Abstract
This paper aims to develop an innovative and practical method to accelerate Pinch Analysis problems using a combination of process integration, process simulation tools, and life cycle assessment techniques to design effective industrial energy efficiency measures rapidly. Data extraction and analysis is accelerated using the workflow, reducing pinch analysis duration, and therefore cost. This lowers financial barriers and is expected to help facilitate an increase in the number of conducted pinch analyses each year. An innovative ecological targeting step has been included in the workflow, which represents the option for end-users to further their CO2 savings, once energy targeting has been completed on a purely cost basis. It is expected that optimizing for costs first will enable the implementation of heat recovery solutions in industry. The methodology is applied to an example case study, and the learnings from industrial application is reported.
Funding source: Swiss Innovation Agency Innosuisse
-
Author contributions: All the authors have accepted responsibility for the entire content of this submitted manuscript and approved submission.
-
Research funding: This research project is financially supported by the Swiss Innovation Agency Innosuisse and is part of the SCCER EIP. Further support is provided by the Lucerne University of Applied Sciences and Arts, Switzerland.
-
Conflict of interest statement: The authors declare no conflicts of interest regarding this article.
Life cycle inventory of brazed plate heat exchanger production.
| Activity name | Geography | Unit | Brazed plate heat exchanger production | Comment | |
|---|---|---|---|---|---|
| Geography | RER | ||||
| Unit | m2 | ||||
| Reference product | Brazed plate heat exchanger production | RER | m2 | A | |
| Inputs from technosphere | Market for steel, chromium steel 18/8, hot rolled | GLO | kg | 0.9·m HEX (A) | [29, 30, 33] |
| Metal working, average for chromium steel product manufacturing | RER | kg | 0.9·m HEX (A) | [33] | |
| Market for copper | GLO | kg | 0.1·m HEX (A) | [29, 30, 33] | |
| Market for sheet rolling, copper | GLO | kg | 0.1·m HEX (A) | [33] | |
| Metal working, average for copper product manufacturing | RER | kg | 0.1·m HEX (A) | [33] |
Life cycle inventory of brazed plate heat exchanger, at plant.
| Activity name | Geography | Unit | Brazed plate heat exchanger, at plant | Comment | |
|---|---|---|---|---|---|
| Geography | CH | ||||
| Unit | m2 | ||||
| Reference product | Brazed plate heat exchanger, at plant | CH | m2 | A | |
| Inputs from technosphere | Brazed plate heat exchanger production | RER | m2 | A | |
| Market for corrugated board box | RER | kg | 0.56·10−6 kg/mm2·A P (A) | m ccb (A), [29, 30, 33, 38] | |
| Market for packaging film, low density polyethylene | GLO | kg | 0.925·10−6 kg/mm3·0.023 mm·3·A P (A) | m pf (A) [29, 30, 33, 39], three layers | |
| Market for transport, freight, lorry, unspecified | RER | tkm | (m HEX (A) + m ccb (A) + m pf (A))/1000 kg/t·2000 km | Reference [33], transport from Sweden to Switzerland | |
| Market for waste polyethylene | CH | kg | m pf (A) | [33] |
Life cycle inventory of operation, brazed plate heat exchanger.
