fundamentals of combustion _nptel
DESCRIPTION
Indian Institute of TechnologyTRANSCRIPT
NPTEL Online - IIT Kanpur
file:///D|/Web%20Course/Dr.%20D.P.%20Mishra/Local%20Server/FOC/lecture1/main.htm[10/5/2012 11:08:14 AM]
Course Name Fundamental of Combustion Department Aerospace Engineering, IIT Kanpur Instructor Dr. D.P. Mishra
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Question can never be silly,
It can be like a beautiful lily,
In the garden of knowledge,
This is still a truth, age after age. - Dr. D.P. Mishra
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Module 1: Introduction to Combustion Lecture 1: Introduction
The Lecture Contains:
Introduction to Combustion
What is Combustion?
Combustion Triangle
Applications of Combustion
Contd..
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Module 1: Introduction to Combustion Lecture 1: Introduction
Introduction to Combustion
Introduction
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Module 1: Introduction to Combustion Lecture 1: Introduction
Combustion Triangle
Essential conditions for combustion to occur
1. Presence of fuel .2. Presence of oxidizer (Not essentially oxygen).3. They must be in right proportions.4. The proportion will be dictated by flammability limit.5. Ignition energy.
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Module 1: Introduction to Combustion Lecture 1: Introduction
Applications of Combustion
Power PlantsChemical IndustriesDomestic BurnerAutomobiles
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Module 1: Introduction to Combustion Lecture 1: Introduction
Contd..
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Module 1: Introduction to Combustion Lecture 2: What is Fuel and Oxidizer?
The Lecture Contains:
What is Fuel and Oxidizer?
Types of Fuels and Oxidizers
Contd..
Characterization of a Gaseous Fuel
Junker's Calorimeter
Liquid Fuels and Oxidizers
Refinery End-Products of Typical Crude Oil
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Module 1: Introduction to Combustion Lecture 2: What is Fuel and Oxidizer?
What is Fuel and Oxidizer?
Electronegativity
The ability of an element to accept or donate electrons.Amount of pull that one atom exerts on the electron that it is sharing with other atom.The term electronegativity was coined by Linus Pauling, a Noble Laureate.
Element Electro-negativity
Element Electro-negativity
Element Electro-negativity
F 4 Br 2.8 B 2.0
O 3.5 C,S,I 2.5 Be,Al 1.5
N,Cl 3.0 H,P 2.1 Mg 1.2
Fluorine is having Highest Electronegativity (Most powerful oxidizer).
Oxygen has second highest electronegativity.
Carbon, Hydrogen, Aluminum and Magnesium have Low Electronegativity (Fuels).
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Module 1: Introduction to Combustion Lecture 2: What is Fuel and Oxidizer?
Types of Fuels and Oxidizers
Gaseous Fuel and Oxidizer
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Module 1: Introduction to Combustion Lecture 2: What is Fuel and Oxidizer?
Contd..
Types of Gaseous Fuel and Oxidizer
Sl. No. Fuel Oxidizer Application
1 LPG Air/O2 Domestic Burner, Furnace
2 Natural Gas (NG) Air/O2 IC Engines, Furnaces
3 Producer Gas Air/O2 EC/IC Engines
4 CH4, C3H8, H2 Air/O2 EC/IC Engines
5 Biogas Air/O2 EC/IC Engines, Burners
6 Acetylene Air/O2 Gas welding, Gas cutting
* EC=External Combustion
IC =Internal Combustion
Composition of Some Gaseous Fuels
Fuel CO2 O2 N2 CO H2 CH4 C2H6 C3H8 C4H10
LPG - - - - - - - 70 30
Natural Gas - - 5 - - 90 5 - -
Producer Gas 8 0.1 50 23.2 17.7 1 - - -
Propane - - - - - - 2.2 97.3 0.5
Biogas 33 - 1 - 1 65 - - -
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Module 1: Introduction to Combustion Lecture 2: What is Fuel and Oxidizer?
Characterization of a Gaseous Fuel
Heating Value:
Amount of heat released per unit volume when it undergoes oxidation at normal pressure andtemperature (0.1 MPa and 298 K).Lower heating value (LHV) – amount of heat released by burning 1 kg of fuel assuming thelatent heat of vaporization in the reaction products is not recovered.
Higher heating value (HHV) – heating value of the fuel when water is condensed. is the Latent heat of vaporization of water at 298.15 K
Junker's Calorimeter
(Figure 2.1)
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Module 1: Introduction to Combustion Lecture 2: What is Fuel and Oxidizer?
Determines the heating value of the gaseous fuel.Fuel and air are burnt in a burner.Cooling water in the water jacket-absorbs the heat released during combustion.Heating value- calculated from the water flow rate and rise in temperature.
Liquid Fuels and Oxidizers
Liquid fuel is one of the major energy sources in the transport sector.Crude oil is formed from organic sources, animals, vegetables – which are entrapped in rocksunder high pressure and temperature for million years.
Fuel Oxidizer Application
1 Gasoline Air S.I. Engine, Aircraft Piston Engine
2 HSD Air C.I. Engine
3 Furnace Oil Air Furnaces
4 Kerosene AirAircraft, Gas Turbine, Engines Ramjet, Domestic Burner
5 Alcohols Air I.C. Engine
6Hydrazine, UDMH, MMH, LiquidHydrogen, Triethyl Amine
Liquid O2, RFNA (Red
Fuming Nitric Acid)N2O4
Liquid propellant rocket Engines
7 Hydrogen, Kerocene Air Ramjet/Scramjet
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Module 1: Introduction to Combustion Lecture 2: What is Fuel and Oxidizer?
Refinery End-Products of Typical Crude Oil
Crude oil undergoes several process in the refinery.Generally separation of petroleum constituents occur in the distillation column.Constituents of typical crude oil is shown below.
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Module 1: Introduction to Combustion Lecture 3: Fuels
The Lecture Contains:
Bomb Calorimeter
Properties of Liquid Fuels
Properties of Common Liquid Fuels
Solid Fuels and Oxidizers
Contd..
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Module 1: Introduction to Combustion Lecture 3: Fuels
Bomb Calorimeter
Used to determine the calorific value of the liquid fuel.Liquid is burnt in the bomb in the presence of oxygen at about 2.5 MPa .The change in temperature in the water bath provides the calorific value of the fuel.
(Figure 3.2)
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Module 1: Introduction to Combustion Lecture 3: Fuels
Properties of Liquid Fuels
SpecificGravity
: Ratio of mass density of fuel to mass density of water at the same temperature
Reference temperature for fuel and water: 288.8 KAmerican Petroleum Institute (API) Scale:
Relation between APISG and HHV:
ForGasoline
:
ForKerosene
:
Auto IgnitionTemperature
: The lowest temperature required to make the combustion self sustained withoutany external aid
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Module 1: Introduction to Combustion Lecture 3: Fuels
Properties of Liquid Fuels
FlashPoint
: Minimum temperature at which liquid fuel will produce sufficient vapors to form aflammable mixture with air. Indicates maximum temperature at which liquid fuel can bestored without any fire hazard.
FirePoint
: Minimum temperature at which liquid fuel produces sufficient vapors to form a flammablemixture with air that continuously supports combustion establishing flame instead of justflashing.
SmokePoint
: Measure of the tendency of a liquid fuel to produce soot.
Properties of Common Liquid Fuels
Fuel Type AutomotiveGasoline
Diesel Fuel Methanol Kerosene ATF(JP8)
Specific gravity 0.72 - 0.78 0.85 0.796 0.82 0.71
Kinematics viscosity @ 293 K
(m2/s)0.8 X 10-6 2.5 X 10-6 0.75 X 10-6
3.626 X
10-6 --
Boiling point range (K) @ STP 303 - 576 483 - 508 338 423-473 442
Flash point (K) 230 325 284 311 325
Auto ignition temperature (K) 643 527 737 483 --
Stoichiometric air/fuel by weight 14.7 14.7 6.45 15 15.1
Heat of Vaporization (kJ/kg) 380 375 1185 298.5 --
Lower heating value (MJ/kg) 43.5 45 20.1 45.2 43.3
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Module 1: Introduction to Combustion Lecture 3: Fuels
Solid Fuels and Oxidizers Solid Fuels:
(Figure 3.2) Constituents of Solid Fuel:
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Module 1: Introduction to Combustion Lecture 3: Fuels
Contd..Types of Solid Fuels and Oxidizers:
S. No. Fuel Oxidizer Applications
1Biomass (Wood, Saw Dust, RiceHusk, Rice Straw, Wheat Straw,
etc)Air/O2
Domestic Burner,Engine With
Producer Gas
2 Coal, Coke, Charcoal do do
3Special Fuels
Nitrocellulose (NC), HTPB,CTPB
Nitroglycerine, AmmoniumPerchlorate , Ammonium Nitrate,
Nitrogen Tetraoxide
Solid PropellantRocket, Hybrid
Rocket
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Module 1: Introduction to Combustion Lecture 4: Characterization of Solid Fuels
The Lecture Contains:
Oxygen, Water and Ash Content of Certain Solid Fuels
Characterization of Solid Fuels
Various Combustion Modes
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Module 1: Introduction to Combustion Lecture 4: Characterization of Solid Fuels
Oxygen, Water and Ash Content of Certain Solid Fuels
Moisture in Solid Fuel:
1. Free2. Bound water
Fuel moisture content will affect rate of combustion and overall efficiency.
Ash: The inorganic materials, which remain as residue even after complete combustion.
Ash content affects the performance of the combustion system.Ash content causes fouling of the boilers.
Fuel Oxygen (Dry, Ash-free) Moisture (Ash-free) Ash (Dry)
Wood 40-45% 15-70% 0.1-1.0%
Peat 30-35% 70-90% 0.1-20%
Lignite coal 20-25% 20-30% >5%
Bituminous coal 3-5% 10-5% >5%
Anthracite coal 1-2% 2-4% >5%
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Module 1: Introduction to Combustion Lecture 4: Characterization of Solid Fuels
Characterization of Solid Fuels:Proximate Analysis:
Used to determine the moisture content, volatile matter, fixed carbon and ash content in thesolid fuel.To determine water content, few grams of fuel is heated around 378 K till it attains constantweight.Volatile matter is determined by heating the sample at 1173 K.
Ultimate Analysis:
Used to determine the major elemental composition of the solid fuel.Nitrogen content is determined by chemical method.Sulphur content is evaluated by burning the fuel to convert it into SO4 followed by precipitation
method. Calorific value can be determined by bomb calorimeter.
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Module 1: Introduction to Combustion Lecture 4: Characterization of Solid Fuels
Various Combustion Modes
Premixed Flame : Fuel and oxidizer are mixed before actual combustion.
Examples: Bunsen burner, LPG Stove
Diffusion Flame : Fuel and oxidizer are mixed in the region where chemical reactiontakes place.
Laminar and TurbulentFlames
: Based on the flow characteristics; Turbulent flow occurs in practicalcombustion devices.
