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OMV BEREDSKAPSPLANLEGGING BJØRNØYA
Generic Oil Spill Response
Plan for Bear Island OMV Norge AS
Report No.: 16, Rev. 0
Document No.: 1GN3V3I-44
Date: 2015-03-30
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page i
Project name: OMV Beredskapsplanlegging Bjørnøya DNV GL AS DNV GL Oil & Gas
BDL Environmental Risk
Management
P.O.Box 300
1322 Høvik
Norway
Tel: +47 67 57 99 00
NO 945 748 931 MVA
Report title: Generic Oil Spill Response Plan for Bear Island
Customer: OMV Norge AS, Postboks 130
4065 STAVANGER
Norway
Contact person: Sønnøve McIvor
Date of issue: 2015-03-25
Project No.: PP109700
Organisation unit: BDL Environmental Risk Management
Report No.: 16, Rev 0
Document No.: 1GN3V3I-44
Applicable contract(s) governing the provision of this Report:
Objective:
Generic Oil Spill Response Plan for Bear Island
Copyright © DNV GL 2014. All rights reserved. This publication or parts thereof may not be copied, reproduced or transmitted in any
form, or by any means, whether digitally or otherwise without the prior written consent of DNV GL. DNV GL and the Horizon Graphic
are trademarks of DNV GL AS. The content of this publication shall be kept confidential by the customer, unless otherwise agreed in writing. Reference to part of this publication which may lead to misinterpretation is prohibited.
DNV GL Distribution: Keywords:
☒ Unrestricted distribution (internal and external) [Keywords]
☐ Unrestricted distribution within DNV GL
☐ Limited distribution within DNV GL after 3 years
☐ No distribution (confidential)
☐ Secret
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page ii
Table of contents
1. EXECUTIVE SUMMARY ..................................................................................................... 4
2. DEFINITIONS AND ABREVATIONS ..................................................................................... 5
3. INTRODUCTION .............................................................................................................. 6
3.1 Background 6
3.2 Plan Objective 7
3.3 Sources 7
3.4 Disclaimer 7
4. SCOPE OF THE GENERIC PREPAREDNESS PLAN .................................................................. 8
4.1 Activity 8
4.2 Geographical extent of the plan 9
5. OPERATIONAL CONDITIONS .......................................................................................... 10
5.1 General description 10
5.2 Climate 10
5.3 Flora and fauna 11
5.3.1 PRIMOS 11
5.3.2 Havmiljø.no 12
5.4 Near-shore and shoreline conditions 13
5.4.1 Tides and currents 13
5.4.2 Accessibility 13
5.4.3 South and East Coast 13
5.4.4 Northern Coast 14
5.4.5 Ice conditions 15
6. PREPAREDNESS SOLUTIONS .......................................................................................... 17
6.1 Organisation and responsibilities 17
6.1.1 The Governor of Svalbard 17
6.1.2 Response organization 17
6.2 Response strategies 18
6.2.1 Outer limitations for Oil Spill Response 19
6.3 Remote sensing 22
6.3.1 General description 22
6.3.2 Potential challenges 22
6.3.3 Current Technologies 22
6.3.4 Related technologies; integrated systems, modelling and forecasting 22
6.3.5 Applicability of remote sensing technologies 23
6.4 Mechanical recovery 24
6.4.1 General description 24
6.4.2 Operating conditions and solutions 24
6.5 Dispersant application 25
6.5.1 General description 25
6.5.2 Operating conditions and solutions 25
6.6 In Situ burning 26
6.6.1 General description 26
6.6.2 Operating conditions and solutions 26
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page iii
6.7 Feasibility of offshore response tactics at Bear Island 28
6.8 Near-shore and shoreline response 31
6.8.1 General description 31
6.8.2 Operational challenges 31
6.8.3 Near-shore/shoreline concept for Bear Island 32
6.8.4 Clean-up endpoints 33
6.9 Response strategies in ice 34
6.9.1 Behaviour of oil in water and ice 34
6.9.2 Operational Challenges 35
6.9.3 Response strategies for the marginal ice zone at Bear Island 36
6.10 Logistics and support 38
6.10.1 General description 38
6.10.2 Key planning issues 38
7. GENERIC OPERATION PLAN (ORDER) BEAR ISLAND .......................................................... 39
7.1 SITUATION 39
7.2 MISSION 40
7.3 EXECUTION 41
7.4 ADMINISTRATION AND LOGISTICS 42
7.5 COMMAND AND SIGNALS 42
8. CONCLUSION AND RECOMMONDATIONS ......................................................................... 43
9. REFERENCES ................................................................................................................ 44
10. APPENDIX .................................................................................................................... 45
10.1 SHORELINE ASSESSMENTS (FROM FIELD SURVEY REPORT)............................................... 46
10.2 ACUTE STRATEGY OIL SPILL RESPONSE (ASO) ................................................................. 92
10.3 RESPONSE RESOURCES (2014) ...................................................................................... 94
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 4
1. EXECUTIVE SUMMARY
This report has been prepared for OMV Norge in order to increase the understanding of potential oil
spill operations at Bear Island by describing operational challenges, site specific issues and other
relevant issues. The plan has been prepared based on a field survey and workshops with experts
and stakeholders, in addition to the use of statistical data of operating conditions. The plan
discusses relevant oil spill strategies and evaluates feasibility of response tactics for Bear Island.
In later years the areas for exploration drilling in the Barents Sea has gradually expanded
northwards. In the announced 23 licensing round, new blocks closer to Bear Island are opened to
applications for exploration activity.
This Generic plan does not relate to a specific future activity level, but is a contribution to the
process of preparing for a future increase in petroleum activities in the vicinity of Bear Island. The
plan is not related to specific oil spill scenarios. Subsequently the plan does not address
dimensioning of oil spill preparedness in the area – this should be addressed through activity
specific contingency analysis and preparedness planning.
Bear Island is the southernmost island of the Norwegian Svalbard archipelago and is located
approximately halfway between Spitsbergen and the North Cape. The plan lists the environmental
and operating conditions that must be taken in to account for oil spill response planning. Some of
the issues that are special for the area are:
No gradual coastal zone separating the open ocean from the shoreline
Limited shoreline access points
Lack of infrastructure (e.g. roads, harbors)
Seasonal sea ice encapsulating the island
As a consequence special considerations should be made when defining requirements for barrier
functions and barrier elements during oil spill analysis and planning processes at Bear Island -
especially with regards to coast and shoreline response measures where response units must be
established without IUA resources. For open water response the plan show that local response
conditions provide relatively broad windows of opportunities for both mechanical recovery as well
as dispersant application year round. In Situ Burning (ISB) may also be applicable – especially in
ice, but its feasibility is likely to be limited by oil weathering due to expected high drift times.
An oil spill response at Bear Island can be executed by the same principal organizational structure
as elsewhere. Logistics is an issue since all resources in an oil spill response must be mobilized and
transported in to the area. The plan concludes that the main delivery chain could be established
from Hammerfest. However, the facilities at the metrological station can represent an important
role especially with regards to use of helicopter. The plan shows that significant amounts of
response resources exist as well as vessels to operate it, but supplements are required for ISB kits.
Practical experience is limited so emphasis should be put on training, exercises and system
verification.
Relevant parts of this generic plan can be adapted and implemented in activity specific spill
contingency planning, and also be used as an input for longer term development. The plan can also
be used as a reference in dialog with authorities and other stakeholders.
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 5
2. DEFINITIONS AND ABREVATIONS Definitions
Action plan The operator's plan and strategy to combat acute pollution
Combating All actions implemented to recover the oil and prevent damage
Influence area The area with greater than or equal to 5 % probability of oil pollution by more than 1 ton of oil within a 10x10 km square, according to oil drift modelling.
IG Kyst Task force for near shore containment and recovery operations
IG Strand Akutt Task force for shoreline containment and recovery operations – mobile oil
IG Strand Task force for shoreline cleaning – stranded oil
NOFO system Includes 1 Transrec skimmer, 400 m offshore boom, 1 oil spill contingency vessel (NOFO-class) and 1 tug vessel.
Oil spill recovery Mitigating measures in the first phase to prevent the spreading of oil and to prevent the oil to reach the shoreline.
Response time Mobilization time added transport time to site.
Abbreviations
ALARP As low as reasonable practicable
ASO Acute Strategy Oil Spill
COP Common Operation Picture
DNV GL Det Norske Veritas GL
FLIR Forward Looking Infra-Red camera
GPR Ground Penetrating Radar
IR Infra-Red (infrarød)
HSE Health, Safety and Environment
IUA
Municipality organisation against acute pollution recovery actions (“Interkommunalt utvalg mot akutt forurensning“)
ISB In Situ Burning
JIP Joint Industri Project
KSAT Kongsberg Satellite Services
NCA The Norwegian Coastal Administration (www.kystverket.no) (“Kystverket”).
NOFO Norwegian Clean Seas Association for operating companies (www.nofo.no)
(“Norsk Oljevernforening For Operatørselskaper”).
NEBA Net Environmental Benefit Analysis
NOROG Norwegian Oil and Gas Assosiation
OR Oil Recovery
OPL Operation Manager
OSPR Oil Spill Preparedness and Response
OSRL Oil Spill Response Limited
PL Production Licence
PRIMOS Priority environmental areas on Svalbard
PTIL Petroleum Safety Authority
PSA Petroleum Safety Authority (www.ptil.no). “Petroleumstilsynet” - PTIL
SCAT Shoreline Cleanup Assessment Technique
SLAR Side Looking Airborne Radar (oil detection radar in aeroplanes)
UV Ultra Violet
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 6
3. INTRODUCTION
3.1 Background
This document – Generic Oil Spill Response Plan for Bear Island – has been prepared by DNV GL on
the initiative of OMV Norge AS. The plan addresses oil spill response in general at Bear Island
(Norwegian: “Bjørnøya”), and discusses the applicability of different response strategies and
measures in relation to local conditions and other relevant factors.
Although the statistical risk for major oil spills from petroleum exploration is small, it cannot be
completely eliminated. As Bear Island is the only land mass between the Norwegian mainland and
the Svalbard archipelago, it requires special considerations for oil spill response. In the announced
23. licensing round, new blocks closer to Bear Island is opened to applications for exploration
activity. OMV Norge AS has thus initiated the work with this plan as a proactive and collaborative
measure in the process of preparing for an expected future increase in petroleum activities in the
area.
The preparation of the plan has included:
A field survey to Bear Island including initial workshops in August 2014
A workshop in November 2014
In the field survey the shoreline and near-shore waters of Bear Island was evaluated with regards
to feasible oil spill response tactics (DNV GL 2014-a). The survey also encompassed initial
workshops with the companies OMV, Statoil, Eni Norge, Lundin, Tullow, NOFO and The Norwegian
Polar Institute, addressing key issues for the work. The workshop in October included additional
participants and followed up the survey report with focus on barrier strategies, operational
concepts and experience exchange.
Figure 3-1 Field survey August 2014 (Photo: DNV GL)
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 7
3.2 Plan Objective
The objectives of the Generic oil spill preparedness plan for Bear Island are to:
Describe operational challenges and site specific issues in the area
Discuss relevant adaptions to the barrier model specific for Bear Island
Describe relevant oil spill strategies and evaluate feasibility of response tactics
Describe local rules, roles and organizational entities that are relevant
Give an example of a tentative tactical plan
Provide relevant information from shoreline assessments
3.3 Sources
The source material used for the development of the plan comes from 3 main sources:
The field survey, including workshops – August 2014 (DNV GL 2014b)
The works shop in November 2014The report “Challenges and best practices of oil spill
response in the Arctic” (DNV GL 2014a).
For further reading and detailed references it is advised to read these reports.
Special thanks go to The Norwegian Polar Institute, The Norwegian Coastal Administration and the
Meteorological Institute who has contributed kindly with their specific expertise in the project.
3.4 Disclaimer
The Generic Oil Spill Response Plan for Bear Island is not a part of any operating company´s
activity specific oil spill preparedness plan, unless the company clearly specifies this in an adequate
way.
The plan discusses and suggests response tactics that could be feasible or not, depending on
activity specific factors such as spill scenario, oil types, discharge volume, time of year etc. These
factors should also be evaluated if the plan should be incorporated in activity specific preparedness
plans.
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 8
4. SCOPE OF THE GENERIC PREPAREDNESS PLAN
4.1 Activity
In recent years the areas for exploration drilling in the Barents Sea has gradually expanded
northwards. With the settlement of the Norwegian-Russian border in 2010, eastern areas are now
also included in this petroleum region.
Bear Island is located just within the northern limit of the currently opened areas, at latitude 74.5 °
N. Some exploration wells, including OMVs current activity in PL 537 Wisting, have already taken
place in its relative proximity. The Wisting area is situated approximately 184 km south east of
Bear Island. The Apollo prospect, drilled in 2014 by Statoil, was approximately 9 km closer. Results
of oil drift modeling from these activities have indicated that oil spills from blow-out scenarios in
certain circumstances can reach Bear Island.
In the announced 23 licensing round, new blocks closer to Bear Island are opened to applications
for exploration activity (Figure 4-1). If these are realized, it is likely that probabilities for simulated
dimensioning oil spills to encounter the island will increase. Subsequently the relevance of
adequate oil spill response measures will also be higher. Hence this plan does not relate to a
specific future activity level, but is a contribution to the process of preparing for a future increase
in petroleum activities in the vicinity of Bear Island.
Figure 4-1 Barents Sea - announced blocks 23. licensing round
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 9
4.2 Geographical extent of the plan
The geographical extent for the Generic Oil Spill Response Plan for Bear Island has for practical
reasons been delimited to the zone from land and 12 nm or 22.2 km into the ocean. The outer
boundary thus equals the border of the Bear Island natural reserve (Figure 4-2). This is a suitable
approach for the purpose of this plan since the reserve regulations as well as the local fauna
represents important considerations in a potential oil spill response. Conversely the plan has no
formal implications to the nature reserve.
Figure 4-2 Geographical extent of the plan
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 10
5. OPERATIONAL CONDITIONS
5.1 General description
Bear Island is located at 74.30° N and 19.01°
E, 235 kilometres south of
mainland Spitsbergen and 397 kilometres
NNW of Ingøy in mainland Norway
(Figure 5-1). The island has a mostly flat
landmass that covers 176 km2. The
mountainous part of the island is in the south
where the highest point reaches 536 m
(Misery-mountain). The islands coastline is
generally steep and exposed, and offer very
few sheltered landing spots.
Bear Island is uninhabited except for a small
group of 9 working permanently at the
island's meteorological station Herwighamna
in the North. In the summerseason scientists
and tourists also visit the island.
Bear Island was discovered by the Dutch
explorer Willem Barents in 1596. The island
was considered unknown until
the Spitsbergen Treaty of 1920 placed it
under Norwegian sovereignty.
5.2 Climate
Being in the arctic, the mean temperature at the island is higher than what could be expected for
the lat/long. The warmest month (August) has an average temperature of 4.4° C and -7.4° C for
the coldest month (January). This is caused by the polar front that often surrounds the island on
the eastern, southern and western side. This also causes rapid changes in the weather and the
area is prone to fog and polar lows (Oct – May). Polar lows are notorious with their rapid
appearance, intense winds and heavy snow showers (Figure 5-2). Fog occurs frequently during the
summer months.
Figure 5-1 Location of Bear Island
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 11
Figure 5-2 Polar lows (L) surrounding Bear Island (www.barentswatch.no)
5.3 Flora and fauna
Bear Island has some of the largest bird colonies in the world, and it was declared a nature
reserve in 2002. Especially in the summer season the island is very rich in seabirds that nest on
the southern cliffs. Breeding populations include northern fulmars (50,000–60,000 pairs), purple
sandpipers, red phalaropes (10 pairs), glaucous gulls (2000 pairs), black-legged
kittiwakes(100,000 pairs), little auks (10,000–100,000 pairs), common guillemots (50,000
pairs), thick-billed guillemots (190,000 individuals) and black guillemots (1000 pairs). Other
species also visit the island during their seasonal migration between Svalbard's northern islands
and mainland Europe, such as pink-footed geese (30,000 individuals), barnacle geese andlong-
tailed ducks. The only land birds are snow buntings and rock ptarmigans.
Despite its name, Bear Island is not a permanent residence of polar bears, although many arrive
with the expanding pack ice in the winter. Occasionally, a bear will stay behind when the ice
retreats in spring and remain through the summer months. Ringed seal and bearded seal, prey of
the polar bear, live in the waters near Bear Island, but the formerly common walrus has nowadays
become a rare guest. Bear Island's freshwater lakes are home to a population of arctic char. The
only indigenous land mammals are a few arctic foxes. There is little plant growth, consisting mostly
of moss and some scurvy grass, but no trees.
5.3.1 PRIMOS
Priority environmental areas on Svalbard (PRIMOS) contain data sets with the most valuable and
vulnerable sites along the coast of Bear Island, and how these are prioritized on the basis of an
assessment of vulnerability to oil and other acute pollution. The data established by the Norwegian
Polar Institute and is accessible on line through NCAs map portal Kystinfo
(http://kart.kystverket.no/). An example showing bird colonies at Bear Island ois presented in
figure Figure 5-3.
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 12
Figure 5-3 Bird colonies at Bear Island (PRIMOS/Kystinfo)
5.3.2 Havmiljø.no
In 2012 the web portal Havmiljø.no was established by the Norwegian Environmental Directorate in
cooperation with several others. Havmiljø.no is used to assess whether specific human activities in
particular areas should be banned or can be accommodated to the ecological properties of the
areas. It gives useful background information when conditions are to be set for human activity. The
service contains maps showing how environmental vulnerability for acute oil pollution is distributed
in Norwegian waters and how it varies from month to month. An example is presented in
Figure 5-4.
Figure 5-4 Environmental vulnerability for acute oil pollution in April. Bear Island
approximately in center (Example-map Havmiljø.no).
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 13
5.4 Near-shore and shoreline conditions
5.4.1 Tides and currents
In the Barents Sea one part of the Gulf Stream and the Norwegian Current sets eastwards along
the Norwegian coast, while another part sets northward and pass west of Bear Island at a distance
of 30-40 nautical miles with a speed of about 0.7 knots. Locally the tide differs significantly around
the island. Tidal differences in the south (Sørhamna) are about 1.2 meters, and 2.2 meters in the
north (Herwig Hamna). High/low tide in the south occurs about 40 minutes earlier than in the north.
Tidal currents chase around the island with extraordinarily strength which in particular places can
result in difficult sea states that can be quite dangerous for smaller vessels. This occurs in
particular around the southern tip of the island (Sørhamna-Sylen), at Framnes and by Cape Dunera,
where it runs with a speed of approx. 3 knots.
The currents around Bear Island may be noticeable a significant way off the coast and is probably
the reason for many reports about unexpected breaking waves. With rising tide the current flows
northwards on the east and west coast, while running westwards on the north coast. After high tide
the current weakens, and for about 1/2 hour it can stand still. With falling tide the current reverses.
Because of the many small bays in the coastline, strong eddies forms close to shore, especially on
the east and north coast.
5.4.2 Accessibility
The waterdepth around the island are generally quite well maped out on the outside of the 20 m
baseline, and smaller vessels that hold more than 1 nautical mil of land will be able to navigate
safely. In the south the waters are deep close to land, exept from a shallow area 12 meters off the
southern tip of the island. The rest of the coast is relatively shallow and variable with submerged
rocks within 2-400 m from the shoreline.
The shoreline mostly consists of vertical cliff walls (brinks) directly from the ocean and to the island
plateau. In several sections the walls are overhanging. Below the cliffs there are sections of narrow
and rocky beach brims. Only at a few locations these brinks are gentler slopes which allows for
access on foot from the beach and up on the island. In general there are very few bays that can
provide good and predictable landing conditions, and the island has no fully protected harbours.
During storms vessels generally must search to the island's leeward side to anchor behind
headlands or in the small bays that exist.
Water can be filled from most rivers along the coast of Bear Island, but in summer they dry up
except Russelva (Lognvika), the English River (Austervåg) and Lakselva (North Hamna).
5.4.3 South and East Coast
The waters around the southern tip of Bear Island are generally deep, but have neither ports nor
landing sites. Strong vertical winds occurs along the cliffs, and under the melting season in the
spring and summer there are constant landslides and rock falls from the cliffs which makes it
dangerous to travel close to shore by boat.
There are powerful tidal races around the south tip and in storms it can develop into massive
waves and overfalls. Vessels should keep a good distance from shore during such conditions. The
best harbors on the east coast are Sørhamna, Whaleross Bay and Austervåg. Sørhamna is a large,
open bay surrounded by up to 100m high brinks. This is the only natural harbor-site considered to
be accessible for larger sized vessels (large fishing boats, coast guard etc.). The harbor provides
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 14
shelter for winds from the north, but during gale from the south the seas at the bay inlet can be
massive with violent currents. In the far end of the Sørhamna bay there is a small sandy beach
that allows for landing. With some difficulty, it is possible to climb from here and up on the brink.
