pollutant formation
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Pollutant Formation and Control
2103471 Internal Combustion Engine
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Pollutant Formation and Control
All IC engines produce undesirable emissions as a result of combustion.
The emissions of concern are unburned hydrocarbons (UHC), carbon
monoxide (CO), oxides of nitrogen such as nitric oxide and nitrogen dioxide
(NOx), sulfur dioxide, and solid carbon particulates.
These emissions pollute the environment and contribute to acid rain, smog
odors, and respiratory and other health problems.
HC emissions from gasoline-powered vehicles include a number of toxic
substances such as benzene, polycyclic aromatic hydrocarbons (PAHs),
1,3-butadiene and three aldehydes (formaldehyde, acetaldehyde, acrolein).
Carbon dioxide is an emission that is not regulated but is the primary
greenhouse gas responsible for global warming.
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Emissions Control
The current emission limits for HC, CO and NOx have been reduced to 4%,
4% and 10% of the uncontrolled pre-1968 values, respectively.
Three basic methods used to control engine emissions:
1) Engineering of combustion process - advances in fuel injectors, oxygensensors, and on-board computers.
2) Optimizing the choice of operating parameters - two NOx control measures
that have been used in automobile engines since 1970s are spark retard and
EGR.
3) After treatment devices in the exhaust system - catalytic converter
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During the 1940s air pollution as a problem was first recognized in the LosAngeles basin.
Two causes of this were the large population density and the natural weather
conditions. Smoke and other pollutants combined with fog to form smog.
In 1966 HC and CO emission limits were introduced in California.
All of North America usually follows Californias lead (all US in 1968).
By making more fuel efficient engines and with the use of exhaust after
treatment, emissions per vehicle of HC, CO, and NOx were reduced by
about 95% during the 1970s and 1980s.
Automobiles are more fuel efficient now (2x compared to 1970) but there are
more of them and the trend is to larger SUVs, as a result fuel usage is
unchanged over this period.
Historical Perspective
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Ontario Drive Clean Program
In Ontario every vehicle must undergo a tail pipe emission test every other
year to check compliance with regulation:
Nitrogen Oxide 984 ppm @ 3000 rpm
Carbon Monoxide 0.48% @ 3000 rpm and 1.0% @ 800 rpm
Unburned hydrocarbons 86 ppm @ 3000 rpm and 200 ppm @ 800 rpm
Particulates (diesels only at present) 30% opacity
Evaporative Emissions (SI only at present)
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Test results between 1999 and March 2004
Light-Duty Program*: 14.6% failed test
Heavy-Duty Diesel**: 4% failed test
Heavy-Duty Non-Diesel**: 27.3% failed test
* 6 million vehicles (automobiles, vans, SUVs, pick-ups) in program
** 200,000 vehicles in program
Ontario Drive Clean Program Stats
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Emission Formation In S.I. EngineThis section provides an introduction to
vehicle emissions components.
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Principle S.I. Engine Exhaust Constituents
The chemical reaction that takes place in the enginecylinder when air is mixed with fuel and ignited is calledcombustion. Although combustion has been studied formany years, scientists and engineers are still unable to
fully predict the behavior of this complicated process. Several variables must be considered in determining the
correct levels of fuel, air, and ignition required forefficient combustion.
Port or direct fuel injection has improved the distributionof the fuel in the cylinders; mass air flow metersaccurately determine the amount of air flowing into anengine; and distributor-less electronic ignition systems
have improved the reliability and accuracy of ignitionsystems.
The entire power-producing process has considerablyreduced emissions and improved driveability over the
last 20 years.
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Consider the combustion of octane, C8H18. Under idealconditions, all of the hydrocarbon fuel consumed by the
engine would be converted to CO2, H2O, and N2. Sinceambient air contains approximately 21% oxygen and78% nitrogen by volume, each mole of oxygenconsumed involves (78/21) = 3.7 moles of N2.
With this information, the ideal combustion equation for afuel such as octane can be written by balancing thenumber of moles of each constituent on either side of the
combustion equation: C8H18 + (12.5)O2 + (12.5)(3.7)N2 --> (8.0)CO2 +
(9.0)H2O + (47.0)N2
Principle S.I. Engine Exhaust Constituents
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Hence, ideal combustion of octane producesapproximately 13% carbon dioxide, 14 % water vapor,
and 73 % nitrogen. However, actual vehicle exhaust gasalso contains unburned hydrocarbons (HC), carbonmonoxide (CO), oxides of nitrogen (NOx), aldehydes,and various other constituents. The emissions in exhaustas it leaves the engine are called engine-out or feedgasemissions; they are carried through a catalytic converter,and the net output to the air is called tailpipe emissions.
The ratio of air mass to fuel mass is called air fuel ratio
(A/F). The stoichiometric or theoretical A/F is defined asthe minimum amount of air that supplies sufficientoxygen for the complete combustion of all the carbon,hydrogen and any other elements in the fuel that may
oxidize. For example, the stoichiometric A/F for the idealcombustion of octane can be calculated as follows:
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On a molar basis:
(A/F)mole = (12.5 moles O2
+ 47.0 moles N2)
(1 mole of fuel)
(A/F)mole = 59.5 mole air/mole fuel
On a mass basis:
(A/F)mass = (59.5 mole air/mole fuel)*(28.97 kg/mole air)
(114.2 kg/mole fuel)
(A/F)mass = 15.0 kg air/kg fuel
Principle S.I. Engine Exhaust Constituents
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In current combustion control systems, air flow iscontrolled by throttle position. Closing the throttle platerestricts airflow, thereby reducing power output.
Fuel flow is regulated by electronic control of the amountof time the solenoid fuel injectors are open.
The electronic engine control system measures airflow
and adjusts the injector control to maintain A/F withinfairly narrow limits around the stoichiometric A/F.
A/F ratio data is often presented as fuel to air ratio, F/A,
or as the equivalence ratio, commonly defined in the twoforms shown below:
= (A/F)/(A/Fstoich)
= (F/A)/(F/Astoich
)
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It is important to define what measure is being used indescribing the relationship between A/F and otherparameters.