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Module 1: Introduction to Combustion Lecture 5: Scope of Combustion
The Lecture Contains:
Scope of Combustion
Image Sources
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Module 1: Introduction to Combustion Lecture 5: Scope of Combustion
Scope of CombustionIndustrial Process
Thermal energy for process chemical plants, sugar industries, food processing industries areobtained through combustion.Iron, steel and other metals are produced from raw materials through combustion.Heat treatment and annealing of metals.Rotary kilns are used to produce Portlant cement.
Sugar Industry Food Processing
Process Chemical Plant Steel Plant
(Figure 5.1)
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Module 1: Introduction to Combustion Lecture 5: Scope of Combustion
TransportationSurface transport vehicles are operated by reciprocating IC EnginesGas turbine combustors are used widely in air and marine transportation sectors.
(Figure 5.2)
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Module 1: Introduction to Combustion Lecture 5: Scope of Combustion
PowerGeneration
Most of the thermal power plants are operated by burning coal.Recently gas turbine power plants are coming up.
Fluidized Bed Power Plant Coal Power Plant
Biomass Based Power Plant Gas Turbine Power Plant
(Figure 5.3)
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Module 1: Introduction to Combustion Lecture 5: Scope of Combustion
Waste Disposal
Combustion finds application in disposing waste materials.Incinerators are used to dispose domestic and industrial wastes.In modern hospitals, incinerators are used to dispose hospital wastes safely.
(Figure 5.4)
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Module 1: Introduction to Combustion Lecture 5: Scope of Combustion
FireSometimes fire causes damage to life and property.Forest Fire: Damages natural resources and lives.Structural Fire: Damages property and human lives.
Effective fire breakers should be designed and implemented to avoid fire hazard. By using properconstruction materials, Fire hazard can be minimized. Marine life is very much affected by oil spillfire.
(Figure 5.5)
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Module 1: Introduction to Combustion Lecture 5: Scope of Combustion
Environmental pollution
Combustion of any fuel produces certain amount of emissions such as smoke, ash, soot, andother harmful gases.Major pollution generated in combustion system are CO, CO2, NO, NO2, SO2, ash, etc.
These are due to incomplete combustion and can be minimized by increasing the residence timeof fuel-oxidizer mixture in the combustor.
Sources Particulates CarbonMonoxide
UnburntHydrocarbon
Nitrogenoxides
Sulfurdioxides
Transportation 7 79 60 15 6
StationaryCombustion
Systems/Electricity8 <1 <1 2 69
Industrial Process 23 8 32 13 25
Miscellaneous 62 13 8 70 <1
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Module 1: Introduction to Combustion Lecture 5: Scope of Combustion
Image Sources
Boiler : http://www.heatingoil.com/blog/39971019/
Incinerator : http://www.winderickx.pl/en/msw_municipal_waste_incinerators.php
IC Engine : http://www.engr.colostate.edu/~dga/mech324/handouts/cam_stuff/index.html
WankelEngine :
http://mazda-rx7.org/
Power Plant : http://www.teachengineering.org/view_lesson.php?url=http://www.teachengineering.org/collection/cub_/lessons/cub_earth/cub_earth_lesson08.xml
PulseDetonation
Engine :http://www.seas.ucla.edu/combustion/projects/pulsed_detonation_wave.html
RocketEngine :
http://www.lr.tudelft.nl/live/pagina.jsp?id=56438fe7-95c8-4c02-927c-82766a35721a&lang=en
Incinerator : http://www.wtert.eu/default.asp?ShowDok=13
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Module 1: Introduction to Combustion Lecture 5: Scope of Combustion
Image Sources Gas Turbine Engine : http://www.azom.com/details.asp?ArticleID=90
Furnace : http://www.macarthurcoal.com.au/Operations/Products/MetallurgicalProducts/tabid/96/Default.aspx
Process ChemicalIndustry :
http://www.hasbrouckengineering.com/aroma_engineering.htm
Steel Plant : http://www.forbesmarshall.com/fm_micro/industries.aspx?id=system
Biomass PowerPlant
: http://www.treehugger.com/files/2006/10/tallahassee_flo.php
Gas Turbine PowerPlant :
http ://www.power-technology.com/projects/knapsackccgt/knapsackccgt6.html
Fluidized BedPower Plant :
http://www.britannica.com/EBchecked/topic-art/1424725/113942/Schematic-diagram-of-a-fluidized-bed-combustion-boiler
Forest Fire : http://www.cartridgesave.co.uk/news/30-amazing-pictures-of-forest-fires/
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Module 1: Introduction to Combustion Lecture 5: Scope of Combustion
Image Sources
Oil Spill Fire : http://zeroequalsthree.blogspot.com/2010/09/chaos-oil-spill-chaos.html
Structural Fire : http://www.forensicmed.co.uk/pathology/fire-deaths/fire-destruction-of-bodies/
Dust Explosion : http://www.industrialairsolutions.com/industrial-vacuums/explosion-proof/explosion-proof-vacuums.htm
Gas Turbine Engine : http://www.ohio.edu/mechanical/thermo/Intro/Chapt.1_6/gasturbine/gas_turbine.html
Car : http://dodge-sprinter.net/wp-content/uploads/2011/02/Dodge-Sprinter-Van-Side-View.jpg
Ambassador Car : http://4.bp.blogspot.com/_rMX3SfIKwNc/TEuA4BHyCSI/AAAAAAAAAQk/BO7ZOgEVHtQ/s1600/ambassador
Aeroplane : http://www.dailymail.co.uk/news/article-564300/Passenger-jet-makes-terrifying-10-000ft-climb-dodge-plane-pilot-showing-child.html
Ship : http://www.a1-discount-cruises.com/cruise-ships.htm
IC Engine : http://www.birkey.com/technical-illustration/engine-piston-pin-sketch/
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One who asks a question fearlessly,
For a moment he may feel miserable,
One who dares not to ask questions,
He remains as a fool year after year.
-Dr. D.P.Mishra
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Module 2: Thermodynamics of Combustion Lecture 6: Introduction
The Lecture Contains:
Introduction
Thermodynamic Properties
Gas Mixture
Dalton's Law of Partial Pressure
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Module 2: Thermodynamics of Combustion Lecture 6: Introduction
Thermodynamics of Combustion
Introduction
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Module 2: Thermodynamics of Combustion Lecture 6: Introduction
Dalton's Law of Partial Pressure
Total no of moles, ..(1)Dividing by ,
Where, are mole fraction of species A, B,..Total mass of the mixture,
Dividing by ,
Where, are mass fraction of species A, B, ..
(Figure 6.2)
= Molecular weight of mixture
Also, from ideal gas law, Substituting in (1),
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Module 2: Thermodynamics of Combustion Lecture 6: Introduction
Gas Mixture
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Module 2: Thermodynamics of Combustion Lecture 6: Introduction
Thermodynamic Properties
(Figure 6.1)
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Module 2: Thermodynamics of Combustion Lecture 7: Thermodynamic Laws
The Lecture Contains:
Enthalpy and Internal Energy
Effect of Temperature on Heat Capacity
Thermodynamic Laws
First Law
Second Law
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Module 2: Thermodynamics of Combustion Lecture 7: Thermodynamic Laws
Enthalpy and Internal Energy
Specific internal energy of the mixture,
Mass specific internal energy of the mixture,
Specific enthalpy ofthe mixture,
Mass specific enthalpy of the mixture,
Enthalpy of a species,
Internal Energy of a species,
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Module 2: Thermodynamics of Combustion Lecture 7: Thermodynamic Laws
Effect of Temperature on Heat Capacity
Specific heats, and are functions of temperaturefor both ideal and real gases
(Figure 7.1)
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Module 2: Thermodynamics of Combustion Lecture 7: Thermodynamic Laws
Thermodynamic Laws
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Module 2: Thermodynamics of Combustion Lecture 7: Thermodynamic Laws
First Law of Thermodynamics
First law applied to a closed system:
Where, – Heat added to the system (Path Function)
– Work done by the system (Path Function)
– Total energy change in the system (Point Function)
First law applied to an open system:
Where, – Specific enthalpy – Velocity of flow – Height of inlet and outlet port
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Module 2: Thermodynamics of Combustion Lecture 7: Thermodynamic Laws
Second Law of Thermodynamics
Clausiusinequality:
For any system undergoing a cyclical process, the ratio of the sum of all heatinteractions to its temperature is equal to or less than zero.
Increase in entropyprinciple:
Second law of thermodynamics for controlvolume:
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Module 2: Thermodynamics of Combustion Lecture 8: Stoichiometry
The Lecture Contains:
Stoichiometry
Stoichiometry Calculation
Thermochemistry
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Module 2: Thermodynamics of Combustion Lecture 8: Stoichiometry
Stoichiometry
Stoichiometry: The elemental mass balance in a chemical reaction, describing exactly howmuch oxidizer has to be supplied for complete combustion of certain amount offuel.
