in a Very High Resolution (VHR) image. Then a
scale invariant feature transform in conjunction with
a hierarchical discriminant regression tree was
employed to detect the airport area. Aytekin et al.
(2013) used a texture-based runway detection
algorithm that uses the Adaboost machine learning
package for identifying 32x32 pixel image tiles as
runway or non-runway. Second, for automatically
monitoring the airport changes, Digital Change
Detection algorithms that provide binary land cover
“change/no-change” information, can be used
(Jensen, 2015). In fact, by automatically detecting
the spatial regions within a bi-temporal image pair
where meaningful change is likely to have occurred,
a human operator (or another process) can then
analyse the changes using his/her knowledge.
ESA’s Sentinel missions are providing us with
reliable and timely open data on land, ocean and
atmosphere with high spatial and temporal
resolutions for state-of-the-art research activities and
services, e.g., natural resources management and
urban land cover mapping (Malenovský et al.,
2012). In this context, synergetic use of Sentinel 1/2
data has been used for urban land cover mapping
and change detection (Ban et al., 2017; Haas and
Ban, 2017). Although the potential of Sentinel 1/2
data has been highlighted in the above works, the
effective use of this data in the context of mapping
and monitoring airports need to be assessed.
This study aims to confirm the needs and verify
how Earth Observation satellites, in particular the
latest Sentinels satellites, can be used to assure the
best up-to-date outdoor mapping for an initial target
of 200 world airports. The work assesses the
temporal and spatial suitability of Sentinels (or other
EO data) and defines a service chain design for
airport mapping and monitoring changes.
2 EO DATA AVAILABILTY
The first step of the analysis was to confirm the
temporal availability of EO data at a global scale, by
defining a timeframe for validation on a set of
worldwide airports.
The selected timeframe was the latest two
months before the study started, from 1st December
2016 to 31st January 2017, while nine airports were
chosen, representative of different geographical
regions from USA, Europe and Asia.
During this period, two Sentinel-1 (S1) and one
Sentinel-2 (S2) were operational. The Sentinel-1
(synthetic-aperture radar) was operating with S1A
and S1B satellites, while the Sentinel-2
(multispectral) had only the S2A satellite active
(S2B was launched just on 7 March 2017).
The data procurement results of Sentinel-1 (S1) and
Sentinel-2 (S2) on these airports are presented in the
table.
Table 1: Sentinels data availability.
Sentinel-2 Sentinel-1
Europe
Lisbon
S2A 2016-12-19
2017-01-19 (S1A
IW VV-VH)
München
None (dense cloud
coverage)
2017-01-25 (S1A
IW VV- VH)
Istanbul
S2A 2017-02-02
2017-01-14 (S1A
IW VV-VH)
Malaga *
S2A 2016-12-20
2014-11-27 (S1A
SM HH-HV)
USA
Atlanta
S2A 2016-11-28
2017-01-06 (S1A
IW VV-VH)
NYC/JFK
S2A 2016-12-04
2017-01-12 (S1A
IW VV-VH)
Miami
S2A 2017-01-06
2017-01-01 (S1A
IW VV-VH)
Asia
Ben Gurion
S2A 2017-02-10
2017-01-04 (S1A
IW_ VV-VH)
AbuDhabi
S2A 2016-12-25
2017-01-07 (S1A
IW_VV)
Shanghai
S2A 2017-01-29
20170122 (S1A IW
VV-VH)
S2A has visible data from almost all airports,
including the 4 relevant bands for this study with 10
m spatial resolution: B2, B3, B4 and B8.
Figure 2: S2A True colour composition.
S1A and S1B were also capturing data in all
airports but using different modes. The main
operational mode for land is Interferometric Wide
(IW) High Resolution, typically using single or dual
polarization, with a spatial resolution up to 25 m.
The best resolution mode is Stripmap (SM) Full
Resolution, with a spatial resolution up to 10 m, that
is used only on request, typically on extraordinary
events, such as emergency management. Both
acquisition modes are available in the SLC product
format, needed for interferometry applications, and
GRD product format that is geo-referenced from
SLC.