Sourced conceptual inventory per tonne of dense-phase CO2 at 15.3 MPa: the wet stripper-vent gas of an ammonia plant is compressed, dried with triethylene glycol and cooled, after the US NETL study of industrial capture (2023). No flowsheet; not reviewed.
CO2 conditioning of a high-purity source (ammonia CO2 stripper vent), compression and TEG drying
Sourced conceptual inventory per tonne of dense-phase CO2 at 15.3 MPa: the wet stripper-vent gas of an ammonia plant is compressed, dried with triethylene glycol and cooled, after the US NETL study of industrial capture (2023). No flowsheet; not reviewed.
Overview
- Capacity
- per tonne of conditioned CO2 (the dataset's basis); the source's case is 55.5 t/h
What goes in and out
In
- Carbon dioxideFeedstockwet CO2 stripper (regenerator) vent of a natural-gas ammonia plant, 97.09 mol% CO2, 0.16 MPa; zero burden from the source plant (system-model section 2, step 4); fossil carbon
- Triethylene glycolFeedstockmake-up of the TEG dryer, linked to ethylene-glycol-1 (lca/mappings.yaml)
- WaterFeedstockcooling-tower make-up of the compressor coolers, withdrawn from nature
Out
- Carbon dioxideMain productdense phase, 15.3 MPa and 30 degC, 99.95 mol% CO2 (500 ppm water), EOR pipeline quality
- WastewaterWastewater knocked out of the raw gas and removed by the dryer
- WastewaterWastecooling-tower blowdown (ASSUMED 4 cycles of concentration)
- WaterEmissioncooling-tower evaporation
Utilities: Electricity (reciprocating CO2 compressor, circulating-water pumps and cooling-tower fans)
Life cycle assessment
No footprint assessed yet; the process is part of the life-cycle inventory below.
In the open LCI database (cheme-as-code-atlas-preview-a3c52e4) as Carbon dioxide, dense phase, >= 99.95 mol%, 153 bara Preliminary.
Download it for Brightway, openLCA and other tools.
In the LCI database: system model, datasets and KPIs against the benchmarks
In the LCI database
- Status
- Preliminary 2 unmapped exchanges. Some exchanges have no background mapping yet: they are exported unlinked and count no burden, so the inventory is incomplete.
- System model
- attributional, cut-off (methodology 1.1.0)
- Allocation
- mass (single-output, from default) · product:CO2 100 %
- Allocation findings
- none
- Change report
- Not available: this build has no change report against an earlier release.
- Dataset pages
- Carbon dioxide, dense phase, >= 99.95 mol%, 153 bara Preliminary
KPI benchmark positions
| KPI | Value | Reference range | Position |
|---|---|---|---|
| Cooling-water make-up per t of CO2 conditioned No open source independent of the dataset found (2026-11-05). The only figures read are NETL (2023), DOE/NETL-2023/3907, Exhibits 5-7 and 5-26: water consumable of the ammonia case (46,000 gal/d, 130.8 kg/t, the dataset itself) and the ethanol case (17,000 gal/d, 164.2 kg/t). They are the dataset's own source, so they are kept only as its uncertainty spread and not as a check. Read without a per-tonne make-up figure: McCollum and Ogden (2006) UCD-ITS-RR-06-14 (no cooling water), IPCC SRCCS (2005) ch. 3; a web search for open make-up water figures of CO2 compression intercooling found none stated per t of CO2. | – kg/t | not available | not evaluated |
| Electricity per t of CO2 compressed (and dried) to pipeline pressure No open source found (2026-11-05) that states a per-tonne electricity for compressing (and drying) high-purity CO2 to pipeline pressure independently of the dataset. Read: McCollum, D.L., Ogden, J.M. (2006) UCD-ITS-RR-06-14, section 'Calculation of Compressor & Pump Power Requirements', pp. 2-4, which prints the compressor and pump power equations and a figure of power against flow, but no per-tonne value. Evaluated by us with the parameter values it states (five stages from 0.1 to 7.38 MPa with their Z and k, inlet 40 degC, isentropic efficiency 0.75; pump from 7.38 to 15 MPa, 630 kg/m3, efficiency 0.75), it gives 100.4 kWh/t compression plus 4.5 kWh/t pumping, 104.8 kWh/t, without cooling-water power or drying. That is our own model evaluation, so it is not recorded as a range. NETL (2023) DOE/NETL-2023/3907 gives 105.6 kWh/t (ammonia, Exhibits 5-3 and 5-4: 5,860 kW over 55,488 kg/h) and 112.7 kWh/t (ethanol, Exhibits 5-22 and 5-23: 1,840 kW over 16,329 kg/h), divided by us; it is the dataset's own source, so it is not a check either. Both are kept as the dataset's uncertainty spread. | – kWh/t | not available | not evaluated |
Maturity and review
Design maturity Concept (claimed): An idea or first flowsheet; numbers are rough. No independent engineering review yet. Automated checks passing is not a review.
