UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk University of Aveiro City Case Overview Department of Environment and Planning.

Slides:



Advertisements
Similar presentations
ATHENS UNIVERSITY OF ECONOMICS AND BUSINESS TRANSPORTATION SYSTEMS AND LOGISTICS LABORATORY (TRANSLOG) © Prof. K. Zografos STEPs STEPs Scenarios for the.
Advertisements

Tackling the Environmental Impact of Transport Presentation by David Jamieson MP to the Institute for Public Policy Research Wednesday 15th October 2003.
Thematic Strategy on Air Pollution: First ideas for scenarios Matti Vainio Clean Air for Europe programme Working Group on Target Setting and Policy Assessment.
An experience on modelling-based assessment of the air quality within the Air Quality Directive framework Ana Isabel Miranda, Isabel Ribeiro, Patrícia.
David J. Sailor1 and Hongli Fan2 1. Portland State University
A numerical simulation of urban and regional meteorology and assessment of its impact on pollution transport A. Starchenko Tomsk State University.
Gdansk Meeting June Scenarios and the Integration of Models Cascading models.
Experimental Evaluation of Various Biofuel-Diesel Blends as Diesel Engine Fuels Georgios Fontaras and Zissis Samaras Laboratory of Applied Thermodynamics.
City expectations and SUTRA project results Jadwiga Kopeć Director of Environmental Protection Department Municipality of Gdańsk 8/12 Nowe Ogrody Str.
PLANNING BY NEURAL NETWORKS OF INTERVENTIONS FOR THE REDUCTION OF OZONE CONCENTRATION IN LOMBARDY Giorgio Corani Dipartimento di Elettronica ed Informazione.
ENAC-SSIE Laboratoire de Pollution de l'Air The energy Consumption is a Consequence of the Industrial Development
ENAC-SSIE Laboratoire de Pollution de l'Air Bogotá air quality Colombia, 2003.
1 Final Review SUTRA: Sustainable Urban Transportation Final Review Gdansk, June 23/ DDr. Kurt Fedra ESS GmbH, Austria
University of Aveiro Final Meeting and Project Review 23/24 June 2003 Gdansk University of Aveiro Emissions and Air Quality Modelling Department of Environment.
SUTRA June 2003 Indicators and Scenarios. Today The objectives of SUTRA SUTRA and the DPSIR framework The set of indicators The set of scenarios The methodology.
Urban mobility organization and governance in Riga Riga March 5, 2015.
CE 573 Transportation Planning1 Societal Changes and Transportation Planning CE 573 Transportation Planning Lecture 8.
Automatic loading of inputs for Real Time Evacuation Scenario Simulations: evaluation using mesoscopic models Josep M. Aymamí 15th TRB National Transportation.
IMPLEMENTATION OF EU AQ LEGISLATION IN THE CZECH REPUBLIC J. FIALA Czech Hydrometeorological Institute Prague, Czech Republic.
fluidyn – PANAIR Fluidyn-PANAIR
Controlling Vehicular Air Pollution in Beijing Professor Kebin He Dept. of Environmental Science & Engineering, Tsinghua University Orlando, Florida, USA.
10th EIONET Workshop on Air Quality Management and Assessment, Vilnius, October 2005 Air pollution at street level in European cities Nicolas Moussiopoulos,
Jenny Stocker, Christina Hood, David Carruthers, Martin Seaton, Kate Johnson, Jimmy Fung The Development and Evaluation of an Automated System for Nesting.
1 icfi.com | 1 HIGH-RESOLUTION AIR QUALITY MODELING OF NEW YORK CITY TO ASSESS THE EFFECTS OF CHANGES IN FUELS FOR BOILERS AND POWER GENERATION 13 th Annual.
Progress of Beijing in Control of Vehicular Emissions Prof. Jiming Hao Institute of Environmental Science & Engineering, Tsinghua University, Beijing Dec.
Brussels, 1-2 September 2004 Improving Air Quality in the enlarged EU: Workshop on Plans and Programmes of Air Quality and National Emission Ceilings Directives.
NEW VISION OF ENGINEERING ECONOMY COURSE (VISION) MODULE 3 LECTURE 7 Cairo, 17 July 2005.
Environmental Management and Sustainable Mobility of Health Care Companies in Emilia-Romagna Region Environmental Management and Sustainable Mobility.
EEA core set of indicators 37 indicators Of known quality: Geographical and temporal coverage Comparable data Nationally representative data Methodological.
Joint Intersectoral Task Force on Environmental Indicators Geneva 5 – 7 November 2013 Transport and environment: newly proposed indicators Vladislav Bizek.
Opportunities and Constraints on Possible Options for Transport Sector CDM Projects – Brazilian Case Studies Suzana Kahn Ribeiro Importance of Transport.
Making Way for Public Rapid Transit in South Asia and its Impact on Energy and Environment Bangalore, Dhaka and Colombo Ranjan Kumar Bose & Sharad Gokhale.
