APPLICATION OF TERRASAR-X DATA TO THE MONITORING OF URBAN SUBSIDENCE
IN THE CITY OF MURCIA
Daniel Monells
(1)
, Giuseppe Centolanza
(1)
, Jordi J. Mallorqui
(1)
, Sergi Duque
(1)
, Paco López-Dekker
(1,4)
,
Roberto Tomás
(2)
, Gerardo Herrera
(3)
, Juan M. López-Sánchez
(2)
, Fernando Vicente
(2)
,
Victor D. Navarro-Sanchez
(2)
, Joaquín Mulas
(3)
(1) Remote Sensing Lab.-UPC, Spain; (2) Universidad de Alicante (UA), Spain; (3) Instituto Geológico
y Minero (IGME), Spain; (4) DLR, Germany
ABSTRACT
This paper presents an analysis of the performance of
TerraSAR-X for subsidence monitoring in urban areas. The
city of Murcia has been selected as a test-site due to its high
deformation rate and the set of extensometers deployed
along the city that provide validation data. The obtained
results have been compared with those ob-tained from
ERS/ENVISAT data belonging to the same period and
validated with the in-situ measurements.
Index Terms— Differential, Interferometry,
Subsidence, Monitoring
1. INTRODUCTION
Orbital DInSAR is a technique widely used to survey the
surface of the Earth and monitor hazards due to natural and
human agents, such as earthquakes or mining [1][2][3].
Nowadays, there are a large number of satellites in orbit
carrying SAR instruments able to perform this monitoring.
In this work we will make a comparison of the results of
urban subsidence moni-toring obtained using data from
veteran satellites ERS-2 and ENVISAT and the new satellite
TerraSAR-X. The objective of the paper is to compare the
performance of each system under different aspects, such as
the management and detection of different kinds of targets
(distributed or deterministic), the preservation of the
coherence/phase stability and its temporal evolution, and a
comparison of the de-formation results using each set of
data.
This work has been supported by the Spanish MICINN and European
Union FEDER funds under project TEC2008-06764-C02. The TerraSAR-X
images were provided by DLR in the framework of the scientific project
GEO0389. ERS and ENVISAT data were provided by ESA in the
framework of the CAT1 1 project 2494. The Cartographical Service of
Murcia (CARTOMUR) has provided the DEM and orto-images used in this
work.
2. THE COHERENT PIXELS TECHNIQUE (CPT)
The Coherent Pixels Technique has been widely used for
monitoring urban subsidence [3]. The algorithm can use
both coherence and amplitude stability criteria to perform
pixels selection. The former is more suited for detecting
stable distributed targets and the latter for detecting the so-
called Permanent Scatterers (PS). The retrieval of the
deformation time-series is done in two steps. Firstly, a linear
model adjustment to data provides the linear velocity of
deformation, the DEM error and the azimuth position of the
PS (only for amplitude-based processing when large
Dopplers are present). Secondly, the non-linear processing
retrieves the non-linear deformation and the atmospheric
phase screen for each image.
3. THE CITY OF MURCIA TEST-SITE
Subsidence has occurred in the metropolitan area of Murcia
City (SE Spain) as a result of soil consolidation due to
piezometric level depletion caused by excessive pumping of
groundwater. The study area is part of Segura River valley
located in the oriental sector of the Betic Cordillera.
Permian and Triassic deformed materials corresponding to
the Internal Zones of the Betic Cordillera make up the
basement. The basin filling comprises Upper Miocene to
Quaternary sediment fluvial deposits. Younger sediments
are highly compressible and the most problematic from a
geotechnical point of view [4]. They constitute an aquifer
system that is divided in two units. The superficial aquifer
reaches 30 meters below the surface, and it is formed by
recent clay, silt and sands facies. The deep aquifer, located
below, is composed of a sequence of gravels and sands
alternating with confined silt and clay layers. Subsidence is
triggered by the excessive water pumping of the first layer
of deep aquifer. In fact a piezometric level decline between
5 and 15 m was measured on this layer during recent
drought periods: 1980–1983, 1993–1995 and 2005–2008.
After the second drought period, ground subsidence was
triggered causing damages in buildings and other structures
with an estimated cost of 50 million Euros, generating a
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