AIR EMISSIONS from OCEANGOING VESSELS INTERTANKO Houston Tanker Event 2007 AIR EMISSIONS from OCEANGOING VESSELS INTERTANKO Houston Tanker Event 2007 Keith.

Slides:



Advertisements
Similar presentations
MARPOL Annex VI TRIPARTITE TOKYO 20th SEPTEMBER 2007.
Advertisements

Air Emissions Regulations Update Tripartite meeting 15/16 September 2006; Seoul
ASTM INTERNATIONAL SEMINAR ENVIRONMENTAL REQUIREMENTS DECEMBER 9, 2009
Air Emissions from Ships
Freight by Water Conference Teesside 7 September 2012 Sulphur Directive Impacts.
Alternative energy for shipping in Nordic waters
Hellenic Forum Athens 6 March 2007 Peter M. Swift.
USE OF MDO BY SHIPS PART OF A HOLISTIC APPROACH BUNKER SUMMIT – GREECE 2007
Green Ship Design Design for Environmentally Friend Ship in Shipbuilding ・ Less Hazardous Materials ・ Less CO 2 Demand for Ship Operation ・ Less Engine.
Environmental Bunker legislation and the Potential Impact on the Vancouver Market May 2014 May
Emission Control Technology for Marine Applications.
1 Air Quality Regulation in California Critical Issues in Greenhouse Gases, Stationary Sources & Mobil Source Emissions January 12, 2007 Jim Flanagan.
UPDATE ON THE REVISION OF MARPOL ANNEX VI LATIN AMERICAN PANEL March 12-13, 2008 Miami Beach, Florida.
UPDATE ON THE REVISION OF MARPOL ANNEX VI NORTH AMERICAN PANEL March 17, 2008 Stamford, CT.
Clean Fuels for Ships Practical Solution for MARPOL Annex VI and GHG Emissions Reduction MARTECMA Seminar 21 January 2008 Athens Dragos Rauta - INTERTANKO.
| 1 | 1 REDUCING THE IMPACT OF SHIPPING ON THE ENVIRONMENT DECARBONISATION.
Air Emissions from Ships. Society is driving the requirement for ships to reduce harmful air emissions from engine exhausts.
1 MARPOL – Annex VI Control of Air Pollution from Ships from Ships and its Current Revision process Dr. Tim Gunner, Technical Consultant, Intertanko.
MARPOL ANNEX VI AMENDMENTS PRACTICAL CONSEQUENCES Tripartite Meeting Beijing CCS Headquarters November 8/9, 2008.
Mitigating Air Emissions – A Shipowner Point of View Kevin Krick APL Head of Security and Environment, Americas NAMEPA 18 FEB 2015.
NAMEPA 2014 Annual Conference New York City Canada and North American Emission Control Area RDIMS #
NAMEPA 2014 World Maritime Day Observance Cozumel, Mexico Canada's Experience with the North American Emission Control Area RDIMS #
Impact of Fuel Sulfur on Vehicle Emissions Nazeer Bhore Fuels Development and Policy Planning ExxonMobil Refining and Supply Co. Fairfax, VA Latin.
INTERTANKO Asian Panel Tokyo 18 September 2007
IMO requirements to reduce emission to air from ships by Manager Research and Projects Gdansk April 2008 ‘
Air pollution from ships: recent developments by Lex Burgel by Lex Burgel.
LNG - LOOKING AHEAD. High speed liner service in US Domestic Trade Washington to Alaska Florida to Puerto Rico Logistics based operations in Alaska, Hawaii.
Study on future fuels for cargo vessels in the Baltic Sea
Sea Water Scrubber. INTRODUCTION Crystallox has developed a new generation of horizontal and vertical scrubbers for marine and land based applications.
Sohail Ghanchi Energy Technology and Policy The University of Texas at Austin.
“ Revision of Marpol Annex VI and its implications for the Gulf region ” Peter M. Swift, MD, INTERTANKO 15 December 2008, Dubai.
Environmental Landscape A burden or opportunity? Tony Field South East Europe Marine Business Manager.
CALIFORNIA STATE LANDS COMMISSION CUSTOMER SERVICE MEETING OCTOBER 28, 2009 MARINE AIR EMISSION CONTROL AND FUEL SWITCHING JOE ANGELO DEPUTY MANAGING DIRECTOR.
