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Monday, May 13th<br />
Tuesday, May 14th<br />
Wednesday, May 15th<br />
Thursday, May 16th<br />
enough evidence to warrant consideration by OEMs for immediate<br />
use in large-bore gas engines.<br />
Wednesday May 15th / 15:30 – 17:00<br />
Aftertreatment – Particulate Filters<br />
Room C<br />
Development of DPF [diesel particulate filter] with a<br />
regenerator for marine diesel engines<br />
Minoru Tsuda, National Fisheries University, Japan<br />
Dai Yamanishi, National Fisheries University, Japan<br />
Kazuyuki Maeda, National Fisheries University, Japan<br />
PM emitted from diesel engines has harmful effects on human<br />
respiratory organs. Consequently, a severe restriction on its emission<br />
amount has been implemented and various PM reduction<br />
devices have been developed for cars. However, these PM reduction<br />
devices which utilise a catalyst are not applicable to ships.<br />
This is because HFO used for ships contains a large amount of<br />
sulphur. PM from marine diesel engines is composed of dry soot,<br />
soluble organic fraction (SOF), and sulfate. Regulations for decreasing<br />
the sulphur content in the fuel have been proposed by<br />
IMO. Implementation of these regulations will reduce the amount<br />
of sulphur in fuel from 3.5% to 0.5% globally by 2020 or 2025,<br />
and from 1.0% to 0.1% in ECAs by 2015. Reducing the sulphate<br />
content will decrease the total amount of PM emission from ships<br />
significantly, but the amount of dry soot and SOF emissions will<br />
remain the same. In this study, a basic experiment to investigate<br />
the effects and reproductions of a PM reduction filter for marine<br />
diesel engines was conducted. And then, a newly developed diesel<br />
particulate filter (DPF) with a regenerator was connected to the<br />
exhaust line of a high-speed marine diesel engine, and the effects<br />
of PM reduction and engine performances were investigated. The<br />
outlines of the experiments are as follows:<br />
• Effect of DPF on PM reduction: To clarify the effect of PM reduction<br />
by DPF, the filter material used for DPF was installed between<br />
the PM sampling probe set in the exhaust line of the test<br />
engine and the dilution tunnel. The components of PM were<br />
compared for the cases with and without the filter material. The<br />
engines used for the experiments are the low-speed marine diesel<br />
engine (7,722 kW) of the training ship Seiun Maru, which<br />
uses HFO and the high-speed marine diesel engine (103 kW) of<br />
the laboratory of the National Fisheries University, which uses<br />
gas oil and marine diesel oil (MDO).<br />
• Effective temperature and time for filter regeneration: Various<br />
temperatures were investigated for a given time in order to determine<br />
the appropriate temperature for filter regeneration in DPF.<br />
The collected elements on the filter were place into a furnace at<br />
a given temperature and the time required for regeneration was<br />
recorded.<br />
• Effect of the newly developed DPF on PM reduction: The DPF<br />
with a regenerator was connected to the exhaust line of a high<br />
speed marine diesel engine, and the effect of the device on PM<br />
emission and engine performance was investigated.<br />
• Regeneration of DPF: To remove PM on the filter, the DPF<br />
equipped with a heating apparatus and the filter was developed.<br />
The DPF was installed in the exhaust line of the engine, and an<br />
experiment on the regeneration of DPF was conducted.<br />
As a result, for practical applications of DPF for marine diesel engines,<br />
the following must be satisfied:<br />
• A comparison of the experimental data demonstrates that most<br />
of the dry soot can be removed by the DPF, but SOF and sulphate<br />
remain. This is because the required high temperature for<br />
the passage of the exhaust gas through DPF causes SOF and sulphate<br />
to become like gases.<br />
