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GROUP 10
Abdullah Ahmad, Andrew Cole, Arani Elanganathan, Chun − Heng
Huang, Jen – Yueh Hu, Joseph I. Ogun, Mohamad Raihaan,
Olajumoke Shonubi, Sara Al − Jebari
Supervised by Prof. Colin Webb
Ammonia Production
(1200 TPD Capacity)
DESIGN PHILOSOPHY
 To maximise energy recovery from exothermic
reactions in the process
 Worst case scenario assumed
 Overdesign of equipments to compensate for
uncertainty of design parameters and allow for
additional capacity
 Inherently safe design features and BAT
employed
PRESENTATION OUTLINE
 Process Outline
 Justifying the Omission of a Pre–reformer
 Unit features that are unique to our plant
 Plant Layout
 Environmental Sustainability
 Safety Considerations
 Energy Efficiency
 Control System
 Economic Analysis
R-1
S-1
R-3 R-4
S-6
S-4
S-8 S-9 S-12
Desulphurisation
R-5
R-6
S-17
R-7
R-9
S-22
S-13
E-4
S-15
S-18
E-6
S-20
Primary
Reformer
Secondary -
Reformer
High Shift Reactor Low Shift Reactor
BFW
E-1
S-3
R-2
S-5
S-11
R-8
S-21
Absorber
Stripper
Methanation
Ammonia Synthesis Flow Sheet – Group 10
Carbon dioxide
Mixer
S = Stream
R = Reactor
E = Heat Exchanger
F = Flash Drum
X = Surge Tank
BFW = Boiling Feed Water
C-1
S-10
S-14
E-5
S-16
Carbon dioxide
Removal
Hydrogen
Natural Gas
S-2
Air
S-19
R-10
R-11
E-10
F-2
F-1
C-2 C-3 C-4
F-3
F-4
C-5
C-6
S-26 S-27 S-28
S-24
S-29
S-31
S-32
S-33
S-35
S-37
S-39
S-36
S-40
S-46
S-43
S-41
S-42
S-44
F-5
S-45
F-6
S-47
S-49
X-1
S-52
S-30
S-50
Purge
S-51
Pure Ammonia
S-48
S-38
E-8
Mixer
Splitter
Mixer
Ammonia Converter
Separation Unit
S-7
E-2
S-6A
E-3
S-23
E-7
S-25
E-9
S-34
Boiler
H2O
PROCESS FLOW SHEET
Desulphuriser
Reformers
Ammonia
converters
CO2 removal
Methanator
Compression
Refrigeration
Shift reactors
JUSTIFYING THE OMISSION OF A PRE -
REFORMER
 Used mostly in plants with heavy gas feeds
 To reduce carbon formation reformer tubes
 To use up remaining heat energy in flue gas to promote
reforming reaction
 Flue gas heat used instead for :
 Combustion air preheat
 Steam duties
 No appreciable improvement in overall energy
consumption
PRIMARY REFORMER
 Uhde cold outlet manifold
system
 Prevents premature failure of the
tubes
 None required replacement from
1968 – 1994 (McKetta, 1994)
 Recommendation
 Explore potential rate of carbon
formation
 Lower S/C ratio – reduced
operating cost
300 600 900
Skin Temperature (°C)
HAZOP ON PRIMARY REFORMER
 Some highlighted plant modifications
 Furnace fuel inlet
 Fail close and pressure relief valves
 Fuel composition analyser
 Control loops
 Combustion air inlet
 Oxygen analyser
SECONDARY REFORMER
 In the event of controlled relief
response being triggered
 Quenching chamber containing
water to neutralise unreacted
reactants
 Pipes from combustion zone to
quenching chamber
 Sprinklers and relief vents
AMMONIA SYNTHESIS P&ID
 Split into two reactors
AMMONIA SYNTHESIS LOOP
 Minimise wastage of synthesis gas in purge
 Minimise energy required to recycle synthesis
gas
 Minimise duty required for refrigeration