The section between Cape Levin and Fram headland to the Cape Nordenskjøld provides the easiest
point of access up on the island from this side. There is however no usable anchoring points, partly
because of the strong currents and shallow waters. The reef off Cape Nordenskiöld extends quite
far out and with some wind violent seas can occur even far offshore.
5.4.4 Northern Coast
The northern coast of the island has generally the best landing sites and is relatively easily
accessible. The most commonly used anchor spots are Herwig Hamna, North Hamna and Kobbe
bay. In Herwighavna, there is a meteorological station which is manned throughout the year
(Figure 5-5).
The station has a crew of nine; a leader, meteorological staff of five, one technician, and two cooks.
In addition to meteorological observations, the station performs measurements for several
scientific institutions. The island is extremely important as a landing and bunkering space for
helicopters. Without bunkering here, no helicopter traffic to and from Svalbard would have been
possible.
Figure 5-5 The Meteorology station (Photo: Kari Finnstad)
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 15
5.4.5 Ice conditions
Land fast ice settles every year in the bays around Bear Island, while in the surrounding ocean this
only happens very seldom and in particularly cold winters. This ice is not thick, and breaks up
easily with the swell.
The drift ice coming from the Barents Sea and the sea farther north with southwesterly currents,
also reaches Bear Island. The highest prevalence occurs by wind directions between North and East,
while winds from the opposite direction normally keep the waters free from drift ice. Figure 5-6
gives an example of the ice conditions early April 2008.
DNV GL has made maps of the average ice extension for the winter season based on daily satellite
data 2003 – 2013. The maps are presented in Figure 5-7. The maps also show the line for
maximum ice extent in the period from 1984 – 2013.
Figure 5-6 Ice Conditions at Bear Island April 2008 (Photos: DNV GL)
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 16
Figure 5-7 Ice extent in winter season
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 17
6. PREPAREDNESS SOLUTIONS
6.1 Organisation and responsibilities
Response to acute pollution to the sea at Bear Island follows the same legislative framework and
regulations as the rest of the Norwegian Continental Shelf. The Norwegian Coastal Administration
(NCA) is the lead governmental agency in case of acute pollution. In case of a discharge from
petroleum activities, NCA will supervise the response of the responsible party and coordinate with
other authorities. In case of a discharge from ships, NCA will normally serve directly as Action
Manager for the oil spill response.
The Operating Company is the responsible party in acute pollution from petroleum activity.is The
Operating Company is obliged to respond to acute pollution according to their established
preparedness plans, and to notify and inform the NCA continuously throughout the duration of the
response.
6.1.1 The Governor of Svalbard
The Governor of Svalbard (No: “Sysselmannen på Svalbard”) represents the
Norwegian government in exercising its sovereignty over the Svalbard archipelago (Spitsbergen),
including Bear Island. The position reports to the Norwegian Ministry of Justice, but it maintains all
Norwegian interests in the area, including environmental protection.
According to the Svalbard Environmental Protection Act § 70, the Governor of Svalbard shall be
notified directly by the responsible party in case of acute pollution, or the risk of such. In addition
the Governor of Svalbard manages nature reserves and national parks in Svalbard in line with
protection regulations. This includes the nature reserve at Bear Island.
6.1.2 Response organization
For offshore petroleum activity in Norway, emergency response operations including oil spill
response towards acute pollution follows a standardized organizational structure. The operating
company has the overall responsibility throughout all phases of the incident, including notification,
mobilization, response and normalization – including contact with the authorities and public
relations. The command of the total operation lies with the operating company´s Incident
Commander (No: “Aksjonsleder”), based on the Incident Action Plan.
The practical execution of an oil spill response is managed by the Operation Manager (No:
“Operasjonsleder/OPL”) and his organization on command from the Incident Commander. The
position as Operation Manager is delegated to NOFO which is a professional oil spill response
organization based on the membership of all operating companies on the NCA.
The Operational Manager has professional staffs that comprises of three branches/sections
corresponding to the main principles of the Incident Command System (Figure 6-1):
Planning and environment Section responsible for the collection, evaluation, and
display of incident information, maintaining status of resources, and preparing the
Incident Action Plan and incident-related documentation.
Logistics Section responsible for providing adequate services, material and support to
meet all incident needs. This includes incident-related costs, personnel, and equipment
records, and administering procurement contracts associated with the incident or event.
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 18
Operations Section responsible for directing the tactical actions to meet incident
objectives.
Figure 6-1 Incident Command structure NCA
The Operations Section comprises of tactical response units under the command of one or several
on scene Commander (s) (No: Innsatsleder) depending on the situation and the Incident Action
Plan. For shoreline response operations, the on scene Command is normally (by the mainland)
delegated from NOFO to the Inter-Municipal Responders (IUA´s), based on contracts. At Bear
Island no corresponding response units to the IUA´s exist, hence adequate response units, if
needed, will be organized directly by NOFO in cooperation with the Operating Company.
6.2 Response strategies
Oil Spill Response can in principle be defined as a set of consequence reducing barriers, which aim
to stop or reduce negative effects of acute pollution to the environment. The Offshore Industry in
Norway has developed common barrier strategies accompanied by a set of minimum requirements
(NOROG 2013) for this purpose. These include:
Barrier 1a: Combat of oil offshore, near the source of the spill
Barrier 1b: Combat of oil offshore, downstream from the source of the spill
Barrier 2: Combat of oil in the coastal and near shore zone
Barrier 3a: Combat of mobile oil by the shoreline
Barrier 3b: Shoreline cleaning
Due to the local conditions at Bear Island outlined in chapter 5, it is required to assess alternative
approaches to one or several of the response/barrier strategies listed above. An overview of
relevant barrier strategies, functions, elements and requirements for oil spill response at Bear
Island is listed in Table 6-1 and Table 6-2. The separate tactics are then discussed in chapter 6.3 –
6.10. A quantitative feasibility assessment for the main offshore tactics for conditions at Bear
Island is presented in chapter6.7.
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 19
6.2.1 Outer limitations for Oil Spill Response
Oil spill response in a marine environment is by its nature a complex undertaking. There are
normally three main factors that may limit the overall effectiveness of active response tactics,
regardless of the barrier strategies and elements in place. These are:
Responder safety is always the no. 1 priority and should never be compromised even
if it leads to a delays or abruption in the response.
Low encounter rates for response systems due to fast spreading of the oil on the sea
surface or in the water column that makes effective treatment difficult
Operating limitations for response technology due to high winds, high waves, strong
current, sea ice etc. Here a distinction should be made between operating conditions
that limit the response but enhance natural degredation of oil (such as high wind and
waves), and conditions that only limits the execution of the response.
These factors represent to a various degree the outer limitations for oil spill response, and should
not be confused with limitations due to inadequate equipment, lack of planning, training etc. which
to a large degree can be eliminated or mitigated by proper planning and preparations.
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Table 6-1 the barrier principles applied to Bear Island conditions (Open water)
Barrier strategies
Barrier functions Barrier elements Functional requirements Considerations
Subsea Well Incident
Intervention (All conditions)
Reduce spill by source control Capping system Subsea dispersants
Contracted availability Logistical solution/plan
Competence and training
Water depth Volatile oil/gas at sea surface
Combat of oil –
open ocean (Ice free
conditions)
Reduce spreading of spill by
containment and recovery of combatable oil on sea surface
NOFO offshore system,
conventional boom NOFO offshore system,
active boom
Cold weather functionality
Rapid deployment and uploading Containment capacity with heating
Oil properties
Operational conditions/limitations One vessel systems
Reduce spreading of oil on sea surface by use of chemical dispersants
Vessel based dispersant system
Helicopter based dispersant system
Fix-wing based dispersant
system
Plan for field resupply of dispersants to vessels
Competence and training Response time
Oil properties Operational conditions/limitations Increased volume of dispersants on
vessels Stockpile of dispersants at the
meteorological station at Bear
Island
Reduce spreading of spill by containment and In situ burning (ISB) on sea surface
ISB system/kit onboard offshore response vessel (fire booms, igniters)
Response time Training and competence System adapted to relevant vessels
Oil properties Hazards Operational conditions/limitations
ISB system/kit must be fitted to offshore response vessel
Permission application regime
Combat of oil – near shore and shoreline
(Ice free conditions)
Protect sensitive areas and combat oil in shoreline areas where wave flushing is unlikely
due to shoreline topography
Regular Near Shore task forces, e.g. :
o “IG Kyst”
o “IG Strand akutt” o “IG Strand”
Not applicable at Bear Island
Multipurpose response vessel with:
o Ribs/skiffs
o Storage capacity o Vacuum technology o Sorbent application o ISB
Contracted availability Response time Competence and training
Local knowledge Capacity and sustainability Safety Treatment of Oiled Wildlife Staging and lodging on keel
Oil properties Hazards Operational conditions/limitations
Home port/mobilization point by mainland
Back up the concept with infrastructure and resources on land at Bear Island
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Table 6-2 the barrier principles applied to Bear Island conditions (Ice infested waters and additional conditions)
Barrier strategies
Barrier functions Barrier elements Functional requirements Considerations
Combat of oil – ice infested
waters
Concentrate efforts upstream towards the spill source and in
ice free conditions, to avoid/reduce oil entering ice infested waters
Relevant offshore elements listed above
Applicability of existing concepts
Combat oil near or in ice infested waters
Relevant offshore elements listed above with adapted
tactics to ice: o Crane and grab o Feasible skimmers o Dispersant
application with added energy
o ISB
Feasible vessels for ice Cold weather functionality
Competence and training
Apply best practice Oil properties
Additional strategies - all barriers
Surveillance and monitoring Multiple sensors from o Satellites o Aerial (fix wing) o Helicopter with
Down link
o Drones o Vessels o Ocean eye
Key functionality Response time Sustainability/robustness Interactivity
Coverage Data communication capacity
Response capability Common Operation Picture (COP)
Logistics
Operational stamina
Competence and training Applicability of existing concepts
Post-response assessments Procedures Experts
Contracted availability Response time
Applicability of existing concepts
No combat of oil Natural dispersion, wave flushing and degradation of oil in open ocean and at exposed shorelines
Surveillance and monitoring NEBA Feasible tactic if natural degradation processes are more effective than other tactics
May also be only feasible tactic due to personnel safety
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6.3 Remote sensing
6.3.1 General description
Remote sensing of oil spills includes detection, monitoring and tracking of oil. By the use of sensors,
oil can to various degrees be detected on the water surface, under the ice, within the ice sheet, or
on top of the ice. The sensors can be mounted on a variety of platforms such as satellites, aircrafts,
helicopters, autonomous underwater vehicles, etc.
Remote sensing is generally required for an effective oil spill response. Information about location
and spreading of the oils provide key input for choosing appropriate response tactics, both for
combatting and protective measures. The ability to forecast oil movement is equally important, as
it makes it possible for the responder to plan ahead and adapt the response objectives and tactics
to the expected conditions ahead in time.
6.3.2 Potential challenges
High north the capability to perform remote sensing generally becomes increasingly important due
to general remoteness/limited access and restricted visibility due to fog, precipitation, snow drift
and seasonal lack of daylight. The presence of ice also inflicts on remote sensing, and may both
facilitate and complicate the tasks of monitoring, detecting, and tracking of oil. Practical experience
from remote sensing in ice is limited, but in general broken ice slows down the spreading of oil on
the sea surface, which makes the location and movements of the oil more predictable compared to
in open water. This may reduce the need for e.g. frequent observations. If oil is located under ice
or snow, it will generally be more challenging to identify the oil from remote sensing.
6.3.3 Current Technologies
The main types of remote sensing platforms are:
Satellite platforms which are widely used for general remote sensing, and are also
applicable to oil spill purposes. Sensors may include high-resolution optical imagers and
synthetic aperture radar. The advantages of using satellites include wide area coverage,
and when combined with radar imagery, it is also independent from cloud cover, fog or
darkness. Satellite technology is considered most efficient in lower ice concentrations.
Airborne Platforms. Norway and other European countries have sophisticated
surveillance aircrafts to search for pollution from oil spills. These aircrafts normally
have very large operational range and carry a suite of sensors that complement each
other to differentiate thin from thick slicks, identify oil type and operate in conditions of
low visibility.
Surface Platforms systems refers to systems that may be deployed either from the sea
surface by vessel, or from the surface of the ice. Sensors may vary from low-cost, non-
cooled, hand-held IR systems, to Ground Penetrating Radar (GPR). GPR have also been
tested successfully from aircraft platforms.
6.3.4 Related technologies; integrated systems, modelling and forecasting
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Tracking and forecasting the position of spilled oil, based on integrating remote sensing information,
environmental data, and numerical modeling will provide important information in planning and
execution of the response. Several technologies aim to provide integration of information from
multiple sensors combined with advanced navigation and plotting technologies.
6.3.5 Applicability of remote sensing technologies
Table 6-3 summarizes the general strengths and weaknesses of different technologies evaluated in
relation to the changing operating environments, scenarios and potential challenges for remote
sensing of oil spills in arctic conditions.
The light green color indicates that the technology is proven and fully validated, and that its
performance and limitations are well understood. The dark blue color indicates that the technology
is potentially applicable and that partial validation may have taken place, but the technology has
not been comprehensively validated for performance under the given scenario. The white color
indicates that the likely performance of the technology is unknown, as it has never been tested
under the given scenario. The light red color indicates that the technology is not applicable to the
given scenario.
Table 6-3 remote sensing technology evaluation
Expected Detection Performance
Technology
Among Pack Ice
On ice
Under Ice/Snow or
encapsulated
Low visibility
Ice concentration
<30% 30-
60% >60%
Blowing
snow Darkness
Rain or
fog
Optical sensors
(Cameras,
multi/hyper spectral
sensors, UV
sensors)
Active
Systems
Thermal and
infrared sensors
Microwave
radiometers
Radar sensors (SLAR/SAR systems,
marine radar)
Ground-penetrating
radar
Fluorosensors
Tunable Diode Laser
Systems
Laser-ultrasonic
system
LIDAR
Acoustic sensors
Dogs
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6.4 Mechanical recovery
6.4.1 General description
Mechanical recovery is the most widely used spill response tactic in Norway. The equivalent term
“containment and recovery” indicates the two main processes involved. Before the oil can be
effectively removed from the water surface, normally with a skimming device, it must first be
collected and concentrated. In open water this is usually done by use of containment booms. The
recovered oil must then be stored in a tank, barge or bladder and transported out of the area for
appropriate waste management.
Figure 6-2 Open-ocean mechanical recovery system
The basic challenge when trying to contain and recover a large oil spill from a marine environment
is that the oil generally spreads out very quickly and form thin and broken slicks on the surface of
the water, and substantial parts of large spills are therefore likely to escape from containment and
recovery.
6.4.2 Operating conditions and solutions
Wind, sea state and current
Combinations of these factors have major impacts on the spreading of oil, which in itself is the key
challenge in containment and recovery. The effectiveness of mechanical recovery systems is also
relatively sensitive to wind and sea states. High sea states may also be considered beneficial in
terms of removing oil from the sea surface. Thus, the upper wave limits for boom performance are
not necessarily a “response failure”. The main mechanical recovery systems used by the Norwegian
Clean Seas Association (NOFO) is designed for use in offshore conditions up to 4 meter significant
wave heights. The system consists of a supply ship/oil recovery (OR) vessel, a smaller tug vessel,
400 meter boom with 800-1200 mm freeboard, a high capacity skimmer and storage capacity of
minimum 1500 m3.
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Another limitation of the conventional containment booms is that they can only be towed very
slowly without loss of oil (0.5 – 1 knots), making them stationary and vulnerable to currents. Boom
systems that can operate at higher towing speeds or in currents exists for coastal waters, and
promising new concepts are also being developed for offshore conditions. This is beneficial as
higher towing speed will increase potential encounter rates significantly, as well as reducing the
loss of oil from the boom in situations with strong currents.
Low temperatures
When air temperatures drop below the freezing point, several operational and technical challenges
occur. There is a potential for icing on vessels and recovery equipment due to water splash, fog or
precipitation. The general operation of equipment becomes more difficult and skimmers and pumps
may freeze. The oil viscosity will also increase which makes it more difficult to handle, including
storage and transfer. Winterization of both vessels and oil spill equipment is therefore important in
arctic conditions. NOFO has a requirement with regards to functionality in low temperatures for
booms and skimmers (-20o C for the Transrec Skimmer and -30oC for the boom).
Sea Ice
Sea Ice may occur at Bear Island during winter and spring season. A conventional booming
strategy will be most effective in open water and in ice concentrations up to 10 %, but could also
be performed with some effectiveness in concentrations up to 30 % especially by deflecting the ice
with active ice management. A single vessel recovery skimming systems with short sections of
boom attached to the sweep arms could maneuver between large ice floes and operate in higher
ice concentrations than conventional boom. The ice concentration will also influence operation of
the skimmers. The most challenging conditions for skimmer operations are the presence of small
ice floes and pieces of ice combined with slush ice. It is also necessary to deal with low
temperatures, and the skimmers should therefore be protected and/or heated to avoid freezing.
6.5 Dispersant application
6.5.1 General description
The use of chemical dispersants is a response technique which does not remove the oil from the
water, but enhance the natural dispersion of oil by applying chemicals that dilute the oil in the
water column. Dispersants are usually sprayed or applied onto oil slicks from vessels or aircrafts.
They are applied using spray nozzles, pumps and hoses. Dispersants operations are usually
monitored from aircraft to make sure that the application is on target. The window-of-opportunity
for dispersants depends on oil characteristics and weathering.
6.5.2 Operating conditions and solutions
Dispersant use can be an effective oil spill response option for many oil spill scenarios, but several
considerations have to be made before dispersion is used.
Wind, sea state and current
Waves are the driving force for the dispersion of dispersant-treated oil spills. Even a small vertical
advection within the water column is sufficient to maintain the oil droplets in the water column and
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prevent the oil droplets from resurfacing. This process of natural dispersion can be enhanced by
the adding of dispersants.
High waves and winds are thus favorable for the dispersion of oil in water; however they can pose
safety risks for crew and equipment. Strong winds make it difficult to accurately spray dispersants
and aerial spraying and monitoring operations may include safety risks. Vessel based application is
mainly limited by high sea states. Very low sea states result in reduced mixing energy. If
dispersants are sprayed onto oil spill from a vessel, mixing energy can be added by the use of the
vessel’s propellers or the use of high pressure water systems.
Low temperatures and ice
Low temperatures do not inhibit dispersants effectiveness directly; however they increase the
viscosity of the oil which limits effective dispersion. Dispersants remain effective for most non
emulsified oils as long as the oil viscosity does not exceed 20,000cP and the pour point of the oil is
lower than the ambient water temperatures. Protective measures such as heating of the dispersant
application system may be required to avoid frezzing of the dispersiant fluid.
Visibility
Low visibility will restricts the use of dispersants as it does for any of the other response techniques
described earlier. Aerial application of dispersants requires good visibility and dispersants cannot be
applied during darkness.
6.6 In Situ burning
6.6.1 General description
In-situ burning (ISB) is the term used for controlled burning of oil directly on the water surface or
in broken ice. In order to burn oil spilled on water, three elements must be present: fuel, oxygen
and a source of ignition. The oil must be heated to a temperature at which sufficient hydrocarbons
are vaporized to support combustion in the air above the slick. The rule of thumb for minimum
ignitable thickness for relative calm conditions is minimum 1 mm for fresh crude oil and 3-5 mm
for diesel fuels and non emulsified crude.
ISB is usually performed by the use of fireproof booms to contain a portion of the spilled oil
followed by ignition by releasing a burning, gelled fuel from a helicopter or from a vessel. The oil
might also be encircled by a stationary fire boom or within ice edges. Once the oil is ignited, most
of the oil will burn off the surface of the water or ice, but some nonvolatile compounds will remain.
These residues may float or sink, depending on the oil type and burn conditions. In comparison
with e.g. mechanical recovery, the technical and logistical complexity of ISB is significantly lower.
6.6.2 Operating conditions and solutions
Wind, sea state and current
ISB in open water with the use of fireproof booms and towing vessels face challenges due to strong
winds, high waves and currents. A special challenge for ISB is a successful ignition of the oil under
high wind conditions. Wind driven, short-period waves and currents can lead to reduction of flame
spreading due to reduced film thickness and blending of cold, underlying oil. The maximum wind
speed for successful ignition of large burns has been determined to be 10-12 m/s. Weak winds (as
little as 2 m/s) and currents can have the advantage that they can hold a slick against a barrier,
such as the ice edge or a towed boom, thus thickening the oil for burning.
