20
Implications of MPAs for the fishing industry Wouter van Broekhoven [email protected] Science and policy advisor, VisNed (Dutch demersal fisheries association) European Parliament Fisheries Committee hearing on: MARINE PROTECTED AREAS (MPAS):VALUING MARINE BIODIVERSITY AND ECOSYSTEMS FOR THE BLUE ECONOMY Brussels, 9 November 2016

Implications of MPAs for the fishing industry · 2016. 11. 16. · fishing industry Wouter van Broekhoven [email protected] Science and policy advisor, VisNed (Dutch demersal

  • Upload
    others

  • View
    4

  • Download
    0

Embed Size (px)

Citation preview

  • Implications of MPAs for thefishing industry

    Wouter van Broekhoven

    [email protected] and policy advisor, VisNed

    (Dutch demersal fisheries association)

    European Parliament Fisheries Committee hearing on:

    MARINE PROTECTED AREAS (MPAS):VALUING MARINE BIODIVERSITY AND ECOSYSTEMS FOR THE BLUE ECONOMY

    Brussels, 9 November 2016

  • North Sea provides 1.8m tonnes = approx. € 2 billion/year

  • Presentation outline

    1. MPA considerationspurpose, limitations

    2. Quantifying impact on fishing industry

  • Conservation

    conservation

    commercial fishstocks

    vulnerable and spatiallydefined features

    Common FisheriesPolicy

    MPAs

  • MPAs & vulnerable features

    Cleaver Bank (Aquasense/PeriPlus)

  • Dynamic habitats

    ICES 2016, WKFBI report, ACOM46

    Aquasense / Periplus

    Dynamic habitat is prevalent in North Sea(this colour = sand)

  • Dynamic habitats

    biologicalcommunity adapted tophysicaldisturbance

    UKNL

  • Seafloor integrity & trawling frequency

    ICES 2016, WKFBI report, ACOM46

    back to target level after 2.3 y

    Target

    Re

    lati

    veb

    en

    thic

    com

    mu

    nit

    y b

    iom

    ass

    (Bio

    mas

    / K

    )

    Initial Mortality

    Recovery Time

  • Seafloor integrity & trawling frequency

    ICES 2016, WKFBI report, ACOM46

    Trawling intensity (frequency per year)

    2.17

    max. 2.17 trawls per year maintains target integrity

  • Fishing effort clustering & unfished area

    Eigaard et al. 2016 (in press)

    37% of North Sea seafloor unfished in study period 2010-2012

    > 0 – 0.10.1 – 0.50.5 – 11 – 10> 10

    Swept area / yr

    90% of effort in lessthan 50% of area

  • Displacement of fishing effort

    Mind the: “… trade-off between recovery in the closed areas and additional trawling effects in the open areas …”1

    Assess the net ecological effects.

    Literature reviews in:

    1. Hiddink et al., 20062. Sweeting & Polunin, 20053. IMARES report C170/154. Caveen et al., 2014

  • Alternatives for impact reduction

  • Spatial claims

    But.. can we quantify this?

  • Tool 1: value maps

    Netherlands fleet landings in area

    2011 2012 2013

    EUR 3.6m 4.1m 3.4m

    UKNL

  • Tool 2: Individual Stress Level Analysis (ISLA)

    Test of method:Future Natura 2000 areas and wind farms NL, DE, DK

    Schulze et al. 2010 (COEXIST)

    • Scenarios: 6 (combinations of these areas)• Fleets: NL, DK, DE • Year: 2015

  • Scenario: A B C D E F

    Tool 2: Individual Stress Level Analysis (ISLA)

    Schulze et al. 2016 (pers.comm.)

    • Impacts differ between scenarios

    • Impacts differ between fleets

  • Tool 2: Individual Stress Level Analysis (ISLA)

    Tool can even be used to compare individual fishing ports:

    Schulze et al. 2010 (COEXIST)

  • Take-home messages

    1. Fishing effort is highly clustered in space and large areas are unfished

    2. Conservation objective appropriate instrument

    3. Quantitative toolbox: seafloor integrity as a function of trawling frequency

    4. Displacement of fishing effort:• Assess net ecological effect (inside & outside)• Avoid closing intensively fished areas

    5. Use the tools to quantify impacts on fleets (segments) to inform policy trade-offs.

    MPA

    other

    what? why? how?

  • Implications of MPAs for thefishing industry

    Wouter van Broekhoven

    [email protected] and policy advisor, VisNed

    (Dutch demersal fisheries association)

    European Parliament Fisheries Committee hearing on:

    MARINE PROTECTED AREAS (MPAS):VALUING MARINE BIODIVERSITY AND ECOSYSTEMS FOR THE BLUE ECONOMY

    Brussels, 9 November 2016

    Thank you for listening

  • References

    www.abpmer.co.uk/experience/fisheries-and-aquaculture-experience/assessing-fisheries-mpas/

    Caveen A, Polunin NVC, Gray T, Marguerite Stead S (2014) The controversy over Marine Protected Areas – Science meets policy. Springer.

    Eigaard OR, Bastardie F, et al (in press) ICES Journal of Marine Science. The footprint of bottom trawling in European waters: distribution, intensity, andseabed integrity.

    Schulze T, Schulte K, Hamon K (2012) Report on economic analysis in coastal fisheries on the basis of revenue for individual profession and fishing trips. COEXIST Project Deliverable D3.2.

    Slijkerman D, Tamis J (2015) Fisheries displacement effects related to closed areas : a literature review of relevant aspects. IMARES report C170/15.

    Sweeting C, Polunin NVC (2005) Marine protected areas for management of temperate North Atlantic fisheries: lessons learned in MPA use for sustainable fisheries exploitation and stock recovery. Report to Defra, London