11 2 8 liquor clarification
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11.2.8 Liquor Clarification Process
11.2.8.1 Facility and Process Description
The Liquor Clarification Process in Tayan Bayer Process involves a
number of key steps, including bauxite storage, bauxite grinding,
digestion, heat recovery from digester slurry, mud settling and
mud washing of insoluble residue, liquor filtration for clarification,
liquor cooling and mud filtration for land dumping.
The Liquor Clarification Process is described along the Process Flow
Diagram specified in Subsection 11.2.2 Scheduled maintenanceshut-down will be carried out every three (3) months.
The accumulated capacity of the Washed Bauxite at the Bauxite
Storage Area of 3,000 m2 provided in the Alumina Site shall be
5,760 WMT at maximum, equivalent to an approximately two (2)
days consumption. The Washed Bauxite stocked in the Bauxite
Storage Area shall be periodically carried by the sloping Belt
Conveyer (CBS-BC-101 depicted in Drawing No. CBS-100-0001-A1)
and the Shuttle Conveyer (CBS-BC-102) to the Bauxite Storage
Tanks (CBS-TK-102, CBS-TK-103 and CBS-TK-104 depicted in
Drawing No. CBS-100-0001-A1) with a volume of 300 m3 each,
equivalent to eight (8) hours reserve of the Washed Bauxite for
avoiding midnight feeding.
From the respective Bauxite Storage Tanks (CBS-TK-102, CBS-TK-
103 and CBS-TK-104), the Washed Bauxite shall be continuously
charged to the two (2) operating Rod Mills (BSC-RM-101 and BSC-RM-102 depicted in Drawing No. BSC-100-0001-A1, and BSC-RM-
103 depicted in Drawing No. BSC-100-0002-A1), each rated at 40 -
45 DMT/Hr in operation, by corresponding variable speed Belt
Conveyer with a weight scale (depicted in Drawing Nos. BSC-100-
0001-A1 and BSC-100-0002-A1). The remaining one (1) Rod Mill
shall be down for spare. The Washed Bauxite shall be ground up to
2 mm passing size using the Rod Mills to ensure sufficient solid-
liquid contact during a digestion phase.
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At the inlet of each Rod Mill, the Washed Bauxite shall be mixed
with hot aluminate liquor, often referred to as spent liquor or
mother liquor, which shall be taken from after-mentioned HeatExchanger provided in a heat recovery area, in order to form slurry.
The charging liquor to each Rod Mill shall be pumped from the
Relay Tank (BDH-TK-101 depicted in Drawing No. BDH-100-0001-
A1), whose flow rate shall be controlled with a flow meter in
proportion to a bauxite consumption rate. The ground bauxite
slurry from each Rod Mill shall be charged through each launder to
the Slurry Relay Tank (BSC-TK-201 depicted in Drawing No. BSC-
100-0002-A1).
The 56% (equivalent to approximately 950 gpl) solids slurry shall
be pumped from the Relay Tank (BSC-TK-201) directly to a series of
the three (3) operating Digesters, each furnished with an agitator
(BDH-D-201, BDH-D-202 and BDH-D-203 depicted in Drawing No.
BDH-100-0004-A1). The remaining one (1) Digester shall be down
for cleaning or spare. Heated spent liquor (often, referred to as
mother liquor) shall be simultaneously introduced to the first
Digester (BDH-D-201 or BDH-202) through one (1) operating Heat
Exchanger (BDH-H-105 or BDH-H-106 depicted in Drawing No.
BDH-100-0003-A1) where it shall be indirectly heated to
approximately 180C by a live steam of approximately 1 MPaG
supplied from the Boiler. In this digestion stage, the bauxite slurry
shall be mixed with this heated spent liquor. Three (3) Digester
vessels shall have approximately forty (40) minutes holding time at
an average temperature of 140C which is measured at the inside
of the first Digester. This would be adequate time for extraction of
solid gibbsite in bauxite and for desilication of reactive silica ofmost Tayan bauxites.
The digestion effluent slurry of approximately 135C from the last
Digester (BDH-D203 or BDH-D-204 depicted in Drawing No. BDH-
100-0004-A1) shall be cooled down at temperature of
approximately 102 - 106C through the heat recovery stage.
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In this heat recovery stage where is correspond to a counter
current system between hot digester effluent and hot spent liquor,
three (3) Flash Tanks provided in series (BDH-FT-201, BDH-FT-202and BDH-FT-203 depicted in Drawing No. BDH-100-0004-A1) and
three (3) Heat Exchangers provided in series (three (3) of BDH-H-
101, BDH-H-102, BDH-H-103 and BDH-H-104 depicted in Drawing
No. BDH-100-0002-A1 for operating) shall be employed. Each
flashed steam through a series of three (3) stages flashing shall be
used to heat the incoming spent liquor supplying to each Heat
Exchanger.
