CHEMICAL PROCESS ENGINEERING · OFFSHORE GAS MONETIZATION · CONCEPTUAL DESIGN · 2026

Offshore methane toexport-grade methanol

A complete conceptual process-design case study converting a 600 kg/h methane-rich offshore gas stream into high-purity methanol through steam reforming, syngas conditioning, four-stage compression, three adiabatic synthesis reactors, recycle and purge control, flash separation and final distillation.

The model connects thermodynamic validation, kinetic reactor design, mass and energy balances, preliminary equipment sizing, CAPCOST economics, uncertainty analysis and environmental hotspots in one auditable engineering chain.

Aspen HYSYSPeng–RobinsonRPlug / PFRRGibbs + REquilRadFracCAPCOSTMonte Carlo · 50,000 runsOffshore conceptual design

Academic team project. The plant, equipment sizes and economics are conceptual and are not a FEED, safety case or investment recommendation.

Process snapshot
ASPEN MODEL · v1.0
Technically consistentEconomic gap
1,025.4 kg/h
Methanol product
99.86 wt%
Product purity
95.5%
Reformer CH₄ conversion
−$6.603m
Base-case NPV
· Thermal conditioning· Reforming· Synthesis· Purification
EXECUTIVE ENGINEERING SNAPSHOT

Process performance at a glance

Ten reconciled indicators summarize the design basis, conversion chain, resource integration and economic conclusion. Values are taken from the stream table, equipment design and CAPCOST model.

600 kg/h
Methane-rich feed
1,025.4 kg/h
Methanol product
8.20 kt/y
Reconciled annual production
99.86 wt%
Product purity
95.5%
Reformer CH₄ conversion
75.5%
Reactive-carbon conversion in synthesis
1,188.5 kg/h
Internal water recycle
50.2%
Reported energy efficiency
$7.57m
Fixed capital investment
−$6.603m
Base-case NPV
4%
Synthesis-loop purge fraction
40 bar
Synthesis inlet pressure
50,000
Monte Carlo samples
0%
Simulated probability of positive NPV

Annual production is reconciled as 1,025.368 kg/h × 8,000 h/y = 8.203 kt/y. The report conclusion contains a conflicting 8.97 kt/y value; the stream-table calculation is used here.

A technically coherent flowsheet with a structural economic shortfall

The process reaches the methanol specification and demonstrates a complete engineering workflow, but the base case cannot recover the investment under the adopted scale, product price and capital assumptions.

Technical performance
  • · Steam reformer: 95.5% CH₄ conversion.
  • · Methanol product: 99.86 wt% purity.
  • · Three-reactor synthesis train with recycle and interstage cooling.
Economic finding
  • · Revenue: $3.277m/y.
  • · COMd: $3.213m/y.
  • · NPV: −$6.603m.
  • · No payback or discounted return rate.
Priority redesign levers
  • · Reduce reformer and R-203 capital intensity.
  • · Intensify heat integration.
  • · Reassess scale and methanol value.
  • · Recover value from purge gases.
Product specification — metMass-balance chain — reconciledEnergy integration — partialEconomic viability — not achieved
PROCESS ARCHITECTURE

An auditable chain from feed basis to investment decision

Each step produces a defined engineering object: composition, stream, reactor model, equipment duty, separation specification, cost estimate, uncertainty result or environmental finding.