Example:
Mass is conserved
(Figure 8.1)
Lean Mixture:
Quantity of oxidizer > Stoichiometric quantity
Rich Mixture:
Quantity of oxidizer < Stoichiometric quantity
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Module 2: Thermodynamics of Combustion Lecture 8: Stoichiometry
Stoichiometry Calculation
Problem: Gasoline Dry air Products (10.02% ; 5.62% ; 0.88% ; 83.48% )Determine (i) A/F Ratio; (ii) Equivalence Ratio; (iii) Stoichiometric Air Used
Solution Equation: 16.32 ( 3.76 ) 7.37 + 0.65 4.13 61.38 9
((12 8 ) 18)/(16.32(32 (3.76 28))) = 0.05089
Stoichiometric Equation:
12.5( 3.76 ) 8 9 47
((12 8 ) 18)/(12.5(32 (3.76 28))) = 0.06643
Equivalence ratio 0.766
Since <1 ; The mixture is leanStoichiometric Air Used:
Stoichiometric air = 100 / = 100/ 0.766 = 130.5%
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Module 2: Thermodynamics of Combustion Lecture 8: Stoichiometry
Thermochemistry
(Figure 8.2)
Consider the burner as shown below:
(Figure 8.3)
Assumption: (i) Negligible change in K.E. & P.E., (ii) No shaft work
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Module 2: Thermodynamics of Combustion Lecture 8: Stoichiometry
Thermochemistry
Where, HR – Total enthalpy of reactants; HP – Total enthalpy of products
niR – No of moles of ith reactant; niP – No of moles of ith product
hiR – Enthalpy of formation per unit mole of ith reactant
hiP – Enthalpy of formation per unit mole of ith product
– Standard heat of reaction
Heat of reaction depends on temperature
(Figure 8.4)
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Module 2: Thermodynamics of Combustion Lecture 9: Heat of Combustion
The Lecture Contains:
Heat of combustion
Hess Law
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Module 2: Thermodynamics of Combustion Lecture 9: Heat of Combustion
Heat of Combustion
For the reaction :Heat of reaction is
given by :
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Module 2: Thermodynamics of Combustion Lecture 9: Heat of Combustion
Heat of formation of important species at 25 °C and 0.1 MPa
Species Formula State Heat of formation (kJ/mol)
Oxygen O2 Gas 0
Hydrogen H2 Gas 0
Hydroxyl OH Gas 42.3
Water H2O Gas -242
Water H2O Liquid -286
Carbon monoxide CO Gas -110.5
Carbon dioxide CO2 Gas -394
Methane CH4 Gas -74.5
Propane C3H8 Gas -103.8
Butane (n) C4H10 Gas -124.7
Kerosene CH1.842 Liquid -51.6
Nitrogen dioxide NO2 Gas 33.9
Nitric acid NO Gas 90.4
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Module 2: Thermodynamics of Combustion Lecture 9: Heat of Combustion
Hess Law
Illustration: Determine the heat of reaction for water gas shift reaction
IntermediateReactions:
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Module 2: Thermodynamics of Combustion Lecture 10: Adiabatic Flame Temperature
The Lecture Contains:
Adiabatic Flame Temperature
Effect of Equivalence Ratio on Adiabatic Flame Temperature
Effect of Initial Temperature on Adiabatic Flame Temperature
Effect of Pressure on Adiabatic Flame Temperature
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Module 2: Thermodynamics of Combustion Lecture 10: Adiabatic Flame Temperature
Effect of Equivalence Ratio on Adiabatic Flame Temperature
(Figure 10.1)
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Module 2: Thermodynamics of Combustion Lecture 10: Adiabatic Flame Temperature
Adiabatic Flame Temperature
Where,
S.W -K.E -P.E -
Shaft workKinetic EnergyPotential Energy
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Module 2: Thermodynamics of Combustion Lecture 10: Adiabatic Flame Temperature
Effect of Initial Temperature on Adiabatic Flame Temperature
(Figure 10.2)
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Module 2: Thermodynamics of Combustion Lecture 10: Adiabatic Flame Temperature
Effect of Pressure on Adiabatic Flame Temperature
(Figure 10.3)
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Module 2: Thermodynamics of Combustion Lecture 10: Adiabatic Flame Temperature
Effect of Pressure on Adiabatic Flame Temperature
System Tu (K) P (MPa) Tad (K)
CH4 Air 300 0.1 2200
CH4 - Air 300 2.0 2270
CH4 - Air 600 2.0 2500
CH4 - O2 300 0.1 3030
C3H8 - Air 300 0.1 2278
H2 - Air 300 0.1 2390
H2 - O2 300 0.1 3080
CO - Air 300 0.1 2400
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Module 2: Thermodynamics of Combustion Lecture 11: Chemical Equilibrium
The Lecture Contains:
Chemical Equilibrium
Procedure for Determining Equilibrium composition
Summary
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Module 2: Thermodynamics of Combustion Lecture 11: Chemical Equilibrium Chemical Equilibrium
Chemical reaction proceeds in the direction of increasing entropy
If the system is not adiabatic, we have to invoke Gibbs free energy, G
From 1st Law,
At constant pressure and temperature,
From 2nd Law, of Thermodynamic
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Module 2: Thermodynamics of Combustion Lecture 11: Chemical Equilibrium
Procedure for Determining Equilibrium Composition
Equilibrium products can be estimated by adopting the following stepsStep 1: Identify probable equilibrium speciesStep 2: Identify equilibrium reactions schemeStep 3: Find out equilibrium constantStep 4: Strike balance for elemental conservationStep 5: Strike overall mass conservationStep 6: Solve all equations by iterative method (Newton- Raphson Method)
For a ideal gas mixture, Gibbs function of i th species is given by
-Gibbs function per mole of ith species.
-Partial pressure of ith species.-Temperature-Universal gas constant
Gibbs function for a ideal gas mixture
At equilibrium,
In the above equation, (Since pressure remains constant)
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Module 2: Thermodynamics of Combustion Lecture 11: Chemical Equilibrium
Consider the reaction
Where, a, b, c and d are stoichiometric coefficientsChange in number of moles of each species is given by,
Substituting above equation in Gibbs function, We can get,
In terms of mole fraction,
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Module 2: Thermodynamics of Combustion Lecture 11: Chemical Equilibrium
Summary
The basic thermodynamic principles are useful in estimation of properties related tocombustion.Stoichiometric calculations are useful in estimation of fuel-air requirements for a combustionprocess.Adiabatic flame temperature indicates maximum possible temperature in combustion process.Thermodynamic relations can be used to relate the change in Gibbs free energy withequilibrium constant.Equilibrium composition can be used to calculate adiabatic flame temperature using aniterative procedure.
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After asking a question about the unknown thing,
Examination of it is a must by own reasoning,
As reasoning is the backbone of everything,
That is the sole objective of all our learning.
-Dr. D.P.Mishra
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Module 3: Physics of Combustion Lecture 12: Introduction
The Lecture Contains:
Introduction
Laws of Transport Phenomenon
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Module 3: Physics of Combustion Lecture 12: Introduction
Physics of Combustion
Introduction
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Module 3: Physics of Combustion Lecture 12: Introduction
Laws of Transport Phenomenon
Newton's Law of Viscosity
Two parallel plates-separated by ‘Y'Lower plate is fixedAt t< 0; system is at restAt t=0; upper plate ismovedVelocity of plate: Vx
(Figure 12.1)
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Module 3: Physics of Combustion Lecture 12: Introduction
Newton's Law of Viscosity can be expressed as,
Where, µ is dynamic viscosity (kg/ms)dVx/dy is the shear strain rate-ve sign: momentum flux in thedirection of decreasing velocity
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Module 3: Physics of Combustion Lecture 12: Introduction
Fourier's Law of HeatConduction
Two parallel plates-separated by ‘Y'Lower plate is fixedAt t < 0; two plates are atthe same temperatureAt t = 0; upper plate issuddenly heated (T1 >T0 )
Lower plate – Maintainedat temperature T0
(Figure 12.2)
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Module 3: Physics of Combustion Lecture 12: Introduction
Fick's Law of Species Diffusion
Two parallel plates-separated by‘Y'.Upper plate is maintained wet.Lower plate is kept dry(Dehydrating agent)Water vapour evaporates at upperplatePartial pressure of water vapour ismaintained at saturated vapourpressure of waterThus concentration gradient existsbetween the two platesMass flux-proportional toconcentration, CA inversely
proportional to distance Y
Differential form of Fick's law
(Figure 12.3)
Binary diffusitivity of species A through B
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Module 3: Physics of Combustion Lecture 13: Transport properties for gas mixture
The Lecture Contains:
Transport properties for gas mixture
Mass conservation equation
Momentum conservation equation
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Module 3: Physics of Combustion Lecture 13: Transport properties for gas mixture
Transport properties for gas mixture
Viscosity of gas mixture
Wassilijewa equation
Mason and Saxena modification
is the viscosity of the pure component
is the mole fraction of the ith component
Thermal Conductivity of gas mixture
Wassilijewa equation
Mason and Saxena modification
is the thermal conductivity of the pure component
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Module 3: Physics of Combustion Lecture 13: Transport properties for gas mixture
Diffusion Coefficient of any component in a gas mixture
Wilke equation
Where, is the collision diameter in
is the pressure (Bar)
is the molecular weight of the components
is the collision integral
=Boltzman's constant
=Intermolecular potential
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Module 3: Physics of Combustion Lecture 13: Transport properties for gas mixture
Mass conservation equationPrinciple of mass conservation
------ (1)
Rate of accumulation in fluid element = ------ (2)
Rate of mass in fluid element across face A = ------ (3)
Rate of mass leaving fluid element across face B = ------ (4)
The net efflux in x-direction = ------ (5)
The net efflux in y-direction = ------ (6)
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Module 3: Physics of Combustion Lecture 13: Transport properties for gas mixture
Substituting (2), (5) and (6) in (1)
Differential form of continuity equationIn vector notation,
Where, is the gradient operator
is the divergence of
For incompressible flow,
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Module 3: Physics of Combustion Lecture 14: Momentum conservation equation
The Lecture Contains:
Momentum conservation equation
Species transport equation
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Module 3: Physics of Combustion Lecture 14: Momentum conservation equation
Momentum conservation equation
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Module 3: Physics of Combustion Lecture 14: Momentum conservation equation
Momentum conservation equation
Rate of momentum accumulation in x-direction =
Rate of momentum accumulation in y-direction =
Momentum in x-direction into fluid elementacross face A
=
Momentum in x-direction leaving the fluid element across face B =
=
Momentum in y-direction entering the fluidelement through face C
=
Momentum in y-direction leaving the fluidelement across face D
=
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Module 3: Physics of Combustion Lecture 14: Momentum conservation equation
Net forces acting on the fluid element in x-direction =
Net body forces acting in fluidelement in the x-direction
=
Momentum equation for fluid elementin x-direction
=
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Module 3: Physics of Combustion Lecture 14: Momentum conservation equation
Momentum equation for fluidelement in x-direction
=
where, , are components of mass velocity vector in x and y direction and are surfacestresses
Applying Stokes viscosity law, the surface stresses are given by
Momentum equation forfluid element in x-direction
=
Momentum equation forfluid element in y-direction
=
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Module 3: Physics of Combustion Lecture 14: Momentum conservation equation
Species transport equation
Rate of accumulation in fluid element=
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Module 3: Physics of Combustion Lecture 14: Momentum conservation equation
Rate of accumulation in fluid element=
Rate of mass of species A into fluid element across face A =
By Taylor's series expansion, the rate of massofspecies A leaving fluid element across face B
=
Net efflux in x direction =
Net efflux in y direction =
Mass production rate of ith species due to chemical reaction =
According to Fick's law,
Species transport equation is given by,
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Module 3: Physics of Combustion Lecture 15: Energy transport equation
The Lecture Contains:
Energy transport equation
Boundary layer concept
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Module 3: Physics of Combustion Lecture 15: Energy transport equation
Energy transport equation
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Module 3: Physics of Combustion Lecture 15: Energy transport equation
Heat accumulated in the fluid element =
Amount of heat entering into fluidelement through face ‘A' is given by:
Amount of heat leaving from the fluidelement through face ‘B' is given by:
Net efflux in x direction
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Module 3: Physics of Combustion Lecture 15: Energy transport equation
Amount of heat interaction in y-direction through faces ‘C' and ‘D' is
In a fluid element, heat may be absorbed or removed due to chemical reaction
The amount of heat interaction in fluid element per unit area:
By striking out an energy balance, the energy equation for a multi-component reactive systembecause.
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Module 3: Physics of Combustion Lecture 15: Energy transport equation
Boundary layer concept
Velocity of fluid increases from zero at wall to free stream velocityVelocity gradients appear near a thin region adjacent to wall
(Figure 15.1)
The thin region adjacent to wall surface is the boundary layerWall friction-causes reduction in velocity near the wall
Boundary layer thickness times the free stream velocity
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Module 3: Physics of Combustion Lecture 16: Boundary layer solutions
The Lecture Contains:
Boundary layer solution
Thermal Boundary layer
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Module 3: Physics of Combustion Lecture 16: Boundary layer solution
Boundary layer solution
Approximate solution for steady 2D incompressible flow over a flat plate
Mass conservation
Momentum conservation
By boundary layer approximations,
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Module 3: Physics of Combustion Lecture 16: Boundary layer solution
Boundary layer solution
By carrying out order of magnitude analysis,
Mass conservation
Momentum conservation
From the above equation, pressure remains constant along ‘y' direction.Analytical method of Blasius gives exact solution of the above equations.
