to local residents (Massey et al.
2001). Detailed information on integrative landslide risk management strategies in
Hong Kong and the efforts and experiences of GEO is available in a collection of
scientific papers published for the 30th anniversary of GEO (Geotechnical Engi-
neering Office 2007). The great success of slope safety in Hong Kong is also
illustrated by significantly lower fatalities due to landslides after the establishment
of GEO’s predecessor in 1977 (Fig. 2.8).
The Hong Kong regional landslide early warning system was launched in 1977
and is managed cooperatively by GEO and Hong Kong Observatory. More than
100 automatic rain gauges built the technical base for early warning. Rainfall
thresholds triggering landslides in Hong Kong were first established by Lumb
(1975), but were modified several times afterwards when improved real time
rainfall and landslide data became available. Initially, warning thresholds
accounted for cumulative 24 h rainfall in relation to rainfall of the preceding
44 2 Theoretical Background
15 days. Warnings were issued if measured rainfall of the last 20 h and the
forecasted rain for the next 4 h exceed 175 mm (Chan et al. 2003). In the 1980s an
hourly rainfall threshold of 70 mm was added to the warning scheme. Progressive
analysis of landslide initiation and related rainfall events led to prediction of the
number of landslides expected for certain storm events. Warnings were only issued
if 15 or more landslides were expected to occur (Chan et al. 2003). Since 2003 a
GIS-based approach has been used for landslide prediction (Yu et al. 2004).
Therein, the entire area of Hong Kong is represented as grid cells accounting for
number of properties contained on the slopes. The number of expected landslides
is then modelled according to a spatially variable susceptibility to slope failure.
A recent development of the landslide early warning system includes the inte-
gration of radar data from the SWIRLS system (Short-range Warning of Intense
Rainstorms in Localised Systems) to track storm cells and improve quantitative
prediction of localised storms (Cheung et al. 2006). Warning dissemination utilises
TV, radio and internet to inform the public. In addition, emergency forces and
hospitals are contacted if large numbers of landslide are expected. In early years
warning messages were mostly aimed at slum dwellers because they lived in most
hazardous areas. However, social and geotechnical developments since the 1980s
changed the focus. Today, the intention of early warning is to inform the entire
population about potentially hazardous events, thus to provoke cautious behaviour.
Mainland China is probably experiencing the highest landslide damage and
number of fatalities in the world (Tianchi 1994). China has begun to address the
landslide problem in the 1990s by starting a nationwide investigation program
including landslide mapping, susceptibility zoning, risk analysis, rainfall threshold
analysis, prevention planning and engineering counter measures (Yin 2009) and
early warning (Zhou and Chen 2005). Since 2003 landslide warning based on
rainfall forecasts are issued after general weather reports on prime time TV shows
(Yin 2009).
A regional landslide early warning system based on susceptibility maps and
rainfall thresholds was installed for Zhejiang Province (Kunlong et al. 2007; Eng
et al. 2009). The system is based on rainfall forecasts and works as a WebGIS.
Warnings are issued if rainfall predictions exceed one of the two defined thresh-
olds and near real-time warnings are spread through various communication
channels (internet, telephone, etc.). The warning system is also combined with an
assessment of economical risks which aim to extend the system to landslide risk
warning (Wu et al. 2009).
Zhong et al. (2009) provide detailed information of the precipitation based early
warning system for Hubei Province. The landslide early warning system was
installed in 2006 and represents a WebGIS. Critical rainfall thresholds have been
determined by analysing the statistic relationship between spatial distribution of
occurred landslides and rainfall data. Warning generation is based on 2 and 15 day
antecedent rainfall, which is compared to 24 h rainfall forecast. If thresholds are
exceeded in any of the 82 divisions in which Hubei is differentiated, the Meteo-
rological Survey of Hubei Province issues a warning on the internet. More
information on the current situation is freely accessible in the form of maps on the
2.4 Landslide Early Warning Systems 45
Fig. 2.9 Comparison of warning curve and warning line thresholds and subsequent time spans
for evacuation (after Aleotti 2004)
Schmidt et al. (2008) present an innovative landslide early warning system for
New Zealand. Therein, probability of landslide failures is computed by combi-
nation of a regional physical-based hydrology and stability model with quantitative
weather forecasts. However, landslide prediction is subject to large uncertainties
which are assessed by probabilistic methods. Unfortunately, the early warning
system was only a prototypic development and is currently not active.
