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Process Intensification for the Green Solvent Ethyl Lactate Production based on Simulated Moving Bed and
Pervaporation Membrane Reactors
A Dissertation Presented to the Faculdade de Engenharia da Universidade do Porto
for the degree of PhD in Chemical and Biological Engineering
by
Carla Sofia Marques Pereira
Supervised by Professor Alírio Egídio Rodrigues and
Dr. Viviana Manuela Tenedório Matos da Silva
Laboratory of Separation and Reaction Engineering, Associate Laboratory LSRE/LCM
Department of Chemical Engineering, Faculty of Engineering, University of Porto
October 2009
FEUP-LSRE/LCM - Universidade do Porto
© Carla Sofia Marques Pereira, 2009
All rights reserved
Acknowledgements
First of all, I want to thank my supervisors, Professor Alírio Rodrigues and Dr Viviana Silva.
Professor Alírio, thank you for all the friendship, constant support and for always challenging
me to reach higher goals within my work. Dr. Viviana, I want to thank you for all the
encouragement, motivation, constant support, for all the long discussions and great ideas that
make me go further and further within my work, and, also, for being a truly and special
friend.
I am very grateful to Professor Simão Pinho, for the friendship and all the support in the
framework of the project “POCI/EQU/61580/2004” and to Professor Madalena Dias for the
support whenever needed.
To all my LSRE colleagues, especially Israel Pedruzzi, Pedro Sá Gomes, Michael Zabka,
João Santos, Miguel Granato, João Pedro Lopes, Alexandre Ferreira and Nuno Lourenço for
the friendship, collaboration, and support whenever I needed.
To my primary school teacher, Professor João Aveiro, for always believing in me and keeping
me motivated along the years.
To Fundação para a Ciência e Tecnologia, for the financial support (Research Fellowship:
SFRH / BD / 23724 / 2005).
To Sofia Rodrigues, Marta Abrantes, Fátima Mota, Miguel Teixeira and Nuno Garrido for all
the great moments spent after work!!!
Last, but not least, I would deeply like to thank my family and friends, for all giving love,
support and trust, especially to my grandmother, Dulcelina, that will always stay in my heart.
To my parents and sisters
“Green chemistry represents the pillars that hold up our sustainable future. It is
imperative to teach the value of green chemistry to tomorrow’s chemists.”
Daryle Busch, President of the American Chemical Society (June 26, 2000)
Resumo
O principal objectivo deste trabalho foi o desenvolvimento de um novo processo eficiente para a
produção do solvente verde, lactato de etilo, através da reacção de esterificação entre etanol e
ácido láctico, utilizando tecnologias híbridas de reacção/separação baseadas em reactores de leito
móvel simulado e processos de membranas por pervaporação. De forma a atingir a meta proposta,
foram abordados os seguintes temas:
Aquisição de dados fundamentais: A resina de permuta iónica, Amberlyst 15-wet, foi avaliada
tanto como catalisador para a reacção de esterificação, como adsorvente selectivo para a água. Os
dados cinéticos e de equilíbrio da reacção foram medidos, na gama de temperaturas 50ºC-90ºC, e
usados para a determinação da constante de equilíbrio e da lei cinética da reacção como função da
temperatura, baseadas em actividades descritas pelo modelo UNIQUAC. Os dados de adsorção
foram também medidos, a 20ºC e a 50ºC, e ajustados a uma isotérmica de Langmuir
multicomponente, tendo-se assumido uma capacidade volumétrica da monocamada igual para
todas as espécies, reduzindo o número de parâmetros de ajuste de 8 para 5, para cada temperatura.
Membranas comerciais hidrófilas da Pervatech foram avaliadas para a desidratação do etanol,
ácido láctico e lactato de etilo, por pervaporação. As permeâncias de todas as espécies foram
determinadas em função da composição e temperatura na gama 48ºC-72ºC.
Intensificação de processo: Modelos matemáticos, considerando resistências internas e externas à
transferência de massa e velocidade variável devido à mudança das propriedades da mistura
multicomponente, foram desenvolvidos para reactores cromatográficos — reactores de leito fixo e
de leito móvel simulado, SMBR — e validados pelos dados experimentais. O modelo matemático
do reactor de membranas por pervaporação, PVMR, considera, adicionalmente, a permeação
através da membrana, os efeitos de polarização por concentração e temperatura e operação não
isotérmica. A avaliação teórica do comportamento da unidade SMBR foi realizada para analisar o
efeito da configuração, da composição da alimentação e tempo de comutação nas regiões de
separação/reacção e/ou no desempenho do processo nos pontos operacionais óptimos. O
desempenho do PVMR foi avaliado para operação isotérmica e não isotérmica, e foram
determinadas condições apropriadas para a maximização quer da conversão do ácido láctico quer
da pureza do lactato de etilo. Finalmente, uma nova tecnologia foi desenvolvida e submetida a
registo de patente, o reactor de membranas de leito móvel simulado, PermSMBR, o qual integra
membranas selectivas dentro das colunas do SMBR.
Abstract
The main objective of this work was the development of a new efficient process to produce the
green solvent ethyl lactate from the esterification reaction between ethanol and lactic acid by
using hybrid reaction/separation technologies based on simulated moving bed reactors and
pervaporation membrane processes. To accomplish this target, the following topics were
addressed:
Basic data acquisition: The acidic ion exchange resin Amberlyst 15-wet was evaluated as both
catalyst for esterification and selective adsorbent for water. Equilibrium and kinetic data were
measured in the temperature range 50-90ºC, and used to obtain the equilibrium constant and
kinetic law as function of temperature, which are based on liquid activities described by the
UNIQUAC model. Adsorption data was also obtained and fitted to a multi-component Langmuir
isotherm assuming a constant monolayer capacity in terms of volume for all species, reducing the
adjustable parameters from 8 to 5, for each temperature. Pervatech hydrophilic commercial
membranes were evaluated for the dehydration of ethanol, lactic acid and ethyl lactate, by
pervaporation. The permeances of all species were determined as function of composition and
temperature in the range 48-72ºC.
Process intensification: Mathematical models, considering external and internal mass-transfer
resistances and velocity variations due to the change of multi-component mixture properties, were
developed for chromatographic reactors — fixed bed and simulated moving bed reactor, SMBR
— and validated by experimental data. The pervaporation membrane reactor, PVMR, model also
takes into account, the permeation through the membrane, concentration and temperature
polarization effects, and non-isothermal operation. The theoretical assessment of the SMBR unit
behaviour was performed to analyse the effect of SMBR configuration, feed composition and
switching time on the reactive/separation regions and/or on the process performance at the
optimal operating points. The performance of the PVMR was evaluated for isothermal and non-
isothermal operation, and suitable conditions for maximization of both lactic acid conversions and
ethyl lactate purity were examined. Finally, a new technology was developed and submitted to
patent registration, the simulated moving bed membrane reactor, PermSMBR, which integrates
perm-selective membranes inside the SMBR columns.
Zusammenfassung
Ziel dieser Arbeit war es einen völlig neuartigen und effizienten Prozess für die Produktion von
“Grünem Lösungsmittel” und Ethyl-Lakton, mittels der Verästerung aus Ethanol und Milchsäure über
die Hybrid-Technologie, zu entwickeln. Die Reaktion/Trennung basiert auf simulierten
Fliessbettreaktoren und Membranprozessen mittels Pervaporization. Um diese Zielsetzung zu
erreichen, wurden folgende Themen diskutiert:
Folgende wichtige Daten wurden gesammelt: Für den Ionen-Austausch wurde das Harz, Amberlyst
15-wet, genutzt. Es wurde sowohl als Katalysator für die Reaktivverästherung, wie auch als selektiver
Adsorbent für Wasser ausgewertet. Die Kinetischen- und chemischen Gleichgewichtsdaten wurden
zwischen 50ºC und 90ºC gemessen. Als Vorlage für die Bestimmung der chemischen
Gleichgewichtskonstante wie auch der Kinetik als Funktion der Temperatur, wurde das UNIQUAC
Model genutzt. Die Adsorptionsdaten wurden zwischen 20ºC und 50ºC gemessen, und entsprechend
einer Langmuir-Isotherme für Multikomponenten angeglichen, wobei eine gleich grosse
Volumenkapazität der Monoschicht für alle Spezies angenommen wurde. Die Anzahl der zu
justierenden Parameter wurde hierbei für jede Temperatur von 8 auf 5 reduziert. Kommerzielle
hydrophile Membranen der Firma Pervatech wurden für die Dehydratisierung von Ethanol,
Milchsäure und Ethyllakton mittels Permeation ausgewertet. Die Permeation aller Spezies wurde als
Funktion der Zusammensetzung und Temperatur, zwischen 48ºC und 72ºC ermittelt.
Intensivierung des Prozesses: Es wurden mathematische Modelle für chromatographische Reaktoren
entwickelt (Modelierte Festbett- und Fliessbettreaktoren SMBR) und experimentell ausgewärtet, unter
Berücksichtigung des internen und externen Massenaustausches, sowie der variablen
Geschwindigkeiten. Es herrschen unterschiedlichen Vermischungseigenschaften der
Multikomponenten. Das mathematische Modell der Pervaporationsmembrane (PVMR) berücksichtigt
gleichfalls die folgenden Effekte: Polarization aufgrund von Temperatur- und
Konzentrationsgradienten sowie nicht-isotherme Reaktionsführung. Das theoretische Verhalten der
SMBR Einheit wurde unter Berücksichting der Konfiguration, der Mischungszusammensetzung beim
Eintritt und der Komutationszeit in den Trennungs- und Reaktionszonen und/oder für die
Prozessleistung an den operationallen Optima ausgewertet. Der Wirkungsgrad der PVMR wurde für
den isothermen und nicht-isothermen Betrieb ermittelt, und es wurden entsprechende Bedingungen für
den maximale Umsatz der Milchsäure und der maximalen Reinheit für Ethyl-Lakton bestimmt. Der
lezte Schritt war die Entwicklung einer neuen Technolgie, ein Membranreaktor mit simuliertem
Fliessbett (PermSMBR), welche als Patent angemeldet wurde. Dieser Reaktor integriert selektive
Membranen innerhalb der SMBR Säule.
Table of contents Pag. 1. Introduction .......................................................................................................................1
1.1 Relevance and Motivation..........................................................................................1 1.2 Objectives and Outline ...............................................................................................3
2. State of the art on Green Solvent Ethyl Lactate.............................................................5
2.1 Green Chemistry ........................................................................................................5 2.2 Ethyl lactate applications ...........................................................................................7 2.2.1 Solvent Market Analysis ................................................................................................................. 8 2.3 Synthesis of ethyl lactate............................................................................................9 2.3.1 Renewable Resources.................................................................................................................... 11
2.3.1.1 Ethanol Platform................................................................................................................................. 12 2.3.1.2 Lactic acid Platform............................................................................................................................ 13
2.3.2 Patented Processes Overview........................................................................................................ 13 2.3.3 Reactive Separations ..................................................................................................................... 16
2.3.3.1 Reactive Distillation (RD) .................................................................................................................. 17 2.3.3.2 Simulated Moving Bed Reactor (SMBR) ........................................................................................... 19 2.3.3.3 Pervaporation Membrane Reactor (PVMR)........................................................................................ 21
2.4 References ................................................................................................................26 3. Batch Reactor: Thermodynamic Equilibrium and Reaction Kinetics.......................35
3.1 Introduction ..............................................................................................................36 3.2 Experimental Section ...............................................................................................40 3.2.1 Chemicals and Catalyst ................................................................................................................. 40 3.2.2 Experimental set-up....................................................................................................................... 41 3.2.3 Analytical method ......................................................................................................................... 42 3.3 Thermodynamic Equilibrium Results ......................................................................42 3.3.1 Thermodynamic equilibrium constant........................................................................................... 42
3.3.1.1 Activity coefficients estimation .......................................................................................................... 44 3.3.2 Equilibrium constant and reaction enthalpy for the synthesis of Ethyl Lactate............................. 45 3.3.3 Application of this methodology to other works ........................................................................... 47 3.4 Kinetic Studies .........................................................................................................49 3.4.1 Preliminary Studies ....................................................................................................................... 50
3.4.1.1 Evaluation of external mass transfer limitations (effect of stirring speed).......................................... 50 3.4.1.2 Evaluation of internal mass transfer limitations (effect of particle size) ............................................. 50 3.4.1.3 Evaluation of catalyst deactivation (effect of catalyst reusability)...................................................... 51
3.4.2 Kinetic Model................................................................................................................................ 52 3.4.2.1 Parameter estimation from experimental data..................................................................................... 54
3.4.3 Modelling and discussion of results .............................................................................................. 55 3.4.3.1 Effect of catalyst loading .................................................................................................................... 56 3.4.3.2 Effect of initial molar ratio of reactants .............................................................................................. 57 3.4.3.3 Effect of reaction temperature............................................................................................................. 58
ii TABLE OF CONTENTS
3.4.3.4 Effect of Lactic acid and Ethyl Lactate oligomers...............................................................................58 3.4.3.5 Effect of polar species .........................................................................................................................62
3.5 Conclusions.............................................................................................................. 63 3.6 Notation.................................................................................................................... 64 3.7 References Cited ...................................................................................................... 66
4. Fixed Bed Adsorptive Reactor....................................................................................... 71
4.1 Introduction.............................................................................................................. 72 4.2 Experimental Section ............................................................................................... 73 4.2.1 Chemicals and Catalyst / Adsorbent ............................................................................................. 73 4.2.2 Experimental Apparatus................................................................................................................ 74
4.2.2.1 Bed Porosity and Peclet Number .........................................................................................................75 4.3 Modelling of Fixed Bed ........................................................................................... 76 4.3.1 Multi-component viscosity ........................................................................................................... 81 4.4 Results and Discussion ............................................................................................ 84 4.4.1 Adsorption Isotherm ..................................................................................................................... 84
4.4.1.1 Binary Adsorption experiments ...........................................................................................................85 4.4.2 Kinetic experiments ...................................................................................................................... 90
4.4.2.1 Fixed Bed Reactor ...............................................................................................................................90 4.5 Conclusions.............................................................................................................. 94 4.6 Notation.................................................................................................................... 94 4.7 References................................................................................................................ 97
5. Simulated Moving Bed Reactor................................................................................... 101
5.1 Introduction............................................................................................................ 102 5.2 Modelling Strategies .............................................................................................. 104 5.2.1 SMBR mathematical model ........................................................................................................ 104 5.2.2 SMBR performance parameters.................................................................................................. 108 5.2.3 Numerical Solution ..................................................................................................................... 108 5.3 Experimental Section ............................................................................................. 109 5.3.1 Chemicals and Catalyst / Adsorbent ........................................................................................... 109 5.3.2 The SMBR LICOSEP 12-26 Unit............................................................................................... 109 5.4 Results and Discussion .......................................................................................... 111 5.4.1 Experimental Results .................................................................................................................. 111 5.4.2 Simulated results......................................................................................................................... 115
5.4.2.1 Comparison of SMBR and TMBR models ........................................................................................115 5.4.2.2 Reactive/separation regions ...............................................................................................................116 5.4.2.3 Separation Region vs Reactive/Separation Region............................................................................117 5.4.2.4 Effect of the Feed Composition .........................................................................................................118 5.4.2.5 Effect of the SMBR columns arrangement ........................................................................................120 5.4.2.6 Effect of Switching Time...................................................................................................................121
5.5 Conclusions............................................................................................................ 123 5.6 Notation.................................................................................................................. 124 5.7 References Cited .................................................................................................... 127
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION iii
6. Pervaporation Membrane Reactor..............................................................................131 6.1 Introduction ............................................................................................................132 6.2 Experimental Section .............................................................................................135 6.2.1 Materials...................................................................................................................................... 135 6.2.2 Pervaporation Membrane Reactor Unit....................................................................................... 135 6.3 Pervaporation Studies.............................................................................................136 6.3.1 Pervaporation Transport .............................................................................................................. 137 6.3.2 Preliminary Studies ..................................................................................................................... 138
6.3.2.1 Evaluation of the membrane quality ................................................................................................. 138 6.3.2.2 Evaluation of mass transfer limitations in the boundary layer .......................................................... 139
6.3.3 Detailed Studies .......................................................................................................................... 140 6.3.3.1 Water/Ethanol System ...................................................................................................................... 140 6.3.3.2 Water/Ethyl lactate System............................................................................................................... 140 6.3.3.3 Water/Lactic acid System ................................................................................................................. 141 6.3.3.4 Membrane performance evaluation................................................................................................... 141
6.3.4 Parameters estimation ................................................................................................................. 143 6.3.4.1 Permeance temperature dependence ................................................................................................. 143 6.3.4.2 Permeance temperature and water content dependence .................................................................... 144 6.3.4.3 Estimation of the boundary layer mass transfer coefficient (kbl)....................................................... 148
6.4 Modelling ...............................................................................................................149 6.4.1 Batch Pervaporation Model......................................................................................................... 149 6.4.2 Pervaporation Membrane Reactor model .................................................................................... 152 6.5 Results and Discussion...........................................................................................155 6.5.1 Batch Pervaporation .................................................................................................................... 155 6.5.2 Pervaporation Membrane Reactor............................................................................................... 157 6.6 Conclusions ............................................................................................................161 6.7 Notation..................................................................................................................162 6.8 References ..............................................................................................................165
7. PermSMBR – A New Hybrid Technology ..................................................................171
7.1 Introduction ............................................................................................................172 7.2 Technical description of the PermSMBR technology............................................174 7.3 PermSMBR mathematical model...........................................................................178 7.4 PermSMBR geometrical specifications .................................................................181 7.5 Simulated Results...................................................................................................182 7.5.1 Reactive/Separation Region: PermSMBR vs SMBR .................................................................. 183 7.5.2 PermSMBR 3 zones .................................................................................................................... 184 7.5.3 Comparison between PermSMBR, SMBR and RD technologies ............................................... 187 7.6 Conclusions ............................................................................................................187 7.7 Notation..................................................................................................................188 7.8 References ..............................................................................................................191
8. Conclusions and Suggestions for Future Work..........................................................193 APPENDIX A. Safety Data ..................................................................................................A1
iv TABLE OF CONTENTS
APPENDIX B. Thermodynamic Properties ...................................................................... B1 APPENDIX C. Calibration ................................................................................................. C1 APPENDIX D. Binary adsorption experiments at 293.15 K ........................................... D1
1. Introduction
1.1 Relevance and Motivation
Petroleum (“black gold”) is at the heart of today’s economics and politics problems. The
traditional petroleum reserves are in decline; moreover, the environmental regulation is every
day more severe, being, therefore, a great challenge to the design and implementation of
green products and processes.