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Due to the weight of materials used for fireproof booms, the weight per unit is generally much
higher than for conventional booms, and the design is normally also stiffer. This results in lower
wave thresholds.
Low temperatures
Low temperatures could make the ignition of the oil difficult and oil may burn more slowly and less
completely.
Sea Ice
ISB can be performed in various ice conditions, and as long as the oil slick is thick enough to be
ignited, there are no limitations on ice coverage and ice type. The window of opportunity is
generally extended for spills in ice affected conditions, compared with open water, due to
decreased oil spreading and lower rates of emulsification.
In open water to approximately 30 – 40 % ice coverage the oil’s spread and movement will not be
greatly affected by the presence of ice and open water ISB techniques may be possible to
implement.
Figure 6-3 In-situ burning test conducted within the JIP Oil in Ice (Photo: SINTEF).
In 30 to 70 % ice coverage, the ice will reduce the spreading and movement of the slick, but not
completely containing the oil. Deployment and operation of booms in these ice concentrations are
difficult or not possible. In pack ice (70 – 90 % ice coverage) ice floes can contain the oil and slicks
are often thick enough to be ignited.
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Visibility
Low visibility (due to fog, ceiling, precipitation, or darkness) generally impacts ISB for safety
reasons. The ability to operate vessels, aircrafts, or other equipment needed to sustain operations
and position is crucial and if visibility is too low operations have to be stopped.
Logistics & HSE
Main challenges for ISB in ice are general logistical issues e.g. accessibility to the oil, operation and
maneuverability within ice which requires successful ice-management. Also the use of a helitorch
igniter system is regarded as a risk due to its flammability and a high risk for the pilots of the
aircraft. Oil spills in remote areas pose a severe problem as remote ignition systems which are
effective and safe are not in place yet.
Emulsification of oil
Emulsification of oil negatively affects in-situ ignition and burning, because of the water uptake.
Water content in oil emulsion are typically in the 60-80 % range. For weathered crude that has
formed a stable water-in-oil emulsion, the upper limit for successful ignition is about 25 % water.
The oil in the emulsion cannot reach a temperature higher than 100 °C until the water is either
boiled off or removed. A two-step process may be applied to burn emulsions: "Breaking" of the
emulsion, and boiling off the water (by the heat of the igniter) to form a layer of non emulsified oil
floating on top of the emulsion slick; and subsequent combustion of this layer. Emulsion breakers,
chemicals commonly used in the oil industry may also be applied. Compared to non emulsified
slicks, emulsions are much more difficult to ignite, and once ignited, display reduced flame
spreading and more sensitivity to wind and wave action. For stable emulsions, the burn rate
declines significantly with increasing water content.
Burn residue
Scientific studies have confirmed that burn residues that remain after in-situ burning are less toxic
than the original oil. Burn residues can still have an ecological impact and removal should be
considered.
6.7 Feasibility of offshore response tactics at Bear Island
As discussed in the sections above there are multiple factors that may affect the overall feasibility
of the main offshore response tactics. In order to study and visualize the effects of the dominating
local seasonal and environmental factors, a feasibility study has been conducted based on a
response gap analysis for the Barents Sea and adjacent areas (DNV GL 2014). The Response Gap
Analysis provides information on to what extent the environmental conditions (wind, temperature,
sea state, ice, visibility, and darkness) pose limitations to mechanical recovery, in-situ burning and
the use of dispersants. 10 years of environmental data were used to eliminate yearly variations of
the datasets (e.g. ice concentrations) and to get the best possible statistical picture.
A response gap of e.g. 65 % means that on 65 out of 100 days no response could be conducted
and no oil would be recovered due to environmental conditions. During the other 35 days there will
be a window of opportunity to carry out response operations. The window of opportunity is further
defined as either favorable or impaired response conditions. It is emphasized that the window of
opportunity does not necessarily equal effective response.
The result is presented in Table 6-4. The results show significant differences over the year. In
summer (July) there is no statistical response gap for offshore response at Bear Island, and the
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dominating response condition is favorable for both mechanical recovery and dispersant from
vessels and aircraft. In fall and spring the maximum statistical response gap is 3 % for vessel
dispersant application, and 6 % for mechanical recovery. In the middle of winter the conditions are
most challenging with no favorable conditions, but the window of opportunity is still 86 % for
dispersant application (14 % response gap) and 68 % for mechanical recovery (32 % response
gap). Dispersant application from aircraft is calculated to 100 % favorable in summertime and 100 %
ineffective in winter. The response gap in winter is related to darkness during the polar night.
Contained in situ burning (with use of fire boom) shows a relative significant response gap
throughout the year. This is mainly due to lower wave thresholds for fire booms than for
conventional booms, and reflects the exposed open ocean conditions at Bear Island.
The overall picture indicates that oil spill response conditions at Bear Island does not differ
significantly from the situation further south in the Barents Sea. Oil spill response will to a large
degree be feasible, but challenging conditions are likely – especially in fall, winter and spring
seasons.
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Table 6-4 Feasibility of offshore response tactics at Bear Island in relation to environmental conditions (Position: Lat. 74.300854, long. 19.319448).
Month
Containment and recovery
Dispersant application
Contained
In situ burning
From ship
From air*
January
April
July
October
Expected monthly response conditions for defined offshore OSPR tactics at Bear Island (% of time). Green = response conditions are favorable. Yellow = Response conditions are impaired. Red = Response conditions are inefficient.
Response conditions are defined as;
Favorable when none of the environmental factors hinder or affect the response
Impaired when environmental factors affect or decrease the efficiency of the response
Ineffective when the response cannot be deployed or when the response efficiency is 0 % due to at least one environmental factor
*Dispersant application from airplanes is governed by aviation-regulations. During polar night (Nov. – Feb.) no flights can be expected due to safety restrictions.
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6.8 Near-shore and shoreline response
6.8.1 General description
Near-shore and shoreline response measures generally comprises of several techniques and
equipment types. For near shore response, mechanical recovery with lighter vessels, booms and
skimmers is normally preferred. For exposed shorelines with sufficient operational water-depths,
active offshore systems are preferable. Technology used for shoreline treatment is generally less
specialized than technologies used in open water. Many shoreline clean-up measures are
dominated by manual work and simple tools. The tactics that can be used to treat or clean
shorelines can be grouped into three response strategies:
Physical Removal:
o Manual collection and removal of oiled vegetation with shovels, rakes, buckets and
knifes.
o Flooding/flushing with water, pumps and hoses
o Passive sorbents such as bark or pit moss applied manually or with mechanical
application systems.
o Mechanical removal techniques with equipment designed for earth- and/or fluid
movement; caterpillars, excavators, high capacity vacuum technology etc.
In-Situ Treatment:
o Mechanical mixing of oiled sediments through agitation either in the absence of
water (“dry” mixing) or in water (“wet” mixing) to create a sediment-oil mixture
that increases weathering and reduces the potential for wildlife impacts
o Sediment transfer involving relocating oiled sediments to another location with
higher wave energy levels – “surf cleaning”
o Chemical or biological tactics that involve the addition of agents to facilitate
removal of oil or accelerate natural, in-situ oil degradation –bioremediation agents,
shoreline washing agents and shoreline dispersants. These are often used in
combination with other treatment methods and strategies.
Natural Recovery:
o Allowing shorelines to recover naturally is often the least damaging alternative for
light and moderate spills, particularly where access is limited or difficult.
6.8.2 Operational challenges
Accessibility and HSE
The shorelines of Bear Island have been field surveyed to assess applicable response options. The
results are presented in appendix 10.1.
The main identified challenges of near-shore and shoreline response at Bear Island are related to
the general lack of shoreline accessibility, and safety issues due to exposure from seaside,
exposure from rock fall, strong currents, and lack of detailed seabed mapping close to shore (see
chap 5). The risk of polar bears should neither be neglected even during the summer. In addition
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Bear Island offers no normal infrastructure to support a shoreline cleanup operation at any
significant size. The facilities at Herwighavna may to some degree be applicable, but the
accessibility to the small harbor is unpredictable due to sea and weather exposure.
In the winter and spring season the shorelines of Bear Island normally will be affected by sea ice
and icing – this can be local ice and/or drift ice from the north. The presence of ice around the
island will to a various degree protect the shoreline against stranding of oil, depending on the
situation. In conclusion a traditional approach to near-shore and shoreline response is not
applicable at Bear Island. As a consequence near-shore and shoreline tactics at Bear Island must
be tailored to fit the local conditions if they are to be implemented.
6.8.3 Near-shore/shoreline concept for Bear Island
As listed in table Table 6-1 a near-shore/shoreline response concept for ice free conditions should
be vessel based and basically self-contained. Key features and functionalities in the concept may
comprise of:
Multipurpose vessel(s) with:
o Staging and lodging of personnel and equipment on keel
o Deployable ribs/skiffs for rapid movement and shoreline access
o Oil radar and infrared sensors on support vessel, supplemented with Ocean Eye
o Portable pumps, skimmers and medium to light booms
o Storage capacity for recovered oil emulsion
o Vacuum technology including high capacity sorbent application/removal
o ISB kit
o Trained response unit/task force
Optional functionality can be Treatment of Oiled Wildlife.
The concept have similarities with the near shore and shoreline taskforces established in Finnmark
(“Innsatsgruppe Kyst” and “Innsatsgruppe Strand Akutt”) as a tactical response unit, but is more
compact and with a broader/multipurpose tool-box. A key issue is to replace traditional and labor
intensive methods with technological alternatives. There are several potential benefits with this,
but the most important incentive is to responder safety by reducing the use of manual work at the
every exposed shore at Bear Island.
Most of the relevant technologies for such a concept already exists and can be organized in an
appropriate design if necessary.
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Figure 6-4 Landing craft at Bear Island (Photo: DNV GL)
6.8.4 Clean-up endpoints
Shoreline clean-up should be based on assessments of the state of the pollution and the related
environmental damages and risks. Endpoints are the defined cleanup targets, and normally the
scale of which the completion of the clean-up is measured. Based on the defined end-points the
following conditions should lead to closure of clean-up operations:
There is no observed oil or the oiling condition is below the established endpoint(s); e.g.
treatment is not required, or:
The agreed endpoint(s) has been met by the treatment program.
Closure of clean-up operations can also result from the additional three conditions:
A safety issue(s) identified may present an unacceptable risk for responders that
cannot be mitigated.
No further treatment is recommended as an assessment of the net environmental
benefit (NEBA). Although the endpoint(s) has not been met, additional activities could
result in a negative effect(s) or could delay recovery.
A point is reached in the cleanup program referred to as low as reasonable practicable
(ALARP), a principle which means that further activity is feasible and practical, but has
little or no value as the risks associated with the remaining oil are tolerable.
At Bear Island all of these conditions are relevant and should be closely assessed.
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6.9 Response strategies in ice
Oil spill response in ice has been partially covered in previous chapters. In this section key
considerations that are relevant in the context of this plan are elaborated.
6.9.1 Behaviour of oil in water and ice
Fate and behaviour of oil spilled in ice
Arctic environmental conditions will influence an oil spill differently compared to in temperate
regions, particularly due to lower temperatures, presence of ice, and different light conditions.
Especially low temperatures and lack of waves due to ice lead to reduced oil spreading, evaporation,
emulsification and dispersion. Figure 6-5 shows the natural physical and chemical processes of oil
spilled in ice infested waters. During freezing, ice grows downwards encapsulating oil lying beneath
it. Once the oil becomes fixed within the ice, it moves only as the ice moves. Oil entrapped in ice is
thus difficult to track during the winter darkness. This results in a secondary discharge situation on
new and unexpected locations during the spring season.
Figure 6-5 Weathering processes of oil spilled in ice infested environments (Wilson et al.
1998)
In general spills under sea ice move with the ice. In winter, currents under the ice in most arctic
areas are insufficient to move spilled oil any significant distance from where it contacts the ice
undersurface. Spilled oil can be encapsulated in ice through the winter. Typically, the oil is re-
exposed in a fresh state. The main processes in open water vs. ectreme ice or cold are described in
Table 6-5.
Table 6-5 Effect of sea ice on main oil weathering processes
Process Open Water Extreme Cold or Ice
Spreading and
dispersion
A thick layer of oil grows
thinner and covers a larger
area of water (depending on
oil type)
Ice acts as a physical barrier (broken ice)
or retardant (grease ice); oil does not
spread or disperse as far and ends up in
a thicker layer
Drifting Oil moves with wind/current Oil will drift separately from the ice at
less than 30 % ice coverage, and with
the ice at 60 – 70 % (or greater)
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coverage. Unpredictable in broken ice
conditions.
Evaporation Relatively fast (thin oil films) Slower where oil spills are thickened
Emulsification Higher in areas with
breaking waves. Rate of
emulsification, total water
uptake, and stability of
emulsion depend on oil type.
Total water uptake and rate of uptake
may be lower as a result of reduced
wave activity because of the presence of
ice.
6.9.2 Operational Challenges
The precence of ice can pose a significant challenge when dealing with spilled oil in a marine
environment. Ice can make it more difficult to find a spill, reach it and deploy equipment and
personnel to respond. Despite this, there are also some conditions where low temperatures and ice
conditions may assist spill response. For example, ice can act as a natural barrier and prevent oil
from spreading. Cooler temperatures and waves dampened by the ice can also slow the weathering
process of oil. This can increase the window of opportumity for recovery, dispersants and in-situ
burning. The following sections list the main challenges and considerations for response strategies
in ice.
Ice can occur in several differents forms and stages, and will normally also occur in combination
with other factors that in sum may affect an oil spill response signifficantly. In general the marginal
ice zone is also a highly dynamic environment and significant changes of e.g. ice concentration can
occur over short periods of time. This means that oil spill operations in ice conditions in general will
have additional challenges compared to in open water. Even if response is possible, and there also
may be some benefits of the ice, the overall effectiveness is likely to be reduced. The main
operational benefits and challenges for oil spill response in ice is listet in Table 6-6.
Table 6-6 Impact on response techniques due to sea ice conditions
Remote Sensing Challenges: Can make remote sensing generally difficult, depending
on the location of the oil in the ice, and the local ice conditions e.g. ice
development stage, ice coverage, ice drift.
Mechanical Recovery Challenges: Reduced availibility to the oil. Ice may tear, lift or move
containment boom, reduced encounter rates for skimmers, clogging of
pumps, limited maneuverability, increased oil velocity, inability to
track and encounter oil
Benefits: Waves dampened by presence of ice
In Situ Burning Challenges: Slush ice may reduce burn effectiveness or impede
ignition, difficult to deploy fire boom and to track/recover burn residue
Benefits: Ice can contain oil/stop oil from spreading
Chemical Dispersants Challenges: Reduced encounter rates, no access of oil under ice,
reduced mixing energy availible
Benefits: Reduced weathering – dispersiability window prolonged
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6.9.3 Response strategies for the marginal ice zone at Bear Island
As presented in chapter 5.4.5 various amount of sea ice will normally occur at Bear Island during
the winter/spring season. In Table 6-2 response measures are further listed for ice infested waters
and additional conditions.
It should be emphasized that if an oil spill (relevant for this plan) was to encounter the sea ice in
this area, it would orginate from a distant source. The spill would thus have drifted on the open
ocean for several days. This influences the selection of the optimal response strategies. Firstly it
means that the primary strategy should be to concentrate efforts upstream towards the spill source
and in ice free conditions, to avoid/reduce oil entering ice infested waters. Secondly it would mean
that if oil ultimately encounters the marginal ice zone, it will be in a weathered state (not fresh oil).
This is likely to limit, depending on oil properties, the feasibility of In Situ Burning and also
dispersiant application (in the ice). The most applicable response measure would in such a case
most likely be mechanical recovery with or without containment booms (depending on ice
consentration). Mechanical Recovery in ice is therefore elaborated in the following.
Mechanical recovery of oil in ice
In open water booms are usually required to contain and thicken spills for mechanical recovery. A
conventional booming strategy is most effective in open water with ice concentrations below 30
percent, depending on the ice. Any mechanical recovery system working in ice-covered waters
needs to deflect the ice in order to gain access to the oil and effectively remove it. Single vessels
with over-the-side-skimming systems using short sections of boom can maneuver between large
ice floes and operate in higher ice concentrations than vessels towing independent booms
(Figure 6-6). As ice concentrations increase beyond 60 percent, ice can provide a natural barrier
for the spreading of oil. This natural containment can provide an advantage for recovery operations
in responding to small spills, using skimmers deployed directly from the side of a vessel.
Several types of skimmers can be applied for recovering oil in ice. The main types are listed below
in Table 6-7.
Table 6-7 Skimmer types and functionality
Skimmer type Description
Oleophilic Systems:
In oleophilic skimming systems, oil adheres to a drum,
belt, brush, disc or “mop” that is rotated at the water’s
surface. The oil is then scraped off into a storage chamber
or reservoir. These devices are efficient and it is common
for them to result in a high recovered oil-to-water ratio.
Light to medium-viscosity oils are most suited to these
systems though very high viscosity oils can be handled
using certain fittings.
Weir Skimmers:
A weir skimmer collects liquid at the surface of the water.
Round floats hold a collection bucket at a level that allows
oil to slip over the edge and into a collector. These units
are less efficient than oleophilic skimmers and collect a
significant amount of water with the oil, requiring
additional storage capacity. A benefit of weir skimmers,
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however, is their ability to handle both light and heavier
oil products.
Vacuum Skimmers:
These skimmers use vacuum to lift oil from the surface of
the water or the shore. Vacuum systems are versatile and
can be used on a variety of oil types, with the exception of
heavy oil and volatile products. A disadvantage is that
they can be inefficient, recovering more water than oil.
Mechanical Skimmers:
These systems physically lift oil from the surface and
include various mechanisms from conveyor belts to grab
buckets to contain it. These types of skimmers are more
suited to very viscous oils.
Figure 6-6 Oil skimming in ice (Photo: SINTEF)
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6.10 Logistics and support
6.10.1 General description
In any oil spill response operation of a certain proportion, logistics will be a major issue. This
reflects the fact that a response normally involves rapid mobilization of multiple types and
quantities of resources like e.g. ships, aircrafts, oil spill equipment and personnel to the spill site
and surrounding areas. As the response passes the initial phase, the need for support, resupply or
detachment will occur at some point. In total this calls for a wide range of assets and services,
such as:
Supply - Receive, store, issue, and resupply materiel for conducting operations;
Maintenance - Actions necessary to preserve, repair, and ensure continued operation
and effectiveness of recovery systems, components and task forces;
Transportation - The movement of units, personnel, equipment, and supplies from
the point of origin to the final destination;
Engineering - Provide damage repair and maintenance of facilities
HSE Services - Support the health and well-being of personnel; and
Other Services - Provide administrative and personnel support to keep response
organization fully operational. Includes internal and external communication systems.
To keep an oil spill response going for some time without unnecessary hesitations, delays or
malfunctions generally requires a highly skilled response organization as well as appropriate
preparations and plans.
6.10.2 Key planning issues
It is equidistant from Svalbard to Bjørnøya as from Finnmark to Bjørnøya. Based on the existing
activity distribution, depot structure etc. the main source of resources will be from the mainland.
Subsequently the main supply chains should be established from the south. Hammerfest is also the
closest NOFO base to Bear Island (Figure 6-7 Distances in the Barents Sea (PTIL).
Figure 6-7 Distances in the Barents Sea (PTIL)
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7. GENERIC OPERATION PLAN (ORDER) BEAR ISLAND
7.1 SITUATION
a. General description of the incident
An accident at the [ ] installation has led to acute discharge of oil. It is a risk that drifting oil slicks will
reach the coast and shoreline area around BJØRNØYA. The extent of the discharge is not yet clarified.
The oil drift modelling indicates a drift time to BJØRNØYA of around [ ] days.
b. Other units involved
Oil spill operations close to the installation is ongoing. Mobilization of relevant resources for oil spill
operations close to BJØRNØYA has started. A staging area is under establishment at POLARBASE in
HAMMERFEST where equipment and personnel can be received, organized, and prepared for deployment
to BJØRNØYA. The staging area will also be used for receiving of demobilized equipment and serve as a
waste storage location. A joint Oil spill organization will gradually be effective during the next days to
support the mobilization phase and to start further planning of the operations at BJØRNØYA.
c. The Incident Managers evaluation of the situation
Purpose:
The purpose of the operation in the coast and shoreline area around BJØRNØYA is to prevent damage to
environmental resources and the natural environment by combating oil spill in the coast and shoreline
area and if necessary register polluted beaches for further cleaning operations.
Action Manager overall priorities for the operation:
1 Safety of life and health
2 Natural Resources
3 Material and business interests
Methodology
The coast and shoreline operation around BJØRNØYA will be organized and executed by NOFO and its
contractual partners under the command of the responsible operator. The shoreline operations will be
executed with both offshore resources and by suitable landing craft vessels.