1
Feed characterization
  • · Input: 600 kg/h gas at 40 °C and ≈10 bar.
  • · Composition: 94.27 mol% CH₄, 5.00 mol% CO₂, 0.73 mol% H₂O.
  • · Output: saturated methane-rich feed basis.
2
Steam and water integration
  • · Fresh water pumped from 1 to 10 bar.
  • · Internal recycle: 1,188.5 kg/h.
  • · Reported steam/carbon design ratio: 2.78.
  • · Output: conditioned reformer feed.
3
Steam methane reforming
  • · RPlug/PFR, Peng–Robinson.
  • · 48 parallel catalyst tubes.
  • · Output: H₂/CO/CO₂ syngas at 855.6 °C.
4
Cooling and water knock-out
  • · Heat recovery followed by cooling to 45 °C.
  • · V-101 separates water-rich liquid from dry syngas.
  • · Output: 1,356.6 kg/h dry syngas.
5
Four-stage compression
  • · 10 → 16 → 24 → 32 → 40 bar.
  • · Interstage cooling limits discharge temperature.
  • · Output: synthesis-pressure syngas.
6
Methanol synthesis train
  • · Three adiabatic RPlug reactors.
  • · Interstage cooling and kinetic model.
  • · Output: 75.5% reactive-carbon conversion.
7
Recycle, purge and purification
  • · High-pressure flash.
  • · 96% recycle / 4% purge.
  • · Second flash and RadFrac distillation.
  • · Output: 99.86 wt% methanol.
8
Decision layer
  • · Mass and energy balance.
  • · Equipment sizing.
  • · CAPCOST.
  • · Monte Carlo.
  • · Environmental hotspot assessment.
FEED → REFORMING → SYNGAS → COMPRESSION → SYNTHESIS → RECYCLE → DISTILLATION → ECONOMICS
Process-flow schematic
Gas feed
  • 600 kg/h
  • 40 °C
  • 10.1 bar
Water preparation
  • P-101
  • fresh + recycle water
Steam reformer
  • H-101 / R-101
  • 550 → 855.6 °C
  • 95.5% CH₄ conv.
Heat recovery + cooler
  • E-101 / E-102
  • 855.6 → 45 °C
Water flash
  • V-101
  • 1,188.5 kg/h water recycle
Compression train
  • C-101 to C-104
  • 10 → 40 bar
Synthesis train
  • R-201 → R-202 → R-203
  • interstage cooling
High-pressure flash
  • V-201
  • recycle + 4% purge
Pressure let-down
  • XV-301
Low-pressure flash
  • V-202
Distillation
  • T-301 / RadFrac
  • 27 stages · 25 trays
Methanol product
  • 1,025.4 kg/h
  • 99.86 wt%
  • 57.4 °C
— main process— water recycle— heat recovery- - purge
DESIGN BASIS

A constrained offshore feed converted through an indirect syngas route

The design begins with a methane-rich saturated gas stream and treats water recycle, high-temperature reforming, synthesis pressure and final purity as the central process constraints.

Design basis
Feed flow
600 kg/h
Feed temperature
40 °C
Feed pressure
10.1 bar
Feed phase
Vapor
CH₄
94.27 mol%
CO₂
5.00 mol%
H₂O
0.73 mol%
Fresh water
756.64 kg/h
Recycled water
1,188.46 kg/h
Combined water
1,945.10 kg/h
Operating time
8,000 h/y
Target methanol purity
99.86 wt%
Reaction system
  1. 1.CH₄ + H₂O ⇌ CO + 3H₂Reforming
  2. 2.CO + H₂O ⇌ CO₂ + H₂Water-gas shift
  3. 3.CO + 2H₂ ⇌ CH₃OHMethanol synthesis
  4. 4.CO₂ + 3H₂ ⇌ CH₃OH + H₂OMethanol synthesis
  5. 5.CO₂ + H₂ ⇌ CO + H₂OReverse water-gas shift

Assumption. The model is steady state and uses a Peng–Robinson property package. The reported steam-to-carbon ratio of 2.78 is preserved as a design assumption and is flagged for independent cross-check in QA.

STEAM METHANE REFORMING

High conversion driven by temperature, steam and distributed heat input

The reformer is modeled as an RPlug/PFR with a supported Rh/MgO–Al₂O₃ catalyst, a high-temperature axial profile and a distributed heat-flux strategy intended to sustain strongly endothermic reactions.

