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7/27/2019 GPR Investigations to Assess the State of Damage of a Concrete Water Tunne
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GPR Investigations to Assess the State of Damage of a Concrete Water Tunnel
Diego Arosio1, Stefano Munda1, Luigi Zanzi1, Laura Longoni2 and Monica Papini2
1Dip. di Ing. Strutturale, Politecnico di Milano, Piazza Leonardo da Vinci 32, 20133 Milano, Italy2Dip. di Ing. Idraulica, Ambientale, Infrastrutture Viarie, Rilevamento, Politecnico di Milano,
Piazza Leonardo da Vinci 32, 20133 Milano, Italy
ABSTRACT
Erosional voids developing around concrete-lined tunnels can compromise the safety of
the surrounding areas, as well as of the tunnels themselves. In this study, ground penetrating
radar (GPR) was used to assess the condition of a water tunnel built to channel a river under a
mountain road. The tunnel is lined with 6080 cm thick concrete and has a semicircular cross-
section with a diameter that varies between 3 m and 4 m. The concrete structure has been
damaged from erosion beneath the concrete floor, creating a sequence of pools and waterfalls,
which further extend the erosive action below the floor and side walls.
After the collapse of a section of the tunnel
running below a nearby parking lot, a GPR investiga-
tion was initiated to assess the extent of the erosive
action behind the tunnel walls and below the concrete
floor. Most GPR measurements were performed from
inside the tunnel with a 200-MHz antenna, which was
selected as the best trade-off between penetration and
resolution. GPR results, integrated with a priori
information and geological investigations, indicated a
highly permeable soil consisting of a thin layer of
alluvial sediments that covers an altered limestone layer
strongly affected by erosion and karst phenomena.Fortunately, GPR inspections on the parking lot surface
were able to exclude the presence of large cavities above
the tunnel vault. On the contrary, GPR inspections
performed inside the tunnel detected many voids
forming behind the walls, especially near the concrete-
rock contact. GPR inspections performed on the tunnel
floor confirm that water erosion is active below the
concrete paving. Overall, the survey was useful for
identifying the damaged tunnel segments where repair
interventions are most urgent.
Introduction
Tunnels are important underground structures
used in the transportation of vehicles, water, electricity,
and other items. Many of these structures have been
built decades earlier, and it is of paramount importance
to assess the integrity of these underground construc-
tions to ensure safety and long-term viability. Towards
this end, several empirical (Schmidt, 1974; Attwell,
1978), analytical (Verruijt and Booker, 1996; Bobet,
2001) and numerical analyses (Leca and Clough, 1992;
Augarde and Burd, 2001; Menguid and Dang, 2009)
have been conducted to evaluate tunnel stability. In
particular, Meguid and Dang (2009) used numerical
models to evaluate the negative effect of erosional voids
developing in close vicinity of tunnels. They studied the
effects of voids on the circumferential stresses in the
lining and the change in lining response caused by the
introduction of voids behind lateral walls (i.e., at the
springline) and below the paving (i.e., at the invert).
While they assumed a homogeneous hosting medium
and a theoretical 2-D geometry of the voids, their workhelped to improve the knowledge of the stress state of
these structures.
In this work, we attempt to identify the erosional
voids in a water-filled tunnel using geophysical methods,
particularly ground penetrating radar (GPR). The
geophysical investigation was part of a broader study
focused on understanding the hydrogeological condi-
tions that potentially could contribute to the deteriora-
tion of the water-carrying infrastructure along a
national road that runs through a narrow valley. The
road is periodically affected by service interruptions
caused by small landslides or partial road collapses
induced by water erosion and intense precipitationevents. The risk of road collapses increases where the
road runs close to the river or where the river crosses the
road by flowing into concrete-lined tunnels. The con-
crete tunnels were built at the beginning of the 20th
century and were not properly maintained over the past
decades. Rapid deterioration induced by water erosion
and lack of maintenance are a major safety concern. For
example, a large sinkhole triggered by a partial collapse
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of one of these underground infrastructures occurred in
2007 in a parking area near the road. No injuries were
reported, but the incident could have been much worse if
the concrete tunnel had collapsed a few meters ahead,
where it passes under the road, or if the sinkhole had
occurred during a weekend when that parking lot is
often crowded.