Desired End State of the operation
The end state of the operation is reached when the free floating oil spill is combated/under control and
polluted shorelines are registered for further cleaning operations.
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d. Organization
The personnel will be mobilized and organized in operative combat units by NOFO based on established
agreements.
e. Special considerations
Coordination and approval from the Governor of Svalbard regarding landing of equipment and
personnel in restricted areas on BJØRNØYA will be arranged through the action management
The shoreline operations will be executed from sea due to reduced accessibility from land. The
landing craft will serve as a support vessel for the operation.
The waters around BJRØNØYA is very challenging and it must be a continuous assessment in
relation to current, wind, waves and depth conditions with regards to HSE issues and type of
tactics and equipment.
7.2 MISSION
The operator has given the following mission to NOFO:
Prevent oil from reaching vulnerable environmental resources in the shoreline area of BJØRNØYA,
based on PRIMOS Svalbard
Operator
Action Manager
NOFO
Operational Manager
OSC Bjørnøya
Combat team 1 Combat team 2
Combat team 3 Combat team 4
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Prevent remobilization of stranded oil
Register polluted beaches
Managing collected oil emulsion and oil infested material according to given logistical guidelines
7.3 EXECUTION
a. Plan for the operation
Within the response time relevant equipment and trained personnel will be mobilized from NOFO and
NCA depots from the mainland and Svalbard and from other contractual partners through NOFO. A
staging area will be established at POLARBASE in HAMMERFEST where personnel and equipment will be
organized in an operativ unit. When this is finished the unit will be deployded to BJØRNØYA and execute
the operation according to the updated situation. The operation will be supproted continously by offshore
units from NOFO.
b. Order to Staging Area Responsible (from NOFO)
Finish the establishment of the staging area within 2 days from DTG [ ] (Date-Time Group)
Prepare for receiving equipment and personnel according to logistical plan.
Establish contact with NCA for coordination of equipment transfer to HAMMERFEST and from
SVALBARD to BJØRNØYA.
c. Order to On Scene Commander BJØRNØYA
Prepare the group for action and start deployment to BJØRNØYA within 4 days from DTG [ ].
At BJØRNØYA start combating of oil according to the updated situation.
Make use of ASO BJØRNØYA for input on tactical dispositions.
Coordinate the combating with offshore response units.
d. Coordinating instructions
HSE objectives: No accidents
HSE objective to be fulfilled through the following measures:
o Risk assessment of all working operations
o Safe Job Analysis
o Report of undesirable incidents
o Safety orientation of personnel
o Correct use of personal protection equipment
o Use of HSE-Data Sheet
o Communication
o First Aid Kit
Resting area for personnel is on the support vessel
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Recovered oil emulsion and oil polluted materials shall be stored on/at the support vessel
Polar Bear observation post must be established when working on shore.
Other: [ ]
7.4 ADMINISTRATION AND LOGISTICS
a. Oil Spill Equipment
See appendix 0
b. Waste management
All waste shall be stored on/at the supporting vessel. Further instructions to be clarified with
Operation Manager.
c. HSE
Execute Safe Job Analysis according to HSE regulations
Personal injury shall be notified to:
o Nearest leader who notify further according to procedure
Each unit is equipped with first aid kit.
Extra first aid equipment is available on board the support vessel
7.5 COMMAND AND SIGNALS
a. Signals
All units is equipped with VHF/INTERCOM radio and satellite communications equipment
b. Command
Incident Commander is localized in STAVANGER.
Operation Management is located in HAMERFEST
On Scene Commander is located on the supporting vessel
Place/time
Signature
Operation Manager
Distribution list primary addresses: Distribution list to orientation:
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8. CONCLUSION AND RECOMMONDATIONS
The purpose of the Generic Oil Spill Response plan for Bjørnøya has been to increase the understanding
of oil spill operations at Bear Island. The plan has been prepared through field survey and workshops
with experts and stakeholders, in addition to the use of statistical data of operating conditions. The plan
has revealed several useful findings and elements that will be relevant for detailed assessments and
development projects if future activity in the area will increase further.
As the plan reveals, the area at Bear Island differs in several ways from the coast at the main land. The
main differences are the remoteness in combination with lack of infrastructure and local resources, and
the extremely exposed and almost inaccessible shoreline. The island is also seasonally encountered by
drift ice. In the summer season Bear Island has one of Europe’s largest colonies of seabird, which make
it environmentally vulnerable towards oil spills. The combination of these factors creates challenges
compared to the established response strategies currently implemented at the mainland.
For open water response the plan show that local response conditions provide broad windows of
opportunities for both mechanical recovery as well as dispersant application year round. During mid-
winter the conditions may be very challenging, but a general response gap should not be expected. In
situ burning may represent a useful addition, but several limitations should be expected due to
weathering and emulsification of oil as well as limited wave limitations for fire booms. For remote
sensing the best available technologies will to a large extent be able to operate without major limitations,
except in situations with calm seas and low visibility such as in thick fog or heavy precipitation. Oil in
thick drift ice and/or covered in snow is also a challenge, but this scenario in not regarded as very likely
at Bear Island.
For near shore response there is a need for a more locally adapted response concept. The reason for this
is mainly that a traditional coast and shoreline response, including a high number of personnel and
labour intensive methods will not be feasible at Bear Island. The shorelines are simply too hazardous to
enter due to shallow water, extreme exposure from the ocean and due to risk of rock fall from the steep
cliffs above the shallow beach brims. A high degree of natural degradation of stranded oil must be
expected. In addition a compact and specialized response concept should be considered. This concept
could comprise of a multipurpose vessel with a shallow draft equipped with tools for mechanical recovery,
In situ burning kit, vacuum capability, and beach cleaning agents, flushing gear, sorbents and oil
detection /monitoring systems. The vessel should be self-contained and have a compact and professional
response units – like a task force.
An oil spill response at Bear Island can be executed by the same organizational structure and principles
as elsewhere, except for the shoreline operations because an IUA organisation is lacking. Logistics is an
issue since all resources in an oil spill response must be mobilized and transported into the area. The
plan concludes that the main delivery chain could be established from Hammerfest. The facilities at the
metrological station can however represent an important asset especially with regards to use of
helicopter. The plan shows that a lot of response equipment exists and also vessels to operate it, but
supplements are relevant for ISB kits. Practical experience is limited so emphasis should be put on
training, exercises and system verification.
Relevant parts of this generic plan can be adapted and implemented in activity specific spill contingency
planning, and also be used as an input for longer term planning. The plan can also be used as a
reference in dialog with authorities and other stakeholders.
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 44
9. REFERENCES
/1/ DNV GL 2014a: Challenges and best practices of oil spill response in the Arctic
/2/ DNV GL 2014b: Befaringsrapport fra tokt til Bjørnøya 10. – 15.8.14
/3/ NOROG 2013: Veiledning for miljørettede beredskapsanalyser
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10. APPENDIX
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10.1 SHORELINE ASSESSMENTS (FROM FIELD SURVEY
REPORT) Registreringsskjemaer for Bjørnøya inkluderer hele øya bortsett fra de områder som er merket med sort og grønt i Bilde 1 Registeringssoner Bjørnøya». Verneområdet (grønt) er veldokumentert, og var også et
område som ikke ble rekognosert på grunn av værbegrensninger. Området merket med sort er «Vesalstranda», dette utgjør foten av Misery fjellet, og er en høy og bratt klippevegg hvor oljevernberedskap blir svært vanskelig, og som også er et risikofylt område å bevege seg på land på grunn av rasfare. Sted/lokasjon i registreringsskjemaer informerer om hvilke registreringsrute det enkelte skjema omhandler. Foto fra sjø er bilder fra rekognoseringstoktet med MS Maursund (landgangsfartøy, også
referert til som LGF). Flyfoto er hentet fra Norsk Polarinstitutts (NP) kartdatabase for Svalbard
(http://toposvalbard.npolar.no/). Adkomstpunktene som det refereres til i skjemaene er hentet fra Norsk Polarinstitutts Svalbard kart «D20 Bjørnøya», 2012.
Bilde 1 Registeringssoner Bjørnøya (DNV GL).
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Sted/lokasjon
1. Fra Landnøringsvika til Parholmane
GPS Waypoint nr. 180
Strandtype Landnøringsvika: Blankskurte berg, noe rullestein. Rekved i bakkant hvor det er noe abrasjons-strand (strand som følge av erosjon).
Hamnevika: Som Landnørdingsvika, men litt større forekomst av rullesteiner i strandsonen. Noe erosjon i bakkant. Rekved. Skredneset: Preges av løsmasse erosjon.
Adkomst Hamnevika kan benyttes for i landsetting av personell, ikke mulig å legge til med større fartøy.
Dybdeforhold/strøm Det ble observert lite strøm innenfor oddene, dette var 1 time etter høyvann.
Hva skal beskyttes Hindre påslag av forurensning, særlig rullesteinområder vil være
vanskelig å rengjøre. Området ligger i umiddelbar nærhet til fuglefjell på sørspissen.
Spesielle forhold Det kan stedvis observeres rekved langt opp i ura i området.
Bilde 2 Landnørdingsvika (DNV GL).
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Bilde 3 Hamnevika (DNV GL).
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Bilde 4 Skredneset (DNV GL).
Bilde 5 Hamnevika og deler av Skredneset, rød sirkel merker mulighet for adkomst som er indikert i kart fra NP (Flyfoto: NP).
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Sted/lokasjon
2. Området mellom Kapp Kåre og Kapp Ruth
GPS Waypoint nr. 181
Strandtype Berg og lave klipper, strand innerst i Ærfuglvika. Kapp Ruth er en lav klippeplattform.
Adkomst Utløp til Benda er egnet for lettbåt. Mulig å gå i land med LGF i Ærfuglvika. Innseiling til vika er ca 60 m bred. Sørlig nord-vest vind vil være ugunstig hvis man ønsker å komme inn i Ærfuglvika.
Store huler i berg/klipper langs sjø ved Kvalkjeften og i Ærfuglvika. Forekomster av rekved.
Dybdeforhold/strøm I Ærfuglvika var det noe strøm som gikk i sørlig retning, men denne ble ikke karakterisert som spesielt sterk.
Hva skal beskyttes Strand innerst i Ærfuglvika.
Spesielle forhold Stort overheng i Ærfuglvika, fare for ras. Det bryter kraftig ved Kapp Ruth.
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Bilde 6 Utløp ved Benda, nært Kapp Kåre (flyfoto: NP).
Bilde 7 Kapp Maria lengst unna - har en karakteristisk hvelving/bro ytterst på neset (DNV GL).
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Bilde 8 Huler i Ærfuglvika (DNV GL).
Bilde 9 Ærfuglvika (flyfoto: NP).
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Bilde 10 MS Maursund i Ærfuglvika (DNV GL).
Bilde 11 Strand, Ærfuglvika (DNV GL).
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Sted/lokasjon
3. Kapp Ruth - Grunnbukta – Kapp Hanna
GPS Waypoint nr. 182
Strandtype Lav klippekyst/berg. Noen smale strender tett opp i klippevegger, rullestein og steinblokker i sjølinja enkelte steder.
Adkomst Kun mulig med lettbåt. Ingen adkomstmulighet fra land. LGF vil ikke ha mulighet til adkomst til land i området mellom Kapp Ruth og Kapp Hanna.
Dybdeforhold/strøm Området er preget av grunner – Grunnbukta. Strøm målt til 1,2 knop.
Hva skal beskyttes Strandsone
Spesielle forhold Grunner kan forårsake utfordringer ved bruk av lenser.
Bilde 12 Oversiktsbilde, Kapp Ruth (flyfoto: NP).
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Bilde 13 Grunnbukta, mot Kapp Ruth (DNV GL).
Bilde 14 Grunnbukta (DNV GL).
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Bilde 15 Deler av Grunnbukta (flyfoto: NP).
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Sted/lokasjon
4. Kapp Hanna – Kapp Elisabeth inkludert Langbukta
GPS Waypoint nr. 183
Strandtype Lav klippekyst med en erosjonsstripe (grov stein og sand) mot sjø. Flere små stapper langs land, spesielt ved Holmengrå.
Det er en del søppel (blåser mm) langt oppe i berg/klipper. Svært værutsatt.
Adkomst Det adkomstpunktet som er satt i Langbukta er ikke tilgjengelig for LGF. Kun tilgjengelig med lettbåt.
Dybdeforhold/strøm Det er mange skjær og grunner i bukta som ikke er avmerket på sjøkart.
Hva skal beskyttes
Spesielle forhold Mye overheng og fare for ras langs land.
Bilde 16 Adkomstpunkt ved Kapp Hanna, skvalpeskjær i sjø utenfor gjorde den utilgjengelig for LGF
(flyfoto: NP).
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Bilde 17 Stapper i sjø ved Holmengrå (flyfoto: NP).
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Bilde 18 Knorten (DNV GL).
Bilde 19 MS Maursund nært land, Knorten (DNV GL).
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Sted/lokasjon
5. Kapp Elisabeth – Grytvika (inkl. Kapp Dunèr)
GPS Waypoint nr. 184
Strandtype Vernevågen: Klipper, bratt og ufremkommelig.
Teltvika: Klipper, strand (abrasjons-plattform) innerst i vika. Mindre huler i strandsonen.
Adkomst Vernevågen: Svært begrenset adkomst med lettbåt, ingen adkomst fra land.
Teltvika: LGF kom 5-10 meter fra å kunne gå helt inntil land innerst i vika. Teltvika er godt egnet for bruk av lettbåt, gode ankringsmuligheter for større fartøy. Vika vil være vanskelig tilgjengelig dersom vind står fra nordvest eller sørøst.
Dybdeforhold/strøm «Straumsundet» utenfor Kapp Dunèr er strømutsatt, innerst i teltvika er strømmen svak og knapt merkbar.
Hva skal beskyttes Teltvika prioriteres.
Spesielle forhold Svært mye strøm utenfor Kapp Dunèr.
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Bilde 20 Kapp Elisabeth (flyfoto: NP).
Bilde 21 Vernevågen (flyfoto: NP).
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Bilde 22 Kapp Dunèr sett fra Teltvika (DNV GL).
Bilde 23 Teltvika, MS Maursund går så nært land som mulig (DNV GL).
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Bilde 24 Adkomstpunkter ved Kapp Dunèr, tilgjengelig for lettbåt (flyfoto: NP).
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Sted/lokasjon
6. Matholmane – Snyta (Amfiet og Drangane)
GPS Waypoint nr. 185
Strandtype Klipper, grov stein og mye huler i bergveggene. Grov strand med rekved og søppel ved Amfiet. Løsmassestrand ved Snyta.
Adkomst De avmerkede adkomstpunktene er kun egnet for innsetting av personell ved hjelp av lettbåt.
Dybdeforhold/strøm Lite strøm registret nært land.
Hva skal beskyttes Huler og steder som kan akkumulere forurensning. Området har mange huler og bratte klipper. «Amfi» er dannet av utløpet til en bekk, og danner beskrivende nok et stort naturlig amfi. Amfi ble
ikke observert å inneholde drivved og søppel.
Spesielle forhold Området er utfordrende hvis man oppholder seg i båt når vindretningen er nordøst til sørvest.
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Bilde 25 Adkomstpunkter ved Amfiet (flyfoto: NP).
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Bilde 26 Amfiet (DNV GL).
Bilde 27 Klippevegger nær Amfiet (DNV GL).
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Sted/lokasjon
7. Snyta – Emmaholmane (inkl. Kobbebukta)
GPS Waypoint nr. 186
Strandtype Flisa: Bratte klipper, berg. Kobbebukta: Sandstrand
Kobbebukta er den eneste sandstranden med betydelig utstrekning på nordsiden av Bjørnøya
Adkomst
Ikke mulig å komme til i Flisa-området, kanskje med lettbåt under svært
gunstige forhold.
Dybdeforhold/strøm Kobbebukta er svært langgrunn, og dermed blir det vanskelig å legge til med LGF, lett tilgjengelig med lettbåt.
Hva skal beskyttes Kobbebukta
Spesielle forhold Sterk strøm utenfor Snyta
Bilde 28 Del a Kobbebukta. Hele bukta er merket som mulig adkomstplass (flyfoto: NP).
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Bilde 29 Kobbebukta sett fra sjøsiden (DNV GL).
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Bilde 30 Emmaholmane, del av Kapp Kjellström og deler av Kobbebukta (strand). Hele bukta er merket
som mulig adkomstpunkt (flyfoto: NP).
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Sted/lokasjon
8. Kapp Kjellstrøm – Gravodden (Nordhamna og Kvalrossfjæra)
GPS Waypoint nr. 188
Strandtype Kvalrossfjæra er en fin sandstrand. Større berg ut mot spissen av
Gravodden og rundt mot Herwighamna.
Adkomst Svenobekken (utløp for elv), lettbåt.
Dybdeforhold/strøm Kvalrossfjæra er langgrunn, LGF kan kanskje legge til på den delen av stranden som er nærmes Gravodden.
Hva skal beskyttes Kvalrossfjæra
Spesielle forhold Svært fin sandstrand, langgrunne.
Bilde 31 Gravodden, Meteorologisk stasjon t.v. (DNV GL).
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 71
Bilde 32 Kvalrossfjæra og Gravodden. Hele Kvalrossfjæra er merket med adkomstpunkter (flyfoto: NP).
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 72
Sted/lokasjon
9. Herwighamna
GPS Waypoint nr. Mangler waypoint
Strandtype Rullesteinsfjære, grove strandberg.
Adkomst Rolige strømforhold inne i havna, vind vil være hovedproblem ved navigasjon.
Dybdeforhold/strøm Renne inn mot kai er ca. 60 m brei, en stor stein ligger 5 m fra molo på styrbord side. Ingen store steiner på stranda innenfor molen.
Hva skal beskyttes
Spesielle forhold
Ugunstig for ankomst ved østlig og nordvestlig vind.
Merknad Havna er ikke lett tilgjengelig, og det kan antas å bli utfordrende å hente eventuelt oljevernutstyr som skulle bli lagret her dersom forholdene ikke er ideelle.
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 73
Bilde 33 Meteorologisk stasjon, Herwighamna, adkomstpunkt (flyfoto (NP)
Bilde 34Meterologisk stasjon sett fra sjø, Herwighamna (DNV GL).
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 74
Bilde 35 MS Maursund inn mot molo i Herwighamna (DNV GL).
Bilde 36 Molo og fjære ved Herwighamna (DNV GL).
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 75
Sted/lokasjon
10. Padda (fra Herwighamna til Nordkapp).
GPS Waypoint nr. 188
Strandtype Smale strender og klipper
Adkomst 3 punkter for adkomst merket i kart, disse er egnet for små båter ved østlig, sør/øst vindrettning. Det innerste punktet antas best.
Dybdeforhold/strøm
Hva skal beskyttes
Spesielle forhold Nord/øst vind er ugunstig for adkomst.
Bilde 37 Adkomstpunkter satt ved Padda, anbefales for lettbåt (flyfoto: NP).
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 76
Sted/lokasjon
11. Nordkapp - Måkestauren
GPS Waypoint nr. 189
Strandtype Klipper, blokker, strand innerst i bukta/Skratteskjer. Drivtømmer.
Adkomst Ingen avmerkede adkomstpunkter
Dybdeforhold/strøm
Hva skal beskyttes Sandstrand ved Skrattskjer
Spesielle forhold Adkomst er svært vanskelig.
Bilde 38 Kapp Olsen (flyfoto: NP).
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 77
Bilde 39 Sandstrand innerst ved Skrattskjer (flyfoto: NP).
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 78
Sted/lokasjon
12. Kapp Forsberg – Kapp Bergersen
GPS Waypoint nr. 190
Strandtype Austervåg: Strand av grov silt/stein på hver side av elveutløpet. Øvrige
områder preges av klipper og grove blokker.
Adkomst Adkomstpunkter: Austervåg: Adkomst mulig med lettbåt.
Silodden: Har rester av lasteanlegg/kai fra tidligere gruvedrift.
LGF kan kanskje legge til ved Silodden dersom forholdene er gunstige.
Dybdeforhold/strøm Lite strøm inne mot Silodden.
Hva skal beskyttes
Spesielle forhold Nord/vest til sør/øst er ugunstige vindretninger for opphold nært land.
Bilde 40 Adkomstpunkter ved utløp av Engelskelva (t.v.) og Silodden (t.h.) (flyfoto: NP).
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 79
Bilde 41 Silodden sett fra sjø (DNV GL).
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 80
Bilde 42 Silodden, spor etter gruvedrift. Tidligere benyttet som lastehavn. Mulig for LGF ved rolig sjø
(flyfoto: NP).
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 81
Sted/lokasjon
13. Kapp Bergersen – Kapp Nordenskiöld
GPS Waypoint nr. 191
Strandtype Steinblokker og klippekyst, smal abrasjons-plattform (grov sandstrand).