Keys for remembering the trends in each measure of A/Fis:
Measure Leaner
Combustion
Richer
Combustion
A/F Bigger Smaller
F/A Smaller Bigger Bigger Smaller
Smaller Bigger
Principle S.I. Engine Exhaust Constituents
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Under normal operating conditions, stoichiometricoperation is maintained by control electronics.
When the control system is operating in closed-loopmode, it utilizes feedback signals from the heatedoxygen sensors. These signals provide a means for
determining how close the vehicle is to stoichiometricoperation.
When the control system is operating in open loop
mode, this feedback signal is not used. In open loopmode, the control electronics uses default operationparameter values for determining correct operation.
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Emission Formation Mechanisms
This section discusses the formation of HC, CO, NOx,
CO2, and aldehydes and explains the effects of designparameters.
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Emission Formation Mechanisms
(i) Hydrocarbon Emissions
Hydrocarbon emissions result from the presence ofunburned fuel in the engine exhaust.
HC emissions are various compounds of hydrogen,carbon, and sometimes oxygen. They are burned orpartially burned fuel and/or oil. HC emissions contributeto photochemical smog, ozone, and eye irritation.
However, some of the exhaust hydrocarbons are notfound in the fuel, but are hydrocarbons derived from thefuel whose structure was altered do to chemical reactionthat did not go to completion. For example: cetaldehyde,
formaldehyde, 1,3 butadiene, and benzene all classifiedas toxic emissions.
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Emission Formation Mechanisms
(i) Hydrocarbon Emissions There are several formation mechanisms for HC, and it
is convenient to think about ways HC can avoidcombustion and ways HC can be removed; we will
discuss each below. Most of the HC input is fuel, and most of it is burned
during normal combustion.
However, some HC avoids oxidation during this process. About 9% of the fuel supplied to the engine is not burnedduring the normal combustion phase of the expansionstroke.
Only 2% ends up in the exhaust the rest is consumedduring the other three strokes.
As a consequence hydrocarbon emissions cause adecrease in the thermal efficiency, as well as being an
air pollutant.
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Emission Formation Mechanisms
(i) Hydrocarbon Emissions
The processes by which fuel compounds escapeburning during normal S.I. combustion are:
1. Fuel vapor-air mixture is compressed into thecombustion chamber crevice volumes.
2. Fuel compounds are absorbed into oil layers on the
cylinder liner.3. Fuel is absorbed by and/or contained within
deposits on the piston head and piston crown.
4. Quench layers on the combustion chamber wall areleft as the flame extinguishes close to the walls.
5. Fuel vapor-air mixture can be left unburned if theflame extinguishes before reaching the walls.
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Emission Formation Mechanisms
(i) Hydrocarbon Emissions
6. Liquid fuel within the cylinder may not evaporate andmix with sufficient air to burn prior to the end ofcombustion.
7. The mixture may leak through the exhaust valveseat.
Each of these seven processes allows some fraction of the
fuel to escape normal combustion. However, there are anumber of hurdles which the HC must pass before it canmake it into the exhaust system
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Emission Formation Mechanisms
(i) Hydrocarbon Emissions
The processes by which HC can oxidize or exit the cylinderare:
1. Outflow of unburned mixture from the crevices, mixingwith the hot burned gases; some of this will oxidize.
2. Diffusion of HC vapor from oil layers and deposits intothe burned gases; some will oxidize.
3. Mixing of wall quench and burned gases; some willoxidize.
4. Exhaust blowdown process carries some HC into theexhaust.
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Emission Formation Mechanisms
(i) Hydrocarbon Emissions
5. Displacement of gases by the piston during theexhaust stroke will transport an additional fraction into
the exhaust.6. Unburned HC leaving the cylinder mixes with hot
exhaust gases; some of this will oxidize in the port andmanifold.
The formation and exhausting of HC is very complex. Norigorous models of HC emissions exist today, although
many labs are working on the problem.
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Hydrocarbon Emission Sources for SI Engines
The six principal mechanisms are believed to be responsible for
hydrocarbon emissions:
% fuel escaping
Source normal combustion % HC emissions
Crevices 5.2 38
Oil layers 1.0 16
Deposits 1.0 16
Liquid fuel 1.2 20Flame quench 0.5 5
Exhaust valve leakage 0.1 5
Total 9.0 100
Emission Formation Mechanisms
(i) Hydrocarbon Emissions
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Emission Formation Mechanisms
(i) Hydrocarbon Emissions
Crevices these are narrow regions in the combustionchamber into which the flame cannot propagate becauseit is smaller than the quenching distance.
Generally, any volume with a dimension less than onemillimeter across will form a crevice.
Crevices are located around the piston, head gasket,spark plug and valve seats and represent about 1 to 2%of the clearance volume.
With walls so close together, the flame cannot burn intothe crevice, so mixture in the crevices escapes primarycombustion.
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Emission Formation Mechanisms
(i) Hydrocarbon Emissions
Figure 1 illustrates the various crevice volumes which
exist in an engine.
Figure 1 Crevice Volume Sites.
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Emission Formation Mechanisms
(i) Hydrocarbon Emissions
The crevice around the piston is by far the largest.
Crevices typically amount to about 2% of the cylinderclearance volume. Fuel-air mixture is compressed intothe crevices during the compression stroke and alsoduring combustion (density higher than cylinder gassince gas is cooler near walls) and released during
expansion.
Crevice
Piston ring
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Emission Formation Mechanisms
(i) Hydrocarbon Emissions
At peak pressure, calculations suggest as much as 6-8%of the mixture may be trapped in the crevices. This is
much higher than the crevice volume fraction becausethe gases in the crevices cool rapidly to something closeto wall temperature, which is much lower than cylindertemperature at peak pressure. As a result of the lower
temperature, their density is 3-4 times higher than theburned gases.
As the piston travels downward, pressure in the cylinder
decreases and mixture comes back out of the crevices.
Crevices are estimated to cause roughly 40% of HCemissions.
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Emission Formation Mechanisms
(i) Hydrocarbon Emissions
The second HC mechanism is related to the thin layerof oil which is always present on the cylinder walls.
Since the piston ring is not 100% effective in preventingoil migration into the cylinder above the piston, oil layersexist within the combustion chamber. This oil layer traps
fuel and releases it later during expansion. Although the rings scrape off most of the oil, there must
be a tiny layer to provide lubrication for the rings on theup strokes.