Calculation maturity, from the checked evidenceNot assessed
The process has no maturity report (cheme maturity, checks/maturity.json), so no calculation maturity is established.
cheme maturity --write.Artifact completeness
Which deliverables exist. They never raise a calculation maturity level: a drawing from unchecked numbers is still unchecked.
Not reported without a maturity report.
Independent review
Not independently reviewed
No independent engineering review yet. Automated checks passing is not a review.
Set by people only. Reaching a calculation maturity level or passing automated checks is not an independent review or an approval.
Where the evidence comes from
- Report
processes/carbon-capture-1/checks/maturity.json(not in the library)- Method
- How ChemE-as-Code checks the levels (requirement by requirement)
Open items
0 open items · 0 closed
New action itemNew engineering holdNew technical queryNew design changeAll issues
Sources
- Library version
- a3c52e4 (process last changed in a3c52e4)
- Data
- Catalog record (JSON) · CC-BY-4.0
- Files
- View the files on GitHub · change history and authors
References
- Hughes, S., Zoelle, A. (2023) Cost of Capturing CO2 from Industrial Sources. National Energy Technology Laboratory, DOE/NETL-2023/3907, section 5.1 (ammonia) and 5.3 (ethanol)
- IPCC (2006) 2006 IPCC Guidelines for National Greenhouse Gas Inventories, Volume 3, Chapter 3 Chemical Industry Emissions, section 3.2 (ammonia: CO2 regenerator, CO2 recovered for downstream use, Boxes 3.1 to 3.3)
- IPCC (2006) 2006 IPCC Guidelines for National Greenhouse Gas Inventories, Volume 2, Chapter 5 Carbon Dioxide Transport, Injection and Geological Storage, section 5.3 (capture boundary)
- McCollum, D.L., Ogden, J.M. (2006) Techno-economic models for carbon dioxide compression, transport, and storage. Institute of Transportation Studies, University of California, Davis, UCD-ITS-RR-06-14 (benchmark note and uncertainty spread only: our evaluation of its compression model)
How to cite
For the data, cite the Process Atlas paper; for the platform that builds and checks it, the ChemE-as-Code paper.
Schweidtmann, A. M. & Weber, J. M. (2026, in preparation). Process Atlas: an open, git-native, reproducible library and life cycle inventory of chemical processes (working title).
For this process: "CO2 conditioning of a high-purity source (ammonia CO2 stripper vent), compression and TEG drying", ChemE-as-Code process library, version a3c52e4.
BibTeX
@unpublished{schweidtmann_process_atlas,
author = {Schweidtmann, Artur M. and Weber, Jana M.},
title = {{Process Atlas: an open, git-native, reproducible library and life cycle inventory of chemical processes (working title)}},
year = {2026},
url = {https://atlas.cheme-as-code.org},
note = {in preparation}
}Schweidtmann, A. M. (2026). ChemE-as-Code: An Open-Source Platform for Agentic AI in Chemical Engineering. arXiv:2611.07947. https://doi.org/10.48550/arXiv.2611.07947
BibTeX
@misc{schweidtmann_cheme_as_code,
author = {Schweidtmann, Artur M.},
title = {{ChemE-as-Code: An Open-Source Platform for Agentic AI in Chemical Engineering}},
year = {2026},
eprint = {2611.07947},
archivePrefix = {arXiv},
doi = {10.48550/arXiv.2611.07947},
url = {https://arxiv.org/abs/2611.07947}
}