The incoming spent liquor, which shall be pumped from after-mentioned vacuum cooling facilities, shall be step-wise heated
from 83C to approximately 112C by the flashed steam generated
in each Flash Tank.
The digestion effluent shall be passed to each Flash Tank provided
in series through an internal downward-streamed piping with a
throttle at its edge, for avoiding flashing at the piping inside and
mitigating entrainment and abrasion to the tank inwards.
The spent liquor flow rate of 650 680 m3/Hr shall be measured
with a flow meter. An approximately 6% of the spent liquor of
approximately 90C at the outlet of the first Heat Exchanger (BDH-
H-101 or BDH-H-102) shall be poured into the Liquor Relay Tank
(BDH-TK-101 depicted in Drawing No. BDH-100-0001-A1) for
preparing the ground bauxite slurry as explained above. The
remaining 94% of the spent liquor shall be flowed into the second
and third Heat Exchanger provided in series to heat up toapproximately 112C by the corresponding flashed steam from
each Flash Tank. The heated spent liquor shall be further heated up
to approximately 180C by live steam through the Heat Exchanger
(BDH-H-105 or BDH-H-106 depicted in Drawing No. BDH-100-0003-
A1), as above mentioned, in order to ensure the digestion
temperature of 140C.
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The four (4) Heat Exchangers (BDH-H-101 to BDH-H-104) shall be
provided for recovery of the flashed steam; three (3) for operating
and one (1) for stand-by in operation. The Heat Exchangers shallbe interchanged for tube cleaning during the scheduled
maintenance shut-down. After cleaning, tube-cleaned Heat
Exchanger shall be provided to allow continuous operation of the
digestion and heat recovery facilities as a spare.
The two (2) Heat Exchangers (BDH-H-105 and BDH-H-106 depicted
in Drawing No. BDH-100-0003-A1) shall be periodically changed in
operation for chemical tube-cleaning, using two (2) automatic
three-way valves provided in spent liquor piping connected tobefore and after the Heat Exchangers. All Heat Exchangers shall be
of the same shell & tube type with four passes.
Three (3) Booster Pumps (BDH-P-103A, BDH-P-103B and BDH-P-
103C depicted in Drawing No. BDH-100-0003-A1) shall be provided
between the live steam heaters and the flashed steam heaters
(depicted in Drawing No. BDH-100-0003-A1). The two (2) Booster
Pumps shall be for operating, and the remaining one (1) shall be
for stand-by or back up for the former Pumps (BDH-P-102A and
BDH-P-102B depicted in Drawing No. BDH-100-0002-A1).
For flashing down of the digestion slurry, the Barometric Condenser
(BDH-FT-401 depicted in Drawing No. BHD-100-0006-A1) with the
two (2) Ejectors (BDH-J-501 and BDH-J-502) shall be provided. A
part of the flashed steam introduced to the first Heat Exchanger
(BDH-H-101 or BDH-H-102) from the last Flash Tank (BDH-FT-203)
shall be fed to the Barometric Condenser for condensation of theflashed steam and shall be condensed by contacting with overflow
liquor from the fourth stage Washer (BRW-TH-104, BRW-TH-105 or
BRW-TH-106 depicted in Drawing Nos. BRW-100-0002-A1 and BRW-
100-0003-A1). Heated liquor discharged from the Barometric
Condenser shall be returned to the Washer (BRW-TH-103 or BRW-
TH-104) for avoiding auto-precipitation.
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And then the slurry in the last Flash Tank (BDH-FT-203) shall be
controlled and maintained to nearly atmospheric pressure with air
injection into the Barometric Condenser. The pressure to becontrolled shall be in the range of -30 to -60 mmHg.
As bauxites usually contain some organic carbons in the form of
humic substances, they will be reacted with hot caustic liquor and
be decomposed to gas and soluble substances. Namely, tenuous
gas containing hydrogen and uncondensed components will be
continuously generated in the Digesters and Flash Tanks, and the
gas will be accumulated in the Digesters and Heat Exchangers.
Therefore, the Digesters shall be periodically degassed by manualto eliminate it. And the gas generated from the Flash Tanks shall be
continuously eliminated through a series of piping provided outside
of the Heat Exchangers, flowed to the Barometric Condenser and
finally degassed by two Ejectors (depicted in Drawing No. BDH-
100-0006-A1).
The condensate drain (DWA) generated from the operating Heat
Exchanger (BDH-H-105 or BDH-H-106 depicted in Drawing No.
BDH-U-0001-A1) shall be directly returned to the Boiler as
condensate water for Boilers after monitored with a conductive
meter. Meanwhile, the condensate drain (DWB) generated from
each flashed steam heater shall be flowed from high temperature
heater to low temperature heater through a level control valve. The
condensate from the last Heat Exchanger shall be pumped to DWB
Tank (DSS-TK-102 depicted in Drawing No. DSS-100-0001-A1) and
primarily used as mud washing water after monitoring with a
conductive meter. When each drain (DWA and DWB) iscontaminated with spent liquor flowing through heater tubes, it
shall be dumped to the washer by changing stream direction of
three way valves (depicted in Drawing No. BDH-U-0001-A1).
