Non-thermal plasma based technologies for the aftertreatment of … · 2014-03-11 · technologies...

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Copyright Accentus 2003 Non-thermal plasma based technologies for the aftertreatment of diesel exhaust particulates and NOx Roy McAdams DEER 2003, Newport, Rhode Island 28th August 2003 accentus

Transcript of Non-thermal plasma based technologies for the aftertreatment of … · 2014-03-11 · technologies...

Page 1: Non-thermal plasma based technologies for the aftertreatment of … · 2014-03-11 · technologies for the aftertreatment of diesel exhaust particulates and NOx Roy McAdams DEER 2003,

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Non-thermal plasma based technologies for the aftertreatment of diesel exhaust particulates and NOx

Roy McAdams

DEER 2003, Newport, Rhode Island28th August 2003

accentus

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Overview

• Passenger car application– Diesel Particulate Filter

• trapping efficiency• testing

– In partnership with Eberspächer• Marine diesel exhaust application

– Plasma Assisted Catalysis of NOx• drivers• programme overview

– In partnership with Ministry of Defence - Warship Support Agency

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Electrocat™ DPF

Dielectric barrier discharge

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Improved Filtration

Pellets 50-60% filtration

Cordierite Monoliths

Ceramic Fibres and Foams

Meshes & Sintered Metal

Improved

Filtration

90%+

80%+

90%+

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DOC

Electrocat DPF

3-litre DIDiesel Engine

Smoke meter

Pressure

Pressure

Pressure&

Temperature

Thermocouples

Electrocat™ DPF

Testing of plasma regenerated sintered metal fibre filter

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Filtration efficiency

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PM Engine Out

PM After DPF

% Filtration Efficiency

Speed 1500rpm Torque 60-260 Nm in 30Nm steps

Filtration efficiency tested from clean condition

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Load 2000rpm 150NmRegen 2000rpm 237NmInlet temp ~375-400°C

Regeneration

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pre

ssu

re (

mb

ar)

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rqu

e (

Nm

) Load phase

Thermal regeneration

Plasmaregeneration

Plasma ON

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Cyclic regeneration

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rege

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DPF Current status

• Highlights– 95-100% filtration efficiency– Filter regeneration demonstrated at powers down to 500W– Rapid initiation of filter regeneration on application of plasma– Regeneration demonstrated over lower temperature range

~90-200°C– Flexible operating strategy demonstrated

• Future development– Increased capacity of system e.g. filter surface area– Improved performance and power efficiency

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Emissions drivers for marine diesels

• Present legislation– MARPOL ANNEX VI (1997)*

• NOx emissions• met by on engine methods

– Fairway & port differential fees (e.g. Sweden, Hamburg)• Probably not presently cost effective for Royal Navy to use

aftertreatment

• Future legislation– NOx - further reduction– Particulate matter (PM)– Others (Poly-Aromatic Hydrocarbons)– Timescales?

*This Annex will enter into force 12 months after being ratified by at least 15 States whose combined fleets of merchant shipping constitute at least 50%of the world fleet. At the time of writing this report 10 States (Bahamas, Bangladesh, Denmark, Greece, Liberia, Marshall Islands, Norway, Panama,

Singapore and Sweden) whose combined tonnage represents 52.56% of the world tonnage have ratified the Annex. (Source: http://www.imo.org).

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NOx emissions limits

MARPOL ANNEX VI and the future

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Aftertreatment - SCR/ Non-thermal Plasmas

MARPOL Annex VI

Pr i ma r y E n g i n e M e a n s

Future NOx legislation?

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SCR - Impact on operational capability

• Royal Navy have tested full scale SCR system– 1.4MW Paxman Valenta

• Liquid urea storage– Type 23 Frigate: estimate converted 35 m3 fuel tank of urea

solution would last 4 months

• Urea purchased as solid– storage before mixing - where on vessel?– impact on water supply

• World-wide bunkering/availability?– Bunkered as aqueous solution (6 month shelf life)?

