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16.1
INTRODUCTION
16.1.1
Background
Each year between 450 and 600 notifications concerning
acute oil and chemical discharges are reported to the Norwegian authorities.
Main sources for discharges are the offshore petroleum industry, ships and
industry on land. The total length of the Norwegian coastline (including
islands) is 83 000 km. High concentrations of environmentally sensitive areas
such as bird nesting islands and fjords, different climatic zones and poor
infrastructure pose great challenges for the national acute pollution
contingency. The population of
16.1.2
General description of national organisation and legislation
The national responsibility for dealing with acute
pollution on Norwegian territory, in the territorial sea and at
The enforcement of the Act and regulations is from 1st
January 2003 the responsibility of the Norwegian Coastal Administration, Kystverket,
through the Department for Emergency Response.
16.2
NATIONAL ORGANISATION AND RESPONSIBILITIES
16.2.1
Decision making levels and information flow
The command system is represented by the following
levels:
The Minister of Fisheries
The Director General of Kystverket.
The Deputy Director of The Department for
Emergency Response.
The officer on duty (24h).
When the national contingency system is in operation,
the Deputy Director of the Department for Emergency Response will act as the
response commander.
16.2.2
National organisation and tasks
The Department for Emergency Response has the following
responsibilities:
·
National response authority against major acute
pollution.
All private industry is required to establish and
maintain its own acute pollution contingency. In addition, about 70 private
enterprises have received dedicated contingency requirements. In
There are 34 intermunicipal contingency regions (IUA)
covering both coastal and inland areas. Acute pollution caused by "normal
activity" within a municipality is the responsibility of the IUA.
The governmental at sea contingency (Kystverket and
Coast Guard resources) is responsible for responding to spills not covered by
private and municipal contingency. Private and municipal contingency
organisations are obliged to provide assistance to the governmental contingency.
16.2.3
Strategy for combating at sea
In general, mechanical recovery of oil pollution has
first priority. Chemical response (dispersants) is considered an important
supplement. If net environmental benefit analysis (NEBA) identifies dispersants
as the preferred method, chemical response may take position as the first
priority response method for dedicated areas and spill scenarios.
16.2.4
Strategy for combating on-shore
The main criteria for selection of on-shore response
methods are the environmental impact, i.e. restitution
period for critical habitats or populations. The possible negative effect of
the response method itself is part of the strategy. Hence, monitoring and
attenuation (natural degradation) may be selected if this represents an
acceptable restitution period.
16.2.5
National resources
In
80 000 metres of harbour booms.
22 000 metres of coastal booms.
30 000 metres of ocean booms.
430 oil recovery devices.
6 Coast Guard vessels with on-board recovery
equipment
4 Oil Recovery vessels belonging to Kystverket.
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