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Power plant Engineering Session 11 Questions from class? Review of HW7 Papers due today – delay 1 pt per day. Final next week – HW5, 6, and 7 Text book, chapters 4 & 5. PPE Lecture 11 Tom Blair, P.E. 1

Power plant Engineering Session 11

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Power plant Engineering Session 11. Questions from class? Review of HW7 Papers due today – delay 1 pt per day. Final next week – HW5, 6, and 7 Text book, chapters 4 & 5. PPE Lecture 11 Tom Blair, P.E. 1. Plant Environmental Control Systems. - PowerPoint PPT Presentation

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Page 1: Power plant Engineering Session 11

Power plant Engineering Session 11

Questions from class?Review of HW7Papers due today – delay 1 pt per day.Final next week – HW5, 6, and 7Text book, chapters 4 & 5.

PPE Lecture 11 Tom Blair, P.E. 1

Page 2: Power plant Engineering Session 11

Plant Environmental Control Systems

PPE Lecture 11 Tom Blair, P.E. 2

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Plant Environmental Control Systems

Proportional Control

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Integral (reset) control

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Derivative control

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Feedfoward (FT) and feedback (TT)

Feedfoward signal summed with output of controller

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Cascade control – 2 single element controllers in series (one FB (primary control) and one FB (secondary control) in this example)

Note both TT and FT function of valve. – No Feed forward here.

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Feedfoward & cascade

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Power plant Environmental ControlsAll emissions – water, air, solid wasteThis presentation on atmospheric emission controlParticulate Emission ControlNitrogen Oxides Emission ControlSulfur Dioxide Emission ControlCombination NOX SO2 removalHazardous Air Pollutant controlContinuous Emissions Monitoring

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Particulate Emission Control –Bottom ash – bottom of boilerEconomizer ash removed after economizer

smallerFly Ash – removed at electrostatic precipitator or

fabric filter

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Electrostatic Precipitator – TR set – HV DC between HV electrode and grounded plate

Particles collect on plates – rappers mechanically vibrate plate and remove particles

Precipitator cross section large to reduce velocityIncreases treatment time.TR set 25kV to 125kVRapping Systems – hammers, vibrators, dropped

weights

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Resistivity = measure of how easily the ask acquires electric charge

Varies with Moisture, SO3, chemical composition, temperature.

For low sulfur coal, add SO3 to reduce resistivity.Weighted wire or pipes as electrodes

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Fabric FiltersFilter media sewn into cylindrical tubes (bags)Reverse gas fabric filter or pulse jet cleaning type.

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Reverse Gas Fabric FilterOperatingCycle

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CleaningCycle

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Pulse Jet Fabric FilterTolerates higher velocityCleaned more thoroughlySmaller footprint for same air flow

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Pulse JetFabricFilterFiltering

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OnlineCleaningCycle

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OfflineCleaningCycle

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Isolated for Maintenance

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Alternate Particulate Control TechnologiesCyclone Collectors – Uses centrifugal force to

separate fly ashWet Venturi Scrubber – Use liquid to capture fly

ash. Flue gas velocity accelerates in venturi where water droplets are used to collect ash.

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Cyclone Separator

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Nitrogen Oxides Emissions Control90% NO, 10% NO2Nitrogen in air (thermal NOx) 25%Nitrogen in fuel (fuel NOx) 75%Low temperature (thermal NOx formation)Control Fuel / Air ratio (fuel NOx formation)Combustion control and/or post combustion

control

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Combustion Control

Reduce temperatureReduce Oxygen concentrationReduce reaction time in Oxygen rich, high temp

conditionLow NOx burners – 2 separate registers 2 air

paths

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Internal FuelStagedLow NOxBurner

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Low NOx burnerA – High Temperature fuel rich devolatilization zoneB – Production of reducing species zoneC – NOx decomposition zoneD – Char oxidizing zone

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Corner Fired SystemLNCFS – Low NOx Concentric Firing System

(retrofits)PM – pollution minimum system (new)LNCFS – auxiliary air directed at 25O of air/coal

stream thereby reducing air in fuel streamOFA – overfired air provides vertical air staging

over furnace height.PM splits fuel and air stream into two, one fuel

rich, one fuel lean.

