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Auto Exhaust Catalysis

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Title: Auto Exhaust Catalysis


1
Auto Exhaust Catalysis
Jude vimal michael.R
  • Childrens club lecture series
  • National Centre for Catalysis Research
  • IIT-Madras
  • 27April 2009

2
What this picture suggest?
3
Composition of Exhaust Gas
4
Major Pollutants
  • The pollutants present in auto exhaust gas are
  • Sulphur dioxide, SO2 (primary pollutant)
  • Nitrogen oxides NOx (primary or secondary
    pollutants)
  • Particulate matter PM (primary and secondary
    pollutants)
  • Carbon monoxide, CO, (primary pollutant)
  • (volatile) organic compounds, HC (or VOCs)
    (primary and secondary pollutants), and
    photochemical oxidants,
  • PAN -peroxyacetyl nitrate(secondary pollutants).

5
Composition of diesel exhaust
  • DE is a complex mixture of hundreds of
    constituents in either a gas or particle form.
  • Gaseous components of DE include carbon dioxide,
    oxygen, nitrogen, water vapor, carbon monoxide,
    nitrogen compounds, sulfur compounds, and
    numerous low-molecular-weight hydrocarbons.
  • Among the gaseous hydrocarbon components of DE
    that are individually known to be of
    toxicological relevance are the aldehydes (e.g.,
    formaldehyde, acetaldehyde, acrolein), benzene,
    1, 3-butadiene, and polycyclic aromatic
    hydrocarbons (PAHs) and nitro-PAHs.

6
Contd..
  • DPM consists of fine particles (fine particles
    have a diameter lt2.5µm), including a subgroup
    with a large number of ultrafine particles
    (ultrafine particles have a diameter lt0.1µm).
    Collectively, these particles have a large
    surface area which makes them an excellent medium
    for adsorbing organics.
  • Their small size makes them highly respirable and
    able to reach the deep lung. A number of
    potentially 1-1 toxicologically relevant organic
    compounds are on the particles.
  • The particles present in DE (i.e., diesel
    particulate matter DPM) are composed of a
    center core of elemental carbon and adsorbed
    organic compounds, as well as small amounts of
    sulfate, nitrate, metals, and other trace
    elements.

7
Ill effects of Exhaust emission
  • The hazards include acute exposure-related
    symptoms, chronic exposure related non-cancer
    respiratory effects, and lung cancer.
  • The health hazard conclusions are based on
    exhaust emissions from diesel engines built prior
    to the mid-1990s. With current engine use
    including some new and many older engines
    (engines typically stay in service for a long
    time)
  • The health hazard conclusions, in general, are
    applicable to engines currently in use. As new
    and cleaner diesel engines, together with
    different diesel fuels, replace a substantial
    number of existing engines, the general
    applicability of the health hazard conclusions
    will need to be reevaluated.

8
Contd..
  • According to the pollutants exposure the effects
    are classified as
  • Acute (Short-Term Exposure) Effects
  • Chronic (Long-Term Exposure) Non-cancer
    Respiratory Effects
  • And Chronic (Long-Term Exposure) Carcinogenic
    Effects.

9
Emission standards
10
Emission Norms
  • The Globally automotive pollution is controlled
    by various emission performance standards set by
    countries according to their population and
    economic considerations.
  • The Emission Performance standard is the
    requirements that set specific limits to the
    amount of pollutants that can be released into
    the environment.
  • Many emissions standards focus on regulating
    pollutants released by automobiles (motor cars)
    and other powered vehicles but they can also
    regulate emissions from industry, power plants,
    small equipment such as lawn mowers and diesel
    generators.
  • Did you notice the Tamil nadu pollution control
    notice board in velachery gate-IITM

11
Overview - Emission norms in India
  • 1991 - Idle CO Limits for Gasoline Vehicles and
    Free Acceleration Smoke for Diesel Vehicles, Mass
    Emission Norms for Gasoline Vehicles.
  • 1992 - Mass Emission Norms for Diesel Vehicles.
  • 1996 - Revision of Mass Emission Norms for
    Gasoline and Diesel Vehicles, mandatory fitment
    of Catalytic Converter for Cars in Metros on
    Unleaded Gasoline.
  • 1998 - Cold Start Norms Introduced.
  • 2000 - India 2000 (Eq. to Euro I) Norms, Modified
    IDC (Indian Driving Cycle), Bharat Stage II Norms
    for Delhi.
  • 2001 - Bharat Stage II (Eq. to Euro II) Norms for
    All Metros, Emission Norms for CNG LPG
    Vehicles.
  • 2003 - Bharat Stage II (Eq. to Euro II) Norms for
    11 major cities.
  • 2005 - From 1 April Bharat Stage III (Eq. to Euro
    III) Norms for 11 major cities.
  • 2010 - Bharat Stage III Emission Norms for
    4-wheelers for entire country whereas Bharat
    Stage - IV (Eq. to Euro IV) for 11 major cities.
    Bharat Stage IV also has norms on OBD (similar to
    Euro III but diluted)