WG2 Meeting, SG4 Models Benchmarking SMHI, Norrkoping, 14 th June 2011 DELTA tool testing for a Portuguese City Ana Miranda and Helena Martins University.
London Low Emission Zone Study David Hutchinson International Union of Air Pollution Prevention and Environmental Protection Association in association.
Simulation of European emissions impacts on particulate matter concentrations in 2010 using Models-3 Rob Lennard, Steve Griffiths and Paul Sutton (RWE.
Sprawl Dynamics Prof. Philip C. Emmi College of Architecture + Planning University of Utah RailVolution 2005.
The ARTEMIS tools for estimating the transport pollutant emissions Artemis project - EC DG Tren COST346 - Heavy duty vehicles emissions M. André, INRETS,
Air quality and health impact assessment AQ information at the regional scale, urban background scale and street scale past, present and future air quality.
Igor Trpevski University of St. Cyril and Methodius Skopje,
The Impact of Biogenic VOC Emissions on Tropospheric Ozone Formation in the Mid-Atlantic Region Michelle L. Bell Yale University Hugh Ellis Johns Hopkins.
SUTRA [ Sustainable Urban TRAnsportation ] Fifth framework programme of the European Community Environment and sustainable development Final Meeting and.
Risks, challenges and mitigation actions in the APICE partners’ area: between the scientific findings and new governance models - Genoa M.C. Bove, P. Brotto,F.
Latvian Environmental, Geology and Meteorology agency Future development scenarios for traffic system and air pollution in Riga city Iveta Steinberga La.
UN ECE CEP Working Group on Environmental Monitoring and Assessment 7th Session Geneva 27 – 29 November 2006 Item 5(a) Guidelines for the Application of.
Air Dispersion Modeling City of Albuquerque Environmental Health Department Air Quality Program Director: Mary Lou Leonard.
P. Otorepec, M. Gregorič IVZ RS Use of rutinely collected air pollution and health data on local level for simple evaluation of health impact.
| Folie 1 Assessment of Representativeness of Air Quality Monitoring Stations Geneva, Wolfgang Spangl.
DEMOCRITOS DEveloping the MObility CRedits Integrated platform enabling travellers TO improve urban transport Sustainability Grant agreement no
Air Quality Forecasting in China using a regional model Bas Mijling Ronald van der A Henk Eskes Hennie Kelder.
Mobility Services Department The integration of environmetal aspects in the Barcelona Urban Mobility Masterplan Julio García 29th March 2007.
Regional Modeling Joseph Cassmassi South Coast Air Quality Management District USA.
1 SUTRA Final Review D13 - Multi Criteria Analysis Gdansk, Poland 23 rd -24 th June 2003 Presented by the Ministry of the Environment, Israel.
21-22 March 2005 LMD, Palaiseau, France CHIMERE workshop Air quality assessment for Portugal A. Monteiro, C. Borrego, A.I. Miranda, R. Vautard Universidade.
National Workshop on Urban Air Quality and Integrated Traffic Management Karachi, September 13-14, 2006.
IEE/12/041/SI – Ele.C.Tra. 01 July 2013 – 31 December 2015 September 2013 Electric City Transport Ele.C.Tra Contract N°: IEE/12/041/SI
Ministry of Infrastructure of Ukraine (former Ministry of Transport and Communications) State Enterprise «State Road Transport Research Institute» (SE.
Forecasting Land Use Change at European and at Urban Level: SASI and PROPOLIS EEA Expert Meeting on Land Use Accounting Copenhagen, 16 March 2005 Spiekermann.
Workshop on the Criteria to establish projections scenarios Sectoral projection guidance: Transport Mario Contaldi, TASK-GHG Emanuele Peschi, TASK-GHG.
The application of Models-3 in national policy Samantha Baker Air and Environment Quality Division, Defra.
Urban Institute Ireland/University College Dublin School of Geography, Planning and Environmental Policy, Dublin, Ireland Eda Ustaoglu.
OPTIMUS SCEAF & Tracker
Konstantinos Alexopoulos Transport Division UNECE
SMOKE-MOVES Processing
Modelling Sustainable Urban Transport
Stakeholder Expert Group on the Review of EU Air Policy 6-7 June 2011
Influence of Driving Restrictions on Pollution Reduction
Impacts of Reducing Freeway Shockwaves on Fuel Consumption and Emissions Meng Wang, Winnie Daamen, Serge Hoogendoorn, Bart van Arem Department.
Forest fires and air pollution in Portugal
Sensitivity Analysis Update
Alexey Gusev, Victor Shatalov, Olga Rozovskaya, Nadejda Vulyh
Presentation transcript:

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk University of Aveiro City Case Overview Department of Environment and Planning University of Aveiro (Portugal) Ana Isabel Miranda and Carlos Borrego

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk An introduction... The cities involved in SUTRA differ widely in terms of culture, environmental conditions, size, economic structure, social composition and demography. But... they face common challenges in their transportation systems:  Air quality  Employment  Traffic congestion  Noise ....  Economic competitiveness €

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk An introduction... A common methodology and a set of tools were used by SUTRA cities to generate directly comparable results for the overall evaluation. Indicators Scenarios Models

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk TOPICS TO BE COVERED  City case description  Models cascade application - baseline - common scenarios  Final comments  City case description  Main conclusions  Models cascade application:  Baseline  Common scenarios

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk  City case description location, urban structure and land-use demography meteo conditions and air pollution input indicators  Main conclusions  Models cascade application:  Baseline  Common scenarios The SUTRA cities Lisbon Geneva Gdansk Thessaloniki Genoa TelAviv

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk Meteorological conditions and air pollution problems GENOA  mild Mediterranean climate  topographic and orographic peculiarity: sea and mountains  affect pollutants dispersion LISBON  complex sea breeze circulations  traffic NO x emissions represents 97% of total anthropogenic NO x emissions. THESSALONIKI  45% of days characterized by stagnant conditions  high insolation  City case description location, urban structure and land-use demography meteo conditions and air pollution input indicators  Main conclusions  Models cascade application:  Baseline  Common scenarios

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk Demographic indicators Demographic changes are crucial to determine traffic demand Population size Population size for VISUM and OFIS domains Population size evolution Age structure  City case description location, urban structure and land-use demography meteo conditions and air pollution input indicators  Main conclusions  Models cascade application:  Baseline  Common scenarios

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk Economic indicators GDP per capita % of employment in services over total employment  City case description location, urban structure and land-use demography meteo conditions and air pollution input indicators  Main conclusions  Models cascade application:  Baseline  Common scenarios

