implementation of the ecosystem approach through marine spatial planning: the norwegian case
TRANSCRIPT
ImplementationoftheecosystemapproachthroughMarineSpatial
Planning:theNorwegiancase
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International Marine Spatial Planning Symposium: Sharing Practical Solutions/11th Annual Ronald C. Baird Sea Grant Science Symposium (IMSPS)
May 14th 2012
Overview
1. Overview of the Norwegian planning process1. Structure2. Governance3. New regulatory tools
2. Final product3. What difference did it make?4. Challenges and potential for improvement
Photo: T. de Lange Wenneck
Norway;the”oceanstate”• Area
– Waters under Norwegian jurisdiction:2,3 million km2
– Land territory: 385 000 km2
• Economic importance– Petroleum, aquaculture
and fisheries are the main exports and foundation our welfare
Agrowingunderstandingforintegratedoceanmanagement
• Response to challenges and pressures:– Climate change and pollution – Petroleum industry seeking expansion into the
north and coastal areas– Increased shipping
• External pressure for implementing the Ecosystem Approach:– North Sea ministerial meeting 1997 calling for
implementation of the Ecosystem Approach– Johannesburg Declaration 2002 calling for
implementation of EA by 2010
• The cumulative impacts necessitate integrated and ecosystem‐based approaches to management.– Marine Spatial Planning, Ocean Zoning, ICZM etc
Potential PetroleumFieldsExp. Value: $100 billion
TheNorwegianManagementplans• Initiated in 2001 to
implement integrated and ecosystem‐based management for Nor. EEZs
• Barents sea: 2006 (revision in 2011)
• Norwegian sea: 2009 (revision due in 2014)
• North Sea: under development (expected in 2013)
Barents sea
Norwegian sea
North Sea
Organization
Similar process for the Norwegian Sea and North Sea plans
Developmentprocess
GovernanceStructure
ImplementationandreviewMinisterial steering group
Monitoring group Management forum Environmental risk forum
2010 Knowledge
base for review of
Management Plan
Political process:
New priorities
2011New Gov.
White paper.
Revised plan
20072008
2009
Annual reports
Outside events
Hybridtop‐downapproach
• Led and initiated by the government (political decision)
• Development carried out by government research institutes and directorates
• Input from stakeholders at various stages:– Hearings– Public meetings
• Important zoning decisions made at political level
Zoning aspects
• Identification of valuable areas• Shipping lanes moving ship traffic further off‐shore
• Area‐based management framework for petroleum activities
Spawning areas for cod, herring, capelin, haddock andsaithe
Olsen et al. 2010. ICES JMS
Larvae areas for cod, herring, capelin, haddock and saithe
Valuableareas
BarentsSeaShippinglanes
0
50
100
150
200
250
300
350
2005 2006 2007 2008 20090
2
4
6
8
10
12
14
16
18
Antall transitter
Antall tonn
Vessle traffic pr year
Petroleummanagementframework2006‐2010
40 °35 °30 °25 °20 °15 °10 °5 °
85 °75 °65 °55 °45 °35 °25 °15 °5 °0 °-5 °-15 °-25 °-35 °-50 °-75 °
81 °
76 °
71 °
76 °
71 °
-65
°-4
0 °
-30
°-2
0 °
-15
°-5
°
45 °
50 °
55 °
60 °
65 °
80 °
Management plan areaShipping routes
Ecologically valuable areasDisputed area
Oil/gas discoveries
High intensity fishingFramework for petroleum industry
No petroleum activityNo new petroleum activities
No drilling, March - September
Norway
Russia
Spitzbergen
Franz Josef Land
Greenland
Lofoten
Polar front
Bear Island65 km zone
Ice-edge
Lofoten - Vesterålen
Tromsøflaketbank area
Olsen et al. 2007, ICES JMS,
No Petroleum Activities-Lofoten – Vesterålen-Eggkanten-Bear Island-Polar front-Ice-edge-Coastal zone 0 – 35km
No NEW Petroleum Activities-Coastal zone 35 – 50 km
No drilling March - August-Coastal zone 50 - 65 km-Tromsøflaket
BarentsSea2011revision• Changes:
– Area from 50‐65 km opened with for petroleum with no restrictions
– Area between 50 and 35 km offshore opened for petroleum activities (w date restrictions)
– Eggakanten valuable area opened for petroleum activities
– Discharges of produced water (containing oil residues) allowed
– Collection of knowledge– Framework to be revised in 2013
following election
What differences did it make?
• No legislation specifically for the plans. Implemented through existing legislation – ‘Marine resources act’ has been designed with this in mind
• New meeting places for advisors, managers and stakeholders• Annual reporting of status (ecosystem, human use) and state of
knowledge• Development of an indicator‐based reporting system
(ecosystem state)• Assessment of environmental risk• Routing system for shipping• Area‐based management framework for petroleum
Photo: T. de Lange Wenneck
KeyScienceChallenges
• Effects of climate change and ocean acidification
• Assessing vulnerability and ecological risk assessment– Identifying , quantifying and mapping
ecological value
• Ecosystem goods and services– Mapping and setting value to G&S
• Mapping all human impacts– Fishing activities and fishing grounds– Effects on benthic habitats
• Total and cumulative impacts of human activities
Photo: E Olsen
Potential for improvements
• STRUCTURAL / ORGANIZATIONAL:– Based on science, but need transparency and peer review– Improve sectoral cooperation, especially at ministerial level– Identifying and clarifying disagreements (between sectors) to
improve decision‐making and enhancing the scientific ethos
• SCIENTIFIC– Socioeconomic effects are not assessed although they are
instrumental in the decision‐making process– Economic impact on communities, region and nation should be better
assessed
– Ecosystem services should be assessed
– Communication of uncertainties!
Photo: T. de Lange Wenneck
Concluding remarks
• The applicability of the Norwegian management plans to other countries can be questioned. – Norway is a small, homogenous and rich country. – Its central administration is highly concentrated and by international standards well coordinated.
– Its research institutions are well funded and have substantial capacity to carry out the research for Integrated oceans management.
• Even under these conditions implementing MSP has been challenging!
Thankyouforyourattention!
Photo: T. de Lange Wenneck