Title: Coal Cowboy Duration: 00:12:51 Link: engr
Environment and Reduction of Emissions The Application in Ships
Maritime Law Association Spring Meeting April 28-30, 2015
Name:Goh Choong Leoong Student No: P Date: 30/08/06.
OTC Mobile Source Committee OTC Committee Meeting September 2009 Buffalo, New York 1.
0 Office of Transportation and Air Quality Update for Air Directors: Transportation and Air Quality Christopher Grundler Deputy Director NACAA Spring Meeting.
Freeport Generating Project Project Description Modernization projects at Power Plant #2 Developers – Freeport Electric and Selected Development Company.
Marine Fuels Where are we? Where are we going? How will we get there?
Compression Ignition Marine Emissions Where are we now? What’s likely to be in the next Marine Rule?
A SEMINAR ON NOx REDUCTION BY FUEL WATER EMULSION INJECTION
Håkon B. Thoresen, DNV Petroleum Services, Norway 31 Jan 2011 Fuel Quality - Update INTERTANKO Bunker Sub-committee, London.
IBC 2009 APRIL 23, 2009 FACING THE CHALLENGES TO REDUCE AIR EMISSIONS FROM SHIPS JOSEPH ANGELO DEPUTY MANAGING DIRECTOR.
University of Turku CENTRE FOR MARITIME STUDIES 0 NOx emissions from ships - consequences for shipping and Baltic ports BPO Seminar & Debate: Baltic Ports.
A Practical guide to wartsila scrubber systems
The INTERTANKO option for the revision of Annex VI - IMO regulation for the Prevention of Air Pollution from ships by Manager.
Maritime Environmental Regulations & the Challenges of Compliance
Dr. Haakon-Elizabeth Lindstad and Professor Gunnar. S. Eskeland
IBIA ANNUAL CONVENTION SEPTEMBER 11, 2007 REDUCING AIR EMISSIONS FROM SHIPS JOSEPH ANGELO DIRECTOR, REGULATORY AFFAIRS AND THE AMERICAS.
AIR EMISSIONS FROM SHIPPING Reducing Atmospheric Pollution Globally: Kristian R. Fuglesang The distillate solution.
Hellenic Forum 27 March 2008 Athens Peter M. Swift.
BUNKERWORLD – MARINE FUEL SUSTAINABILITY FORUM OCTOBER 25, 2007
The INTERTANKO options to meet marine environmental challenges by Manager Research and Projects Global Forum Strategic Planning.
Insert a DP2 Photo here GE Transportation Freight, Fuel, & Emissions Introduction to Engineering Design EDGSN 100 Section 001 Team Armadillo, Team #7 Dan.
Why LNG? Fuelling Operations Feb 2016 Tom Strang SVP Maritime Affairs Carnival Corp & plc.
Greek Shipping Summit 2007 Athens 8 November 2007 Peter M. Swift.
What have we learned in the meantime?
2007 Emissions Inventory. Topics First emissions inventory under Clean Air Action Plan (CAAP) Emissions inventory methodology Cargo throughput changes.
EEB Clean Air Seminar 20 Nov Lisbon Air Pollution from ships Portuguese perspective.
Air Emissions from Ships: The Changing Landscape Bryan Wood-Thomas EEB Clean Air Seminar World Shipping Council 20 November 2008.
NORTH AMERICAN PANEL OCTOBER 22, 2007 REDUCING AIR EMISSIONS FROM SHIPS JOSEPH ANGELO DEPUTY MANAGING DIRECTOR.
MARPOL.
MARITIME AIR EMISSIONS Lloyd’s List events 11 December 2007 Distillates THE Solution THE holistic solution for the revision of MARPOL Annex VI Peter.
First in Service First in Value
Low Emissions Products from Aalborg Industries
Vapor Emission Control System
“The Environmental Challenge”
M. Amann, W. Asman, I. Bertok, J. Cofala, C. Heyes,
Presentation transcript:

AIR EMISSIONS from OCEANGOING VESSELS INTERTANKO Houston Tanker Event 2007 AIR EMISSIONS from OCEANGOING VESSELS INTERTANKO Houston Tanker Event 2007 Keith Michel Herbert Engineering Corp.