Adkomst Tre adkomstmuligheter er merket av, en av dem er en naturlig molo hvor LGF kan legge til under gunstige forhold. Nord/øst til sør/øst er ugunstige forhold.
Dybdeforhold/strøm Havn mellom Kapp Nordenskiöld og Evensenbukta er en gunstig havn, og LGF kan gå helt inn.
Hva skal beskyttes Hindre påslag ettersom det er veldig mye søppel og rekved langt forbi strandsonen. Dette tyder på at området er svært værutsatt og eventuell forurensning vil havne langt opp på land.
Spesielle forhold Veldig mye søppel og rekved i strandsonen.
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 82
Bilde 43 Adkomstpunkter ved Kapp Nordenskiöld, blått punkt merker adkomstmulighet for LGF (flyfoto: NP).
Bilde 44 Adkomstmulighet for LGF ved kapp Nordenskiöld (DNV GL).
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 83
Sted/lokasjon
14. Rifleodden - Losbrotet
GPS Waypoint nr. Ingen signal for GPS
Strandtype Raskjegler med begynnende stranddannelse. Rullestein og grove blokker.
Adkomst Avmerket adkomst ved Rifleodden er blokkert med en stor stein i forhold til eventuell adkomst med LGF. Må komme til med lettbåt fra Schivebukt. Kapp Levin og Losbrotet: Stor rasfare og bratt, adkomst mulig med liten båt, men dette vil innebære risiko ifm. ras fra klipper/overheng.
Dybdeforhold/strøm Skjær, vanskelig å navigere.
Hva skal beskyttes Mye rekved i bukta nedenfor hytte v/Rifleodden, bukta bør beskyttes.
Spesielle forhold Svært mye ras/erosjon, sjøen er tydelig brunfarget langs land.
Bilde 45 Adkomstpunkt merket for Rifleodden (flyfoto: NP)
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 84
Bilde 46 Adkomstpunkt ved Kapp Levin (flyfoto: NP)
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 85
Bilde 47 Adkomstpunkt ved Losbrotet, svært rasutsatt (flyfoto: NP)
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 86
Sted/lokasjon
15. Russehamna – Kapp Heer (inkl. Kvalrossbukta)
GPS Waypoint nr. 192 (svakt gps signal, usikker på om denne ble rett plassert)
Strandtype Russehamna: sand/grusstrand Kvalrossbukta: Små rullesteiner
Adkomst Russehamna: ureint farvann inn til stranda. Kan gå inn med LGF v/stille sjø. Lett tilgjengelig fra liten båt. Kvalrossbukta: LGF kan legge til.
Vind fra nord til sør er ugunstig.
Dybdeforhold/strøm Russehamna: Mye rekved. Trang innseiling – denne blir bredere ved elveutløp innerst. Kvalrossbukta: Veldig skjermet. Ugunstig vind vil være nordlig og sør/øst.
Hva skal beskyttes En del fugl/fuglefjell,
Spesielle forhold Berg rett i havet /steile klipper
Bilde 48 Adkomstpunkter for Russehamna (flyfoto: NP)
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 87
Bilde 49 MS Maursund på tur inn i Russehamna (DNV GL).
Bilde 50 Fjæra innerst i Russehamna (DNV GL).
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 88
Bilde 51 Hytte i Russehamna og stappe i sjø (DNV GL).
Bilde 52 Adkomstpunkt, Kvalrossbukta (flyfoto: NP)
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 89
Bilde 53 Nærbilde Kvalrossbukta, drivved (flyfoto: NP)
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 90
Sted/lokasjon
16. Kapp Heer – Beinneset (inkl. Sørhamna).
GPS Waypoint nr. Ikke satellittdekning.
Strandtype Smal strand innerst i Sørhamna. Øvrig landskap preges av bratte
klippevegger og store overheng.
Adkomst På grunn av stort overheng og fare for ras fra disse er det ikke å anbefale
at personell settes i land inne i selve havna. Sørhamna egner seg som
«nødhavn» ved ugunstige forhold da den er godt skjermet fra vind og vær. Det kan være mulig å gå fra Sørhamna og over til Kvalrossbukta, det anbefales da at personell settes i land med lettbåt på halvøy som ligger ut i havet.
Dybdeforhold/strøm Lite strøm, gode ankringsmuligheter.
Hva skal beskyttes
Spesielle forhold Ligger svært nær fuglefjellene på sørspissen av øya
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 91
Bilde 54 Indre del av Sørhamna (flyfoto: NP)
Bilde 55 Smal strand og bratte klippevegger innerst i Sørhamna (flyfoto: NP)
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 92
10.2 ACUTE STRATEGY OIL SPILL RESPONSE (ASO)
DNV GL – Report No. 16, Rev. 0 – www.dnvgl.com Page 93
94
10.3 RESPONSE RESOURCES (2014) NOFO resources Offshore response systems:
Preparedness Central with state-of-the-art technology. Can communicate with NCA emergency
response center when needed.
31 recovery vessels with corresponding number of tugboats, including the use of
Redningsselskapets resources 25 oceangoing system for mechanical recovery, of which 11 of
these systems are permanently placed on board vessels in standing readiness
Five spill response bases with 100 equipment operators
Permanent dispergeringskapasitet on 10 vessels in standing readiness
Access to OSRL aircraft for dispersion and access to their stock of 100 m3 dispersant
Access to 780 m3 dispersant according to:
o 536 m3 of 12 vessels in standing readiness
o 252 m3 of stock in 4 bases
Agreement with Teekay for access to shuttle tankers for use caching collected oil emulsion
Agreement with KSAT8 about remote monitoring of the continental shelf
Oil-radar system (OSD) and infrared sensors (IR) on vessels in standing readiness for detection
of oil, SLAR radar, FLIR (forward looking infrared camera) and established procedures
dispersing BV spray developed in NOFO R & D program Oljevern 2010
Two aerostats for operational remote sensing developed in Oljevern 2010 program
Access to a MOS Sweeper. This was developed Oljevern 2010 program. The system handles
both high waves and stronger power than traditional booms and represent in reality a 26
oceangoing system.
Access to resources through NOFO agreements Agreements on the use of public emergency resources include both national and international resources.
Some of the most important are: National agreements:
Agreement with NCA (NCA) for access to:
o Governmental depots (materials and depot personnel)
o Recovery vessels
o tugs
o Coast Guard (outer and inner coastguard, oil spill response equipment, command vessel)
o Armed Forces (personnel)
o NAV (personnel beach actions)
o Civil Defence (logistical support to shore actions)
Agreements with IUA for access to:
o Personnel, materials, separate agreements and plans within each IUAs responsibility
status for oil spill preparedness on the Norwegian shelf
Agreement with NCA on the use of two reconnaissance (LN-KYV and LN-TRG)
o Booking / call for routine surveillance with specially equipped aircraft.
Agreement with the meteorological department (weather, drive lanes, special notice etc)
Agreement with Norway Firefighting Tjeldsund municipality in Nordland and Finnmark County
Council's maritime college in Honningsvag about courses / training
o Training of personnel, especially from IGK (task group Coastal) and IGSA (Stake Group
beach acute) and IUA, the themes team management and scene management for coastal
and shoreline operations and equipment care courses.
International agreements: Agreement between OSRL and NOFO, which gives access dispersant aircraft and 100 m3
dispersant
OCES sharing agreement resources.
95
Access to resources through other agreements: Operators international agreements:
Agreements between operators and Tier 3 response organizations. OSRL mentioned above is an
example of such an organization. Several operators have established agreements that go beyond
the agreement NOFO with OSRL where they get access to extensive resources. Among other
things this significant amounts of dispersants and equipment. For dispersion by plane there is
access to preliminary well 300 m3 dispersant. In addition, it is being developed, a stock of
several thousand cubic meters for use in undervannsdispergering at source.
Encapsulation of well (capping) is not included in oil spill response, but should still be mentioned
as a consequence reducing measures that reduce the likelihood of protracted campaigns. PSA
considers this as an important risk mitigation measures and in a separate letter communicated
that an agreement on access to this type of equipment should be available before the consent
will be given. The industry has established plan and exercises to ensure coordination in the
interfaces between company and supplier.
Governmental international agreements: NORBRIT on cooperation between the UK and Norway o NORBRIT
o Agreement between Norway and the UK about interaction by spills from offshore
operations
Copenhagen Agreement on cooperation between the Nordic countries o Copenhagen Agreement
is a collaboration between the Nordic countries in the oil and chemical incidents.
Bonn Agreement on cooperation between the countries bordering the North Sea
o Bonn agreement is cooperation on combating acute pollution, oil and chemicals. Besides
Norway participates Belgium, Denmark, England, France, Netherlands, Sweden,
Germany and Ireland as an observer.
EMSA increased satellite coverage (EU agreement with KSAT)
o EMSA has acquired satellite service from KSAT. Through NCA can increase coverage by
actions ordered and delivered from this EU organization
Joint Action Plan (Norway-Russia in the northern regions)
o Joint Action Plan is an agreement between Norway and Russia on emergency cooperation
in northern regions. Cooperation agreements also cover joint exercises and coordination
of the organization.
96
Depos at Svalbard and at the Coast-Guard Depot Utstyrsbetegnelse Kapasitet Utstyrstype Utsyrsundertype Antall
Kystverket
Svalbard
Lenser-T/M NOFI 250EP i
pakkramme
4x25m
Kystverket
Svalbard
Lenser-T/M Expandi 4300 på
pall
152m x 2
Kystverket
Svalbard
Lenser-T/M NOFI 500EP i
container
100m x 4
Kystverket
Svalbard
Lenser-T/M 10 Current Buster 4 1
Kystverket
Svalbard
Lett lensesystem Current Buster 2 1
Kystverket
Svalbard
Lett lense NOFI 250EP 4x25m i
pakkramme
x8 800 m
Kystverket
Svalbard
Absorberende
lenser
med skjørt 1000 m
Kystverket
Svalbard
Absorberende
lenser
uten skjørt 225 m
Kystverket
Svalbard
Oljeopptaker 30 m3 Uniskim
Multiskimmer 30
2 stk
Kystverket
Svalbard
Oljeopptaker Lamor LWS 500
m/børste/skive
1 stk
Kystverket
Svalbard
Oljeopptaker Desmi Terminator Overløpsskimmer 1 stk
Kystverket
Svalbard
Oljeopptaker Foxtail VAB 4-9 I trsp.cont 1 stk
Kystverket
Svalbard
Oljeopptaker Foxtail VAB 2-9 I trsp.cont 1 stk
Kystverket
Svalbard
Oljeopptaker Foxtail VAB 2-6 I trsp.cont 2 stk
Kystverket
Svalbard
Pumper Rabbit P265
brannpumpe
1 stk
Kystverket
Svalbard
Pumper Elro slangepumpe 1 stk
Kystverket
Svalbard
Oljecontainer 10 kbm Unibag 3 stk
Kystverket
Svalbard
Oljecontainer 25 kbm Unibag/Oilbag 3 stk
Kystverket
Svalbard
Hydraulikk
aggregat
39kw Fast Henriksen 150-110-D 1 stk
Kystverket
Svalbard
Hydraulikk
aggregat
26kw Fast Henriksen 120-60-D 1 stk
Kystverket
Svalbard
Hydraulikk
aggregat
35 kw Fast Lamor LPP-35L 1 stk
Kystverket
Svalbard
Kjøretøy Løfteåk for
gaffeltruck
1 stk
Kystverket
Svalbard
Nødlossepakke for
bunkersoljer
Nødlossepakke for
bunkersoljer
1 stk
Kystverket
Svalbard
Strandrens Barkspreder Foxblower 1 stk
Kystverket
Svalbard
Strandrens Barkspreder Melbu Oilfighter 2 stk
Kystverket
Svalbard
Strandrens Nilfisk Alto.
Dieseldrevet
1 stk
Kystverket
Svalbard
Strandrens Oljebark Absorbent 1000
sekk
Kystverket
Svalbard
Diverse Dregger: 5x36 kg,
5x25m tau
5 sett
Kystverket
Svalbard
Diverse Expandi
pakkemaskin
for E4300 1 stk
Kystverket
Svalbard
Diverse Karmkasse Liten utgave 3 stk
97
Kystverket
Svalbard
Diverse Prøvetakingskoffert 1 stk
Kystverket
Svalbard
Personlig
verneutstyr
50 sett
Kystverket
Svalbard
Vaskestasjon mobil for personell 2 stk
Sysselmannen,
Longyearbyen
Båter 2 x 1560 HK
71,6 m
M/S Nordsyssel Isgående (mai-desember) 1 stk
Sysselmannen,
Longyearbyen
Båter 140 HK 21
ft
Vaktbåt (Polarcirkel) Eier SMS 1 stk
Sysselmannen,
Longyearbyen
Båter 130 HK 19
ft
Fjordtor 1
(Polarcirkel)
Eier SMS 1 stk
Sysselmannen,
Longyearbyen
Båter 130 HK 19
ft
Fjordtor 2
(Polarcirkel)
Eier SMS 1 stk
Sysselmannen,
Longyearbyen
Båter 130 HK 19
ft
Fjordtor 3
(Polarcirkel)
Eier SMS 1 stk
Sysselmannen,
Longyearbyen
Båter 40 HK 3,7
meter
Zodiac Eier SMS 5 stk
Sysselmannen,
Longyearbyen
Helikopter Super Puma Airlift AS 2 stk
Sysselmannen,
Longyearbyen
Beltevogn 2 stk
KV Svalbard Oljeopptaker Expandi 4300 430 mm fribord,
selvoppblåsende
304 m
KV Svalbard Oljeopptaker Foxtail VAB 2-6 VAB Oil Skimmer. 2 bånd
à 6 tommer
1 stk
KV Svalbard Lagrings tank 25 m3 Unibag 2 stk
KV Svalbard
KV Svalbard
KV Svalbard
KV Harstad Tunge lenser NOFI 800 S på
trommel
m/krysshanefot
innfestning
260m
KV Harstad Mellomtunge lenser Expandi 4300 430 mm fribord,
selvoppblåsende
152 m
KV Harstad Oljeopptaker Foxtail VAB 4-9 VAB Oil Skimmer. 4 bånd
à 9 tommer
1 stk
KV Harstad Oljeopptaker Trans Rec 250 ekstra losseslanger og
pumpe for nødlossing
1 stk
KV Harstad Lagrings tank 1000 m3 tank 1 stk
KV Harstad Lagrings tank 25 m3 Unibag 1 stk
KV Barensthav Tunge lenser NO-800-R på
trommel
m/krysshanefot
innfestning
300 m
KV Barensthav Oljeopptaker NORMar 200 1 stk
KV Barensthav Tankkapasitet 1075 m3
KV Sortland Tunge lenser NO-800-R på
trommel
m/krysshanefot
innfestning
300 m
KV Sortland Oljeopptaker NORMar 200 1 stk
KV Sortland Tankkapasitet 1075 m3
Nordsyssel Mellomtunge lenser NOFI 500 EP 50cm fribord m/fast
flytelegeme
100 m
98
Nordsyssel Lette lenser NO35 F 34cm fribord m/fast
flytelegeme
150 m
Nordsyssel Oljeopptaker Foxtail VAB 4-9 VAB Oil Skimmer. 4 bånd
à 9 tommer
1 stk
Nordsyssel Lagrings tank 200 m3 tank 1 stk
Nordsyssel Lagrings tank 25 m3 Unibag 1 stk
Svea Mellomtunge lenser Ro-Boom 1500 Ledelense 350 m
Svea Lette lenser Ro-Boom 200 300 m
Svea Oljeopptaker Desmi Terminator Belteskimmer, på taubåten 1 stk
Svea Lagrings tank 10 m3 Unibag 1 stk
Svea Lagrings tank 25m3 Ro-tank m/slepesett På taubåten 1 stk
Svea Lagrings tank 40m3 Tank m/slepesett På taubåten 1 stk
Svea
Svea.Store
Norske/LNSS
Lette lenser Havnelense, 300 m
Svea.Store
Norske/LNSS
Lette lenser Ledelense Ro-boom
1500
600 m
Svea.Store
Norske/LNSS
Lagrings tank 6 tonn Portable tank 2 stk
Svea.Store
Norske/LNSS
Lagrings tank 10m3 Lagrings tanker
10m3
30 stk
Svea.Store
Norske/LNSS
Lagrings tank 100 l Polypropylene big
bags
10 stk
Svea.Store
Norske/LNSS
Lagrings tank 10m3 Fleksibel flytende
lagrinsbag
1 stk
Svea.Store
Norske/LNSS
Pumper Sjøvannspumpe
BGM 5 m/tilbehør
2 stk
Svea.Store
Norske/LNSS
Personlig
verneutstyr
Personlig verneutstyr 15 sett
Svea.Store
Norske/LNSS
Absorbenter Oljebark 50.ltr
sekker
300 stk
Svea.Store
Norske/LNSS
Båter 20', fritidsbåter 4 stk
Svea.Store
Norske/LNSS
Båter arbeidsbåter 2 stk
Svea.Store
Norske/LNSS
Pumper, (Sigyn og
Bonden)
Desmi Dop-160, screw off loading pump 1 stk
Svea.Store
Norske/LNSS
Båt (på Sigyn og
Bonden)
MP-741 Springer
mob.båt, vannjet
Beredskapsbåt 1 stk
Ny-Ålesund Lette lenser NO35 F 34cm fribord m/fast
flytelegeme
300 m
Ny-Ålesund Båter 375 HK aluminumsbåt Kings Bay AS 1 stk
Ny-Ålesund Båter 100 HK PVC Kings Bay AS 1 stk
Ny-Ålesund Båter 40 HK aluminumsbåt Velferden 1 stk
Ny-Ålesund Båter 40 HK aluminumsbåt Velferden 1 stk
Ny-Ålesund Båter 40 HK aluminumsbåt Velferden 1 stk
Barentsburg Absorberende
lenser
BL-BOM 20/25/12,5 200 mm, 200 m med skjørt 400 m
Barentsburg Oljeopptaker NORMar Multi 1 stk
Barentsburg Lette lenser NO35F 35cm fribord m/fast 400 m
99
flytelegeme
Barentsburg Båter Polarcirkel 760 1 stk
Barentsburg Oljeopptaker NorMar 15 multiskimmer 1 stk
Barentsburg Diverse fortøyningssett 16 stk
Barentsburg Personlig
verneutstyr
Personlig verneutstyr 10 sett
Depos at the Norwegian mainland
Kystverket Vadsø Lenser-T/M Norlense NO-800R 10 fot container,
trommel
300m
Kystverket Vadsø Lenser-T/M NOFI 450 S Lagret på trommel 200m
Kystverket Vadsø Lenser-T/M Expandi 4300 selvoppblåsende. 608m
Kystverket Vadsø Lenser-T/M 10 Current Buster 4 10’ container. 1 stk
Kystverket Vadsø Lenser-T/M 5 Harbour Buster 10’ container
m/paravan
1 stk
Kystverket Vadsø Lette lenser NOFI 350EP 4x25 m i
pakkramme
300 m
Kystverket Vadsø Diverse Expandi
Pakkemanskin
for EP 4300 1 stk
Kystverket Vadsø Olje opptagere 9 Foxtail VAB 2-6 adhesjons skimmer 1 stk
Kystverket Vadsø Olje opptagere KLK402 Trommelskimmer 2 stk
Kystverket Vadsø Olje opptagere 30 Desmi Overløpsskimmer 1 stk
Kystverket Vadsø Olje opptagere KLK602/Foxdrum m/transportcontaine
r
1 stk
Kystverket Vadsø Olje opptagere Lamor LWS 500 m/børste/skive 1 stk
Kystverket Vadsø Olje opptagere Foxtail VAB 2-6 m/transportcontaine
r
1 stk
Kystverket Vadsø Absorberende lenser med skjørt 1000 m
Kystverket Vadsø Absorberende lenser uten skjørt 1200 m
Kystverket Vadsø Pumper Rekors/Vogelsang R
120
1 stk
Kystverket Vadsø Pumper 20 Elro slangepumpe Bensin 1 stk
Kystverket Vadsø Spylepumpe Rabbit P265M Brannpumpe. 1 stk
Kystverket Vadsø Kjøretøy Løfteåk for gaffeltruck 1 stk
Kystverket Vadsø Hydraulikk Henriksen 150-110-D
39kW Fast
Diesel 1 stk
Kystverket Vadsø Hydraulikk Henriksen 120-60-D 26
kW Fast
Diesel 1 stk
Kystverket Vadsø Hydraulikk Lamor LPP-35L
35kW Fast
2 stk
Kystverket Vadsø Hydraulikk Rexroth 50kW Fast 1 stk
Kystverket Vadsø Strømaggregat Honda E2500
Bensindrevet
2 stk
Kystverket Vadsø Oljecontainer 25 Container 25m3 Unibag/Oilbag 1 stk
Kystverket Vadsø Båt 80 Arb.båt Rana 20 1 stk
Kystverket Vadsø Diverse Oppankringsutstyr Dregger, 36kg
m/25m tau
15 stk (3 sett
a 5 stk)
Kystverket Vadsø Diverse Grabb for operasjon i
kran
1 stk
Kystverket Vadsø Diverse Karmkasse, liten 3 stk
Kystverket Vadsø Diverse Prøvetakingskoffert 1 stk
100
Kystverket Vadsø Strandrens Akuttfase Strand -
Container 1
10-fots akuttfase
strandutstyr
1 stk
Kystverket Vadsø Strandrens Akuttfase Strand -
Container 2
10-fots akuttfase
strandutstyr
1 stk
Kystverket Vadsø Strandrens Akuttfase Strand -
Container 3
10-fots akuttfase
strandutstyr
1 stk
Kystverket Vadsø Strandrens Akuttfase Strand -
Container 4
10-fots akuttfase
strandutstyr
1 stk
Kystverket Vadsø Strandrens Barkspreder Foxblower 1 stk
Kystverket Vadsø Strandrens Barkspreder Melbu Oilfighter 2 stk
Kystverket Vadsø Strandrens Nilfisk Alto. Dieseldrevet 1 stk
Kystverket Vadsø Strandrens Absorbent Oljebark 1000 sekker
Kystverket Vadsø Nødlosse utstyr Nødlossepakke for
bunkersolje
1 stk
Kystverket
Hammerfest
Norlense NO- 800 - R lagret på trommel i
cont.