SYNTHESIS LOOP PFD
 Surge tank
 Variable operating conditions
 Usage of leftover methane/hydrogen stream
LAYOUT OF PLANT
Tank 1 Tank 2 Tank 3
Tank 5
Tank 4
Tank 1
Tank 3
D-2
PR
SR
LS
Canteens
Change House, Gym and Social Rooms
ABS
STP
MET
HS
FD
D-1
C-1
C-2
C-3
AC-2
REF
AC-1
Offices
CCR
(Centre of Control Room)
Laboratory
Maintenance Room
Fire Station
Medical Centre
Garden
Waste Treatment Tanks
Tank 2 Storage Tanks
Plant Warehouse for Product Storage
and for Other Purpose
Car Park
Security
Loading/Unloading
Area
STK
ENVIRONMENT/SUSTAINABILITY
 Ammonia production generates some environmental
impact
 Impacts can be minimised
 Gaseous emissions:
 Desulphuriser: H2S, ZnS, SO2
 Primary Reformer: CO2, Nox , SO2, CO
 Secondary Reformer: CO2 & CH4
 High & Low Temperature Shift: FeCr Catalyst, Cu, CO,CO2
 Carbon dioxide Removal: CO2 and MDEA solvent
 Methanation: CO
 Ammonia Synthesis and Recycle Loop: CH4, NH3, H2, N2 ,Ar
TO MINIMISE OR REDUCE THE ACID GAS
Wet scrubber
low Nox burners
Electrostatic precipitator
AMMONIA PLANT LIQUID EFFLUENT
 Ammonia liquid emissions can be limited by
applying good management practices
 Stripping to reduce ammonia in purge effluent
 Other effluents include
 Boiler blowdown
 Cooling water blowdown.
 These effluents are recycled and reused
 Limits amount requiring treatment
SAFETY CONSIDERATIONS
 Personal Protective Equipment (PPE)
 COSHH
 Hydrogen Sulphide and Nickel Carbonyl - Toxic
 Natural gas and Hydrogen – Potentially explosive
 MDEA – Irritant
 Flammability limits
 Flammability limits calculated at exit of each major section
 Overpressure
 Control valves
HEAT EXCHANGER NETWORK
 Process integration saves ~£24M yr-1 heating costs
 Excess energy of 179 MW used to raise steam
783
783
600
613
443
313
490
288
P3
P1
c
P2
640
P4
-
C5
C4
C1 C3
C2
C
S6A
S5
S22
S48
S13
S17
S17
S33
S34
333
683
383
-
456
1262
616
450
689
490
- H
32333
5628
11511
44778
56306
14985
40250
68611
93056
H1
Heat Exchanger Network Design
Ammonia Synthesis Plant
kW kW
K
K
CONTROL ROOM & SOFTWARE USED
 6 operators to work in plant; 3 shifts per day;
 Proposed control system: Honeywell’s Profit Controller (Robust Multivariable
Predictive Controller)
 Real time system to calculate current output
Perturbed
Normal
Operation
Upset
Shut Down
Control
System
Operator
Intervention
ESD
X
X
X
X
X
X
X = Alarm
X
X
X
X
X
X
X
Image from:
Brown, D., & O'Donnell, M. (199?). Too much of a good thing? Alarm management experience in BP oil. Part 1: Generic
Problems with DCS Alarm Systems. BP .
ECONOMIC ANALYSIS - PROFITABILITY
 Total Capital Investment needed ≈ £134 million
 Pre-tax Profit ≈ £38 million
 The plant can achieve an internal rate of return of 20%
CONCLUSION
 Extra ~42 TPD capacity from 588 TPD natural gas
 Achieve IRR of 20% over 10 year operating period
 Excess energy of ~ 179 MW
 Environmentally sustainable, surpassing UK & Welsh
legislation requirements
 Safe operating conditions
 Plant layout takes into account minimum safe distances
THANK YOU FOR LISTENING.