Transport Mode Efficiency (assumes Aframax Tanker burning 2.6% Sulfur Fuel with return voyage in ballast) Shipping is the most efficient mode for moving cargo Shipping is the most efficient mode for moving cargo

Air Emissions from Cargo Ships Over 90% of world trade is moved by the international commercial shipping industry. Over 90% of world trade is moved by the international commercial shipping industry. Oceangoing ships are responsible for a significant percentage of total worldwide emissions: 18-30% of NOx, 6-10% of SOx, 3-5% of CO 2. Oceangoing ships are responsible for a significant percentage of total worldwide emissions: 18-30% of NOx, 6-10% of SOx, 3-5% of CO 2. Studies clearly demonstrate the health hazards of NOx and PM pollutants. Studies clearly demonstrate the health hazards of NOx and PM pollutants. Anthropogenic input now widely accepted as a major contributor to global warming. Anthropogenic input now widely accepted as a major contributor to global warming.

Regulations: ANNEX VI Maximum 4.5% sulfur content. Maximum 4.5% sulfur content. Established limits for NOx (example: 17 g/kW h applicable to slow speed diesel engines) Established limits for NOx (example: 17 g/kW h applicable to slow speed diesel engines) Established concept of SECA’s Initially in Baltic; North Sea in Aug 2007 (max. 1.5% sulfur or equivalent) Established concept of SECA’s Initially in Baltic; North Sea in Aug 2007 (max. 1.5% sulfur or equivalent)

Proposal for Revision of Annex VI INTERTANKO (BLG-WGAP 1/2/5) A Global Sulfur Emission Control Area (applicable worldwide) A Global Sulfur Emission Control Area (applicable worldwide) From 2010, distillate fuels with a 1.0% sulfur cap. From 2010, distillate fuels with a 1.0% sulfur cap. For ship engines installed from 2015, a maximum 0.5% sulfur cap. For ship engines installed from 2015, a maximum 0.5% sulfur cap.

Proposal for Revision of Annex VI United States (BLG 11/5/15) Sulfur Emission Control Area (applicable within 200 nm of coastlines) --Use distillate with 0.1% sulfur cap or comply with SOx and PM limits Sulfur Emission Control Area (applicable within 200 nm of coastlines) --Use distillate with 0.1% sulfur cap or comply with SOx and PM limits For new engines > 30 liters / cylinder: Tier II: 15-25% NOx reduction in 2011 Tier III: 80% NOx reduction in 2016 For new engines > 30 liters / cylinder: Tier II: 15-25% NOx reduction in 2011 Tier III: 80% NOx reduction in % reduction in NOx for certain existing engines by % reduction in NOx for certain existing engines by 2012.

Proposal for Revision of Annex VI NORWAY ( BLG 11/5/22, 11/5/23, 11/5/24 ) Global sulfur emission area -- a 0.5% sulfur cap by 2015 applicable to all ships Global sulfur emission area -- a 0.5% sulfur cap by 2015 applicable to all ships NOx reduction for new ships Tier II: 20% reduction in 2010 Tier III: 40% reduction in 2015 NOx reduction for new ships Tier II: 20% reduction in 2010 Tier III: 40% reduction in 2015 NOx reduction for existing S/S diesel ships Tier I: in 2010 for ships built (to ANNEX VI limit of 17 g/kW h) NOx reduction for existing S/S diesel ships Tier I: in 2010 for ships built (to ANNEX VI limit of 17 g/kW h)

California (CARB) Regulation for Auxiliary Engines Applicable to vessels operating within 24nm of coast of California Applicable to vessels operating within 24nm of coast of California As of Jan. 1, 2007, requires burning of MGO or MDO with a maximum sulfur content of 0.5%. As of Jan. 1, 2007, requires burning of MGO or MDO with a maximum sulfur content of 0.5%. As of Jan. 1, 2010, requires burning of MGO with a maximum sulfur content of 0.1%. (subject to review in 2008) As of Jan. 1, 2010, requires burning of MGO with a maximum sulfur content of 0.1%. (subject to review in 2008)