This thin layer (on the order of tens of microns inthickness) absorbs HC. Oil layers are thought to causeroughly 10-30% of HC emissions.
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Emission Formation Mechanisms
Figure 2 Unburned Hydrocarbon Solubility in Oil.
(i) Hydrocarbon Emissions
Figure 2 shows the effect on HC of fuel solubility in oil.Oils with higher fuel solubility increase HC emissions.Unfortunately, practical oils - i.e., those which prevent
mechanical wear acceptably, have a very limited rangeof solubilities so that we cannot do too much about thismechanism.
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Emission Formation Mechanisms
(i) Hydrocarbon Emissions Deposits - With continued use carbon deposits build up
on the valves, cylinder and piston head. These deposits
are porous with pore sizes smaller than the quenchingdistance so trapped fuel cannot burn. Deposits can
absorb fuel in a manner similar to oil. However, deposits
are not present on new engines but accumulate withmileage. The fuel is released later during expansion.
Operating conditions also affect the deposition and
removal of deposits. As a result, the effect of deposits onHC emissions is rather difficult to identify.
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Hydrocarbon Exhaust Process
(i) Hydrocarbon Emissions When the exhaust valve opens the large rush of gas
escaping the cylinder drags with it some of the hydrocarbons
released from the crevices, oil layer and deposits.
During the exhaust stroke the piston rolls the hydrocarbons
distributed along the walls into a large vortex that ultimately
becomes large enough that a portion of it is exhausted.
Blowdown ExhaustStroke
Emission Formation Mechanisms
Emission Formation Mechanisms
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Hydrocarbon Exhaust Process
(i) Hydrocarbon Emissions The first peak is due to blowdown and the second peak is
due to vortex roll up and exhaust (vortex reaches exhaust
valve at roughly 290o)
Emission Formation Mechanisms
Exhaust
valve
opens
Exhaust
valve
closes
TCBC
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Emission Formation Mechanisms
(i) Hydrocarbon Emissions Liquid fuel For some fuel injection systems there is a
possibility that liquid fuel is introduced into the cylinder
past an open intake valve. The less volatile fuelconstituents may not vaporize (especially during enginewarm-up) and be absorbed by the crevices or carbondeposits.
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Emission Formation Mechanisms
(i) Hydrocarbon Emissions Flame quenching It has been shown that the flame
does not burn completely to the internal surfaces, theflame extinguishes at a small but finite distance from the
wall. Most of this gas eventually diffuses into the burnedgas during expansion stroke.
Flame quenching is another HC producing mechanism
but one not very well understood. Under extremeconditions of lean A/F, high exhaust gas recirculation(EGR), or high residual gas fraction, the flame may notpropagate fully across the chamber. Very severe
decelerations may produce such conditions. Figure 3 summarizes the path of HC through the engine.
The percentages are rough estimates of the percent ofthe input fuel which goes through each path for a typicalpartial load condition.
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Emission Formation Mechanisms
Figure 3 Hydrocarbon Path Through Engine.
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Emission Formation Mechanisms
(i) Hydrocarbon Emissions HC emissions are also dependent on several other
parameters such as spark advance, A/F ratio, and
EGR. High advance generally increases HC emissions,
primarily because the temperature of the charge is lowerduring the expansion stroke. This reduces oxidationduring expansion as the HC comes off the walls and outof the crevices.
Lower A/F ratios (richer combustion) cause more HC
emissions because there is less O2 to oxidize fuel. Verylean A/F ratios cause HC emissions to increase due tomisfires, partial burns, and reduced temperature duringexpansion.
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Emission Formation Mechanisms
Figure 4 EGR Effect on
Hydrocarbon Formation.
Figure 4 depicts HC formation versus EGR rate.
High EGR causes an increase in HC emissions. Theincrease is gradual at first, but the curve becomes steep
as the combustion degrades.
In fast burn engines, the combustion degradation sets inat higher EGR rates than in slow burn engines.
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Emission Formation Mechanisms
(ii) Carbon Monoxide
Formation of CO is well established. Under someconditions, there is not enough O2 available for complete
oxidation and some of the carbon in the fuel ends up asCO.
The amount of CO, for a range of fuel composition andC/H ratios, is a function of the relative air-fuel ratio. Evenwhen enough oxygen is present, high peak temperaturescan cause dissociation - chemical combustion reactionsin which carbon dioxide and water vapor separate intoCO, H2, and O2. Conversion of CO to CO2 is governed
by reactionCO + OH CO2 + H
Dissociated CO may freeze during the expansion stroke.
Figure 5 shows CO production as a function of A/F ratio.
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Emission Formation Mechanisms
Figure 5 Air/Fuel Ratio Effects on Carbon Monoxide Concentration.
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Emission Formation Mechanisms
(ii i) Oxides of Nitrogen
NOx is a generic term for the compounds nitric oxide(NO) and nitrogen dioxide (NO2). Both are present to
some degree in the exhaust, and NO oxidizes to NO2 inthe atmosphere.
NOx contributes to acid rain and photochemical smog; itis also thought to cause respiratory health problems at
atmospheric concentrations found in some parts of theworld.
To understand NOx formation, we must recognizeseveral factors that affect NOx equilibrium. Rememberthat all chemical reactions proceed toward equilibrium atsome reaction rate.
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Emission Formation Mechanisms
(ii i) Oxides of Nitrogen
In SI engines the dominant component of NOx is NOforms as a result of dissociation of molecular nitrogen
and oxygen. Since the activation energy of the critical elementary
reaction O+N2NO+N is high the reaction rate is verytemperature dependent, w''~ exp (-E/RT)
Therefore NO is only formed at high temperatures andthe reaction rate is relatively slow.
At temperatures below 2000K the reaction rate is
extremely slow, so NO formation not important.
Equilibrium NO (which comprises most of the NOxformation) is formed at a rate that varies strongly with
temperature and equivalence ratio, as shown in Figure 6.
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Emission Formation Mechanisms
Figure 6 Temperature and Equivalence Ratio Effects on NO Formation Rate.