Green solvents, which are produced from the processing of agricultural crops, were
developed as a more environmentally friendly alternative to petrochemical solvents. Lactate
esters solvents are 100% biodegradable, easy to recycle, non-corrosive, non-carcinogenic and
non-ozone depleting. Lactate esters have found industrial applications in specialty coatings,
inks, cleaners and straight cleaning use.
Ethyl lactate is a green solvent derived from nature-based feedstocks and it is so benign that
the U.S. Food and Drug Administration approved its use in food products. Ethyl lactate could
replace a range of environment-damaging halogenated and toxic solvents, including ozone-
depleting chlorofluorocarbons, carcinogenic methylene chloride, and toxic ethylene glycol
ethers and chloroform. In Figure 1.1 the ethyl lactate life-cycle is shown.
Ethyl lactate is produced from the esterification of lactic acid with ethanol through a
reversible reaction, having water as a by-product. Traditionally, ethyl lactate is synthesized in
a reactor followed by separation units in order to recover it, to remove the by-product (water)
and to recycle the unconverted reactants to the reactor; however, this represents high costs.
The objective of this work is to study equipments and techniques that are more compact,
2 CHAPTER 1. Introduction
energy efficient, and environment-friendly sustainable processes for the ethyl lactate
production.
From NatureTo
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Figure 1.1- Ethyl Lactate life-cycle.
Process intensification, regarding the integration of reaction and separation processes into a
single device, provides the most feasible engineering solution to the sustainable synthesis of
ethyl lactate, since at least one of the products is being removed from the reaction medium to
lead to depletion of the limiting reactant. In this perspective, continuous chromatographic
reactor and membrane reactor will be considered for ethyl lactate production, namely the
Simulated Moving Bed Reactor (SMBR) and the Pervaporation Membrane Reactor (PVMR),
respectively. The SMBR is a competitive technology for systems involving equilibrium
controlled reactions catalysed by ion exchange resins, which are also selective adsorbent for
water (the by-product formed in the ethyl lactate synthesis), given that the products are
formed and simultaneously separated and removed from the reaction medium. The PVMR
technology is a clean and economic alternative to conventional processes, since equilibrium
could be shifted by continuously removing water through a selective membrane, allowing
costs reduction and higher product purity. Combining the advantages of both technologies,
finally, a new hybrid technology will be developed, the Simulated Moving Bed Membrane
Reactor (SMBMembR or PermSMBR) that combines a reactor with two different separation
techniques into a single device: continuous counter-current chromatography (SMB) with a
selective permeable membrane (Pervaporation or Permeation).
PROCESSES INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 3
1.2 Objectives and Outline
The main goal of this work is the development of a process for simultaneous reaction and
separation in a single device for ethyl lactate production with a high purity, yield and
complete reactants conversion. Three technologies will be studied: the Simulated Moving
Bed Reactor (SMBR) using a catalyst that is also a selective adsorbent for water/ethyl lactate
separation, the Pervaporation Membrane Reactor (PVMR) using a hydrophilic water
permselective membrane for continuous removal of the by-product water and the Simulated
Moving Bed Membrane Reactor (PermSMBR), where the SMBR is integrated with the
PVMR by using selective permeable membranes inside the columns of the SMBR.
The thesis comprises 8 chapters dealing with different aspects of ethyl lactate production, in
addition to the present one.
In Chapter 2, the state of the art of production process aspects as patented processes for esters
production; the advantages of heterogeneous catalyst, such as ion-exchange resins; the
methods used to displace equilibrium towards ester formation are addressed. An overview in
some reactive separations as reactive distillation, chromatographic reactors and membrane
reactors applied to the production of oxygenates is reviewed in order to improve the overall
efficiency of the process of ethyl lactate synthesis.
Chapter 3 addresses the kinetic studies for ethyl lactate production by heterogeneous
catalysis; the influence of catalyst loading, temperature and initial molar ratio of reactants are
analysed. A methodology based in the UNIQUAC model for determination of the
thermodynamic equilibrium constant is developed.
Experimental and simulated results for the ethyl lactate production in a fixed bed adsorptive
reactor are shown in Chapter 4. Dynamic adsorption experiments of binary non-reactive
mixtures were performed in order to obtain multicomponent adsorption equilibrium isotherms
of Langmuir type. The reaction kinetics and adsorption data were used in the mathematical
model of the adsorptive reactor, which also included axial dispersion, velocity variations and
external and internal mass-transfer resistances.
In Chapter 5, the simulated moving bed reactor technology for the ethyl lactate production is
evaluated by experiments as well as by simulations. In order to describe the dynamic
behaviour of this unit, a mathematical model considering external and internal mass-transfer
resistances and variable velocities is developed. The influence of operational parameters, as
4 CHAPTER 1. Introduction
feed composition, SMBR configuration and switching time, on the SMBR performance is
presented.
Pervaporation processes using hydrophilic silica membranes are evaluated in Chapter 6 for
the ethyl lactate system. The effects of feed composition and operating temperature on the
membrane performance are analyzed. Mathematical models, considering concentration and
temperature polarization and non-isothermal effects, are developed and applied to analyze the
performance of batch pervaporation and continuous pervaporation membrane reactor, in both
isothermal and non-isothermal conditions.
In Chapter 7, a new technology, the simulated moving bed membrane reactor, is presented
and applied for the ethyl lactate synthesis. The potential of this new equipment is
demonstrated by comparing its performance to other reactive separation processes.
Finally, the general conclusions drawn from this work and the suggestions for future work
will be presented in Chapter 8.
2. State of the art on Green Solvent Ethyl Lactate
In this chapter, a review on the green chemistry principles is made and a literature survey on
applications of ethyl lactate and production processes (renewable resources, patents, reactive
separations) is presented.
2.1 Green Chemistry
Green chemistry is the best use of chemistry for pollution prevention. More specifically,
green chemistry is the design of chemical products and processes that reduce or eliminate the
use and generation of hazardous substances. It is a highly effective approach to pollution
prevention because it applies innovative scientific solutions to real-world environmental
situations.
Currently, a great challenge is the design and implementation of completely green products
and processes. There is not a systematic and reliable method for ensuring that the chemistry
being implemented is green, since the number of chemicals synthesis pathways is enormous.
Indeed, it is more correct to verify if a proposed manufacturing process is “greener” than
other alternatives. Anastas and Warner have developed the “Twelve Principles of Green
Chemistry” to aid one in assessing how green is a product or a process (Anastas and Warner,
1998), which are:
1. It is better to prevent waste than to treat or clean up waste after it is formed.
2. Synthetic methods should be designed to maximize the incorporation of all materials
used in the process into the final product.
6 CHAPTER 2. State of the art on Green Solvent Ethyl Lactate
3. Wherever practicable, synthetic methodologies should be designed to use and generate
substances that possess little or no toxicity to human health and the environment.
4. Chemical products should be designed to preserve efficacy of function while reducing
toxicity.
5. The use of auxiliary substances (e.g. solvents, separation agents, etc.) should be made
unnecessary whenever possible and, innocuous when used.
6. Energy requirements should be recognized for their environmental and economic
impacts and should be minimized. Synthetic methods should be conducted at ambient
temperature and pressure.
7. A raw material or feedstock should be renewable rather than depleting whenever
technically and economically practical.
8. Unnecessary derivatization (blocking group, protection/deprotection, and temporary
modification of physical/chemical processes) should be avoided whenever possible.
9. Catalytic reagents (as selective as possible) are superior to stoichiometric reagents.
10. Chemical products should be designed so that at the end of their function they do not
persist in the environment and break down into innocuous degradation products.
11. Analytical methodologies need to be further developed to allow for real-time in-
process monitoring and control prior to the formation of hazardous substances.
12. Substances and the form of a substance used in a chemical process should be chosen so
as to minimize the potential for chemical accidents, including releases, explosions, and
fires.
Based on these twelve principles, this thesis focuses:
1) The synthesis of the green solvent Ethyl lactate produced from renewable raw
material that is a more environmentally friendly alternative to petrochemical
solvent: 7th principle.
2) Ethyl lactate is 100% biodegradable, easy to recycle, non-corrosive, non-
carcinogenic and non-ozone depleting: 3rd, 4th and 10th principles.
3) The use of solid acid catalysts to improve the reaction kinetics without using
increase the stoichiometric of reactants, and it is more advantageous then
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 7
homogenous catalysts, since these are more corrosive and require a further step
of neutralization: 1st and 9th principles.
4) The process intensification by using hybrid technologies where reaction and
separation of at least one product take place in a single unity (SMBR, PVMR
and PermSMBR) will reduce/eliminate the use of solvents and requires less
energy consumption: 5th and 6th principles.
2.2 Ethyl lactate applications
The reaction between an alcohol and a carboxylic acid to form an ester and water is of
considerable industrial interest (Dhanuka et al., 1977). Organic esters are a very important
class of chemicals having applications in a variety of areas in the chemical industries such as
perfumes, flavours, pharmaceuticals, plasticizers, solvents and intermediates (Weissermel and
Arpe, 1997).
Ethyl lactate is an important organic ester, which is biodegradable and can be used as food
additive, in perfumery, as flavour chemicals and solvent, which can dissolve acetic acid
cellulose and many resins (Tanaka et al., 2002). It is a particularly attractive solvent for the
coatings industry as a result of its high solvency power, high boiling point, low vapour
pressure and low surface tension. Ethyl lactate is a desirable coating for wood, polystyrene
and metals and also acts as a very effective paint stripper and graffiti remover. It has replaced
solvents including N-methyl Pyrrolidone (NMP) (Reisch, 2008), toluene, acetone and xylene,
which has resulted in the workplace being made a great deal safer. In Table 2.1 solvating
properties of ethyl lactate and NMP are presented.
Table 2.1 Solvating properties of ethyl lactate and N-methyl Pyrrolidone.
Ethyl Lactate N-methyl pyrrolidone
Kauri Butanol(KB) Value >1000 350
Hildebrand 21.3 23.1
Disperse 7.8 8.8
Polar 3.7 6.0
Hydrogen 6.1 3.5
Solubility Miscible in Water and Hydrocarbons
Miscible in Water and Hydrocarbons
8 CHAPTER 2. State of the art on Green Solvent Ethyl Lactate
Other applications of ethyl lactate include being an excellent cleaner for the polyurethane
industry and for metal surfaces, efficiently removing greases, oils, adhesives and solid fuels.
Beyond all these applications, ethyl lactate can also be used in the pharmaceutical industry as
a dissolving/dispersing excipient for various biologically active compounds without
destroying the pharmacological activity of the active ingredient. It proves to be a very
effective agent for solubilising biologically active compounds that are difficult to solubilise in
usual excipients (Muse and Colvin, 2005).
Ethyl lactate can also be applied as a more environment friend alternative route to produce
1,2-propanediol, which is normally produced by the hydration of propylene oxide derived
from petrochemical resource (Huang et al., 2008). In Table 2.2 the major benefits of the ethyl
lactate are presented.
Table 2.2 Ethyl lactate major benefits.
Ethyl Lactate Benefits 100% Biodegradable Renewable - made from corn and other carbohydrates
FDA approved as a flavour additive EPA approved SNAP solvent
Non carcinogenic Non corrosive
Great penetration characteristics Stable in solvent formulations until exposed to water
Rinses easily with water High solvency power for resins, polymers and dyes
High boiling point Easy and inexpensive to recycle
Low VOC Not a Ozone Depleting Chemical
Low Vapor Pressure Not a Hazardous Air Pollutant
2.2.1 Solvent Market Analysis
Almost all manufacturing and processing industries depend on the use of solvents (see Figure
2.1). The world solvent market is estimated at 30 million pounds per year at prices from $0.90
to $1.70 per pound. The ethyl lactate green solvent has the potential to displace 80 % of these
solvents (Energetics Incorporated, 2003).
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 9
Figure 2.1 Solvent demand (AAE Chemie, 2009).
Selling prices for ethyl lactate have ranged from $1.50 to $2.00 per pound, but processing
advances could drive the price as low as $1.00 to $0.85 per pound (Argonne, 2006), enabling
ethyl lactate to compete directly with the petroleum-derived toxic solvents currently used.
Moreover, the crude prices have risen sharply, making of ethyl lactate green solvent more
commercially attractive. Among this, due to an environmental consciousness, some
consumers are willing to pay more for products that are less detrimental to the environment.
2.3 Synthesis of ethyl lactate
The conventional way to produce ethyl lactate is the esterification of lactic acid with ethanol
catalyzed by an acid catalyst, according to the reaction:
)()()()( WWaterELLactateEthylLaAcidLacticEthEthanol H +⎯⎯→←++
The use of these reactants (ethanol and lactic acid) has the advantage of both being produced
from renewable resources (by glucose or sugar fermentation processes).
Esterifications are self-catalyzed reactions, since the H+ cation released from the partial
dissociation of the carboxylic acid used as reactant catalyses the reaction. However, the use of
catalyst is favourable for the reaction rate as the kinetics of the self-catalyzed reaction is
extremely slow, since its rate depends on the autoprotolysis of the carboxylic acid. For
Agricultural chemicals 2% Dry Cleaning 1%
Others 8%
Paints 46%
Pharmaceuticals 9%
Adhesives 6%
Printing Inks 6%
Personal Care 6%
House/Car 6%
Metal/Industrial Cleaning 4%
Rubber/Polymer Manufacture 4%
Oil Seed Extract 2%
10 CHAPTER 2. State of the art on Green Solvent Ethyl Lactate
example, the lactic acid acidity constant is pKa=3.86 @ 25 ºC, and therefore an aqueous
solution with 85 % of lactic acid (about 10.8 M) has a pH=1.4. Typically, the catalytic
production of lactates is performed with homogeneous catalysts using acids, such as sulphuric
acid, phosphoric acid and anhydrous hydrogen chloride. However, the use of heterogeneous
catalyst (as for example, zeolites, ion-echange resins like Amberlyst 15-wet, Nafion NR50,
among others) has clear advantages:
- easy to separate from the reaction medium;
- long life time;
- higher purity of products (side reactions can be eliminated or are less significant);
- elimination of the corrosive environment caused by the discharge of acid
containing waste.
As previously mentioned, the esterification is a reversible reaction and, in order to obtain
acceptable ester yields, the equilibrium must be displaced towards the ester production, which
might be accomplished by different methods, such as:
1. to use a large excess of one of the reactants, in general the alcohol; however, this
results in a relatively inefficient use of reactor space and in very diluted products,
which will require an efficient separation afterwards;
2. to eliminate the water by azeotropic distillation between a solvent and water – the
solvent and water must be partially miscible and the boiling points of the different
components in the reaction medium must be compatible with that azeotrope;
3. to use reactive separations (as reactive distillation, simulated moving bed reactor,
pervaporation reactor, etc.) in order to remove the products from the reaction medium.
In reactions limited by chemical equilibrium where more than one product is formed
conversion can be enhanced in multifunctional reactor where the products are separated as
they are formed. Novel reactor configurations and choice of operating conditions can be used
to maximise the conversion of reactants and improve selectivity of desired product, thereby
reducing the costs associated with the separation step. Recently, reactive distillation,
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 11
chromatographic reactors and membrane reactors have been intensively applied to
esterifications processes, as it will be discussed latter within this chapter.
2.3.1 Renewable Resources
In recent years, an increasing demand on using biorenewable materials instead of petroleum
based feedstocks for producing chemicals, driven by environmental concerns and by the
concept of sustainability, has been noticed. Biobased products are one of the main pillars of a
sustainable economy. Nature produces 170 billion tons of biomass per year by
photosynthesis, 75 % of which belong to the class of carbohydrates; however, just 3-4 % of
these compounds are used by humans for food and non-food purposes (Röper, 2002).
Carbohydrates are very abundant renewable resources and they are currently considered as an
important feedstock for the Green Chemistry of the future (Lichtenthaler, 1998; Lichtenthaler,
2002; Lichtenthaler and Peters, 2004). Industrial plants, named as biorefineries, have been
created where biomass is converted economically and ecologically, in chemicals, materials,
fuels and energy (see Figure 2.2). The biorefineries could be the basis of the new bioindustry
and its concept is similar to the petroleum refinery; the difference is that the biorefinery is
based on conversion of biomass feedstocks instead of crude oil.
Figure 2.2 Schematic diagram of a biorefinery for precursor-contained
biomass. (Kamm and Kamm, 2004a; Kamm and Kamm, 2004b)
12 CHAPTER 2. State of the art on Green Solvent Ethyl Lactate
2.3.1.1 Ethanol Platform
Ethanol is an important raw material in the chemical industry and can also be used as
transportation fuel. It can be produced from a variety of biomass crops, including sugar crops
(e.g., sugarcane and sugar beet), starch crops (e.g., corn and cassava), or cellulosic feedstocks
(e.g., wood, grasses and agricultural residues).The production of ethanol from starch crops
involves as main steps: liquefaction and saccharification (conversion to sugar), milling,
pressing, fermentation and distillation. The production from cellulosic feedstocks is similar,
however it is significantly more difficult and costly to convert cellulose and hemicellulose
into their component sugars (glucose and xylose, respectively) than is the case for starches
(Sagar and Kartha, 2007). Currently, more than 37 billion litters of ethanol are produced
worldwide per year from starch and sugar crops (Rass-Hansen et al., 2007; Tilman et al.,
2006). In 2008, cellulosic ethanol industry developed some new commercial-scale plants. In
the United States, plants with 12 million liters capacity per year were operational, and an
additional 80 million liters per year of capacity (26 new plants) was under construction. In
Canada, capacity of 6 million liters per year was operational. In Europe, several plants were
operational in Germany, Spain, and Sweden, and capacity of 10 million liters per year was
under construction (REN21, 2009). Ethanol derived from cellulosic crops is appealing since it
broadens the scope of potential feedstocks beyond starch and sugar-based food crops.
Moreover, cellulosic ethanol can be more effective and promising as an alternative renewable
biofuel than corn ethanol because its use reduces even more the net greenhouse gas (GHG)
emissions when compared with the petroleum fuel (Wang et al., 2008) (see Figure 2.3).
Figure 2.3 Percent change in greenhouse gas emissions (adapted from Wang et al, 2008).
