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Melanie Josefsson Swedish Environmental Protection Agency Waterford, Ireland June 1, 2010

Explore the harmonies and contradictions between EU and local laws in the aquatic environment, emphasizing management strategies. Dive into commitments like CBD IAS guidelines, Bern Convention strategies, and relevant EU communications. Learn the significance of IMO Ballast Water Convention, Baltic Sea Action Plan, and the Marine Strategy Framework. Understand the impacts of alien species usage in aquaculture and directives like Habitats, Plant Health, and Animal Health. Uncover the importance of regional agreements and the control of harmful aquatic organisms. Discover how the Water Framework and Marine Strategy Directives shape environmental assessments and standards for good environmental status.

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Melanie Josefsson Swedish Environmental Protection Agency Waterford, Ireland June 1, 2010

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  1. Cohabitating with the EUAn environmental manager’s viewpoint on the synergies and conflicts between EU and national regulations in the aquatic environment Melanie Josefsson Swedish Environmental Protection Agency Waterford, Ireland June 1, 2010

  2. Commitments to developing EWS • CBD Guiding Principles on IAS VI/23, GP 7 • Bern Convention’s European Strategy on IAS • EU Communication on Biodiversity (COM (2006)216) Halting the loss of biodiversity • Obj 5. To substantially reduce the impact of IAS and alien genotypes • IMO Ballast Water Convention • HELCOM Baltic Sea Action Plan: Regional Information System with Early Warning by 2013

  3. What do we need to consider? • IMO Ballast Water Convention • EU regulations • Use of alien and locally absent species in aquaculture (708/2007/EC) • Marine Strategy Framework (2008/56/EC) • Water Framework Directive (2000/60/EC) • Habitat Directive • Plant Health Directive (2000/29/EC) • Animal Health Directive (2006/88/EC) • Regional agreements /HELCOM, OSPAR

  4. Ballast water ConventionInternational Convention for the Control and Management of Ships’ Ballast Water and Sediment 2004 • To prevent, minimize and ultimately eliminate the transfer of harmful aquatic organisms and pathogens through the control and management of ships’ ballast water and sediments. • Requires a Warning System for harmful organisms and uptake areas - Areas known to contain outbreaks, infestations or populations of Harmful Aquatic Organisms and Pathogens (e.g. harmful algal blooms) which are likely to be taken up in Ballast Water, should be identified and avoided where possible (Guidelines on designation of areas for Ballast Water Exchange (G14).

  5. Marine Strategy DirectiveGeneral requirements • General requirements • MS develop a Marine strategy with the aim of achieving or maintaining good environmental status in the marine environment by 2021 • Ecosystem approach • MS should make an initial assessment of current environmental status by 2012 • MS establish environmental targets and indicators by 2012 • MS establish monitoring program by 2016 • Program of measures 2016-2020

  6. Assessments of water’s environmental status 1. Analysis of essential characteristics and current environmental status of waters • Table 1. Biological features • An inventory of the temporal occurrence, abundance and spatial distribution of non-indigenous, exotic species or, where relevant, genetically distinct forms of native species, which are present in the region/sub- region • Table 2 – Pressures and Impacts - Biological Disturbance. Introduction of non-indigenous species and translocations

  7. Assessments of water’s environmental status (cont.) 2. Analysis of predominant pressures and impacts including human activity on characteristics and environmental status of waters 3. Economic and social analysis of their use and cost of degradation of the marine environment

  8. Criteria for good environmental status relevant to the descriptors of Annex I to Directive 2008/56/EC • Descriptor 2 Non-indigenous species • 2.1 Abundance and state characterisation of non-indigenous species, in particular invasive species • 2.1.1 Trends in abundance, temporal occurrence and spatial distribution in the wild of non-indigenous species, particularly invasive non-indigenous species, notably in risk areas, in relation to main vectors and pathways of such species.

  9. Descriptor 2 Non-indigenous species(cont.) • 2.2 Environmental impact of invasive species • 2.2.1 Ratio between invasive species and native species in some well studied taxonomic groups, e.g. fish, macroalgae, molluscs that may provide a measure of change in species composition further to displacement of native species • 2.2.2 Impacts of invasive species at the level of species, habitats and ecosystem

  10. Conclusion • Additional scientific and technical development is required for developing potentially useful indicators, especially of impacts of invasive species (such as biopollution indexes), which remain the main concern for achieving good environmental status.

  11. Biopollution index BPL= relative abundance, distribution, magnitude of impacts • Magnitude of IAS impacts on native species • No displacement av inhemska arter • Local displacement , no extinction • Large scale displacement • Population extinctions • Population extinctions of native keystone species • Assess impact on habitats • Assess impacts on ecosystem functioning

  12. Water Framework Directive • Purpose of the WFD – to ensure that inland, transitional and coastal waters achieve or maintain a good ecological status • IAS not specifically mentioned in the WFD, but considered by most countries as a pressure and detract from naturalness. Annex V consider IAS as “potential “anthropogenic impact” • Guidance from the EC on WFD

  13. Options for Assessing IAS in the Ecological Status Classification Approaches to dealing with IAS vary greatly between countries (and within countries) 1) Water body classified using pressure-based classification tools, classification then modified in an additional step based on IAS 2) Water body classed then modified depending on the abundance or percentage coverage of IAS 3) No additional assessment of IAS on the assumption that impacts of IAS are detected in existing instruments 4) Separate risk assessment for IAS undertaken, biopollution indexes published alongside water classification, but doesn’t affect classification

  14. Other regional agreements • HELCOM - Undertake monitoring in order to undertake risk assessments. Species that pose the major ecological harm and those that can be easily identified and monitored - Alert to ships not to take up ballast water during outbreaks of harmful species and other high risk conditions - Exchange of information • OSPAR - Voluntary Guidelines for the management of ships’ ballast water and sediment • EPPO, Bern Convention, Bonn Convention, RAMSAR, CBD, ICAO

  15. National regulations and Objectives • Need for national monitoring and EW systems • Requirements rapidly increasing while resources are dwindling • Need for coordination in developing warning systems to ensure no double work • Need for an ”ultimate solution” ”Mother-of all-warning systems” paid for by someone else?

  16. National approaches • Go ahead and take measures and develop systems at the risk of wastage and/or censure • Wait and see what the EC will require of MS

  17. Proposed Swedish Early Warning and Rapid Response System Analysis of the surrounding world International information systems – New species can enter Sweden Monitoring – New species discovered Information to the Rapid Response Group Reports to the Species Information System, Quality control and verification Information to the secretariate, competent authorities and country administration boards Risk analysis Authorities, secretariate and experts Rapid Response Plans Secretariate, Sectoral authorities, County Administrative Boards Measures Secretariate, Sectoral authorities, County Administrative Boards

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