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(ii i) Oxides of Nitrogen
Since the cylinder temperature changes throughout the
cycle the NO reaction rate also changes.
In figure 6, much of the mixture in the cylinder is burnedessentially adiabatically (without loss or gain of heat). Aswe can see, more NO will be formed rapidly during theengine cycle when the peak temperature is highest and/or
when the equivalence ratio is slightly lean of stoichiometry. During the combustion process, O2 and N2 are heated to
high temperatures, and NO is formed very rapidly at the
peak temperatures. Then, during expansion, the temperature drops so rapidly
that the reaction rate slows before the concentration cango all the way down; the NO concentration freezes at a
level typical of equilibrium at an elevated temperature.
SI Engine In-cylinderNO Formation
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Each fluid element burns to its AFT based on its initialtemperature, elements that burn first near the spark plug
achieve a higher temperature.
Since the chemistry is not fast enough the actual NOconcentration tends toward but never achieves the
equilibrium value.IfNO concentration is lower than equilibrium value NO forms
IfNO concentration is higher than equilibrium value NO decomposes
Once the element temperature reaches 2000K the reaction
rate becomes so slow that the NO concentration effectively
freezes at a value greater than the equilibrium value.
The total amount ofNO that appears in the exhaust is
calculated by summing the frozen mass fractions for all the
fluid elements: =1
0dxxx NONO
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x = 0
-15o (x = 0)x = 1
25o (x = 1)
x = 0
x = 1
Equilibrium concentration:
based on the local temperature, pressure,
equivalence ratio, residual fraction
Actual NO concentration:
based on kinetics
(assuming no mixing of fluid elements)
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Figure 7 Air/Fuel Effect on NO
Formation.
One would expect the peak NO concentrations to
coincide with highest AFT.
Figure 7 shows feed-gas emission of NOx versus A/F
ratio. A peak occurs at about 16:1 A/F.
Under rich conditions, the amount of available O2 is
less than optimal for NOx formation. Under leaner conditions, the peak temperatures drop.
(ii i) Oxides of Nitrogen
Emission Formation Mechanisms
(ii i) O id f Nit
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Typically peak NO concentrations occur for slightly leanmixtures that corresponds to lower AFT but higher oxygen
concentration.
Effect of Equivalence Ratio on NO Concentration
(ii i) Oxides of Nitrogen
Emission Formation Mechanisms
(ii i) O id f Nit
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Exhaust NO Concentration Reduction
Since the formation of NO is highly
dependent on cylinder gastemperature any measures taken to
reduce the AFT are effective:
increased residual gas exhaust gas recirculation (EGR)
moisture in the inlet air
In CI engines the cylinder gastemperature is governed by the load
and injection timingIDI/NA indirect injection
naturally aspirated
DI/NA direct injectionnaturally aspirated
(ii i) Oxides of Nitrogen
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(ii i) Oxides of Nitrogen
Exhaust Gas Recirculation is used to reduce NOx. Byrecirculating a fraction of the exhaust into the intakecharge, the heat capacity (Cp) of the mixture in thecylinder is increased.
This means that the temperature of the charge increases
less during compression (including the compression ofunburned charge during combustion). As we have seen,even a small drop in peak temperature can have adramatic effect on NO formation.
Thus, EGR has a strong effect on NO, as shown inFigure 8. A 2:1 reduction is obtained with as little as 10%EGR.
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Figure 8 EGR Effect on NO Formation.
(ii i) Oxides of Nitrogen
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(ii i) Oxides of Nitrogen
Unfortunately, EGR also reduces flame speed.
Excessive EGR rates can slow burn rate so drastically
as to cause surge, misfire, and other combustionproblems.
However, EGR can increase fuel economy.
When used optimally, EGR can reduce NO and improvefuel economy while avoiding rough engine operation.
This optimum varies with speed, load, and enginedesign.
NOx also varies with spark timing. More spark advancemeans that parts of the mixture spend more time at hightemperatures, so more NO is formed.
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(ii i) Oxides of Nitrogen
Effect of Various Parameters on NO Concentration
Increased spark advance and intake manifold pressure
both result in higher cylinder temperatures and thus
higher NO concentrations in the exhaust gas
= 0.97
= 1.31
= 1.27
= 0.96
Pi= 354 mm HgPi= 658 mm Hg
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(iv) Carbon Dioxide While not normally considered a pollutant, CO2 may
contribute to the greenhouse effect. Proposals to reduceCO2 emissions have been made.
CO2 controls strongly influence fuel economyrequirements.
(v) Aldehydes
Aldehydes are the result of partial oxidation of alcohols.They are not usually present in significant quantities in
gasoline-fueled engines, but they are an issue whenalcohol fuels are used.
Aldehydes are thought to cause lung problems. So far,little information of engine calibration effects on aldehyde
formation is available.
Fuel and Combustion Control
For S I Engine
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For S.I. Engine
Fuel Injection Technology
Fuel injectors are solenoid valves which deliver andatomize precisely controlled amounts of fuel into an airintake system.
The operation of fuel injectors is controlled by thepowertrain control module (PCM) or engine control unit
(ECU). Use of fuel injection provides for better cold-driveability,
lower emissions, and eliminates dieseling when the key
ignition is turned off.
Fuel Injection Technology
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The three principle fuel injection systems are as follows: Central Fuel Injection (CFI)--Injector delivers fuel
above the throttle plate.
Multiport Fuel Injection (MFI)--Injector placed neareach intake valve; injectors arranged on commonfuel rails open and close simultaneously.
Sequential Electronic Fuel Injection (SEFI)--
Injector placed near each intake valve; injectoroperation matched to operation of correspondingIntake valve. SEFI is also called SFI (SequentialFuel Injection).
SEFI provides better performance, driveability, and loweremissions than CFI and MFI.
Fuel Injection Technology
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Figure 9 shows the various components of a fuel injector. Pressurized fuel enters the fuel injector at the top, then
passes through a filter and into the injector body, where a
needle blocks it from passing out the injector orifice.When the solenoid activates, it pulls back the needle,thus allowing fuel to pass out of the injector through themetering plate. When the coil is de-energized a spring
pulls the needle back to its seated position, therebyclosing off the exit orifice to further fuel flow. The amountof fuel delivered depends on how long the injector isopen.
