——
igation will
R-B. Int. J.
r Data
579-1581.
APRS, Vol.
requency
Mapping,
‘RS-1
RS, Vol.28,
edings of
Juerg Lichtenegger
A NEAR-REAL TIME OIL SLICK MONITORING DEMONSTRATOR FOR THE MEDITERRANFAN
Juerg LICHTENEGGER, Gianna CALABRESI, ESA/ESRIN, Frascati Italy
Andrea PETROCCHI, Vitrociset, Rome, Italy
Working Group IV/2
KEY WORDS: ERS, Radar, Image Processing, Hazard, Real-time
ABSTRACT
A demonstration service has been set up which provides near-real time information on oil slicks in support
of national coast guards surveillance. From a 2-year continuous monitoring of busy ship route locations in
the Mediterranean, it has been found that every fifth ERS-SAR image contains at least one man-made slick
of several kilometers length. At night, the percentage of images showing slicks, increases to about 22%.
Due to the many features visible on SAR images from sea areas the correct attribution of dark patches to
oil slicks is not easy and needs considerable experience. Useful assistance is provided by semi-automatic
image processing tools, those, based on neural network techniques, assess the probability of an operator-
proposed object to be an oil slick.
1 INTRODUCTION
Coastal and sea surface monitoring at large scale is performed generally by air. However, as a complement
to airborne surveys, spaceborne imaging radar has already been proofed to be cost-effective for providing
a much-enlarged coverage in time and space.
Such combined surveillance is successfully applied in northern European waters and more recently has
also been tested in the Mediterranean basin, mainly along the coasts of Italy, France, Spain and Greece. In
this region only a few countries, aside of institutional anti-pollution preparedness, have implemented a
monitoring system. This is due to primarily not affordable costs but also due to other priorities.
With the willingness to pursue rigorous enforcement of international and national laws and regulations as
a deterrent towards polluters, frequent sea area surveillance can be achieved using such an integrated
airborne-spaceborne surveillance system. This approach could well be also the basis of a collection of
statistic information on the status of pollution in relevant areas of special interest (touristic sites, protected
areas, etc.).
With regard to the Mediterranean it also has to be considered a closed sea area with reduced exchange of
water and therefore highly vulnerable. For this reason International law do not tolerated any pollution,
neither as river discharge nor from ships, while elsewhere in open ocean waters ship waste disposal is
regulated. Our preliminary experience as well other works confirm that the Mediterranean is pollution-wise
probably one of the worst treated area in the world, and in places comparable to the heavily polluted
waters of the Caspian Sea, the Black Sea and certain areas in Southeast Asia (Gadimova 2000). In all those
areas international solidarity needs urgently to be developed, and as first concerted action at least a
satellite monitoring service to be install. It can be expected that only based on reality, i.e. by demonstrating
the horrendous level of daily pollution through a data base of mapped oil slicks, a political awareness can
be developed.
The presented paper aims to give an overview of the experiences made in setting up an oil spill monitoring
demonstrator for the Mediterranean. It also reports on contacts with coast guards and on the difficulty to
communicate with operational entities. It finally reports on the results achieved by a cautious acceptance
of satellite technology. It has to be stated already at this point that today the aim of running an integrated
service is still not reached, but the achievements so-far are encouraging to continue the work.
International Archives of Photogrammetry and Remote Sensing. Vol. XXXIII, Part Bl. Amsterdam 2000. 193