Marine Emission Inventory Tool

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Marine Emission Inventory Tool for the Commercial Marine Sector Klym Bolechowsky, P.Eng., ClearSky Engineering Developed For: Environment Canada Transport Canada

Background Need was identified to reliably develop bottomup marine emission inventories: IMO global initiatives: Emission Control Area (ECA) Pollution Data Branch CAC Inventory, Marine Sector Marine Emission Inventory Tool (MEIT) originally developed in 2005 under Environment Canada contract Several revisions and enhancements have been added by ClearSky Engineering, SENES, Levelton under Transport Canada & Environment Canada contracts

Objectives The Marine Emission Inventory Tool (MEIT) developed to generate emission estimates by: Vessel type, engine type Operating Mode: underway, reduced speed, manoeuvring, at berth Temporally: monthly and annual Spatially at port, regional, provincial/territorial, national levels

Scope Marine vessels with compression-ignition engines > 37 kw (50 hp) Capability to process vessel data sets from Lloyd s Register, Canadian Coast Guard (INNAV) CACs HC TPM GHGs CO 2 SO 2 NO x CH 4 CO N 2 O CO 2 e PM 10 PM 2.5

Vessel Types - OGVs Auto Bulk Container Ferry General RO/RO Dry Ore Passenger Reefer Coastal Crude Gasoline Chemical Molasses Ore/Bulk/Oil Liquefied Gas Tanker Super Tanker ULCC VLCC Warship - General Warship Surface Ocean Tugs

Platform Database back-end run by menus Originally designed in MS Access Recently converted from Access to SQL Server 2005 (Feb, 2009)

Calculation Method 1 Emissions (NOx, CO, HC, CO2, CH4, N2O) = Σ (P x LF x EF x T Mode ) input file look-up table calculated P = maximum power output of main or auxiliary engine in kw LF = engine or auxiliary system load factor as a fraction of maximum rated power output EF = emission factor (pollutant specific) in grams per kw-h engine output for main and auxiliary T = time in mode, hours: underway, maneuvering, or dockside

Calculation Method 2 PM, SO x Recent studies indicated a linear relationship between fuel sulphur content and engine PM emissions Source: SENES Consultants Ltd., 2007. Emission Factors and SECA Forecast. Produced for Transport Canada under contract with Weir Marine Engineering Ltd.

Vessel Movement Region 1 Region 2 40% 60% Distance Underway (km) Port PLACE_IDNO Vessel Type HP Speed DWT PREV_PLACE_IDNO

Main Menu 1. Pre-Processing: scan input records, data validation, error checking, flag rejected records 2. Calculate emissions by individual vessel movement 3. Generate forecasts & backcasts if required 4. View reports in Excel "pivot table" format Modify parameters: emission factors, fuel sulphur content, etc.

Software Demonstration

Pre-Processing Raw Vessel movement data format: Canadian Coast Guard (INNAV) Lloyd s Register Fill Data Gaps If HP is null, estimate based on DWT using EPA regression model If DWT is null, estimate based on GT in TRENDS study If Vessel speed is null, look up default value if available If insufficient data is available to estimate above values, the record is rejected and flagged in the reject table Range Checks 0 < HP < 2 x Max Value in database 0 < DWT < 2 x Max Value in database 0 < Speed < 2 x Max Value in database

Emission Factors Unlike diesel engines in trucks and land-based equipment, very few ocean-going vessel engines have been tested for developing emissions factors ICF report for the EPA described emissions factors for OGVs as the weakest link in deep sea vessel emission inventories (ICF, 2005) because factors continue to be derived from limited data Emission testing of OGVs is expensive and difficult undertaking, therefore emissions data are relatively rare

Emission Factors Emission factor sources: Quantification of Emissions from Ships Associated with Ship Movements Between Ports in the European Community, Entec UK Ltd (2002) Emissions Estimation Methodology for Ocean-Going Vessels, California Air Resources Board (CARB),October 2005 Marine Emission Factor and Inventory Study,Transport Canada, March 2007, report pending http://www.tc.gc.ca/innovation/tdc/projects/marine/g/5 673.htm

Case Study 1 Marine Emission Inventory Study Eastern Canada and Great Lakes Transportation Development Centre (TDC) Levelton, Dr. J. Corbett, Maritime Innovation March 2006 http://www.tc.gc.ca/innovation/tdc/summary/14500/14564e.htm

Marine Emission Inventory Study Eastern Canada and Great Lakes A regional emission inventory was prepared for commercial ocean-going marine vessels operating on the Great Lakes, the St. Lawrence Seaway, and the East Coast of Canada in 2002: 1. Development of a detailed inventory of emissions of air contaminants and CO 2 by mode of operation using activity-based information from the Canadian Coast Guard INNAV database using the MEIT. 2. Preparation of a baseline emission forecast for 2010 and 2020, allowing for growth in vessel traffic and changes in engine technology and the sulphur content of domestic marine diesel oil. 3. Preparation of an emission forecast for SO x and PM in 2010 and 2020 that incorporates the emission reductions that could potentially occur by implementation of a Sulphur Emission Control Area (SECA) under Annex VI of MARPOL 73/78 of the IMO. 4. Spatial resolution of the emission inventory to regional polygons and then to 4 km by 4 km grid cells for use in regional air quality modeling studies.