Relation between B. L. thickness and Re is
Drag coefficient for laminar flow over flat plate:
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Module 3: Physics of Combustion Lecture 16: Boundary layer solution
Thermal Boundary layer
Free stream temperature Flat plate temperature
Heat transferred from fluid toplate
(Figure 16.1)
Thermal boundary layer thickness , Value of y for which
Thermal boundary layer grows with increase in distance from the leading edge
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Module 3: Physics of Combustion Lecture 16: Boundary layer solution
Local heat flux due to convection,
(Newton's law of cooling)
Local heat flux at the wall,
(Fourier's law of conduction)
Combining there two equations, the convective heat transfer coefficient (h) is given by,
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Module 3: Physics of Combustion Lecture 16: Boundary layer solution
Using Pohlhausen method, Nusselt number (Nu) can be expressed as
Valid for can be used for most of the gases
For laminar fully developed pipe flow, Valid for constant temperature
For laminar fully developed pipe flow, Valid for constant heat flux
Average Nusselt number for developingpipe flow,
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Module 3: Physics of Combustion Lecture 17: Transport in Turbulent Flow
The Lecture Contains:
Transport in Turbulent Flow
Characterization of Turbulent Flow
Turbulent Boundary layer
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Module 3: Physics of Combustion Lecture 17: Transport in Turbulent Flow
Transport in Turbulent Flow
Turbulent Flow:
At high Reynolds and Grashof'snumber, the properties, velocity andtemperature exhibits random variation.Eddies move randomly back and forthacross the adjacent fluid layers.Turbulence reduces the B.L. thickness.Enhanced mass, momentum, andenergy transfer rates.
(Figure 17.1)
Where, – Time averaged value ofvelocity
– Fluctuating component ofvelocity
Turbulent diffusivity is given by,
(Figure 17.2)
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Module 3: Physics of Combustion Lecture 17: Transport in Turbulent Flow
Characterization of Turbulent Flow
Length scale of Turbulence:
The distance covered by an eddy before it disappears or loses its identity.
Intensity of Turbulence:
Measure of violence of eddies.
Turbulence Intensity:
Length Scales usedin Turbulent Flow:
1. Macroscopic scale, L (Characteristic width of flow)2. Integral Scale,
3. Taylor micro scale, 4. Kolmogorov length Scale,
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Module 3: Physics of Combustion Lecture 17: Transport in Turbulent Flow
Taylor microscale,
where, is the mean strain rate
Kolmogorov length scale,
Note:Kolmogorov length scale ( ) is related to integral length scale ( )( ) - Thickness of the smallest vortex present in turbulent flow
Turbulent Reynolds number based on the length scales
Note: is the characteristic velocity
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Module 3: Physics of Combustion Lecture 17: Transport in Turbulent Flow
Turbulent Boundary layer
Consider 2D steady incompressible turbulent flow over a flat plate,
Momentum equation in x direction is given by,
The term is known as Reynolds stress
Energy equation for turbulent boundary layer is given by,
A simple model for Reynolds stress suggested by Bossinesq,
Similarly,
; where, is the turbulent diffusivity
; where, is the eddy diffusivity
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Module 3: Physics of Combustion Lecture 17: Transport in Turbulent Flow
In analogy to kinetic theory of gases, Prandtl suggested an expression for turbulent diffusivity
Where, is the mixing length, and I is the turbulence intensity
Combining these two equations,
C, is the constant, obtained from the experimental data
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Asking a question is not the end of a thing,
One can assume it to be a humble beginning,
If explored earnestly without bothering,
One can definitely have a happy ending. -Dr. D.P. Mishra
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Module 4: Chemistry of combustion Lecture 18: Introduction
The Lecture Contains:
Introduction
Basic Reaction Kinetics
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Module 4: Chemistry of combustion Lecture 18: Introduction
Chemistry of combustion
Introduction
Chemical kinetics:The specialized branch of physical chemistry dealing with the study of chemical reactions and theirgoverning factors.
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Module 4: Chemistry of combustion Lecture 18: Introduction
Basic Reaction Kinetics
Reaction rate:Rate of decrease of reactant concentration or rate of increase of product concentration. Expressed in
terms of mole/m3sCompact expression for chemical reaction:
Where, and are stoichiometric coefficients of reactants and products.N is the total number of speciesM is the arbitrary specification of all chemical species
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Module 4: Chemistry of combustion Lecture 18: Introduction
Expressing the reaction using index notation:
Here, N=2
Here, N=3
Note: The above reactions are elementary in nature
Global reactions,3 bonds have to be broken,4 bonds have to be formed
Unlikely to occur!!
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Module 4: Chemistry of combustion Lecture 18: Introduction
Global reactions,
Bimolecular reactionsReaction between two molecules,
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Module 4: Chemistry of combustion Lecture 19: Law of Mass Action
The Lecture Contains:
Law of Mass Action
Collision Theory
Elementary Reactions
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Module 4: Chemistry of combustion Lecture 19: Law of Mass Action
Law of Mass Action
The rate of reaction, RR of a chemical species is proportional to the product of the concentrations ofthe participating chemical species, where each concentration is raised to the power equal to thecorresponding stoichiometric coefficient in the chemical reaction.
Where, is the specific reaction rate or rate coefficient
Note :
-depends on temperature and activation energy and not on concentration. Law of mass actionholds good only for elementary reactions
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Module 4: Chemistry of combustion Lecture 19: Law of Mass Action Collision Theory
(Figure 19.1)The colliding molecules must possess higher energy than the mean energy
Boltzman's energy distribution law:The probability of a molecule possessing the threshold energy, E is proportional to exp
Conditions for chemical reactions to occur:
Suitable molecule must collide with each otherThe molecules must collide with proper orientation (Determined by steric factor)Colliding molecules must possess energy greater than the threshold energy(E).
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Module 4: Chemistry of combustion Lecture 19: Law of Mass Action
From collision theory,
- Collision frequency,
- Steric factor,
- Boltaman's energy probability factor
- Activation energy
(Figure 19.2)From kinetic theory,
- Average effective collision diameter between molecules A and B,
- Boltaman's constant = 1.381 X 10-23J/K
- Reduced mass
Reaction rate
(Pre-exponential Factor)
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Module 4: Chemistry of combustion Lecture 19: Law of Mass Action
The form of equation in previous section is Arrhenius law
Limitations of Arrhenius law:
It cannot simulate combustion processover wide range of temperature.Rate law matches experimental data athigh temperature, but not so at lowtemperature.
Variation of RR with temperature: (Figure 19.3)An increase in temperature by 10% forsame activation energy can cause RRto be enhanced by 250 %
(Figure 19.4)
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Module 4: Chemistry of combustion Lecture 19: Law of Mass Action
Elementary Reactions
If the reaction occurs successfully at molecular level, the reaction is termed as elementary.
Molecularity :Number of molecules or atoms participating in each reaction leading to product.
1. Unimolecular reaction 2. Bimolecular reaction 3. Trimolecular reaction
Order of Reaction:Number of molecules or atoms whose concentration would determine the reaction rate.
Example:
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Module 4: Chemistry of combustion Lecture 20: Order reaction
The Lecture Contains:
First Order Reaction
Second Order Reaction
Third Order Reaction
Reverse Reaction
Chain Reaction
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Module 4: Chemistry of combustion Lecture 20: Order reaction
First order reaction,
Consider the first order reaction,
Reaction rate,
Sepataring the variables and integrating, (Figure 20.1)
First order combustion reactions!
Note : concentration decreases exponentially with time (Refer Fig),All unimolecular reactions obey first order kinetics!All first order reactions need not to be unimolecular!!
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Module 4: Chemistry of combustion Lecture 20: Order reaction
Second Order Reaction
Consider the second order bimolecular reaction,
Reaction rate for the above reaction,
General second order reaction
Concentration of species A and B
Reaction rate for the above reaction,
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Module 4: Chemistry of combustion Lecture 20: Order reaction
Multiplying both sides by
Integrating,
Second order combustion reactions!
By applying we will get
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Module 4: Chemistry of combustion Lecture 20: Order reaction
Third Order Reaction
Consider the third order, trimolecular reaction,
RR proportional to third power of concentration of participating species,
Third order combustion reactions !
Reverse Reaction Chemical reactions may proceed in both forward and reverse directions.
Net rate of consumption of A,
Substituting in the above equation, we will get
By integreting the above equation, we can get
can be estimated from the knowledge of
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Module 4: Chemistry of combustion Lecture 20: Order reaction
Chain Reaction
In reality, combustion process involves several reactionsThe overall stoichiometric chemical reaction is unlikely to occur in nature. The elementary reactionscan be classified as;
Chain initiatingChain branchingChain carryingChain terminating
Chain branchingThe ratio of number of free radicals in the product to the reactant > 1
Chain carryingThe ratio of number of free radicals in the product to the reactant = 1
Chain terminatingThe ratio of number of free radicals in the product to the reactant < 1
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Module 4: Chemistry of combustion Lecture 21: Chain Branching Explosion
The Lecture Contains:
Chain Branching Explosion
Multistep Reaction Mechanism
Quasi-Steady State Approximation
Partial Equilibrium Approximation (PEA)
Global Kinetics
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Module 4: Chemistry of combustion Lecture 21: Chain Branching Explosion
Chain Branching Explosion
Explosion:
Very rapid combustion of fuel andoxidizer, leading to violent release ofenergy.
(Figure 20.2)
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Module 4: Chemistry of combustion Lecture 21: Chain Branching Explosion
Chain Branching Explosion
To begin with, stoichiometric mixture of H2 and
O2 is kept in a container.
Temperature is increased beyond 773 K.Result: Very rapid chemical reaction withexplosion.
(Figure 21.1)
Regimes in the explosion chart1. First limit2. Second limit3. Third limit
(Figure 21.2)
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Module 4: Chemistry of combustion Lecture 21: Chain Branching Explosion
Multistep Reaction Mechanism
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Module 4: Chemistry of combustion Lecture 21: Chain Branching Explosion
Quasi-Steady State Approximation
Radicals are formed during combustionHalf life period of radicals - Very smallRate of formation = Rate of destruction
Relate radical concentration withmeasurable concentration of other species
Consider the two step chain reaction,
; ;
Reaction rate of the three species,
Initial condition,
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Module 4: Chemistry of combustion Lecture 21: Chain Branching Explosion Applying initial condition,
Applying QSSA method to A2, (Figure 21.3)
; ;
; ;
QSSA method predicts the concentration of species especially when
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Module 4: Chemistry of combustion Lecture 21: Chain Branching Explosion
Partial Equilibrium Approximation (PEA)
PEA expresses concentration of unknown species in terms of known concentrations.
Consider NO formation mechanism,
Reaction Rate (RR) for NO species:
Note 1: O and N2 concentration are required to determine RR
Note 2: Rate of formation and destruction of O is very high
Difficult to measure the concentration of O!!!