300m
Kystverket
Hammerfest
Lenser-T/M NO-450S på trommel i
container
200m
Kystverket
Hammerfest
Lenser-T/M Current Buster 4 Container 1 stk
Kystverket
Hammerfest
Lenser-T/M Current Buster 2 Container
m/paravan
1 stk
Kystverket
Hammerfest
Lette lenser NOFI 350 EP 4x24m Fast flytelegeme, i
pakkramme
200m
Kystverket
Hammerfest
Oljeopptagere 30 Foxtail VAB 4-9 Vertikal Adhesjon
Band
1 stk
Kystverket
Hammerfest
Oljeopptagere 9 Foxtail VAB 2-6 Vertikal Adhesjon
Band
2 stk
Kystverket
Hammerfest
Oljeopptagere KLK402 Trommelskimmer 1 stk
Kystverket
Hammerfest
Oljeopptagere Uniskim
Multiskimmer 30
Multiskimmer 1 stk
Kystverket
Hammerfest
Oljeopptagere 40m3/tim
e
Lamor Minimax 40 Børsteskimmer 1 stk
Kystverket
Hammerfest
Oljeopptagere NorMar 30
Børstekonfigurasjon
Børsteskimmer 1 stk
Kystverket
Hammerfest
Oljeopptagere KLK 602 / Foxdrum
m/ trsp.cont
Multiskimmer 1 stk
Kystverket
Hammerfest
Oljeopptagere Lamor LWS 500 m/
børste/skive
Multiskimmer 1 stk
Kystverket
Hammerfest
Oljeopptagere Desmi Termite.
Overløp
Overløpskimmer 1 stk
Kystverket
Hammerfest
Oljeopptagere Desmi Terminator.
Skive/børste
Multiskimmer 1 stk
Kystverket
Hammerfest
Oljeopptagere Desmi Terminator.
Overløp
Overløpskimmer 1 stk
Kystverket
Hammerfest
Pumper Rabbit P265
Brannpumpe
1 stk
Kystverket
Hammerfest
Pumper Elro slangepumpe Bensindrevet. 1 stk
Kystverket
Hammerfest
Pumper Eksenterskruepumpe 1 stk
Kystverket
Hammerfest
Kjøretøy Toyota 7FBMF25.
El.drift. 2,5t
1 stk
Kystverket
Hammerfest
Kjøretøy Toyota 7FDF45.
Dieseldrevet
1 stk
Kystverket
Hammerfest
Kjøretøy Løfteåk for gaffeltruck 1 stk
Kystverket
Hammerfest
Diesel Hydraulikk
aggregat
60 Henriksen 120-60-D 26
kW Fast
1 stk
101
Kystverket
Hammerfest
Diesel Hydraulikk
aggregat
40 Henriksen 150-200-D
53kW Fast
1 stk
Kystverket
Hammerfest
Diesel Hydraulikk
aggregat
19 Markleen DHPP
40kW
1 stk
Kystverket
Hammerfest
Diesel Hydraulikk
aggregat
9 Markleen DHPP
60kW
1 stk
Kystverket
Hammerfest
Diesel Hydraulikk
aggregat
53 Lamor LPP-35L
35kW Fast
1 stk
Kystverket
Hammerfest
Diesel Hydraulikk
aggregat
Rexroth 50kW Fast 1 stk
Kystverket
Hammerfest
Båt Arbeids/insp.båt T650KYV 22ft 1 stk
Kystverket
Hammerfest
Båt GB Cat
arbeidkatamaran
m/ kran 1 stk
Kystverket
Hammerfest
Oljecontainer 25 m3 Unibab / oilbag 1 stk
Kystverket
Hammerfest
Oljecontainer 10 m3 Unibag 1 stk
Kystverket
Hammerfest
Diverse Oppankringsutstyr Dregger, 5x36kg
m/5x25m tau
6 sett
Kystverket
Hammerfest
Diverse Karmkasse, liten 3 stk
Kystverket
Hammerfest
Diverse Prøvetakingskoffert 1 stk
Kystverket
Hammerfest
Diverse Expandi
Pakkemanskin
for EP 4300 1 stk
Kystverket
Hammerfest
Strandrens Akuttfase Strand -
Container 1
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Hammerfest
Strandrens Akuttfase Strand -
Container 2
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Hammerfest
Strandrens Akuttfase Strand -
Container 3
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Hammerfest
Strandrens Akuttfase Strand -
Container 4
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Hammerfest
Strandrens Barkspreder Foxblower 1 stk
Kystverket
Hammerfest
Strandrens Barkspreder Melbu Oilfighter 1 stk
Kystverket
Hammerfest
Strandrens Nilfisk Alto. Dieseldrevet 1 stk
Kystverket
Hammerfest
Strandrens Absorbent Oljebark 1000 sekker
Kystverket
Hammerfest
Strømaggregat Honda E2500
Bensindrevet
2 stk
Kystverket Tromsø Lenser-T/M Norlense NO-800R trommel i 10 fot
cont.
300m
Kystverket Tromsø Lenser-T/M Expandi 4300 152m på pall x3 456m
Kystverket Tromsø Lenser-T/M NO-450S trommel i 10 fot
cont.
200m
Kystverket Tromsø Lenser-T/M NOFI 500 EP 50cm fribord 400m
Kystverket Tromsø Lenser-T/M 10m3
tank
Current Buster 4 10' container m.
paravan
1 stk
Kystverket Tromsø Lenser-T/M 5m3 tank Current Buster 2 10' container m.
paravan
1 stk
Kystverket Tromsø Lette lenser NOFI 350 EP 4x25m i pakkramme 300m
Kystverket Tromsø Absorberende lenser Abs. lense med skjørt 1000 m
Kystverket Tromsø Absorberende lenser Abs. lense uten skjørt 1600m
Kystverket Tromsø Oljeopptagere 15 Foxtail VAB 2-9 Adhesjon 1 stk
Kystverket Tromsø Oljeopptagere 30 Foxtail VAB 4-9 Adhesjon 2 stk
102
Kystverket Tromsø Oljeopptagere Foxtail VAB 2-6 Adhesjon 1 stk
Kystverket Tromsø Oljeopptagere Sandvikband Transportbånd 1 stk
Kystverket Tromsø Oljeopptagere KLK 602 Trommelskimmer 1 stk
Kystverket Tromsø Oljeopptagere KLK 402 Trommelskimmer 2 stk
Kystverket Tromsø Oljeopptagere Desmi Terminator.
Belte
1 stk
Kystverket Tromsø Oljeopptagere Desmi Terminator. Overløpskimmer 2 stk
Kystverket Tromsø Oljeopptagere 65 Foilex TDS 200 Overløpskimmer 2 stk
Kystverket Tromsø Oljeopptagere Lamor LWS 500 m/
børste/skive
Multiskimmer 1 stk
Kystverket Tromsø Pumper Rabbit P265
Brannpumpe
1 stk
Kystverket Tromsø Pumper 20 Elro slangepumpe Bensindrevet. 1 stk
Kystverket Tromsø Pumper Rekord/Vogelsang
R120
1 stk
Kystverket Tromsø Pumper Framo TK5* 1 stk
Kystverket Tromsø Kjøretøy Løfteåk for gaffeltruck 1 stk
Kystverket Tromsø Diesel Hydraulikk 39kwF Henriksen 150-110-D
39kW Fast
1 stk
Kystverket Tromsø Diesel Hydraulikk Henriksen 120-60-D 26
kW Fast
1 stk
Kystverket Tromsø Diesel Hydraulikk 53kwF Henriksen 150-200-D
53kW Fast
1 stk
Kystverket Tromsø Diesel Hydraulikk Lamor LPP-35L
35kW Fast
1 stk
Kystverket Tromsø Oljecontainer 10m3 RO-Tank 2 stk
Kystverket Tromsø Oljecontainer 25m3 NOFI oljelekter
25kbm
1 stk
Kystverket Tromsø Båt Arbeids/insp.båt Rana
20ft
påhengsmotor 1 stk
Kystverket Tromsø Diverse Oppankringsutstyr Dregger, 5x36kg
m/5x25m tau
5 sett
Kystverket Tromsø Diverse Karmkasse, liten 3 stk
Kystverket Tromsø Diverse Prøvetakingskoffert 1 stk
Kystverket Tromsø Diverse Expandi
Pakkemanskin
for EP 4300 1 stk
Kystverket Tromsø Diverse Mooring 500kg 4 sett
Kystverket Tromsø Diverse Grabb for operasjon i
kran
1 stk
Kystverket Tromsø Strandrens Akuttfase Strand -
Container 1
10-fots akuttfase
strandutstyr
1 stk
Kystverket Tromsø Strandrens Akuttfase Strand -
Container 2
10-fots akuttfase
strandutstyr
1 stk
Kystverket Tromsø Strandrens Akuttfase Strand -
Container 3
10-fots akuttfase
strandutstyr
1 stk
Kystverket Tromsø Strandrens Akuttfase Strand -
Container 4
10-fots akuttfase
strandutstyr
1 stk
Kystverket Tromsø Strandrens Barkspreder Foxblower 1 stk
Kystverket Tromsø Strandrens Barkspreder Melbu Oilfighter 2 stk
Kystverket Tromsø Strandrens Nilfisk Alto. Dieseldrevet 1 stk
Kystverket Tromsø Strandrens Absorbent Oljebark 1000 sekker
Kystverket Tromsø Strømaggregat Honda E2500
Bensindrevet
2 stk
Kystverket Tromsø Nødlosse utstyr Nødlossepakke for
bunkersolje
1 stk
103
Kystverket
Lødingen
Lenser-T/M Norlense NO-800R på trommel m/ 10 fot
cont
300m
Kystverket
Lødingen
Lenser-T/M Expandi 4300 selvoppblåsende, 152
mx2.
304m
Kystverket
Lødingen
Lenser-T/M 10m3
tank
Current Buster 4 10' container m.
paravan
1 stk
Kystverket
Lødingen
Lenser-T/M 5m3 tank Current Buster 2 10' container m.
paravan
1 stk
Kystverket
Lødingen
Lette lenser NOFI 350EP 4x25m i
pakkramme
300m
Kystverket
Lødingen
absorberende lenser Absorberende lense
uten skjørt
200 m
Kystverket
Lødingen
absorberende lenser Absorberende lense
med skjørt
1000 m
Kystverket
Lødingen
Oljeopptagere KLK402/Foxdrum i pakkramme 1 stk
Kystverket
Lødingen
Oljeopptagere KLK 602 / Foxdrum m/børste /skive 1 stk
Kystverket
Lødingen
Oljeopptagere Lamor LWS 500 m/
børste/skive
1 stk
Kystverket
Lødingen
Oljeopptagere Foxtail VAB 4-9 i
trsp.cont
Adhesjons skimmer 1 stk
Kystverket
Lødingen
Oljeopptagere 15 Foxtail VAB 2-9 i
trsp.cont
Adhesjons skimmer 1 stk
Kystverket
Lødingen
Oljeopptagere Foxtail VAB 2-9 i
pakkramme 1
Adhesjons skimmer 1 stk
Kystverket
Lødingen
Oljeopptagere 9 Foxtail VAB 2-6 Adhesjons skimmer 1 stk
Kystverket
Lødingen
Båt Arbeids/insp.båt
T650KYV 22ft
aluminiumsbåt 1 stk
Kystverket
Lødingen
Båt GB Cat
arbeidkatamaran m/
kran
Flåte 1 stk
Kystverket
Lødingen
Kjøretøy Toyota TC40 8
FD70N. Diesel
1 stk
Kystverket
Lødingen
Kjøretøy Løfteåk for gaffeltruck 1 stk
Kystverket
Lødingen
Strømaggregat Honda E2500
Bensindrevet
Diesel Hydraulikk 1 stk
Kystverket
Lødingen
Pumper Rabbit P265
Brannpumpe
1 stk
Kystverket
Lødingen
Pumper Elro slangepumpe 1 stk
Kystverket
Lødingen
Diesel Hydraulikk 39kwF Henriksen 150-110-D
39kW Fast
1 stk
Kystverket
Lødingen
Diesel Hydraulikk Lamor LPP-35L
35kW Fast
1 stk
Kystverket
Lødingen
Diesel Hydraulikk Rexroth 50kW Fast 1 stk
Kystverket
Lødingen
Oljecontainer 10m3 RO-Tank, Desmi 2 stk
Kystverket
Lødingen
Oljecontainer 25m3 Unibag Oilbag 1 stk
Kystverket
Lødingen
Diverse Oppankringsutstyr Dregger, 5x36kg
m/5x25m tau
3 sett
Kystverket
Lødingen
Diverse Karmkasse, liten 3 stk
Kystverket
Lødingen
Diverse Prøvetakingskoffert 1 stk
Kystverket
Lødingen
Diverse Expandi
Pakkemanskin
for EP 4300 1 stk
104
Kystverket
Lødingen
Strandrens Akuttfase Strand -
Container 1
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Lødingen
Strandrens Akuttfase Strand -
Container 2
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Lødingen
Strandrens Akuttfase Strand -
Container 3
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Lødingen
Strandrens Akuttfase Strand -
Container 4
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Lødingen
Strandrens Barkspreder Foxblower 1 stk
Kystverket
Lødingen
Strandrens Barkspreder Melbu Oilfighter 2 stk
Kystverket
Lødingen
Strandrens Nilfisk Alto. Dieseldrevet 1 stk
Kystverket
Lødingen
Strandrens Absorbent Oljebark 1000 sekker
Kystverket Bodø Lenser-T/M Norlense NO-800R på trommel m/ 10 fot
cont
300m
Kystverket Bodø Lenser-T/M NO-450S luftkompressor 200m
Kystverket Bodø Lenser-T/M Expandi 4300 selvoppblåsende,
152mx4
608m
Kystverket Bodø Lenser-T/M Current Buster 4 10' container m.
paravan
1 stk
Kystverket Bodø Lette lenser Current Buster 2 10' container m.
paravan
1 stk
Kystverket Bodø Lette lenser NOFI 350EP 4x25m i pakkramme 300m
Kystverket Bodø absorberende lenser med skjørt 1000m
Kystverket Bodø absorberende lenser uten skjørt 100 m
Kystverket Bodø Oljeopptagere KLK402 Foxdrum i
pakkramme
Trommel 1 stk
Kystverket Bodø Oljeopptagere KLK 602 Trommelskimmer 1 stk
Kystverket Bodø Oljeopptagere 65 Foilex TDS200 Overløpskimmer 1 stk
Kystverket Bodø Oljeopptagere Lamor LWS 500 m/
børste/skive
Multiskimmer 1 stk
Kystverket Bodø Oljeopptagere Foxtail VAB 8-14 Adhesjon 1 stk
Kystverket Bodø Oljeopptagere 9 Foxtail VAB 2-6 Adhesjon 2 stk
Kystverket Bodø Nødlossing Nødlossepakke for
bunkersoljer
1 stk
Kystverket Bodø Nødlossing Nødlossepakke for
Lastolje
1 stk
Kystverket Bodø Pumper Honda WB20XT
Spylepumpe
1 stk
Kystverket Bodø Pumper Rabbit P265
Brannpumpe
1 stk
Kystverket Bodø Pumper 20 Elro slangepumpe Bensindrevet. 1 stk
Kystverket Bodø Båt Arbeids/insp.båt
T650KYV 22ft
1 stk
Kystverket Bodø Kjøretøy Toyota 7FBMF25.
El.drift. 2,5t
1 stk
Kystverket Bodø Kjøretøy Løfteåk for gaffeltruck 1 stk
Kystverket Bodø Strømaggregat Honda E2500
Bensindrevet
Diesel Hydraulikk 1 stk
Kystverket Bodø Diesel Hydraulikk 39kwF Henriksen 150-110-D
39kW Fast
1 stk
Kystverket Bodø Diesel Hydraulikk Henriksen 120-60-D 26
kW Fast
1 stk
Kystverket Bodø Diesel Hydraulikk Lamor LPP-35L 1 stk
105
35kW Fast
Kystverket Bodø Diesel Hydraulikk Rexroth 50kW Fast 1 stk
Kystverket Bodø Oljecontainer 25m3 Unibag Oilbag 1 stk
Kystverket Bodø Diverse Oppankringsutstyr Dregger, 5x36kg
m/5x25m tau
3 sett
Kystverket Bodø Diverse Karmkasse, liten 3 stk
Kystverket Bodø Diverse Prøvetakingskoffert 1 stk
Kystverket Bodø Diverse Expandi
Pakkemanskin
for EP 4300 1 stk
Kystverket Bodø Strandrens Akuttfase Strand -
Container 1
10-fots akuttfase
strandutstyr
1 stk
Kystverket Bodø Strandrens Akuttfase Strand -
Container 2
10-fots akuttfase
strandutstyr
1 stk
Kystverket Bodø Strandrens Akuttfase Strand -
Container 3
10-fots akuttfase
strandutstyr
1 stk
Kystverket Bodø Strandrens Akuttfase Strand -
Container 4
10-fots akuttfase
strandutstyr
1 stk
Kystverket Bodø Strandrens Barkspreder Foxblower 1 stk
Kystverket Bodø Strandrens Barkspreder Melbu Oilfighter 2 stk
Kystverket Bodø Strandrens Nilfisk Alto. Dieseldrevet 1 stk
Kystverket Bodø Strandrens Absorbent Oljebark 1000 sekker
Kystverket
Sandnessjøen
Lenser-T/M Norlense NO-800R på trommel m/ 10 fot
cont
300m
Kystverket
Sandnessjøen
Lenser-T/M Expandi 4300 selvoppblåsende,
152mx4
608m
Kystverket
Sandnessjøen
Lenser-T/M Current Buster 4 10' container m.
paravan
1 stk
Kystverket
Sandnessjøen
Lette lenser Current Buster 2 10' container m.
paravan
1 stk
Kystverket
Sandnessjøen
Lette lenser NOFI 350EP 4x25m i pakkramme 300m
Kystverket
Sandnessjøen
absorberende lenser med skjørt 1000m
Kystverket
Sandnessjøen
Oljeopptagere Lamor Minimax 40. 1 stk
Kystverket
Sandnessjøen
Oljeopptagere KLK402 Foxdrum i
pakkramme
Trommel 2 stk
Kystverket
Sandnessjøen
Oljeopptagere KLK 602 Dbl
pakkramme
Trommelskimmer 1 stk
Kystverket
Sandnessjøen
Oljeopptagere Lamor LWS 500 m/
børste/skive
Multiskimmer 1 stk
Kystverket
Sandnessjøen
Oljeopptagere Foxtail VAB 4-9 i
transp.cont
Adhesjon 1 stk
Kystverket
Sandnessjøen
Oljeopptagere 9 Foxtail VAB 2-6 i
transp.cont
Adhesjon 2 stk
Kystverket
Sandnessjøen
Nødlossing Nødlossepakke for
bunkersoljer
1 stk
Kystverket
Sandnessjøen
Pumper Rabbit P265
Brannpumpe
1 stk
Kystverket
Sandnessjøen
Pumper 20 Elro slangepumpe Bensindrevet. 1 stk
Kystverket
Sandnessjøen
Båt Arbeids/insp.båt
T650KYV 22ft
aluminiumsbåt 1 stk
Kystverket
Sandnessjøen
Båt GB Cat
arbeidkatamaran m/
kran
Flåte 1 stk
Kystverket
Sandnessjøen
Kjøretøy Toyota 7FBMF25.
