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7/25/2019 Gasloop Guide
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Gas Loop
Gas Loop
Discuss the typical components of the gas loop using the prepared
schematic diagram.
Figure ----Schematic Diagram of Gas Loop
Combustion Analysis
Provide introductory statement. Use the complete data of the
selected fuel, to include ash, sediments and others. Present the results in
terms of weight and mass.
Sample computation
Ultimate Analysis
Carbon ( C ) 64%
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Hydrogen ( H ) 4%
Nitrogen ( N ) 1.4%
Sulfur ( S ) 1.2%
Oxygen ( O ) 6.8%
Ash, sediments
Computing the required O2:
Briefly discuss the procedure in computing the required oxygen.
For Carbon (C):
32
12x0.64=1.71
For Hydrogen (H):
32
4x0.04=0.32
For Sulfur (S):
32
32x0.012=0.012
1.71 + 0.32 + 0.012 = 2.042kg O
2
kgcoal0.068 =1.974
kg O2
kgcoal
Computing the Product of Combustion:
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Briefly discuss the procedure in computing the product of
combustion. Include in the computation the gravimetric and
volumetric analysis of the flue gas
For Carbon (C):
44
12x0.64=2.35
For Hydrogen (H):
18
2x0.04=0.36
For Sulfur (S):
64
32x 0.012=0.024
2.35 + 0.36 + 0.024 + 0.08 =2.814kg O
2
kgcoal
Prepare a table showing the summary of computed values
Combustion Analysis
Corresponding
Reaction
Required
O2
(include values in
terms of volume and
mass)
Product of
Combustion
(include values in
terms of volume and
mass)
C ~ C + O2CO2 1.71 2.35
H ~ 2H2+ O2 2H2O 0.32 0.36
N ~ Inert Gas Inert Gas 0.08
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S ~ S2+ 2O2 2SO2 0.012 0.024
O ~ --------------- -0.068 --------------------
TOTAL 1.974 2.814
Computation for Air-Fuel Ratio and Gas-Fuel Ratio:
For Air-Fuel Ratio:
Maf=1.974 + 1.974 (0.768
0.232)
Maf=13.07kg of air
kgof fuel
For Gas-Fuel Ratio:
Mfg= 2.814 + 1.974 (0.768
0.232)
Mfg= 15.85kgof flue gas
kgof fuel
Briefly discuss the procedure in computing the concentration of
various products of combustion here. Compare the results with the
existing emission standard (e.g. particulate matter, sulfur dioxide).
Results shall be used as basis in determining whether there is a
need to provide an air pollution control facility or not.
Air Preheater
Discuss the importance of air pre-heater and its function. Also
include the type/ kind of air preheater.
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Briefly describe each of the type/kind of air preheater focusing on
its major feature / components.
Types:
Tubular Type
Regenerative Air pre-heater
Rotating-plate regenerative air pre-heater
Selected Air Pre-heater
Briefly discuss type /kind of air preheater to be provided for the system
Air Pollution Control Facility and Management
Briefly discuss the type of pollutant that the plant would generate.
Cite the result of computation (flue gas concentration) and use it as basis
whether to provide control facility or employ appropriate management
measures to lessen it.
If pollution control facility is needed, discuss different type of
control facility and select which is more effective and economical.
Examples of control facility or measures are:
Electrostatic (Plate) Precipitator
Wet electrostatic precipitator
Baghouses
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Use of low sulfur fuel
Burner configuration/method of burning
Stack
Briefly discuss the function of stack. Cite importance of a properly
designed stack(economics , allow dispersion of pollutants)
Calculating Stack Height
Introductory statement:
Summary of operating conditions
Maximum continuous rate 1215 t/h of steam
Superheated steam pressure 17.2 MPa
Superheated steam temperature 541 CReheated steam temperature 541 C
Fuel bituminous coal
Tb= 353.33C + 37.78C
Tb= 391.11C
Where:
Tb= saturation boiler temperature,
Mfg= mass flue gas,
Mf= mass of fuel,
dfg= density of flue gas,
Qfg= volume flow rate of flue gas.