Aleotti (2004) presents a prototype of a regional landslide early warning system
for shallow landslides in the Piedmont Region of north-western Italy. Rainfall
thresholds were determined by analysing intensity-duration, antecedent rainfall
and mean annual precipitation. Warning thresholds, however, were established
lower than triggering thresholds to provide more safety. Instead of a warning
threshold parallel to the triggering threshold (Aleotti 2004) applied a curve to
account for different rain paths (Fig. 2.9). By doing so time spans until landslide
triggering threshold exceedance are integrated, which are important for initiation
of evacuations. The technical warning system includes rainfall forecasts and sta-
tion measurements. The system remains in an ordinary attention state until
thresholds are exceeded by rainfall forecasts. A preceding warning procedure is
launched if landslide prone areas are affected by threshold exceedance. Rainfall
paths are then plotted according to antecedent and real-time rainfall and an alert is
issued according to the pre-defined thresholds.
Recent developments of the regional landslide early warning system concen-
trated on the improvement of thresholds by including local properties, such as
topography and geological properties (Tiranti and Rabuffetti 2010). Consequently,
three thresholds were established, i.e. regional, sub-regional and a pragmatic
threshold, which accounts for multiple occurrences of landslide in single rain
events. All thresholds were tested for their performance in a back-analysis in terms
of correct, false and missed alarms. In addition, a technical system named SMART
was developed which analyses rainfall time series for each rain gauge in real time
and identifies where thresholds are exceeded. The current early warning system
utilises rainfall forecast and real-time measurements and applies the pragmatic
threshold (Tiranti and Rabuffetti 2010).
The Åknes rockslide in Norway is one of the most intensely investigated and
monitored landslides worldwide (e.g., Derron et al. 2005; Ganerød et al. 2008;
Kveldsvik et al. 2008, 2009; Eidsvig et al. 2011; Heincke et al. 2010; Grøneng
et al. 2010). The rockslide itself does not pose direct threat to a community,
however, slope failure is supposed to trigger a tsunami affecting ships and towns
along the fjord. The rockslide mass has a volume of 30–40 million m3 and dis-
placements vary with seasons and reach 3–10 cm/year with daily movements up to
1 mm (Blikra 2008). The technical monitoring system includes extensometers,
inclinometers, crackmeters, tiltmeters, geophones, piezometers, automated mea-
surements by theodolites, laser and GPS and ground based radar, and a climate
station. All data is available in a web-based database and supervised by experts
24 h a day. Threshold values for displacement velocity have been established
which relate to five alert levels colour-coded from green to red. In case of
imminent slope failure sirens warn the population in potentially affected towns.