A team of geologists, geophysicists, hydrologists,
and civil engineers from Politecnico di Milano were
involved to assess the risk of similar events along two
segments of the concrete tunnel responsible for the 2007
sinkhole. The most severely damaged section of the
tunnel runs parallel to the valley for 300 m before
intersecting the road, where the valley makes a
pronounced left turn. No traces of regular maintenance
operations or previous assessment studies were found in
the archives of the local environmental agency in charge
for the management of the water infrastructures. An
exception was a partial visual inspection performed
inside the tunnel in the year 2004, which reported asevere deterioration of the concrete structure and
suggested further investigations to be performed with
the georadar method. Although the archives do not
report any repair operation, the visual inspection of the
tunnel assessed the existence of some provisional
reinforcements that were installed in two points of the
tunnel where the concrete structure is highly fractured.
These reinforcements, consisting of timber and metal
elements, were likely installed in the 1990s and already
had presented signs of deterioration. We mention these
details because it is likely that other tunnels of similar
vintage have incomplete inspection records or less-than-
effective maintenance.The team of Politecnico di Milano planned to
perform a visual inspection of the entire tunnel to assess
the present condition (concrete fracturing, water infil-
trations, floor erosion, etc.) and to explore the feasibility
of non-destructive investigations testing (NDT) of the
tunnel. One of the more common NDT methods that
have been used to perform investigations on concrete
liners of tunnels, sewers, and railway or road tunnels is
GPR. For example, Maekawa and Fenner (1994)
reported the use of GPR to assess the extent of cavities
behind concrete tunnel linings. Cardarelli et al. (2003)
used GPR to evaluate the quality of the contact between
concrete lining and massive rock from inside a potablewater supply tunnel. Davis et al. (2005) reported the use
of GPR to examine the efficiency of tunnel lining
groutings and showed examples from investigations
performed on water supply and sewer tunnels. Parkin-
son and Ekes (2008) showed the use of GPR to map
tunnel lining condition, to locate concrete deterioration,
and to detect voids developed between the concrete liner
and rock surface caused by water flowing either in or
out via defects in the liner. Zhang et al. (2008) used GPR
to evaluate the lining quality of a railway tunnel and to
detect the hidden flaws in the lining. The investigation
results were used to direct subsequent grouting, with a
follow-up survey to assess the quality of the grouting.
Finally, Zhang et al. (2010) described a similar applica-
tion where the use of GPR was proposed to detect the
grout thickness behind the lining segments of metro lines
in Shanghai, China.
In the literature that focused on GPR investigations
of underground and concrete-lined tunnels, most of the
focus was on the inspection of the upper part of the
tunnels, i.e., walls and vaults, where overburden stresses
were the highest. However, in the case of water-filled
tunnels, the floor has been given little attention, likely
because of the difficulties of performing NDT without
service interruptions. However, it is important to mention
that the lower part of a water tunnel can be as critical or
even more so than the upper part, depending on the
geometry of the tunnel cross-section (circular or semicir-cular) and on flow regime and water pressure.
GPR is a method that is often proposed to perform
near-surface geophysical investigations on karst areas
where the risk of sinkhole formation is high. Carpenter
et al. (1998) and Batayneh et al. (2002) reported examples
where GPR and other geophysical methods were tested to
locate buried sinkholes as a means of inferring the
existence of hydraulically-active karst features. Leucci
et al. (2004) applied GPR and ERT for mapping
karstified zones. Beres et al. (2001) combined GPR and
microgravimetric methods to achieve the same objective.
Conroy and Guy (2005) and Conroy and Daniels (2006)
described GPR surveys conducted along a section ofhighway that had collapsed into underground coal mine
workings to detect other locations of mine-related
disruptions. Miller et al. (2008) showed GPR data
collected at two Vermont highway sites exhibiting
pavement subsidence. The GPR data were useful to
study the soil properties and to understand the subsidence
mechanism, in one case related with water erosion and
resulting in fine particle migration. Pueyo-Anchuela et al.
