OMV BEREDSKAPSPLANLEGGING BJØRNØYA …...OMV BEREDSKAPSPLANLEGGING BJØRNØYA Generic Oil Spill...

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

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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


6.4.2 Operating conditions and solutions 24

6.5 Dispersant application 25



6.6 In Situ burning 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


6.8.2 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


6.10.2 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.

http://en.wikipedia.org/wiki/Norway

http://en.wikipedia.org/wiki/Svalbard

http://en.wikipedia.org/wiki/Spitsbergen

http://en.wikipedia.org/wiki/North_Cape,_Norway


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

http://www.kystverket.no/

http://www.nofo.no/

http://www.ptil.no/


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)


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.


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


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


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

http://en.wikipedia.org/wiki/Spitsbergen

http://en.wikipedia.org/wiki/Ing%C3%B8y

http://en.wikipedia.org/wiki/Meteorological_station

http://en.wikipedia.org/wiki/Willem_Barents

http://en.wikipedia.org/wiki/Spitsbergen_Treaty


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.

http://kart.kystverket.no/


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).


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


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)


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)


Figure ‎5-7 Ice extent in winter season


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.

http://en.wikipedia.org/wiki/Norwegian_language

http://en.wikipedia.org/wiki/Sysselmann

http://en.wikipedia.org/wiki/Norway

http://en.wikipedia.org/wiki/Government_of_Norway

http://en.wikipedia.org/wiki/Sovereignty

http://en.wikipedia.org/wiki/Norwegian_Ministry_of_Justice_and_the_Police

http://en.wikipedia.org/wiki/Environmental_protection


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.


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.


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


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


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


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


6.4 Mechanical recovery


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.


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


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.


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.


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


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


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.



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.


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.


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


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.


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.


6.8 Near-shore and shoreline response


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


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.


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.


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)


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


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,


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)


6.10 Logistics and support


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)


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.


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


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


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:


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.


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


10. APPENDIX


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).


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).


Bilde 3 Hamnevika (DNV GL).


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).


Sted/lokasjon

2. Området mellom Kapp Kåre og Kapp Ruth


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.


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).


Bilde 8 Huler i Ærfuglvika (DNV GL).

Bilde 9 Ærfuglvika (flyfoto: NP).


Bilde 10 MS Maursund i Ærfuglvika (DNV GL).

Bilde 11 Strand, Ærfuglvika (DNV GL).


Sted/lokasjon

3. Kapp Ruth - Grunnbukta – Kapp Hanna


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).


Bilde 13 Grunnbukta, mot Kapp Ruth (DNV GL).

Bilde 14 Grunnbukta (DNV GL).


Bilde 15 Deler av Grunnbukta (flyfoto: NP).


Sted/lokasjon

4. Kapp Hanna – Kapp Elisabeth inkludert Langbukta


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).


Bilde 17 Stapper i sjø ved Holmengrå (flyfoto: NP).


Bilde 18 Knorten (DNV GL).

Bilde 19 MS Maursund nært land, Knorten (DNV GL).


Sted/lokasjon

5. Kapp Elisabeth – Grytvika (inkl. Kapp Dunèr)


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.


Bilde 20 Kapp Elisabeth (flyfoto: NP).

Bilde 21 Vernevågen (flyfoto: NP).


Bilde 22 Kapp Dunèr sett fra Teltvika (DNV GL).

Bilde 23 Teltvika, MS Maursund går så nært land som mulig (DNV GL).


Bilde 24 Adkomstpunkter ved Kapp Dunèr, tilgjengelig for lettbåt (flyfoto: NP).


Sted/lokasjon

6. Matholmane – Snyta (Amfiet og Drangane)


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.


Bilde 25 Adkomstpunkter ved Amfiet (flyfoto: NP).


Bilde 26 Amfiet (DNV GL).

Bilde 27 Klippevegger nær Amfiet (DNV GL).


Sted/lokasjon

7. Snyta – Emmaholmane (inkl. Kobbebukta)


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).


Bilde 29 Kobbebukta sett fra sjøsiden (DNV GL).


Bilde 30 Emmaholmane, del av Kapp Kjellström og deler av Kobbebukta (strand). Hele bukta er merket

som mulig adkomstpunkt (flyfoto: NP).


Sted/lokasjon

8. Kapp Kjellstrøm – Gravodden (Nordhamna og Kvalrossfjæra)


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).


Bilde 32 Kvalrossfjæra og Gravodden. Hele Kvalrossfjæra er merket med adkomstpunkter (flyfoto: NP).


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.


Bilde 33 Meteorologisk stasjon, Herwighamna, adkomstpunkt (flyfoto (NP)

Bilde 34Meterologisk stasjon sett fra sjø, Herwighamna (DNV GL).