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 13
2.3.1.2 Lactic acid Platform
Lactic acid (2-hydroxypropionic acid) is an important platform chemical for the biorenewable
economy. It is an α-hydroxy acid containing a hydroxyl group adjacent to the carboxylic acid
functional group; a review on the lactic acid chemistry can be found in literature (Holten,
1971). Lactic acid can be produced through chemical synthesis or through the fermentation of
different carbohydrates, such as, glucose (from starch), maltose (produced by specific
enzymatic starch conversion), sucrose (from syrups, juices, and molasses), or lactose (from
whey) (Corma Canos et al., 2007). Nowadays, it is commercially produced by fermentation
of glucose. One of the most important steps in the lactic acid production is the recovery from
fermentation broths. The separation and purification stages represent about 50 % of the total
production cost. However, current advances in membrane-based separation and purification
technologies, particularly in microfiltration, ultrafiltration and electrodialysis, have originated
new processes which should reduce the lactic acid cost production (Wasewar et al., 2004).
The lactic acid production is around 350,000 tons per year and it is defended by some
observers that the worldwide growth per year is of 12-15 % (Wasewar et al., 2004). A lot of
products are derived from lactic acid; some of them are new chemical products and others,
which represent biobased routes to chemicals, currently produced from petroleum. The most
important ones are shown in Figure 2.4.
Figure 2.4 Some potential derivatives of lactic acid (Corma Canos et al., 2007).
2.3.2 Patented Processes Overview
There are a great number of patents related to esters production. A summary of those patented
processes is presented in Table 2.3.
Table 2.3 Patented processes for esters production. Commercial Solvents
Corporation (Bannister, 1936)
Lactic acid is dehydrated and mixed with ethanol and concentrated sulphuric acid (catalyst). This mixture is refluxed for one hour and the esterification takes place to a determined extent. Afterwards, distillation is started to separate the components of the reaction mixture.Temperature range of the process 135ºC-145ºC.
USA-Secretary of Agriculture
(Filachione and Fisher, 1951)
Process to produce esters from the reaction between the basic nitrogen salt of the carboxylic acid with an alcohol. It is a batch process and distillation is applied to separate the final mixture components. The process achieved from 61 to 92% ammonia removal and from 49 to 67% conversion to butyl lactate. Temperature range 89ºC-195ºC.
The American Oil Company (Jennings and Binning, 1960)
Process, where the esterification extent is enhanced, using pervaporation membranes in order to selective remove water from the reaction zone. It is a continuous method, which integrates reaction and separation in the same unit and uses as catalyst acid ion exchange resins. A temperature of 100ºC to 200ºC is maintained in the feed zone and the pressure is kept in order to maintain the water in liquid phase.
BASF Aktiengesellschaft (Bott et al., 1986)
Process to produce optically pure alkyl D- or L-lactates by reaction of calcium lactate with an alcohol in the presence of a strong acid; the water present in the reaction mixture or formed during the esterification is separated off by azeotropic distillation with the aid of an entraining agent.
Battelle Memorial Institute (Walkup et al., 1991; Walkup
et al., 1993)
Batch process for the preparation of esters of lactic acid directly from ammonium lactate and an alcohol. In this method the use of CO2 as acatalyst is required and the preferred range for the reaction mixture temperature is from 100ºC to 200ºC. A yield of lactate of about 75% is reported.
E. I. Du Pont de Nemours and Company
(Cockrem and Johnson, 1993)
Recovery of high purity lactate ester from fermentation broth containing ammonium lactate or other basic salt of lactic acid; acidifying in the presence of an alcohol using continues addition of sulphuric acid or other strong acid and crystallizing to precipitate out some or all of the basic salt of the strong acid; simultaneously or sequentially removing water while also esterifying the lactic acid with the alcohol to form impure lactate ester; removing the crystals formed; distilling the lactate ester to remove impurities.
Musashino Chemical Laboratory Ltd.
(Akira et al., 1994)
Method for producing a lactic ester by microorganic fermentation of lactic acid with a simple apparatus. A pressure in the range of 100 to 760 mmHg and a temperature of about 130ºC are recommended for this process.
BASF Aktiengesellschaft (Sterzel et al., 1995)
Process for the synthesis of lactates by fermentation of sugars mixtures, conversion of the lactic acid obtained during the fermentation to its salts, followed by esterification.
DAICEL CHEM IND LTD (Yukio, 1996)
In this process lactic acid is esterified with ethanol in the presence of a catalyst such as p-toluenesulfonic acid. The catalyst, water and unreacted ethanol are removed to give a solution (A). The solution A is neutralized with (B) a solution of an alkali metal salt in an alcohol and distilled to give the ethyl lactate.
(Feng et al., 1996) Rectification process to produce ethyl lactate from lactic acid and ethanol. This patented process includes technological steps, such as, determination of lactic acid, ethanol, sulphuric acid and benzene amounts, catalytic reaction, rectification for dewatering, neutralization and reduced distillation. Yield rate up to over 90% is reported.
Argonne National Laboratory
(Rathin and Shih-Perng, 1998)
Process for the synthesis of high purity ethyl lactate and other lactate esters from carbohydrate feedstock. This process consists in a reactor coupled with a pervaporation membrane unit for water removal and followed by separation of the reaction mixture in two consecutive distillation columns. Alternatively, the reactor is followed by a plurality of pervaporation steps. It is reported a conversion greater than 99 %, for an initial ethanol/lactic acid molar ratio of 2:1, a reaction mixture temperature of 95ºC, a permeate-side vacuum pressure less than 0.5 mbar and as catalyst an ion-exchange resin, Amberlyst XN-1010, at 10% of lactic acid weight.
Mitsubishi Gas Chemical Company, Inc.
(Abe et al., 1998)
Process to produce lactates from acetaldehyde and formate; The method described is characterized by the fact that there is no formation of ammonium salts as by-products as in the case of the conventional techniques.
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 15
A.E. Staley Manufacturing Co.
(Cockrem, 2001)
Process for the simultaneously production of an organic acid and of an ester of the organic acid. A mixture of ammonium salt of an organic acid with alcohol is rapidly heating in order to produce a liquid stream containing acid, ester, and unreacted ammonium salt.
Eastman Chemical Company (Arumugam et al., 2003)
Process where a solution of carboxylic acid in a solvent and an alcohol are fed to a simulated moving bed reactor (SMBR), that contains a solid(s) (adsorber/catalyst) to produce two streams, one comprising a solution of the ester of the carboxylic acid and the alcohol and other comprising the solvent. The process is particularly valuable for the preparation of an alkanol solution of an alkyl 2-keto-L-gulonate ester (AKLG). The simulated moving bed reactor is maintained at a temperature of 30 to 60ºC and a pressure of 3.5 to 20 bars.
Cargill, Incorporated (Eyal et al., 2003; Eyal et al.,
2006)
Techniques for processing lactic acid/lactate salt mixtures obtained from fermentation broths. These techniques generally concern the provision of separated lactic acid and lactate streams from the mixtures. In this patent preferred methods of separation and processing of each of the streams are provided.
A.E. Staley Manufacturing Co.
(Cockrem, 2003)
Process to produce an ester that comprises the following steps: (a) feeding to a first vessel a mixture of organic acid, alcohol, and water, where the organic acid and alcohol react to form monomeric ester and water (temperature of 150 to 220ºC) (b) feeding the mixture obtained in to a second vessel (temperature range 30 to 100ºC), where are produced a vapour stream, that comprises alcohol, ester and water, and a liquid one, that can be recycled to the first vessel.
La Chemical SpA (Ruggieri et al., 2003)
Process to produce esters in a chromatographic reactor in which the heterogeneous solid phase acts both as catalyst and as a means exhibiting preferential adsorption towards one of the reaction products (typically water). This process is particularly improved compared with the conventional technology since for regenerating the catalyst, it is used a desorbent mixed with a second compound, normally the anhydride of the acid used in the esterification reaction, which, by chemical reaction, completes the removal of the water adsorbed.
(Xueming and Jing, 2003) Disclose a technique that uses ammonium lactate as raw material to make ethyl lactate by rectifying. The adopted equipment includes rectifying tower, condenser on the top of tower and oil-water separator. It uses metal halide as catalyst, an initial molar ratio of lactic acid and ethanol being 1:1 and benzene being 30%-50% of lactic acid ammonium weight.
Arkema (FR) (Tretjak et al., 2006; Tretjak
and Teissier, 2004)
Process that relates to a continuous method to produce ethyl lactate from the esterification between lactic acid and ethanol in the presence of a catalyst (H2SO4 98%) ; this method consists in continuously extracting a mixture comprising ethyl lactate, ethanol, water and different heavy products from the reaction medium at partial lactic acid conversion rate and, then, fed the mixture to a reduced-pressure flash separation, producing an overhead stream containing a mixture of ethyl lactate, ethanol and water, that is subjected to a fractional distillation column. A purity higher than 94.6 % of ethyl lactate is reported for an initial ethanol/lactic acid molar ratio equal to 2.5; esterification carried out at 80ºC; flash separation at 85ºC and 50 mbar, and fractional distillation at a column bottom temperature of 155°C and top temperature of 77.2ºC.
Arkema (FR) (Martino-Gauchi and Teissier,
2004; Martino-Gauchi and Teissier, 2007)
Continuous method for preparing ethyl lactate which consists in reacting lactic acid with ethanol (ethanol/lactic acid molar ratio higher than 2.5) in the presence of a catalyst (H2SO4 98%) at a reflux of the reaction medium of about 100ºC under pressure ranging between 1.5 to 3 bars. This method is characterized by the continuous extraction of a near-azeotropic water/ethanol gas mixture from the esterification reaction medium, followed by dehydration of this mixture using molecular sieves and recuperation from the dehydration mixture an ethanol gas stream capable of being recycled to the esterification reaction medium and a flow consisting of water and ethanol which is fed to a distillation column.
Board of Trustees of Michigan State
(Miller et al., 2006)
Lactic acid esterification by continuous countercurrent reactive distillation with alcohols, especially ethanol (to produce ethyl lactate). In this invention recycle of dimmers and trimmers and other oligomers of lactic acid are provided in order to improve yields. For absolute ethanol fed near to the bottom of the column at 82ºC and lactic acid solution (85 wt % in water) fed near to the top of column at 25ºC (molar ratio ofethanol to lactic acid of 3.3) it is reported a lactic acid conversion of 83% and a ethyl lactate yield of 82%.
Roquette Freres (Fuertes et al., 2008)
Method for preparing a lactic acid ester composition based on a lactic acid composition involving two steps: (a) transforming of the composition into a lactic acid oligomeric composition; (b) mixing and reacting the oligomeric composition with an alcohol, in the presence of a transesterification catalyst, to esterify all or part of the lactic acid contained in the oligomeric composition. This invention also discloses the use of ethyl lactate as solvent for preparing gelified compositions.
The esterification reaction is usually catalyzed by a strong acid, being most common
sulphuric acid. However, the use of solid acid catalysts, as ion exchange resins, is also
mentioned. In order to overcome equilibrium limitations excess of one reactant is commonly
applied, normally the alcohol. Another technique is the use of a solvent, as benzene,
substantially immiscible with water in order to extract the ester. Reaction and separation are,
in almost all patented processes, separated steps, being distillation the most used separation
technology.
2.3.3 Reactive Separations
In the last years, chemicals, petrochemicals and pharmaceuticals industries have been gone
through a permanently increasing interest in the development of hybrid processes combining
reaction and separation mechanisms into a single, integrated operation known as ‘reactive
separation’. The combination of the two stages into a single unit brings important advantages,
such as energy and capital cost reductions, increased yield and removal of some
thermodynamic restrictions, e. g. azeotropes. A variety of separation principles and concepts
can be incorporated into a reactor, see Figure 2.5.
Figure 2.5 Separation functions integrated into a reactor.
Important examples of reactive separations are reactive distillation, reactive absorption,
reactive extraction or reactive membrane separation. Until now, such processes have had
industrial application, mainly in areas like the homogeneously catalysed synthesis of acetates
and the heterogeneously catalysed production of fuel additives. The potential is much wider;
however, optimal functioning depends on careful process design, with appropriately selected
PROCESSES INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 17
column internals, feed locations and catalyst placement. Greater understanding of the general
and particular features of the process behaviour is equally essential.
2.3.3.1 Reactive Distillation (RD)
Reactive distillation (RD) is an unit operation that combines chemical reaction and distillation
within a single vessel, thereby reducing equipment and recycle costs. A typical RD column is
shown in Figure 2.6. Other advantages offered by reactive distillation include high selectivity,
reduced energy uses, and reduction or elimination of solvents (Malone and Doherty, 2000). It
is an effective method that has considerable potential for carrying out equilibrium-limited
reactions, such as esterification and ester hydrolysis reactions; conversion can be increased
far beyond chemical equilibrium conversion due to the continuous removal of reaction
products from the reactive zone.
B
D
Reactive Section
A
C
Figure 2.6 Typical Reactive Distillation Column ( b,C b,B b,A b,DT < T < T < T ).
Reactive distillation has received much attention in the last years (Sundmacher and Kienle,
2002; Taylor and Krishna, 2000; Tsai et al., 2008). It has been used for the esterification of
fatty acids (Dimian et al., 2008; Steinigeweg and Gmehling, 2003), as well as being devised
as a new method to clean industrial water from acetic acid (Bianchi et al., 2003). The RD
technology was, also, applied on the ethyl lactate synthesis, first by Asthana and collaborators
(Asthana et al., 2005), where it is reported higher lactic acid conversions (>95 %) and good
ethyl lactate yields (>85 %), and, more recently, by Gao and co-workers (Gao et al., 2007).
18 CHAPTER 2. State of the art on Green Solvent Ethyl Lactate
However, applications of this technology in industry are still limited to a few reactive
systems, mainly etherification (e.g. MTBE), esterification (e.g. methyl acetate), and
alkylation (e.g. ethylbenzene or cumene) (Tuchlenski et al., 2001).
The production of methyl acetate is a classic example of successful RD (Agreda and Partin,
1984; Agreda et al., 1990). Conventional processes use one or more liquid-phase reactors
with large excess of one reactant in order to achieve high conversions of the other. A typical
flow sheet of a conventional process for the methyl acetate production is shown in Figure 2.7
in which the reaction section is followed by eight distillation columns, one liquid-liquid
extractor and a decanter. This process requires a large capital investment, high energy costs
and a large inventory of solvents. In the reactive distillation process for methyl acetate, the
entire process is carried out in a single unit (see Figure 2.7), which represents one-fifth of the
capital investment of the conventional process and consumes only one-fifth of the energy
(Krishna, 2002).
Figure 2.7 Task-integrated methyl acetate column is much simpler than conventional plant (Stankiewicz and Moulijn, 2000).
In spite of all advantages of the RD technology, there are still some constraints and
difficulties in its implementation, mainly due to volatility limitations. In order to maintain
high concentrations of reactants and low concentrations of products in the reaction zone, the
reactants and products must have suitable volatility. Also, it is necessary that both products
have different boiling points to ensure the separation. The major disadvantage of RD
PROCESSES INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 19
technology, for exothermic reactions, is that chemical reaction has to show significant
conversion at distillation temperature (Pöpken et al., 2000).
2.3.3.2 Simulated Moving Bed Reactor (SMBR)
Simulated Moving Bed (SMB) systems are used in industry for separations that are either
impossible or difficult using traditional techniques. This technology uses differences in the
adsorptivity of the different components involved rather than differences in their volatility,
being an interesting alternative to distillation when the species involved exhibit small
volatility differences, are non-volatile or are sensitive to temperature, as in the case of many
fine chemical and pharmaceutical applications.
The combination of SMB and chemical reaction has been, in the last years, a subject of
considerable attention in the scientific research, being this integrated reaction-separation
technology called Simulated Moving Bed Reactor (SMBR). A schematic diagram of a SMBR
unit is presented in Figure 2.8 where a reaction of type A+B↔C+D is considered, for the case
of D being more adsorbed than C. The SMBR consists of a set of columns connected in series
that are packed with a solid, which acts as both adsorbent and catalyst. Typically, there are
two inlets (feed and desorbent) and two outlets (extract and raffinate). The component A is
used as reactant and desorbent, therefore it is introduced in the system in the feed and
desorbent streams. The other reactant B is used as feed. The products D and C are collected in
the extract and the raffinate, respectively, since D is more adsorbed than C. At regular time
intervals, called switching time period, all streams are switched for one bed distance in
direction of the fluid flow. A cycle is completed when the number of switches is equal to a
multiple of the columns number. In this way, the countercurrent motion of the solid is
simulated with a velocity equal to the length of a column divided by the switching time.
According to the position of the inlet and outlet stream the unit can be divided in four
sections. In section I, positioned between the desorbent and extract nodes, the adsorbent is
regenerated by desorption of the more strongly adsorbed product (D) from the solid. In
section II (between the extract and feed node) and section III (between the feed and raffinate
node) the reaction is taking place and products (C and D) are formed. The more strongly
adsorbed product D is adsorbed and transported with the solid phase to the extract port. The
less strongly adsorbed product C is desorbed and transported with the liquid in direction of
the raffinate port. In section IV, positioned between the raffinate and desorbent node, the
desorbent is regenerated before being recycled to section I.
20 CHAPTER 2. State of the art on Green Solvent Ethyl Lactate
Desorbent (A) Raffinate (A+C)
Extract(A+D)
Direction of fluid flow and port switching
1 2
3 4
5 6
12 11
10 9
8 7
Feed(A+B)
A + B C + D
Figure 2.8 Scheme of a Simulated Moving Bed Reactor (SMBR).
The simultaneous reaction and separation in a SMBR has shown that considerable
improvements in some processes performance can be achieved, as for example, on the
synthesis of acetals (Pereira et al., 2008; Rodrigues and Silva, 2005; Silva and Rodrigues,
2005), fructose (Azevedo and Rodrigues, 2001; Da Silva et al., 2005; Zhang et al., 2004),
lactosucrose (Kawase et al., 2001; Pilgrim et al., 2006), methylacetate (Lode et al., 2003) and
MTBE (Zhang et al., 2001). In the last years, cation exchange resins are being widely used as
catalyst of esterifications and acetalizations. Moreover, those resins adsorb selectively water,
a by-product of those kind of reactions. Therefore, combining these two properties of acidic
resins, and knowing that esterifications are reversible reactions, chromatographic reactors
appear as promising technologies; in particular the SMBR, since the products are
continuously separated and removed from the reaction medium, leading to complete
conversion. This has motivated several studies on esterification reactions by means of the
SMBR technology; examples are the esterification of acetic acid with methanol (Lode et al.,
2003; Yu et al., 2003), ethanol (Mazzotti et al., 1996) and β-phenethyl alcohol (Kawase et
al., 1996), and the esterification of acrylic acid with methanol to form methyl acrylate
(Ströhlein et al., 2006).