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Scale deposited on the wall of the heater tubes equipped in the
digestion and heat recovery areas shall be periodically eliminated
by sulfuric acid cleaning adding corrosion inhibitor (depicted inDrawing No. APS-100-001-A1). The main composition of the scale is
sodalite denoted by rational formula of
3(2SiO2Al2O3Na2O)Na2XnH2O(S).
IWB water shall be firstly charged into the rubber-lined Tank (APS-
TK-101 or APS-TK-102 depicted in Drawing No. APS-100-0001-A1)
for adjusting sulfuric concentration, and then sulfuric acid solution
of 98% packed in a liquid one (1) ton container shall be poured into
the Tank, adding inhibitor. Diluted sulfuric solution of 15% shall be
circulated between specific Heat Exchanger tubes and the Tankthrough rubber-lined piping. After cleaning, the circulating liquid
shall be discharged to the Tank (APS-TK-101 or APS-TK-102). And
spent liquor shall be charged into the Tank (APS-TK-101 or APS-TK-
102 depicted in Drawing No. APS-100-0001-A1) for neutralization of
the rubber-lined piping and tubes. Waste slurries including
neutralized spent liquor shall be transferred to the Mud Slurry Feed
Tank (BRF-TK-102 depicted in Drawing No. BRF-100-0101-A1) for
filtration. Finally, all relating piping including tubes shall be flushed
by drain (DWB) or pressurized air.
Safety sequence shall be provided for protecting from the
unacceptable upper limit of temperature and pressure. In the case
of abnormality of temperature and/or pressure, namely in
emergency cases, all pumps in the digestion area shall be
automatically stopped by interlock sequence and control valves in
the same area shall be simultaneously closed except the flashed
steam control valves for blow off to the atmosphere (depicted inDrawing No. B-P-A-0200-004). This interlock sequence shall be also
worked by operating a corresponding switch manually, if an
operator implements an emergency shut-down.
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Slurry from the bottom of the last Flash Tank (BDH-FT-203) at
temperature of 102 - 106C shall be pumped to the mud settling
area through the Sand Catcher (BDH-SN-301 depicted in DrawingNo. BDH-100-0005-A1). As the slurry contains coarse sand particles
of 1 - 5 mm in size, they shall be separated by an inclined spiral
classifier equipped in the Sand Catcher. Separated sand particles
shall be discharged to an adjoining Tank (BDH-TK-301 depicted in
Drawing No. BDH-100-0005-A1) in which the sand shall be mixed
with mud slurry came from mud washing circuit. The mixed slurry
shall be transported to the mud filtration stage using the inverter
Pump (BDH-P-301A or BDH-P-301B depicted in Drawing No. BDH-
100-0005-A1).
The slurry pumped from an upper zone of the Sand Catcher,
containing approximately 3% solids, shall be continuously charged
to the two (2) single deck Thickeners (or Settlers) operating in
parallel (BOS-TH-101, BOS-TH-102 or BOS-TH-103 depicted in
Drawing No. BOS-100-0001-A1). The remaining one (1) Thickener
(or Settler) shall be for spare or stand-by for manual cleaning. The
three (3) Settlers shall not be converted to mud washer.
Achieving good performance for high compaction of mud and
clarification of liquor in the feed stream by gravity sedimentation,
conventional cable-arm or cable torque thickeners with a central
bottom discharge shall be provided as the settlers and the
succeeding washers. These thickeners shall be supported by a
stationary steel or concrete center column and raking arms shall
be attached to a driving cage which rotates around the center
column.
The settlers called as a conventional cable-arm thickener or cable
torque thickener, in which cables shall be attached to upper
trusses near liquid surface to move two (2) rake arms with plural
blades, which are hinged to drive structure, shall allow the rakes to
be raised when excessive torque is encountered. And also the
settlers shall be furnished with drive assemblies, a drive lifting unit,
feed well, and radial inside launder.
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The slurry from the Sand Catcher shall be tangentially fed to the
feed well through a feeding launder at which bubble entrained in
the slurry during transportation shall be separated. Emulsionflocculants, effective to goethite bauxite, shall be continuously also
added to the slurry existed in the feed well at three (3) feeding
points for forming flocculation. The emulsion flocculants of high
polymer type shall be used as it enters the settlers to aid in
flocculation, compaction and consolidation of mud. Further lime
slurry as a clarification aid shall be occasionally added to the
operating settlers according to turbidity of settler overflow liquor.
All underflow pumps of the settlers shall be located, whereverpossible, in adjacent to a discharging center cone of each settler.