Bilde 35 MS Maursund inn mot molo i Herwighamna (DNV GL).

Bilde 36 Molo og fjære ved Herwighamna (DNV GL).


Sted/lokasjon

10. Padda (fra Herwighamna til Nordkapp).


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).


Sted/lokasjon

11. Nordkapp - Måkestauren


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).


Bilde 39 Sandstrand innerst ved Skrattskjer (flyfoto: NP).


Sted/lokasjon

12. Kapp Forsberg – Kapp Bergersen


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).


Bilde 41 Silodden sett fra sjø (DNV GL).


Bilde 42 Silodden, spor etter gruvedrift. Tidligere benyttet som lastehavn. Mulig for LGF ved rolig sjø

(flyfoto: NP).


Sted/lokasjon

13. Kapp Bergersen – Kapp Nordenskiöld


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.


Bilde 43 Adkomstpunkter ved Kapp Nordenskiöld, blått punkt merker adkomstmulighet for LGF (flyfoto: NP).

Bilde 44 Adkomstmulighet for LGF ved kapp Nordenskiöld (DNV GL).


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)


Bilde 46 Adkomstpunkt ved Kapp Levin (flyfoto: NP)


Bilde 47 Adkomstpunkt ved Losbrotet, svært rasutsatt (flyfoto: NP)


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)


Bilde 49 MS Maursund på tur inn i Russehamna (DNV GL).

Bilde 50 Fjæra innerst i Russehamna (DNV GL).


Bilde 51 Hytte i Russehamna og stappe i sjø (DNV GL).

Bilde 52 Adkomstpunkt, Kvalrossbukta (flyfoto: NP)


Bilde 53 Nærbilde Kvalrossbukta, drivved (flyfoto: NP)


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


Bilde 54 Indre del av Sørhamna (flyfoto: NP)

Bilde 55 Smal strand og bratte klippevegger innerst i Sørhamna (flyfoto: NP)