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LNCFS (Auxiliary air)

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CT NOx controlReduction of flame temperature usingSteamWaterN2Premixing of fuel/air upstream of combustion

zone

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Post combustion Control – Selective Catalytic Reduction Systems (SCR)

Ammonia and NO react in presence of catalyst to form N2 and H2O

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Desired SCR Reactions (exothermic) as Ammonia and NOX flow over catalyst

4NO + 4NH3 + O2 –(catalyst) 4N2 + 6H2O + heat

2NO2 + 4NH3 + O2 –(catalyst) 3N2 + 6H2O + heat

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Undesirable SCR Reactions (exothermic) as Ammonia and NOX flow over catalyst

2SO2 + O2 2SO3 (SO2 oxidation)

2NH3 + SO3 + H2O NH4HSO4 (ammonium bisulfate formation)

2NH3 + 2SO3 + H2O + 0.5O2 2NH4HSO4 (ammonium sulfate formation)

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SO2 oxidation increased above 700oF, so SCR temps typically held 650oF to 700oF

No less than 570oF to minimize formation of ammonia salts

For non sulfur fuel, max temp 780oF (vanadium/titanium catalyst)

Ammonium sulfate and bisulfate are salts and can deposit on surfaces downstream.

Ammonia slip may effect reuse of fly ash collected.

Anhydrous ammonia – 100% NH3

Aqueous – 25% NH3, 75% H2OPPE Lecture 11 Tom Blair, P.E. 37

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SCR ArrangementHigh Dust – Catalyst located at the outlet of the

economizer and upstream of the air heaterLow Dust – Catalyst located at the outlet of the hot

side ESP and upstream of the air heaterTail End – Catalyst located at the outlet of

particulate removal and FGD system and upstream of stack.

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High Dust – SCR Arrangement

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Low Dust – SCR Arrangement

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Tail End – SCR Arrangement

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Catalyst poisoned by alkali metals such as: Arsenic Lead Beryllium ManganeseCadmium Mercury Calcium NickelChromium Thorium Copper Uranium

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Post combustion Control – Selective NonCatalytic Reduction System (SNCR)

Depend on temperature, gas mixing and reaction time rather than catalyst.

Use ammonia or urea as reagents.Injection Temperature = 1500oF to 2200oF

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Desired NSCR Reactions (exothermic) as reagent and NOX flow over catalyst

4NO + 4NH3 + O2 -> 4N2 + 6H2O + heat (ammonia)

4NO + 2(CO(NH2)2 + O2 -> 4N2 + 2CO2 + 4H20 + heat (urea)

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Note only remove NO not NO2(does cover about 95% of NOx)

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Undesirable NSCR Reactions (exothermic) as reagent and NOX flow over catalyst

Same as SCR plus:

4NH3 + 5O2 -> 4NO + 6H2O(ammonia oxidation to NO)

4NH3 + 3O2 -> 2N2 + 6H2O(ammonia thermal decomposition)

2NH3 + 2O2 -> N2O + 3H2O(nitrous oxide emission)PPE Lecture 11 Tom Blair, P.E. 45

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Sulfur Dioxide Emission Control

Dry Furnace Sorbent Injections (FSI)Limestone forms Calcium oxide (CaO)

(calcination) and reacts with SO2 and Oxygen to form calcium sulfate CaSO4 (Sulfation)

Following are equations of reaction depending on if Limestone, dolomite, lime, or hydrated lime are reagents

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Post combustion – Wet scrubbing

1.Forced Oxidized Wet Limestone2.Magnesium Enhanced Wet Lime3.Seawater4.Ammonium Sulfate

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Wet FGD Systems – Comparison of Attributes

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Forced Oxidized Wet LimestoneBall Mill crush limestone and mix with water.Slurry pumped into absorber tower where slurry

mixes with gas.Forced Oxidation compressors inject air into

reaction tank to convert calcium sulfite (CaSO3) into gypsum (CaSO4*2H2O)

Mist eliminators remove slurry droplets from gas on exit of tower

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Wet limestone FGD system

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Flow diagram for wet limestone grinding system

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Absorber cutaway view

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Counter flow mist eliminator

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Magnesium enhanced processHigher removal efficiency Absorber tower height lessPumping head lowerRequired Lime to Gas ratio less

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Seawater and Ammonia are emerging technology

Seawater injection into absorber tower to scrub SO2

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Seawater scrubber PFD

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Ammonia scrubbing Very high efficiencyResalable ammonium sulfate fertilizer byproduct

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Ammonium sulfate PFD

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Semidry ScrubbingCa(OH)2 contacts gas as slurry and dried before

exit.Benefits:Lower energy usage & water consumptionFGD byproducts dryReduced slurry requirementsLess complex systemDisadvantageGreater reagent quantities needed and more

solids produced

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Continuous Emission Monitoring System (CEMS)In situ systems – monitor the flue gas at the

conditions present in the stack at the monitoring location

Extractive systems – draw gas sample to remote location.

Absorption Spectroscopy – scattering of lightOpacity Monitoring – visible light Gas Monitoring IR AnalysisLuminescence Spectroscopy – light emission of

molecules when excitedElectro-analytical – chemical reactions

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Questions?

Final Exam next week.

HW5, HW6, HW7Electrical & Instrumentation and control sections

PPE Lecture 11 Tom Blair, P.E. 63