(2009) tested the GPR method to study the internal
structure of sediments in search of indicators of active
karst processes. They performed a classification of karst
hazard problems in terms of cavities, evidences of
subsidence and paleocollapses. In a following paper thesame authors propose a combination of geophysical
techniques that can be successfully applied in alluvial
karst regions to locate areas of high sinkhole risk (Pueyo-
Anchuela et al., 2010).
From a summary of the collected works, it is clear
that GPR is a robust method to effectively determine
trouble spots along the water-filled tunnel at the test
site. Therefore, this paper addresses the geophysical
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investigation in three different areas to determine those
needing further investigation: a) inside the tunnel, b) in
the parking lot near the road, and c) along the segment
of the road that runs close to or above the tunnel.
Particularly, the investigations inside the tunnel were
aimed to assess the extent of water erosion behind the
tunnel walls and below the segments of the tunnel floor
that are still preserved. Since the mechanism of collapse
of the structure was likely triggered by the erosion of the
wall foundations, the investigations on the preserved
concrete floor, especially near the wall-floor contact, are
particularly important (Meguid and Dang, 2009).
Furthermore, these studies represent an interestingapplication that is not well documented in the GPR
literature. To conduct these measurements, the GPR
antennae were placed inside a PVC box and the
surveying of the concrete floor was performed by
preserving the contact between the antenna and the
floor. Investigations in the parking lot and along the
national road were aimed to detect GPR anomalies that
could be related to cavity formation caused by erosional
activity above the tunnel vault, whose depth varies from
1 m in the parking lot to about 8 m at the end of the
second segment of the tunnel.
Site Description
The geophysical investigations were conducted in
the area of the waterfalls located in the Valganna valley
(Fig. 1), 60-km north of Milan (Italy). Geological
mapping of the site was performed at the beginning of
the study and it was determined that two different
carbonate facies, pertaining to a dolomitic-limestone
sedimentary succession of Mesozoic age, outcrop in thearea of the Valganna waterfalls. The travertine is highly
karstified, whereas the dolomite rock is heavily frac-
tured with the presence of thick folds. The tunnel was
built along the contact between alluvial deposits of the
Olona River and the strongly karstified travertine. At
shallow depth, close to the tunnel, alluvial deposits are
characterized by loose, unconsolidated soil in a sandy
matrix with centimeter-sized clasts. The deposit shows a
Figure 1. Location of the GPR investigations and map of the tunnel. The area is located in the Pre-alpine region, 60 km
north of Milan (Italy). The drawing illustrates the section of the national S.S.233 road where the Olona River is forced to
enter the first segment of a concrete-lined tunnel to underpass both the parking area of the Valganna Waterfalls and the
road. A second segment of the tunnel runs parallel to the road before crossing it again. On top right, a drawing of the
tunnel cross-section shows the position of the antenna for the GPR profiles undertaken inside the tunnel.
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variable thickness across the area, with a maximum
depth of 1.5 m. Beneath the alluvial deposits, the
bioconstructed limestone bedrock is heavily weatheredbecause of karst processes in the first 2 m (Fig. 2), while
its mechanical properties tend to improve at greater
depth.
From a hydrogeological point of view, this site is
subjected to a double erosion process: the first is directly
related to water flowing inside the tunnel and a second is
caused by water infiltration in the heavily fractured and
karstified hosting rock mass. The Mesozoic sedimentary
succession shows a significant secondary permeability
(i.e., permeability developed in a rock after its deposi-
tion), mostly because of karst processes, giving rise to the
second erosional process. However, it is worth noting
that permeability of dolomites is mainly related toextensive fracturing, while limestones are heavily affected
by karst phenomena that give rise to subsurface water
flow.