EPA Regulations for U.S. Flag Vessels - Tier 2 For newbuildings after Jan 1, 2007, Tier 2 requirements for Category 1 & 2 engines (<30 liters per cylinder). For newbuildings after Jan 1, 2007, Tier 2 requirements for Category 1 & 2 engines (<30 liters per cylinder). Tier 2 levels add particulate (PM) limits, and includes hydrocarbon (HC) in the allowable NOx levels that are lower than Annex VI requirements. Tier 2 levels add particulate (PM) limits, and includes hydrocarbon (HC) in the allowable NOx levels that are lower than Annex VI requirements. Tier 2 PM + NOx limits have been obtained only by burning MGO. Native ash + sulfur in MDO are higher than allowed in exhaust. Engine modifications to meet NOx requirements are needed (or equivalent after-treatment) Tier 2 PM + NOx limits have been obtained only by burning MGO. Native ash + sulfur in MDO are higher than allowed in exhaust. Engine modifications to meet NOx requirements are needed (or equivalent after-treatment) Applicable to new US Flag vessels worldwide. Applicable to new US Flag vessels worldwide. Over the next 10 years, reduction from U.S. flag oceangoing vessels will impact total emissions of Sox, PM, and NOx within U.S. coastal waters by less the 0.25%. Over the next 10 years, reduction from U.S. flag oceangoing vessels will impact total emissions of Sox, PM, and NOx within U.S. coastal waters by less the 0.25%.

EPA Regulations for U.S. Flag Vessels - Tier 3 For newbuildings beginning in , EPA has proposed Tier 3 requirements for Category 1 & 2 engines. For newbuildings beginning in , EPA has proposed Tier 3 requirements for Category 1 & 2 engines. Tier 3 further reduces PM by 50% and NOx by 20% and returns to separate HC and NOx limits. Tier 3 further reduces PM by 50% and NOx by 20% and returns to separate HC and NOx limits. Tier 3 limits are expected to be made by engine modifications and low sulfur distillate fuel. Tier 3 limits are expected to be made by engine modifications and low sulfur distillate fuel.

EPA Regulations for U.S. Flag Vessels – Basis For newbuildings beginning in , EPA proposes Tier IV requirements for Category 1 & 2 engines. Tier 4 reduces PM, and lowers all NOx to 1.8 g/kW-hr and all HC to 0.19 g/kW-hr. (NOx by 80% and PM by 90%). For newbuildings beginning in , EPA proposes Tier IV requirements for Category 1 & 2 engines. Tier 4 reduces PM, and lowers all NOx to 1.8 g/kW-hr and all HC to 0.19 g/kW-hr. (NOx by 80% and PM by 90%). Tier 4 limits are based on % S distillate and after treatment of exhaust. Tier 4 limits are based on % S distillate and after treatment of exhaust. Proposed rules for Category 3 engines (>30 liters) originally expected in April, 2007 have been delayed. Conjecture is that these will resemble the proposal to IMO (BLG 11/5/15) Proposed rules for Category 3 engines (>30 liters) originally expected in April, 2007 have been delayed. Conjecture is that these will resemble the proposal to IMO (BLG 11/5/15)

Scrubbers Seawater is the scrubbing medium Seawater is the scrubbing medium SOx reduction to 99% SOx reduction to 99% NOx reduction to 5% NOx reduction to 5% Particulate reduction to 80% Particulate reduction to 80% Currently have designs to 9MW; designs for range 25MW to 50MW under development Currently have designs to 9MW; designs for range 25MW to 50MW under development Web based emissions monitoring Web based emissions monitoring In stack exhaust gas monitoring for NO NO2 CO2 & SO2…… SWS HC Funnel Space Discharge water monitor pH 7.0 Oil <0.5ppm CCS 50t/hr 1 MW Exhaust Dry gas <80%RH 10 kg dry sludge/day Engine Room KRYSTALLON SCRUBBING SYSTEM