The overflow from the settlers shall be removed in a peripheral
inner launder with level flat weirs provided inside each settler. The
overflow, which contains solids of approximately 100 ppm, shall be
pumped directly from the Overflow Relay Tank (BOS-TK-102
depicted in Drawing No. BOS-100-0001-A1) to mud filtration area
for final clarification.
The underflow from the settlers containing mud solids shall be
combined with overflow from the second mud washing stage and
fed to the first mud washing stage (depicted in Drawing No. BRW-
100-0001-A1).
The mud washing circuit (depicted in Drawing Nos. BRW-100-0001-
A1, BRW-100-0002-A1 and BRW-100-0003-A1) for reduction of soda
content in liquor shall be designed as a four (4) stage, counter-
current decantation system (CCD) utilizing four (4) operating singledeck settlers. A total of six (6) similar washing vessels shall be
provided; four (4) for operating and two (2) for spares for
maintenance or manual cleaning, so that there shall always be a
four (4) stage for the washing. Stream direction of each underflow
and overflow shall be changeable by changing piping when timing
of thickener cleaning.
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Two (2) pump stations consisting of three (3) centrifugal pumps
shall be provided for two (2) washers; one station for overflow
transportation, the other for underflow transportation. Two (2) ofthree (3) centrifugal pumps shall be used for the respective
washers and the remaining one (1) shall be used as common
stand-by.
As described above, the liquor in the second or third stage washer
shall be recycled through the Barometric Condenser located in the
heat recovery areas.
Wash water (DWB) shall be fed to the last stage through theFiltrate Tank (BRF-TK-101 depicted in Drawing No. BRF-100-0101-
A1) for the mud washing. Other miscellaneous liquid containing
soda shall be introduced into intermediate stage. Piping shall be
provided to bypass any washing vessels.
Emulsion flocculants shall be continuously added to all operating
washers (depicted in Drawing No. TAP-100-0001-A1) in the range of
30 100 ppm. The flocculants packed in a one (1) ton liquid
container shall be mixed with the plant drain water (DWC) and
shall be stored in the Stock Tank with an agitator (TAP-TK-101
depicted in Drawing No. TAP-100-0001-A1).
This flocculants shall be diluted to 1 - 3% concentration by mixing
the flocculants handled with a plunger pump and DWC water
measured with a flow meter by means of an inline mixer. The
diluted solution shall be stocked in the stock Tank with a viscosity
meter (TAP-TK-101) and shall be continuously fed to each thickenerin the mud settling and mud washing areas through single
transportation piping for each thickener.
In the operation of the mud settling and mud washing, the rake
torque of each operating thickener shall be continuously monitored
and shall be controlled by changing each rate of the underflow
volumetric flow and flocculants adding, periodically measuring mud
level and overflow turbidity.
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The underflow from the last washer shall be charged to the Mud
Slurry Tank with an agitator (BRF-TK-102 depicted in Drawing No.
BRF-100-0101-A1) through the Tank (BDH-TK-301) at which thesand shall be picked up, as mentioned above. And then the slurry
containing the sand shall be fed to the one (1) operating Pressure
Disc Filter (BRF-F-101A or BRF-F-101B depicted in Drawing No. BRF-
100-0101-A1).
The effluent from the settlers and the first washer shall be flowed
into the Overflow Tank (BOS-TK-102 depicted in Drawing No. BOS-
100-0001-A1) through bridge launders connecting with the three
(3) settlers and pumping of the first washer overflow.
Tri-calcium aluminate particles (3CaOAl2O36H2O or TCA) shall be
added to the Overflow Tank (BOS-TK-102) as a filter aid for
reduction of filtration resistance at the liquor filtration stage.
TCA as a filter aid shall be prepared by reacting slaked lime with
sodium aluminate liquor according to the following reaction:
3Ca(OH)2(s) + 2NaAlO2(l) + 4H2O(l) 3CaOAl2O36H2O(s) +
2NaOH(l)
As the first step, lime packed in a 500 kg bag container shall be
mixed with drain water (DWC) by batch-wise manner in the Re-
slurry Tank with an agitator (LSP-TK-101 depicted in Drawing No.
LSP-100-0001-A1). The resultant lime slurry treated with a constant
concentration of approximately 500 gpl shall be held in the Stock
Tank with an agitator (LSP-TK-102) and shall be continuously fed tothe insulated Tank with an agitator (TCA-TK-101 depicted in
Drawing No. TCA-100-0001-A1), simultaneously adding filtered
liquor (depicted in Drawing No. PFS-100-0004-A1) and pure caustic
liquor (depicted in Drawing No. CSS-100-0001-A1). These three (3)
liquids shall be controlled by a cascade control linking with each
flow meter.
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As liquor discharged from the Overflow Tank (BOS-TK-102 depicted
in Drawing No. BOS-100-0001-A1) contains traces of ultra fine solid
up to approximately 100 ppm, the liquor shall be continuouslypumped to the liquor filtration stage for final clarification (depicted
in Drawing Nos. PFS-100-0003-A1 and PFS-100-0004-A1).