R-101
Block · RPlug / PFR
48
Parallel catalyst tubes
6.0 m
Tube length
0.1016 m
Tube diameter
2,595.6 kg
Reforming catalyst mass
550 °C
Reactor feed
855.6 °C
Reactor outlet
95.5%
CH₄ conversion
Reformer model
Thermodynamic packagePeng–Robinson
Reactor blockRPlug
Catalyst density2,355.2 kg/m³
Bed porosity0.528
Tube count48
Tube length6 m
Tube diameter0.1016 m
Approx. catalyst volume2.3349 m³
Reported residence time7.97 × 10⁻⁴ s
Feed pressure10.1 bar
Outlet pressure10.1 bar (simplified)
Axial heat flux

Heat input is front-loaded to match the endothermic demand and avoid excessive downstream firing.

Reformer outlet composition (stream 4)
H₂
50.42%
H₂O
32.87%
CO
10.20%
CO₂
5.79%
CH₄
0.71%
Temperature
  • · Higher temperature increases methane conversion.
  • · Selected design region: approximately 850 °C.
Pressure
  • · Lower pressure favors reforming equilibrium.
  • · Around 10 bar avoids additional upstream expansion/compression.
Coke mitigation
  • · Steam excess and Rh-based catalyst support mitigate carbon deposition.
  • · Catalyst deactivation is not dynamically modeled.
SYNGAS CONDITIONING

Water removal and staged compression protect the synthesis section

The reformer effluent is heat-integrated, cooled, flashed and compressed in four stages with intercooling before entering the high-pressure methanol loop.

Water knock-out
Reformer effluent
2,545.09 kg/h
Heat-recovery outlet
560.1 °C
Final cooling temperature
45 °C
V-101 pressure
10 bar
Recycled water
1,188.46 kg/h
Dry syngas
1,356.63 kg/h

Removing most of the water before synthesis limits equilibrium penalty and catalyst exposure to excess water.

Dry-syngas composition (stream 8)
  • H₂74.47 mol%
  • CO15.07 mol%
  • CO₂8.56 mol%
  • CH₄1.05 mol%
  • H₂O0.85 mol%
Compression train

Intercooling is used to keep compressor discharge temperatures below the adopted industrial safety limit.

METHANOL SYNTHESIS

Three adiabatic reactors, interstage cooling and a controlled recycle loop

The synthesis section uses a Cu/Zn/Al₂O₃ kinetic model in three RPlug reactors. Cooling between reactors restores equilibrium driving force, while recycle increases overall reactant utilization.

40 bar
Nominal synthesis inlet
200 °C
First-reactor feed
3
Adiabatic reactors
75.5%
Reactive-carbon conversion
4%
Purge fraction
2,370.90 kg/h
Recycle gas
98.79 kg/h
Purge gas
3,727.53 kg/h
Mixed synthesis feed
R-201
  • Diameter: 1 m
  • Length: 2 m
  • Inlet: 200 °C, 40 bar
  • Outlet: 255.4 °C, 39.9 bar
  • Reported per-reactor conversion field: 40.5%
ΔT 55.4 °C
R-202
  • Diameter: 1 m
  • Length: 6 m
  • Inlet: 200 °C, 39.9 bar
  • Outlet: 229.8 °C, 39.6 bar
  • Reported per-reactor conversion field: 32.4%
ΔT 29.8 °C
R-203
CAPEX hotspot
  • Diameter: 3 m
  • Length: 12 m
  • Inlet: 180 °C, 39.6 bar
  • Outlet: 202.3 °C, 39.6 bar
  • Reported per-reactor conversion field: 39%
ΔT 22.3 °C
Reactor inlet vs. outlet temperature

Per-reactor conversion fields are reported individually. They must not be summed — overall synthesis conversion is 75.5%.

Recycle and purge governance
  • High-pressure flash gas2,469.69 kg/h
  • Recycle · 96%2,370.90 kg/h
  • Purge · 4%98.79 kg/h
Notes

The 4% purge is the lowest reported fraction that prevented hydrogen accumulation while retaining the target conversion.

Risk. The purge contains H₂, CO, CO₂, CH₄ and trace methanol. It requires controlled handling — flare, thermal oxidation or a future value-recovery route.

DOWNSTREAM PURIFICATION

Two flashes and RadFrac distillation achieve the methanol specification

A high-pressure flash separates recycle gas from crude liquid. After pressure let-down, a second flash removes residual light gases before final methanol–water separation in a distillation column.