As shown in Fig. 1, the Olona River was diverted
into an underground concrete chamber below the hotel
of the Valganna Waterfalls, after which it enters a
concrete-lined tunnel to underpass the parking area of
the waterfalls and the national road (S.S.233). Splitting
the study site effectively into two segments, the first
segment ends on the south side of the parking area,
highlighted in Fig. 1. Within 50 m, the river enters a
second segment of the tunnel that runs parallel to theroad for about 300 m. At the end of the second segment
of the tunnel the road turns left in the direction of a
brewery.
The investigations were planned after the formation
of the 2007 sinkhole. The sinkhole was caused by the
collapse of the tunnel, which created a void 13-m long
and 3.5-m high. Figure 3 shows the construction site
during the repair of the tunnel. The picture shows that the
internal section of the tunnel is semicircular with a
diameter of about 3 m and a height of about 2 m. The
thickness of the concrete wall varies from 60 to 80 cm and
the vault is about 1 m below the parking level.
The internal inspection of the tunnel revealed anextreme deterioration of the concrete structure. Figures
4(a)(b) show large areas where the concrete floor of the
tunnel partially collapsed as a result of bedrock erosion.
Bedrock erosion caused the most dangerous situations
at the base of the lateral walls of the tunnel, as depicted
on the right side of Fig. 4(b). As a result of the erosion
action, the water flow was quite irregular with pools and
waterfalls existing throughout (see Figs. 4(c)(d)), espe-
cially in the second segment of the tunnel. Temporary
bridges were assembled to perform inspections and
geophysical investigations. The second segment also
showed evidence of water seeping through the concrete
ceiling (Fig. 4(e)). Finally, Fig. 4(f) was taken near theend of the second segment and showed timber and metal
reinforcements that were used in the past for repair.
The internal inspection revealed a major conse-
quence of water erosion and subsequent collapse of the
concrete slabs that forms the tunnels pavement. That
is, the erosional activity can progress laterally below
the tunnel walls at a much higher rate than would be
expected from water infiltration through secondary
Figure 2. The lapideous rock layer consists of weathered
limestone highly affected by karst phenomena.
Figure 3. The construction site that followed the tunnel
collapse in 2007. The tunnel section is semicircular (about
3-m across and 2-m high) with a concrete wall thickness of
about 6080 cm.
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Figure 4. Inspection of the tunnel. a) and b) Examples of damages of the concrete paving created by water erosion below the
tunnel floor. Note also the very dangerous erosive actions of the water below the lateral walls of the tunnel. c) and d)
Examples of waterfalls and water pools caused by collapsed portions of the concrete floor induced by water erosion.
Temporary bridges were needed to bypass the larger pools with the GPR equipment. e) Signs of water seeping through the
concrete vault in the second segment of the tunnel. f) Remains of an old repair intervention in the second segment of the tunnel.
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permeability features (fractures and karst) alone. This
creates a very dangerous situation, with the potential
to trigger new tunnel collapses. Thus, the results of
the internal inspections underline the importance of
further diagnostic investigations to assess the extent
of water erosion activity beyond the tunnel walls and
especially below the still preserved slabs of the concrete
floor.
Data Acquisition
Despite the adverse conditions created by floor
collapses and water pools, an extensive GPR survey was
undertaken from inside the tunnel. The late summer
(September 2008) was chosen for operation inside the
tunnel because of the reduced rate of water flow. After
some preliminary testing performed with two different
antennae frequencies (200 MHz and 600 MHz), the
lower frequency was selected as the best tradeoff
between resolution and penetration. Both the antennaswere able to detect areas of detachment between the
concrete liner and the rock, but the 200 MHz antenna
was offering higher penetration thus extending the
ability to detect cavities and karst features a few meters
beyond the tunnel wall. The 200 MHz antenna was also
selected for the radar survey of the parking lot and for
the radar profiles along the national road to ensure a
penetration of several meters. Thus, the equipment for
all the investigations consists of a 200 MHz shielded
antenna with a TX-RX separation of 19 cm controlled
by a radar unit from IDS S.p.A.
GPR data were initially collected on the surface by
exploring the parking area of the hotel near the waterfallsand the road that runs close to the river. The aim of these
surface measurements was to evaluate GPR penetration
in the specific area and to assess the ground properties
above the tunnel with special attention to detect karst
features and cavities. The parking area was explored by
selecting seven zones above the tunnel route that were
scanned in 3-D mode by executing parallel profiles spaced
50-cm apart.