Typical fuel injection "pulse width"--the amount of time thefuel injector is delivering fuel--is between one and fifteenmilliseconds, depending on what the PCM commands.
Heated Oxygen Sensors
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The Heated Oxygen Sensor (HO2S, formerly known asHEGO), shown in Figure 10, is located in the exhaustmanifold and monitors the oxygen content in theexhaust. This information is used by the PCM to controlthe fuel metering to keep the desired air-fuel mixtureentering the cylinder chamber.
An HO2S has a ceramic surface coated in platinum. This
ceramic surface can conduct oxygen ions when exposedto a gas of at least 300 oC, and when the oxygen sensoris internally heated it is functional for exhaust gastemperatures as low as 200 oC. When the surface is
exposed to both the exhaust gas and ambient air, avoltage signal is generated indicative of how muchoxygen is in the exhaust.
Heated Oxygen Sensors
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The Heated Oxygen Sensor (HO2S, formerly known asHEGO), shown in Figure 10, is located in the exhaustmanifold and monitors the oxygen content in theexhaust.
This information is used by the PCM to control the fuelmetering to keep the desired air-fuel mixture entering thecylinder chamber.
An HO2S has a ceramic surface coated in platinum. Thisceramic surface can conduct oxygen ions when exposedto a gas of at least 300 oC, and when the oxygen sensor
is internally heated it is functional for exhaust gastemperatures as low as 200 oC. When the surface isexposed to both the exhaust gas and ambient air, avoltage signal is generated indicative of how much
oxygen is in the exhaust.
Heated Oxygen Sensors
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Figure 9 Fuel Injector.
Figure 10 Heated Oxygen Sensor.
Heated Oxygen Sensors
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HO2S are located in the exhaust pipe both before andafter the catalytic converter.
The HO2S before the catalytic converter gives thefeedback necessary to keep the desired air-fuel mixture.
The output of the HO2S after the catalyst is compared tothe output of the HO2S before the catalyst as anindication of catalytic converter efficiency with respect to
oxygen. This is used in the On-Board Diagnostics to determine
catalyst burnout.
Powertrain Control Module
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The powertrain control module (PCM) controls avehicle's powertrain (P/T) by monitoring electronic
signals generated by various sensors in order toascertain current powertrain conditions.
Based on these P/T conditions, the PCM'smicroprocessing unit will signal various actuators to
perform certain control functions according to acomputer program referred to as the vehicle's enginecontrol calibration.
This calibration is composed of smaller programs calledstrategies.
Powertrain Control Module
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Different strategies are used to control engine operationfor the following: Engine Cranking;
Cold Start/Warm Up;
Cold Driveaway; Warm Driveaway;
Warm Cruise;
Part-Throttle Acceleration; Full-Throttle Acceleration;
Deceleration; and
Warm-Idle.
The strategies, stored in the PCM's Programmable ReadOnly Memory (PROM) chip, contain the logic to controlthe powertrain. Strategy development is an integral partof the development of a powertrain.
Powertrain Control Module
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Within each strategy there exists a vast quantity ofvariables used by the logic.
Certain variables, referred to as Random AccessMemory (RAM) variables, are set by calibratorsduring vehicle operation to reflect current signalstatus.
Other variables, referred to as Read Only Memory
(ROM) variables, are set by calibrators duringdevelopment for use as references in the logic.
We can significantly enhance a powertrain'sperformance by setting the ROM variables at optimum
values during strategy development.
We refer to this process as engine calibration.
Exhaust Gas Recirculation (EGR)
Th EGR t h i Fi 11 i i l d t
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The EGR system, shown in Figure 11, is mainly used to
reduce nitrogen oxides (NOx) which are formed in the
combustion chamber at high temperatures.
Figure 11 EGR System.
Exhaust Gas Recirculation (EGR)
The EGR system recirculates already combusted exhaust
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The EGR system recirculates already combusted exhaust
from the exhaust manifold back to the air-fuel mixture andis drawn into the cylinder chamber. This reduces the peakcombustion temperature in the cylinder chamber. Thistemperature reduction in turn reduces NOx formation.
The EGR flow is directed by a solenoid valve that iscontrolled by the Powertrain Control Module (PCM). ThePCM uses inputs such as engine speed, intake-manifold
pressure, and engine temperature to determine how muchexhaust flow to meter back to the air-fuel mixture.
Exhaust Gas Recirculation (EGR)
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Disadvantages of EGR are increases in hydrocarbonemissions and fuel consumption.
Consequently, EGR is not used during conditions of lowNOx formation such as idle.
EGR is also not used during wide open throttle (WOT)when full power is needed for acceleration.
Emission Formation In C.I. Engine
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For many years, diesel engines have had a reputation ofgiving poor performance and producing black smoke, anunpleasant odor, and considerable noise.
However, it would find it difficult to distinguish todaysmodern diesel car from its gasoline counterpart. Fordiesel engines the emphasis is to reduce emissions ofNOx and particulates, where these emissions are
typically higher than those from equivalent port injectedgasoline engines equipped with three-way catalysts.
Catalyst of diesel exhaust remains a problem insofar as
research has not yet been able to come up with aneffective converter that eliminates both particulate matter(PM) and oxide of nitrogen (NOx).
Principle C.I. Engine Exhaust Constituents
Acquired load of diesel engines is accomplished by
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Acquired load of diesel engines is accomplished bymodifying the fuel quantity supplied, whereas the airquantity per work cycle is drawn in without any throttling.The air to fuel mixture ratio is therefore adjusted toachieve load required.
This means that the mixture in its working range is madeleaner or richer, respectively. Depending on friction
power and the combustion process of the engine, themixture setting, as shown in Figure 12,may made leanerup to levels of = 10.
This diesel-engine processes is referred to as qualitymanagement.
Principle C.I. Engine Exhaust Constituents
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Figure 12 Excess air ratio map of a diesel engine.
Principle C.I. Engine Exhaust Constituents
I th ith SI i th i /f l ti
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In the same manner as with SI engines, the air/fuel ratio
of the diesel engine has a significant impact on the level
of pollutant concentrations but this parameter is not
freely available for minimizing pollution.