V-201 · High-pressure flash
  • · 30 °C
  • · 39.6 bar
  • · Liquid: 1,257.85 kg/h
  • · Gas: 2,469.69 kg/h
XV-301 · Pressure let-down
  • · 39.6 → 1.1 bar
  • · Outlet ≈ 31 °C
V-202 · Low-pressure flash
  • · Liquid: 1,255.91 kg/h
  • · Gas purge: 1.94 kg/h
  • · Liquid CH₃OH: 81.686 wt%
T-301 · RadFrac
  • · 27 Aspen stages
  • · 25 physical trays
  • · 0.75 m diameter
  • · 20 m height
Final design values
Final RadFrac reflux ratio1.03829
Distillate/feed ratio0.71656
Feed stage (shortcut)≈ 19.5
Distillate temperature57.4 °C
Bottom temperature100.2 °C
Methanol recovery≈ 99.7%
Product purity99.86 wt%
Product flow1,025.368 kg/h
Bottom-water flow229.162 kg/h
Model evolution
DSTWU minimum reflux0.30
DSTWU preliminary actual reflux0.36
DSTWU minimum stages8.54
DSTWU estimated actual stages26.98
Final modelRadFrac
Final reflux ratio1.03829
DSTWU shortcut sizing → RadFrac rigorous specification

The second flash is retained because bypassing it failed to meet the target purity at the desired recovery.

MASS, WATER & ENERGY BALANCES

The key streams expose where material, heat and recycle circulate

The website does not reproduce all 37 streams in the main view. It presents the controlling streams and provides an expandable table for technical review.

13 of 13 rows
StreamServiceTPPhaseMass flowCH₄H₂OH₂COCO₂CH₃OH
1Methane-rich saturated feed40 °C10.1 barVapor600 kg/h94.27%0.73%0%0%5%0%
3Reformer feed550 °C10.1 barVapor2,545.17 kg/h22.76%76.03%0%0%1.21%0%
4Reformer effluent855.6 °C10.1 barVapor2,545.09 kg/h0.71%32.87%50.42%10.2%5.79%0%
7Recovered process water45 °C10 barLiquid1,188.46 kg/h0%100%0%0%0%0%
8Dry syngas after V-10145 °C10 barVapor1,356.63 kg/h1.05%0.85%74.47%15.07%8.56%0%
15Compressed fresh syngas93.6 °C40 barVapor1,356.63 kg/h1.05%0.85%74.47%15.07%8.56%0%
16Mixed synthesis feed with recycle200 °C40 barVapor3,727.53 kg/h4.25%0.18%90.1%2.74%2.36%0.38%
21Three-reactor train effluent202.3 °C39.6 barVapor3,727.53 kg/h4.61%1.67%87.79%0.28%1.08%4.58%
24Crude methanol liquid30 °C39.6 barLiquid1,257.85 kg/h0.06%28.15%0.08%0%0.14%71.58%
32Synthesis-loop purge30 °C39.6 barVapor98.79 kg/h4.89%0.04%93.19%0.29%1.13%0.45%
33Synthesis recycle gas30 °C39.6 barVapor2,370.9 kg/h4.89%0.04%93.19%0.29%1.13%0.45%
31Purified methanol57.4 °C1 barLiquid1,025.37 kg/h0%0.01%0%0%0.1%99.89%
30Water-rich column bottoms100.2 °C1 barLiquid229.16 kg/h0%99.5%0%0%0%0.5%
Water balance
Fresh
756.64 kg/h
Recycled
1,188.46 kg/h
Combined
1,945.10 kg/h
Recycle share: 61.10%. Fresh-water replacement avoided: 1,188.46 kg/h.

This is an internal process recycle, not a full offshore water-system design.

