RDKit-checked aqueous, gas, nutrient, corrosion, inhibitor, and fuel-gas molecule markers
Docker-Generated Aqueous Valorization
Aqueous Valorization Lab
A 3D route workspace for deciding whether HTL process water can help close hydrogen demand, COD removal, water reuse, fuel-gas recovery, nutrient handling, and WRRF compatibility instead of remaining the main scale-up liability.
route options ranked across COD destruction, H2 closure, water reuse, readiness, and risk
top current route by Docker-generated score
average hydrogen-closure score in the selected support train
RuOx/Ti electrochemical oxidation flow cell
flow-cell stability on real sludge HTL water, ammonium tolerance, chloride byproducts, and H2 cleanup
- Readiness
- 60
- Fuel gas
- 74
- Energy risk
- 44
- N risk
- 62
Pyomo-formulated aqueous valorization train with deterministic enumeration across hydrogen, COD, biological-compatibility, and readiness constraints. Current train covers 4 route classes and 14 molecule markers.
Acetic acid; Propionic acid; Butyric acid; Phenol; Pyridine; Ammonia; Chloride ion; Hydrogen; Ethane; Propane; Butane
The route is only useful if these water-side markers move with COD, nitrogen, H2 purity, and corrosion evidence.
- Top molecule
- Butyric acid
- Source IDs
- valorization-eco-pnnl-2025; valorization-cleanset-pnnl
The highest-upside route is electrochemical: use HTL aqueous COD to make H2 and C2-C4 gases, while reducing wastewater load before recycle or WRRF return.
Aqueous valorization can close hydrogen and water loops only if ammonium, chloride, nitrogen heterocycles, PFAS, electrode/catalyst life, and plant biological compatibility are measured together.
This is a support-train discovery screen. It does not replace oil upgrading, fuel specifications, residual routing, or TEA/LCA validation.
Current aqueous decision
Treat HTL water as the next discovery surface
Recent sources make the strongest new improvement path clear: the HTL aqueous phase should be tested as a coupled H2, COD, heat, fuel-gas, nutrient, and WRRF-compatibility problem. ECO/CleanSET and microbial electrolysis are high-upside H2 routes, wet air oxidation is a robust COD and toxicity reducer, and ambient catalytic upgrading is a TEA/LCA monetization lead. None of these remove the need for measured nitrogen, chloride, PFAS, corrosion, and biological-compatibility gates.
RuOx/Ti electrochemical oxidation flow cell is the top route because it can connect COD removal with H2 and C2-C4 fuel-gas value.
The selected train covers electrochemical, catalytic, bioelectrochemical, and high-severity carbon-recovery options.
Deep COD removal is possible on paper, but refractory acids and N-heterocycles decide whether the route actually de-risks the plant.
Selected support train
Four aqueous routes to test before scaling the HTL-hydrotreating loop
RuOx/Ti electrochemical oxidation flow cell
Score 350; COD 88; H2 closure 100; water reuse 82; readiness 60. Must prove: flow-cell stability on real sludge HTL water, ammonium tolerance, chloride byproducts, and H2 cleanup.
Ambient-pressure aqueous catalytic upgrading
Score 335.1; COD 90; H2 closure 56; water reuse 78; readiness 54. Must prove: catalyst cost/life, real HTL-water poisons, gas cleanup, and nutrient product quality.
Pilot microbial electrolysis cell
Score 330.8; COD 72; H2 closure 88; water reuse 64; readiness 64. Must prove: site-specific biofilm stability, methanogen suppression, H2 purity, and inhibitory HTL-water tolerance.
Catalytic hydrothermal gasification
Score 296.2; COD 96; H2 closure 46; water reuse 84; readiness 52. Must prove: high-pressure catalyst life, salts and sulfur poisons, heat recovery, and pressure-system economics.
Route ledger
Every treatment option moves a different part of the risk
RuOx/Ti electrochemical oxidation flow cell
- Score
- 350
- COD
- 88
- H2
- 100
- Energy risk
- 44
Ambient-pressure aqueous catalytic upgrading
- Score
- 335.1
- COD
- 90
- H2
- 56
- Energy risk
- 30
Pilot microbial electrolysis cell
- Score
- 330.8
- COD
- 72
- H2
- 88
- Energy risk
- 34
Catalytic hydrothermal gasification
- Score
- 296.2
- COD
- 96
- H2
- 46
- Energy risk
- 72
Ozone plus biological polishing
- Score
- 215.3
- COD
- 78
- H2
- 0
- Energy risk
- 50
Continuous wet air oxidation
- Score
- 212
- COD
- 95
- H2
- 0
- Energy risk
- 54
Diluted aerobic co-treatment at WRRF
- Score
- 174.6
- COD
- 64
- H2
- 0
- Energy risk
- 38
Controlled aqueous recycle to HTL
- Score
- 112.2
- COD
- 18
- H2
- 0
- Energy risk
- 18
Category ledger
Route classes separate the hydrogen, COD, water, and treatment claims
- Routes
- 1
- Score
- 350
- COD
- 88
- H2
- 100
- Routes
- 1
- Score
- 335.1
- COD
- 90
- H2
- 56
- Routes
- 1
- Score
- 330.8
- COD
- 72
- H2
- 88
- Routes
- 1
- Score
- 296.2
- COD
- 96
- H2
- 46
- Routes
- 1
- Score
- 215.3
- COD
- 78
- H2
- 0
- Routes
- 1
- Score
- 212
- COD
- 95
- H2
- 0
- Routes
- 1
- Score
- 174.6
- COD
- 64
- H2
- 0
- Routes
- 1
- Score
- 112.2
- COD
- 18
- H2
- 0
Aqueous molecule ledger