El.drift. 2,5t
1 stk
106
Kystverket
Sandnessjøen
Kjøretøy Toyota TC40 8
FD70N. Diesel
1 stk
Kystverket
Sandnessjøen
Kjøretøy Løfteåk for gaffeltruck 1 stk
Kystverket
Sandnessjøen
Strømaggregat Honda E2500
Bensindrevet
Diesel Hydraulikk 1 stk
Kystverket
Sandnessjøen
Diesel Hydraulikk Henriksen 120-60-D 26
kW Fast
1 stk
Kystverket
Sandnessjøen
Diesel Hydraulikk Lamor LPP-35L
35kW Fast
1 stk
Kystverket
Sandnessjøen
Diesel Hydraulikk Isuzu 54kW Fast 1 stk
Kystverket
Sandnessjøen
Oljecontainer 25m3 Unibag Oilbag 1 stk
Kystverket
Sandnessjøen
Oljecontainer 10kbm Desmi RO-tank Oilbag 1 stk
Kystverket
Sandnessjøen
Diverse Oppankringsutstyr Dregger, 5x36kg
m/5x25m tau
3 sett
Kystverket
Sandnessjøen
Diverse Karmkasse, liten 3 stk
Kystverket
Sandnessjøen
Diverse Prøvetakingskoffert 1 stk
Kystverket
Sandnessjøen
Diverse Expandi
Pakkemanskin
for EP 4300 1 stk
Kystverket
Sandnessjøen
Strandrens Akuttfase Strand -
Container 1
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Sandnessjøen
Strandrens Akuttfase Strand -
Container 2
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Sandnessjøen
Strandrens Akuttfase Strand -
Container 3
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Sandnessjøen
Strandrens Akuttfase Strand -
Container 4
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Sandnessjøen
Strandrens Barkspreder Foxblower 1 stk
Kystverket
Sandnessjøen
Strandrens Barkspreder Melbu Oilfighter 2 stk
Kystverket
Sandnessjøen
Strandrens Nilfisk Alto. Dieseldrevet 1 stk
Kystverket
Sandnessjøen
Strandrens Absorbent Oljebark 1000 sekker
Kystverket Ørland Lenser-T/M Norlense NO-800R trommel i 10 fot
cont.
300m
Kystverket Ørland Lenser-T/M Expandi 4300 152m på pall x4 608 m
Kystverket Ørland Lenser-T/M NO-450S trommel i 10 fot
cont.
200m
Kystverket Ørland Lenser-T/M 10m3
tank
Current Buster 4 10' container m.
paravan
1 stk
Kystverket Ørland Lenser-T/M 5m3 tank Current Buster 2 10' container m.
paravan
1 stk
Kystverket Ørland Lette lenser NOFI 350 EP 4x25m i pakkramme 300m
Kystverket Ørland Absorberende lenser Abs. lense med skjørt 1000 m
Kystverket Ørland Oljeopptagere 15 Foxtail VAB 2-9 Adhesjon 1 stk
Kystverket Ørland Oljeopptagere 30 Foxtail VAB 4-9 Adhesjon 1 stk
Kystverket Ørland Oljeopptagere Foxtail VAB 2-6 Adhesjon 1 stk
Kystverket Ørland Oljeopptagere KLK 602 Foxdrum i
pakkramme
Trommelskimmer 1 stk
Kystverket Ørland Oljeopptagere KLK 402Foxdrum m/
trsp.cont
Trommelskimmer 1 stk
Kystverket Ørland Oljeopptagere Desmi Terminator. Overløpskimmer 1 stk
107
Kystverket Ørland Oljeopptagere Lamor LWS 500 m/
børste/skive
Multiskimmer 1 stk
Kystverket Ørland Pumper 20 Elro slangepumpe Bensindrevet. 1 stk
Kystverket Ørland Kjøretøy Løfteåk for gaffeltruck 1 stk
Kystverket Ørland Diesel Hydraulikk Henriksen 140-90-D
26kW Fast
1 stk
Kystverket Ørland Diesel Hydraulikk Markleen DHPP
60kW
1 stk
Kystverket Ørland Diesel Hydraulikk Rexroth 50kW Fast 1 stk
Kystverket Ørland Diesel Hydraulikk Lamor LPP-35L
35kW Fast
1 stk
Kystverket Ørland Oljecontainer 10m3 RO-Tank Desmi 2 stk
Kystverket Ørland Oljecontainer 25m3 Unibag/Oilbag 1 stk
Kystverket Ørland Båt Arbeids/insp.båt
T650KYV 22ft
påhengsmotor 1 stk
Kystverket Ørland Diverse Karmkasse, liten 3 stk
Kystverket Ørland Diverse Prøvetakingskoffert 1 stk
Kystverket Ørland Diverse Expandi
Pakkemanskin
for EP 4300 1 stk
Kystverket Ørland Diverse Grabb for operasjon i
kran
1 stk
Kystverket Ørland Strandrens Akuttfase Strand -
Container 2
10-fots akuttfase
strandutstyr
1 stk
Kystverket Ørland Strandrens Akuttfase Strand -
Container 3
10-fots akuttfase
strandutstyr
1 stk
Kystverket Ørland Strandrens Akuttfase Strand -
Container 4
10-fots akuttfase
strandutstyr
1 stk
Kystverket Ørland Strandrens Barkspreder Foxblower 1 stk
Kystverket Ørland Strandrens Barkspreder Melbu Oilfighter 2 stk
Kystverket Ørland Strandrens Nilfisk Alto. Dieseldrevet 1 stk
Kystverket Ørland Strandrens Absorbent Oljebark 1000 sekker
Kystverket Ørland Strømaggregat Honda E2500
Bensindrevet
2 stk
Kystverket Ålesund Lenser-T/M Norlense NO-800R på trommel m/ 10 fot
cont
300m
Kystverket Ålesund Lenser-T/M NO-450S luftkompressor 200m
Kystverket Ålesund Lenser-T/M Uniboom A-1300HD 100m x 4 400 m
Kystverket Ålesund Lenser-T/M Expandi 4300 selvoppblåsende,
152mx3
456m
Kystverket Ålesund Lenser-T/M Current Buster 4 10' container m.
paravan
1 stk
Kystverket Ålesund Lette lenser Current Buster 2 10' container m.
paravan
1 stk
Kystverket Ålesund Lette lenser NOFI 350EP 4x25m i pakkramme 300m
Kystverket Ålesund absorberende lenser med skjørt 1000m
Kystverket Ålesund Oljeopptagere KLK402 Foxdrum i
pakkramme
Trommel 2 stk
Kystverket Ålesund Oljeopptagere KLK 602 / Foxdrum
m/ trsp.cont
Trommelskimmer 1 stk
Kystverket Ålesund Oljeopptagere 65 Foilex TDS200 Overløpskimmer 1 stk
Kystverket Ålesund Oljeopptagere Lamor LWS 500 m/
børste/skive
Multiskimmer 1 stk
Kystverket Ålesund Oljeopptagere Foxtail VAB 4-9 Adhesjon 1 stk
108
Kystverket Ålesund Oljeopptagere 9 Foxtail VAB 2-6 Adhesjon 1 stk
Kystverket Ålesund Nødlossing Nødlossepakke for
bunkersoljer
1 stk
Kystverket Ålesund Pumper 20 Elro slangepumpe Bensindrevet. 1 stk
Kystverket Ålesund Båt Arbeids/insp.båt
T650KYV 22ft
1 stk
Kystverket Ålesund Båt/flåte GB Cat
arbeidkatamaran m/
kran
1 stk
Kystverket Ålesund Kjøretøy Jungheinrich EFG
216. El drift
1 stk
Kystverket Ålesund Kjøretøy Løfteåk for gaffeltruck 1 stk
Kystverket Ålesund Kjøretøy Caterpillar V140
Diesel. 6,5t
1 stk
Kystverket Ålesund Diesel Hydraulikk 39kwF Henriksen 150-110-D
39kW Fast
1 stk
Kystverket Ålesund Diesel Hydraulikk Lamor LPP-35L
35kW Fast
1 stk
Kystverket Ålesund Diesel Hydraulikk Rexroth 50kW Fast 1 stk
Kystverket Ålesund Oljecontainer 25m3 Unibag Oilbag 1 stk
Kystverket Ålesund Diverse Karmkasse, liten 3 stk
Kystverket Ålesund Diverse Prøvetakingskoffert 1 stk
Kystverket Ålesund Diverse Expandi
Pakkemanskin
for EP 4300 1 stk
Kystverket Ålesund Strandrens Akuttfase Strand -
Container 1
10-fots akuttfase
strandutstyr
1 stk
Kystverket Ålesund Strandrens Akuttfase Strand -
Container 2
10-fots akuttfase
strandutstyr
1 stk
Kystverket Ålesund Strandrens Akuttfase Strand -
Container 3
10-fots akuttfase
strandutstyr
1 stk
Kystverket Ålesund Strandrens Akuttfase Strand -
Container 4
10-fots akuttfase
strandutstyr
1 stk
Kystverket Ålesund Strandrens Barkspreder Foxblower 1 stk
Kystverket Ålesund Strandrens Barkspreder Melbu Oilfighter 2 stk
Kystverket Ålesund Strandrens Nilfisk Alto. Dieseldrevet 1 stk
Kystverket Ålesund Strandrens Absorbent Oljebark 1000 sekker
Kystverket Florø Lenser-T/M Norlense NO-800R trommel i 10 fot
cont.
300m
Kystverket Florø Lenser-T/M Expandi 4300 152m på pall x4 608 m
Kystverket Florø Lenser-T/M NOFI 500EP 100m i
container
200m
Kystverket Florø Lenser-T/M 10m3
tank
Current Buster 4 10' container m.
paravan
1 stk
Kystverket Florø Lette lenser 5m3 tank Current Buster 2 10' container m.
paravan
1 stk
Kystverket Florø Lette lenser NOFI 350 EP 4x25m i pakkramme 300m
Kystverket Florø Absorberende lenser Abs. lense med skjørt 1000 m
Kystverket Florø Absorberende lenser Abs. lense uten skjørt 400 m
Kystverket Florø Oljeopptagere Foxtail VAB 8-14 Adhesjon 1 stk
Kystverket Florø Oljeopptagere 30 Foxtail VAB 4-9 Adhesjon 1 stk
Kystverket Florø Oljeopptagere Foxtail VAB 2-6 Adhesjon 1 stk
Kystverket Florø Oljeopptagere KLK 602 Foxdrum i
pakkramme
Trommelskimmer 1 stk
109
Kystverket Florø Oljeopptagere Lamor LWS 500 m/
børste/skive
Multiskimmer 1 stk
Kystverket Florø Pumper 20 Elro slangepumpe Bensindrevet. 1 stk
Kystverket Florø Pumper Rabbit P265
Brannpumpe
1 stk
Kystverket Florø Kjøretøy Toyota 7FBMF25.
El.drift. 2,5t
1 stk
Kystverket Florø Kjøretøy Løfteåk for gaffeltruck 1 stk
Kystverket Florø Diesel Hydraulikk Henriksen 150-110-D
39kW Fast
1 stk
Kystverket Florø Diesel Hydraulikk Henriksen 150-200-D
53kW Fast
1 stk
Kystverket Florø Diesel Hydraulikk Henriksen 150-75-D
26kW Fast
1 stk
Kystverket Florø Diesel Hydraulikk Rexroth 50kW Fast 1 stk
Kystverket Florø Diesel Hydraulikk Lamor LPP-35L
35kW Fast
1 stk
Kystverket Florø Oljecontainer 10m3 RO-Tank Desmi 2 stk
Kystverket Florø Båt Arbeids/insp.båt Rana
20ft
påhengsmotor 1 stk
Kystverket Florø Båt GB Cat
arbeidkatamaran m/
kran
1 stk
Kystverket Florø Diverse Dregger: 5x36kg,
5x25m tau
5 stk
Kystverket Florø Diverse Karmkasse, liten 3 stk
Kystverket Florø Diverse Prøvetakingskoffert 1 stk
Kystverket Florø Diverse Expandi
Pakkemanskin
for EP 4300 1 stk
Kystverket Florø Diverse Mooring 500kg 6 stk
Kystverket Florø Strandrens Akuttfase Strand -
Container 1
10-fots akuttfase
strandutstyr
1 stk
Kystverket Florø Strandrens Akuttfase Strand -
Container 2
10-fots akuttfase
strandutstyr
1 stk
Kystverket Florø Strandrens Akuttfase Strand -
Container 3
10-fots akuttfase
strandutstyr
1 stk
Kystverket Florø Strandrens Akuttfase Strand -
Container 4
10-fots akuttfase
strandutstyr
1 stk
Kystverket Florø Strandrens Barkspreder Foxblower 1 stk
Kystverket Florø Strandrens Barkspreder Melbu Oilfighter 2 stk
Kystverket Florø Strandrens Nilfisk Alto. Dieseldrevet 1 stk
Kystverket Florø Strandrens Absorbent Oljebark 1000 sekker
Kystverket Florø Strømaggregat Honda E2500
Bensindrevet
2 stk
Kystverket Florø Strømaggregat Loncin LC3800DC
Bensindrevet
2 stk
Kystverket Solund Lenser-T/M NOFI 500EP 100m i
container
300m
Kystverket Solund Lenser-T/M Expandi 4300 selvoppblåsende,
152mx5
760 m
Kystverket Solund Lenser-T/M Current Buster 4 10' container m.
paravan
1 stk
Kystverket Solund Lette lenser Current Buster 2 10' container m.
paravan
1 stk
Kystverket Solund Lette lenser NOFI 350EP 4x25m i pakkramme 300 m
Kystverket Solund absorberende lenser med skjørt 1000 m
110
Kystverket Solund absorberende lenser uten skjørt 225 m
Kystverket Solund Oljeopptagere KLK 602 / Foxdrum
m/ trsp.cont
Trommelskimmer 1 stk
Kystverket Solund Oljeopptagere Lamor LWS 500 m/
børste/skive
Multiskimmer 1 stk
Kystverket Solund Oljeopptagere Foxtail VAB 4-9 Adhesjon 1 stk
Kystverket Solund Oljeopptagere 9 Foxtail VAB 2-6 Adhesjon 1 stk
Kystverket Solund Pumper Rabbit P265
Brannpumpe
1 stk
Kystverket Solund Pumper 20 Elro slangepumpe Bensindrevet. 1 stk
Kystverket Solund Båt Arbeids/insp.båt Rana
20ft
1 stk
Kystverket Solund Kjøretøy Toyota 7FBMF25.
El.drift. 2,5t
1 stk
Kystverket Solund Kjøretøy Løfteåk for gaffeltruck 1 stk
Kystverket Solund Kjøretøy Caterpillar V140
Diesel. 6,5t
1 stk
Kystverket Solund Diesel Hydraulikk 39kwF Henriksen 150-110-D
39kW Fast
1 stk
Kystverket Solund Diesel Hydraulikk Lamor LPP-35L
35kW Fast
1 stk
Kystverket Solund Diesel Hydraulikk Rexroth 50kW Fast 1 stk
Kystverket Solund Diesel Hydraulikk Henriksen 150-75-D
26kW Fast
1 stk
Kystverket Solund Strømaggregat Honda E2500
Bensindrevet
1 stk
Kystverket Solund Oljecontainer 10m3 Desmi RO-tank 2 stk
Kystverket Solund Oljecontainer 25m3 Unibag Oilbag 1 stk
Kystverket Solund Diverse Karmkasse, liten 3 stk
Kystverket Solund Diverse Prøvetakingskoffert 1 stk
Kystverket Solund Diverse Expandi
Pakkemanskin
for EP 4300 1 stk
Kystverket Solund Diverse Mooring 500kg 4 stk
Kystverket Solund Diverse Dregger: 5x36kg,
5x25m tau
5 sett
Kystverket Solund Strandrens Akuttfase Strand -
Container 1
10-fots akuttfase
strandutstyr
1 stk
Kystverket Solund Strandrens Akuttfase Strand -
Container 2
10-fots akuttfase
strandutstyr
1 stk
Kystverket Solund Strandrens Akuttfase Strand -
Container 3
10-fots akuttfase
strandutstyr
1 stk
Kystverket Solund Strandrens Akuttfase Strand -
Container 4
10-fots akuttfase
strandutstyr
1 stk
Kystverket Solund Strandrens Barkspreder Foxblower 1 stk
Kystverket Solund Strandrens Barkspreder Melbu Oilfighter 2 stk
Kystverket Solund Strandrens Nilfisk Alto. Dieseldrevet 1 stk
Kystverket Solund Strandrens Absorbent Oljebark 1000 sekker
Kystverket Fedje Lenser-T/M NO-600 S 300m på trommel 300m
Kystverket Fedje Lenser-T/M Expandi 4300 152m på pall x4 608 m
Kystverket Fedje Lenser-T/M NO-600 S 200m på
trommel
på trommel 400m
Kystverket Fedje Lenser-T/M 10m3
tank
Current Buster 4 10' container m.
paravan
1 stk
111
Kystverket Fedje Lette lenser 5m3 tank Current Buster 2 10' container m.
paravan
1 stk
Kystverket Fedje Lette lenser NOFI 350 EP 4x25m i pakkramme 600m
Kystverket Fedje Absorberende lenser Abs. lense med skjørt 1000 m
Kystverket Fedje Absorberende lenser Abs. lense uten skjørt 400 m
Kystverket Fedje Oljeopptagere NorMar30 Overløpsskimmer 1 stk
Kystverket Fedje Oljeopptagere 30 Foxtail VAB 4-9 Adhesjon 3 stk
Kystverket Fedje Oljeopptagere KLK 402/Foxdrum i
pakkramme
Trommelskimmer 1 stk
Kystverket Fedje Oljeopptagere Lamor LWS 500 m/
børste/skive
Multiskimmer 1 stk
Kystverket Fedje Kjøretøy Toyota 7FBMF25.