Energy panel
  • Reported process heat-transfer rate1,025 kW
  • Reported energy efficiency50.2%
  • E-101 recovered heat duty143 kW
  • E-204 recovered heat duty63 kW
  • Reformer furnace duty used in CAPCOST10,800 MJ/h
  • Actual reformer duty (cost appendix)8,762 MJ/h
  • HP steam consumption (environmental)741 kg/h

Optimization opportunity. Further heat-integration opportunities remain. The report identifies additional exchanger configurations with reported exchanger-match opportunities of approximately 24.69% and 14.29% for selected matches. These are not whole-plant guaranteed savings.

TECHNO-ECONOMICS

Positive operating cash flow does not offset the capital burden

CAPCOST and Turton-style factors were used for preliminary equipment and manufacturing-cost estimates. The base case assumes methane is available inside the offshore battery limit at zero purchase cost.

Assumptions
Operating time
8,000 h/y
Operating life
10 y
Construction
3 y
FCIL distribution
30% / 40% / 30%
Discount rate after tax
16%
Marginal tax
35%
Methanol price
$400/t
Residual value
10% of FCIL
Methane cost
$0 inside battery limit
Water price
$2.50/m³

Warning: assigning an opportunity cost to methane would make the economics less attractive.

CAPEX distribution
Capital summary
  • Total Module Cost$6.010m
  • FCIL / Total Grass Roots Cost$7.570m
  • Working capital$3.605m
  • Land$0.151m
  • Pre-operational outlay$11.326m
Utility-cost distribution
$3.277m/y
Revenue
$0.0157m/y
Raw materials
$1.130m/y
Utilities
$0.160m/y
Operating labor (exec)
$3.213m/y
COMd
$0.063m/y
Pre-depreciation margin
$0.279m/y
After-tax operating cash flow

Methodology note. The detailed CAPCOST appendix also contains a separate labor calculation near $0.994m/y. The executive result table reports $0.160m/y. The website preserves the official executive COMd result and flags the labor reconciliation in QA rather than silently mixing both figures.

Discounted cash flow
−$6.603m
NPV
−$4.018m
Final non-disc.
−5.31%/y
ROROI
Not defined
DCFROR
Not achieved
Payback
Monte Carlo uncertainty
Precomputed summary from 50,000 samples. No runtime randomization.
min -11.86
P5 -9.12
median -6.42
mean -6.43
P95 -3.77
max -0.62
−12 MMUSD
0 MMUSD
50,000
Samples
0%
P(NPV > 0)
−6.603 MMUSD
Base-case NPV
−0.619 MMUSD
Best simulated NPV

The entire reported NPV distribution remains negative within the adopted uncertainty ranges.

Sensitivity and break-even
Break-even price
≈ $800/t methanol
Break-even FCIL
≈ $0.98m
Required FCIL reduction
≈ 87%
ENVIRONMENTAL HOTSPOTS

Thermal utilities and the reformer furnace dominate the preliminary footprint

The environmental assessment is an order-of-magnitude calculation based on process energy demand and literature emission factors. Direct and indirect emissions must remain clearly separated.

741 kg/h
High-pressure steam
116 kg CO₂/h
Indirect steam-related emissions
0.93 kt CO₂/y
Annual indirect emissions
0.10 kg CO₂/kg MeOH
Normalized indirect footprint
581.8 kW
Reported reformer thermal demand
138 kg CO₂/h
Estimated direct furnace emissions
1.10 kt CO₂/y
Annual direct furnace emissions
1,188.5 kg/h
Water internally recycled
Emissions comparison

The two sources are shown separately and must not be presented as a verified cradle-to-gate carbon footprint.

Thermal hotspot
  • · Steam reforming is strongly endothermic.
  • · Furnace efficiency assumption: 85%.
  • · Natural-gas emission factor: 56 kg CO₂/GJ.
Purge-gas management
  • · Contains H₂, CO, CO₂, trace CH₄ and methanol.
  • · Requires controlled treatment.
  • · Suggested concepts: flare, thermal oxidizer, or future energy/value recovery.
Water stewardship
  • · 1,188.46 kg/h internal recycle.
  • · 61.1% of combined process water supplied by recycle.
  • · Bottom stream is approximately 99.5 mol% water.
  • · Offshore water logistics remain outside the conceptual battery limit.
Potential system benefit
  • · Conversion to liquid methanol may reduce direct platform methane flaring.
  • · This benefit is qualitative and is not quantified in the report.
MODELING METHODOLOGY

Thermodynamics, kinetics, separation and economics are linked explicitly

The model progresses from property-method validation to equilibrium screening, kinetic reactor design, rigorous separation, equipment sizing and uncertainty analysis.