Several long profiles were collected along the
national road, which runs near the underground tunnel.
GPR data acquisition was particularly focused on the
road segments that cross over the tunnel. GPR measure-
ments were also collected inside the tunnel, which tookseveral days to complete, and were performed to achieve
the following goals: a) detect possible voids excavated by
water behind the lateral walls of the tunnel either
proximal to the concrete-rock contact area or within a
3-m distance from the wall; and b) explore the apparently
undamaged segments of the tunnel floor to assess the
extent of the water erosion below the concrete paving.
Profiles were collected along both tunnel walls by walking
in the tunnel direction, except for those segments where
the tunnel floor had collapsed creating large and deep
water pools. We were forced to collect profiles at a height
of about 45u on both sides of the tunnel section (top right
in Fig. 1) because at lower angles from the floor metal
reinforcements protrude from the concrete. Floor profiles
were also collected where possible, i.e., on the preserved
concrete slabs, by walking in the tunnel direction with the
GPR antenna placed inside a waterproof PVC box. A
large wheel with encoder was attached to the box to
trigger the radar unit to help with geo-referencing. The
floor profiles run close to the walls rather than in thetunnel center (top right in Fig. 1) because the erosive
action of the water is particularly dangerous for the
stability of the tunnel when it creates large voids below
the lateral walls, as visible in Fig. 4(b).
Data Processing and Interpretation
Data processing was performed with 2-D and 3-D
software developed at Politecnico di Milano. The data
were bandpass filtered and time calibrated before
applying a gain function to compensate for signal loss
caused by divergence and absorption. A function for
background subtraction was applied where needed toenhance very shallow targets. Some data were also
migrated to focus the diffractions produced by cavities
or other scattering targets.
On the whole, all the surface profiles collected in
the parking area or along the national road show good
penetration. Reflections or diffractions from targets 5-m
deep (about 80 ns) are often observed (Fig. 5). This
suggests that the subsoil contains little to no clay and is
Figure 5. Example of a 40-m GPR profile along the
national road. Penetration down to 80 ns (i.e., about 5 m)
is observed. Alluvial sediments (1- or 2-m thick) overlay a
layer of altered limestone. Reflection A comes from the
base of the paved road. Reflection B comes from the
interface that separates the sediments from the limestone,
while reflection C comes from a change of compaction
within the alluvial sediments. Many diffractions and short
discontinuous reflections are observed in the image as a
result of karst phenomena. Some diffractions within the
alluvial sediments might be caused by pipes crossing the
road (e.g., diffraction D).
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rather coarse so that minimal water is retained. This
observation is also consistent with the relatively high
velocity obtained from diffraction analysis: a stable
value of about 12 cm/ns, not compatible with saturated
sediments, was found in all the GPR records. Thesediments are typified by alluvial deposits in a sandy
matrix with centimetric clasts, overlaying a travertine
layer characterized by high permeability caused by both
karst phenomena and significant fracturing. The tran-
sition between alluvial deposits and limestone is visible
in Fig. 3 at about 1 m below the parking level (see the
color change of the exposed rock). In Fig. 5, this
transition generates reflection B, gently dipping from
right to left in the 1040 ns range corresponding to a
depth range of 0.52.5 m. Reflection C comes from a
change of compaction within the alluvial deposits.
The profiles collected on the parking lot and alongthe national road generally present images with a greater
number of diffractions than the tunnel profiles. Figure 6
is an example where the diffraction density is particularly
evident. Some diffractions also show strong reverbera-
tions that suggest the possibility of metal pipes or open
voids (e.g., Radzevicius et al., 2000; Kofman et al., 2006).
Given that no buildings exist along this section of the
road to justify a great number of lateral connections to
sewer or other utilities, it is likely that most of these
diffractions are associated with small voids resulting from
intense karst activity. The voids are also visible on the
trench sides in Fig. 3.
