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Process Design and Technoeconomic Analysis for the
Downstream Recovery and Purification of Diethyl Malonate
Team 7
Chris Bilham
Brian Coventry
Mark Kelsic
Yekaterina Pokhilchuk
Dan Sriratanasathavorn
Matthew Lipscomb, PhD.
CEO & Founder
DMC Limited
❖ Agenda
• Introduction
• Project Goals
• Purification Method 1
• Purification Method 2
• Environmental
• Economics
• Conclusions
• Acknowledgements
diethyl malonate
Image from:
http://www.sigmaaldrich.com/catalog/product/aldrich
/d97754?lang=en&region=US
http://www.directindustry.com/prod/solaris-biotechnology/product-54387-443440.html https://en.wikipedia.org/wiki/Malonic_acid
http://culmotrialattorneys.com/bpa-may-alter-gene-regulation/ https://en.wikipedia.org/wiki/Continuous_stirred-tank_reactor
Uses
● pharmaceuticals
● fragrances
● dyes
● adhesives
❖ Diethyl Malonate (DEM)
❖ Project Goal Statement
Two methods for purification of diethyl malonate (DEM)
from a fermentation reactor are to be designed and
economically analyzed.
Deliverables
● Economical, environmental, and safety analysis
DEM production specifications
● 10,000,000 kg/year
● >99% purity
Image from:
http://www.sigmaaldrich.com/catalog/product/aldrich/d
97754?lang=en&region=US
❖ Experimental Data and Solvent Selection
Models:
● Decanter
● LLE & distillation
Solvent Selection:
● Separation factor
● Boiling point
● Cost
Solvent of choice - Pentane
K = 2.64 (DEM in petane-
water solution)
❖ Method 1 - Decant
Assumptions:
● No salts entrain with the water to the
evaporator
● No salts entrain with the DEM product
● All salts leave with waste stream
❖ Method 1 - Decant
❖ Method 2 - Liquid-Liquid Extraction (LLE)
Assumptions:
● Salts do not enter pentane phase
● Water does not enter pentane phase
● Pentane does not enter water phase
❖ Method 2 - Liquid-Liquid Extraction (LLE)
❖ Series Process - Decanting followed by LLE
❖ Environmental and Safety
Hazardous Waste
● Listed by the EPA
● Ignitability
● Corrosivity
● Reactivity
● Toxicity
Safety
● 12 M HCl is extremely corrosive
● 1 M NaOH
Image from: http://rapidwasteenviro.com/wp-
content/uploads/2014/12/hazardous-waste-types.png
❖ Wastewater
Image from: http://lasvegaszipcodes.org/wp-
content/uploads/2013/01/bouldercityzipcodemap.jp
g
Industrial Wastewater for Boulder
● Permit $7,050 per year
● Publicly owned treatment works
(POTW)
● Specific pollutant limitation
● pH 5.5- 10
● $70 per 1000 gallons
❖ Operating expense sensitivity analysis parameters
Parameters that were investigated:
● Feed DEM production price
● Feed stream DEM %
● LLE column stages
● LLE column solvent to feed ratio
● Decanter pH
● Decanter temperature
Note: The following slides to not take into account waste
disposal fees which did not vary during sensitivity analysis
❖ Sensitivity to feed composition and price
• Series Process is cheapest at
every condition
• Solid line shows low DEM
production price ($1.90/kg)
• Dotted line shows high DEM
production price ($3.10/kg)
❖ Operating cost breakdown
Series Process Only LLE Only Decant
99.95% DEM recovery 99.96% DEM recovery 94.76% DEM recovery
• Distillation represents the biggest operational expense
• DEM sent to waste considered an operational expense
❖ Liquid-Liquid Extraction sensitivity
• Careful balance between
losing DEM and distillation
costs
• Increasing LLE stages lowers
operating costs but increases
capital costs
• Series Process most
economical at 99.1%
recovery in LLE unit
Increasing DEM recovery
Increasing distillation costs
Series Process
❖ Decanter sensitivity
• Most economical to not
change temperature of feed
• Decreasing pH lowers DEM
solubility in water
• Process economics may
continue to improve at lower
pH
Series Process
❖ Effect of wastewater treatment
• Boulder has very expensive wastewater prices
• Wastewater increases the unit operating cost by a constant
amount for each process
Series Process Only LLE Only Decant
+$0.11/kg+$0.11/kg +$0.14/kg
❖ Economics
• Lowest initial capital investment is
for LLE only process.