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Module 4: Chemistry of combustion Lecture 21: Chain Branching Explosion
Step 1: Assume partial equilibrium for O2
molecule
Step 2:
Relate O2 molecule to O by
Equilibrium constant
Reaction Rate (RR) for NO species:
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Module 4: Chemistry of combustion Lecture 21: Chain Branching Explosion
Global Kinetics
Single step methane combustion:
Overall reaction rate (CH4)
Global kinetic scheme for an arbitrary hydrocarbon (CxHy):
Overall reaction rate (CxHy)
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One has to pursue questions earnestly,
Like a faithful shadow meticulously,
One should bear questions in mind,
Like a small innocent inquisitive child. -Dr. D.P. Mishra
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Module 5: Premixed Flame Lecture 22: Introduction
The Lecture Contains:
Introduction
One-dimensional Combustion Wave
Analysis of 1D Flame
Hugoniot Curve...
Laminar Premixed Flame
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Module 5: Premixed Flame Lecture 22: Introduction
Premixed Flame
Introduction
Premixed Flame: Fuel and oxidizer are mixed well at the molecular level before combustion
Examples of premixed flame :Bunsen burner, LPG domestic burner, SI Engine, Afterburner in jet engine
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Module 5: Premixed Flame Lecture 22: Introduction
One-dimensional Combustion Wave
(Figure 22.1)
(Figure 22.2)
(Figure 22.3)
(Figure 22.4)
s
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Module 5: Premixed Flame Lecture 22: Introduction
Analysis of 1D Flame
Continuity Equation : State Equations:
Momentum Equation :
Energy Equation :
are the density, velocity, pressure and temperature
q is the heat release per unit mass
is the mass fraction of species
heat of formation of species
Combining Continuity and Momentum Equations and expressing them in terms of Mach number,
Rearranging the energy equation, we can get
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Module 5: Premixed Flame Lecture 22: Introduction
Hugoniot Curve ..Hugoniot Curve : vs. for a
fixed value of q, inlet pressure ,and inlet density
Region I: Pressure of burnedgas Pressureof C-J detonationwave Strong detonation
Gasvelocity relativeto wave front isslowedto subsonic speed
Pressure and
density increasessignificantlyfor will be
rarely observed (Figure 22.5)
Region II: Pressure of burned gas Pressure ofC-J detonation wave Weak detonation
Gas velocity relative to wave front is slowed to subsonic speed
Burned gas velocity > speed of sound at isochoric condition weak
detonation attains infinite velocity
Region III: In this region Therfore
Hence in this region is imaginary and physically impossible
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Module 5: Premixed Flame Lecture 22: Introduction Laminar Premixed Flame
(Figure 22.6)
(Figure 22.7)
First laboratory premixed
Glame burner : Invented by
Robert Bunsen in 1855
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Module 5: Premixed Flame Lecture 22: Introduction
Luminous Zone
Flame radiation: 3300 to 4400 A°
(Figure 22.8)
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Module 5: Premixed Flame Lecture 23: Structure of 1D Premixed Flame
The Lecture Contains:
Structure of 1D Premixed Flame
Laminar Flame Theory
Flame Thickness
Burning Velocity Measurement Methods
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Module 5: Premixed Flame Lecture 23: Structure of 1D Premixed Flame
Structure of 1D Premixed Flame
Preheat zone: Negligibly small heatrelease
(Figure 23.1)
Certain chemical reactions takeplace in this zone
Reaction zone:most of the chemical energy isreleased in the form of heatDecomposition of fuel takes place,leading to intermediate radicalformationReaction zone is very thin ascompared to the preheat zone.Temperature gradient andconcentration gradient are high.
Recombination zone: CO2 and H2O are formed;
No heat release in this zone
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Module 5: Premixed Flame Lecture 23: Structure of 1D Premixed Flame
Laminar Flame Theory
Assumptions:1D, steady, inviscid flow.Flame is quite thin.Ignition temperature is very close to flame temperature.No heat loss including radiation; Adiabatic flame.Pressure difference across the flame is negligibly small.Binary diffusion, Fourier and Fick's law are valid.Unity Lewis number.Constant transport properties
Mass conservation: (1)
Species conservation: Energy equation:
Fuel: (2) (5)
Oxidizer: (3) Global reaction mechanism:
Product: (4) (6)
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Module 5: Premixed Flame Lecture 23: Structure of 1D Premixed Flame
Laminar Flame Theory (Contd.)
Heat release due to chemical reaction:
(7)
Now energy equation becomes In the reaction zone,
(8)
Boundary conditions (For preheat zone)
(10)
(11)
Recasted energy equation forpreheat zone,
Rewriting, E.g. (11).
(9) (12)
Heat transfer due to conduction is balanced byconvective heat transfer. (13)
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Module 5: Premixed Flame Lecture 23: Structure of 1D Premixed Flame
Laminar Flame Theory (Contd.)
Combining equations (10) and (13),
(14)
(15)
Also,Mean fuel burning rate can also beexpressed as,
(16) (19)
Combining equations (15) and (16),Expression for burning velocitybecomes,
(17)
Mean fuel burning rate per unit volume,
(18)
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Module 5: Premixed Flame Lecture 23: Structure of 1D Premixed Flame
Flame Thickness
Ignition temperature can be approximated as
The temperature gradient at the flame surface is
Flame thickness:
(Figure 23.2)
Where,
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Module 5: Premixed Flame Lecture 23: Structure of 1D Premixed Flame
Burning Velocity Measurement Methods
(Figure 23.3)Flame front visualization
Luminous photographyShadowgraph photographySchlieren Photography
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Module 5: Premixed Flame Lecture 24: Tube Method
The Lecture Contains:
Tube Method
Combustion Bomb Method
Soap Bubble Method
Stationary Flame Method (Bunsen Burner)
Flat Flame Burner
Effect of Equivalence Ratio on SL
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Module 5: Premixed Flame Lecture 24: Tube Method
Tube Method
(Figure 24.1) Procedure: Combustible mixture is filled in the tube
On ignition at one end, the flame propagates through the tube
Features: Inner dia of tube should be greater than the quenching diameterThe flame is planar in the beginning and curved towards downstream, due tobuoyancyNatural convection distorts the planar flame front due to difference in densitiesFriction at the tube wall is also a reason for parabolic shape of the flame
The burning velocity is given by : Flame front velocity
: Unburnt gas velocity
: Cross-sectional area of tube
: Flame surface area
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Module 5: Premixed Flame Lecture 24: Tube Method
Combustion Bomb Method
(Figure 24.2)
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Module 5: Premixed Flame Lecture 24: Tube Method
Soap Bubble Method
(Figure 24.3)
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Module 5: Premixed Flame Lecture 24: Tube Method
Stationary Flame Method (Bunsen Burner)
(Figure 24.4)
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Module 5: Premixed Flame Lecture 24: Tube Method
Flat Flame Burner
(Figure 24.5)
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Module 5: Premixed Flame Lecture 24: Tube Method
Effect of Equivalence Ratio on SL
(Figure 24.6)
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Module 5: Premixed Flame Lecture 25: Effect of Oxygen Concentration on SL
The Lecture Contains:
Effect of Oxygen Concentration on SL
Effect of Initial Pressure and Temperature on SL
Effect of Inert Additives
Flame Extinction
Flame Quenching
Simplified Analysis for Quenching Diameter
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Module 5: Premixed Flame Lecture 25: Effect of Oxygen Concentration on SL Effect of Oxygen Concentration on SL
(Figure 25.1)
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Module 5: Premixed Flame Lecture 25: Effect of Oxygen Concentration on SL
Effect of Initial Pressure and Temperature on SL
This relation is supported byexperimental datan: Overall order of global chemicalreaction
for HC flames with
for HC flames with
for HC flames with
Pressure index,
For , m is negative,indicating burning velocity increaseswith decreasing pressure
(Figure 25.2)
For , m isconstant, indicating burning velocity isconstant
For , m is positive,indicating burning velocity decreaseswith decrease in initial pressure
(Figure 25.3)
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Module 5: Premixed Flame Lecture 25: Effect of Oxygen Concentration on SL
Effect of Inert Additives
(Figure 25.4)
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Module 5: Premixed Flame Lecture 25: Effect of Oxygen Concentration on SL
Flame Extinction
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Module 5: Premixed Flame Lecture 25: Effect of Oxygen Concentration on SL
Flame Quenching
Fuel Oxidizer SL (cm/s) dq (mm)CH4 Air 40 2.5
CH4 O2 0.3
C3H8 Air 45 2.0
C3H8 O2 0.25
C2H2 Air 140 0.8
C2H2 O2 0.2
CO Air 2.8
H2 Air 210 0.5
H2 O2 0.2
Quenching diameter for various stoichiometricfuel-oxidizer ratio.
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Module 5: Premixed Flame Lecture 25: Effect of Oxygen Concentration on SL
Simplified Analysis for Quenching Diameter
Rate of heat generated per unit volume
Heat generated in flame volume
Heat loss rate due to wall conduction
(Figure 25.5)Assuming linear temperature distribution inflame, Quenching diameter
After simplification,
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Module 5: Premixed Flame Lecture 26: Flammability Limits
The Lecture Contains:
Flammability Limits
Effect of Pressure on Limit Mixture
Ignition
Flame Stabilization
Flame Stabilization by Burner Rim
Turbulent Premixed Flame
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Module 5: Premixed Flame Lecture 26: Flammability Limits Flammability Limits
Instrument to determine flammabilitylimit
Vertical glass tube of 1.2 m lengthand 50 mm ID
(Figure 26.1)
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Module 5: Premixed Flame Lecture 26: Flammability Limits
Effect of Pressure on Limit Mixture
(Figure 26.2)
Fuel Oxidizer Stoichiometry (% Fuel) LFL (%) UFL (%)
Methane Air 9.5 5 15
Ethane Air 5.6 2.8 12.4
Propane Air 5.6 2.1 9.1
CO Air 29.5 12 74.2
Hydrogen Air 29.2 4 74.2
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Module 5: Premixed Flame Lecture 26: Flammability Limits
Ignition
Energy generated in flame = Ensible enthalpy Mass
Substituting quenching diameter
Substituting flame thickness (Figure 26.3)
Fuel-Air MIE (mJ)
Dependence on pressure Methane-air 0.47
Ethane-air 0.4
Butane-air 0.34
Acetylene-air 0.03
CO-air 0.05
Hydrogen-air 0.02
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Module 5: Premixed Flame Lecture 26: Flammability Limits
Flame Stabilization
Local gas flow velocity = Local burning velocity
(Figure 26.4)
(Figure 26.5)
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Module 5: Premixed Flame Lecture 26: Flammability Limits
Flame Stabilization by Burner Rim
(Figure 26.6)
Stability of flame front near the rim of Bunsen burner
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Module 5: Premixed Flame Lecture 26: Flammability Limits
Turbulent Premixed Flame
(Figure 26.7)
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Module 5: Premixed Flame Lecture 27: Flame Stabilization
The Lecture Contains:
Turbulent Flame Regimes
The Borghi Diagram
Turbulent Burning Velocity
Wrinkled Laminar Flame
Distributed Reaction
Flamelet in Eddies
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Module 5: Premixed Flame Lecture 27: Flame Stabilization
Turbulent Flame Regimes
Turbulent Flame Regimes
Reynolds number for turbulent flame: Chemical reaction time:
Chemical reaction time: Damkohler number
If Da >> 1, fast chemistry regime
If Da <<1, fast mixing regime
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Module 5: Premixed Flame Lecture 27: Flame Stabilization
The Borghi Diagram
Borghi Diagram
The plot of Da against on a log-log scaleDepicts various regimes of turbulentflames
(Figure 27.1)
Weak turbulent flameUpper region of the Borghi diagram
Wrinkled laminar flameRegion between and Chemical reaction takes place in athin zone
Flamelets in eddiesRegion between upper bold line
and
Distributed reaction regimeRegion below Reaction sheets are distributed in theturbulent flame surface This type of combustion can beestablished in a well stirred reactor.