Although the SMBR technology allows 100 % of conversion with 100 % of recovery of the
desired product, a further step is necessary to separate the product from the raffinate mixture,
and to recover the reactant A, used as desorbent, from both extract and raffinate streams, in
order to recycle it to the SMBR unit.
PROCESSES INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 21
2.3.3.3 Pervaporation Membrane Reactor (PVMR)
Pervaporation is one of the membrane processes that can be employed for the separation of
liquid mixtures that are difficult or not possible to separate by conventional methods, such as
distillation. One example is the application of pervaporation to break the azeotrope of the
mixture ethanol-water, where it is much more economical to use pervaporation or vapour
permeation than other conventional methods (see Table 2.4).
Table 2.4 Dehydration costs of ethanol from 99.4 to 99.9 vol % by different methods (Drioli and Romano, 2001).
Utilities Vapor
Permeation ($/ton)
Pervaporation ($/ton)
Entrainer Distillation
($/ton)
Molecular Sieve
Adsorption ($/ton)
vapor - 12.8 120.0 80.0
electricity 40.0 17.6 8.0 5.2
cooling water 4.0 4.0 15.0 10.0
Entrainer - - 9.6 -
Replacement of membranes and molecular sieves
19.0 30.6 - 50.0
total costs 63.0 65.0 152.6 145.2
The pervaporation process has significant separation potential for various types of solutions,
being specially suited for organic-water and organic-organic separations (Feng and Huang,
1996; Fleming and Slater, 1992; Huang and Rhim, 1991; Neel, 1991; Neel, 1995). It is used
to separate a liquid mixture by partly vaporizing it through a nonporous permselective
membrane, as shown in Figure 2.9. The feed liquid mixture is allowed to flow along one side
of the membrane, and a fraction of it, the “permeate”, is recovered in the vapour state on the
other side of the membrane, by means of vacuum or sweep gas. The mass transport through
the membrane is induced by maintaining a low vapour pressure on the permeate side,
eliminating thereby the effect of osmotic pressure. The permeate stream, enriched in the most
22 CHAPTER 2. State of the art on Green Solvent Ethyl Lactate
permeating component, might be then condensed in order to recover it. The remaining feed
that does not permeate through the membrane, called the “retentate”, is depleted in the
permeating component (Neel, 1995).
Feed Retentate
Permeate
Pervaporation membrane
Liquid
Vapor
Figure 2.9 Schematic representation of the pervaporation process.
There are a number of reviews on pervaporation processes (Dutta et al., 1996; Song et al.,
2004; Van Hoof et al., 2004) and also on pervaporation membrane reactors (PVMRs) (Lim et
al., 2002; Lipnizki et al., 1999; Waldburger and Widmer, 1996), since its application to
equilibrium-limited reactions improves conversion by selectively removing one reaction
product e.g. (Benedict et al., 2006; Castanheiro et al., 2006; David et al., 1991; Domingues et
al., 1999; Lauterbach and Kreis, 2006; Peters et al., 2005a; Peters et al., 2005b; Sanz and
Gmehling, 2006; Tanaka et al., 2002). PVMRs are, therefore, a type of membrane reactors
that combines chemical reaction and separation by pervaporation, which is usually
implemented by two different semi-batch processes: (i) the pervaporation unit (PV) is
coupled to the reactor, i.e., the PV unit is an external process unit (see Figure 2.10a); and (ii)
the reactor and the membrane are integrated in the same unit (see Figure 2.10b).
Although there is a recent interest in PVMRs, its discovery goes back to 1960, according to
the first patent for a continuous process that integrates reaction and pervaporation in the same
unit applied to an esterification reaction catalyzed by an acid ion exchange resin and using
water selective membrane in order to remove it from the reaction zone and therefore
enhancing the conversion (Jennings and Binning, 1960). Also, in 1986, another process was
patented for the acetic acid esterification reaction with ethanol (Pearce, 1986), which reports
complete conversion of the acetic acid by using a pervaporation membrane reactor consisting
of two half-cells with a flat membrane disk (commercial PVA or Nafion) placed in the
middle, as shown in Figure 2.11.
PROCESSES INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 23
Figure 2.10 Layout of a Semi-batch Pervaporation Membrane Reactor (SBPVMR):
(a) external pervaporation unit;
(b) membrane and reactor in the same unit.
Figure 2.11 Experimental set-up for the pervaporation membrane reactor (Pearce, 1986).
Even though PVMRs are finding broad uses, esterifications appear to be a key application
(Marcano and Tsotsis, 2002). The esterification reactions are a typical example of
equilibrium-limited reaction that produces by-product water. Considering a catalytic
esterification reaction scheme of the type:
HA B C D+
⎯⎯→+ +←⎯⎯
where C is the desired ester product and D is the by-product (water). Due to the
thermodynamic equilibrium limitation of the esterification reaction, a conventional reactor
Membrane
(a) (b)
24 CHAPTER 2. State of the art on Green Solvent Ethyl Lactate
Feed
(A+B) Retentate
(C)
Permeate (D)
Membrane
will operate at low conversion; however, if a membrane is integrated in the reactor, as shown
in Figure 2.12, wherein the water is removed through the permselective membrane from the
reaction zone to the other side of the membrane, the reaction will proceed in the forward
direction and therefore high conversion is expected to be attained in a reasonably short time.
Figure 2.12 Schematic representation of a membrane reactor for by-product withdrawal in a reversible reaction.
Zhu and collaborators studied the esterification reaction of acetic acid with ethanol both by
experiment and simulation in a continuous-flow PVMR using a polymeric/ceramic composite
membrane (Zhu et al., 1996). The same reaction was studied in a continuous tube membrane
reactor (Waldburger and Widmer, 1996). This reaction was also studied in a PVMR, housing
the reactor and membrane in the same unit, applying a zeolite T-membrane since it is stable
under acidic conditions (Tanaka et al., 2001). Nafion tubular membranes, which also act as
catalyst, were applied for the esterification of acetic acid with methanol and n-butanol, where
the equilibrium conversions of 73 % and 70 % were increased to 77 % and 95 %, respectively
(Bagnell et al., 1993). The esterification of acetic acid with butanol was more significantly
improved than with methanol, due to the higher membrane selectivity towards water in
butanol/water system. This particular esterification was also studied using Zr(SO4)·4H2O as
catalyst and using cross-linked polyvinyl alcohol (PVA) membranes (Liu et al., 2001; Liu
and Chen, 2002). Experiments and simulations were conducted to investigate the effects of
several operating parameters, such as reaction temperature, initial molar ratio of acetic acid to
n-butanol, ratio of the membrane area to the reacting mixture volume and catalyst
concentration.
Regarding the operating modes of PVMR, semi-batch esterification process coupled by
pervaporation is the most used (Xuehui and Lefu, 2001), being applied for the synthesis of
ethyl tert-butyl ether (ETBE) from tert-butyl alcohol (TBA) and ethanol (Kiatkittipong et al.,
2002); and applied for the esterification of acetic acid with isopropanol leading to conversions
higher than 90 % (Sanz and Gmehling, 2006). The esterification of lactic acid and succinic
PROCESSES INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 25
acid with ethanol were studied in semi-batch well-mixed reactors coupled by pervaporation
(Benedict et al., 2006), using two different pervaporation membranes, a GFT-1005 membrane
(Deutsche Carbone AG) and a T-1b (TexSep 1) membrane (Texaco Research), both with
organic acid compatibility and very high water permeation selectivity. The conversion of
lactic acid obtained in the PVMR was 71 %, being the usual equilibrium value of 55 %.
Based on the synthesis of methyl acetate from methanol and acetic acid catalysed by
Amberlyst-15 and using a polyvinyl alcohol (PVA) membrane, three different configurations
of PVMRs were compared (Assabumrungrat et al., 2003): (i) semi-batch (SBPVMR), (ii)
plug-flow (PFPVMR) and (iii) continuous stirred tank (CSPVMR): Simulations, carried out
using the experimental determined kinetic and permeation parameters, conclude that the
PFPVMR is the most favourable mode, although there are some conditions (at low values of
Damkohler number (0.5 and 1)) where CSPVMR is superior to PFPVMR. A new concept of a
hybrid PVMR system, which integrates the pervaporation step through a membrane with
adsorption in the permeate side, proved to enhance in 5 % the conversion reported in the
PVMR in the absence of the adsorbent (Park and Tsotsis, 2004). Based on the concept of
catalytic membranes (Bagnell et al., 1993), the performance of a composite catalytic
membrane was examined for the esterification of acetic acid and butanol aiming to develop a
continuous composite catalytic pervaporation membrane reactor (Peters et al., 2005a). It was
proved by simulations that the outlet conversion for the catalytic pervaporation-assisted
esterification reaction exceeds the conversion of a conventional pervaporation membrane
reactor, with the same loading of catalyst dispersed in the liquid bulk. At the same conditions,
a conversion of 85 % for the catalytic pervaporation-assisted esterification reactor is reported
against 79 % for a conventional pervaporation membrane reactor.
The scientific literature on PVMRs is abundant, since it is an area where significant activity is
under way and many advances are expected in the future, due to the many advantages of
PVMRs: the simultaneous removal of a product from the reactor enhances the conversion;
undesired side reactions can be suppressed; high conversion is possible at almost
stoichiometric feed flow rates and the heat of reaction can be used for separation. Therefore,
lower energy consumption and higher product yields make of the pervaporation membrane
reactor an interesting alternative to conventional processes. However, no large-scale
industrial applications have been reported yet. The main reason for this should be related to
factors as small fluxes of the desired species and mechanical and thermal stability of the
26 CHAPTER 2. State of the art on Green Solvent Ethyl Lactate
membranes. Further developments in the field of materials engineering will certainly change
this picture.
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3. Batch Reactor: Thermodynamic Equilibrium and
Reaction Kinetics
Abstract. The heterogeneous catalysis of lactic acid (88 wt. %) esterification with ethanol
in presence of Amberlyst 15-wet, was studied for catalyst loading of 1.2 wt. % to 3.9 wt. %,
initial molar ratio of reactants of 1.1 to 2.8 and temperature from 50ºC to 90ºC.
In this work a methodology based in the UNIQUAC model was developed to determine the
thermodynamic equilibrium constant since in literature there is inconsistency concerning the
temperature dependence of the thermodynamic equilibrium constant. A simplified Langmuir-
Hinshelwood kinetic model was used to describe the experimental data. The proposed rate
law is ( ) 2)1(/ WWEthEthWELLaEthc aKaKKaaaakr ++−= ; the kinetic parameters are the
pre-exponential factor, 1170, min..1070.2 −−×= gmolkc and the activation energy,
molkJEa /98.49= . The equilibrium reaction constant is ( ))(/13.515exp35.19 KTK −= with
reaction enthalpy 4.28 kJ/mol. The model reasonably predicts the kinetic experimental data
and it will be very useful to apply for the design and optimization of industrial hybrid reactive
separation processes.
Adapted from: Pereira C. S. M., S. P. Pinho, V. M. T. M. Silva and A. E. Rodrigues, "Thermodynamic
Equilibrium and Reaction Kinetics for the Esterification of Lactic Acid with Ethanol Catalyzed by acid ion
exchange resin", Ind Eng Chem Res. 47: 1453-1463, 2008.
36 CHAPTER 3. Thermodynamic Equilibrium and Reaction Kinetics
3.1 Introduction
The ethyl lactate synthesis comprises a liquid-phase reversible reaction between ethanol and
lactic acid, wherein water is a sub-product:
)()()()( WWaterELLactateEthylLaAcidLacticEthEthanol H +⎯⎯→←++
The lactic acid contains a hydroxyl group adjacent to the carboxylic acid and because of its
bifunctional nature undergoes intermolecular esterification in aqueous solutions above
20 wt. % to form linear dimer and higher oligomer acids (Montgomery, 1952; Vu et al.,
2005):
WLaLa +⇔ 212 (lactic acid dimer formation)
WLaLaLa +⇔+ 321 (lactic acid trimer formation)
…
WLaLaLa nn +⇔+ −11 (lactic acid oligomer formation)
with 2≥n
where:
OH
O
OH
Lactic acid (La1) Lactic acid oligomers (Lan+1)
OH
O
O
O
OHn
The use of lactic acid as reactant is then complicated, since the extent of the self-esterification
increases with the increase of the acid concentration. A method to purify the lactic acid is
through the esterification with lower alcohols, such as methanol, ethanol or butanol; and then
the produced ester is separated and hydrolyzed back into pure lactic acid and the alcohol is
recovered and reused (Troupe and DiMilla, 1957).
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 37
For the process of ethyl lactate production it will be desirable to use a high lactic acid
concentration, with lower water content, in order to increase the yield of the reaction and the
concentration of the ethyl lactate. However, this will imply the presence of lactic acid
oligomers during the esterification, which will be converted into the corresponding esters:
WELEthLa +⇔+ 11 (ethyl lactate formation)
WELEthLa +⇔+ 22 (ethyl lactate dimer formation)
WELEthLa +⇔+ 33 (ethyl lactate trimer formation)
…
WELEthLa nn +⇔+ (ethyl lactate oligomer formation)
where:
OH
O
OC2H5
OH
O
O
O
OC2H5n
Ethyl lactate (EL1) Ethyl lactate oligomers (ELn+1)
For an aqueous solution with 88 wt. % of lactic acid, the molar percentage of the monomer
(La1), dimer (La2) and trimer (La3) are of about 43.5 mol %, 9.2 mol % and 1.8 mol %,
respectively; and about 45 mol % of water. While a 20 wt. % aqueous solution of lactic acid
is constituted only by monomer and water, being the monomer molar percentage of about
5.6 mol % (Asthana et al., 2006). However, the percentage of lactic acid and ethyl lactate
oligomers is less then 5% at equilibrium (Asthana et al., 2006; Tanaka et al., 2002) and the
use of an aqueous solution with a high lactic acid concentration is desirable to produce ethyl
lactate at industrial scale by means of a continuous hybrid process as reactive pervaporation,
reactive chromatographic processes, among others.
The kinetics of ethyl lactate production has been studied since 1957 (Troupe and DiMilla,
1957), but lately has deserved more attention since it is a green solvent and an alternative to
the traditionally petroleum derived solvents. Troupe and Dimilla (1957) studied the
esterification reaction between lactic acid and ethanol using sulphuric acid as catalyst.
38 CHAPTER 3. Thermodynamic Equilibrium and Reaction Kinetics
However, this kind of homogeneous catalysts may be the origin of a lot of problems, because
of their miscibility with the reaction medium, which causes separation problems; in addition,
strong acid catalysts lead to corrosion of the equipment. The replacement of homogeneous
catalysts by heterogeneous catalysts is gaining importance due to their ecofriendly nature.
Besides being non-corrosive and easy to separate from the reaction mixture, the
heterogeneous catalyst can be used repeatedly over a prolonged period without any difficulty
in handling and storage. Many solid-acid catalysts have been used, such as acid treated clays
(Yadav and Krishnan, 1998), heteropolyacids (Dupont et al., 1995; Lacaze-Dufaure and
Mouloungui, 2000; Schwegler et al., 1991; Yadav and Krishnan, 1998), iodine (Ramalinga et
al., 2002), MCM-41 (Koster et al., 2001), zeolite-T membrane (Tanaka et al., 2002), smopex-
101 (Lilja et al., 2002; Mäki-Arvela et al., 1999), HY zeolite (Chen et al., 1989; Kirumakki et
al., 2003; Ma et al., 1996), zeolite beta (Kirumakki et al., 2003) and ZSM-5 (Kirumakki et
al., 2003; Ma et al., 1996; Wu and Chen, 2004; Yadav and Krishnan, 1998). However, ion-
exchange resins are the most commonly used solid catalysts and they have been proved to be
effective in liquid phase esterification (Benedict et al., 2003; Lee et al., 2002; Lee et al.,
2000; Liu and Tan, 2001; Yadav and Mujeebur Rahuman, 2002; Zhang et al., 2004). Since
the heterogeneous catalysis is clearly advantageous, some studies have been already
performed for the esterification of lactic acid with ethanol. Zhang and co-workers studied the
kinetic of esterification of lactic acid (20 wt. %) with ethanol catalyzed by five different
cation-exchange resins (Zhang et al., 2004). They proposed a simplified mechanism based on
Langmuir-Hinshelwood model to describe the kinetic behaviour. Delgado et al. (2007b) also
investigated the esterification of lactic acid with ethanol and the hydrolysis of the ethyl lactate
in the presence of a commercial cation-exchange resin; an aqueous lactic acid solution of
20 wt. % and a mechanism based on the Langmuir-Hinshelwood model to describe the
kinetics was used. This esterification with/without a solid catalyst (Amberlyst XN-1010) was
also investigated by Benedict and their collaborators. A kinetic model based in concentrations
to describe the behaviour of the reaction between an 88 wt. % of lactic acid solution with
ethanol was used (Benedict et al., 2003). The presence of oligomers was not mentioned in
their work. In Tanaka and co-workers studies about this esterification, the oligomers presence
was considered and the reactions were described by simple nth-order reversible rate
expressions based on the species concentration (Tanaka et al., 2002). Three different
solutions of lactic acid (20 wt. %, 50 wt. % and 88 wt. %) were used in the esterification
reaction with ethanol in Asthana’s and collaborators work (2006). The oligomers presence
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 39
was also taken into account and a similar model based on the species concentration was used
to describe the reaction kinetics.