48 2 Theoretical Background
Fig. 2.10 Early warning system at Winkelgrat landslide equipped with automatic extensometers
(left) and traffic light for road closure (right)
flows was installed and described in detail by Badoux et al. (2009). The
overarching early warning concepts includes ongoing education and allocation of
information for the local population regarding debris flows and possible conse-
quences, a monitoring system, repeated field surveys to assess changes in the
catchment, and integration of meteorological measurements to increase forewarn
time (Graf et al. 2006). Several education campaigns were performed to inform
local population about potential hazards and the early warning systems. In addi-
tion, children at elementary level learn about debris flows in school. Tourists are
provided information at local tourist information centre. Along the debris flow
channel warning signs were put up every 200 m explaining the threat of debris
flow occurrences in five languages. Moreover, warning lights and loud speakers
were installed at three spots where hiking trails cross the debris flow channel. The
early warning system is managed and maintained by Illgraben Security Com-
mission and contacts local emergency task forces if potentially dangerous situa-
tions emerge. The technical system includes several geophones located at check
dams, which can automatically trigger warning lights and speakers further down
the debris channel if a seismic signal lasts for more than five seconds. At the same
time SMS and emails are sent to local decision makers. A forewarn time of 5 to
15 min between measurement of debris flow by geophones and a debris flow
reaching settlement areas in the valley is provided by the system. Alarms can be
cancelled if geophones further downslope do not detect seismic signals 10 min
after the first signal. This is done to decrease chances of false alarms due to other
potential geophone triggers, e.g., rock fall, thunderstorms or earthquakes. Further
technical equipment of the Illgraben monitoring systems includes measurement of
discharge by ultrasonic sensors, laser and radar. Based on their experiences
Badoux et al. (2009) propose radar as the most suitable method for early warning,
as it provides smooth and reliable data on discharge even in situations of rapidly
fluctuating discharge amounts. The catchment is visited and mapped regularly to
detect changes in the debris flow source area, such as landslides that provide
material for further debris flow occurrences. Including meteorological forecasts
into the early warning systems and defining rainfall thresholds was also trialled.
However, integration failed because local thunderstorms in alpine areas are diffi-
cult to predict. The debris flow early warning system at the Illgraben can be
regarded successful. Since its implementation 20 alarms were issued, of which
only one was a false alarms, and in only three cases a warning was cancelled even
though the debris flow had not stopped. The Illgraben catchment is also part of the
national IFKIS-Hydro early warning and information platform, which provides
monitoring data and event documentation (Romang et al. 2010).
In the North Italian community of Nals a local debris flow early warning system
was installed after devastating debris flow events in 2000 (Egger and Mair 2009).
The aim of the early warning system was to be an addition to structural protection
measures. Debris flow material is supplied by landslide processes in the upper
catchment. However, due to the high activity it was decided not to install an
automatic system there, but to place a series of geophones into the debris flow
channel to detect already initiated events. Still, a forewarn time of 20 to 60 min
52 2 Theoretical Background
between a geophone alarm and the debris reaching settled areas is accomplished.
Further technical equipment includes a piezometer, rainfall stations and a remote
controlled video camera with flood lights.
Another Italian case study on a debris flow warning system utilising geophones
is presented by Arattano (1999), however, it only was active for one summer.
A prototype of a mudflow early warning system for the Italian city Sarno is
described by Sirangelo and Braca (2004). Therein, the probabilistic hydrology
model FLaIR (Forecasting of Landslides Induced by Rainfall) was applied, which
correlates rainfalls with landslide occurrence. Warning thresholds were established
by back analysis and included the large 1998 event. According to these thresholds
three warning levels were determined, i.e. attention, alert and alarm.
The same model has been applied to Lanzo Valley of the Piedmont, Italy
(Capparelli and Tiranti 2010). Promising performance led to the current imple-
mentation of an automatic early warning system.
Hübl (2000) describes the application of a prototypic early warning system for
the Wartschenbach catchment in Austria, which frequently experiences debris
flows and flash flood events. The developed early warning system is thought as a
passive protection measure. The technical system is based on measurement of
rainfall and flow discharge by ultrasonic sensors in the upper catchment. If mea-
surements exceed pre-defined thresholds it is up to experts to decide whether to
close lower lying roads to prevent cars being hit by debris flows. By developing
adequate response plans for hazardous events they have tried to address the
response of the local community. The implemented system was planned and
implemented as a prototype and should be installed in other catchments which
could potentially produce debris flows after a test period.
A novel a landslide early warning system is described by Sakai (2008). Earlier
research (Sakai and Tarumi 2000) indicated that concentrations of sodium, cal-
cium and, sulphate ions in groundwater changed before phases of landslide
activity. Landslide failures could be predicted up to 90 days in advance. Therefore,
a prototypic landslide early warning system was set up which utilises automated
ion-selective electrodes to provide early warning to railroads in Japan. Data is
transmitted from the sensors in the field to train dispatchers and track maintenance
engineers via mobile phone networks. Measurements are taken every 1 to 3 days,
but frequency can be increased in the case of unusual sensor readings.