10.2 ACUTE STRATEGY OIL SPILL RESPONSE (ASO)


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


Kystverket

Svalbard


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



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


Container 2

10-fots akuttfase

strandutstyr

1 stk


Container 3

10-fots akuttfase

strandutstyr

1 stk


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


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


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


Container 2

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Hammerfest


Container 3

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Hammerfest


Container 4

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Hammerfest


Kystverket

Hammerfest


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


Container 2

10-fots akuttfase

strandutstyr

1 stk


Container 3

10-fots akuttfase

strandutstyr

1 stk


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


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


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


Kystverket

Lødingen


pakkramme 1


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


Kystverket

Lødingen


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


m/5x25m tau

3 sett

Kystverket

Lødingen


Kystverket

Lødingen


Kystverket

Lødingen

Diverse Expandi

Pakkemanskin

for EP 4300 1 stk

104

Kystverket

Lødingen


Container 1

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Lødingen


Container 2

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Lødingen


Container 3

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Lødingen


Container 4

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Lødingen


Kystverket

Lødingen


Kystverket

Lødingen


Kystverket

Lødingen


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


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


Container 2

10-fots akuttfase

strandutstyr

1 stk


Container 3

10-fots akuttfase

strandutstyr

1 stk


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


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


børste/skive

Multiskimmer 1 stk

Kystverket

Sandnessjøen


transp.cont

Adhesjon 1 stk

Kystverket

Sandnessjøen


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


El.drift. 2,5t

1 stk

106

Kystverket

Sandnessjøen

Kjøretøy Toyota TC40 8

FD70N. Diesel

1 stk

Kystverket

Sandnessjøen


Kystverket

Sandnessjøen


Bensindrevet


Kystverket

Sandnessjøen

Diesel Hydraulikk Henriksen 120-60-D 26

kW Fast

1 stk

Kystverket

Sandnessjøen


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


m/5x25m tau

3 sett

Kystverket

Sandnessjøen


Kystverket

Sandnessjøen


Kystverket

Sandnessjøen

Diverse Expandi

Pakkemanskin

for EP 4300 1 stk

Kystverket

Sandnessjøen


Container 1

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Sandnessjøen


Container 2

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Sandnessjøen


Container 3

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Sandnessjøen


Container 4

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Sandnessjøen


Kystverket

Sandnessjøen


Kystverket

Sandnessjøen


Kystverket

Sandnessjøen


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


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


Kystverket Ørland Oljeopptagere KLK 402Foxdrum m/

trsp.cont


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


Container 3

10-fots akuttfase

strandutstyr

1 stk


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


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


Container 2

10-fots akuttfase

strandutstyr

1 stk


Container 3

10-fots akuttfase

strandutstyr

1 stk


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


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


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


53kW Fast

1 stk


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


Container 2

10-fots akuttfase

strandutstyr

1 stk


Container 3

10-fots akuttfase

strandutstyr

1 stk


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


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


Container 2

10-fots akuttfase

strandutstyr

1 stk


Container 3

10-fots akuttfase

strandutstyr

1 stk


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


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


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


53kW Fast

1 stk

Kystverket Fedje Diesel Hydraulikk Henriksen 120-60-D 26

kW Fast

1 stk


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


Container 2

10-fots akuttfase

strandutstyr

1 stk


Container 3

10-fots akuttfase

strandutstyr

1 stk


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


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


Container 2

10-fots akuttfase

strandutstyr

1 stk


Container 3

10-fots akuttfase

strandutstyr

1 stk


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


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


paravan

1 stk

Kystverket

Stavanger


paravan

1 stk

Kystverket

Stavanger


Kystverket

Stavanger


Kystverket

Stavanger

absorberende lenser uten skjørt 50 m

Kystverket

Stavanger


pakkramme

Trommel 3 stk

Kystverket

Stavanger

Oljeopptagere KLK 602, Dbl

pakkramme


Kystverket

Stavanger

Oljeopptagere Desmi Termite.

Overløp


Kystverket

Stavanger


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


El.drift. 2,5t

1 stk

Kystverket

Stavanger


Kystverket

Stavanger


Bensindrevet


Kystverket

Stavanger


39kW Fast

1 stk

Kystverket

Stavanger


kW Fast

1 stk

Kystverket

Stavanger


35kW Fast

1 stk

Kystverket

Stavanger

Oljecontainer Desmi RO-tank

10kbm

2 stk

Kystverket

Stavanger

Oljecontainer NOFI oljelekter

25kbm

1 stk

Kystverket

Stavanger


Kystverket

Stavanger


Kystverket

Stavanger

Diverse Expandi

Pakkemanskin

for EP 4300 1 stk

Kystverket

Stavanger


Container 1

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Stavanger


Container 2

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Stavanger


Container 3

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Stavanger


Container 4

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Stavanger


Kystverket

Stavanger


Kystverket

Stavanger


Kystverket Strandrens Absorbent Oljebark 1000 sekker

114

Stavanger

Kystverket

Kristiansand


cont

300m

Kystverket

Kristiansand


152mx5

760m

Kystverket

Kristiansand


paravan

1 stk

Kystverket

Kristiansand


paravan

1 stk

Kystverket

Kristiansand


Kystverket

Kristiansand


Kystverket

Kristiansand

absorberende lenser uten skjørt 50 m

Kystverket

Kristiansand


pakkramme

Trommel 1 stk

Kystverket

Kristiansand

Oljeopptagere KLK 602 / Foxdrum

m/ trsp.cont


Kystverket

Kristiansand

Oljeopptagere 65 Desmi Terminator.

Skive/børste

multiskimmer 1 stk

Kystverket

Kristiansand


børste/skive

Multiskimmer 1 stk

Kystverket

Kristiansand


trans.kont.

Adhesjon 1 stk

Kystverket

Kristiansand


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


El.drift. 2,5t

1 stk

Kystverket

Kristiansand

Kjøretøy Caterpillar V140

Diesel. 6,5t

1 stk

Kystverket

Kristiansand


Kystverket

Kristiansand


Bensindrevet

1 stk

Kystverket

Kristiansand

Strømaggregat Loncin LC3800DC

Bensindrevet

1 stk

Kystverket

Kristiansand


39kW Fast

1 stk

Kystverket

Kristiansand


kW Fast

1 stk

Kystverket

Kristiansand


53kW Fast

1 stk

Kystverket

Kristiansand


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


Kystverket

Kristiansand


Kystverket

Kristiansand

Diverse Expandi

Pakkemanskin

for EP 4300 1 stk

Kystverket

Kristiansand


Container 1

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Kristiansand


Container 2

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Kristiansand


Container 3

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Kristiansand


Container 4

10-fots akuttfase

strandutstyr

1 stk

Kystverket

Kristiansand


Kystverket

Kristiansand


Kystverket

Kristiansand


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


trsp.cont

2 stk


trsp.cont

1 stk

116


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


39kW Fast

2stk


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


Container 2

10-fots akuttfase

strandutstyr

1 stykk

117


Container 3

10-fots akuttfase

strandutstyr

1 stykk


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


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


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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OMV BEREDSKAPSPLANLEGGING BJØRNØYA …...OMV BEREDSKAPSPLANLEGGING BJØRNØYA Generic Oil Spill...

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