Figure 13 shows an example of the dependence of major
pollutant concentrations on the air /fuel ratio in the case
of a direct-injection diesel engine.
Principle C.I. Engine Exhaust Constituents
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Figure 13 Exhaust concentrations as a function of air/fuel ratio.
Emission Formation Mechanisms
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Carbon monoxide: The mean air-fuel mixture present in the combustion
chamber per cycle is far leaner in the diesel engine than
in the SI engine. Due to a lack of homogeneity of themixture built up by stratification, however, extremelyrich local zones are exist. This produces high COconcentrations that are reduced to a greater or lesser
extent by post-oxidation. When the coefficient increases, i.e. when the excess-air
ratio increases, dropping temperatures cause the post-
oxidation rate to be reduced. The reactions freeze up.The CO concentrations of diesel engines therefore arefar lower than in SI engines.
The basic principles of CO formation, however, are the
same as in SI engine.
Carbon Monoxide
Emission Formation Mechanisms
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Carbon monoxide appears in the exhaust of fuel rich running engines.
For fuel rich mixtures there is insufficient oxygen to convert all the
carbon in the fuel to carbon dioxide.
C8H18-air
Carbon Monoxide
Emission Formation Mechanisms
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Carbon Monoxide The C-O-H system is more or less at equilibrium during combustion
and expansion.
Late in the expansion stroke when the cylinder temperature gets
down to around 1700K the chemistry in the C-O-H system becomesrate limited and starts to deviate from equilibrium.
In practice it is often assumed that the C-O-H system is in
equilibrium until the exhaust valve opens at which time it freezes
instantaneously.
The highest CO emission occurs during engine start up (warm up)
when the engine is run fuel rich to compensate for poor fuel
evaporation.
Since CI engines run lean overall, emission of CO is generally low
and not considered a problem.
Emission Formation Mechanisms
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Unburned hydrocarbons:
Since the air-fuel mixture is not homogeneous
throughout, extremely too lean (high excess air ratios)
are present in certain zones during the dieselcombustion process.
The leaner the air-fuel mixture, the lower is the local
temperature. This means that chemical reactions proceed fairly slowly
or may even freeze up, thus leading to increased HC
emissions. On the whole, HC concentrations of diesel engines are
lower than those of SI engines.
Emission Formation MechanismUnburned hydrocarbons:
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Crevices - Fuel trapped along the wall by crevices, deposits, or oil due toimpingement by the fuel spray (not as important as in SI engines).
Undermixing of fuel and air- Fuel leaving the injector nozzle at low velocity,
at the end of the injection process cannot completely mix with air and burn.
Overmixing of fuel and air- During the ignition delay period evaporated fuel
mixes with the air, regions of fuel-air mixture are produced that are too lean to
burn. Some of this fuel makes its way out the exhaust.
Longer ignition delay more fuel becomes overmixed.
ExhaustHC,
ppm
C
Emission Formation Mechanism
Unburned hydrocarbons:
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Note for the direct injection diesel the hydrocarbon emission are the worst at
light load (long ignition delay)
y
Emission Formation Mechanisms
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Nitrogen oxides: NOx concentrations are lower than in SI engines; the
share of NO2 in the NOx emissions is slightly higher.
When comparing an SI engine with three-way closed-loop catalytic converter with a diesel engine with
oxidation catalyst, it is found that NOx concentrations of
the SI engine are lower.
The type of combustion process has a significant effect
on nitrogen oxide formation.
Emission Formation MechanismsNitrogen oxides:
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Diesel engine with IDI combustion chamber: Inengines with an IDI combustion chamber, combustioninitially occurs in the pre-chamber or swirl chamberunder conditions of extreme oxygen deficiency. Thisgenerates high temperatures, but NOx levels are lowdue to a lack of oxygen. This process is reversed in themain combustion chamber. Extreme excess air ratiosand, hence, low temperatures also result in low NOx
formation.
Emission Formation Mechanisms
Nitrogen oxides:
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Diesel engine with DI combustion chamber: The
direct-injection diesel engine does not have the above
features that keep NOx emissions low. As a result, NOx
formation is approximately twice as high as with an IDI
combustion chamber engine. When exhaust recirculation
(EGR) systems are used, both systems show virtually
identical NOx levels as the direct-injection diesel engineis far more compatible with large re-circulated exhaust
quantities (more than 50% of the fresh charge).
Emission Formation Mechanisms
Sulphur compounds:
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Sulphur compounds are caused by the sulphur contentof the diesel fuel.
According to modern world-wide fuel regulations, this
content may have to be reduced to below 0.05 weightpercent.
When combined with the water produced during the
combustion process, SO2 produces sulphuric acid. Sulphur compounds cause problems with regard to acid
rain and particulate formation via sulphates.
Emission Formation MechanismsParticulates:
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A high concentration ofparticulate matter(PM) ismanifested as visible smoke in the exhaust gases.
Particulates are any substance other than water that can be
collected by filtering the exhaust, classified as:1) solid carbon material or soot
2) condensed hydrocarbons and their partial oxidation products
Diesel particulates consist of solid carbon (soot) at exhaustgas temperatures below 500oC. HC compounds becomeabsorbed on the surface.
Particulate can arise if leaded fuel or overly rich fuel-airmixture are used. Burning crankcase oil will also producesmoke especially during engine warm up where the HCcondense in the exhaust gas.
Emission Formation Mechanisms
Particulates:
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According to the California Air Resources Board (CARB),particulate matter is defined as all exhaust componentsthat are deposited on a defined filter after having been
diluted with air to a temperature below 51.7o
C. Basically, soot emissions also are part of particulate
emissions.
Soot formation occurs at extreme air deficiency. This airor oxygen deficiency is present locally inside dieselengines. It increases as the air/fuel ratio approaches avalue = 0.
Emission Formation MechanismsParticulates:
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Most particulate material results from incompletecombustion of fuel HC which occurs in fuel rich mixtures.