1
P0 — Scope and battery limits

Feed, product, purge, water and conceptual offshore boundary.

Output: Design basis.
2
P1 — Feed saturation calculation

Antoine equation and Raoult-style ideal-gas calculation.

Output: 0.73 mol% water in feed.
3
P2 — Thermodynamic validation

Peng–Robinson versus pure-component data. NIST dataset 160 for H₂O–CH₃OH.

Output: Property-method rationale.
4
P3 — Reforming equilibrium screening

RGibbs sensitivity to pressure, temperature and steam.

Output: Reformer operating window.
5
P4 — Reforming kinetic model

RPlug with catalyst properties and distributed heat flux.

Output: 95.5% CH₄ conversion.
6
P5 — Syngas conditioning

Cooling, flash separation and water recycle.

Output: Dry syngas.
7
P6 — Methanol synthesis screening

REquil pressure/temperature analysis.

Output: 40 bar / 200 °C starting point.
8
P7 — Methanol kinetic reactor train

Three adiabatic RPlug reactors and interstage cooling.

Output: 75.5% reactive-carbon conversion.
9
P8 — Downstream specification

Two flashes, DSTWU shortcut, then RadFrac.

Output: 99.86 wt% methanol.
10
P9 — Decision analysis

Heat integration, preliminary sizing, CAPCOST, Monte Carlo and environmental hotspots.

Output: Technical/economic conclusion.
Thermodynamic validation
  • · Pure components: CO₂, CO, H₂, H₂O, CH₄, CH₃OH.
  • · Properties compared: heat capacity, vapor pressure, density.
  • · Binary validation: water–methanol; NIST dataset 160.
  • · Result: generally good agreement; hydrogen vapor-pressure deviation noted; no material impact on gas-phase operating region.
Model hierarchy
Equilibrium screening → kinetic reactor model → shortcut separation → rigorous separation → preliminary costing
RGibbsREquilRPlugFlashDSTWURadFracCAPCOSTMonte Carlo
Turton et al.
Process design, preliminary equipment sizing, manufacturing-cost and CAPCOST methodology
Analysis, Synthesis and Design of Chemical Processes, 4th ed., 2012
Vanden Bussche & Froment
Steady-state kinetic model for methanol synthesis and water-gas shift
Journal of Catalysis, 1996
Rostrup-Nielsen
Steam reforming catalyst behavior, carbon formation and industrial reforming context
Steam Reforming of Hydrocarbons, 1975; Catalytic Steam Reforming, 1984
Luyben
Methanol reactor/column process design reference
Design and Control of a Methanol Reactor/Column Process, 2010
NIST
Water–methanol binary thermodynamic validation
Dataset 160
IPCC
Combustion-emission factor framework
2006 IPCC Guidelines for National Greenhouse Gas Inventories
Claim boundaries
· Steady-state only.
· No dynamic control study.
· No catalyst aging model.
· No detailed pressure-drop network.
· No vendor quotes.
· No offshore layout, weight or safety study.
QA & RECONCILIATION

Every headline value is traceable — and inconsistencies are not hidden

The report contains several narrative, table and appendix values that require reconciliation. The website uses a declared hierarchy: stream table and explicit calculation first, detailed appendix second, narrative rounding third.