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk Technological indicators passenger car peak occupancy rate % of public transport over total passenger transport  City case description location, urban structure and land-use demography meteo conditions and air pollution input indicators  Main conclusions  Models cascade application:  Baseline  Common scenarios

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk Which scenarios? A baseline scenario (specific of each city) Common scenarios of development Which models? VISUM TREM VADIS OFIS MARKAL  City case description  Main conclusions  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk Common scenarios...definition  City case description  Main conclusions  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL Land use Young and virtuous Young and vicious Old and virtuous Old and vicious Demography Economic srtructure Technology € € €

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk VISUM transportation model...domain  AREA: 241 km 2  POPULATION:  N. NODES: 936  N. LINKS: 888 GENOA  AREA: 2793 km 2  POPULATION:  N. NODES: 1124  N. LINKS: 2940 LISBON  AREA: 1447 km 2  POPULATION:  N. NODES: 3144  N. LINKS: TEL AVIVTHESSALONIKI  AREA: 1100 km 2  POPULATION:  N. NODES: 1386  N. LINKS: 2034 GENEVA  AREA: 282 km 2  POPULATION:  N. NODES: 936  N. LINKS: 2900  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL -GENOA -LISBON -GENEVA

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk VISUM transportation model...input data Trips by purposes OD matrixes  road category and capacity  maximum velocity allowed +  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk VISUM transportation model...results  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL Results example: Lisbon public network

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk Pressure indicator: passenger transport demand (pkm/year) VISUM transportation model...indicators State indicator: time spent in crowding and traffic jams (hours)  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk Ex. Genoa input data from the common scenario implementation VISUM transportation model...methodology A spreadsheet (CommonScenarios.xls) was developed to modify the O/D matrixes according to the scenarios. The obtained results reflect the characteristics of each traffic network. Ex. Lisbon output data from the common scenario spreadsheet  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk VISUM transportation model...results and analysis CS1 –Young and virtuousCS2 – Young and vicious CS3 – Old and virtuous CS4 – Old and vicious Ex. Lisbon private network  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk VISUM transportation model...results and analysis  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL Ex. Comparison of scenarios results for private transport in Geneva

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk TREM emissions model...domain and input data For every city-case TREM domain coincides with VISUM domain. Main inputs required by TREM:  traffic volume and vehicle speed (provided by VISUM)  distribution of vehicles by categories  distribution of vehicles by classes ex. Gdansk  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk Hourly variation of CO emissions for Lisbon (Prata and Ouro streets) CO emission for Genoa domain TREM emissions model...results  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk TREM emissions model...indicators  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk TREM emissions model...scenarios input data Main inputs in TREM scenario application:  technological indicators  new technologies penetration rates  vehicle fleet changes  fuel properties  VISUM outputs  vehicle volume  vehicle speed Ex. Fleet composition for different scenarios  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk TREM emissions model...results and analysis Ex. Genoa CO emissions CS1 –Young and virtuousCS2 – Young and vicious CS3 – Old and virtuous  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL CS4 – Old and vicious

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk TREM emissions model...results and analysis Ex. Thessaloniki results Only CO 2 emissions for Scenario 2 represent values above the reference situation. All other pollutants are expected to decrease primary due to emission reduction technologies and low sulphur levels in gasoline and diesel.  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL VADIS local scale model...domain

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk VADIS local scale model...input data Buildings volumetry Geneva GenoaLisbon Wind velocity and direction for Lisbon simulation Meteorological data Emission data (provided by TREM)  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk Wind and CO dispersion fields for Lisbon for 6p.m. of 8th of July 1997 Wind and CO dispersion simulation for Thessaloniki for 7 a.m. of 9 September 1998 VADIS local scale model...results  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk VADIS local scale model...results and analysis Ex. Lisbon CO dispersion fields CS1 –Young and virtuousCS2 – Young and vicious CS3 – Old and virtuous CS4 – Old and vicious  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk VADIS local scale..results and analysis  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL European Legislation CO CO µg.m -3 (8-hours average limit value) Ex. Lisbon results