The tunnel vault is observed by the surface radarmeasurements, but only where the tunnel depth is less
than 45 m, i.e., in the parking area and below the road
at the first road/tunnel intersection. Here the vault is
often well depicted and both the reflections from the
outer and the inner sides of the concrete ceiling are
distinguished (Fig. 7). The tunnel floor appears with a
non-flat reflection because of the expected image
distortion caused by the circular vault, enhanced by
the much higher velocity of the radar wave within the
air-filled tunnel.
The GPR data collected on the lateral walls were
processed to enhance diffractions and reflections coming
from the concrete-rock discontinuity and from the voids
in the limestone rock created by both erosion and karstphenomena. All the radar signals that were attributed to
voids very close to the concrete tunnel (within 1 m) were
mapped on the radar images with a solid box, whereas a
dash-dot box was used to map signals attributed to voids
at a distance greater than 1 m from the tunnel. To
separate erosional features from metallic infrastructure, a
dashed box was used to highlight the possibility of pipes.
As an example, Fig. 8 shows a 13-m long section of a wall
profile where voids were detected near the rock-concrete
contact and also far from the contact, at a distance of
about 160 cm. The features are particularly evident in the
migrated section, shown in Fig. 8(b). An accurate report
was produced during the GPR survey to monitor theexistence of any construction elements that could disturb
the radar data. This was important to ensure a correct
interpretation of signals like the artifacts shown in Fig. 8
resulting from two pairs of lateral intake pipes. The radar
image in Fig. 9 illustrates another 13-m long section of a
wall profile. Most of this section is affected by a persistent
detachment of the concrete wall from the rock. In
addition, a strong reflection indicates a suspected cavity
Figure 6. Example of another 44-m GPR profile along
the national road. Reflection A comes from the base of the
paved road. Diffractions B and C are superficial pipes
crossing the road. Many other diffractions are observed as
a result of small voids created by water erosion and
karst phenomena.
Figure 7. Example of a vertical section extracted from a
3-D survey in the parking area. Note the reflection from
the upper (U) and lower (L) sides of the concrete vault of
the tunnel. The time difference, about 11 ns, indicates a
concrete thickness of 55 cm assuming a concrete velocityof 10 cm/ns. Note also the distorted reflection from the
tunnel floor (F). This arrives with a delay from L
(measured at the center of the tunnel) of about 13 ns,
which gives a tunnel height of 195 cm assuming a velocity
of 30 cm/ns (air velocity) within the tunnel.
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2-m long located at a distance of about 180 cm from the
tunnel.
Similarly, the data from the investigations on the
tunnel floor were interpreted by mapping with solid
boxes all the signals that were attributed to water pools
created by erosion and karst phenomena below the
concrete paving. An example is given in Fig. 10, wherefour water-filled cavities were detected in a 7-m long
segment of the tunnel floor. Since the radar velocity in
water is very low (about 3.3 cm/ns), the thickness of the
suspected pools observed in Fig. 10 varies from 8 cm to
3540 cm. The signals associated with these phenomena
sometimes appear as diffractions (small cavities filled by
water), while at other times they appear as reflections
(wider water pools). In some cases, the reflection
reverberates indicating that the horizontal size of the
water pool is not much larger than its thickness
(Kofman et al., 2006). The radar velocity resulting from
the diffraction analysis on floor profiles (generally lower
than 6 cm/ns) validate the presence of water below theconcrete paving.