Reconciliation hierarchy
  1. 1. Controlling stream table or explicit equation
  2. 2. Detailed equipment/economic appendix
  3. 3. Narrative section
  4. 4. Figure-only qualitative evidence
QA-01
Annual methanol production
Reconciled
Sources: 8.19 kt/y; 8.97 kt/y; 1,025.368 kg/h; 8,000 h/y
Website value: 8.203 kt/y
Logic: 1,025.368 × 8,000 / 1,000,000
Severity: Medium
QA-02
Reformer tube diameter
Reconciled
Sources: 4 m in narrative/table; 0.1016 m in catalyst sizing
Website value: 0.1016 m per tube
Logic: Detailed catalyst-volume basis controls
Severity: High
QA-03
Synthesis conversion
Rounded
Sources: 75.5% and 75.8%
Website value: 75.5%
Logic: Balance calculation and conclusion value used; 75.8% treated as narrative rounding
Severity: Low
QA-04
Distillation reflux ratio
Clarified
Sources: 0.36 and 1.03829
Website value: 0.36 DSTWU preliminary; 1.03829 final RadFrac
Logic: Values belong to different model stages
Severity: Low
QA-05
Product purity basis
Clarified
Sources: 99.86 wt%; 99.89 mol%
Website value: Both retained with basis labels
Logic: Mass and molar fractions are not interchangeable
Severity: Low
QA-06
Steam-to-carbon ratio
Open
Sources: Reported design value 2.78; stream table not fully reconciled
Website value: 2.78 reported assumption
Logic: Do not present as independently verified
Severity: Medium
QA-07
Operating labor cost
Open
Sources: $0.160m/y executive table; approximately $0.994m/y appendix calculation
Website value: $0.160m/y in executive economics; discrepancy disclosed
Logic: Preserve official COMd result and avoid mixing cost bases
Severity: High
QA-08
Reformer furnace duty
Clarified
Sources: 8,762 MJ/h actual note; 10,800 MJ/h CAPCOST input
Website value: Both retained with purpose labels
Logic: 10,800 MJ/h is the conservative CAPCOST regression minimum
Severity: Low
QA-09
Direct versus indirect emissions
Passed
Sources: 116 kg CO2/h indirect; 138 kg CO2/h direct
Website value: Separate bars and labels
Logic: Avoid false single-footprint claim
Severity: Low
QA-10
Methane economic boundary
Passed with boundary
Sources: Methane purchase cost set to zero
Website value: Explicit boundary assumption
Logic: Opportunity cost would worsen economics
Severity: Medium
6
Team authors correctly credited
37
Process streams in source model
26
Report figures reviewed
41
Report tables/appendix referenced
50,000
Monte Carlo samples
2
Open reconciliations retained
ENGINEERING DECISIONS

What works, what fails, and what should be redesigned next

The case study is valuable because the technical and economic conclusions are not forced into the same answer.

What works
  • · High reformer conversion.
  • · Methanol purity specification achieved.
  • · Water recycle integrated.
  • · Multi-stage compression and intercooling defined.
  • · Recycle/purge logic operationally explicit.
  • · Full technical-to-economic chain documented.
What does not work in the base case
  • · NPV remains negative.
  • · No payback.
  • · Revenue and COMd are nearly equal.
  • · R-203 and the reformer furnace dominate FCIL.
  • · Utility costs remain high.
  • · Monte Carlo probability of positive NPV is 0%.
30 days — Reconcile and harden the model
  • · Resolve steam-to-carbon ratio.
  • · Reconcile labor-cost basis.
  • · Confirm reformer tube geometry.
  • · Separate Aspen design values from CAPCOST conservative inputs.
  • · Produce a controlled data dictionary.
60 days — Re-optimize the flowsheet
  • · Revisit synthesis reactor sizing, especially R-203.
  • · Explore alternative heat-exchanger matches.
  • · Test lower-pressure-drop and alternative reactor configurations.
  • · Evaluate purge-gas energy recovery.
  • · Reassess methanol recovery versus utility load.
90 days — Rebuild the business case
  • · Test larger scale.
  • · Include methane opportunity cost explicitly.
  • · Apply offshore location and installation factors.
  • · Add product-price and carbon-value scenarios.
  • · Compare against gas export, LNG, GTL or continued flaring alternatives.
  • · Advance to safety, operability and offshore-layout studies only if economics improve.
REPOSITORY & EVIDENCE

Open, traceable and ready for technical review

The website is the executive layer. The report, model package, methodology and QA artifacts remain the technical evidence layer.