| Activity name | Geography | Unit | Operation, brazed plate heat exchanger | Comment | |
|---|---|---|---|---|---|
| Geography | CH | ||||
| Unit | Year | ||||
| Reference product | Operation, brazed plate heat exchanger | CH | year | LT | |
| Inputs from technosphere | Brazed plate heat exchanger, at plant | RER | m2 | A |
| Manufacturer | Model | Weight | Height | Width | Length |
|---|---|---|---|---|---|
| (kg) | (mm) | (mm) | (mm) | ||
| Alfa laval | CB10/CBH10 | 0.13 + 0.04·n | 191.5 | 73.5 | 7 + 2.16·n |
| CB11/CBH11 | 0.132 + 0.04·n | 192 | 74 | 7.4 + 2.14·n | |
| CB16/CBH16 | 0.14 + 0.04·n | 209.5 | 73.5 | 7 + 2.16·n | |
| CB18/CBH18 | 0.22 + 0.07·n | 315.5 | 73.5 | 7 + 2.16·n | |
| CB20 | 0.6 + 0.08·n | 324 | 94 | 8 + 1.5·n | |
| CB30/CBH30/CBP30 | 1.2 + 0.11·n | 313 | 113 | 13 + 2.31·n | |
| CB60/CBH60 | 2.1 + 0.18·n | 527 | 113 | 13 + 2.32·n | |
| CB62/CBH62 | 2.1 + 0.18·n | 529 | 113 | 13 + 1.98·n | |
| CB65/CBH65 | 2.1 + 0.14·n | 535 | 120.5 | 11.5 + 1.4·n | |
| CB110/CBH110/CBP110 | 4.82 + 0.35 · n | 768 | 191 | 15 + 2.56·n | |
| CB112/CBH112/CBP112/CBXP112 | 4.82 + 0.35·n | 616 | 191 | 16 + 2.07·n | |
| CB200/CBH200 | 12 + 0.6·n | 742 | 324 | 11 + 2.7·n | |
| CB300/CBH300 | 21 + 1.26·n | 990 | 366 | 11 + 2.62·n | |
| CB400 | 24 + 1.35·n | 990 | 390 | 14 + 2.56·n | |
| CB410 | 30 + 1.14·n | 793 | 490 | 14.2 + 2.17·n | |
| CBXP27 | 2 + 0.13·n | 310 | 111 | 13 + 2.4·n | |
| CBXP52 | 2.5 + 0.22·n | 526 | 111 | 14 + 2.37·n | |
| SWEP | B5T | 0.50 + 0.044·n | 193 | 76 | 4.00 + 2.24·n |
| B10T | 1.15 + 0.096·n | 289 | 119 | 4.00 + 2.24·n | |
| B12 | 1.12 + 0.12·n | 287 | 117 | 4.40 + 2.34·n | |
| B15T | 1.25 + 0.104·n | 468 | 76 | 4.00 + 2.24·n | |
| B16 | 1.48 + 0.12·n | 376 | 119 | 4.00 + 2.24·n | |
| B28 | 2.09 + 0.164·n | 526 | 119 | 4.00 + 2.24·n | |
| B30 | 5.88 + 0.18·n | 243.50 | 243.50 | 14.00 + 2.12·n | |
| B35T | 15.76 + 0.256·n | 393 | 243 | 22.00 + 2.26·n | |
| B60 | 16.16 + 0.47·n | 374 | 364 | 16.00 + 2.14·n | |
| B65 | 27.44 + 1.03·n | 864 | 363 | 17.00 + 2.32·n | |
| B80 | 2.09 + 0.164·n | 526 | 119 | 4.00 + 2.24·n | |
| B315 | 6.98 + 0.312·n | 392.50 | 242.50 | 10.00 + 2.86·n | |
| B633 | 80.33 + 1.224·n | 830 | 537 | 61.38 + 2.39·n | |
| B649 | 79.45 + 1.941·n | 1232 | 537 | 45.08 + 2.09·n |
Environmental impacts of utility systems based on eco-invent 3.5, cut-off system model [33].
| Category | Technology | Unit | Geography | Cumulative energy demand total (mJ eq) | Cumulative energy demand non-renewable (mJ eq) | Cumulative energy demand renewable (mJ eq) | CO2 equivalent (kg CO2 eq) | Eco-points (UBP) | |
|---|---|---|---|---|---|---|---|---|---|
| Heat | Hard coal | Hard coal industrial furnace 1–10 MW | mJ | RER w/o CH | 1.28 | 1.26 | 0.02 | 0.138 | 119.6 |
| Coke | Coal coke industrial furnace 1–10 MW | mJ | RoW | 1.34 | 1.32 | 0.02 | 0.153 | 208.9 | |
| Diesel | Heat and power co-generation, 200 kW electrical, SCR-NOx reduction | mJ | CH | 0.44 | 0.44 | 0.00 | 0.032 | 23.3 | |
| Light fuel oil | Industrial furnace 1 MW | mJ | CH | 1.37 | 1.36 | 0.01 | 0.090 | 70.1 | |
| Heavy fuel oil | Industrial furnace 1 MW | mJ | CH | 1.28 | 1.27 | 0.01 | 0.092 | 78.8 | |
| Natural gas | Boiler modulating > 100 kW | mJ | RER w/o CH | 1.25 | 1.24 | 0.00 | 0.069 | 42.5 | |
| Boiler condensing modulating > 100 kW | mJ | RER w/o CH | 1.17 | 1.17 | 0.00 | 0.065 | 39.9 | ||
| Heat and power co-generation, 200 kW electrical, lean burn | mJ | CH | 0.48 | 0.48 | 0.00 | 0.030 | 18.9 | ||