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Module 5: Premixed Flame Lecture 27: Flame Stabilization
Turbulent Burning Velocity
How to measure (ST) ? From the reactant flow rate
Turbulent Burning Velocity
is the reactant flow rate
is the time average flame surface area
is the density of unburnt gas
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Module 5: Premixed Flame Lecture 27: Flame Stabilization
Wrinkled Laminar Flame
Turbulent burning velocity is given by, (Figure 27.2)
According to Damkohler, for constant laminarburning velocity According to Klimov,
Similarly for turbulent flame, According to Calvin and William,
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Module 5: Premixed Flame Lecture 27: Flame Stabilization
Distributed Reaction
(Figure 27.3)Turbulent burning velocity is given by,
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Module 5: Premixed Flame Lecture 27: Flame Stabilization
Flamelet in Eddies
(Figure 27.4)
Fuel mass burning rate,
Typically, is root mean square offluctuating fuel mass fraction, is the turbulentkinetic energy per unit.
References
1. D. P. Mishra, Fundamentals of Combustion, PHI leaming, Pvt Ltd., New Delhi, 2010.2. Stephen R. Turns, An Introduction to Combustion, McGraw Hill Publication, Singapore, 1996.3. Irvin Glassman, Combustion, Academic Press, New York, 1977.
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Module 6: Diffusion Flame Lecture 29: Theoretical Analysis
The Lecture Contains:
Theoretical Analysis
Theoretical Analysis (Contd.)
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Module 6: Diffusion Flame Lecture 29: Theoretical Analysis
Theoretical Analysis
Consider a 2D diffusion flame,
(Figure 29.1)Assumptions:
i. 2D steady laminar inviscid flow.ii. Velocity above the channel is constant everywhere iii. Fuel and oxidizer react in stoichiometric proportion at the flame surface with infinite reaction
rate (Thin flame approximation).iv. Binary diffusion between participating species.v. Mass diffusion is along x-direction only.vi. Unity Lewis number.vii. Single step irreversible reaction.viii. Radiation heat transfer is negligibly small.ix. Constant thermophysical properties.x. Mass diffusivity of both fuel and oxidizer are the same.xi. Buoyancy force is neglected.
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Module 6: Diffusion Flame Lecture 29: Theoretical Analysis
Theoretical Analysis (Contd.)
Conservation equations:Mass conservation:
Using assumption (ii), we can have,
Axial momentum conservation:
Species conservation equation:
Mass fraction of the product can be found from
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Module 6: Diffusion Flame Lecture 29: Theoretical Analysis
Theoretical Analysis (Contd.)
By thin flame approximation,
Single step irreversible reaction,
Universal concentration variables,
Rate of fuel transport from the centre to the flame surface is equal to stoichiometric rate of oxidizertransport.
Let be the mass fraction of the reactant, Instead of solving two equations (For fuel and oxidizer), we can solve a single equation as givenbelow,
This analysis is known as the Burke-Schumann's analysis
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Module 6: Diffusion Flame Lecture 29: Theoretical Analysis
Theoretical Analysis (Contd.)
Above equation can be converted into a diffusion equation by substituting
Inner wall exists at and outer wall at The initial and boundary conditions are as follows.
Applying boundary conditions, we obtain a closed form series solution
where, is the non-dimensional mass fraction of the reactant.
The infinite series must have a constant value at the flame surface as given below
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Module 6: Diffusion Flame Lecture 29: Theoretical Analysis
Theoretical Analysis (Contd.)
The series solution depends on and At the burner rim, the series constant (E) becomes a square wave
When F/A ratio is stoichiometric E becomes zero.
Roper extended the Burke-Schumann model by varying thevelocity to vary along the axial direction.
The flame height is given by,
(Figure 29.2)
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Module 6: Diffusion Flame Lecture 30: Mechanism of Soot Formation
The Lecture Contains:
Mechanism of Soot Formation
Liquid Fuel Combustion
Processes during droplet combustion
Liquid Fuel Combustion (Contd.)
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Module 6: Diffusion Flame Lecture 30: Mechanism of Soot Formation
Mechanism of Soot Formation
Process of soot formation:
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Module 6: Diffusion Flame Lecture 30: Mechanism of Soot Formation
Mechanism of Soot Formation
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Module 6: Diffusion Flame Lecture 30: Mechanism of Soot Formation
Liquid Fuel Combustion
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Module 6: Diffusion Flame Lecture 30: Mechanism of Soot Formation
Processes during droplet combustion
(Figure 30.1)
Factors affecting the shape of the flame front:
Condition under which combustion takes place!
Zero gravity : Spherical flame front (No buoyancy)
Normal gravity : Elongated (Due to natural convection)
Forced convection condition : Fame aligned with flow
Energy required to vaporize the liquid fuel:
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Module 6: Diffusion Flame Lecture 30: Mechanism of Soot Formation
Liquid Fuel Combustion (Contd.)
Assumptions 1. Single droplet in quiescent
atmosphere.2. Droplet temperature is uniform.3. Density of liquid fuel much
higher than the gas phase.4. Fuel is a single component with
no solubility for gases.5. Flow velocities are assumed to
be low6. Single step irreversible
reaction! Thin flameapproximation.
7. Constant thermo-physicalproperties.
8. Unity Lewis number.9. Radiation heat transfer is
neglected.10. No other phase is formed in
the liquid fuel droplet.
(Figure 30.2)
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Module 6: Diffusion Flame Lecture 31: Overall mass conservation
The Lecture Contains:
Overall mass conservation
Liquid Fuel Combustion (Contd.)
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Module 6: Diffusion Flame Lecture 31: Overall mass conservation
Overall mass conservation:
-----(1)
for all r V - bulk velocity; -gas density
Momentum conservation:
Species conservation:
-----(2)
-----(3)
Single step reaction:-----(4)
T - Temperature; - energy release rate due to chemical reaction
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Module 6: Diffusion Flame Lecture 31: Overall mass conservation
Liquid Fuel Combustion (Contd.)
Fuel, oxidizer and product can be related to heat release rate as follows
-----(5)
Rearranging,
-----(6)
We can rewrite fuel species conservation equation as,
-----( 7)
Multiply eq.7 by and add by eq.3,
-----( 8)
Here a is the thermal diffusivity
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Module 6: Diffusion Flame Lecture 31: Overall mass conservation
Liquid Fuel Combustion (Contd.)
Using eq.6, eq.8 becomes,
-----(9)
Elimination of the non-linear term simplifies the analysis. This simplification is known asSchwab- Zeldovich Transformation.
Dividing eq.9 by ,
-----(10)
– Heat input required for vaporization of droplet
– Mass fraction of species at the surface of the droplet
Conserved variable for oxidizer
`
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Module 6: Diffusion Flame Lecture 31: Overall mass conservation
Liquid Fuel Combustion (Contd.)
General format of all the equations
-----(11)
Boundary conditions
;
Integrating eq.11 twice and applying the boundary conditions,
-----(12)
By applying boundary condition to Eq. 12, We can have,
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Module 6: Diffusion Flame Lecture 31: Overall mass conservation
Liquid Fuel Combustion (Contd.)
The transfer number, B is given by
Values of transfer number, B for some typical fuel:
Combustion in air B Combustion in air BISO-Octane 6.41 Kerosene 3.4
Benzene 5.97 Gas oil 2.5
n-Heptane 5.82 Light fuel oil 2.0
Avation gasoline 5.5 Heavy fuel oil 1.7
Automobile gasoline 5.3
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Module 6: Diffusion Flame Lecture 32: The Temperature Profile
The Lecture Contains:
The Temperature Profile
Droplet Burning Time
Droplet Combustion in Convective Environment
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Module 6: Diffusion Flame Lecture 32: The Temperature Profile The Temperature Profile
No oxygen exists in the inner flame region.No fuel exists in the outer region of flame.Using the transfer function for fuel andoxidizer,
Temperature profile for the inner region,
(Figure 32.1)Rearranging the above equation,
Temperature profile for the outer region,
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Module 6: Diffusion Flame Lecture 32: The Temperature Profile
Droplet Burning Time
Importance of droplet burning time:Essential for desining combustion chamberFor complete combustion, residence time > life timeof largest droplet in spray.
Factors dictating residence time of droplet:
Air stream velocityDroplet velocityFuel injection angleCombustor geometry
Continuity equation at the surface of the droplet: (Figure 32.2)
-------(1)
Droplet mass is evaluated as follows, -------(2) Where, D is the droplet diameter at any instant
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Module 6: Diffusion Flame Lecture 32: The Temperature Profile
Droplet Burning Time (Contd.)
Recall, Burning constant for typical hydrocarbons
-------(3) Fuel k 10-7 m2/s
(Calculated)k 10-7 m2/s(Measured)
Ethyl alcohol 9.3 8.1
N-Heptane 14.2 9.7
ISO-Octane 14.4 9.5
Kerosene 9.7 9.6
Benzene 11.2 9.7
Toluene 11.1 6.6
Using (1) & (2) in (3),
-------(4)
Expressing droplet diameter interms of ,
-------(5)
In this expression, varies linearly with time (See figure 32.3). Slope of the plot is the burning rateconstant, K
-------(6)
Integrating (5) with time, is law
(Figure 32.3)
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Module 6: Diffusion Flame Lecture 32: The Temperature Profile
Droplet Combustion in Convective Environment
In practical devices, both free and forced convection will prevail,
Flow past the fuel droplet for Re > 20
Front portion of the droplet – Boundary layer.Rear portion – Wake region
In practical devices, forced convection is more predominant
Boundary condition at the droplet surface,
-------(1)
Where,
-------(2)
- Convective heat transfer coefficient Combining the above two expressions,
-------(3)
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Module 6: Diffusion Flame Lecture 32: The Temperature Profile
Droplet Combustion in Convective Environment
Rearranging the above equation,
-------(4)
-------(5)
For high Reynolds number,
-------(6)
For unit Prandtl number, Re >> Pr,
-------(7)
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Module 6: Diffusion Flame Lecture 32: The Temperature Profile
Droplet Combustion in Convective Environment
-------(8)
Then Eq. (7) becomes,
The above expression would not provide accurate predictionWake region behind the droplet is not considered here.For predicting the experimental data, the above expression is modified as,
-------(9)
Under convective condition, laminar droplet burning rate follows
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Module 6: Diffusion Flame Lecture 33: Spray Combustion Model
The Lecture Contains:
Spray Combustion Model
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Module 6: Diffusion Flame Lecture 33: Spray Combustion Model
Spray Combustion Model
Assumption:
Steady, 1-D flow, Laminar, inviscidMono-dispersed droplets.Pressure remains constant duringcombustion.Droplets move with same velocityas that of air.Vaporization and ignition begins atx=0.Mixing and chemical reaction timesare quite small as compared todroplet vaporization time.Constant thermophysicalproperties.Dilute spray.