12
What is that Euro Norms
13
Contd..
  • The European Union standards for emission limits
    of automotive exhaust gases (values in g km-1)
    are given in the Table previous slide.
  • The typical concentration of the various
    pollutants are listed out and when our (Bharat
    stage IV) compared to the European standards we
    lag behind nearly 5 years.

14
VARIOUS METHODS OF AUTO EMISSION ABATEMENT
  • Modification of engine design (e.g., the fuel
    management system) and the engine calibration
    (e.g., the ignition timing) to decrease the
    engine output (also called raw emission)
  • Aftertreatment of the engine exhaust by solid
    catalysts, to convert the engine raw emission
  • A combination of engine exhaust after treatment
    by solid catalysts with engine design
    modification and/or controlled engine operation,
    to allow optimal functioning of the
    aftertreatment device.

15
Particulate Filter
16
Various Methods
  • Retrofit
  • Diesel retrofit involves the addition of an
    emission control device to remove emissions from
    the engine exhaust.
  • Retrofits can be very effective at reducing
    emissions, eliminating up to 90 percent of
    pollutants in some cases.
  • Some examples - Diesel oxidation catalysts,
    diesel particulate filters, NOx catalysts,
    selective catalytic reduction, and exhaust gas
    recirculation. Devices to control crankcase
    emissions also exist.
  • Repower
  • Repowering involves replacing an existing engine
    with a new engine. This strategy is most
    effective for use in diesel-powered equipment
    with a useful life longer than that of the
    engine.
  • Rebuild
  • All diesel equipment requires periodic
    maintenance. Routine maintenance and repairs help
    to ensure that engines operate at maximum
    performance and emission rates do not exceed the
    designed standard.

17
Contd..
  • Refuel
  • A variety of alternative fuels can be used in
    diesel engines. Some require little or no
    modification to the engine while others require
    engine conversion or replacement.
  • Some of the alternative fuels include emulsified
    diesel, biodiesel, natural gas, propane and
    ethanol. In addition to these fuels, use of
    diesel fuel with lower sulfur content can help to
    reduce emissions.
  • Replace
  • Replacement involves retiring higher polluting
    equipment from service before it would otherwise
    be retired. Newer equipment that meets more
    stringent emission standards is purchased to
    replace the retire equipment.

18
Challenges in the development automotive catalyst
  • Reducing the base emissions from the engine by
    improvements to the combustion process and fuel
    management, addition of air injection or exhaust
    gas recycle or by changes to the type of fuel or
    its composition.
  • Decreasing the time taken for the catalytic
    converter to reach its full operating efficiency.
  • Increasing the conversion efficiency of
    catalysts at their working temperature.
  • Store pollutants during the cold start for the
    release when the catalyst is working.
  • Device catalysts or strategies to destroy
    nitrogen oxides under lean (oxygen rich)
    operation.
  • Devise reliable ways to regenerate particulate
    filters.
  • Increase the operating lifetime during which
    autocatalysts and their supporting systems
    efficiently convert pollution.

19
Location of catalytic converter
20
Monolith
Typical automotive exhaust converters. The one on
the left has been cut open to reveal the
monolith. The insert shows a blow up of the upper
part of the monolith where a part has been
chipped off
21
Reactions
22
Concepts for catalytic aftertreatment
  • Five basic catalytic concepts have been used in
    the development of catalytic emission control
    they are
  • Closed loop control catalyst
  • Open loop catalyst
  • Dual bed catalyst
  • Oxidation catalyst
  • Lean oxidation catalyst

23
Operating window concept
24
(No Transcript)
25
Closed loop control catalyst
  • In the closed-loop-controlled three-way catalyst,
    one type of catalyst, which is placed in the
    exhaust gas stream, is able to promote all the
    main reactions that lead to the simultaneous
    removal of CO, HCs and NOx.
  • To balance the extent of the oxidation and the
    reduction reactions, the composition of the
    engine-out exhaust gas is maintained at or around
    stoichiometry.
  • This is achieved by a closed-loop engine
    operation control, in which the oxygen content of
    the engine-out exhaust gas is measured upstream
    of the catalyst with an electrochemical oxygen
    sensor, also called the lambda sensor.
  • This component is used by the engine management
    system to regulate the amount of fuel fed into
    the engine, and so to regulate the engine
    operation around the stoichiometric A/F ratio.