| Heat and power co-generation, 500 kW electrical, lean burn | mJ | CH | 0.46 | 0.46 | 0.00 | 0.029 | 17.9 | ||
| Heat and power co-generation, 1 MW electrical, lean burn | mJ | CH | 0.44 | 0.44 | 0.00 | 0.028 | 17.2 | ||
| Industrial furnace > 100 kW | mJ | RER w/o CH | 1.26 | 1.25 | 0.00 | 0.070 | 43.0 | ||
| Industrial furnace low-NOx > 100 kW | mJ | RER w/o CH | 1.37 | 1.36 | 0.01 | 0.075 | 47.4 | ||
| Market, district or industrial | mJ | CH | 0.46 | 0.46 | 0.00 | 0.029 | 18.0 | ||
| Other than natural gas | Market, district or industrial | mJ | CH | 0.05 | 0.03 | 0.02 | 0.002 | 2.4 | |
| Propane | Industrial furnace > 100 kW | mJ | RoW | 1.19 | 1.19 | 0.01 | 0.088 | 62.9 | |
| Solar/electric | Hot water tank, flat plate, multiple dwelling | MJ | CH | 2.39 | 1.55 | 0.84 | 0.024 | 66.2 | |
| Solar/gas | Hot water tank, flat plate, multiple dwelling | mJ | CH | 1.23 | 0.93 | 0.30 | 0.055 | 36.8 | |
| Steam | Energy carrier, chemical industry | mJ | RER | 1.56 | 1.52 | 0.04 | 0.103 | 73.8 | |
| Market, chemical industry | mJ | RER | 1.56 | 1.52 | 0.04 | 0.103 | 73.8 | ||
| Straw | Furnace, 300 kW | mJ | GLO | 0.17 | 0.09 | 0.07 | 0.010 | 57.2 | |
| Organic, furnace 300 kW | mJ | GLO | 0.34 | 0.09 | 0.25 | 0.009 | 81.7 | ||
| Waste | Municipal waste incineration, generic market, district or industrial | mJ | CH | 0.00 | 0.00 | 0.00 | 0.000 | 0.5 | |
| Wood chips | Heat and power co-generation, 2000 kW | mJ | CH | 0.88 | 0.03 | 0.85 | 0.003 | 26.6 | |
| Heat and power co-generation, 2000 kW, state-of-the-art 2014 | mJ | CH | 0.88 | 0.03 | 0.85 | 0.003 | 21.7 | ||
| Heat and power co-generation, 6667 kW | mJ | CH | 0.72 | 0.02 | 0.69 | 0.002 | 19.3 | ||
| Heat and power co-generation, 6667 kW, state-of-the-art 2014 | mJ | CH | 0.72 | 0.02 | 0.69 | 0.002 | 16.0 | ||
| Heat and power co-generation, 6667 kW, state-of-the-art 2014, label-certified | mJ | CH | 0.72 | 0.02 | 0.69 | 0.002 | 16.0 | ||
| Wood chips from industry | Furnace 300 kW | mJ | CH | 0.90 | 0.25 | 0.65 | 0.014 | 62.7 | |
| Furnace 300 kW, state-of-the-art 2014 | mJ | CH | 0.85 | 0.23 | 0.61 | 0.013 | 46.8 | ||
| Furnace 1000 kW | mJ | CH | 0.90 | 0.25 | 0.65 | 0.013 | 56.2 | ||
| Furnace 1000 kW, state-of-the-art 2014 | mJ | CH | 0.85 | 0.23 | 0.61 | 0.012 | 46.2 | ||
| Furnace 5000 kW | mJ | CH | 0.90 | 0.25 | 0.65 | 0.013 | 51.5 | ||
| Furnace 5000 kW, state-of-the-art 2014 | mJ | CH | 0.84 | 0.23 | 0.61 | 0.012 | 38.0 | ||
| Wood chips from post-consumer wood | Furnace 300 kW | mJ | GLO | 0.08 | 0.08 | 0.01 | 0.006 | 30.0 | |
| Softwood chips from forest | Furnace 300 kW | mJ | CH | 1.31 | 0.08 | 1.23 | 0.006 | 46.2 | |
| Furnace 300 kW, state-of-the-art 2014 | mJ | CH | 1.23 | 0.08 | 1.15 | 0.006 | 31.3 | ||
| Furnace 1000 kW | mJ | CH | 1.31 | 0.08 | 1.23 | 0.006 | 38.5 | ||
| Furnace 1000 kW, state-of-the-art 2014 | mJ | CH | 1.23 | 0.08 | 1.15 | 0.005 | 29.6 | ||
| Furnace 5000 kW | mJ | CH | 1.36 | 0.08 | 1.28 | 0.005 | 34.1 | ||
| Furnace 5000 kW, state-of-the-art 2014 | mJ | CH | 1.23 | 0.07 | 1.15 | 0.004 | 26.3 | ||
| Hardwood chips from forest | Furnace 300 kW | mJ | CH | 1.36 | 0.08 | 1.28 | 0.006 | 48.3 | |
| Furnace 300 kW, state-of-the-art 2014 | mJ | CH | 1.28 | 0.08 | 1.20 | 0.006 | 33.3 | ||
| Furnace 1000 kW | mJ | CH | 1.37 | 0.08 | 1.28 | 0.006 | 42.1 | ||
| Furnace 1000 kW, state-of-the-art 2014 | mJ | CH | 1.28 | 0.08 | 1.20 | 0.005 | 33.0 | ||