El.drift. 2,5t
1 stk
Kystverket Fedje Kjøretøy Løfteåk for gaffeltruck 1 stk
Kystverket Fedje Diesel Hydraulikk Henriksen 150-110-D
39kW Fast
1 stk
Kystverket Fedje Diesel Hydraulikk Henriksen 150-200-D
53kW Fast
1 stk
Kystverket Fedje Diesel Hydraulikk Henriksen 120-60-D 26
kW Fast
1 stk
Kystverket Fedje Diesel Hydraulikk Henriksen 140-90-D
26kW Fast
1 stk
Kystverket Fedje Oljecontainer 10m3 RO-Tank Desmi 1 stk
Kystverket Fedje Båt Arbeids/insp.båt Rana
20ft
påhengsmotor 1 stk
Kystverket Fedje Diverse Dregger: 5x36kg,
5x25m tau
9 stk
Kystverket Fedje Diverse Karmkasse, liten 3 stk
Kystverket Fedje Diverse Prøvetakingskoffert 1 stk
Kystverket Fedje Diverse Expandi
Pakkemanskin
for EP 4300 1 stk
Kystverket Fedje Strandrens Akuttfase Strand -
Container 1
10-fots akuttfase
strandutstyr
1 stk
Kystverket Fedje Strandrens Akuttfase Strand -
Container 2
10-fots akuttfase
strandutstyr
1 stk
Kystverket Fedje Strandrens Akuttfase Strand -
Container 3
10-fots akuttfase
strandutstyr
1 stk
Kystverket Fedje Strandrens Akuttfase Strand -
Container 4
10-fots akuttfase
strandutstyr
1 stk
Kystverket Fedje Strandrens Barkspreder Foxblower 1 stk
Kystverket Fedje Strandrens Barkspreder Melbu Oilfighter 2 stk
Kystverket Fedje Strandrens Nilfisk Alto. Dieseldrevet 1 stk
Kystverket Fedje Strandrens Absorbent Oljebark 1000 sekker
Kystverket Bergen Lenser-T/M Norlense NO-800R på trommel m/ 10 fot
cont
600m
Kystverket Bergen Lenser-T/M NO 450S. 200m på trommel 200m
Kystverket Bergen Lenser-T/M Expandi 4300 selvoppblåsende,
152mx3
456m
Kystverket Bergen Lenser-T/M Current Buster 6, tung 10' container m.
paravan
1 stk
Kystverket Bergen Lette lenser Current Buster 2 10' container m.
paravan
1 stk
Kystverket Bergen Lette lenser NOFI 350EP 4x25m i pakkramme 300m
Kystverket Bergen absorberende lenser med skjørt 1000m
112
Kystverket Bergen absorberende lenser uten skjørt 25m
Kystverket Bergen Oljeopptagere KLK402 Foxdrum i
pakkramme
Trommel 2 stk
Kystverket Bergen Oljeopptagere KLK 602 / Foxdrum
m/ trsp.cont
Trommelskimmer 1 stk
Kystverket Bergen Oljeopptagere Lamor LWS 500 m/
børste/skive
Multiskimmer 1 stk
Kystverket Bergen Oljeopptagere Desmi Terminator. Overløpsskimmer 1 stk
Kystverket Bergen Oljeopptagere 9 Foxtail VAB 2-6 Adhesjon 1 stk
Kystverket Bergen Pumper Rabbit P265
Brannpumpe
1 stk
Kystverket Bergen Pumper 20 Elro slangepumpe Bensindrevet. 1 stk
Kystverket Bergen Båt Arbeids/insp.båt Rana
20ft
1 stk
Kystverket Bergen Båt/flåte GB Cat
arbeidkatamaran m/
kran
1 stk
Kystverket Bergen Kjøretøy Henriksen 120-50-D
19kW
1 stk
Kystverket Bergen Kjøretøy Løfteåk for gaffeltruck 1 stk
Kystverket Bergen Diesel Hydraulikk 39kwF Henriksen 150-110-D
39kW Fast
1 stk
Kystverket Bergen Diesel Hydraulikk Henriksen 120-50-D
19kW
1 stk
Kystverket Bergen Diesel Hydraulikk Rexroth 50kW Fast 1 stk
Kystverket Bergen Strømaggregat Honda E2500
Bensindrevet
1 stk
Kystverket Bergen Oljecontainer 10m3 Desmi RO-tank
10kbm
2 stk
Kystverket Bergen Oljecontainer 25m3 Unibag Oilbag 1 stk
Kystverket Bergen Diverse Karmkasse, liten 3 stk
Kystverket Bergen Diverse Prøvetakingskoffert 1 stk
Kystverket Bergen Diverse Expandi
Pakkemanskin
for EP 4300 1 stk
Kystverket Bergen Diverse Dregger: 5x36kg,
5x25m tau
5 stk
Kystverket Bergen Diverse Grabb for operasjon i
kran
1 stk
Kystverket Bergen Strandrens Akuttfase Strand -
Container 1
10-fots akuttfase
strandutstyr
1 stk
Kystverket Bergen Strandrens Akuttfase Strand -
Container 2
10-fots akuttfase
strandutstyr
1 stk
Kystverket Bergen Strandrens Akuttfase Strand -
Container 3
10-fots akuttfase
strandutstyr
1 stk
Kystverket Bergen Strandrens Akuttfase Strand -
Container 4
10-fots akuttfase
strandutstyr
1 stk
Kystverket Bergen Strandrens Barkspreder Foxblower 1 stk
Kystverket Bergen Strandrens Barkspreder Melbu Oilfighter 2 stk
Kystverket Bergen Strandrens Nilfisk Alto. Dieseldrevet 1 stk
Kystverket Bergen Strandrens Absorbent Oljebark 1000 sekker
Kystverket
Stavanger
Lenser-T/M Expandi 4300 selvoppblåsende,
152mx9
1368 m
Kystverket
Stavanger
Lenser-T/M NO 450S. 200m på
trommel
på trommel 200m
Kystverket
Stavanger
Lenser-T/M Uniboom A-1300HD
100m
400 m
113
Kystverket
Stavanger
Lenser-T/M Current Buster 4 10' container m.
paravan
1 stk
Kystverket
Stavanger
Lette lenser Current Buster 2 10' container m.
paravan
1 stk
Kystverket
Stavanger
Lette lenser NOFI 350EP 4x25m i pakkramme 300m
Kystverket
Stavanger
absorberende lenser med skjørt 1000m
Kystverket
Stavanger
absorberende lenser uten skjørt 50 m
Kystverket
Stavanger
Oljeopptagere KLK402 Foxdrum i
pakkramme
Trommel 3 stk
Kystverket
Stavanger
Oljeopptagere KLK 602, Dbl
pakkramme
Trommelskimmer 1 stk
Kystverket
Stavanger
Oljeopptagere Desmi Termite.
Overløp
Overløpskimmer 1 stk
Kystverket
Stavanger
Oljeopptagere Lamor LWS 500 m/
børste/skive
Multiskimmer 1 stk
Kystverket
Stavanger
Oljeopptagere Foxtail VAB 2-9 Adhesjon 1 stk
Kystverket
Stavanger
Nødlossing Nødlossepakke for
bunkersoljer
1 stk
Kystverket
Stavanger
Pumper Rabbit P265
Brannpumpe
1 stk
Kystverket
Stavanger
Båt Arbeids/insp.båt Rana
20ft
1 stk
Kystverket
Stavanger
Kjøretøy Toyota 7FBMF25.
El.drift. 2,5t
1 stk
Kystverket
Stavanger
Kjøretøy Løfteåk for gaffeltruck 1 stk
Kystverket
Stavanger
Strømaggregat Honda E2500
Bensindrevet
Diesel Hydraulikk 1 stk
Kystverket
Stavanger
Diesel Hydraulikk 39kwF Henriksen 150-110-D
39kW Fast
1 stk
Kystverket
Stavanger
Diesel Hydraulikk Henriksen 120-60-D 26
kW Fast
1 stk
Kystverket
Stavanger
Diesel Hydraulikk Lamor LPP-35L
35kW Fast
1 stk
Kystverket
Stavanger
Oljecontainer Desmi RO-tank
10kbm
2 stk
Kystverket
Stavanger
Oljecontainer NOFI oljelekter
25kbm
1 stk
Kystverket
Stavanger
Diverse Karmkasse, liten 3 stk
Kystverket
Stavanger
Diverse Prøvetakingskoffert 1 stk
Kystverket
Stavanger
Diverse Expandi
Pakkemanskin
for EP 4300 1 stk
Kystverket
Stavanger
Strandrens Akuttfase Strand -
Container 1
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Stavanger
Strandrens Akuttfase Strand -
Container 2
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Stavanger
Strandrens Akuttfase Strand -
Container 3
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Stavanger
Strandrens Akuttfase Strand -
Container 4
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Stavanger
Strandrens Barkspreder Foxblower 1 stk
Kystverket
Stavanger
Strandrens Barkspreder Melbu Oilfighter 2 stk
Kystverket
Stavanger
Strandrens Nilfisk Alto. Dieseldrevet 1 stk
Kystverket Strandrens Absorbent Oljebark 1000 sekker
114
Stavanger
Kystverket
Kristiansand
Lenser-T/M Norlense NO-800R på trommel m/ 10 fot
cont
300m
Kystverket
Kristiansand
Lenser-T/M Expandi 4300 selvoppblåsende,
152mx5
760m
Kystverket
Kristiansand
Lenser-T/M Current Buster 4 10' container m.
paravan
1 stk
Kystverket
Kristiansand
Lette lenser Current Buster 2 10' container m.
paravan
1 stk
Kystverket
Kristiansand
Lette lenser NOFI 350EP 4x25m i pakkramme 300m
Kystverket
Kristiansand
absorberende lenser med skjørt 1000m
Kystverket
Kristiansand
absorberende lenser uten skjørt 50 m
Kystverket
Kristiansand
Oljeopptagere KLK402 Foxdrum i
pakkramme
Trommel 1 stk
Kystverket
Kristiansand
Oljeopptagere KLK 602 / Foxdrum
m/ trsp.cont
Trommelskimmer 1 stk
Kystverket
Kristiansand
Oljeopptagere 65 Desmi Terminator.
Skive/børste
multiskimmer 1 stk
Kystverket
Kristiansand
Oljeopptagere Lamor LWS 500 m/
børste/skive
Multiskimmer 1 stk
Kystverket
Kristiansand
Oljeopptagere Foxtail VAB 4-9 i
trans.kont.
Adhesjon 1 stk
Kystverket
Kristiansand
Oljeopptagere 9 Foxtail VAB 2-6 i
transp. Kont.
Adhesjon 2 stk
Kystverket
Kristiansand
Pumper Eksenterskruepumpe 1 stk
Kystverket
Kristiansand
Pumper Rabbit P265
Brannpumpe
1 stk
Kystverket
Kristiansand
Pumper 20 Elro slangepumpe Bensindrevet. 1 stk
Kystverket
Kristiansand
Båt Arbeids/insp.båt Rana
20ft
1 stk
Kystverket
Kristiansand
Båt GB Cat
arbeidkatamaran m/
kran
1 stk
Kystverket
Kristiansand
Kjøretøy Toyota 7FBMF25.
El.drift. 2,5t
1 stk
Kystverket
Kristiansand
Kjøretøy Caterpillar V140
Diesel. 6,5t
1 stk
Kystverket
Kristiansand
Kjøretøy Løfteåk for gaffeltruck 1 stk
Kystverket
Kristiansand
Strømaggregat Honda E2500
Bensindrevet
1 stk
Kystverket
Kristiansand
Strømaggregat Loncin LC3800DC
Bensindrevet
1 stk
Kystverket
Kristiansand
Diesel Hydraulikk 39kwF Henriksen 150-110-D
39kW Fast
1 stk
Kystverket
Kristiansand
Diesel Hydraulikk Henriksen 120-60-D 26
kW Fast
1 stk
Kystverket
Kristiansand
Diesel Hydraulikk 39kwF Henriksen 150-200-D
53kW Fast
1 stk
Kystverket
Kristiansand
Diesel Hydraulikk Lamor LPP-35L
35kW Fast
1 stk
Kystverket
Kristiansand
Diesel Hydraulikk Markleen DHPP
60kW
1 stk
Kystverket
Kristiansand
Oljecontainer Desmi RO-tank
10kbm
2 stk
Kystverket Oljecontainer 25m3 Unibag Oilbag 1 stk
115
Kristiansand
Kystverket
Kristiansand
Diverse Karmkasse, liten 3 stk
Kystverket
Kristiansand
Diverse Prøvetakingskoffert 1 stk
Kystverket
Kristiansand
Diverse Expandi
Pakkemanskin
for EP 4300 1 stk
Kystverket
Kristiansand
Strandrens Akuttfase Strand -
Container 1
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Kristiansand
Strandrens Akuttfase Strand -
Container 2
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Kristiansand
Strandrens Akuttfase Strand -
Container 3
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Kristiansand
Strandrens Akuttfase Strand -
Container 4
10-fots akuttfase
strandutstyr
1 stk
Kystverket
Kristiansand
Strandrens Barkspreder Foxblower 1 stk
Kystverket
Kristiansand
Strandrens Nilfisk Alto. Dieseldrevet 1 stk
Kystverket
Kristiansand
Strandrens Absorbent Oljebark 1000 sekker
Kystverket Horten Lenser-T/M Expandi 4300
152mx10
selvoppblåsende på
pall
1520m
Kystverket Horten Lenser-T/M NOFI 500EP 1x25m i pakkramme 100m
Kystverket Horten Lenser-T/M NOFI 500EP 100m i container 400m
Kystverket Horten Lenser-T/M NO 450S. 200m på trommel 200m
Kystverket Horten Lenser-T/M NO 800R 300m på
trommel
300m
Kystverket Horten Lenser-T/M Current Buster 4 10' container m.
paravan
1 stk
Kystverket Horten Lenser-T/M Current Buster 2 10' container m.
paravan
1 stk
Kystverket Horten Lette lenser NOFI 350EP 4x25m i
pakkramme
400m
Kystverket Horten Absorberende lense med skjørt 1000m
Kystverket Horten Nødlossing Nødlossepakke for
bunkersoljer
1 stk
Kystverket Horten Oljeopptagere Uniskim
Multiskimmer 30
1 stk
Kystverket Horten Oljeopptagere Lamor Minimax 40. 1 stk
Kystverket Horten Oljeopptagere NorMar 30
Børstekonfigurasjon
1 stk
Kystverket Horten Oljeopptagere KLK 402/Foxdrum i
pakkramme
2 stk
Kystverket Horten Oljeopptagere KLK 602 / Foxdrum
m/ trsp.cont
1 stk
Kystverket Horten Oljeopptagere Foilex TDS200 1 stk
Kystverket Horten Oljeopptagere Lamor LWS 500 m/
børste/skive
1 stk
Kystverket Horten Oljeopptagere Desmi Terminator.
Belte
1 stk
Kystverket Horten Oljeopptagere Normar mini
skive/børste
1 stk
Kystverket Horten Oljeopptagere Foxtail VAB 8-14 i
trsp.cont
5 stk
Kystverket Horten Oljeopptagere Foxtail VAB 4-9 i
trsp.cont
2 stk
Kystverket Horten Oljeopptagere Foxtail VAB 2-9 i
trsp.cont
1 stk
116
Kystverket Horten Oljeopptagere Foxtail VAB 2-6 i
trsp.cont
3 stykk
Kystverket Horten Oljeopptagere Sandvik Bånd
Opptaker
1 stk
Kystverket Horten Pumper Honda WB20XT
Spylepumpe
2 stk
Kystverket Horten Pumper Rabbit P265
Brannpumpe
1 stk
Kystverket Horten Pumper 20 Elro slangepumpe Bensindrevet. 2 stk
Kystverket Horten pumpe Exenterpumpe
Wangen
Hydraulikkdrevet 1 stk
Kystverket Horten Pumper Rekord/Vogelsang R60 1 stk
Kystverket Horten Diesel Hydraulikk Henriksen 150-150-D
V 39kW
1 stk
Kystverket Horten Diesel Hydraulikk Henriksen 150-110-D
39kW Fast
2stk
Kystverket Horten Diesel Hydraulikk Henriksen 150-200-D
53kW Fast
1 stk
Kystverket Horten Diesel Hydraulikk Lamor LPP-35L
35kW Fast
1 stk
Kystverket Horten Diesel Hydraulikk Rexroth 50kW Fast 1 stk
Kystverket Horten Kjøretøy Doosan B18T-5.
Elektrisk drift
1 stk
Kystverket Horten Kjøretøy Kaldnes H10-600V.
Dieseldrevet
1 stk
Kystverket Horten Kjøretøy Løfteåk for gaffeltruck 1 stk
Kystverket Horten Strømaggregat Honda E2500
Bensindrevet
1 stk
Kystverket Horten Strømaggregat Honda 4500
Bensindrevet
1 stk
Kystverket Horten Strømaggregat Loncin LC3800DC
Bensindrevet
1 stk
Kystverket Horten Oljecontainer 10kbm Desmi RO-tank 1 stk
Kystverket Horten Oljecontainer 25kbm Unibag / Oilbag 1 stk
Kystverket Horten Oljecontainer 25 NOFI oljelekter
25kbm
1 stk
Kystverket Horten Båt Alubåt NOR-SUB 20ft påhengsmotor 1 stk
Kystverket Horten Båt GB Cat
arbeidkatamaran m/
kran
Flåte med kran 1 stk
Kystverket Horten Båt Malo 30'
"Borregutten"
1 stk
Kystverket Horten Båt Arbeids/insp.båt
T650KYV 22ft
3 stk
Kystverket Horten Båt GroEva 9m arbeidsbåt 1 stk
Kystverket Horten Båt Sea hunter.
Arbeidsbåt/flåte
1 stk
Kystverket Horten Diverse Oppankringsutstyr Dregger, 5x36kg
m/5x25m tau
12 sett
Kystverket Horten Diverse Karmkasse, liten 3 stykk
Kystverket Horten Diverse Prøvetakingskoffert 9 stykk
Kystverket Horten Diverse Expandi
Pakkemanskin
for EP 4300 2 stykk
Kystverket Horten Diverse Grabb for operasjon i
kran
1 stykk
Kystverket Horten Strandrens Akuttfase Strand -
Container 1
10-fots akuttfase
strandutstyr
1 stykk
Kystverket Horten Strandrens Akuttfase Strand -
Container 2
10-fots akuttfase
strandutstyr
1 stykk
117
Kystverket Horten Strandrens Akuttfase Strand -
Container 3
10-fots akuttfase
strandutstyr
1 stykk
Kystverket Horten Strandrens Akuttfase Strand -
Container 4
10-fots akuttfase
strandutstyr
1 stykk
Kystverket Horten Strandrens Barkspreder Foxblower 2 stykk
Kystverket Horten Strandrens Barkspreder Melbu Oilfighter 2 stykk
Kystverket Horten Strandrens Nilfisk Alto. Dieseldrevet 1 stykk
Kystverket Horten Strandrens Absorbent Oljebark 1000 sekker
Kystverket Horten Strandrens Mose Barkbørste og -
suger
1 stykk
Kystverket Horten Strandrens Bekledningscontainer
20ft
1 stykk
NOFO Hammerfest Tunge lenser NOFO system 6
NOFO Hammerfest Mellomtunge lenser Current Buster 4 m/Paravan 3
NOFO Hammerfest Dispergeringsmiddel Dascic Slickgone NS 53m3
NOFO
Sandnessjøen
Tunge lenser NOFO system 1
NOFO
Sandnessjøen
Mellomtunge lenser Current Buster 4 m/Paravan 3
NOFO
Sandnessjøen
Dispergeringsmiddel
NOFO
Kristiansund
Tunge lenser NOFO system 2
NOFO
Kristiansund
Mellomtunge lenser Current Buster 4 m/Paravan 3
NOFO
Kristiansund
Dispergeringsmiddel Dascic Slickgone NS 52m3
NOFO Mongstad Tunge lenser NOFO system 2
NOFO Mongstad Mellomtunge lenser Current Buster 4 3
NOFO Mongstad Dispergeringsmiddel Dascic Slickgone NS 70m3
NOFO Stavanger Tunge lenser NOFO system 2
NOFO Stavanger Mellomtunge lenser Current Buster 4 m/Paravan 3
NOFO Stavanger Dispergeringsmiddel Dascic Slickgone NS 92m3
OB Haltenbanken Tunge lenser NOFO system 1
OB Haltenbanken Dispergeringsmiddel Dascic Slickgone NS 52m3
Barentshavet NOFO system NOFO system 1
Barentshavet Dispergeringsmiddel Dascic Slickgone NS 50m3
Hammerfest Dispergeringsmiddel Dascic Slickgone NS 50m3
Gjøa Tunge lenser NOFO system 1
Gjøa Dispergeringsmiddel Dascic Slickgone NS 45m3
Statoil
Avløserfartøy
Tunge lenser NOFO system 1
Statoil
Avløserfartøy
Dispergeringsmiddel Dascic Slickgone NS 33m3
Tampen Tunge lenser NOFO system 1
Tampen Dispergeringsmiddel Dascic Slickgone NS 62m3
Troll-Oseberg II Tunge lenser NOFO system
Troll-Oseberg II Dispergeringsmiddel Dascic Slickgone NS 48,5m3
118
Troll-Oseberg I Tunge lenser NOFO system
Troll-Oseberg I Dispergeringsmiddel Dascic Slickgone NS 46m3
OB Balder Tunge lenser NOFO system 1
OB Balder Dispergeringsmiddel Dascic Slickgone NS 60m3
Sleipner/Volve Tunge lenser NOFO system 1
ULA/Gyda/Tamber Tunge lenser NOFO system 1
ULA/Gyda/Tamber Dispergeringsmiddel Dascic Slickgone NS 33m3
Ekofisk Tunge lenser NOFO system 1
Stavanger Dispergeringsmiddel Dascic Slickgone NS 18m3
Resources at Bear Island
Depot Utstyrsbetegnelse Kapasitet Utstyrstype Utsyrsundertype Antal
l
Bjørnøya
meteorologiske
stasjon
Båt 25 hk motor. 6 hk
reservemotor.
Rana 17 fot. 1
Bjørnøya
meteorologiske
stasjon
Båt «posebåt»/«dorry for å slepe flåte 1
Bjørnøya
meteorologiske
stasjon
Flåte 3,5x6,5 meter. Tar 5-6
tonn.
1
Bjørnøya
meteorologiske
stasjon
Transportmiddel,
land
Traktor Ford 4630, 1994
mod.
1
Bjørnøya
meteorologiske
stasjon
Transportmiddel,
land
Traktor John Deere,
5090, 2012 mod.
1
Bjørnøya
meteorologiske
stasjon
Lastekapasitet, land enakslet henger
med tipp
1
Bjørnøya
meteorologiske
stasjon
Transportmiddel,
land
Scooter med slede Polaris 2
Bjørnøya
meteorologiske
stasjon
Kran på kai 3 tonn på 8 meter 1
Bjørnøya
meteorologiske
stasjon
Kai Ved kai er dybdene,
innerst 2M og ytterst
3,5M ved flo. 1,5M
mindre ved fjære
1
Bjørnøya
meteorologiske
stasjon
Helikopter i hangar 1
Bjørnøya
meteorologiske
stasjon
bensin 90 m3 Helifuelanlegg 6 x 15 m3 tanker 1
Bjørnøya
meteorologiske
stasjon
overnattingskapasiti
t
21 stk (+ 9 fast stasjonert
på øya)
119
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