26
Various catalyst types
27
Contd..
  • The extent of the secondary reactions is minimal
    under these conditions. The feedback control of
    the engine causes a small cyclic variation of the
    engine exhaust gas composition.
  • This variation occurs in a second, which means a
    frequency of 1 Hz, and with amplitude of 510 of
    the A/F set point. This transient operation of
    the catalyst, however, has a significant effect
    upon its performance, as will be described below.
  • There exists a multitude of engine management
    systems with various degrees of complexity and
    refinement, affecting the speed and the amplitude
    range of control of the engine A/F ratio at each
    of the engine load and speed operation
    conditions.
  • The refinement of the engine management system
    affects both the performance and the durability
    of the emission control catalyst.

28
Open loop catalyst
  • This concept is a simplification of the first, as
    again a multifunctional catalyst is used, that is
    able to promote all of the reactions that lead to
    the removal of CO, HCs and NOx.
  • The composition of the exhaust gas is not
    controlled and therefore varies over a wide
    range. This wider operation range results in an
    overall lower simultaneous conversion of the
    three exhaust gas constituents
  • This concept is used if the legislative limits
    can be reached with a conversion of about 50, or
    for the retrofitting of engines that were not
    designed to be equipped with catalytic emission
    control devices.

29
Dual bed catalyst
  • Two different types of catalyst are used. The
    first catalyst is either multifunctional, or is
    at least of capable of promoting NOx reduction
    reactions.
  • The engine is calibrated so as to guarantee a net
    reducing exhaust gas composition. Under these
    conditions, the first catalyst will lead to an
    elimination of the nitrogen oxides. The second
    catalyst is an oxidation catalyst.
  • Extra air is injected in front of the second
    catalyst to assist the removal of CO and HCs. The
    secondary air can be added either by mechanically
    or by electrically driven air pumps.
  • The dual-bed concept allows for a wider engine
    A/F range and also maintains high conversion
    efficiency for the three exhaust gas constituents
    under these conditions. Therefore, a
    less-sophisticated engine management system can
    be used.

30
Oxidation catalyst
  • In this emission control concept, secondary air
    is added to the exhaust gas to ensure a lean
    composition, independent of the engine operation
    condition. The catalyst is designed to promote
    reactions between oxygen and both CO and HCs,
    which can be removed to a great extent, but NOx
    cannot be removed in this manner.

31
Lean oxidation catalyst
  • The fifth concept is also an oxidation catalyst,
    but it is applied to engines that operate under
    lean conditions, the so-called lean-burn engines.
    The A/F ratio of these engines reaches values up
    to 26, corresponding to a lambda value of about
    1.8.
  • The function of the catalyst could be limited to
    converting CO and HCs. Because of the dilution
    effect in lean combustion, the exhaust gas is
    colder than for closed-loop controlled engines,
    and therefore special catalysts with good
    low-temperature activity for the oxidation
    reactions are needed.To date, however, this
    concept has not achieved widespread application.
  • The latest generation of lean-burn gasoline
    engines applies the direct fuel injection
    principle, which enables different catalytic
    exhaust gas after treatment concepts to be used,
    such as the NOx-adsorber systems

32
Three-way Catalyst
  • The three-way catalyst, consisting of Pt and Rh
    particles supported on a ceramic monolith,
    represents a remarkably successful piece of
    catalytic technology. It enables the removal of
    the three pollutants CO, NO and hydrocarbons
  • Additionally, NO is reduced by H2 and by
    hydrocarbons. To enable the three reactions to
    proceed simultaneously notice that the two
    first are oxidation reactions while the last is a
    reduction the composition of the exhaust gas
    needs to be properly adjusted to an air-to-fuel
    ratio of 14.7
  • At higher oxygen content, the CO oxidation
    reaction consumes too much CO and hence NO
    conversion fails.