The Pressure Plate Filters (PFS-F-101 to PFS-F-104 depicted in
Drawing No. PFS-100-0003-A1) shall be employed; three (3) for
operating and one (1) for stand-by. The Filters (PFS-F-101 to PFS-F-
104) shall mainly comprise a vessel, vertical filter elements inside
the vessel, a top reservoir for backflushing, five (5) pneumatic
valves for full automatic operation and automatic control system.The Filters shall be automatically operated by opening and/or
closing the pneumatic valves sequentially under the automatic
control system such as the below table Schematic Cycle of
Vertical Filters in Operation. The cycle time shall be approximately
one (1) hour. Each cycle shall be composed of leveling, cake
formation, filtering, decompressing and discharging. For the
leveling, liquor charging pipe through the Feed Valve V1 shall be
vertically inserted near top level of the leaf plates. And for the
decompressing, two (2) pipes, which are independently and
vertically inserted inside the filter, shall be employed through the
Decompressing Valve V3 and the Overflow Valve V4 respectively.
Each length of three (3) inside pipes is as follows; Decompression
Pipe > Overflow Pipe > Liquor Charging Pipe.
The time schedule of three (3) operating Filters shall be set so that
the liquor is continuously poured into the Filter(s) based on flow
rate control.
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Schematic Cycle of Vertical Filters in Operation
Cycle Step 1 2 3 4 5
Cycle Function Leveling Cake
formation
Filtrating Decompressin
g
Discharging
Cycle Time (min.) 0 0 - 2 2 - 58 58 - 59 56 - 60
Valve Valve NameV1 Feed valve Open Open Open Close Close
V2 Backflow valve Close Open Close Close Close
V3 Decompressin
g valve
Close Close Close Open Open
V4 Overflow valve Close Close Close Open Open
V5 Extraction
valve
Close Close Close Close Open
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In the period of cake formation, liquor pumped from the Overflow
Tank (BOS-TK-102) shall be filled into the vessel to form cake
adhered to filter clothes and cloudy filtrate shall be flowed to theTank (PFS-TK-701 depicted in Drawing No. PFS-100-0004-A1)
through the Backflow Valve V2. The discharged liquor with turbidity
shall be recycled through the Overflow Tank (BOS-TK-102 depicted
in Drawing No. BOS-100-0001-A1). In the period of filtrating, solids
shall be blocked onto the filter clothes to form cake, while clear
filtrate (turbidity: less than 15 mg/l) shall be flowed into the top
reservoir above the filter through the external manifold and finally
to the Filtrate Tank (PFS-TK-104 depicted in Drawing No. PFS-100-
0004-A1). In the period of decompressing and discharging,pressure inside the vessel shall be fallen to the normal value, and
then fresh cake shall be fallen off the filter clothes by filtrate
flushed back from the top reservoir and discharged to the Cake Re-
slurry Tank (PFS-TK-101 and PFS-TK-102 depicted in Drawing No.
PFS-100-0003-A1). In the period of leveling, liquid level shall be
adjusted, a cushion of air in the top of vessel shall be reestablished
and then a new filtration shall be started.
The fresh cake collected in the Cake Re-slurry Tank (PFS-TK-101 and
PFS-TK-102) shall be pumped to the third or fourth washing stage in
order to recover the soda associated with the mud (depicted in
Drawing No. BRW-100-0002-A1).
During the stand-by time, the filter clothes shall be cleaned using
hot and high caustic aluminate liquor with 200 grams caustic per
litter at 95C (depicted in Drawing No. PFS-100-0003-A1). The hot
caustic liquor for cleaning shall be circulated between the saidFilter and the Cloth Cleaning Tank (CSS-TK-105 depicted in Drawing
No. PFS-100-0003-A1) for an hour. The caustic liquor for cleaning
shall be always heated by indirect steam and shall be manually
supplemented adding new pure caustic liquor at a low level of the
Cloth Cleaning Tank (CSS-TK-105).
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The precious filtrate from the Filter shall be run to the Filtrate Tank
(PFS-TK-104 depicted in Drawing No. PFS-100-0003-A1), if it is less
than 15 ppm. The precious filtrate shall be charged to the vacuumFlash Tanks (VHI-FT-101, VHI-FT-102, VHI-FT-103 and VHI-FT-104
depicted in Drawing No. VHI-100-0001-A1) provided in the liquor
cooling stage.
At the liquor cooling stage, the precious filtrate at temperature of
approximately 100C from each Filter, namely pregnant liquor,
shall be heat-transferred to the spent liquor of approximately 58C
from the Stock Tanks (PLS-TK-101, PLS-TK-102, PLS-TK-103 and PLS-
TK-104 depicted in Drawing No. PLS-100-0001-A1) by a countercurrent heat-transfer system using a series of the Flash Tanks (VHI-
FT-101, VHI-FT-102, VHI-FT-103 and VHI-FT-104) and the Heat
Exchangers (VHI-H-101, VHI-H-102, VHI-H-103 and VHI-H-104
depicted in Drawing No. VHI-100-0002-A1) of shell and tube type
and shall be cooled down for controlling an initial precipitation
temperature of 66C of the Chain-1 of the Hydrate Production
Process. The system is the same as the heat recovery system in
the bauxite digestion stage.