(Figure 33.1)
Stoichiometric fuel-air ratio:
-------(1) =Density of liquid
= Cross sectional area
= Number of droplets = Initial diameter
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Module 6: Diffusion Flame Lecture 33: Spray Combustion Model
Spray Combustion Model
Number of droplets,
-------(2)
From mass conservation,
-------(3)
- Density of droplet laden air
-------(4)
From above two equations,
-------(5)
Energy equation across the element dx
-------(6)
- Heat release rate
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Module 6: Diffusion Flame Lecture 33: Spray Combustion Model
Spray Combustion Model
Simplifying,
-------(7)
Heat release rate per unit volume,
-------(8)
Relationship for quasi-steady state droplet vaporization,
-------(9)
Where, K – droplet combustion rate constant that can be experienced as
-------(10)
By using Eqs. (7) , and (10), we can have,
-------(11)
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Module 6: Diffusion Flame Lecture 33: Spray Combustion Model
Spray Combustion Model
Droplet diameter will vary by law
-------(12)
Boundary and initial conditions
-------(13)
By using above condition in Eq. 6.11 and integrating it, we can get
-------(14)
Adiabatic flame temperature is given as
-------(15)
By using Eng. (14), we get
-------(16)
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Module 6: Diffusion Flame Lecture 33: Spray Combustion Model
Spray Combustion Model
Zone length is given by
-------(17)
Integrating Eq. (17), we can get
-------(18)
Combustion Intensity is given by
-------(19)
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Module 6: Diffusion Flame Lecture 34: Solid Fuel Combustion
The Lecture Contains:
Solid Fuel Combustion
Theory For Single Coal Combustion
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Module 6: Diffusion Flame Lecture 34: Solid Fuel Combustion
Solid Fuel Combustion
Factors influencing solid fuel burning
Nature of the solid fuelType of application
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Module 6: Diffusion Flame Lecture 34: Solid Fuel Combustion Solid Fuel Combustion
(Figure 34.1) (Figure 34.2)
(Figure 34.3)
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Module 6: Diffusion Flame Lecture 34: Solid Fuel Combustion
Solid Fuel Combustion
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Module 6: Diffusion Flame Lecture 34: Solid Fuel Combustion
Theory For Single Coal Combustion
1. Burning process is quasi steady.2. Burning takes place in quiescent, infinite ambient air medium.3. No interaction with other particles.4. Effect of natural convection is ignored.5. Burning is diffusion controlled.6. Constant thermodynamic properties7. Unity Lewis number8. Gaseous species do not enter into gaseous species9. No radiation heat transfer
10. Ideal gas law
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Module 6: Diffusion Flame Lecture 34: Solid Fuel Combustion
Theory For Single Coal Combustion
Mass conservation
--------(1)
Oxidizer species conservation
--------(2)
Energy conservation
--------(3)
Stoichiometric fuel-air ratio
--------(4)
Boundary Conditions:
--------(5)
--------(6)
Combining Eq. 4 and 6,
--------(7)
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Module 6: Diffusion Flame Lecture 34: Solid Fuel Combustion
Theory For Single Coal Combustion
Integrating Eq. 2 and applying b.c.,
--------(8)
Integrating the above equation further,
--------(9)
Applying the boundary condition,
--------(10)
increases exponentially with the increase in radius
at the solid surface
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Module 6: Diffusion Flame Lecture 34: Solid Fuel Combustion
Theory For Single Coal Combustion
At moderate temperature and for small particle, the oxygen mass fraction at the surface is given by
--------(11)
B is the mass transfer number
--------(12)
The carbon sphere burning rate is also governed by Law
where is the carbon burning constant.
Table: Combustion properties of slid spheres [7]
Fuel (g/cm3) MWfuel B.Pfuel (ºC) f Boxygen Bair
Aluminium 2.70 27.0 2.467 1.12 1.12 0.26
Boron 2.34 10.8 2.550 0.451 0.451 0.105
Carbon 1.50 12.0 4.827 0.75 0.750 0.174
Carbon 1.50 12.0 4.827 0.375 0.375 0.087
Magnesium 1.74 24.3 1.107 1.107 1.520 0.353
Zirconium 6.44 91.2 3.578 3.578 2.850 0.662
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You can question everything around you,
You may find tangible answers to few,
You can question everything around me,
The answers, I posses are not necessarily mine. - Dr. D.P. Mishra
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Module 7: Combustion and Environment Lecture 35: Introduction
The Lecture Contains:
Introduction
Air Pollution Sources
Effect of CO Exposure on Human Health[1]
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Module 7: Combustion and Environment Lecture 35: Introduction
Combustion and Environment
Introduction
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Module 7: Combustion and Environment Lecture 35: Introduction
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Module 7: Combustion and Environment Lecture 35: Introduction
Major Health Ailments Due to Environmental pollution
(Figure 35.1)
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Module 7: Combustion and Environment Lecture 35: Introduction
Air Pollution Sources
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Module 7: Combustion and Environment Lecture 35: Introduction
Effect of CO Exposure on Human Health [1]
Source [1] D.P. Mishra Fundamental of Combustion, PHI Learning Rt Ltd., New Delhi, 2008
(Figure 35.2)
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Module 7: Combustion and Environment Lecture 36: Atmosphere
The Lecture Contains:
Atmosphere
Chemical Emission From Combustion
Chemicals From Combustion (Contd..)
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Module 7: Combustion and Environment Lecture 36: Atmosphere
Atmosphere
Figure 1: Variation of temperature with altitude
(Figure 35.3)
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Module 7: Combustion and Environment Lecture 36: Atmosphere Atmosphere
Source: http://www.theresilientearth.com/files/images/stratosphere_diagram.jpg
(Figure 36.1)
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Module 7: Combustion and Environment Lecture 36: Atmosphere
Atmosphere (Contd..)
TroposphereRegion where we are living.Contains 90% of the mass of the atmosphere.Starts at ground level with 228 K and ends at 18 km (200 K) with 6 K drop in temperature perkm altitude.Beyond 18 km, temperature rises. This inflection point is called “Tropopause”.Tropopause divides troposphere from stratosphere.Atmospheric boundary layer - 2 km from the ground level.Combustion byproducts instantly affects this region.
Photochemical chain reaction begin with dissociation of ozone as given below
--------(1)
The atomic oxygen reacts with water vapor to form hydroxyl radical
--------(2)
The OH radical reacts with CO and initiates other chain reactions as below
--------(3)
--------(4)
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Module 7: Combustion and Environment Lecture 36: Atmosphere
Atmosphere (Contd..)
The peroxy radicals are recycled to OH by the following reaction:
----------(5)
Cycling of OH and is turned off by several reactions involving OH, and ----------(6)
NO and pair is produced via the following chain reactions.
----------(7)
----------(8)
----------(9)
--------(10)
Concentration of ozone and can also be influenced by non-photolytic reactions during nighttime.
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Module 7: Combustion and Environment Lecture 36: Atmosphere
Atmosphere (Contd..)
StratosphereRegion between tropopause (18 km) and stratopause (50 km).Contains 9.5% of atmospheric mass.The temperature increases from tropopause (220 K) to stratopause (280 K).The chemicals from troposphere that are not destroyed are dissociated in this region.CFC is converted into HF and mixture of CI compounds.The photochemistry in the stratosphere is strongly affected by ozone layer.The short wavelength cannot reach below 25 km due to the photochemistry.This is how we are protected from the harmful UV rays.Stratospheric column is the major absorber of solar UV between 220 and 320 nm.Depletion of ozone layer will change the tropospheric chemistry in two ways
i. Lowers the flux of into troposphereii. Enhances the production of OH
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Module 7: Combustion and Environment Lecture 36: Atmosphere
Chemical Emission From Combustion
Most of the fossil fuels can be depicted by the following chemical equation
Fuels contain sulphur , oxygen, nitrogen and certain heavy metals.Air contains large amount of nitrogen.Combustion process leads to the formation of The quantities are sufficient enough to affect the quality of atmospheric air.Total amount of fossil fuel burnt was around 6.2 Gt/Yr.Another source of pollutant emission from combustion process is the biomass.Total amount of biomass fuel burnt was around 3 to 5 Gt/Yr.The combustion conditions for biomass combustion leads to higher emissions.
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Module 7: Combustion and Environment Lecture 36: Atmosphere
Chemicals From Combustion (Contd..)
Emission of
It has been observed that there is an imbalance in the atmospheric carbon-oxygen cycle.CO is released directly into the atmosphere by incomplete combustion.About 40% of CO in the atmosphere is contributed by the burning of fossil fuel.CO level in southern hemisphere in around 50 ppb and in northern hemisphere it is 120 ppb.Is the major portions CO produced form combustion?NO! from the oxidation of methane generated by anaerobic bacteria in swamps and paddies.
Why there is a climate change?
Due to the change in CO2 level.
Deforestation in recent days is the main cause for the accumulation of CO2 in the biosphere.
Changes in land used by human beings contribute around 1 Gt(C)/yr CO2 to atmosphere.
Global carbon cycle involves exchange of atmospheric CO2 with carbon reservoir in ocean
and biosphere in several time scales.It has been predicted that the freezing of current emissions would not really solve our problemimmediately.CO2 emission does not impact atmospheric chemistry directly but changes the temperature
and circulation, which indirectly changes the chemistry and climate.
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Module 7: Combustion and Environment Lecture 37: Major Sources of CO Emission
The Lecture Contains:
Major Sources of CO Emission
Chemicals From Combustion
Major Sources of NO Emission
Chemicals From Combustion (Contd..)
Quantification of Emission
Species Emission and Its Corrected Value
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Module 7: Combustion and Environment Lecture 37: Major Sources of CO Emission
Major Sources of CO Emission
Source category Emissions (Millions tons per year) %Gasoline motor vehicles 95.8 36.69
Diesel, aircraft, trains, vessels 5.6 2.14
Off-highway vehicles 9.5 3.64
Coal 0.5 0.19
Fuel oil 0.1 0.038
Natural gas 0.1 0.038
Wood 0.1 0.038
Total stationary sources 0.8 0.30
Total fuel combustion 111.7 42.78
Industrial processes 11.4 4.36
Agricultural burning 13.8 5.28
Solid waste disposal 7.2 2.75
Miscellaneous 4.5 1.72
Total 261.1 100.0
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Module 7: Combustion and Environment Lecture 37: Major Sources of CO Emission
Chemicals From Combustion
Emission of
NO and are main components producing in troposphere.
The life of these gases are quite short even less than 1 day.
Combustion of fossil fuel is the largest source of .
The quantities are sufficient enough to affect the quality of atmospheric air.
Combustion of fossil fuel is the largest source of around 22 Mt/yr.
Stationary source contribution is around 13 Mt/yr.