To create a synthetic map of the deterioration
progress that might be used by the engineers to evaluate
the residual risk and to plan the most urgent actions, all
the voids that were observed behind the concrete walls
and all the water pools that were detected below the
concrete paving were transferred on a CAD map, as
shown in Fig. 11. According to the synthetic map,
moving from right to left by following the direction of
the river, we note the following results. The parking area
(section C in Fig. 11), before the first river-road
intersection, shows an average density of radar events
with a number of them generated by suspected cavities
located about 2 m behind the tunnel wall. The short
section where no events are reported corresponds to thearea of the 2007 collapse that was under repair during the
GPR investigations. The second segment of the tunnel
apparently shows two safe sections where no radar events
are reported. Actually, they correspond to areas affected
by large and extended pools that prevented the possibility
to walk and investigate the walls. Thus, they are the most
damaged sections of the tunnel where the concrete floor
has been almost totally eroded. From the entrance of the
second segment to the first unexplorable area (section B
in Fig. 11), we note a higher density of events compared
to the parking area, especially related with detachments
between the concrete wall and the hosting rock. In
between the two unexplorable areas, we note a section(section A in Fig. 11) affected by a very high density of
events of various types (detachments, cavities, water
pools). This section and the two neighboring unexplor-
able areas, especially at the intersection with the road,
define the most damaged stretch of the tunnel where local
authorities and engineers should plan renovation works
with the highest priority. The last section of the tunnel
before the final exit shows an average density of events;
Figure 8. Example of a wall profile: a) before migration, b) after migration. Voids were detected behind the concrete wall
near the rock-concrete contact (solid boxes) and at a distance of about 160 cm (dash-dot box). The dashed boxes indicate
artifacts, followed by reverberations, created by metal water pipes that enter the concrete tunnel from the side of the
GPR profile.
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this is where the remains of old repair interventions are
still present so that the tunnel is partially protected.
Conclusions
The GPR method contributed successfully to the
characterization of damaged sections around a water-
filled tunnel. Surface profiles showed good penetration(up to 45 m) and high velocity (12 cm/ns) suggesting a
rather coarsely textured soil and excluding the presence of
significant clay content. The GPR data indicated a
pseudo-horizontal reflection at about 1 m and a large
number of diffractions commensurate with a thin layer of
alluvial sediments that covers an altered limestone layer
strongly affected by erosion and karst phenomena. This
suggests that water erosion and karst phenomena
represent the main hazards associated with this concrete
tunnel and a collapse in 2007 was most probably caused
by water excavation at the tunnels base. As further
revealed by internal inspections, water erosion tends to
create variably-sized voids below the tunnel paving,
especially where the semicircular concrete structure is
expected to rest on the bedrock, i.e., below the lateral
walls.
The 3-D GPR inspections performed on the
parking lot surface along the trajectory of the tunneldid not locate any large anomaly that could be related
with the formation of a large cavity above the tunnel
vault. On the contrary, the GPR inspections performed
inside the tunnel detected many voids forming behind the
walls, especially near the concrete-rock contact. Although
less frequently, some voids were also detected inside the
limestone layers at distances of 1 or 2 m from the concrete
wall. The amount of these events is remarkably higher
along the second segment of the tunnel, parallel to the
national road, indicating that this area is much more
deteriorated.
The GPR inspections performed on the apparently
undamaged segments of the tunnel floor validated thehypothesis that water erosion is particularly active below
the concrete paving. Where this paving has not collapsed
yet, the radar often detected water pools where the signal
propagates at lower velocity with reverberations (or
ringing). The results of the GPR investigations were re-
ported on a synthetic CAD map of the tunnel to facilitate
local authorities and engineers in defining the areas where
renovation works are required with higher priority.
Figure 9. Example of a wall profile: a) before migration, b) after migration. A long detachment of the concrete wall from
the rock is observed in the solid box. A strong reflection from a suspected cavity was also detected at a distance of about
180 cm (dash-dot box).
Figure 10. Example of a floor profile. Reflections from
water pools created by erosion below the concrete paving
were observed and are marked with solid boxes.
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The information gained by means of the GPRsurveys could also be employed in numerical simulations
to improve the knowledge on the state of stress of the
tunnel and to estimate the risk of collapse. This approach
would allow producing a risk erosion map, which may be
an additional tool for evaluating tunnel safety.
Acknowledgements
The authors are grateful to Alberto Bonaldi, Alessia
Thevenet and Eva Zattera that were part of the GPR team
during the acquisition days. The GPR equipment was kindly
supplied by IDS S.p.A.. The authors gratefully acknowledge
Dr. Dale Rucker for the extensive recommendations andcomments which have contributed to making this manuscript
acceptable for publication.
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