The pregnant liquor shall be continuously pumped to a series of
four (4) vacuum Flash Tanks (VHI-FT-101, VHI-FT-102, VHI-FT-103
and VHI-FT-104 depicted in Drawing No. VHI-100-0001-A1). Each
flash steam from the three (3) Flash Tanks (VHI-FT-101, VHI-FT-102
and VHI-FT-103) shall be used to heat up the spent liquor in a
series of the three (3) operating indirect Heat Exchangers (VHI-H-
101, VHI-H-102, VHI-H-103 or VHI-104 depicted in Drawing No. VHI-
100-0002-A1).
Flashing at the fourth Flash Tank (VHI-FT-104) shall be used to
control the liquor temperature for the Chain-1s precipitation by
condensing a desired quantity of flashed steam in the Barometric
Condenser (VHI-CD-101 depicted in Drawing No. VHI-100-0001-A1).
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The pregnant liquor from the last Flash Tank (VHI-FT-104) shall be
charged to Precipitators in the Chain-1, Chain-2 and Chain-3
through the Relay Tank (VHI-TK-101). The spent liquor ofapproximately 58C from the Stock Tanks in the Chain-1 (PLS-TK-
101, PLS-TK-102, PLS-TK-103 and PLS-TK-104 depicted in Drawing
No. PLS-100-0001-A1) shall be pumped to the first Heat Exchanger
(VHI-H-101 or VHI-H-102). And the spent liquor of approximately
82C discharged from the last Heat Exchanger (VHI-H-103 or VHI-
H-104) shall be charged to the Digester Pumps (BDH-P-102A and
BDH-P-102B depicted in Drawing No. BDH-100-0002-A1).
A total of the four (4) Heat Exchangers of shell and tube type (VHI-H-101, VHI-H-102, VHI-H-103 and VHI-H-104) shall be provided;
three (3) for operating and one (1) for spare for maintenance and
manual tube bowling. Tubes of the Heat Exchanger shall be
cleaned with caustic liquor from the Heat Exchanger (CSS-H-101
depicted in Drawing No. CSS-100-0002-A1) every scheduled
maintenance shut-down in order to reduce fouling to the heater
tubes.
The pregnant liquor shall be continuously introduced into each
Flash Tank with a tangential stream which shall be passed through
a top-covered circler launder provided inside of each Flash Tank to
form a falling film. In addition, for preventing the entrainments
such as droplets and mist containing caustic soda, an internal
demister made of metal fiber shall be bedded at the upper inside
of each Flash Tank. The demister shall be washed with pure caustic
using internal spray nozzles periodically.
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Noncondensable gas, which is mainly carbon dioxide, generated
from the pregnant liquor during flushing down shall be vented from
each Flash Tank (VHI-FT-101, VHI-FT-102 or VHI-FT-103) to therespective Heat Exchangers (VHI-H-101, VHI-H-102, VHI-H-103 or
VHI-H-104) through its succeeding flash steam line. Furthermore,
the noncondensable gas shall be transferred to the last Flash Tank
(VHI-FT-104) through the flash steam line connected with each
Heat Exchanger, gone to the Barometric Condenser (VHI-CD-101
depicted in Drawing No. VHI-100-0001-A1) and finally eliminated
from the two (2) stage steam Ejectors (VHI-J-101, VHI-J-102 and
VHI-J-103 depicted in Drawing No. VHI-100-0001-A1).
The direct-contact countercurrent Barometric Condenser (VHI-CD-
101) furnished with multi stage impingement plates internally, in
which vapor is condensed by rising against a rain of cooling water,
shall be provided for cooling the pregnant liquor came from the last
Flash Tank (VHI-FT-401). Inner pressure of the last Flash Tank shall
be controlled by an air suction volume using a control valve for
maintaining the precipitation temperature of 66C in the Chain-1.
Sedimentation treatment water (IWA) from the Water Pool-1 shall
be directly pumped to the Barometric Condenser (VHI-CD-101) and
shall be discharged by gravity to the Hot Well (W-TK-101) provided
beneath the Barometric Condenser. The noncondensable gas shall
be also discharged to the Hot Well through the Ejector (VHI-J-103).
Condensate drain from each Heat Exchanger shall be gone to the
Condensate Tank (VHI-TK-103 depicted in Drawing No. VHI-U-0001-
A1) and finally fed to the DWC Relay Tank (DSS-TK-101 depicted inDrawing No. DSS-100-0001-A1). It shall be utilized mainly as
washing water for hydrate filtration. The condensate drain
discharged from the Condensate Tank (VHI-TK-103) shall be
continuously monitored with a conductive meter. If the conductivity
of the condensate drain will be over an upper limit, the
contaminated condensate shall be automatically dumped to the
mud washing stage with three directions valve.