In spite of the number of kinetic studies available in the literature, the thermodynamic
equilibrium of the reaction in the liquid phase has not been clearly studied, and some of the
authors do not report the values of the equilibrium constant (Zhang et al., 2004). In some
works (Delgado et al., 2007b; Troupe and DiMilla, 1957) different equilibrium constants
based in concentration (Kx) at the same temperature are reported. The authors of those studies
have concluded that the equilibrium constant Kx vary significantly with the initial molar ratio
of the reactants, being less sensitive to the temperature. However, the thermodynamic
equilibrium constant defined as function of the species liquid activities, which is only
temperature dependent, is not presented in their works. In order to overcome the lack of
thermodynamic data, Delgado and co-authors have studied the vapor-liquid reactive equilibria
for the ethyl lactate synthesis, and they have proposed the following expression to describe
the reaction equilibrium constant (Delgado et al., 2007a):
)(2.2431893.7)(ln
KTK −= (3.1)
Nevertheless, they have found some difficulties in measuring the vapor phase composition,
that affect significantly the experimental values of the experimental equilibrium constant,
leading to high deviations between experimental values and those predicted by Equation 3.1,
as shown in Figure 3.1.
0.00
0.50
1.00
1.50
2.00
2.50
0.00265 0.0027 0.00275 0.0028 0.002851 / T (K)
experimental [26]
ln (K
)
ln K = 7.893 - 2431.2 / T (K)
experimental
Figure 3.1 Representation of experimental values of ln K as function of 1/T. (Data
collected from Delgado et al. (2007b)).
40 CHAPTER 3. Thermodynamic Equilibrium and Reaction Kinetics
This work was undertaken to obtain the reaction equilibrium and kinetic data for the synthesis
of the ethyl lactate in the liquid phase, avoiding the vaporization of all species by working at
6 bar (helium pressurization). The pressure influence in the value of equilibrium constant is
negligible for this system for the temperature and pressure operating range, as it can be
estimated by the correction factor PK (Smith and Van Ness, 1987). Therefore the
thermodynamic equilibrium constant was estimated by the UNIQUAC method and the
esterification reaction catalyzed by the ion-exchange resin Amberlyst 15-wet was described
by a simple activity based kinetic model, which will be applied in the modelling of some
reactive separation processes, such as membrane reactors. In this work a high lactic acid
concentration was used with the objective of maximizing the ethyl lactate productivity for an
industrial process. The presence of oligomers was neglected, since at equilibrium the total
amount of lactic acid and ethyl lactate oligomers represents less than 5 % according to
Tanaka et al. (2002) and Asthana et al. (2006) studies. However, in the final section of this
paper the presence of oligomers will be addressed.
3.2 Experimental Section
3.2.1 Chemicals and Catalyst
The chemicals used were ethanol (>99.9% in water), lactic acid (>85% in water) and ethyl
lactate (>98% in water) from Sigma-Aldrich (U.K.). A commercial strong-acid ion-exchange
resin named Amberlyst 15-wet (Rohm & Haas) was used as catalyst and adsorbent. This resin
is a bead-form macroreticular polymer of styrene and divinylbenzene, with particle diameter
varying between 0.3 to 1.2 mm, an ion exchange capacity of 4.7 meq H+/g of dry resin and
inner surface area of 53 m2/g. According to Ihm et al. (Ihm et al., 1988) only 4 % of the
active sites are located at the macropores (surface of the microspheres) and the others 96 %
are inside gel polymer microspheres. Since the water adsorbed on the catalyst surface
decreases the reaction kinetics, because it is one of the reaction products, it was necessary to
guarantee anhydrous resin. For that, the resin was washed several times with deionised water
and dried at 90ºC until the mass remains constant. This method is of value for the reuse
experiments, since the water is abundantly present due to the lactic acid solution.
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 41
3.2.2 Experimental set-up
The experiments were carried out in a glass-jacketed 1 dm3 autoclave (Büchi, Switzerland),
operating in a batch mode, mechanically stirred at 600 rpm, equipped with pressure and
temperature sensors and with a blow-off valve (Figure 3.2). The temperature was controlled
by thermostated ethylene glycol/water solution (Lauda, Germany) that flows through the
jacket of the reactor and feed vessel. To maintain the reacting mixture in liquid phase over the
whole temperature range, the pressure was set at 0.6MPa with helium. The lactic acid solution
is charged into the reactor and heated to the desired reaction temperature. The dry catalyst is
placed in a basket at the top of the stirrer shaft. Ethanol is heated up to the desired
temperature into the feed vessel and then charged to the reactor opening the on/off valve. The
agitation is immediately turned on and the basket of catalyst falls down in the reactant
solution. This time is considered to be the starting time of the esterification reaction. One of
the outlets of the reactor was connected directly to a liquid sampling valve (Valco, USA),
which injects 0.2 µl of pressurised liquid to a gas chromatograph.
TB
GCHe
He
BR
BV
TT
PTM
NVPM
NV
V2
V1vacuun
vent
vent
FV
Figure 3.2 Experimental set-up for kinetic studies. BR-batch reactor; FV-feed vessel; M motor; TT-temperature sensor; PT-pressure sensor; PM-manometer; BV-blow-off valve; V1-sampling valve; V2-injection valve; NV-needle valve; GC-gas chromatograph; TB-thermostatic bath.
42 CHAPTER 3. Thermodynamic Equilibrium and Reaction Kinetics
3.2.3 Analytical method
All the samples were analysed in a gas chromatograph (Chrompack 9100, Netherlands) using
a fused silica capillary column (Chrompack CP-Wax 57 CB, 25 m x 0.53 mm ID, df = 2.0
μm) to separate the compounds and a thermal conductivity detector (TCD 903 A) to quantify
them. The column temperature was programmed with a 1.5 min initial hold at 110ºC,
followed by a 50ºC/min ramp up to 190ºC and held for 8.5 min. The injector and detector
temperature were maintained at 280ºC and 300ºC, respectively. Helium N50 was used as the
carrier gas with flowrate 10.50 ml/min. In order to analyze the lactic acid and ethyl lactate
oligomers at equilibrium a HPLC system from Gilson (France) using an ICSep ION-300
column held at 20ºC was used. A 0.0085 N H2SO4 solution was used as mobile phase (0.4 ml
/ min) and species were quantified by a refractive index detector.
3.3 Thermodynamic Equilibrium Results
The experiments to measure the equilibrium constant were done in a temperature range of
323-363 K. At each temperature different experiments were performed using different initial
molar ratios ( 0.1/ =LaEthR to 8.2/ =LaEthR ) and different mass of catalyst (2.3 wt. % to
6.0 wt. %) (see Table 3.1). All the experiments lasted long enough to ensure that the
equilibrium was reached.
3.3.1 Thermodynamic equilibrium constant
In its most general form the chemical equilibrium constant ( K ) for a reaction is given by:
=⎟⎟⎠
⎞⎜⎜⎝
⎛ Δ−=
RTGK exp ∏
ii
iaν (3.2)
where GΔ is the reaction standard free Gibbs energy, R the ideal gas constant, T the
absolute temperature, ia is the activity of species i, and iν its stoichiometric coefficient in the
reaction.
For the esterification reaction, occurring in the liquid phase at low pressure:
γγγγγ
KKxxxx
aaaa
K xLaEth
WEL
LaEth
WEL
LaEth
WEL === (3.3)
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 43
being x and γ the mole fraction and the activity coefficient of each species, respectively.
The thermodynamic chemical equilibrium constant is only temperature dependent. From the
experimental point of view, however, changing isothermically the initial mass of each
reactant will give, most probably, different values for the equilibrium constant. Naturally, that
is a consequence of experimental errors as well as deficiencies in the thermodynamic models
used to calculate the activity coefficients. For example, as can be observed in Table 3.1 three
different runs were carried out at 323.15 K. Estimating the activities coefficients by the
UNIFAC method (Fredenslund et al., 1977), using the relative molecular volume, surface
area and the interaction parameters presented in literature (Reid et al., 1987); the resulting
equilibrium constants are quite different; 4.126, 3.813, and 4.637, respectively, from top to
bottom.
Table 3.1 Conditions of the experiments performed to measure the thermodynamic equilibrium constant.
Initial number of moles Equilibrium number of moles
T (K)
Catalyst loading (wt. %) Ethanol
Lactic acid Water Ethanol
Lactic acid
Ethyl Lactate Water
323.15 5.67 0.8154 0.4051 0.2968 0.5459 0.1356 0.2695 0.5662
323.15 5.95 0.7329 0.4051 0.2966 0.4786 0.1508 0.2543 0.5509
323.15 5.63 0.4033 0.4051 0.2957 0.1983 0.2000 0.2051 0.5008
333.15 5.67 0.8154 0.4051 0.2968 0.5403 0.1300 0.2751 0.5719
333.15 5.95 0.7329 0.4051 0.2966 0.4744 0.1465 0.2586 0.5551
333.15 5.63 0.4033 0.4051 0.2957 0.1963 0.1981 0.2070 0.5027
343.15 5.67 0.8154 0.4051 0.2968 0.5351 0.1249 0.2802 0.5770
343.15 5.95 0.7329 0.4051 0.2966 0.4730 0.1452 0.2599 0.5565
343.15 5.63 0.4033 0.4051 0.2957 0.1969 0.1986 0.2065 0.5022
343.41 2.82 5.6988 2.0197 1.4837 4.1506 0.4716 1.5481 3.0319
343.41 2.82 5.6988 2.0197 1.4837 4.1361 0.4570 1.5627 3.0464
353.15 2.37 3.9033 3.4444 2.5154 1.9555 1.4966 1.9477 4.4632
362.87 2.82 5.6988 2.0197 1.4837 4.1173 0.4382 1.5815 3.0652
362.87 2.82 5.6988 2.0197 1.4837 4.1029 0.4239 1.5958 3.0796
One possibility to get a single equilibrium constant value for each temperature would be to fit
all the equilibrium constants using an equation of the type:
44 CHAPTER 3. Thermodynamic Equilibrium and Reaction Kinetics
TbaK +=ln (3.4)
This, however, presents a big deficiency. In fact, using a unique value for the equilibrium
constant at a given temperature, the equilibrium composition must be recalculated for each
specific initial condition, which immediately will introduce changes in the magnitude of the
activity coefficients.
Assuming a given value for the equilibrium constant at 323.15 K, solving Equation 3.3 in
order to the equilibrium composition involves an iterative procedure. First, all the activity
coefficients must be assumed equal to one, obtaining the equilibrium composition of an ideal
solution. After the activity coefficients can be determined using a model such as UNIQUAC
or UNIFAC, and a new equilibrium composition can now be calculated. The procedure is
repeated until convergence. It must be stressed that this final equilibrium composition will
certainly not be the same as the one presented in Table 3.1, which was used to calculate the
equilibrium constant and to regress the coefficients in Equation 3.4. So this inconsistency
must be avoided.
To overcome this problem, in this work it is suggested to obtain the coefficients in Equation
3.4 that allow the calculation of the equilibrium composition as closer as possible to that
observed experimentally. Therefore, the coefficients were estimated minimizing the following
objective function (Fob):
∑ ⎟⎟⎠
⎞⎜⎜⎝
⎛ −=
k k
calckk
XXX
Fob2
exp
exp
(3.5)
where expkX and calc
kX are the experimental and the calculated equilibrium conversion for
experiment k, respectively.
3.3.1.1 Activity coefficients estimation
In this work, instead of using the UNIFAC method it was preferred to apply the UNIQUAC
model. Indeed, there are some available experimental vapor-liquid equilibrium data involving
mixtures of species involved in the reaction under study, which makes preferable to use a
correlation model instead of a pure predictive method.
Initially the parameters between ethanol and ethyl lactate were estimated based on the data
published by Peña-Tejedor et al. ( 2005) and Vu et al. (2006). Following, the parameters
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 45
between water and ethyl lactate were obtained based on the data by Vu et al. ( 2006). Finally
the parameters between lactic acid and all other species were estimated using data from the
quaternary system measured by Delgado et al. (2007a). The parameters were estimated
minimizing the following objective function (Fob):
∑∑ ⎟⎟⎠
⎞⎜⎜⎝
⎛ −=
j i ji
calciiFob
2
exp
exp
γ
γγ (3.6)
where i is the species and j the experimental data point. It should be mentioned that the
parameters between water and ethanol were found in the DECHEMA books (Gmehling et al.,
1981). The interaction parameters are given in Table 3.2.
Table 3.2 UNIQUAC interaction parameters (K).
Ethanol Ethyl lactate Water Lactic acid
Ethanol 0.0000 -152.319 -17.554 + 0.2797 T (K)* -35.008
Ethyl Lactate 264.990 0.0000 207.789 -20.986
Water -21.987 + 0.2276 T (K)* -13.093 0.0000 -99.183
Lactic Acid 33.741 219.89 213.19 0.0000
*DECHEMA (Gmehling et al., 1981)
The average relative deviation found for the activity coefficients were 12.9 %, but special
difficulties were found when describing the behaviour of diluted solutions, which was never
the case when the chemical equilibrium experimental studies were carried out in this work.
3.3.2 Equilibrium constant and reaction enthalpy for the synthesis of Ethyl Lactate
Using the data found experimentally for the chemical equilibrium compositions in 14
different runs, at 4 different temperatures in the range between 323.15 and 362.87 K, it was
found the following relation for the equilibrium constant:
515.13ln( ) 2.9625( )
KT K
= − (3.7)
Using this result and the iterative procedure described before, the deviations found between
the experimental and calculated equilibrium compositions for all experiments are given in
Table 3.3. It can be seen that the higher deviation found between the experimental and
calculated equilibrium composition is of about 5.6 %.
46 CHAPTER 3. Thermodynamic Equilibrium and Reaction Kinetics
Table 3.3 Experimental and calculated equilibrium compositions for all the experiments performed and the correspondent deviation percent.
Equilibrium composition (mole fraction)
Experimental Calculated T (K)
Ethanol Ethyl lactate Water Lactic
acid Ethanol Ethyl lactate Water Lactic
acid
average deviation
(%)
323.15 0.3598 0.1776 0.3732 0.0894 0.3561 0.1813 0.3769 0.0857 2.06
323.15 0.3336 0.1773 0.384 0.1051 0.3264 0.1845 0.3913 0.0978 3.77
323.15 0.1812 0.1854 0.4527 0.1808 0.1931 0.1734 0.4407 0.1928 5.58
333.15 0.3561 0.1813 0.3769 0.0857 0.3528 0.1846 0.3802 0.0824 1.87
333.15 0.3307 0.1802 0.3869 0.1021 0.3228 0.1881 0.3948 0.0943 4.11
333.15 0.1794 0.1871 0.4544 0.179 0.1881 0.1784 0.4457 0.1878 4.08
343.15 0.3527 0.1847 0.3803 0.0823 0.3498 0.1876 0.3832 0.0794 1.67
343.15 0.3297 0.1812 0.3879 0.1012 0.3194 0.1915 0.3982 0.0909 5.41
343.15 0.1799 0.1866 0.4539 0.1796 0.1835 0.1831 0.4504 0.183 1.64
343.41 0.451 0.1682 0.3295 0.0512 0.451 0.1683 0.3295 0.0512 0.01
343.41 0.4495 0.1698 0.3311 0.0497 0.451 0.1683 0.3295 0.0512 1.18
353.40 0.1983 0.1975 0.4525 0.1517 0.202 0.1937 0.4488 0.1555 1.78
362.87 0.4474 0.1719 0.3331 0.0476 0.4474 0.1718 0.3331 0.0477 0.07
362.87 0.4459 0.1734 0.3347 0.0461 0.4474 0.1718 0.3331 0.0477 1.30
In Table 3.4 the activity coefficients for the equilibrium composition and the thermodynamic
equilibrium constant are presented. In terms of equilibrium conversion the average relative
deviation found was 2.60%, being possible to find an average reaction enthalpy of
4.28 kJ·mol-1 in that temperature interval. Some authors (Zhang et al., 2004) have also
indicated the reaction is slightly endothermic, but uncertainty is high. In fact using the values
found for the standard state enthalpy of formation in the DIPPR 801 database (DIPPR, 1998)
(see Table 3.5) it is possible to calculate -20.97 ± 186.7 kJ·mol-1 for the reaction enthalpy at
298.15 K. This considerable high error (± 186.7 kJ·mol-1) is mainly due to the high
uncertainty on the ethyl lactate standard state enthalpy of formation. Nevertheless the value
found is in good agreement to values given in the literature (Benedict et al., 2003; Zhang et
al., 2004).
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 47
Table 3.4 Activity coefficients for the equilibrium composition and the thermodynamic equilibrium constant.
Activity coefficients T (K)
Ethanol Lactic acid
Ethyl lactate Water
K
323.15 1.0563 1.2391 1.3557 1.6928 3.9291
323.15 1.0563 1.2632 1.3941 1.6629 3.9291
323.15 1.0263 1.3238 1.7011 1.5288 3.9291
333.15 1.0652 1.2397 1.3386 1.6847 4.1217
333.15 1.0660 1.2643 1.3749 1.6547 4.1217
333.15 1.0398 1.3285 1.6644 1.5200 4.1217
343.15 1.0737 1.2396 1.3222 1.6771 4.3116
343.15 1.0755 1.2649 1.3564 1.6467 4.3116
343.15 1.0531 1.3325 1.6300 1.5117 4.3116
343.41 1.0607 1.1543 1.2338 1.7832 4.3165
343.41 1.0607 1.1543 1.2338 1.7832 4.3165
353.40 1.0749 1.3350 1.5295 1.5267 4.5035
362.87 1.0707 1.1511 1.2125 1.7715 4.6781
362.87 1.0707 1.1511 1.2125 1.7715 4.6781
Table 3.5 Standard state enthalpy of formation of the different species (Gmehling et al., 1981).
Ethanol Lactic acid Ethyl lactate Water
fH 0Δ (kJ·mol-1) -234.950 -682.960 -695.084 -241.814
Error < 1 % < 10 % < 25 % < 0.2 %
3.3.3 Application of this methodology to other works
The equilibrium compositions and equilibrium conversions of other studies (Benedict et al.,
2003; Delgado et al., 2007b; Troupe and DiMilla, 1957) were predicted by the UNIQUAC
model and the equilibrium constant proposed in this work. It should be noticed that those
equilibrium compositions were not used in the estimation of the UNIQUAC parameters nor in
the estimation of chemical equilibrium constant presented by Equation 3.7. The comparison
48 CHAPTER 3. Thermodynamic Equilibrium and Reaction Kinetics
between the experimental and calculated equilibrium compositions is shown in Figure 3.3.a
for ethanol and water; and Figure 3.3.b for lactic acid and ethyl lactate.
0.0
0.2
0.4
0.6
0.8
1.0
0.0 0.2 0.4 0.6 0.8 1.0xexp
xcal
c
Ethanol
Water
Molar Fraction
Figure 3.3.a Experimental and calculated equilibrium molar fraction
of ethanol and water species.