| Furnace 5000 kW | MJ | CH | 1.36 | 0.08 | 1.28 | 0.005 | 37.4 | ||
| Furnace 5000 kW, state-of-the-art 2014 | mJ | CH | 1.23 | 0.08 | 1.15 | 0.004 | 26.6 | ||
| Cooling energy | Natural gas | Cogen unit with absorption chiller 100 kW | mJ | CH | 2.07 | 2.00 | 0.06 | 0.113 | 86.0 |
| Market | mJ | GLO | 2.44 | 2.40 | 0.04 | 0.148 | 114.1 |
Life cycle inventory of cooling water.
| Activity name | Geography | Unit | Cooling energy, from tap water | Comment | |
|---|---|---|---|---|---|
| Geography | CH | ||||
| Unit | MJ | ||||
| Reference product | Cooling energy, from tap water | CH | mJ | 1 | |
| Inputs from technosphere | Market for tap water | CH | kg | 1000 kJ/mJ/(4.2 kJ/(kg·K)·5 K)·1 mJ | [33] |
References
1. Kaiser, T, Maus, K, Schmitz, R, Faust, A-K, Eckmanns, A, Pulfer, M, et al.. Federal energy research masterplan for the period from 2017 to 2020; 2015. Available from: www.energieforschung.ch.Suche in Google Scholar
2. The Intergovernmental Panel on Climate Change. Geneva: The Intergovernmental Panel on Climate Change; 2020. Available from: https://www.ipcc.ch/.Suche in Google Scholar
3. Bundesamt für Energie BFE. Schweizerische Gesamtenergiestatistik 2019. Bern, Switzerland: Bundesamt für Energie; 2020.Suche in Google Scholar
4. El-Halwagi, MM. Pollution prevention through process integration: systematic design tools. New York: Academic Press; 1997.Suche in Google Scholar
5. Linnhoff, B, Flower, JR. Synthesis of heat exchanger networks: I. Systematic generation of energy optimal networks. AIChE J 1978;24:633–43.10.1002/aic.690240411Suche in Google Scholar
6. Klemeš, JJ, Varbanov, PS, Walmsley, TG, Jia, X. New directions in the implementation of pinch methodology (PM). Renew Sustain Energy Rev 2018;98:439–68. https://doi.org/10.1016/j.rser.2018.09.030.Suche in Google Scholar
7. Varbanov, PS, Walmsley, TG, Klemeš, JJ, Seferlis, P, Sabev Varbanov, P, Yong, JY, et al.. Data extraction for heat integration and total site analysis: a review. Chem Eng Trans 2019;76:67–72. https://doi.org/10.3303/CET1976012.Suche in Google Scholar
8. Klemes, JJ, editor. Handbook of process integration (PI): minimisation of energy and water use, waste and emissions. Cambridge: Woodhead Publishing; 2013.Suche in Google Scholar
9. Kemp, IC. Some aspects of the practical application of pinch technology methods. TransI Chem E 1991;69:10.Suche in Google Scholar
10. Klemeš, JJ, Varbanov, PS. Implementation and pitfalls of process integration. Chem Eng Trans 2010;21:1369–74. https://doi.org/10.3303/CET1021229.Suche in Google Scholar
11. Bergamini, R, Nguyen, T-V, Bühler, F, Elmegaard, B. Development of a simplified process integration methodology for application in medium-size industries. In: Proceedings of ECOS 2016: 29th International Conference on Efficiency, Cost, Optimization, Simulation and Environmental Impact of Energy Systems; 2016.Suche in Google Scholar
12. Wen, Y, Shonnard, DR. Environmental and economic assessments of heat exchanger networks for optimum minimum approach temperature. Comput Chem Eng 2003;27:1577–90. https://doi.org/10.1016/S0098-1354(03)00097-8.Suche in Google Scholar
13. Papoulias, SA, Grossmann, IE. A structural optimization approach in process synthesis—II: heat recovery networks. Comput Chem Eng 1983;7:707–21. https://doi.org/10.1016/0098-1354(83)85023-6.Suche in Google Scholar