• Lowest operational cost is for the
Series process
Adding in capital costs for equipment
and installation...
❖ Economics
• Fastest return on investment is always the LLE only,
when considering all associated costs.
❖ Conclusion
• Decanting alone is a poor choice.
• Series and LLE have similar operational costs
• Our model suggests that LLE is the best option including all
costs.
• Plant should be considered somewhere with lower waste
disposal costs.
• Capital costs should be further investigated to determine
tradeoff of long term operation against initial investment
• Further investigation into salting and pH effects on the
solubility of DEM is warranted.
❖ Acknowledgements
● Professor Thomas Belval - University of Colorado Boulder
● Dr. Mathew Lipscomb - DMC Limited
● Professor Rainer Volkamer - CU
● Dr. Molly Larsen - CU
● Zachary Finewax - CU
● Theodore Koenig - CU
❖ References
BMU (Bundesministerium für Umwelt, Naturschutz und Reaktorsicherheit),. (2016). Malonic Acid Diesters. Paris, France:
SIAM. Retrieved from http://www.inchem.org/documents/sids/sids/malonates.pdf
Characteristics of Hazardous Waste (CHW)) Subpart C- 261.32 (Hazardous wastes from specific sources.) .2012
https://www.gpo.gov/fdsys/pkg/CFR-2012-title40-vol27/xml/CFR-2012-title40-vol27-part261.xml#seqnum261.21
Dietrich, J., Fortman, J., & Steen, E. (2016). Recombinant host cells for the production of malonate. US.
Henley, E. J., Seader, J. D., & Roper, D. K. (2011). Separation process principles. Hoboken, NJ: Wiley.
Hernandez, M., & Abu-Dalo, M. (2016). Removing metals from solution using metal binding compounds and sorbents therefor.
US.
Lyons, J., White, C. W., & Loh, H. P. (2002). Process Equipment Cost Estimation Final Report (Rep.). NETL.
National Center for Biotechnology Information (NCBI). PubChem Compound Database; CID=6097028,
https://pubchem.ncbi.nlm.nih.gov/compound/6097028 (March 21, 2006).
National Center for Biotechnology Information (NCBI 2). PubChem Compound Database; CID=24450,
https://pubchem.ncbi.nlm.nih.gov/compound/24450 (March 15, 2006).
National Center for Biotechnology Information (NCBI 3). PubChem Compound Database; CID=516951,
https://pubchem.ncbi.nlm.nih.gov/compound/516951 (March 15, 2006).
National Center for Biotechnology Information (NCBI 4). PubChem Compound Database; CID=6097028,
https://pubchem.ncbi.nlm.nih.gov/compound/6097028 (March 15, 2006).
National Center for Biotechnology Information (NCBI 5). PubChem Compound Database; CID=311,
https://pubchem.ncbi.nlm.nih.gov/compound/311 (March 15, 2006).
National Center for Biotechnology Information (NCBI 6). PubChem Compound Database; CID=5727,
https://pubchem.ncbi.nlm.nih.gov/compound/5727 (March 15, 2006).
National Center for Biotechnology Information (NCBI 7). PubChem Compound Database; CID=5284359,
https://pubchem.ncbi.nlm.nih.gov/compound/5284359 (March 15, 2006).
Product and Process Design Principles: Synthesis, Analysis and Design. (2009). S.l.: John Wiley and Sons.
Protection of Environment. Code of Federal Regulations (CoFR), Title 40 - (n.d.). 2012, from
https://www.gpo.gov/fdsys/pkg/CFR-2012-title40-vol27/xml/CFR-2012-title40-vol27-part261.xml#seqnum261.21
❖ References
Susan E. Bailey, Trudy J. Olin, R.Mark Bricka, D.Dean Adrian, A review of potentially low-cost sorbents for heavy metals,
Water Research, Volume 33, Issue 11, August 1999, Pages 2469-2479, ISSN 0043-1354, http://dx.doi.org/10.1016/S0043-
1354(98)00475-8.
(http://www.sciencedirect.com/science/article/pii/S0043135498004758)
Yaws, Carl L.. (2012). Yaws' Handbook of Properties for Aqueous Systems. Knovel. Online version available at:
http://app.knovel.com/hotlink/toc/id:kpYHPAS006/yaws-handbook-properties/yaws-handbook-properties
Zeppieri, S., Rodriguez, J., & Lopez de Ramos, A. L. (2001). Interfacial Tension of Alkane and Water Systems. J. Chem. Eng.