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If the increasing of evaporation capacity is required to maintain the
water balance in the Bayer Process when heavy rain falls, vapor re-
compressive evaporator (VRCE) shall be intermittently operated(described in Drawing No. B-P-A-0200-015). SDK Yokohama Plant
has operated its Bayer Process without evaporation unit. However,
considering heavy tropical rainfall in Indonesia, it shall be provided
in Tayan plant which is estimated as the evaporation capacity of 10
tons per hour.
The VRCE process has designed by Sumiju Plant Engineering Co.,
LTD. The process and equipment will be installed in space beneath
the Flash Tanks in the liquor cooling area.
Spent liquor discharged from the liquor cooling stage shall be
passed to the first evaporation section in the VRCE which shall be
composed of four (4) evaporation sections in a body. The liquor
shall be circulated through the falling film evaporator. As the liquor
shall be flowed down through an inner plate, it shall be heated by
re-compressed vapor which condenses inside the plate and goes to
the sump. The liquor becomes progressively more concentrated as
it passes through the units. Finally, it shall be discharged from the
fourth section. The vapor leaving the evaporator shall be passed
through an internal demister and then entered into a blower where
it shall be adiabatically compressed. The compressed and heated
vapor shall be used as a source of heat for all evaporation sections.
Chemical cleaning shall be periodically performed by H 2SO4 with
corrosion inhibitor for precipitated sodalite scale and water
washing for sodium fluoride scale at the evaporation stage. Thewashing piping shall be equipped in the evaporation section. The
liquor from evaporation shall be supplied to the suction side of the
Digester Pumps (BDH-P-102A and BDH-102B depicted in Drawing
No. BDH-100-0002-A1).
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The underflow slurry from the last washer (BRW-TH-105 or BRW-TH-
106) shall be pumped to the Relay Tank (BRF-TK-102 depicted in
Drawing No. BRF-100-0101-A1) for the mud filtration. At this mudfiltration stage, pressure disk filters shall be adopted to prevent
environmental contamination such as groundwater infiltration and
spill caused by rainfall as possible. The pressure disc filter has
been designed based on laboratory experiments with BOKELA who
is an engineering firm in Germany
A pressure-filtered mud cake with approximately 30% moisture
content, which is corresponding to permeability coefficients of 10 -4
to 10-6, shall be capable of reducing dumping alkalinity andimpounding it into the cake.
Two (2) Pressure Disk Filters (BRF-F-101A depicted in Drawing No.
BRF-100-0101-A1 and BRF-F-101B depicted in Drawing No. BRF-
100-0102-A1) shall be provided. A conventional rotary disk filter
shall be housed inside the respective horizontal pressure vessels
that shall be filled with compressed air up to 4 - 6 kg/cm3 supplied
from air compressors during operation.
The Pressure Disk Filters (BRF-F-101A and BRF-F-101B) shall be
provided for the mud filtration available continuously to achieve
the filtered cake with 30 - 31% moisture content. One (1) Pressure
Disk Filter shall be for operating and the other one shall be for
spare or chemical cloth-cleaning with hot caustic liquor periodically.
The mud slurry from the Relay Tank (BRF-TK-102 depicted in
Drawing No. BRF-100-0101-A1) shall be pumped into the filter vatwithout an agitator via slurry feed pipes in the pressurized vessel.
The main components of variable-speed disk filter shall be disk
filter of approximate 3.2 m in diameter with six (6) filter disks, each
arranged with twenty (20) filter segments, pressure vessel, cake
discharge sluice, filtrate receiver and blow-off tank.
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The filter segments of the disk shall be connected to individual
process zones; namely cake formation zone, dewatering zone, cake
discharge zone by gas blow-back and filter cloth cleaning zone, bymeans of openings in a control plate provided inside a control
head.
Focusing on one single filter segment of the rotary filter under the
main drive activating and disk rotating in normal speed, the
process-steps shall be taken place one after the other. After
submerging a cell of filter in the slurry, the cell shall be connected
to the cake formation zone according to filtration pressure
difference. While, the slurry shall be entered into the filter segmentand the solids shall be kept back by the filter cloth where a filter
cake shall be formed. Mother liquor or filtrate shall be flowed via
filtrate pipes and the control head out of the pressure vessel to the
Filtrate Receiver Tank (BRF-TK-107A and BRF-TK-107B) and be
separated there from accompanying gas.
After the cake formation zone, the dewatering zone shall be
followed where compressed gas displaces pore liquor and flows
through the filter cake. The gas as well as the filtrate from the
dewatering zone shall be also transported to the filtrate receiver.