Marine Emission Inventory Study Eastern Canada and Great Lakes

Marine Emission Inventory Study Eastern Canada and Great Lakes

Case Study 2 Sulphur Emission Control Area (SECA), Engine Control Technologies and Emission Standards Transportation Development Centre (TDC) Levelton, ClearSky Engineering, Genesis Engineering May 2008

SECA, Engine Control Technologies and Emission Standards Evaluation of the feasibility of a SECA designation for Canada through analyses of technology options available to the marine sector: 1. Additional evaluation of the feasibility of a SECA region in Canada; Refinement of the marine emissions inventory for SO x and particulate matter (PM); 2. Examination of technical barriers associated with fuel switching and fuel blending; 3. Determination and assessment of developing technologies for the reduction of NO x ; 4. Evaluation of benefits associated with the implementation or promulgation of emissions standards for EPA Engine Categories 1, Category 2 and Category 3 ; and 5. Update and expand the MEIT.

SECA, Engine Control Technologies and Emission Standards MEIT used to model 3 SECA scenarios based on an assumed limit of sulphur content in fuel of 1,000 ppm (0.1%), 5,000 ppm (0.5%), and 10,000 ppm (1.0%) Fuel Type Source Sulphur Content (wt%) Scenarios Baseline 10,000 ppm limit 5,000 ppm limit 1,000 ppm limit Percent Change from Baseline 10,000 ppm limit 5,000 ppm limit 1,000 ppm Limit HFO Domestic 1.5 1 0.5 0.1-33 -67-93 HFO International 2.7 1 0.5 0.1-63 -81-96 MDO Domestic 1 1 0.5 0.1 0-50 -90 MDO International 1 1 0.5 0.1 0-50 -90 MGO Domestic 0.17 0.17 0.17 0.1 0 0-41 MGO International 0.2 0.2 0.2 0.1 0 0-50

SECA, Engine Control Technologies and Emission Standards Update and Expansion of the MEIT: 1. Updated to accept multiple years of vessel data and calculate emission forecast/backcasts yearly from 1980 to 2030 2. West coast marine vessel traffic allocated to modelling regions:

SECA, Engine Control Technologies and Emission Standards Source: (VTOSS, Chamber of Shipping, 2007)

SECA, Engine Control Technologies and Emission Standards Update and Expansion of the MEIT (cont.): 3. Expanded MEIT s GHG emission estimation capabilities to include CO 2 e, CH 4, and N 2 O based on emission factors from Environment Canada s National Inventory Report, 2008 submission 4. Fuel consumption report was expanded to show fuel quality, domestic & international fuel proportion based on each fuel type 5. Marine vessel engines categorized based on the US EPA definition: Category C1 C2 C3 Rated Power 37 kw Displacement per Cylinder < 5 litres 5 and < 30 litres 30 litres

Future Enhancements update GHG emission factors based on new data from Environment Canada GHG Division add lock to database tables when running 'preprocessing' and 'calculate emissions' steps Forecasting: modify to use actual data when base year data is available in database (ex 2002, 2003, 2004) instead of growth factors add an interpolate/extrapolate function to fill gaps and project forward and backward

Future Enhancements (cont.) Speed up long processing times by moving away from 'record by record' approach to batch updates investigate reducing size of 'Emissions' table (5.9 million rows), eliminate data columns based on pivot table reporting needs migrate existing VBA code to SQL Server stored procedures to take advantage of server's superior performance (RAM, CPU, disk)

Exercise 1 Your boss has to make a presentation this afternoon and asks you to run the Marine Emission Inventory Tool to estimate emissions for the following scenario: Container Ship traffic at the Port of Québec NO x and SO 2 in tonnes 2004 base year

Exercise 2 Generate a greenhouse gas emission report for main engines from all vessels operating on Lake Erie while in cruise (underway) mode in January 2004.

Exercise 3 New economic indicators predict significant growth in container vessel shipments by 2030. Use the Marine Emission Inventory Tool to forecast SO x and PM 2.5 emissions at a 29% growth rate by 2030.

Wrap Up Thank-you for your interest. Questions? Klym Bolechowsky klym@clearskyeng.com (403) 982-5596