• Additional manpower requirements – Royal Navy moving to Reliability Centred Maintenance

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Non-Thermal Plasma NOx reduction

• Non-thermal plasma– well placed to meet future legislation

• potential for combined NOx/particulate– diesel fuel reductant

• already available on board• fuel penalty 2 - 5% over operating cycle

– low load potential & shock tolerance

• Programme– 1/10th scale

• build• test• evaluate• retest

Laboratory scale evaluation

1/10th scale demonstrator

Full scale system build

STAGE 1 STAGE 2 STAGE 3

Electrocat™ / plasma development and exploitation

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NTP Target specifications

• NOx reduction >90%• Noise attenuation >25 dB(A)• Weight 20-50% additional to

silencer• Space requirement equivalent to

silencer• Power increase <5% • Lifetime of mean engine overhaul

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Plasma assisted NOx reduction

NOx catalyst in synthetic exhaust• 2% Ag/Al2O3 with propene or RF73 fuel reductant

90% N2, 10% O2, 500 ppm NOxSV = 10,000/h, C1:NOx = 6 RF73 fuel

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Specific energy = 60 J/L 90% N2 10% O2

Space velocity ~ 10,000/hr C1:NOx = 6 propene

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THC, no plasma

THC + plasma

Inlet values

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NOx reduction in genset exhaust

NOx catalyst in genset exhaust• RF73 (~0.043% sulphur) fuel in genset

RF73 fuel, FilteredSV = 10,000/h, C1:NOx = 6, propene

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RF73 fuel, FilteredSV = 10,000/h, C1:NOx = 6, RF73 reductant

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Full scale concept to 1/10th scale system

• 1/10th scale system design– treat 1/10th flow from indicative

engine– based on (evolving) full scale

concept• minimises potential for new

development issues – full scale concept will match

predefined envelope for an example Type 23 fit

• ship integration/safety needs accounted for

– maximise flexibility to address other fits as easily as possible

• modularity

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Type 23 Frigate fit

• Notional fit within both UAMR and FAMR

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Integrated 1/10th scale system

• Type 23 Frigate gensets– 4x Paxman Valenta 1.4 MW– exhaust ~ 8200 kg/hr @ rated

speed and power

• 1/10th scale system– 10kW capability (>5% at 1/10th

scale)

• Functional testing before trials– power– diagnostics– EMC (radiated and conducted)

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Plasma and catalyst system

• Flow through plasma and catalyst controlled by divertor valve

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Initial test cell trials

• Carried out at MAN B&W Paxman site, Colchester, Essex– Development 18VP185 engine (0.1%S fuel)

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Plasma/catalyst performance

• D2 Cycle Mode 1– rated power and speed (3.25MW, 1800 rpm)

Mode 1 C1: NOx = 6 Space velocity ~ 9000/hr 37mm orifice plate

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NO

x, N

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m v

ol)

NOxNONO2

Inlet values

Flow ~ 300 m3/hr

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Plasma/catalyst performance

• “Sprint Mode”– 4MW, 1950 rpm - hotter exhaust gas

Sprint Mode C1: NOx = 6 Space velocity ~ 10000/hr 37mm orifice plate

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Performance enhancement

Lab scale vs 1/10th scaleISSUE EFFECT STATUS COMMENT

Power measurement Specific energy error Checked Power measurement

Flow measurement Specific energy/spacevelocity error

Checked Flow measured independentlyCatalyst volume variedFlow varied

Catalyst temperaturelow

Lower NOx reduction Checked Temperature measurement in catalyst module

Flow distributionthrough modules

Lower specific energy/higher space velocity

Initial check Use of alternative catalyst modules with simpler, knownflow distributionCFD?

Fuel sulphur level Catalyst poisoning Being checked Sulphur measured on used catalystCatalyst testing at various sulphur levels

Particulate build up inplasma module

Lower hydrocarbonactivation

To be checked Effect on waveforms?Testing at module or system level in air or diesel exhaustwithout particulates

Particulate build up oncatalyst

Catalyst deactivation To be checked Carbon measured on used catalystTesting at module or system level in air or diesel exhaustwithout particulates

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Sulphur tolerance of catalyst

• Used varying sulphur level fuels– F76 is Royal Navy fuel specification

• typically 0.1%S but can be up to 1%SF76 - 0.12% sulphur fuel, Filtered, Catalyst temp ~ 420 oC,

SV = 10,000/h, C1:NOx = 6, propene, 60 J/l

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Ongoing / Future work

• Optimising system performance - ongoing– catalyst development and sulphur tolerance– identify performance limitations

• Further test cell trials of 1/10th scale system– early 2004

• Project HERCULES (start early 2004)– High Efficiency R&D on Combustion for Ultra-Low Emissions

from Ships - diesel engines– EU VIth Framework programme-33M -43 partners– Technology showcase