0.00
0.05
0.10
0.15
0.20
0.00 0.05 0.10 0.15 0.20
xexp
xcal
c
Ethyl LactateLactic Acid
Molar Fraction
Figure 3.3.b Experimental and calculated equilibrium molar fraction
of ethyl lactate and lactic acid species.
The equilibrium compositions are very well predicted for ethanol and water; while for the
ethyl lactate and lactic acid deviations are higher, but even so satisfactory. The larger
deviations can be due to the fact that the interaction parameters used in UNIQUAC model for
those particular species are not based in a large and consistent set of experimental vapour
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 49
liquid equilibrium (VLE) data as is the case for water and ethanol species. Furthermore the
composition range is now much restricted (maximum mole fraction around 0.20), for which
the model presents more difficulties to calculate accurately the activity coefficients and the
analytical method for these species is not as precise as it is for water and ethanol compounds.
In terms of the deviation of experimental and calculated equilibrium conversion (Figure 3.4),
it can be seen that when 85 wt. % lactic acid feed is used, the model prediction is quite good.
In the remaining cases, for 44 wt. % lactic acid and mainly for 20 wt. % lactic acid solution
the deviations are more significant. This is maybe due to the fact that diluted solutions in
lactic acid and, obviously, in ethyl lactate are used, and like mentioned before the UNIQUAC
model does not describe with the desired accuracy the behaviour of that kind of solutions. If
possible it would be preferable to use activity coefficients at infinite dilution.
0.0
0.2
0.4
0.6
0.8
1.0
0.0 0.2 0.4 0.6 0.8 1.0Xexp
Xcal
c
La 20 wt.% (Delgado et al., 2007a) La 44 wt.% (Troupe and Dimilla, 1957) La 85 wt.% (Troupe and Dimilla, 2003) La 85 wt.% (Benedict et al., 2003) La 85 wt.% (This work)
Equilibrium conversion
Figure 3.4 Experimental and calculated equilibrium conversion. (Data collected
from Troupe and Dimilla (1957), Benedict et al. (2003), Delgado et al. (2007) and this work).
3.4 Kinetic Studies
The experimental results of the reaction kinetics of the esterification of lactic acid and ethanol
catalyzed by the Amberlyst 15-wet resin are presented in this section. The effect of various
conditions, such as, catalyst loading, initial molar ratio between ethanol and lactic acid and
reaction temperature on lactic acid conversion as function of time is studied. This study was
50 CHAPTER 3. Thermodynamic Equilibrium and Reaction Kinetics
performed varying the condition under evaluation and keeping constant the remaining
conditions, in absence of mass transfer limitations and catalyst deactivation as shown by the
preliminary studies performed.
3.4.1 Preliminary Studies
3.4.1.1 Evaluation of external mass transfer limitations (effect of stirring speed)
To quantify the influence of external mass transfer resistance preliminary experiments at
different stirring speed were run using a molar ratio of ethanol to lactic acid of 1.82 at
324.18 K and 2.4 wt. % of Amberlyst 15-wet with particle diameter 0.5 < dp < 0.6 mm.
Figure 3.5 shows the conversion of lactic acid as a function of time at different stirring speed.
With a stirring speed of 600 rpm, there is no limitation due to external resistance, so all
further experiments were done at 600 rpm.
0
0.1
0.2
0.3
0.4
0.5
0.6
0 200 400 600 800
Conv
ersi
on
Time (min)
600 rpm
800 rpm
Figure 3.5 Experimental data obtained at different stirrer speeds for a
molar ratio of ethanol to lactic acid of 1.82 at 324.18 K using 2.4 wt. % of Amberlyst 15-wet as catalyst with particle diameter 0.5 < dp < 0.6 mm.
3.4.1.2 Evaluation of internal mass transfer limitations (effect of particle size)
The Amberlyst 15wet was separated by particle size and three classes with different diameters
were obtained: 0.425mm<dp<0.5mm; 0.5mm<dp<0.6mm and 0.6mm<dp<0.85mm. Figure
3.6 shows the effect of the different particle diameters, including the unsieved resin, which
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 51
has an average diameter of 0.685 mm, on the conversion of lactic acid; it can be seen that
there are no significant internal diffusion limitations for the experiments performed.
Therefore, the unsieved resin was used for the following kinetic experiments performed in
this work. This is in agreement with several works performed with this kind of resin and type
of reaction (Delgado et al., 2007b; Liu and Tan, 2001; Pöpken et al., 2000; Zhang et al.,
2004).
0
0.1
0.2
0.3
0.4
0.5
0.6
0 200 400 600 800
Conv
ersi
on
Time (min)
unsieved resin
0.6<dp<0.85
0.5<dp<0.6
0.425<dp<0.5
Figure 3.6 Effect of catalyst particle size on the conversion of lactic acid history
for a molar ratio of ethanol to lactic acid of 1.82 at 324.18 K using 2.4 wt. % of catalyst and stirrer speed of 600 rpm.
3.4.1.3 Evaluation of catalyst deactivation (effect of catalyst reusability)
The Amberlyst 15-wet catalyst reusability was studied at 344.05 K. The resin was reused up
to three times. First, a reaction was carried out using fresh catalyst. Then the catalyst used
was separated from the reaction mixture by filtration, washed several times with deionised
water and dried at 90ºC until the mass remained constant and charged again to the reactor. A
new esterification reaction was performed using the same conditions that the first one and so
on. The lactic acid conversion as a function of time was analyzed and the three conversion
histories are presented in Figure 3.7. As it can be seen no significant changes were observed.
The resin activity was kept the same in the three runs. However, each experiment was
performed using fresh Amberlyst 15-wet catalyst. Some authors (Dixit and Yadav, 1996)
studied the reusability of the Amberlyst 15-wet in the alkylation reaction of o-xylene with
styrene and they observed a drastic reduction in the conversion of styrene due to the direct
deposition of the by-products on the active sites and the loss of accessibility of the active sites
52 CHAPTER 3. Thermodynamic Equilibrium and Reaction Kinetics
due to pore blockage. So, it can be concluded that the catalytic activity of the resins depends
on its interaction with the reaction medium.
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0 200 400 600 800 1000 1200
Con
vers
ion
Time (min)
fresh catalyst2nd use3rd use
Figure 3.7 Effect of the Amberlyst 15-wet reusability on the conversion of lactic acid
history at 344.05 K for a molar ratio of ethanol to lactic acid of 1.82 using 2.4 wt. % of Amberlyst 15-wet catalyst with an average particle diameter of 0.685 mm and stirrer speed of 600 rpm.
3.4.2 Kinetic Model
The esterification reactions have been described using different models, such as, pseudo-
homogeneous, Eley-Rideal and Langmuir-Hinshelwood model (L-H model) (Lee et al., 2002;
Lilja et al., 2005; Pöpken et al., 2000; Sanz et al., 2002; Teo and Saha, 2004). However, the
L-H model has been considered the most appropriate model for the reaction between lactic
acid and ethanol (Delgado et al., 2007b; Zhang et al., 2004). Therefore, the model developed
is based on an L-H mechanism and it considers the following steps:
Ethanol and Lactic acid adsorption:
SEthSEth EthsK .,⎯⎯ →←+
SLaSLa LasK .,⎯⎯ →←+
Surface reaction between the adsorbed species of ethanol and lactic acid:
SWSELSLaSEthK
....1
++ ⇔
desorption of ethyl lactate and water:
SELSEL ELsK +⎯⎯ →←*,.
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 53
SWSW WsK +⎯⎯ →←*,.
Surface reaction is assumed to be the controlling step, with the other steps remaining in
equilibrium. Multi-component Langmuir adsorption isotherms, written in terms of activities,
are assumed to describe the adsorption behaviour of the compounds of the reaction mixture in
the surface of the resin. Taking into account the above considerations the following rate
expression, written in terms of activities of components, due to the non-ideality of the
reaction mixture, is obtained:
2
,1 ⎟⎠
⎞⎜⎝
⎛+
−=
∑=
W
Ethiiis
WELLaEth
c
aK
Kaaaa
kr (3.8)
where kc is the kinetic constant, isK , is the adsorption constant for species i and K is the
equilibrium reaction constant.
In order to reduce the number of optimization parameters it was taken into account only those
components that had the strongest adsorption. It was considered that the most polar
molecules, water and ethanol, have the strongest adsorption strength on the Amberlyst 15-wet
surface, being therefore neglected the adsorption of lactic acid and ethyl lactate. This
consideration is corroborated by several works of adsorption in similar resins (Mazzotti et al.,
1997; Sanz et al., 2002; Silva and Rodrigues, 2002; Zhang et al., 2004). Thus, the simplified
rate expression used to describe the experimental data is:
2,, )1( WWsEthEths
WELLaEth
c aKaKKaa
aakr
++
−= (3.9)
In this kinetic model (Equation 3.9) there are three parameters to be estimated, at each
temperature, the kinetic constant (kc) and the two adsorption parameters (Ks,Eth and Ks,W),
instead of five if the rate Equation 3.8 was used to describe the experimental data.
The temperature dependence of kinetic constant was fitted with the Arrhenius equation:
⎟⎠
⎞⎜⎝
⎛−=RTE
kk aCC exp,0 (3.10)
where aE is the reaction activation energy, ck ,0 is the pre-exponential constant, R is the gas
54 CHAPTER 3. Thermodynamic Equilibrium and Reaction Kinetics
constant and T is the temperature.
The temperature dependence of the adsorption equilibrium constants were fitted with:
⎟⎠
⎞⎜⎝
⎛ Δ−=
RTH
KK sss exp,0 (3.11)
where sK ,0 is the constant for Equation 3.11 and SHΔ is the adsorption enthalpy.
3.4.2.1 Parameter estimation from experimental data
The mass balance in the batch reactor for a component i, in liquid phase, at constant
temperature is given by:
rwvtdnd
catii = (3.12)
where in is the number of moles of component i, t is the time, catw is the mass of catalyst
and r is the reaction rate expressed in moles i / (mass of catalyst .min).
The number of moles of component i ( in ) as a function of the conversion X of the limiting
reactant ( l ) is:
⎟⎟⎠
⎞⎜⎜⎝
⎛+=
lilili
XRnnν
ν/0, (3.13)
where 0,ln and lν are, respectively, the initial moles number and the stoichiometric
coefficient of the limiting reactant and /i lR is given by:
0,
0,/
l
ili n
nR = (3.14)
where 0,in is the initial number of moles of component i .
Introducing Equation 3.13 into Equation 3.12 we get:
0,l
catl
nrw
tdXd ν= (3.15)
with the initial condition: 00; Xt == .
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 55
The differential Equation 3.15 combined with the suggested rate expression, Equation 3.9,
was solved numerically with the DASOLV integrator implemented in gPROMS-general
PROcess Modelling System version: 3.0.3, which is a commercial package from Process
Systems Enterprise. For all simulations a tolerance equal to 10-5 was fixed. The estimation of
the unknown parameters ( aE , ck ,0 , EthK ,0 , WK ,0 , EthHΔ and WHΔ ) was carried out using the
“Parameter estimation in gProms” that attempts to determine the values for the parameters, in
order to maximize the probability that the mathematical model will predict the values
obtained from experiments. Assuming independent, normally distributed measurements
errors, ikε , with zero means and standard deviations, ikσ , this maximum likelihood goal can
be captured through the following objective function:
⎪⎭
⎪⎬⎫
⎪⎩
⎪⎨⎧
⎥⎦
⎤⎢⎣
⎡ −++=Φ ∑∑
= =
NE
i
NM
k ik
ikikik
i XXN1 1
2
'2 )ln(
21)2ln(
2 min σσπ
θ (3.16)
Where, N is the total number of measurements taken during the experiments ( 290=N ), θ is
the set of model parameters to be estimated ( 6=θ ), NE is the number of experiments
performed ( 15=NE ), iNM is the number of measurements of the conversion in the ith
experiment, 2ikσ is the variance of the kth measurement of the conversion in experiment i
( 321083.1 −×=σ ) , '
ikX is the kth measured value of conversion in experiment i and,
finally, ikX is the kth (model-) predicted value of conversion in experiment i. The quality of
the model fit was tested through the mean relative deviation (MRD) between the calculated
conversion values (Xcalc) and the experimental ones (Xexp) (see Equation 3.17).
%100*1
exp
exp
⎟⎟
⎠
⎞
⎜⎜
⎝
⎛ −= ∑
N
calc
XXX
NMRD (3.17)
3.4.3 Modelling and discussion of results
The simplified L-H model (Equation 3.9) was used to describe the kinetic behaviour of the
esterification of lactic acid with ethanol using Amberlyst 15-wet as catalyst. In order to obtain
the unknown parameters at least two different experiments (different initial molar ratio) were
performed for each temperature, which varied from 323.15 K to 363.15 K. The values of the
56 CHAPTER 3. Thermodynamic Equilibrium and Reaction Kinetics
optimized parameters along with the MRD value are presented in Table 3.6. A value of MRD
between experimental and calculated conversion of 6.8 % was obtained.
As mentioned before in section 3.4.2 the Arrhenius equation was used to fit the kinetic (kc)
constant (Figure 3.8) and the Equation 3.11 was used to fit the adsorption constants (Ks,Eth and
Ks,W) which are given by ( ))(/01.12exp19.15 KTKW = and ( ))(/63.359exp22.1 KTK Eth = . From
the temperature dependence of the kinetic constant the apparent activation energy was
calculated being the correspondent value 49.98 kJ/mol.
Table 3.6 Parameters of the kinetic model expressed in terms of activities (Equation 3.9) and the mean relative deviation, MRD.
k0,c (mol.g-1.min-1)
Ea (kJ.mol-1) K0, W WHΔ
(J.mol-1) K0, Eth EthHΔ
(J.mol-1) MRD (%)
2.70×107 49.98 15.19 - 99.85 1.22 - 29.95×102 6.84
-2
-1.5
-1
-0.5
0
0.5
1
2.7 2.8 2.9 3 3.1 3.2
ln kc
1000/T (K-1) Figure 3.8 Representation of experimental values of ckln as
function of T/1 and linear fitting.
3.4.3.1 Effect of catalyst loading
The catalyst loading was varied from 1.2 wt. % to 3.9 wt. % (weight of catalyst/total weight
of reaction mixture) keeping the rest of the experimental conditions similar. The effect of the
catalyst loading on the esterification reaction between lactic acid and water is shown in
Figure 3.9. As may be observed the reaction rate increases with the percentage of Amberlyst
15-wet. This was expected since the increase of catalyst implies an increase in the number of
active sites available for the reaction.
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 57
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0 50 100 150 200 250 300
Conv
ersi
on
Time (min)
1.2 wt.%2.4 wt.%3.9 wt.%L-H model
Figure 3.9 Effect of catalyst loading on the conversion of lactic acid history for a
molar ratio of ethanol to lactic acid of 1.82 at 353.49 K and using an average particle diameter of 0.685 mm and stirrer speed of 600 rpm.
3.4.3.2 Effect of initial molar ratio of reactants
To study the effect of the initial molar ratio of reactants (REth/La) on the conversion of lactic
acid, this condition was varied from 1.1 to 2.8, as presented in Figure 3.10. It can be seen that
the equilibrium conversion increases with the increase of the initial molar ratio of ethanol to
lactic acid and that the equilibrium is achieved faster for larger initial molar ratio values.
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0.9
0 500 1000 1500 2000 2500
Conv
ersi
on
Time (min)
REth/La = 1.1
REth/La = 1.8
REth/La = 2.8
L-H model
Figure 3.10 Effect of initial molar ratio of ethanol to lactic acid on the conversion
of lactic acid history at 353.40 K and using 2.4 wt. % of Amberlyst 15-wet catalyst with an average particle diameter of 0.685 mm and stirrer speed of 600 rpm.
58 CHAPTER 3. Thermodynamic Equilibrium and Reaction Kinetics
It may be observed from Figure 3.10 that the experiments are initially well predicted by the
model (until about 120 minutes); and due to the methodology developed in this work, the
equilibrium is also well described. However, there is a transient state (between 120 minutes
till the equilibrium), where the model fails to describe the experiments, being more significant
for higher values of initial molar ratio between ethanol and lactic acid.
3.4.3.3 Effect of reaction temperature
The effect of reaction temperature is shown in Figure 3.11. The reaction rate increases with
the reaction temperature. The same effect is noticed on the equilibrium conversion. Once
again, it can be noticed that in the transient state, the model predicts higher conversion of
lactic acid values than those obtained experimentally.
0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
0.8
0 500 1000 1500 2000 2500 3000
Conv
ersi
on
Time (min)
T = 324.14 KT = 333.11 KT = 344.05 KT = 353.40 KT = 363.50 KL-H model
Figure 3.11 Effect of the reaction temperature on the conversion of lactic acid
history for a molar ratio of ethanol to lactic acid of 1.82 and using 2.4 wt. % of Amberlyst 15-wet catalyst.
3.4.3.4 Effect of Lactic acid and Ethyl Lactate oligomers
The proposed model shows a kinetic behaviour with two limiting situations:
a) first slope at the beginning of the experiment, corresponding to the initial reaction
rate;
b) final plateau, corresponding to the reaction equilibrium.
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 59
However, experimentally, it seems that there are three limiting situations, where the first and
third are the same that the ones described by the proposed model, but the transient state is
represented by a line with very small slope. This could be due to the presence of the lactic
acid oligomers, and consequently ethyl lactate oligomers that where formed. To confirm this
assumption an evaluative modelling study was made considering the oligomers presence
using the kinetic model and the correspondent’s parameters reported in literature (Tanaka et
al., 2002).
In Figure 3.12a the molar fractions of the ethyl lactate, lactic acid, ethanol and water as
function of time are presented, being the correspondent’s oligomers presented in Figure
3.12b. Analysing the simulated kinetic curve for the ethyl lactate monomer, here denominated
just as ethyl lactate, one can conclude a similar behaviour with the experimental results
shown in this work, where there are three limiting steps:
a) initial conversion of lactic acid oligomers in ethyl lactate oligomers, but the kinetic
rate is much higher for the monomers than for the dimers and trimers. Therefore the
experiments are initially well predicted;
b) transient state, where the ethyl lactate monomer concentration increases slowly, since
several reversible reactions are occurring and the equilibrium is shifted towards lactic
acid monomer formation and consequently ethyl lactate monomer. In this transient
step, firstly, the dimers concentrations of lactic acid and ethyl lactate decrease due to
their hydrolysis, and then the same happens to the trimers that are converted into
dimers and finally again into monomers, till the equilibrium is reached;
c) reaction equilibrium, when all the reversible reactions are in equilibrium, the total
amount of lactic acid and ethyl lactate oligomers are less then 0.4%. Therefore, the
experiments are well predicted at the equilibrium since oligomers presence is
negligible.