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Mfg= 15.85kgof flue gas
kgof fuel
Mf= 136.47
kgof fuel
sec
Compute individually for plants that have multiple generating units
(example if 3 units)
Mf= 136.47 / 3
Mf= 45.49kgof fuel
sec
dfg= 0.55kg
m3
Qfg=MfgPfg
=15.85
kg of flue gas
kgof fuel x 45.49
kgof fuel
sec
0.55kg
m3
Qfg =1,310.93m3/s
Use the recommended excess air
TypicalRanges of Excess Air Requirements for Various
Fuels and Methods of Firing
Fuel Excess air, % by
weight
Pulverized Coal 15 20
Fluidized bed Combustion 15 20
Spreader stoker 2535
Water-cooled vibrating grate stoker 2535
Chain and traveling grate stoker 2535
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Underfeed stoker 2540
Fuel oil 315
Natural gas 315
Coke oven gas 315
Blast furnace gas 1530
Wood/bark 2025
Refuse-derived fuel (RDF) 4060
Municipal solid waste (MSW) 80100
Source: Babcock & Wilcox, a McDermott company
Qfg= 1,310.93 x (excess air)
Qfg= ------- m3/s
Determine/calculate the draft every 30m of stack:
From PPE by Morse (pp.494);
D30=k (da- dg) 0.007578 da V
5
Q g
Where:
D = available draft per 30 m. of chimney
= cm. of water
k = 2.7 for brick of chimney and 2.4 for steel stack
da =density of air kg/m3
dg= density of flue gas kg/m3
V = gas velocity in the chimney m/s
Qg= gas flow in m3/s
D1= 0.004 V2dg
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Hchimney=Chimney Draft
D30
x 30
Computation for Height of Stack: (sample only)
For velocity
@ 6.1 m/s;(from PPE by Morse)
D30=2.4 (1.2kg
m3 0.55
kg
m3 ) 0.007578 (1.2
kg
m3
6.15
1,573.12
D30= 1.54 m
From PPE by (Morse, pp.496)
Hstack=0.004 (6.1 )2 (0.55 )+2
1.54x 30
Hstack= 40.56 m
Computation for Stack Diameter:
ID = 1.3
Q gV
ID = 1.3 1,573.12
6.1= 20.88 m
Repeat the procedure / calculate by assuming other values within
the range. Option is to have it in excel format for faster calculation.
Present the result in table form (sample shown below).
Computed Stack height and diameter at different velocity
(sample)
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Velocity
V
Height of chimney
H
Inside diameter
ID
Product
H x ID
6.1 m/s 40.56 m 20.88 856.08 m
2
11 m/s 46.25 m 15.55 719.19 m2
15.24 m/s 55.88 m 13.21 738.17 m2
The lowest value of the product is the ideal stack dimension
Fans and Blower
Introductory statement, which could include purpose of the
equipment and the need to provided one.
The design of fans and blowers would depend on the combustion
technology or type of the power plant.
For boilers with built-in burners, fan capacity need not be
computed. Just mention the type or capacity of the fan for supply air if
available in the specification.
Induced Draft Fan
Types of induced draft fan are as follows:
Centrifugal Fan
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Axial-Flow Fan
Briefly discuss the advantage and disadvantage of different type of
fan. Type of fan to be used should be justified.
Induced Draft Fan Computation
Figure ----shows the variations of air and the flue gas densities
with flue gas temperature.
(Source: PPD Morse, 1953)
Figure -----Variations of Air and Flue Gas Densities with Flue Gas
Temperatures
Sample computation :
Mg=15.85kg gas
kg fuel
Mf=136.47kg fuel
sec
For three (3) stack
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Mf= 136.47 / 3
Mf= 45.49kgof fuel
sec
Vfg=11ms(From stack design chosen for velocity of flue gas)
Pb=17.2Mpa (Super heated steam pressure from our boiler selection)
dg=0.55kg
m3
Qg=m ' g
dg,
But
m
m( f)( g)m' g=
where;
Qg=Volume flow rate of flue gas
mg= Mass flow rate of the gas
dg= Density of the flue gas
tfg= Flue gas temperature
tbsat= Saturation boiler
temperature
@ tfg=tbsat+100 F
tfg=tbsat+37.78 C
Pb=17.2Mpa ; tbsat=353.33 C (using steam table)
From figure 4.4, it shows that with a flue gas temperature of
391.11C, the density of flue gas is 0.55 kg/m3
tfg=353.33+37.78
tfg= 391.11 C
dg=0.55 kg
m3
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m
m( f)( g)m' g=
(15.85 )(45.49)
721.02 kg gas
s
Qg=721.02
0.55
Qg=1,310.93m
3
s
Qg=1310.93 (1.2 )
Qg=157312m
3
s
For volume flow rate, CFM
1573.12m
3
s x (3.28 ft1m)
3
x 60s
1min
3,330,925.12CFM
For total head, !"
!"=hs+h#
Velocity head, h#
h#=V
2
2 g
h#= (11)2
2(9.81)
h#=6.17m
h#=6.17 (1.2)(100)
1000
h#=0.74 cm $ater
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Static head, hs (typical values from PPD Morse pp. 477)
Boiler = 2.73
Super heater = 2.73,
Economizer = 2.54,
Air heater = 3.81,
Dust collector = 6.48
Note:
specify or use typical values of chosen dust collector or air
pollution control facility;
values would differ depending on the type of equipment used;
and use other data if available
hs=(2.73+2.73+2.54+3.81+6.48+2 )x 1.2
hs=24.35 cm of $ater
Therefore;
!"=hs+h#
!"=24.35+0.74
!"=25.0926 cm$ater
Select fan that is available in the market. Parameters to be used
in selecting should be volumetric flow rate and draft. Include picture of
the selected fan and no. of units to be used.