Molecules that make or break the water-side value claim
Butyric acid C4H8O2
- Priority
- 255.1
- COD
- 72
- H2
- 62
- Inhibition
- 30
Propionic acid C3H6O2
- Priority
- 242.4
- COD
- 70
- H2
- 58
- Inhibition
- 28
Phenol C6H6O
- Priority
- 220.1
- COD
- 76
- H2
- 34
- Inhibition
- 82
Pyridine C5H5N
- Priority
- 219.5
- COD
- 58
- H2
- 28
- Inhibition
- 86
Hydrogen H2
- Priority
- 217.4
- COD
- 0
- H2
- 100
- Inhibition
- 0
Acetic acid C2H4O2
- Priority
- 201.2
- COD
- 66
- H2
- 46
- Inhibition
- 26
Urea CH4N2O
- Priority
- 152.9
- COD
- 32
- H2
- 20
- Inhibition
- 34
Butane C4H10
- Priority
- 141.1
- COD
- 0
- H2
- 36
- Inhibition
- 0
Propane C3H8
- Priority
- 134.4
- COD
- 0
- H2
- 34
- Inhibition
- 0
Ethane C2H6
- Priority
- 127.6
- COD
- 0
- H2
- 32
- Inhibition
- 0
Ammonia H3N
- Priority
- 109.5
- COD
- 0
- H2
- 8
- Inhibition
- 58
Methane CH4
- Priority
- 101.8
- COD
- 0
- H2
- 36
- Inhibition
- 0
Nitrogen N2
- Priority
- 73
- COD
- 0
- H2
- 0
- Inhibition
- 0
Chloride ion Cl-
- Priority
- 70.6
- COD
- 0
- H2
- 0
- Inhibition
- 22
Carbon dioxide CO2
- Priority
- 30.4
- COD
- 0
- H2
- 0
- Inhibition
- 0
Top molecule markers
Short-chain acids and inhibitors define the first bench assays
Butyric acid
water-soluble carbon that can be converted to C2-C4 gas and hydrogen. Electrochemical fit 84; fuel-gas potential 82; water signal 84.5.
Propionic acid
short-chain acid candidate for electrochemical fuel-gas conversion. Electrochemical fit 82; fuel-gas potential 74; water signal 87.
Phenol
slow-oxidizing toxicity marker for WAO and biological polishing. Electrochemical fit 62; fuel-gas potential 28; water signal 76.8.
Pyridine
refractory nitrogen heterocycle and recycle-toxicity marker. Electrochemical fit 54; fuel-gas potential 20; water signal 71.5.
Hydrogen
hydrotreating loop closure product. Electrochemical fit 92; fuel-gas potential 74; water signal 56.
Acetic acid
dominant slow-oxidizing acid after partial wet oxidation. Electrochemical fit 72; fuel-gas potential 42; water signal 88.8.
Urea
water-soluble protein nitrogen proxy. Electrochemical fit 46; fuel-gas potential 14; water signal 95.4.
Butane
CleanSET C4 gas product signal. Electrochemical fit 74; fuel-gas potential 84; water signal 43.5.
Electrocatalytic oxidation of HTL aqueous phase for on-site wastewater treatment and H2 production
PNNL 2025 source reporting ECO COD-removal efficiency, stability dependence on AP composition, ammonium/chloride effects, and a preliminary H2 balance for sludge HTL.
Open sourceContinuous wet air oxidation of HTL aqueous product from wet wastes
PNNL 2025 source reporting continuous WAO COD reduction, refractory acids and N compounds, and improved downstream methane kinetics.
Open sourcePilot microbial electrolysis cell closes the hydrogen loop for hydrothermal wet-waste conversion
PNNL 2025 source reporting a >250 L pilot MEC treating HTL wastewater with high-purity H2 and hydrogen recovery.
Open sourceCleanSET electrochemical treatment technology
PNNL technology source for RuOx/Ti flow-cell treatment of HTL wastewater and conversion of small organics to H2 and C2-C4 fuel gases.
Open sourceAqueous-phase product treatment and monetization options for wet-waste HTL
PNNL TEA/LCA source identifying ambient-pressure catalytic upgrading as a low-MFSP and low-GHG aqueous-phase monetization route.
Open sourceRecent advances on treatment and valorization of HTL aqueous phase
2026 process-intensification review indicating integrated treatment trains outperform single units and summarizing WAO/ECO COD-reduction opportunities.
Open sourceWet-waste HTL TEA/LCA with different biocrude upgrading strategies
Open-access 2026 TEA/LCA source framing sludge, manure, and food-waste HTL with marine fuel, renewable diesel, and SAF upgrading strategies.
Open sourceContinuous-flow aerobic co-treatment of municipal-sludge HTL aqueous phase
2025 source for direct WRRF cotreatment economics, aeration-cost penalty, and activated-sludge integration gate.
Open sourceOzone enhancement of biological treatment for municipal-sludge HTL aqueous streams
2025 source for ozone-assisted biological treatment of municipal-sludge HTL aqueous streams and recalcitrant inhibitor handling.
Open sourceAdvancing integration of HTL aqueous into WRRF digestion processes and assessing PFAS fate
Water Research Foundation project source for HTL aqueous integration, digestion inhibition, pretreatment needs, and PFAS fate.
Open sourceCombined HTL and catalytic hydrothermal gasification system
PNNL technology source for CHG treatment of aqueous HTL effluents containing residual organics.
Open sourceAqueous-phase recirculation effects in sewage-sludge HTL
2026 source showing AP recycle can raise yield while increasing oxygen content and accumulating N-heterocycles.
Open sourceaqueous valorization is a support train, not proof of finished fuel, until COD removal, hydrogen balance, nitrogen fate, electrolyte corrosion, PFAS, and WRRF compatibility are measured on site-specific sludge HTL water