60 CHAPTER 3. Thermodynamic Equilibrium and Reaction Kinetics
0 10 20 30 40 50 480 490 5000.0
0.1
0.2
0.3
0.4
0.5
0.6
0.7
Mol
ar fr
actio
n
Time (min)
Ethyl lactate Ethanol Lactic acid Water
Figure 3.12a Molar fraction histories of the compounds: ethyl lactate monomer, ethanol,
lactic acid monomer and water. KT 15.363= and 3/ =LaEthR . The kinetic model and the parameters used were taken from Tanaka et al. (2002).
0 10 20 30 40 50 480 490 5000.00
0.01
0.02
0.03
0.04
0.05
0.06
Mol
ar fr
actio
n
Time (min)
Ethyl lactate dimer Ethyl lactate trimer Lactic acid dimer Lactic acid trimer
Figure 3.12b Molar fraction histories of the oligomers: ethyl lactate dimer, ethyl lactate trimer, lactic acid dimer and lactic acid trimer.
KT 15.363= and 3/ =LaEthR . The kinetic model and the parameters used were taken from Tanaka et al. (2002).
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 61
The transient behaviour, where the hydrolysis of dimers and trimers of lactic acid and ethyl
lactate are dominant to produce the ethyl lactate monomer, is even more noticeable for higher
values of initial molar ratio of ethanol/lactic acid, as it can be shown in Figure 3.13a. This is
due to the fact that the excess of ethanol benefits more the ethyl lactate dimer formation as
shown in Figure 3.13b, that will be further hydrolysed and the lactic acid dimer formed will
be converted into lactic acid monomer that will be finally converted into ethyl lactate
monomer. Nevertheless, in the equilibrium composition the excess of ethanol leads to smaller
amounts of oligomers (2.4 molar % in the case of 1/ =laEthR and 0.4 molar % in case
of 3/ =laEthR ).
0 10 20 30 40 50 480 490 5000.00
0.05
0.10
0.15
0.20
0.25
Mol
ar fr
actio
n
Time (min)
Ethyl lactate, REth/La= 1 Lactic acid, REth/La= 1 Ethyl lactate, REth/La= 3 Lactic acid, REth/La= 3
Figure 3.13a Molar fraction histories of ethyl lactate and lactic acid for different
initial molar ratios. KT 15.353= . The kinetic model and the parameters used were taken from Tanaka et al. (2002).
62 CHAPTER 3. Thermodynamic Equilibrium and Reaction Kinetics
0 10 20 30 40 50 480 490 5000.000
0.002
0.004
0.006
0.008
0.010
0.012
0.014
0.016
0.018M
olar
frac
tion
Time (min)
Ethyl lactate dimer, REth/La= 1 Ethyl lactate dimer, REth/La= 3
Figure 3.13b Molar fraction histories of ethyl lactate dimer for different initial
molar ratios. KT 15.353= . The kinetic model and the parameters used were taken from Tanaka et al. (2002).
3.4.3.5 Effect of polar species
The activity of the resin varies with the polarity of the reaction medium, since it influences
the number of available sulfonic groups and their acidity (Fite et al., 1998). The polarity of
the medium, mainly due to the water and alcohol concentrations, can affect the reaction rate
in two ways:
i) the more adsorbed species (water and alcohol) inhibit the others to adsorb onto the
active sites.
ii) water can ionize, solvate and dissociate the acidic protons of the sulfonic groups,
depending on their concentration; when the sulfonic sites are completely dissociated
the reaction occurs in the liquid phase as in the case of homogeneous catalysis
(Gomez et al., 2004).
In this case, the reaction medium has a high water concentration; besides the water initially
present in the reaction due to the lactic acid solution, more water is being formed during the
course of the esterification of lactic acid with ethanol. Although the kinetic model proposed in
this work has taken into account the inhibitory effect caused by adsorption, it doesn’t consider
the remaining effects that could be due to water or ethanol presence. Therefore, this could
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 63
also be a reason for the deviations between the experimental results and the predicted by the
kinetic model in the transient stage. Françoisse and Thyrion studied the ETBE synthesis
catalyzed by Amberlyst 15 (Françoisse and Thyrion, 1991). In that study the influence of
ethanol in the reaction rate was taken into account. A kinetic model to describe the behaviour
of the reaction for low and high ethanol concentrations was developed. However, this case is
different from the one presented in this work, since the most adsorbed component is ethanol
and there is no water as reaction product. They use a non-polar solvent (n-pentane) and the
other reactant (isobutene) is also non-polar. In the case under study, besides ethanol there is
also lactic acid concentrated solution that has high water content. Therefore, at the beginning
of the reaction there are three polar species competing to the acid sites; it was observed that
the initial kinetic rate increases with the ethanol concentration till a plateau, which was not
the behaviour observed in the ETBE kinetics. Most of the works about the esterification
reaction of ethanol and lactic acid considers that water and ethanol are the most adsorbed
species that supports our kinetic model assumptions (Delgado et al., 2007b; Zhang et al.,
2004). Moreover, in a later work for the esterification of lactic acid with butanol catalyzed by
Amberlyst 15, the authors didn’t observe different mechanisms for high and low alcohol
concentration, and similarly with our model, they neglect the oligomers presence and only
considered the water adsorption (Dassy et al., 1994).
The proposed model describes quite well the experimental data up to 80 % of the equilibrium
conversion as well as the equilibrium stage, which are the most important to apply to a hybrid
reactive separation technology.
3.5 Conclusions
The equilibrium composition for the liquid phase reaction of ethyl lactate synthesis catalyzed
by the acid ion exchange resin Amberlyst 15-wet was measured in the temperature range of
50-90ºC, at 6 bars. The thermodynamic equilibrium constant estimated by the UNIQUAC
method was ( )KTK 13.5159625.2ln −= and the average reaction enthalpy was of
4.28 kJ·mol-1 in that temperature interval. This relation was also successfully applied to
describe the equilibrium compositions of other published studies; better prediction was found
for systems where high concentrations of lactic acid was used.
64 CHAPTER 3. Thermodynamic Equilibrium and Reaction Kinetics
Because of the strong non-ideality of the liquid reaction mixture, the reaction rate model was
formulated in terms of activities. The rate-controlling step for the esterification reaction
between lactic acid and ethanol, heterogeneously catalyzed by the Amberlyst 15-wet, was the
surface reaction, since external and internal mass resistances were insignificant for the
temperature range of 50-90ºC. The catalyst reusability was also studied and it was not
verified catalyst deactivation till 3 usages of the same resin sample.
A three-parameter model based on a Langmuir-Hinshelwood rate expression was proposed to
describe the experimental kinetic results:
( ) 2)1(/ WWEthEthWELLaEthc aKaKKaaaakr ++−= ; and the model parameters are
( )7 1 12.70 10 exp 6011.55 / ( ) ( . .min )ck T K mol g − −= × − , ( ))(/01.12exp19.15 KTKW =
and ( ))(/63.359exp22.1 KTKEth = . The agreement between experimental and simulated
results was good for the following operating conditions: catalyst loading from 1.2 wt. % to
3.9 wt. %, initial molar ratio of reactants from 1.1 to 2.8 and temperature from 50ºC to 90ºC.
3.6 Notation
a liquid phase activity
pd pellet diameter (m)
df film thickness (µm)
aE apparent reaction activation energy (J mol-1)
K equilibrium reaction constant
xK equilibrium constant based on molar fractions
γK equilibrium constant based on activity coefficients
sK equilibrium adsorption constant
ck kinetic constant (mol g-1 min-1)
ck ,0 pre-exponential factor (mol g-1 min-1)
sK ,0 constant for Equation 3.11
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 65
MRD mean residual deviation
n number of moles (mol)
N total number of measurements taken during the experiments
NE number of experiments performed
iNM number of measurements of the conversion in experiment i
sHΔ enthalpy of adsorption (J mol-1)
fH 0Δ standard enthalpy of formation (J mol-1)
ºGΔ standard Gibs energy of reaction (J mol-1)
R gas constant (J mol-1 K-1)
r reaction rate (mol g-1 min-1)
LaEthR / initial molar ratio of ethanol to lactic acid
t time coordinate (min)
T temperature (K)
X conversion of the limiting reactant
x molar fraction
catw mass of dry catalyst (g)
ikX kth (model-) predicted value of conversion in experiment i
'ikX kth measured value of conversion in experiment i
Greek letters
ν stoichiometric coefficient
γ activity coefficient
θ set of model parameters to be estimated
2ikσ variance of the kth measurement of conversion in experiment i
2σ average of variance
66 CHAPTER 3. Thermodynamic Equilibrium and Reaction Kinetics
Subscripts
0 initial value
Eth ethanol
La lactic acid
EL ethyl lactate
W water
exp experimental
calc calculated
i relative to component i
l relative to limiting reactant
3.7 References Cited
Asthana N. S., A. K. Kolah, D. T. Vu, C. T. Lira and D. J. Miller, "A kinetic model for the esterification of lactic acid and its oligomers", Ind. Eng. Chem. Res. 45(15): 5251-5257, 2006.
Benedict D. J., S. J. Parulekar and S.-P. Tsai, "Esterification of Lactic Acid and Ethanol with/without Pervaporation", Ind. Eng. Chem. Res. 42(11): 2282-2291, 2003.
Chen Z. T., J. S. Zhong, Q. F. Li, Y. H. Li and Z. H. Ou, "Esterification on Zeolites", Science in China Series B-Chemistry 32(7): 769-775, 1989.
Dassy S., H. Wiame and F. C. Thyrion, "Kinetics or the liquid phase synthesis and hydrolysis of butyl lactate catalysed by cation exchange resin", J. Chem. Technol. Biotechnol. 59(2): 149-156, 1994.
Delgado P., M. T. Sanz and S. Beltran, "Isobaric vapor-liquid equilibria for the quaternary reactive system: Ethanol + water + ethyl lactate + lactic acid at 101.33 kPa", Fluid Phase Equilib. 255(1): 17-23, 2007a.
Delgado P., M. T. Sanz and S. Beltran, "Kinetic study for esterification of lactic acid with ethanol and hydrolysis of ethyl lactate using an ion-exchange resin catalyst", Chem. Eng. J. 126(2-3): 111-118, 2007b.
DIPPR, "Thermophysical Properties Database", (1998).
Dixit A. B. and G. D. Yadav, "Deactivation of ion-exchange resin catalysts. Part I: Alkylation of o-xylene with styrene", React. Funct. Polym. 31(3): 237-250, 1996.
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 67
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Lee M. J., J. Y. Chiu and H. M. Lin, "Kinetics of catalytic esterification of propionic acid and n-butanol over Amberlyst 35", Ind. Eng. Chem. Res. 41(12): 2882-2887, 2002.
Lee M. J., H. T. Wu and H. M. Lin, "Kinetics of catalytic esterification of acetic acid and amyl alcohol over dowex", Ind. Eng. Chem. Res. 39(11): 4094-4099, 2000.
Lilja J., D. Y. Murzin, T. Salmi, J. Aumo, P. Mäki-Arvela and M. Sundell, "Esterification of different acids over heterogeneous and homogeneous catalysts and correlation with the taft equation", J. Mol. Catal. A: Chem. 182-183: 555-563, 2002.
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68 CHAPTER 3. Thermodynamic Equilibrium and Reaction Kinetics
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PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 69
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4. Fixed Bed Adsorptive Reactor
Abstract. Multi-component adsorption equilibrium data were measured through binary
adsorption experiments performed in a fixed bed column packed with Amberlyst 15-wet for
the ethyl lactate system, at 20ºC and 50ºC. A novel approach based on multi-component
Langmuir isotherm was used assuming a constant monolayer capacity in terms of volume for
all species, reducing the adjustable parameters from 8 to 5, for each temperature. Reactive
adsorption experiments were performed and used to validate a mathematical model developed
for both fixed bed and simulated moving bed reactors, which involves velocity variations due
to the change of multi-component mixture properties.
Adapted from: Pereira C. S. M., V. M. T. M. Silva and A. E. Rodrigues, "Fixed Bed Adsorptive Reactor for
Ethyl Lactate Synthesis: Experiments, Modelling, and Simulation", Sep. Sci. Technol. 44(12): 2721 - 2749,
2009.
72 CHAPTER 4. Fixed Bed Adsorptive Reactor: Experiments, Modelling and Simulation
4.1 Introduction
The conventional way to produce ethyl lactate is by the esterification of lactic acid with
ethanol in the presence of an acid catalyst. The conversion of this kind of reactions is limited
by the chemical equilibrium; therefore, the technology for the industrial preparation of esters
involves two consecutive steps. The first is the reaction itself, which stops when the
equilibrium is reached. The second is the separation of the products from the equilibrium
mixture containing products and unconverted reactants. The disadvantage of this technology
is in its economics, because of the high energy costs and investment in several reaction and
separation units. Multifunctional reactors, where reaction and separation take place into a
single unit, allow, in addition to obvious savings in equipment costs, significant
improvements in process performance for reactions limited by chemical equilibrium. By
removing one of the products from the reaction zone, the equilibrium limitation can be
overcome and the conversion can be driven to completion.
In the esterification reaction between lactic acid and ethanol the catalyst used is usually
concentrated sulphuric acid (Zhang et al., 2004). However, its application has several
drawbacks (as separation problems and corrosion of equipment) and, thus, the use of
heterogeneous catalysts is preferable. Among this type of catalysts, strongly acid resins, like
Amberlyst 15-wet (A15), are of great interest in the case of reversible reactions, as
esterifications and acetalizations, since they can act as catalyst and also as selective adsorbent
(Funk et al., 1995; Gandi et al., 2006; Kawase et al., 1996; Mazzotti et al., 1996; Ruggieri et
al., 2003; Silva and Rodrigues, 2002). Accordingly, the synthesis of ethyl lactate in a
chromatographic reactor using the A15 resin is very attractive. The simulated moving bed
reactor (SMBR) is one of the most interesting chromatographic reactors and has been applied
to several reversible reactions catalyzed by acidic resins (Borges da Silva et al., 2006;
Kawase et al., 1996; Lode et al., 2003; Mazzotti et al., 1996; Minceva et al., 2008; Pereira et
al., 2008; Silva and Rodrigues, 2005; Yu et al., 2003) improving the reaction conversion,
given that the products are formed and simultaneously separated and removed from the
reaction medium in two different streams (extract and raffinate). In order to provide a better
understanding of the performance of the SMBR and to validate kinetic and adsorption data it
is appropriate to evaluate first the dynamic behaviour of the fixed bed adsorptive reactor
(Gandi et al., 2006; Kawase et al., 1999; Lode et al., 2001; Mazzotti et al., 1997; Silva and
Rodrigues, 2002). The present work addresses the detailed experimental study of the ethyl
lactate synthesis in a fixed bed adsorptive reactor in order to validate the mathematical model
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 73
to be later used to define operating conditions of the SMBR. Binary adsorption experiments
were carried out on a fixed bed packed with A15 resin, in absence of reaction, at 293.15 and
323.15 K to determine the multi-component adsorption parameters.
4.2 Experimental Section
4.2.1 Chemicals and Catalyst / Adsorbent
The chemicals used in the experiments were ethanol (>99.9% in water), lactic acid (>85% in
water) and ethyl lactate (>98% in water) from Sigma-Aldrich (U.K.)
The column was packed with Amberlyst 15-wet (A15), which is a highly cross-linked
polystyrene-divinylbenzene ion exchange resin functionalized with sulfonic groups (SO3H),
that acts as catalyst and adsorbent in this system. The properties of the A15 resin are
presented in Table 4.1. A15 is a macroreticular-type resin, but according to Ihm et al. (Ihm et
al., 1988) only 4 % of the active sites are located at the macropores (surface of the
microspheres) and the others 96 % are inside gel polymer microspheres.
Table 4.1 Physical and chemical properties of resin A15.
Properties A15
Manufacturer Rohm and Haas
Concentration of acid sites (eq H+/kg) 4.7
Surface area (m2/g) 53
Average pore diameter (nm) 30
Particle diameter (mm) 0.3-1.2
This kind of resins swell selectively in the presence of a liquid phase constituted of a
multi-component mixture. The swelling is due to the sorption of the different components of
the mixture, depending on their relative affinities to the resin. The polymeric resins that
contain sulfonic acid functional groups, like the A15, exhibit a strong selectivity for polar
species. Some authors (Mazzotti et al., 1997) studied the sorption equilibrium of acetic acid,
74 CHAPTER 4. Fixed Bed Adsorptive Reactor: Experiments, Modelling and Simulation
ThermostaticBath
Reservoir
Resin
Refrigeratingwater
Three-wayvalve
Sampling line
Feed Stream
ThermostaticBath
ReservoirReservoir
Resin
Refrigeratingwater
Three-wayvalve
Sampling line
Feed Stream
ethanol, water and ethyl acetate on A15. They verified that the components can be listed by
the following decreasing order of affinity to the resin: water, ethanol, acetic acid and ethyl
acetate and that the swelling ratio is, respectively, 1.52, 1.48, 1.30 and 1.22. This conclusion
agrees with the polarity of the components. So, it is expected for the system hereby presented
that the order of decreasing affinity of the components to the resin will be: water, ethanol,
lactic acid and ethyl lactate. The swelling effect might change the length and the bulk
porosity of the fixed bed reactor; however, in the system under study, just a insignificant
variation in the bed length was noticed; and, therefore, a constant bed length was considered.
4.2.2 Experimental Apparatus
The experiments were performed in a laboratory-scale jacketed glass column that was
maintained at constant temperature through a thermostatic bath (293.15 or 323.15 K), at
atmospheric pressure (see Figure 4.1). The experimental breakthrough curves were obtained
by analysing with a gas chromatograph, small samples withdrawn at different times from the
column exit.
Figure 4.1 Experimental set-up (configuration: top-down flow direction).