Based on equilibrium the composition of the fuel-oxidizer
mixture at the onset of soot formation occurs when x 2a(orx/2a 1) in the following reaction:
i.e. when the (C/O) ratio exceeds 1. Experimentally it is
found that the critical C/O ratio for onset of soot formation
is between 0.5 and 0.8 The CO, H2, and C(s) are subsequently oxidized in the
diffusion flame to CO2 and H2O via the following second
stage
)()2(2
2 22 sCaxHy
aCOaOHC yx +++
OHOHCOOsCCOOCO 2222222 2
1)(2
1
+++
Emission Formation MechanismsParticulates:
Any carbon not oxidized in the cylinder ends up as soot in
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the exhaust! Soot is produced by thermal cracking of long-chain
molecules at oxygen deficiency. A separation of hydrogenleads to C-structures showing an increasing lack of
hydrogen. Acetylene and other polymerization processes lead to
formation of molecules rich in carbon that form sootparticulates.
Once soot has formed, it can be oxidized only to a limitedextent.
The process described here is shown schematically in
Figure 14. The logarithm of the molecular mass is shown asa function of the hydrogen contents of the hydrocarboncomponents.
Soot formation produces molecules with an increasingly low
hydrogen content and higher weight that will finallyagglomerate to form soot particulates.
Emission Formation Mechanisms
Particulates:
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Figure.14 Potential soot formation process.
Emission Formation Mechanisms
Particulates:
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Particulates consist of solid (organically insoluble) andliquid (organically soluble) phases.
The solid phase consists of
Soot in the form of amorphous carbon, ash, oiladditives, corrosion products and abrasion products.
Sulphates and its molecule-bound water.
The liquid phase consists of
fuel and lubricant contents that are, usually, combined
with soot. The hydrocarbons contained in the hot
exhaust still are largely gaseous and are convertedinto a liquid, organically soluble phase (particulates)
only after having been cooled by turbulent intermixing
with air.
Emission Formation Mechanisms
Particulates:
Th i f h ti l t i 0 01 t 1 d
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The size of such particulates is approx. 0.01 to 1m andabove. Most particulates have a size below 0.3m and
some of them can therefore penetrate into the lungs.
Particulate composition is largely dependent on theoperating point and the combustion process.
Figure 15 shows a typical particulate composition of
diesel engine exhaust gas.
Emission Formation Mechanisms
Particulates:
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Figure 15. Particulate composition of diesel engine exhaust.
Particulates are a major emissions problem for CI engines.
E h t k li it th f ll l d ll i l ti t b t 0 7
Particulates and CI Engines
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Exhaust smoke limits the full load overall equivalence ratio to about 0.7
An outstanding problem for diesel engine designers is that in order to reduce
NOx one wants to reduce the AFT but this has the adverse effect of decreasing
the amount of soot oxidized, or increases the amount of soot in the exhaust.
= 0.7
= 0.5
= 0.3
One technique for measuring particulate
involves diluting the exhaust gas with
cool air to freeze the chemistry before
measurements
An example of this dilemma is changing the start of injection, e.g., increasing
the advance increases the AFT
Particulates and CI Engines
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the advance increases the AFT
Crank angle bTC for
start of injection
Fuel and Combustion Control For C.I. Engine
I i l t i t i i l i l ti th t
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Increasingly stringent emission legislation means that
the high speed CI engine will have to employ advanced
fueling technologies to meet these requirements
principally by employing systems which use very highfuel injection pressures with electronic control of
injection timing and fueling.
These large pressure differences across the injectornozzle are required so that the injected liquid fuel enters
the chamber at sufficiently high velocity to:
Atomize into small-sized droplets to enable rapidevaporation.
Traverse the combustion chamber in the time available
and fully utilize the air charge.
Electronic Fuel Injection Technology
DI diesel engines will use electronic fuel injection
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DI diesel engines will use electronic fuel injection
systems. Replacing traditional mechanical systems,
which are now approaching the end of their effective
life. In what are termed full authority fuel injectionsystems, the benefits include emission reduction,
improved driveability. Smoother idling, integration with
other vehicle systems, self-diagnostics, andperformance checks.
The benefits of higher injection pressure on particulates
and smoke are shown in Figure 16.
Electronic Fuel Injection Technology
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Figure 16 Benefits of higher mean injection pressure
on particulate and smoke.
Electronically Controlled Distributor Pumps
The fuel injection pumps are able to vary the fueling and
injection timing using electro hydraulic devices
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injection timing using electro-hydraulic devices. The cam ring is rotated to vary injection timing using a
hydraulic actuator.
The working fluid is diesel fuel, the pressure beingregulated by a solenoid valve acting on a pulse widthmodulation (PWM) signal from the electronic control unit(ECU).
Fueling is varied by moving the rotor mechanism axiallyusing a second actuator. Or a solenoid-operated spillvalve Injection timing is still set by rotating the cam ringthe use of the solenoid-operated spill valve may allowrate shaping and pre-injection.
Electronically Controlled Distributor Pumps
If the cam profile has a varying rate of rise, the injection
rate can be varied by using the appropriate section of the
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rate can be varied by using the appropriate section of thecam. Errors in the timing of the valve operation willinfluences start of injection timing, injection rate, andinjected quantity.
In addition to controlling the fuel pump, the ECUsupervises a EGR control, inlet throttle control (if fitted),and turbocharger wastegate or variable geometryturbocharger (if fitted).
The ECU will generally have other abilities including on-board diagnostics (OBD), cruise control, and networkingwith other controllers. The advent of electronic controlhas opened up a variety of alternative approaches.
Electronic Unit Injector (EUI) System
The EUI is a fueling system. Both pump and injector are
combined in a single unit for each cylinder (Figure 17)
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combined in a single unit for each cylinder (Figure 17). Each pumping plunger is driven directly by the engines
camshaft, and this enables very high injection pressures
(in the region of 1500-2000 bar) to be obtained. The main benefits of these very high injection pressure
are smaller droplet sizes, better fuel-air mixing, andreduced ignition delay.
Electronic Unit Injector (EUI) System
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Figure 17 Schematic of EUI system.
Electronic Unit Injector (EUI) System The timing and quantity of fuel can be adjusted to give
optimum conditions over the complete engine operatingprofile
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optimum conditions over the complete engine operatingprofile.
The system also has the capability to act as a pilotinjection device to reduce NOx and engine noise.