ANY QUESTIONS?
IMPORTANT CONTROL LOOPS
 The temperature of the stream entering the tubes of the primary reformer;
 The ammonia reactor temperature of the outlet gas after each compression
ECONOMIC ANALYSIS - PROFITABILITY
Bachelor’s Thesis

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Bachelor’s Thesis

  • 1. GROUP 10 Abdullah Ahmad, Andrew Cole, Arani Elanganathan, Chun − Heng Huang, Jen – Yueh Hu, Joseph I. Ogun, Mohamad Raihaan, Olajumoke Shonubi, Sara Al − Jebari Supervised by Prof. Colin Webb Ammonia Production (1200 TPD Capacity)
  • 2. DESIGN PHILOSOPHY  To maximise energy recovery from exothermic reactions in the process  Worst case scenario assumed  Overdesign of equipments to compensate for uncertainty of design parameters and allow for additional capacity  Inherently safe design features and BAT employed
  • 3. PRESENTATION OUTLINE  Process Outline  Justifying the Omission of a Pre–reformer  Unit features that are unique to our plant  Plant Layout  Environmental Sustainability  Safety Considerations  Energy Efficiency  Control System  Economic Analysis
  • 4. R-1 S-1 R-3 R-4 S-6 S-4 S-8 S-9 S-12 Desulphurisation R-5 R-6 S-17 R-7 R-9 S-22 S-13 E-4 S-15 S-18 E-6 S-20 Primary Reformer Secondary - Reformer High Shift Reactor Low Shift Reactor BFW E-1 S-3 R-2 S-5 S-11 R-8 S-21 Absorber Stripper Methanation Ammonia Synthesis Flow Sheet – Group 10 Carbon dioxide Mixer S = Stream R = Reactor E = Heat Exchanger F = Flash Drum X = Surge Tank BFW = Boiling Feed Water C-1 S-10 S-14 E-5 S-16 Carbon dioxide Removal Hydrogen Natural Gas S-2 Air S-19 R-10 R-11 E-10 F-2 F-1 C-2 C-3 C-4 F-3 F-4 C-5 C-6 S-26 S-27 S-28 S-24 S-29 S-31 S-32 S-33 S-35 S-37 S-39 S-36 S-40 S-46 S-43 S-41 S-42 S-44 F-5 S-45 F-6 S-47 S-49 X-1 S-52 S-30 S-50 Purge S-51 Pure Ammonia S-48 S-38 E-8 Mixer Splitter Mixer Ammonia Converter Separation Unit S-7 E-2 S-6A E-3 S-23 E-7 S-25 E-9 S-34 Boiler H2O PROCESS FLOW SHEET Desulphuriser Reformers Ammonia converters CO2 removal Methanator Compression Refrigeration Shift reactors
  • 5. JUSTIFYING THE OMISSION OF A PRE - REFORMER  Used mostly in plants with heavy gas feeds  To reduce carbon formation reformer tubes  To use up remaining heat energy in flue gas to promote reforming reaction  Flue gas heat used instead for :  Combustion air preheat  Steam duties  No appreciable improvement in overall energy consumption
  • 6. PRIMARY REFORMER  Uhde cold outlet manifold system  Prevents premature failure of the tubes  None required replacement from 1968 – 1994 (McKetta, 1994)  Recommendation  Explore potential rate of carbon formation  Lower S/C ratio – reduced operating cost 300 600 900 Skin Temperature (°C)
  • 7. HAZOP ON PRIMARY REFORMER  Some highlighted plant modifications  Furnace fuel inlet  Fail close and pressure relief valves  Fuel composition analyser  Control loops  Combustion air inlet  Oxygen analyser
  • 8. SECONDARY REFORMER  In the event of controlled relief response being triggered  Quenching chamber containing water to neutralise unreacted reactants  Pipes from combustion zone to quenching chamber  Sprinklers and relief vents
  • 9. AMMONIA SYNTHESIS P&ID  Split into two reactors