Contribution of emission by biomass is quite small.
Due to combustion, there is a four fold increase in the tropospheric .
The major sources of emission and their contributions are depicted in the next section.
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Module 7: Combustion and Environment Lecture 37: Major Sources of CO Emission
Major Sources of NO Emission
Source category Emissions (Millions tons per year) %Gasoline motor vehicles 7.8 17.53
Diesel, Aircraft , trains, ships 2.0 4.49
Off-highway vehicles 1.9 4.27
Coal 3.9 8.76
Fuel oil 1.3 2.92
Natural gas 4.7 10.56
Wood 0.1 0.22
Total fuel combustion 21.7 48.76
Industrial processes 0.2 0.45
Agricultural burning 0.3 0.67
Solid waste disposal 0.4 0.90
Miscellaneous 0.2 0.45
Total 44.5 100
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Module 7: Combustion and Environment Lecture 37: Major Sources of CO Emission
Chemicals From Combustion (Contd..)
Emission of Hydrocarbon
Non-methane hydrocarbons (NMHC) are short lived and highly reactive.Oxidization of these hydrocarbons leads to the formation of .Volatile organic compounds include NMHC as well as oxygenated species such as aldehydesand alcohols.These are mainly contributed by gasoline vehicles, solvent evaporation and biomass burning.These bio-organic hydrocarbons are quite reactive and are usually destroyed within theboundary layer.
Emission of Sulphur Dioxide and Sulphate AerosolsSulphur content of fossil fuels such as coal and oil is in the range of 0.5 – 2.5 by mass.Sulphur in the fossil fuel is usually emitted as and leads to the formation of sulphuricacid.
takes very less time to get converted into sulphate to wet or dry deposition on the earthsurface.Combustion of fossil fuels contributes significant amount of in troposphere, which is about80 Mt/yr.
Source SO2 (Million tons per year)
Fossil fuel 80
Metal smelting 8
Biomass burning 2
Natural sources (Ocean, oil, vegetables) 25
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Module 7: Combustion and Environment Lecture 37: Major Sources of CO Emission
Quantification of Emission
Emission levels are reported in several different ways while dealing with different devices.Gas turbine combustors: ppm by volume at 15% O2
Furnace: ppm at 3% O2
Automobiles: g/kmBoiler: g/kW
Species emission and its corrected valueGenerally combustion system is characterized in terms of level of emissions.Confusion prevails due to the change in sampling condition
Degree of dilutionDry or wet condition
If the moisture is removed from the exhaust sample then it will yield dry concentration.In some situations, it may not be possible to remove moistures, then it is known as wetconcentration.
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Module 7: Combustion and Environment Lecture 37: Major Sources of CO Emission
Species Emission and Its Corrected Value
Consider a hydrocarbon fuel-air mixture at lean or stoichiometric condition
Wet mole fraction of species is defined as
Dry mole fraction of species is defined as
Carrying out an atom balance for O atom,
Ratio of total number of moles in wet mixture to dry mixture is
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Module 7: Combustion and Environment Lecture 38: Species Emission and Its Corrected Value
The Lecture Contains:
Species Emission and Its Corrected Value
Emission Control Methods
SOx Emission and Its Control
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Module 7: Combustion and Environment Lecture 38: Species Emission and Its Corrected Value
Species Emission and Its Corrected Value
The oxygen coefficient is given by
OR
The measured concentration of species at given oxygen level can be corrected to a specificoxygen level as below
In order to assess the emission in a combustor or engine, it is important to define a normalizedindicator of emission level as below,
For combustion of hydrocarbon fuel, the emission index species is given by,
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Module 7: Combustion and Environment Lecture 38: Species Emission and Its Corrected Value
Emission Control Methods
Best method of reducing emission is to avoid using excess fuel.Public awareness must be initiated to avoid unwanted burning of fuels.Eco-friendly combustion devices have to be designed and developed.Cost effective methods can be devised to treat the combustion products before allowing themto the atmosphere.
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Module 7: Combustion and Environment Lecture 38: Species Emission and Its Corrected Value
Emission Control Methods
COx Emission control
Storage in oceans may not be feasible due to non-availability of technology, however, geologicalreservoirs are promising options for CO2 storage.
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Module 7: Combustion and Environment Lecture 38: Species Emission and Its Corrected Value
Emission Control Methods
Figure: Schematic diagram of a CO2 capture pilot plant for coal-based power plant
(Figure 38.1)CO2 is separated by means of absorption using mono-ethanol amine (MEA).
The plant consists of three partsi. Absorber,ii. Regenerator,iii. Exchanger.
Exhaust gas is cooled to to 40-50°C and fed to the absorption tower.In the absorber, exhaust gas is mixed with mono-ethanol amine (MEA), which captures 90%of CO2 in the exhaust gas.
Amine stripper is used in the regenerator, which separates MEA and sends back to amineabsorption tower. This plant captures 1 million CO2 per hour.
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Module 7: Combustion and Environment Lecture 38: Species Emission and Its Corrected Value
SOx Emission and Its Control
Sulphur is relatively inert and harmless to human beings.Oxides of sulphur poses serious environmental problem.Sulphur oxides are corrosive in nature.Organic fuels such as coal, oil, wood, etc contain some sulphur.SO is a highly reactive radical and its life time is few milliseconds.Under fuel rich conditions, in addition to sulphur oxides, hydrogen sulphide, carbonyl sulphide,and elemental sulphur are formed.Understanding of the mechanism of sulphur oxides have not evolved to a maturity level.
(Figure 38.2)
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Module 7: Combustion and Environment Lecture 38: Species Emission and Its Corrected Value
SOx Emission and Its Control
Hydrosulphurization methodEffective method of desulphurizing coal and oil fuels.This method treats fuels in the presence of hydrogen at high pressure and temperature.Finely grounded coal is mixed with anthracene oil along with hydrogen to produce slurry.The dissolved coal is passed through a pressure filtration unit in which pyretic sulphur isremoved.A flash evaporator is used to convert the dissolved coal to low sulphur coal.
(Figure 38.3)
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Module 7: Combustion and Environment Lecture 39: Emission and Its Control
The Lecture Contains:
SOx Emission and Its Control
Forced Oxidation Limestone Wet Scrubber
Zeldovich Mechanism
Fenimore (Prompt) Mechanism
Fuel (N2O – Intermediate) Mechanism
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Module 7: Combustion and Environment Lecture 39: Emission and Its Control
SOx Emission and Its Control
Gasification methodSulphur dioxide emission due to burning of coal or fuel oil can be minimized by gasifyingthem.During gasification, coal undergoes partial oxidation resulting in CO and .
Sometimes, and other gases can also be produced during gasification of coal.In this case, sulphur content gets converted into hydrogen sulphide , which can be removedby absorption or adsorption method..In absorption method, gases are scrubbed with alkaline reagent such as sodium carbonate orethylamine.Subsequently elemental sulphur is produced.In adsorption method, ferric oxide is used to adsorb hydrogen sulphide using fluidized bedaround 400°C.
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Module 7: Combustion and Environment Lecture 39: Emission and Its Control
Forced Oxidation Limestone Wet Scrubber
(Figure 39.1)
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Module 7: Combustion and Environment Lecture 39: Emission and Its Control
NOx Emission and Its Control
Nitrogen in atmosphere forms 8 different oxides during combustion.The important oxides are NO, .Is NO harmful to health than ?
is more harmful as compared to NO. By what reaction NO and are formed ?
For any chemical reaction, Gibbs free energy attains a minimum value for a particulartemperature and pressure
Equilibrium constant
Standard Gibbs free energy change
Table: Equilibrium concentration of NO and NO2
300 7 X 10-31 1.4 X 106 3.4 X 10-10 2 X 10-4
500 2.7 X 10-18 130 7 X 10-4 0.04
1000 7.5 X 10-9 0.11 35 1.9
1500 1.07 X 10-5 0.011 1320 6.8
2000 0.0004 0.0035 8100 13.2
2500 0.0035 0.0018 24000 20.0
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Module 7: Combustion and Environment Lecture 39: Emission and Its Control
Zeldovich Mechanism
From the above table it is clear that emission can be reduced by decreasing thetemperature.
(Figure 39.2)Thermal are formed by simple heating of oxygen and nitrogen.The radical ‘N' can react with to form NO.Thermal NO contribution is low till 1300 K and beyond which it increases rapidly.The thermal mechanism consists of the following two chain reactions.
--------(1)
--------(2)
--------(3)
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--------(6) --------(8)
--------(7) --------(9)
Module 7: Combustion and Environment Lecture 39: Emission and Its Control
Fenimore (Prompt) Mechanism
Prompt mechanism refers to the which are formed very quickly by interaction of activehydrocarbon species derived from fuel with nitrogen and oxygen.They are generally not observed in flames of non-hydrocarbon flames.They cannot be formed by just heating nitrogen with oxygen.During initial phase of combustion, the radials with carbon atom react with to produce N.
--------(4)
This reaction is the main path which dictates the rate at which radical ‘N' is formed.The radical ‘N' can also be formed by the following reaction.
--------(5)
When the equivalence ratio is less than 1.2, HCN can be converted to NO as follows,
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Module 7: Combustion and Environment Lecture 39: Emission and Its Control
Fuel (N2O – Intermediate) Mechanism
Thermal NOis quitesmall below
1300oCThermal NOrises sharplywithtemperatureBoth fuel NO& promptNO do notvary withtemperatureBut promptNOincreasesmarginallywithtemperature.
N2O intermediate
mechanism plays a veryimportant role for NOcontrol in lean premixedcombustion.
Three steps of N2O
intermediate mechanismare given below;
(Figure 39.3)
Several techniques are devised to control in combustion as described in next section.
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Module 7: Combustion and Environment Lecture 40: Combustion Modification Methods
The Lecture Contains:
NOx Control Technologies
Combustion Modification Methods
Particulate Controls
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Module 7: Combustion and Environment Lecture 40: Combustion Modification Methods
NOx Control Technologies
(Figure 40.1)
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Module 7: Combustion and Environment Lecture 40: Combustion Modification Methods
NOx Control Technologies
(Figure 40.2)
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Module 7: Combustion and Environment Lecture 40: Combustion Modification Methods
Combustion Modification Methods
Low excess air
(Figure 40.3)Proper comprise between combustion efficiency, CO and emissions have to be arrived beforedeciding the excess air.
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Module 7: Combustion and Environment Lecture 40: Combustion Modification Methods
Combustion Modification Methods
Staged Combustion
(Figure 40.4)Most effective method to control formation.Upstream burner operates in fuel rich mode.Additional air is added in the downstream for burning of fuel in stages.
emissions can be reduced by 10 to 40%.
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Module 7: Combustion and Environment Lecture 40: Combustion Modification Methods
Combustion Modification Methods
Flame CoolingThermal NO can be controlled by reducing the temperature.
These three methods reduce the peak temperatures.May lead to the formation of CO.10 to 15% reduction in NO can be achieved by these methods
(Figure 40.5)
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Module 7: Combustion and Environment Lecture 40: Combustion Modification Methods
Particulate Controls
Cyclone and hydro-cyclone separators are also employed to remove particulates.