Data, 1086-1088. Retrieved April/May, 2016, from http://pubs.acs.org/doi/pdf/10.1021/je000245r

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Finall PP Oral Presentation SrDesign

  • 1. Process Design and Technoeconomic Analysis for the Downstream Recovery and Purification of Diethyl Malonate Team 7 Chris Bilham Brian Coventry Mark Kelsic Yekaterina Pokhilchuk Dan Sriratanasathavorn Matthew Lipscomb, PhD. CEO & Founder DMC Limited
  • 2. ❖ Agenda • Introduction • Project Goals • Purification Method 1 • Purification Method 2 • Environmental • Economics • Conclusions • Acknowledgements diethyl malonate Image from: http://www.sigmaaldrich.com/catalog/product/aldrich /d97754?lang=en&region=US
  • 4. ❖ Project Goal Statement Two methods for purification of diethyl malonate (DEM) from a fermentation reactor are to be designed and economically analyzed. Deliverables ● Economical, environmental, and safety analysis DEM production specifications ● 10,000,000 kg/year ● >99% purity Image from: http://www.sigmaaldrich.com/catalog/product/aldrich/d 97754?lang=en&region=US
  • 5. ❖ Experimental Data and Solvent Selection Models: ● Decanter ● LLE & distillation Solvent Selection: ● Separation factor ● Boiling point ● Cost Solvent of choice - Pentane K = 2.64 (DEM in petane- water solution)
  • 6. ❖ Method 1 - Decant Assumptions: ● No salts entrain with the water to the evaporator ● No salts entrain with the DEM product ● All salts leave with waste stream
  • 7. ❖ Method 1 - Decant
  • 8. ❖ Method 2 - Liquid-Liquid Extraction (LLE) Assumptions: ● Salts do not enter pentane phase ● Water does not enter pentane phase ● Pentane does not enter water phase
  • 9. ❖ Method 2 - Liquid-Liquid Extraction (LLE)
  • 10. ❖ Series Process - Decanting followed by LLE
  • 11. ❖ Environmental and Safety Hazardous Waste ● Listed by the EPA ● Ignitability ● Corrosivity ● Reactivity ● Toxicity Safety ● 12 M HCl is extremely corrosive ● 1 M NaOH Image from: http://rapidwasteenviro.com/wp- content/uploads/2014/12/hazardous-waste-types.png
  • 12. ❖ Wastewater Image from: http://lasvegaszipcodes.org/wp- content/uploads/2013/01/bouldercityzipcodemap.jp g Industrial Wastewater for Boulder ● Permit $7,050 per year ● Publicly owned treatment works (POTW) ● Specific pollutant limitation ● pH 5.5- 10 ● $70 per 1000 gallons
  • 13. ❖ Operating expense sensitivity analysis parameters Parameters that were investigated: ● Feed DEM production price ● Feed stream DEM % ● LLE column stages ● LLE column solvent to feed ratio ● Decanter pH ● Decanter temperature Note: The following slides to not take into account waste disposal fees which did not vary during sensitivity analysis
  • 14. ❖ Sensitivity to feed composition and price • Series Process is cheapest at every condition • Solid line shows low DEM production price ($1.90/kg) • Dotted line shows high DEM production price ($3.10/kg)
  • 15. ❖ Operating cost breakdown Series Process Only LLE Only Decant 99.95% DEM recovery 99.96% DEM recovery 94.76% DEM recovery • Distillation represents the biggest operational expense • DEM sent to waste considered an operational expense
  • 16. ❖ Liquid-Liquid Extraction sensitivity • Careful balance between losing DEM and distillation costs • Increasing LLE stages lowers operating costs but increases capital costs • Series Process most economical at 99.1% recovery in LLE unit Increasing DEM recovery Increasing distillation costs Series Process
  • 17. ❖ Decanter sensitivity • Most economical to not change temperature of feed • Decreasing pH lowers DEM solubility in water • Process economics may continue to improve at lower pH Series Process
  • 18. ❖ Effect of wastewater treatment • Boulder has very expensive wastewater prices • Wastewater increases the unit operating cost by a constant amount for each process Series Process Only LLE Only Decant +$0.11/kg+$0.11/kg +$0.14/kg
  • 19. ❖ Economics • Lowest initial capital investment is for LLE only process. • Lowest operational cost is for the Series process Adding in capital costs for equipment and installation...