Sensors provide information to the electronic control unit(ECU) on the relevant functions of engine operation,which are: Acceleration position
Engine speed Camshaft position
Inlet manifold temperature and pressure
Coolant temperature
This information is continuously compared with theoptimum values stored in the ECU memory. The result ofthat comparison is translated into signals instructing theunit injector solenoid-actuated spill valve system to
deliver the fuel at the timing required by the engine.
Caterpillar HEUI System
This hydraulic electronic unit injector (HEUI) requires no
mechanical actuation or mechanical control devices
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mechanical actuation or mechanical control devices Inherent features of the HEUI fuel system include
injection pressure control independent of engine speed
or load, totally flexible injection timing, and full control ofinjection parameters.
High-pressure oil from the pump flows to a manifold or
rail, which is connected to the injectors. A solenoidoperates a control valve to start and end the injection
process. Initial injection rate shaping is achieved with a
Ported spill control device in the plunger and barrel; thisis called PRIME (preinjection metering).
The HEUI system is time based, so injection
characteristics are independent of engine speed.
Caterpillar HEUI System
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Figure 18 caterpillar HEUI system.
The Common Rail System
The common rail system in which high-pressure fuel is
fed into a manifold (or rail), which then serves individuali j t (Fi 19)
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fed into a manifold (or rail), which then serves individualinjector (Figure 19).
Figure 19 Schematic of a common rail system
The Common Rail System
The injector is simply a solenoid-actuated nozzle, which
is opened under the control of the ECU when injection isrequired
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p jrequired.
In principle the system is very simple, a low-drive torquemechanical pump pressurizes the distribution rail withdiesel fuel at the desired injection pressure Short pipesconnect the rail to each injector. There is no pressureintensification within the injector.
The injection process is controlled by a solenoid valve ineach injector.
The final fuel injected quantity being dependent on the
opening period and system pressure. The solenoid is controlled by the ECU, as is the railpressure via a pressure sensor.
The Common Rail System
The key advantage of the common rail fuel system
compared to a traditional pump-line-nozzle system, isthat injection pressure is independent of engine speed
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p p p y ,that injection pressure is independent of engine speedand load.
Injection timing, rate, and duration can be variedprecisely over the operating range.
At part load the higher injection pressure available givesa reduction of particulate emissions. The lower
particulate emissions allow higher EGR rates, so theNOx emissions can be reduced, leading to a superiorNOx particulates trade off.
Pilot injection for combustion noise control is feasiblewith common rail. Small fuel quantities of 1 to 2 m3 /stroke can be injected before the main injection.
The Common Rail System
The high-pressure pump acts continuously and so has a
more uniform drive torque than the highly cyclic loadsimposed by distributor and unit injector pump
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q g y yimposed by distributor and unit injector pump.
A comparison between the capabilities of pump-line-nozzles systems, EUIs, common rail systems is shown inFigure 20.
Figure 20 Comparison of different electronic fuelling system capabilities.
Exhaust Gas Recirculation Exhaust gas recirculation (EGR) is a well-proven
technique for the effective suppression of NOxemissions. The reductions in emissions due to the
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influence of EGR are shown in Figure 20.
Figure 20 General trend on emissions due to the influence
of EGR in DI diesel engine.
Control of EGR EGR systems consist of an electronically controlled,
vacuum-operated poppet valve mounted mounted ont ehexhaust or the intake manifold.
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A current-to-vacuum transducer (CVT) controls theamount of vacuum applied to the EGR valve diaphragm,
which in turn lifts the poppet off its seat. The engine ECU contains schedules (look-up tables),
which relate engine speed, fueling rate, and mass airflow (MAF).
The MAF sensor is located in the air intake system andprovides the information to determine EGR valveposition and, hence, EGR mass flow is calculated by
implication.
Control of EGR There are a number of disadvantages with this method,
namely:
Volumetric characteristics of the engine can drift with
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gtime due to wear and tear and the build-up of deposits
The flow capacity of the EGR system can be affected
by partial blocking through deposit build-up (i.e., soot,particulates, and so on and wear of the EGR valve)
Blockages in the inlet air filter can seriously affect
EGR mass flow Blockages in the exhaust can cause increased
exhaust pressure
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After Treatment Devices
Catalytic Converter
All catalytic converters are built in a honeycomb or pellet geometry to expose
the exhaust gases to a large surface made of one or more noble metals:
platinum, palladium and rhodium.
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Rhodium used to remove NO and platinum used to remove HC and CO.
Lead and sulfur in the exhaust gas severely inhibit the operation of a catalytic
converter (poison).
Three-way Catalytic Converter
A catalyst forces a reaction at a temperature lower than normally occurs.
As the exhaust gases flow through the catalyst, the NO reacts with the CO,HC and H2 via a reduction reaction on the catalyst surface
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HC and H2 via a reduction reaction on the catalyst surface.e.g., NO+CON2+CO2 , NO+H2 N2+H2O, and others
The remaining CO and HC are removed through an oxidation reaction formingCO2 and H2O products (air added to exhaust after exhaust valve).
A three-way catalysts will function correctly only if the exhaust gas composition
corresponds to nearly (1%) stoichiometric combustion.
If the exhaust is too lean NO are not destroyed
If the exhaust is too rich CO and HC are not destroyed
A closed-loop control system with an oxygen sensor in the exhaust is used to
determine the actual A/F ratio and used to adjust the fuel injector so that the
A/F ratio is near stoichiometric.
Effect of Mixture Composition
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Since thermal efficiency is highest for slightly lean conditions it may seem thatthe use of a catalytic converter is a rather severe constraint.
The same high efficiency can be achieved using a near stoichiometric mixture
and diluting by EGR
Effect of Temperature
The temperature at which the converter becomes 50% efficient is referred to
as the light-off temperature.
The converter is not very effective during the warm up period of the engine
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Catalytic Converter for Diesels
For Diesel engines catalytic converters are used to control HC and CO, but
reduction of NO emissions is poor because the engine runs lean in order to
avoid excess smoke.
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The NO is controlled by retarding the fuel injection from 20o to 5o before TC in
order to reduce the peak combustion temperature.
This has a slight negative impact, increases the fuel consumption by about 15%