  • 10. AMMONIA SYNTHESIS LOOP  Minimise wastage of synthesis gas in purge  Minimise energy required to recycle synthesis gas  Minimise duty required for refrigeration
  • 11. SYNTHESIS LOOP PFD  Surge tank  Variable operating conditions  Usage of leftover methane/hydrogen stream
  • 12. LAYOUT OF PLANT Tank 1 Tank 2 Tank 3 Tank 5 Tank 4 Tank 1 Tank 3 D-2 PR SR LS Canteens Change House, Gym and Social Rooms ABS STP MET HS FD D-1 C-1 C-2 C-3 AC-2 REF AC-1 Offices CCR (Centre of Control Room) Laboratory Maintenance Room Fire Station Medical Centre Garden Waste Treatment Tanks Tank 2 Storage Tanks Plant Warehouse for Product Storage and for Other Purpose Car Park Security Loading/Unloading Area STK
  • 13. ENVIRONMENT/SUSTAINABILITY  Ammonia production generates some environmental impact  Impacts can be minimised  Gaseous emissions:  Desulphuriser: H2S, ZnS, SO2  Primary Reformer: CO2, Nox , SO2, CO  Secondary Reformer: CO2 & CH4  High & Low Temperature Shift: FeCr Catalyst, Cu, CO,CO2  Carbon dioxide Removal: CO2 and MDEA solvent  Methanation: CO  Ammonia Synthesis and Recycle Loop: CH4, NH3, H2, N2 ,Ar
  • 14. TO MINIMISE OR REDUCE THE ACID GAS Wet scrubber low Nox burners Electrostatic precipitator
  • 15. AMMONIA PLANT LIQUID EFFLUENT  Ammonia liquid emissions can be limited by applying good management practices  Stripping to reduce ammonia in purge effluent  Other effluents include  Boiler blowdown  Cooling water blowdown.  These effluents are recycled and reused  Limits amount requiring treatment
  • 16. SAFETY CONSIDERATIONS  Personal Protective Equipment (PPE)  COSHH  Hydrogen Sulphide and Nickel Carbonyl - Toxic  Natural gas and Hydrogen – Potentially explosive  MDEA – Irritant  Flammability limits  Flammability limits calculated at exit of each major section  Overpressure  Control valves
  • 17. HEAT EXCHANGER NETWORK  Process integration saves ~£24M yr-1 heating costs  Excess energy of 179 MW used to raise steam 783 783 600 613 443 313 490 288 P3 P1 c P2 640 P4 - C5 C4 C1 C3 C2 C S6A S5 S22 S48 S13 S17 S17 S33 S34 333 683 383 - 456 1262 616 450 689 490 - H 32333 5628 11511 44778 56306 14985 40250 68611 93056 H1 Heat Exchanger Network Design Ammonia Synthesis Plant kW kW K K
  • 18. CONTROL ROOM & SOFTWARE USED  6 operators to work in plant; 3 shifts per day;  Proposed control system: Honeywell’s Profit Controller (Robust Multivariable Predictive Controller)  Real time system to calculate current output Perturbed Normal Operation Upset Shut Down Control System Operator Intervention ESD X X X X X X X = Alarm X X X X X X X Image from: Brown, D., & O'Donnell, M. (199?). Too much of a good thing? Alarm management experience in BP oil. Part 1: Generic Problems with DCS Alarm Systems. BP .
  • 19. ECONOMIC ANALYSIS - PROFITABILITY  Total Capital Investment needed ≈ £134 million  Pre-tax Profit ≈ £38 million  The plant can achieve an internal rate of return of 20%
  • 20. CONCLUSION  Extra ~42 TPD capacity from 588 TPD natural gas  Achieve IRR of 20% over 10 year operating period  Excess energy of ~ 179 MW  Environmentally sustainable, surpassing UK & Welsh legislation requirements  Safe operating conditions  Plant layout takes into account minimum safe distances
  • 21. THANK YOU FOR LISTENING. ANY QUESTIONS?