  • 20. ❖ Economics • Fastest return on investment is always the LLE only, when considering all associated costs.
  • 21. ❖ Conclusion • Decanting alone is a poor choice. • Series and LLE have similar operational costs • Our model suggests that LLE is the best option including all costs. • Plant should be considered somewhere with lower waste disposal costs. • Capital costs should be further investigated to determine tradeoff of long term operation against initial investment • Further investigation into salting and pH effects on the solubility of DEM is warranted.
  • 22. ❖ Acknowledgements ● Professor Thomas Belval - University of Colorado Boulder ● Dr. Mathew Lipscomb - DMC Limited ● Professor Rainer Volkamer - CU ● Dr. Molly Larsen - CU ● Zachary Finewax - CU ● Theodore Koenig - CU
  • 23. ❖ References BMU (Bundesministerium für Umwelt, Naturschutz und Reaktorsicherheit),. (2016). Malonic Acid Diesters. Paris, France: SIAM. Retrieved from http://www.inchem.org/documents/sids/sids/malonates.pdf Characteristics of Hazardous Waste (CHW)) Subpart C- 261.32 (Hazardous wastes from specific sources.) .2012 https://www.gpo.gov/fdsys/pkg/CFR-2012-title40-vol27/xml/CFR-2012-title40-vol27-part261.xml#seqnum261.21 Dietrich, J., Fortman, J., & Steen, E. (2016). Recombinant host cells for the production of malonate. US. Henley, E. J., Seader, J. D., & Roper, D. K. (2011). Separation process principles. Hoboken, NJ: Wiley. Hernandez, M., & Abu-Dalo, M. (2016). Removing metals from solution using metal binding compounds and sorbents therefor. US. Lyons, J., White, C. W., & Loh, H. P. (2002). Process Equipment Cost Estimation Final Report (Rep.). NETL. National Center for Biotechnology Information (NCBI). PubChem Compound Database; CID=6097028, https://pubchem.ncbi.nlm.nih.gov/compound/6097028 (March 21, 2006). National Center for Biotechnology Information (NCBI 2). PubChem Compound Database; CID=24450, https://pubchem.ncbi.nlm.nih.gov/compound/24450 (March 15, 2006). National Center for Biotechnology Information (NCBI 3). PubChem Compound Database; CID=516951, https://pubchem.ncbi.nlm.nih.gov/compound/516951 (March 15, 2006). National Center for Biotechnology Information (NCBI 4). PubChem Compound Database; CID=6097028, https://pubchem.ncbi.nlm.nih.gov/compound/6097028 (March 15, 2006). National Center for Biotechnology Information (NCBI 5). PubChem Compound Database; CID=311, https://pubchem.ncbi.nlm.nih.gov/compound/311 (March 15, 2006). National Center for Biotechnology Information (NCBI 6). PubChem Compound Database; CID=5727, https://pubchem.ncbi.nlm.nih.gov/compound/5727 (March 15, 2006). National Center for Biotechnology Information (NCBI 7). PubChem Compound Database; CID=5284359, https://pubchem.ncbi.nlm.nih.gov/compound/5284359 (March 15, 2006). Product and Process Design Principles: Synthesis, Analysis and Design. (2009). S.l.: John Wiley and Sons. Protection of Environment. Code of Federal Regulations (CoFR), Title 40 - (n.d.). 2012, from https://www.gpo.gov/fdsys/pkg/CFR-2012-title40-vol27/xml/CFR-2012-title40-vol27-part261.xml#seqnum261.21
  • 24. ❖ References Susan E. Bailey, Trudy J. Olin, R.Mark Bricka, D.Dean Adrian, A review of potentially low-cost sorbents for heavy metals, Water Research, Volume 33, Issue 11, August 1999, Pages 2469-2479, ISSN 0043-1354, http://dx.doi.org/10.1016/S0043- 1354(98)00475-8. (http://www.sciencedirect.com/science/article/pii/S0043135498004758) Yaws, Carl L.. (2012). Yaws' Handbook of Properties for Aqueous Systems. Knovel. Online version available at: http://app.knovel.com/hotlink/toc/id:kpYHPAS006/yaws-handbook-properties/yaws-handbook-properties Zeppieri, S., Rodriguez, J., & Lopez de Ramos, A. L. (2001). Interfacial Tension of Alkane and Water Systems. J. Chem. Eng. Data, 1086-1088. Retrieved April/May, 2016, from http://pubs.acs.org/doi/pdf/10.1021/je000245r