As the last process step, the cake shall be discharged after
finishing of the cake dewatering. The filter media of the segment
shall be inflated by a sharp gas blow-back so that the filter cake
falls off and is directed to a conveyer with a deflector plate. The
conveyer transports the cake to the discharged sluice where the
cake shall be sluiced out of the pressure vessel periodically. The
cake discharged sluice shall be a chamber sluice consisting of anupper and a lower slide gate. It can be operated with a timer.
A cloth wash spray bar for filter cloth cleaning shall be situated
underneath the deflector plate. The filter cloth, now free of filter
cake, shall be cyclically free from particle adhesion with the cloth
wash spray bar. Afterwards the filter cell shall be submerged again
in the slurry, and the filtration process shall be started anew.
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In this control cycle, the cake formation shall be controlled by
adjusting a filter speed with cascade sequence of feeding flow rate
and level of the cell.
Steam cabin shall cover a part of the filter area and form a
separated room with live steam inside the vessel for reduction of
cake moisture and cloth washing. Although steam injection for
further dewatering shall not be applied at this stage, the steam
cabin and related piping shall be provided.
The filtrate from the Pressure Disk Filter shall be fed to the Filtrate
Tank (BRF-TK-101) via the Filtrate Receiver Tank (BRF-TK-107A andBRF-TK-107B) by gravity and recycled to the last mud washing
stage. Mud cake from the Pressure Disk Filter shall be conveyed to
the Cake Yard by the two (2) Belt Conveyers (BRF-BC-101 and BRF-
BC-102 depicted in Drawing No. BRF-100-0101-A1). The piled cake
in the Cake Yard will be periodically transported to the Bauxite
Residue Dumping Site by trucks. Air Compressors (BRF-CP-101 to
BRF-CP-109 depicted in Drawing No. BRF-100-0103-A1) shall be
provided near the Pressure Disk Filters.
The operation of the mud filtration stage shall be controlled with
local panel switches and shall be monitored at the Central Control
Room (CCR).
The treatment facility for seepage water and rainy sewerage from
area where bauxite residue will be dumped, shall be provided at
the appropriate location in the Bauxite Residue Dumping Site
based on the attached PFD (Drawing No. B-W-A-002-003) andEquipment List. Electric power for this facility shall be supplied
from Substation in Mining Site. Signal of indication and alarm of the
facility shall be sent to CCR.
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11.2.8.2 Plot Plan
Plot Plans for the Liquor Clarification Process are attached inChapter 11.2.4 for the WTNCs reference.
11.2.8.3 Process Flow Diagram
Process Flow Diagrams for the Liquor Clarification Process are
attached in Chapter 11.2.2 for the WTNCs reference.
11.2.8.4 Piping and Instrument Diagram
Piping and Instrument Diagrams for the Liquor Clarification Process
are attached in Chapter 11.2.3 for the WTNCs reference.
11.2.8.5 Heat & Mass Balance Sheet
Heat & Mass Balance for the Liquor Clarification Process shall be
referred to Table 10-3-2-5-1 and 10-3-2-5-2 attached in Chapter
11.2.1 for the WTNCs reference.
11.2.8.6 Equipment List
Equipment List for the Liquor Clarification Process is attached in
Chapter 11.7 for the WTNCs reference.
11.2.8.7 Technical Requirements
1) Technical requirements for all equipment shall be referred toEquipment List attached in Chapter 11.7. And the technical
requirements for main equipment shall be referred to drawings
also attached in Chapter 11.2.5 and 11.2.6.
2) The maintenance manholes and access doors of tanks shall be
provided based on each P&ID.
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3) The height of each outlet of the Flash Tank (BDH-FT-203) and
the Flash Tank (VHI-FT-104) shall be referred to Drawing Nos. B-
P-A-0501-004 and B-P-A-0501-016, respectively.
4) The quantities of piping with 150 mm and larger in nominal
diameter shall be minimized.
5) As no drawings of small tanks with the volume not exceeding
100 m3 and their agitators are attached, the WTNC shall provide
them based on Drawing Nos. B-P-V-0300-023 and B-P-V-0300-
025.
6) The Evaporator described in Subsection 11.2.8.1 is based on
the design basis of VRCE designed and manufactured by Sumiju
Plant Engineering Co., LTD. However, the WTNC may provide
the different type of evaporator designed based on the
following design conditions and manufactured strictly.
a) Steam Pressure of Plant Liquor
P = (0.068046)(10^(6.733(2057.6+0.2084N/0.891.0
106/80)/(273+T))
Where: P: Steam pressure (atm)
N: Caustic concentration (g/l)
T: Temperature (C)
b) Feed Liquor
Temperature T = 85C
Caustic Concentration N (aOH) = 160 gpl
Dissolved Al2O3 (l) = 75 gpl
Solid Al2O3 (s) = 0 gpl
Specific Gravity = 1.220
Specific Heat = 0.850
c) Amount of Evaporation = 10 tons per hour
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