  • 22. IMPORTANT CONTROL LOOPS  The temperature of the stream entering the tubes of the primary reformer;  The ammonia reactor temperature of the outlet gas after each compression
  • 23. ECONOMIC ANALYSIS - PROFITABILITY

Editor's Notes

  1. Made of carbon steel, there are no high-alloy pig tails or outlet manifolds which work at creep condition Prevents premature failure of the components due to creep and embrittlement therefore there are no thermal expansion problems it has an almost unlimited service life (Uhde, 2007) with no maintenance required other than painting The potential rate of carbon formation in the proposed primary reformer should be explored. This is recommended because the sensitivity studies carried out indicate that an increase of the S/C ratio to 4 gives a 10% increase in the amount of energy required for the reaction and a decrease to 2, gives a 10% reduction in the required energy. There may be a potential here for reduction in operating costs and hence increased profitability if further investigation suggests that a lower S/C ratio than that proposed in this design (3.1) can be operated at without compromising the reformer tube life.
  2. Some of the highlighted plant modifications Furnace fuel Fail close valves for fuel flow, control loops monitoring temperature of reformer tubes, flue gas composition and fuel to air ratio. Install pressure relief valve to furnace fuel pipe, S1, to direct the fuel to a large reserve tank Install a fuel composition analyser to enable control of fuel flow rate and air flow rate, to give the heat required and complete combustion respectively Install a nitrogen blanket on the fuel tank Combustion air Install a pressure controller on the combustion air line. Pressure relief valve to atmosphere. Install an oxygen analyser on the inlet air flow line to monitor air flow in terms of oxygen flow rate.
  3. Acid gas that might escape during the process are (say for each process) are: (refer to Process in slide) Table each of gas emission and impact (refer to table): H2S – if hydrogen sulphide reacts with atmospheric water and oxygen it will produce sulphuric acid. The impact of hydrogen sulphide is acid rain and it will lower the pH of soil and freshwater in the ground. ZnS – zinc sulphide is very toxic to human. CO2 – Carbon dioxide is considered as first important gas in greenhouse gasses (GHGs) which leads to global warming. This gas is potentially having a major effect on climate change in atmosphere. Nox – Nitrogen oxides also contributes to the acid rain and depletion of the ozone. It is also one of major greenhouse gasses (GHGs). If Nitrogen dioxide goes to the air, it will can react with organic peroxy radicals (formed from the breakdown of Volatile Organic Compounds in the air) to form PANs (peroxyacetyl nitrates) (The Environment Agency, 2010). SO2 – Sulphur dioxide is one of chemical gas that caused acid rain. This gas can dissolves in water droplets in clouds and potentially will make the rain more acidic. CO – Carbon monoxide is man-made gas which reacts with other acid gases to produce ground level ozone. This gas has a direct impact to the human health. CH4 – Methane is considered as second important gas in greenhouse gasses (GHGs) after carbon dioxide which leads to global warming.
  4. These gasses can be minimise or reduce by some common methods. Those methods are like flue gas recirculation, wet scrubber, cyclone separators, baghouse, low Nox burners, selective and non-selective catalytic reduction (SCR and NSCR) and electrostatic precipitator (ESP). These gasses can be minimise or reduce by some common methods. Those methods are like flue gas recirculation, wet scrubber, cyclone separators, baghouse, low Nox burners, selective and non-selective catalytic reduction (SCR and NSCR) and electrostatic precipitator (ESP). These gasses can be minimise or reduce by some common methods. Those methods are like flue gas recirculation, wet scrubber, cyclone separators, baghouse, low Nox burners, selective and non-selective catalytic reduction (SCR and NSCR) and electrostatic precipitator (ESP).