Concentration of Exhausted Flue Gas
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Briefly discuss the expected pollutants to be emitted by the plant
and the need of addressing it.
Dispersion Model ( derivation of formula used in estimating pollutants at variousdistance from the plant):
The Gaussian dispersion equations to calculate the chemical concentration
along the plume centerline at ground level and maximum ground level concentration
(MGLC) were used in the stud! The said equations were derived from the general
Gaussian dispersion equation (designated as equation ") which is given #elow:
C(x$$%)& ' exp"*+(*)
+
, -exp"*+(%.*%)
+
, / exp"*+(%/.*%)
+
,0 +%
where:
C& concentration of pollutants at coordinates x$$% (mg*m1)
'& emission rate of pollutants (mg*sec)
% & hori%ontal (crosswind) and vertical standard deviations of pollutants
concentration along the centerline of the flume (m)
& mean wind velocit (m*sec)
x & downwind distance along the centerline of the plume (m)
& hori%ontal distance from the centerline of the plume (m)
% & vertical distance from the ground level (m)
. & plume height (m)
To estimate the concentration along the plume centerline at ground level$
and % is #oth set equal to %ero! Thus equation " reduces to the following form:
C(x$2$2)& ' exp"*+(.*%)+, - equation +0
%
3quation + is further simplified # setting .&2$ which is used in estimating
MGLC (no thermal or momentum flux)!
C(2$2$2)& ' - equation 10
(%)2
where Cmax& maximum concentration of chemicals*su#stance (mg*m1)
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( %)2& hori%ontal and vertical deviations at x&2
4olving for emission rate of pollutant (') from equation 1 and su#stituting the
value of ' to equation +$ then the resulting equation is:
C(x$2$2)& C(2$2$2)(%)2 exp"*+(.*%)+
, -equation 50%
3quation 5 is then used in estimating the concentration of chemicals (Cx$2$2) at
distance (x) from the source$ along the plume center line at ground level! The
equation does not ta6e into account the dispersion of the air contaminants in the
crosswind direction (axis)! .ence$ it can #e expected that estimated values will #e
higher than the actual concentration!
7n using equation 5$ it is assumed that stac6 height (h) is equal to plume
height (.)! This assumption would li6ewise result in higher values$ as plume rise is
not considered! 8lume rise however$ could #e not so significant as the temperature
of the flue gas will #e much lower after passing a series of treatment! The
temperature of the flue gas is usuall lowered to the designed operating temperature
of the equipment!
The assumptions in using Gaussian dispersion equation should also #e
considered in the interpretation of data! These assumptions are: (a) wind and
velocit and direction are constant over height and over averaging period9 (#) the
emission rate is constant9 (c) the plume reflects completel at the ground (i!e!$ no
deposition)9 and (c) no diffusion occurs in the direction of the plume travel (La
Grega$"5)!
Calculated concentration of pollutants (sample only)
Formula estimating concentration at various distance from the plant;
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C= Q
%(Q& Qy)
Where:
C = pollution concentrationQ = emission rate, mg/s
(Q& Qy ) = horizontal and vertical standard deviation
= mean wind velocity (data based on Philippine condition)
Q = Qfg(concentration of pollutant; g/N.cm)
Qfg= use design data ; m3/s
H = ------ m (From Stack Height Design)
TSP = calculated concentration after control facility ;g/N.cm
Values taken from figure below:
(Q& Qy ) = horizontal and vertical standard deviation; taken from
figure below
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Figure -----Horizontal Dispersion Coefficient
Source: http://www.lenntech.com/
Figure -----Vertical Dispersion Coefficient
For Maximum ground level concentration (x=0;y=0;z=0)
Q&=6m
Qy=10m
C=
471.94
%(10) (6)(2)
C(000)= 471.94
%(10) (6 )(2)
= 1.25mg
m3
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Maximum ground level concentration:
@ x = 0;
(x00)=
C(000)(Q& Qy)e
[ 1
2(!Q&)2]
(Q& Qy)
(x00)=1.25 (6 )(10)e
[ 1
2 ( 46.256 )2]
(6 )(10)
= 1.24
mg
m3
= 1,240'g
m3
Table ----- shows the concentration of flue gas with respect to
distance from source.
Concentration with respect to distance
Distance,
In meter Qy Q&
g
m3
200 22 14 229.25
225 24 15 199.24
230 26 16 169.54
250 28 17 149.55
300 40 20 81.96
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The maximum ambient concentration of Total Suspended
Particulates (TSP) is 90 g/m3. Table ----- shows that the allowable
concentration will be met at 300 m away from the stack.
Gas Loop Summary
Summarized the gas loop components and update and show the
resulting / revise diagram indicating the number and specifications.
Figure ----Proposed Diagram of Gas Loop for---------Unit