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk VADIS local scale model..results and analysis  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL European Legislation NO 2 NO µg.m -3 (not exceeding more than 18 times in a year) Hourly value for the protection of human health Ex. Lisbon results

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk VADIS local scale model..results and analysis  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL European Legislation PM10 PM µg.m -3 (not exceeding more than 35 times in a year) Daily maximum value for the protection of human health Ex. Lisbon results

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk OFIS photochemical model...domain  AREA: 150 km x 150 km GDANSK GENEVA GENOA THESSALONIKI TEL AVIV  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk OFIS photochemical model...input data Main inputs required by OFIS:  emissions: hourly non-urban, suburban and urban emissions rates  meteorological data: daily average wind speed and direction, temperature and temperature lapse rate above the mixing layer  boundary conditions: daily average regional background concentrations (NO, NO 2, O 3 and other species)  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk Number of days with maximum 8 hour running average ozone concentration exceeding 120  g.m -3 (IND120). OFIS photochemical model...results  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk AOT60 (maximum and average)AOT60 (suburbs and town), OFIS photochemical model...indicators  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk OFIS photochemical model...results and analysis  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL CS1 –Young and virtuousCS2 –Young and vicious CS3 –Old and virtuousCS4 –Old and vicious GENEVA Ozone AOT60

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk OFIS photochemical model...results and analysis Thessaloniki Indicators  Significant differences between scenarios  Scenario 1 presents the highest results  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL Lisbon Indicators  Only Scenario 3 presents different results  Scenario 3 indicators are higher due to lower ozone consumption pollutants

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk MARKAL...domain techno-economic energy model  Lisbon municipality  82 km 2 LISBON THESSALONIKI  Thessaloniki municipality + 18 municipalities and 2 communes  1100 km 2  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk MARKAL...input data techno-economic energy model Main inputs required by MARKAL:  imported energy prices  demand data  residual capacities  techno-economic data  input/output coeficients  pollutants emissions associated with technologies Ex. html file for input data  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk MARKAL...results techno-economic energy model Lisbon Installed capacity in the private transport sector Lisbon Installed capacity in the public transport sector  Main conclusions  City case description  Models cascade application:  Baseline  Common scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk MARKAL...methodology techno-economic energy model Lisbon application:  The inclusion of MARKAL in the models cascade is in progress, trying to use VISUM outputs as MARKAL scenarios input.  A simple exercise was carried out, with a new strategy in order to calculate MARKAL inputs for different scenarios Two environmental constraints were considered:  reduction of ozone precursors  reduction of CO 2 emissions in conformity with Kyoto/Marrakech agreements  Main conclusions  City case description  Models cascade application:  Baseline  Scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk MARKAL...results and analysis CS1 –Young and virtuous CS2 – Young and vicious CS3 – Old and virtuous CS4 – Old and vicious Lisbon results for private transport  When comparing installed capacity, only for the Scenario 3 this parameter decreases  Clean technologies (fuel cell and hydrogen) are significant only for CS1  Main conclusions  City case description  Models cascade application:  Baseline  Scenarios  VISUM  TREM  VADIS  OFIS  MARKAL

UNIVERSITY OF AVEIRO Final Meeting and Project Review 23/24 June 2003 Gdansk Some final comments  Genoa, Lisbon and Thessaloniki are successful city-cases: the model cascade was applied for the baseline and for the 4 common scenarios  MARKAL was used to generate baseline and also common scenarios allowing to test the technological, economical and energetic approach  The produced indicators allow a easy and practical analysis of the scenario results  The Old and Virtuous City (Scenario 3) seems to be the best choice, but it is linked to a shrinking and getting older citty.  This complex approach was not completely feasible for all the cities, due to several constraints (data availability, model specificity,...)  City case description  Main conclusions  Models cascade application:  Baseline  Common scenarios