14. López-Maldonado, LA, Ponce-Ortega, JM, Segovia-Hernández, JG. Multiobjective synthesis of heat exchanger networks minimizing the total annual cost and the environmental impact. Appl Therm Eng 2011;31:1099–113. https://doi.org/10.1016/j.applthermaleng.2010.12.005.Suche in Google Scholar
15. Vaskan, P, Guillén-Gosálbez, G, Jiménez, L. Multi-objective design of heat-exchanger networks considering several life cycle impacts using a rigorous MILP-based dimensionality reduction technique. Appl Energy 2012;98:149–61. https://doi.org/10.1016/j.apenergy.2012.03.018.Suche in Google Scholar
16. Ravagnani, MASS, Mano, TB, Carvalho, EP, Silva, AP, Costa, CBB. Multi-objective heat exchanger networks synthesis considering economic and environmental optimization. Comput Aided Chem Eng 2014;33:1579–84. https://doi.org/10.1016/B978-0-444-63455-9.50098-2.Suche in Google Scholar
17. Mano, TB, Jiménez, L, Ravagnani, MASS. Incorporating life cycle assessment eco-costs in the optimization of heat exchanger networks. J Clean Prod 2017;162:1502–17. https://doi.org/10.1016/j.jclepro.2017.06.154.Suche in Google Scholar
18. Mano, TB, Guillén-Gosálbez, G, Jiménez, L, Ravagnani, MASS. Synthesis of heat exchanger networks with economic and environmental assessment using fuzzy-analytic hierarchy process. Chem Eng Sci 2019;195:185–200. https://doi.org/10.1016/j.ces.2018.11.044.Suche in Google Scholar
19. Furman, KC, Sahinidis, NV. A critical review and annotated bibliography for heat exchanger network synthesis in the 20th century. Ind Eng Chem Res 2002;41:2335–70. https://doi.org/10.1021/ie010389e.Suche in Google Scholar
20. Linnhoff, B. Process integration Gothenburg-20 years later. Historical overview of early development. Gothenburg, Sweden: International Process Integration Jubilee Conference, Chalmers University; 2013.Suche in Google Scholar
21. Linnhoff, B, Akinradewo, CG. Linking process simulation and process integration. Comput Chem Eng 1999;23:S945–53. https://doi.org/10.1016/s0098-1354(99)80229-4.Suche in Google Scholar
22. Brunner, F, Krummenacher, P. Einführung in die Prozessintegration mit der Pinch-Methode, Handbuch für die Analyse von kontinuierlichen Prozessen und Batch-Prozessen. Zweite Auflage 2017:1–175.Suche in Google Scholar
23. Linnhoff, B, Townsend, DW, Boland, D, Hewitt, GF, Thomas, BEA, Guy, AR, et al.. A user guide on process integration for the efficient use of energy. London: The Institue of Chemical Engineers; 1982.Suche in Google Scholar
24. Linnhoff, B, Hindmarsh, E. The pinch design method for the heat exchanger networks. Chem Eng Sci 1983;38:745–63.10.1016/0009-2509(83)80185-7Suche in Google Scholar
25. Shenoy, U. Heat exchanger network synthesis-process optimization by energy and resource analysis. Houston, USA: Gulf Publishing Company; 1995.Suche in Google Scholar
26. Kemmler, A, Spillmann, T. Analyse des schweizerischen Energieverbrauchs 2000-2019 nach Verwendungszwecken. Bern, Switzerland: Bundesamt für Energie; 2020.Suche in Google Scholar
27. Guthörl, D. Life cycle assessment of energy efficiency measures in industrial processes: the role of embedded energy. Dublin: Dublin Institute of Technology; 2016.Suche in Google Scholar
28. Alfa Laval. Brazed plate heat exchangers. Products; 2015. Available from: https://www.alfalaval.com/products/heat-transfer/plate-heat-exchangers/brazed-plate-heat-exchangers/.Suche in Google Scholar
29. Alfa Laval. Environmental product declaration: brazed plate heat exchanger. Lund: Alfa Laval; 2016:2 p.Suche in Google Scholar
