Ammonia deposition reductions required post-2025 to protect Annex I habitats Jane Hall, UK NFC, CEH Bangor Tony Dore, CEH Edinburgh Ed Rowe, CEH Bangor.

Slides:



Advertisements
Similar presentations
EU political background – why an EU ship emissions policy Ships now the biggest source of air emissions in the EU Ships now the biggest source of air emissions.
Advertisements

Workshop on Climatic Analysis and Mapping for Agriculture
TFIAM, Haarlem, The Netherlands, 7-9 May 2003 UK Integrated Assessment Model (UKIAM) T.Oxley, H.ApSimon, A.Dore, J.Hall, E.Heywood, T.Gonzales del Campo.
RAINS1 ECON 4910 Spring 2007 Environmental Economics Lecture 7, The RAINS model Memorandum No 37/99 Lecturer: Finn R. Førsund.
From Uncertain Depositions to Uncertain Critical Load Exceedances Maximilian Posch RIVM Coordination Center for Effects (CCE/TF M&M) Balancing Critical.
Federal Department of the Environment, Transport, Energy and Communications DETEC Federal Office for the Environment FOEN CCE Call for Data , Swiss.
LINKING EUROPEAN, NATIONAL & CITY SCALES UK National Focal Centre for Integrated Assessment Modelling Helen ApSimon and Tim Oxley, Imperial College in.
N Deposition in the Netherlands Implications for Natura 2000 Jan BakkerSeptember 2009.
“Acid” in the Atmosphere Pollution and Impact on Ecosystems.
The Clean Air For Europe (CAFE) program: Scientific and economic assessment Markus Amann International Institute for Applied Systems Analysis.
Developing Biodiversity Indicators Measuring Conservation Impact at Global and Project Scales Valerie Kapos.
Conservation Targets the building blocks Conservation Coaches Network New Coach Training.
Baseline emission projections for the revision of the Gothenburg protocol All calculations refer to Parties in the EMEP modelling domain Markus Amann Centre.
Air Pollution Impacts on Global Crop Productivity and Nitrogen Deposition AGU Fall Meeting December 17, 2014 Colette L. Heald Amos P.K. Tai (now at CUHK),
Non-pollutant ecosystem stress impacts on defining a critical load Or why long-term critical loads estimates are likely too high Steven McNulty USDA Forest.
Baseline projections of European air quality up to 2020 M. Amann, I. Bertok, R. Cabala, J. Cofala, F. Gyarfas, C. Heyes, Z. Klimont, K. Kupiainen, W. Winiwarter,
Valuation of damage to ecosystems due to air pollution Preliminary findings ECLAIRE-project Rome, 7-10 April 2014 Rob Maas, TFIAM.
LBG/LB 1 Working Group on Effects, ICPM&M-Coordination Center for Effects, J.-P.Hettelingh, Gothenburg, October 2004 New developments on air pollution.
Threat status Europe Least concern Protected by EU Nature Directives and 2 international agreement(s) Protected in 1140 Natura 2000 sites Lives in forest.
Coordination Centre for Effects Jean-Paul Hettelingh, EC4MACS kick off meeting, IIASA, 6-7 March 2007 EC4MACS Task 3: Ecosystem Impact Assessment by the.
Development of a new method for peat acidity critical loads in the UK Chris Evans, Jane Hall, Ed Rowe.
Coordination Centre for Effects, TFIAM Meeting, Bilthoven, 8-10 June 2009 (Further) (Possible) ICP M&M Contribution to Integrated Assessment Maximilian.
Natura EU ambitions for a coherent ecological network State of Play and Challenges Saskia Richartz Institute for European Environmental Policy.
Lecture notes 2, 4910 spring 2005, The RAINS model Transboundary pollution  UN 1972 conference on the human environment: States have...the responsibility.
Baseline emission projections for the revision of the Gothenburg protocol Markus Amann Centre for Integrated Assessment Modelling (CIAM) International.
Attaining urban air quality objectives- links to transboundary air pollution Helen ApSimon, Tim Oxley and Marios Valiantis UK Centre for Integrated Assessment.
A critical evaluation of country-dependent impact factors for acidification in Europe summary of a scientific paper submitted for review -Do Not Quote.
Baseline emission projections and scope for further reductions in Europe up to 2020 Results from the CAFE analysis M. Amann, I. Bertok, R. Cabala, J. Cofala,
1 Examples on Natura 2000 forest management on private areas Timo Soininen, M.Sc. Forestry Forestry Development Centre Tapio
Arjen van Hinsberg, Janet Mol Dynamic modelling of impacts in Natura 2000 habitats the Dutch response to the call for data.
1. The Study of Excess Nitrogen in the Neuse River Basin “A Landscape Level Analysis of Potential Excess Nitrogen in East-Central North Carolina, USA”
Coordination Centre for Effects, Workshop to Promote the Ratification of the Protocols, St. Petersburg, October 2009 Critical Loads and their exceedances;
Calculate, map and used of critical loads and exceedances for acidity and nitrogen in Europe Professor Harald Sverdrup Chemical Engineering, Lund University,
By Diego Luna Quevedo Highlights in the Southern Cone and connections with WHMSI.
Development of a process for setting Conservation Objectives Dr Rebecca Jeffrey Science and Biodiversity Section National Parks and Wildlife Service Ireland.
11 September 2007 How do the dispersion calculations in the IIAS work? Magnuz Engardt Swedish Meteorological and Hydrological Institute January 2008.
Scope for further emission reductions: The range between Current Legislation and Maximum Technically Feasible Reductions M. Amann, I. Bertok, R. Cabala,
European Topic Centre on Biological Diversity Preparation of the Atlantic Natura 2000 Seminar Draft pre-scoping document.
Baseline and MTFR scenarios EECCA and Balkan countries Janusz Cofala and Stefan Astrom.
Aims Of The REPS establish farming practices and production methods which reflect the increasing concern for conservation, landscape protection and wider.
The GAINS optimization approach – Basic background information Fabian Wagner International Institute for Applied Systems Analysis (IIASA) IIASA workshop.
EEA Biodiversity, Agriculture and Forest work in 2010 and beyond EEA/NRC Agriculture Meeting 2010 Ivone Pereira Martins, HoG – Biodiversity, Agriculture.
Carlos Romao / Annemarie Bastrup-Birk 13 th meeting Standing Forestry Committee Brussels, 18 September 2015 State of nature in the EU - focus on forest.
Preliminary ECLAIRE findings Budapest, 2 October 2014 Rob Maas, RIVM.
17 th TFMM Meeting, May, 2016 EMEP Case study: Assessment of HM pollution levels with fine spatial resolution in Belarus, Poland and UK Ilia Ilyin,
Alejandro Gallego Schmid Department of Chemical Engineering University of Santiago de Compostela (Spain) Boston, 30 th September 2009 Calculation of LCA.
Reducing Ammonia Emissions in Europe – with focus on Denmark Senior Researcher Brian H. Jacobsen Institute of Food and Resource Economics University of.
From Economic Activity to Ecosystems Protection in Europe
WGE Extended Bureau Meeting LRTAP Convention, Geneva, 20 March 2017
Results: ICP M&M call for data Jean-Paul Hettelingh, Max Posch, Jaap Slootweg, Anne-Christine Le Gall 3rd Joint session of the Working Group.
Action Planning for Irish Birds
Low Hanging Fruits Mora Aronsson ETC-BD/SLU
European Red List of Habitats
Guidance on Natura 2000 and Forests – Scoping Document
European Red List of Habitats
European Commission – DG ENV
1. The Study of Excess Nitrogen in the Neuse River Basin
1st Pre-scoping Document
European Topic Centre on Biological Diversity 15th March 2016
Structure of the guidelines Reminder on next steps
ARTICLE 17 REPORTING: SUMMARY OF MAIN RESULTS
From Economic Activity to Ecosystems Protection in Europe
M. Amann, I. Bertok, R. Cabala, J. Cofala, F. Gyarfas, C. Heyes, Z
New PAF format for Presentation & next steps
on the way to designate SACs…
Environmental objectives and target setting
European Red List of Habitats
Atlantic Natura 2000 Seminar
Draft Pre-scoping Document
progress in activities and results of call for data
Presentation transcript:

Ammonia deposition reductions required post-2025 to protect Annex I habitats Jane Hall, UK NFC, CEH Bangor Tony Dore, CEH Edinburgh Ed Rowe, CEH Bangor

Background Habitats Directive Member States report every 6 years on conservation status of habitats and species listed in Annexes Conservation Status includes ranking current pressures & future threats L = low importance/impact M = medium importance/impact H = high importance/impact Air pollution category: Nitrogen input [deposition]

Study aim To determine the ammonia deposition reductions required post-2025 to meet protection targets for Annex I habitats within UK SACs UK Targets: Low <5% habitat area exceeded (95% protected) Medium 5-25% habitat area exceeded (75% protected) High >25% habitat area exceeded (<75% protected)

Nitrogen critical loads Bobbink, R. & Hettelingh, J.P. (eds) 2011: Review and revision of empirical critical loads and dose-response relationships. Coordination Centre for Effects, RIVM. SAC containing one/more of the 41 Annex 1 habitats SAC without any of the 41 Annex 1 habitats Based on empirical critical loads of nitrogen (Bobbink & Hettelingh, 2011) “Recommended” values from ranges for 41 Annex I habitats Applied to Annex I habitats within SACs Habitat area assumed to be the same as site area

Annex I habitats: CLnutN exceedances 2025 coastalduneswoodlandbog/fengrasslandheath

Nitrogen deposition Maps show deposition to moorland Five scenarios based on UEP45 scenario for 2025: 100% NOx 100% NOx 100% NOx 100% NOx 100% Nox 100% NHx 75% NHx 50% NHx 25% NHx 0% NHx kg N ha -1 year -1

Exceedance results: H4010 wet heath

Results for Annex I Heath/scrub habitats

Results for Annex I Dune habitats

Results for Annex I Grassland habitats

Results for Annex I Bog & Fen habitats

Results for Annex I Forest habitats

N deposition threat to Annex I habitats No reduction in NHx 25% reduction in NHx 50% reduction in NHx 75% reduction in NHx 100% reduction in NHx

All habitat areas: not just SAC Annex I...

Conclusions 9 out of 41 habitats need removal of all NHx deposition and NOx reductions to meet 95% protection target 4 out of 41 habitats need removal of all NHx deposition and NOx reductions to meet 75% protection target A 75% reduction in NHx deposition post 2025 would allow 20/41 habitats to meet both 75% and 95% protection targets Annex I habitat analysis is based on the assumption that each habitat occupies the entire area of the SACs in which it occurs Cannot meet UK protection targets for Annex I habitats within SACs without significant reductions in ammonia deposition Similar results for the wider distribution of habitats beyond designated sites