33
Contd..
34
Contd..
35
Contd..
  • If, however, the oxygen content is too low, the
    entire NO is converted, but hydrocarbons and CO
    are not completely oxidized.
  • An oxygen sensor (?-probe) is mounted in front of
    the catalyst to ensure the proper balance of fuel
    and air via a microprocessor-controlled injection
    system.

36
Oxygen sensor
  • It is a simple oxygen sensor made in a similar
    manner to the solid oxide fuel cell. An oxide
    that allows oxygen ions to be transported is
    resistively heated to ensure sufficiently high
    mobility and a short response time (1 s.).
  • The oxygen content in the exhaust is measured
    against a suitable reference, in this case
    atmospheric air.
  • The response is given by the Nernst equation

37
Oxygen sensor Contd..
38
Oxygen sensor Contd..
39
Contd..
  • The ?-probe relies on the diffusion of atomic
    oxygen through a solid electrolyte and,
    therefore, it will have a certain response time.
  • Reducing the thickness of the oxide membrane and
    increasing the temperature both shorten the
    response time, but a certain delay cannot be
    avoided.
  • For example, if the driver suddenly steps on the
    gas pedal the exhaust becomes reducing.
    Consequently, sulfur deposited in the catalyst
    becomes hydrogenated to H2S, causing the
    characteristic rotten eggs smell (this smell
    sometimes arises during the startup of a cold
    engine).
  • New types of sensors with faster response are
    therefore being explored to avoid these effects.
    Ideally these should be placed immediately after
    each cylinder and therefore they should be
    capable of withstanding high temperatures.

40
Location of Gas sensor
41
Performance of Three-way catalyst
  • The Performance of the catalyst depends upon the
    various factors such as
  • the chemistry of the catalyst (e.g., the wash
    coat, precious metals, age and preparation),
  • the physics of the catalyst (e.g., support and
    converter design) and
  • the chemical engineering aspects of the catalyst
    (e.g., reaction temperature, residence time, gas
    composition and dynamic conditions)

42
Factors affecting performance of TWC
43
Contd..
44
What is that operating window
  • The catalytic converters have three important
    layers. First is a wash coat, which increases the
    surface area that the catalysts are on a large
    surface area is essential for high-efficiency
    exhaust emission reductions.
  • Next, a layer of noble metals like platinum and
    palladium are vaporized on to the wash coat
    these encourage carbon monoxide and hydrocarbons
    to react into water vapor and carbon dioxide.
  • Then there is a third layer of platinum and
    rhodium that reduces nitrogen oxides (the third
    layer is what makes the converter 'three-way').
  • These reactions seem contradictory the oxidation
    process is more efficient when large amounts of
    oxygen are present, but reduction happens more
    efficiently in a low oxygen environment. But
    there is a small window of exhaust stoichiometry,
    called the lambda window, which creates favorable
    conditions for both reactions to take place.
    Maintaining the air/fuel ratio to keep exhaust
    gasses in this window is extremely important,
    hence the requirement of oxygen sensor
    monitoring.

45
Role of Ceria in the TWC
  • Ceria is well known for his Oxygen storage
    capacity and redox properties and these
    properties are the key for the three-way catalyst
    development.
  • The major problem for the catalyst to stay active
    is that to have adequate contact points between
    the pollutant soot and the catalyst.
  • When these catalysts are used through fuel borne
    then this increases the contact points between
    the soot and the catalyst and in turn decreases
    the temperature of oxidation from 600 ?C to 400
    ?C.

46
Interesting mechanism
47
Contd..
  • CeO2 is one of the extensively used catalytic
    components in many of the above described
    after-treatment technologies due to its high
    activity in the redox reactions
  • . CeO2 is used in a well- known three-way
    catalyst for CO, HC, and NOx abatement, as a
    fuel-borne catalyst, and in the catalysed soot
    ?lters in elimination of the soot particulates.
  • The fuel-borne ceria catalyst leads to the
    formation of the CeO2 nano-particles trapped
    within the soot particle.

48
NOx assisted soot oxidation
49
Future catalyst-Precious metals?
  • Improving the cold-start performance
  • HC adsorbers into the aftertreatment system-like
    activated carbon, zeolites etc.,
  • usage of precious metals should be limited to
    achieve cost reduction
  • future development will be the exchange of a
    substantial portion of the platinum by palladium
    in high performance oxidation catalyst
  • In order to cope with the changing boundary
    conditions, and especially the further reduction
    in exhaust gas temperature, it is highly probable
    that at least a portion of the catalyst volume
    will be moved closer to the engine outlet.

50
Catalysis can do this
Thanks
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