30. SWEP International AB. Environmental product declaration: brazed plate heat exchangers. Landskrona, Sweden: SWEP International AB; 2017:1–6 pp.Suche in Google Scholar
31. SWEP International AB. Process industry. Products; 2019. Available from: https://www.swep.kr/.Suche in Google Scholar
32. Frischknecht, R. LCI modelling approaches applied on recycling of materials in view of environmental sustainability, risk perception and eco-efficiency. Int J Life Cycle Assess 2010;15:666–71. https://doi.org/10.1007/s11367-010-0201-6.Suche in Google Scholar
33. Wernet, G, Bauer, C, Steubing, B, Reinhard, J, Moreno-Ruiz, E, Weidema, B. The ecoinvent database version 3 (part I): overview and methodology. Int J Life Cycle Assess 2016:1218–1230.10.1007/s11367-016-1087-8Suche in Google Scholar
34. Althaus, H-J, Bauer, C, Doka, G, Dones, R, Frischknecht, R, Hellweg, S, et al.. Implementation of life cycle impact assessment methods. St. Gallen, Switzerland: Swiss Centre for Life Cycle Inventories; 2010.Suche in Google Scholar
35. Linnhoff, B, Ahmad, S. Supertargeting: optimum synthesis of energy management systems. J Energy Resour Technol 1989;111:121. https://doi.org/10.1115/1.3231413.Suche in Google Scholar
36. Chemstations. Chemstations | offering CHEMCAD chemical process simulation software; 2020. Available from: https://www.chemstations.com/.Suche in Google Scholar
37. Olsen, D. Pinch software development; 2013.Suche in Google Scholar
38. FEFCO. Corrugated board production. European Database for Corrugated Board Life Cycle Studies; 2019. Available from: https://www.fefco.org/lca.Suche in Google Scholar
39. PlasticsEurope. Polyolefins. About plastics; 2020. Available from: https://www.plasticseurope.org/en/about-plastics/what-are-plastics/large-family/polyolefins#:∼:text=Polyolefins are a family of,popular plastics in use today.Suche in Google Scholar
© 2021 Walter de Gruyter GmbH, Berlin/Boston
Artikel in diesem Heft
- Frontmatter
- Editorial
- CPPM special issue in honour of Emeritus Professor W.Y. “Bill” Svrcek
- Research Articles
- Asphaltene precipitation from heavy oil mixed with binary and ternary solvent blends
- Kinetic modeling of biosurfactant production by Bacillus subtilis N3-1P using brewery waste
- A user workflow for combining process simulation and pinch analysis considering ecological factors
- An improved Wilson equation for phase equilibrium K values estimation
- Process model correlating Athabasca bitumen thermally cracked at edge of coking induction zone
- Flexible digital twins from commercial off-the-shelf software solutions: a driver for energy efficiency and decarbonisation in process industries?
Artikel in diesem Heft
- Frontmatter
- Editorial
- CPPM special issue in honour of Emeritus Professor W.Y. “Bill” Svrcek
- Research Articles
- Asphaltene precipitation from heavy oil mixed with binary and ternary solvent blends
- Kinetic modeling of biosurfactant production by Bacillus subtilis N3-1P using brewery waste
- A user workflow for combining process simulation and pinch analysis considering ecological factors
- An improved Wilson equation for phase equilibrium K values estimation
- Process model correlating Athabasca bitumen thermally cracked at edge of coking induction zone
- Flexible digital twins from commercial off-the-shelf software solutions: a driver for energy efficiency and decarbonisation in process industries?