Another example of an early warning system in Japan is presented by Chiba
(2009). The warning system strongly emphasises warning communication and is
regarded as an integral element of the local disaster prevention program against
sediment-related processes (debris flows and debris floods). Earlier research on
local hazards provided information on potential hazardous zones and return
periods, which was utilised to allocate warning and evacuation zones in the
occurrence of debris flow events. Several people were employed to carry out
education programs in which local residents were informed about potential hazards
and appropriate reactions in case of a warning. If exceedance of pre-defined river
flow thresholds occurs a disaster management headquarter is assigned in which all
information about the current hazard status is collected. Information is gathered
2.4 Landslide Early Warning Systems 53
primarily by the employees by calling local residents by cell phone. Moreover, all
data is updated to a GIS platform which is available online. Chiba (2009) illus-
trates the effectiveness of the warning system by comparing its performance to a
neighbouring town, in which no early warning system was installed, and no
detailed hazard maps and evacuation plans were available. During a debris flow
event local disaster managers were overwhelmed by incoming information and no
efficient evacuation could be initialised. In contrast, disaster managers of the town
with a warning system were able to quickly determine where debris flows had
occurred and to initialise evacuation according to the pre-determined schemes.
Flentje et al. (2005) present a real-time monitoring network for time pore water
pressure, slope movement and rainfall in Wollongong, Australia, which aims to
enhance understanding of landslide triggering process and improve quantitative
assessment of landslide hazards. All data is automatically sent via a cell phone
network to a web-based database available online. Threshold values have been
determined and current measurements are colour-coded to allow for easy inter-
pretation. However, the described system is essentially technical and does not aim
to provide warning messages or initiate counter measures or evacuation.
Besides the ILEWS project several other research programs focussing on early
warning systems for natural hazards were funded within the Geotechnologien
framework. Three of these projects also concentrated on landslide processes, and
will briefly be described in the following.
The SLEWS (Sensor-based Early Warning System) project focused on three
sensor types measuring acceleration, inclination and pressure to monitor landslide
initiation (Fernandez-Steeger et al. 2009). The project emphasized technological
developments accounted for sensor development and laboratory testing. A large
proportion of the accomplished work concentrated on wireless sensor networks to
ensure smooth data transmission. Developed sensors were applied to several real
case studies on the Barcolonette earthflow in France, and rockfall warning in Rathen,
Germany. However, besides the technical research, the integration of early warning
in social decision making process was another topic of the SLEWS project.
The main goal of the alpEWAS project was sensor-based monitoring and early
warning in the Bavarian Alps (Singer et al. 2009; Thuro et al. 2009). Thereto, three
main methods were utilised to detect displacements, i.e. TDR measurements,
prism-less tachymetrie and low-cost GPS measurements. In addition, an infor-
mation platform was set up to collect all data and inform involved experts by email
and SMS if pre-defined thresholds were exceeded.
The EGIFF project adopted a technical approach and concentrated on the devel-
opment of new methods applicable within landslide early warning. A wide range of
geotechnical data for a test slope south of Munich, Germany, was compiled and
modelled by a finite element model (Breunig et al. 2009). In addition, 3D/4 D databases
were developed for effective data visualisation. Moreover, the project implemented an
automated system to interpret media news and extract landslide related information.
From the examples of landslide early warning systems illustrated above some
conclusions can be drawn. Regional landslide early warning systems that focus on
shallow landslides or debris flows generally rely on rainfall thresholds derived by
54 2 Theoretical Background
The work described within this thesis is embedded into the ILEWS project (Inte-
grative Landslide Early Warning Systems) which will be briefly introduced in the
following. Integrativity therein does not only refer to a strong interdisciplinary and
cooperative work between the project partners, but also to involvement of social
sciences aiming to cooperatively embed early warning into the prevalent political
2.5 The ILEWS Project 55
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