84
Le Lann - Chemical dispersion as an oil pollution response - French approach
be sufficient to generate dispersion of the oil, while the efficiency of the mechanical recovery
would be maximal.
Once all these points examined, if the decision to use chemical dispersants is taken, then
one must proceed to implementation.
Implementation of the decision, availability of qualified dispersants and spraying plat
forms
Once the decision to treat an oil slick with chemical dispersants has been made, it is neces
sary to proceed quickly with the implementation of the decision, because the time slot during
which hydrocarbons can be chemically dispersed is limited. In addition, as time elapses,
even while remaining within the time slot, the efficiency of chemical dispersion decreases.
For an effective action, it is essential to have a quick access to qualified chemical disper
sants from stockpiles and to the platforms for spraying the product, whether ships or aircraft.
This can be achieved by implementing dispersant stockpiles at national level and by equip
ping ships for the application of dispersants. Fitting aircraft for this purpose is not impossible
but is much more complicated because of aeronautical constraints.
Another solution is to rely, via partnership agreements or trade agreements, on structures
able to provide the service very quickly. The British company OSRL offers this type of service
and can provide equipped aircraft and dispersants from its own stocks within 24 hours from
initial call. The European Maritime Safety Agency is currently setting up a dispersant spray
ing capability on its oil spill response stand-by vessels. It seems to be currently studying the
possibility to set up chemical dispersant stockpiles to be made available to Member States in
case of necessity. A consultation was launched recently for the procurement of chemical
dispersants by the Agency.
Conclusion
The process used in France for the selection of qualified chemical dispersants and for mak
ing decision on the operational use of dispersants can inspire processes in other countries.
The first point is to define the criteria for qualification of products for use in areas under na
tional jurisdiction. To do this, it is necessary to select an efficiency test from the existing ones
and set the efficiency threshold beyond which the dispersant would be acceptable. An ac
ceptable level of toxicity shall also be defined and the corresponding test shall be selected,
keeping in mind that the OSPAR tests have a wide international recognition. Once some dis
persants have been qualified, it is necessary either to constitute a national stockpile or to
implement any other solution that would enable use of the products from a partner’s stock.
The difficulty of conducting a full cost - benefit analysis in real time during an accident makes
it necessary to define a simple process for decision making in emergency situations. The
principle to keep in mind is that this process shall ensure that hydrocarbon concentration in
the water column remains below a value for which no significant and lasting toxicity to marine
species is observed. A concentration of 10 ppm seems to be reasonable. Any solution meet
ing this basic requirement and relying only on readily available data for decision making is
acceptable.
Finally, it is important to consider the implementation phase of pollution response through the
use of chemical dispersants. It is necessary to provide quick and easy access to platforms
for the application of dispersants on oil spills at sea. Public service vessels may be fairly
simply equipped, but if product spraying from aircraft is necessary, it seems preferable to rely
on a service provider.