Urea carried as 40% solution Urea carried as 40% solution Injection rate 5% to 8% by weight of the fuel Injection rate 5% to 8% by weight of the fuel NOx reduction % NOx reduction % With additional oxidation catalyst HC reduction % With additional oxidation catalyst HC reduction % Exhaust gas temperature must be maintained between 320 and 500 o C for reaction Exhaust gas temperature must be maintained between 320 and 500 o C for reaction Not tolerant of high sulfur. As sulfur increases, temperature must increase. Not tolerant of high sulfur. As sulfur increases, temperature must increase. Not tolerant of used lube oil mixed into fuel. Not tolerant of used lube oil mixed into fuel. Catalyst life is 10,000 to 40,000 hours with max of 100,000 hours Catalyst life is 10,000 to 40,000 hours with max of 100,000 hours Selective Catalytic Reduction (SCR) Urea Injection Urea Tank Urea Pump SCR MUNTERS –SCR CONVERTER

SCR Retrofit on Matson Containership Mokihana SCR Connection to Injection Pipe Injection Pipe Connection to Turbocharger

Emulsified Fuel Oil Sea to Sky Emulsifier unit 5 to 25% fresh water (by weight) added to fuel 5 to 25% fresh water (by weight) added to fuel Fuel water emulsion has higher viscosity than fuel alone Fuel water emulsion has higher viscosity than fuel alone Higher fuel delivery temperature is required to achieve proper viscosity Higher fuel delivery temperature is required to achieve proper viscosity Fuel pressure must be higher than the saturation pressure of the water at delivery temperature Fuel pressure must be higher than the saturation pressure of the water at delivery temperature Addition of water without increasing pump sizes limits maximum power output Addition of water without increasing pump sizes limits maximum power output NOx reduction of 20% expected with 20% fresh water injection NOx reduction of 20% expected with 20% fresh water injection Manufacture claims PM reduction of 40% to 60% Manufacture claims PM reduction of 40% to 60% No affect on SOx and CO 2 No affect on SOx and CO 2

Comparison of Emission Control Methods Emission Control Method NOxSOxPMCO2HC MDO (1.0% S) 5%65% 5% MGO (0.5% S) 5%85% 5% SCR * 80%---15%---70% Scrubber 5%95%80%---- Emulsification 20%---40%--- Reductions for MDO & MGO based on comparison to 2.7% S HFO * assumes SCR arranged with oxidation catalyst stage ** assumes 20% water injection (reduction estimates per manufacturer literature)

Expected Emission Reductions A global SECA with MDO (1% S Cap) will lower overall oceangoing vessel SOx and PM emissions by approx. 45%. With MGO (0.5% S Cap), reduction in Sox and PM will be approximately 65%. A global SECA with MDO (1% S Cap) will lower overall oceangoing vessel SOx and PM emissions by approx. 45%. With MGO (0.5% S Cap), reduction in Sox and PM will be approximately 65%. A 200nm worldwide SECA with 0.1% S fuel will reduce SOx and PM in SECA’s by about 75%. Overall, reductions of about 40% can be expected. A 200nm worldwide SECA with 0.1% S fuel will reduce SOx and PM in SECA’s by about 75%. Overall, reductions of about 40% can be expected.

Open Questions Should low sulfur fuel caps be mandated, or should emission limits be set and alternative technologies permitted? Should low sulfur fuel caps be mandated, or should emission limits be set and alternative technologies permitted? Should a global SECA be established, or should emission standards be applied for defined regions? Should a global SECA be established, or should emission standards be applied for defined regions?

Need for Comparative Study There is a need for a comparative study that: Considers all pollutants of concern (SOx, NOx, PM, GHG, effluent into water, disposal of waste, …). Considers all pollutants of concern (SOx, NOx, PM, GHG, effluent into water, disposal of waste, …). Considers emissions over the complete chain from manufacture of equipment and refinement of crude through recyling & disposal. Considers emissions over the complete chain from manufacture of equipment and refinement of crude through recyling & disposal. Accounts for all relevant costs (capital, operating, M&R, etc.) Accounts for all relevant costs (capital, operating, M&R, etc.) Account for the relative safety and performance risk of the different technologies. Account for the relative safety and performance risk of the different technologies. Also, further research is needed on the fate and transport of emissions from ships. Also, further research is needed on the fate and transport of emissions from ships.