• The optimum temperature for assuring a complete regeneration<br />
within the first few minutes at a minimum electric power is determined<br />
to be 650°C. Temperatures lower than 650°C result in<br />
longer regeneration times, which is insufficient. Temperatures<br />
higher than 650°C may lead to shorter regeneration times, but<br />
the cost for the required electric power increases.<br />
• Though most of the dry soot and some of the SOF and sulphate<br />
in PM can be removed by DPF, it has been known that specific<br />
fuel consumption deteriorates by 3% when the exhaust gas pressure<br />
increases by a10-kPa interval.<br />
• PM can be removed by heating the filter to 650°C or more. As a<br />
result, a continuous regeneration of the DPF becomes possible<br />
without the need to change the filter.<br />
Verification testing of the l-ccrt(tm) particulate<br />
control system on an NREC 3GS21B genset<br />
locomotive<br />
John Hedrick, Southwest Research Institute, USA<br />
Steven Fritz, Southwest Research Institute, USA<br />
Paul Anderson, Johnson Matthey ECT, USA<br />
Jose Ramirez, Johnson Matthey ECT, USA<br />
Saji Pillai, Johnson Matthey, USA<br />
Richard Paczewski, Johnson Matthey, USA<br />
The Air Quality Improvement Program (AQIP), established by the<br />
California Alternative and Renewable Fuel, Vehicle Technology,<br />
Clean Air, and Carbon Reduction Act of 2007 (California Assembly<br />
Bill (AB) 118, Statutes of 2007, Chapter 750), is a voluntary<br />
incentive programme administered by the California Air Resources<br />
Board (CARB) to fund clean vehicle and equipment projects,<br />
research on biofuels production and the air quality impacts of<br />
alternative fuels, and workforce training. Within the AQIP are<br />
Advanced Technology Demonstration Projects, with the purpose<br />
of helping accelerate the next generation of advanced technology<br />
vehicles, equipment, or emission controls which are not yet commercialised.<br />
On May 28th, 2010, the City of Los Angeles Harbor<br />
Department and the Port of Long Beach jointly submitted a proposal<br />
to CARB for AB118 AQIP Advanced Technology Demonstration<br />
grant funding to demonstrate a Tier IV locomotive DPF retrofit<br />
system on a 2,100 HP genset switcher locomotive. The project<br />
partners included Johnson Matthey, Inc, the technology provider,<br />
and Union Pacific Railroad, which will use the retrofit system on<br />
a switching locomotive operating in the San Pedro Bay Ports. The<br />
test locomotive used for this project was UPY2755, an NREC model<br />
3GS21B, originally manufactured in July 2007. This locomotive<br />
uses three diesel-engine driven generator sets (Gen Set 1, 2, and<br />
3) to provide power to the locomotive traction motors. The locomotive<br />
was moved from the Los Angeles operating fleet of Union<br />
Pacific Railroad and sent to SwRI Locomotive Technology Center<br />
(LTC) in San Antonio, Texas, for installation and testing of three<br />
Johnson Matthey’s Diesel Particulate Filter (DPF) retrofit systems,<br />
L-CCRT. The JM L-CCRTTM system consists of a flow-through<br />
diesel oxidation catalyst (DOC) in front of a catalysed soot filter<br />
(CSF) coated with an oxidation catalyst. The system catalytically<br />
oxidises engine derived NO to NO 2<br />
and that NO 2<br />
continuously<br />
oxidises soot trapped in a catalysed wall flow filter. This continuous<br />
soot removal prevents the occurrence of excessive exhaust gas<br />
back pressure on the engine. The locomotive was modified to fit<br />
the three JM DPF housings, in place of the standard mufflers for<br />
each of the three engines. While the DPF housing is roughly the<br />
same footprint as the muffler, the DPF housing is taller than the<br />
stock muffler. As part of the modifications of the locomotive, the<br />
roof sections over the engines were modified to accept the taller<br />
DPF housing. After degreening the L-CCRT systems for 20 hours<br />
May 2013 | Schiff&Hafen | Ship&Offshore SPECIAL 63