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 75
4.2.2.1 Bed Porosity and Peclet Number
The bed porosity and the Peclet number were determined by pulse experiments of tracer using
a blue dextran solution (5 kg/m3), which is a polymer whose molecule is large enough
(M.W. = 2,000,000) to diffuse only in the bulk fluid phase between resin particles. Samples
of the blue dextran solution (0.2 cm3) were injected under different flow rates and the column
response was monitored using a UV-VIS detector at 300 nm. The bed porosity was calculated
from the stoichiometric time of the obtained experimental curves. An average Peclet number
was obtained for the range of flow rates to be used in the fixed bed experiments by
calculating the second moment of the experimental curves. Figure 4.2 shows the different
tracer experiments performed and the respective values of bed porosity and Peclet number are
presented in Table 4.2. The characteristics of the fixed bed column are summarized in Table
4.3.
0.00
0.20
0.40
0.60
0.80
1.00
0 4 8 12 16 20
C/C 0
Time (min)
run 1run 2run 3
Figure 4.2 Tracer experiments using a blue dextran solution. Points
are experimental values and lines are simulated curves.
Table 4.2 Results obtained from tracer experiments.
Q (mL/min) τ (min) ε σ 2 Pe
run 1 1.985 11.23 0.347 3.528 71.48
run 2 4.981 4.69 0.364 0.556 79.24
run 3 8.026 2.92 0.365 0.229 74.54
76 CHAPTER 4. Fixed Bed Adsorptive Reactor: Experiments, Modelling and Simulation
Table 4.3 Characteristics of the fixed bed column.
Solid weight (A15) 25 g
Length of the bed (L) 12 cm
Internal diameter (Di) 2.6 cm
Average radius of resin beads (rp) 372.5 μm
Bulk density (ρ b) 390 kg/m3
Bed porosity (ε) 0.36
Resin particle porosity (εp) 0.36 (Lode et al., 2001)
Peclet number 75
All the samples removed from the column exit were analysed in a gas chromatograph; the
analytical method is described in Chapter 3.
4.3 Modelling of Fixed Bed
Several mathematical models have been developed to explain the kinetic behaviour of the
fixed adsorptive reactor and to predict the breakthrough curves. In order to interpret correctly
the behaviour of a fixed bed adsorptive reactor, it is necessary to characterize on one hand the
partitioning equilibrium on the solid sorbent and on the other hand the reaction kinetics on the
solid catalyst. A rigorous modelling of the sorption in the swelling polymer should include an
appropriate model to predict the polymer-phase activities. Mazzoti and co-workers used the
extended Flory–Huggins model to determine the chemical activities of the species in the
polymer phase for the esterification of acetic acid to ethyl acetate in the presence of A15 ion
exchange resin catalyst (Mazzotti et al., 1996). They assumed, in their kinetic model, that the
activities of the species in the bulk liquid phase (estimated by UNIFAC method) were in
equilibrium with the ones in the resin polymer phase (estimated by the extended Flory–
Huggins model). However, in latter papers (Lode et al., 2001; Pöpken et al., 2000), it is
mentioned that the extended Flory–Huggins model is not well suited for high cross-linked
resins bearing highly polar groups on almost all monomer and should be regarded as an
empirical tool to correlate the equilibrium data and to predict the behaviour of
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 77
multi-component mixtures. Yu and collaborators state that using the extended Flory–Huggins
model based in adsorption equilibrium data is not viable for most adsorption systems, given
that non-reactive binary mixtures are scarce in the literature and the model involves
complexity and inconvenience in computation (Yu et al., 2004). Thus, an alternative
approach based on the multi-component Langmuir model was considered in this work, since
it is able to represent satisfactorily the experimental adsorption data and is simpler than the
Flory-Huggins model. Nevertheless, it has to be mentioned that one of the assumptions of the
Langmuir model considers that the monolayer adsorption has energetically equal binding
sites, which do not describe the actual physical adsorption phenomena. Therefore, some
authors (Pöpken et al., 2000) proposed a multi-component Langmuir adsorption isotherm
which assumes a constant monolayer capacity in terms of mass for all species, after having
measured mono-component adsorption data expressed in terms of volumes, masses and moles
of different species per gram of A15. In this work we will consider a constant volumetric
monolayer capacity for all species, which will reduce the adjustable adsorption parameters
from 8 (one molar monolayer capacity and one equilibrium constant for each component) to 5
(one volumetric monolayer capacity for all components and one equilibrium constant for each
component).
A detailed model was used to describe the dynamic behaviour of the fixed bed adsorptive
reactor taken into account the following assumptions:
- Isothermal operation;
- The flow pattern is described by axial dispersed plug flow model;
- External and internal mass transfer for absorbable species is combined in a global
resistance;
- Constant column length and packing porosity;
- Extended Langmuir Isotherm model for multi-component adsorption;
- Velocity variations due to changes in bulk composition.
The model equations are constituted by the following system of four second order partial
differential equations in the bulk concentration of the ith component ( iC ), four ordinary
differential equations in the average concentration of the ith component into the particle pores
78 CHAPTER 4. Fixed Bed Adsorptive Reactor: Experiments, Modelling and Simulation
( ,p iC ) and four algebraic equations in the adsorbed concentration in equilibrium with
,p iC ( iq ):
Bulk fluid mass balance to component i:
( ) ( ), ,(1 ) 3ii i
L i i p i ax Tp
u CC xK C C D Ct z r z z
εε
∂ ⎛ ⎞∂ ∂− ∂+ + − = ⎜ ⎟∂ ∂ ∂ ∂⎝ ⎠
(4.1)
where iLK , is the global mass transfer coefficient of the component i, ε is the bed porosity, t
is the time variable, z is the axial coordinate, axD and u are the axial dispersion coefficient
and the interstitial velocity respectively, pr is the particle radius and xi is the component
molar fraction in liquid phase.
The axial dispersion coefficient axD was calculated from the Peclet number:
ax
u LPeD
= (4.2)
The interstitial fluid velocity variation is calculated using the total mass balance:
( ) ( ),, ,1
1 3 NC
p iL i mol i iip
du K V C Cdz r
εε =
−= − −∑ (4.3)
where Vmol,i is the molar volume of component i .
Pellet mass balance to component i:
( ) ( )ipbii
pip
pipiiLp
Crt
qt
CCCK
r ,,
,, 1)1(3
ερν
εε−
−∂
∂−+
∂
∂=− (4.4)
Where iν is the stoichiometric coefficient of component i , bρ is the bulk density, pε is the
particle porosity, iq is the average adsorbed phase concentration of species i in equilibrium
with ipC , , and r is the kinetic rate of the chemical reaction relative to the average particle
concentrations in the fluid phase given by (see Chapter 3):
2
,1
1
Eth La EL W eqc NC
s i ii
a a a a Kr k
K a=
−=
⎛ ⎞+⎜ ⎟
⎝ ⎠∑
(4.5)
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 79
where kc is the kinetic constant, isK , is the adsorption constant for species i and Keq is the
equilibrium reaction constant, a is the species activity (calculated by UNIQUAC model) and
the subscripts WELLaEth and , , refer to ethanol, lactic acid, ethyl lactate and water,
respectively. Kinetic and thermodynamic parameters, essential for the Equation 4.5, were
taken from Chapter 3 and are given in Table 4.4.
Table 4.4 Kinetic and thermodynamic parameters.
Langmuir Adsorption equilibrium isotherm to component i:
,
,1
1
p ii ii NC
p jjj
Q K CqK C
=
=+∑
(4.6)
where ,/i V mol iQ Q V= , QV is the volumetric monolayer capacity, ,mol iV is the molar volume of
species i and iK is the equilibrium constant for component i.
Initial and Danckwerts boundary conditions:
0,,0 iipi CCCt === (4.7)
,0
0 ii ax T i F
z
xz u C D C u Cz
=
∂= − =
∂ (4.8a)
0u u= (4.8b)
0=∂
∂=
=Lz
i
zC
Lz (4.9)
where subscripts F and 0 refer to the feed and initial states, respectively.
The proposed model considers a global mass transfer coefficient ( LK ) defined, for each
component, as:
ipeL kkK ε111
+= (4.10)
Temperature (K)
kc (mol/(g.min)) Ks,w Ks,Eth Keq
293.15 0.035 15.82 4.16 3.34
323.15 0.225 15.77 3.71 3.93
80 CHAPTER 4. Fixed Bed Adsorptive Reactor: Experiments, Modelling and Simulation
wherein ek and ik are, respectively, the external and internal mass transfer coefficients.
Santacesaria and co-workers (Santacesaria et al., 1982) showed that the internal mass
transfer coefficient varies in time, and the calculation of the rigorous values requires the
solution of the complete model equations inside particles. As an approximation, the mean
value estimated by the Equation 4.11 (Glueckauf, 1955) was used:
5 /mi
p
Dkr
τ= (4.11)
The external mass transfer coefficient was estimated by the Wilson and Geankoplis
correlation (Ruthven, 1984):
( ) 550015.009.1 33.0 <<= ppp ReScReShε
(4.12)
where pSh and pRe are, respectively, the Sherwood and Reynolds numbers, relative to
particle:
m
pep D
dkSh = (4.13)
pp
d uRe
ρη
= (4.14)
and Sc is the Schmidt number:
m
ScD
ηρ
= (4.15)
The infinite dilution diffusivities were estimated by the Scheibel correlation (Scheibel, 1954)
which modified the Wilke-Chang equation in order to eliminate the association factor:
2/38
,0 2, 1/3
, ,
38.2 10( / ) 1 mol BA B
B mol A mol A
VTD cm sV Vη
− ⎡ ⎤⎛ ⎞× ⎢ ⎥= + ⎜ ⎟⎜ ⎟⎢ ⎥⎝ ⎠⎣ ⎦ (4.16)
where 0,A BD is the diffusion coefficient for a dilute solute A into a solvent B, T is the
temperature, ,mol iV is the molar volume of the component i, Bη is the viscosity of solvent B.
Table 4.5 shows the diffusion coefficients for all binary systems:
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 81
Table 4.5 Diffusion coefficients for the binary mixtures estimated using the Scheibel correlation (equation 4.16).
Di,jº (cm2/s) Ethanol Lactic acid Ethyl lactate Water
Ethanol 0 1.6796E-06 2.583E-05 2.3655E-05
Lactic acid 2.5056E-05 0 2.1087E-05 2.0236E-05
Ethyl lactate 1.8034E-05 9.8526E-07 0 1.5444E-05
Water 8.2195E-05 4.6733E-06 7.4567E-05 0
For binary systems, Vignes equation (Vignes, 1966) was used to predict ,A BD in
concentrated solutions from the infinite dilute coefficients as a simple function of
composition:
2 10 02,1 1,2 1,2 2,1( ) ( )x xD D D D= = (4.17)
For concentrated multi-component systems there are several mixing rules (Umesi and
Danner, 1981) to predict the molecular diffusivity coefficient of a solute in a mixture. In this
work it was used the Perkins and Geankoplis method (Perkins and Geankoplis, 1969):
0.8 0 0.8, ,
1#
n
A m m i A i iii A
D x Dη η=
= ∑ (4.18)
where iη is the viscosity of pure component i and mη is the viscosity of the mixture. The
viscosities of the mixtures play an important role in the estimation of the diffusion coefficient.
The methods used to predict binary and multi-component mixtures viscosities are detailed in
the next sub-section.
In this model, the mixture viscosity and the components diffusivities in the liquid mixture
were calculated at each time and at every axial position; therefore, the mass transfer
parameters also depend on the liquid composition (estimated at each time and axial position
from the equations presented).
4.3.1 Multi-component viscosity
One of the most used and recommended liquid mixture viscosity correlation is the one by
Grunberg–Nissan (Grunberg and Nissan, 1949), which for binary mixtures is:
82 CHAPTER 4. Fixed Bed Adsorptive Reactor: Experiments, Modelling and Simulation
1 1 2 2 1 2 1,2ln( ) ln( ) ln( )m x x x x Gη η η= + + (4.19)
where ix is the mole fraction of component i and 1,2G is an empirical interaction parameter
adjusted by experimental data.
For aqueous lactic acid solutions, the interaction parameters were found to be
, (20º ) 5.240LA WG C = and , (50º ) 4.369LA WG C = using viscosities determined experimentally
presented in literature (Troupe et al., 1951). As can be seen in Figure 4.3, the Equation 4.19
describes well the viscosity in a large range, from diluted solutions till concentrated lactic
acid (85% mass fraction).
0
5
10
15
20
25
30
35
40
0.0 0.2 0.4 0.6
Visc
osity
(cP)
Mole fraction of lactic acid
Exp. 20 ºC (Troupe et al, 1951)Exp. 50 ºC (Troupe et al,1951)Theoretical (Eq. 4.19)
Figure 4.3 Viscosities of aqueous lactic acid solutions.
For the system water ethanol, experimental data at 20 ºC (Gonzalez et al., 2007) and 50 ºC
(Motin et al., 2005) are not well fitted by Equation 4.19 ( , (20º ) 2.568Eth WG C = and
, (50º ) 1.799Eth WG C = ), as it can be seen in Figure 4.4. It was stated by several authors, that
the Grunberg–Nissan correlation is not suitable for several aqueous system (Li and Carr,
1997; Macias-Salinas et al., 2003). Normally, the correlation used to describe the viscosity of
those systems involves at least 3 adjustable parameters (Gonzalez et al., 2007; Motin et al.,
2005). We propose a new correlation with just one adjustable parameter similar to that of
Grunberg–Nissan, but the excess viscosity function is averaged by the volume fractions
instead of molar ones:
1 1 2 2 1 2 1,2ln( ) ln( ) ln( )m x x Gη η η φ φ= + + (4.20)
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 83
where ix is the mole fraction of component i , iφ is the volume fraction of component i and
1,2G is an empirical interaction parameter adjusted by experimental data. Using the new
interaction parameters in Equation 4.20 ( , (20º ) 3.833Eth WG C = and , (50º ) 2.698Eth WG C = ), the
ethanol/water system viscosities are very well predicted, as it can be seen in Figure 4.5.
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
0.0 0.2 0.4 0.6 0.8 1.0
Visc
osity
(cP
)
Mole fraction of ethanol
Exp. 20 ºC (Gonzalez et al, 2007)Exp. 50 ºC (Motin et al, 2005)Theoretical (Eq. 4.19)
Figure 4.4 Viscosities of ethanol/water mixtures. Solid line calculated by Equation 4.19.
0.0
0.5
1.0
1.5
2.0
2.5
3.0
3.5
0.0 0.2 0.4 0.6 0.8 1.0
Visc
osity
(cP)
Mole fraction of ethanol
Exp. 20 ºC (Gonzalez et al, 2007)
Exp. 50 ºC (Motin et al, 2005)
Theoretical (Eq. 4.20)
Figure 4.5 Viscosities of ethanol/water mixtures. Solid line calculated by Equation 4.20.
Since there are no experimental data available for the systems ethanol/ethyl lactate and
ethanol/lactic acid, these systems are considered as ideal, i.e., , 0Eth ELG = and , 0Eth LAG = .
84 CHAPTER 4. Fixed Bed Adsorptive Reactor: Experiments, Modelling and Simulation
The liquid viscosity of the multi-component system ethanol, lactic acid, ethyl lactate and
water is calculated by the following model:
, ,ln( ) ln( ) ln( ) ln( ) ln( )m Eth Eth LA LA EL EL W W LA W LA W Eth W Eth Wx x x x x x G Gη η η η η φ φ= + + + + + (4.21)
The viscosities of pure components at 20 and 50ºC are presented in Table 4.6 (see appendix B
for details in calculation).
Table 4.6 Viscosities (cP) of ethanol, lactic acid, ethyl lactate and water at 20ºC and 50ºC.
Temperature Ethanol Lactic acid Ethyl lactate Water
20 ºC 1.1617 53.6564 2.5986 1.0254
50 ºC 0.6885 13.9919 1.1233 0.5530
Numerical Solution
The model equations were solved numerically using the gPROMS-general PROcess
Modelling System version: 3.0.3 (www.psentreprise.com). gPROMS is a software package
for modelling and simulation of processes with both discrete and continuous as well as
lumped and distributed characteristics. The mathematical model involves a system of partial
and algebraic equations (PDAEs). Third order orthogonal collocation over twenty one finite
elements was used in the discretization of axial domain. The system of ordinary differential
and algebraic equation (ODAEs) was integrated over time using the DASOLV integrator
implementation in gPROMS. For all simulations was fixed a tolerance equal to 10-7.
4.4 Results and Discussion
4.4.1 Adsorption Isotherm
As the resin A15 acts simultaneously as adsorbent and as catalyst, in order to have
information on the adsorptive equilibrium alone it is necessary to perform experiments with
non reactive binary mixtures. So, the breakthrough curves of ethanol, lactic acid, ethyl lactate
and water were measured in the absence of reaction. The resin was saturated with a certain
component A and then the feed concentration of component B was changed stepwise. The
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 85
experimental data were used to calculate the number of moles adsorbed/desorbed of each
component for all the experiments. The adsorption parameters were optimized by minimizing
the difference between experimental and theoretical values, according to Equation 4.26:
[ ]∫∞
−=0exp )( dttCCQn outF
ads (4.22)
[ ]∫∞
−=0exp )( dtCtCQn Fout
des (4.23)
[ ]( ) [ ]( )VCqCqCCn FpFpadstheo )()()1()1()1( 00 −−−+−−+= εεεεε (4.24)
[ ]( ) [ ]( )VCqCqCCn FpFpdestheo )()()1()1()1( 00 −−−+−−+= εεεεε (4.25)
( ) ( )2 2
exp exp1
NEads ads des des
theo theok
fob n n n n=
⎡ ⎤= − + −⎢ ⎥⎣ ⎦∑ (4.26)
4.4.1.1 Binary Adsorption experiments
As mentioned above, for the determination of the adsorption parameters over the A15 resin it
was necessary to perform experiments with non reactive pairs of species. The possible binary
mixtures to run the breakthrough experiments in absence of reaction are ethanol / water, ethyl
lactate / ethanol and lactic acid / water. In all the experiments, the correct liquid flow
direction (bottom-up or top-down) was considered in order to obtain reproducibility in the
experimental results, since the hydrodynamic regime has an important effect on them and the
difference in densities of the species can lead to axial backmixing driven by natural
convection. The densities of ethanol, lactic acid, ethyl lactate and water at 293.15 K are
0.79 g/cm3, 1.21 g/cm3, 1.04 g/cm3 and 1 g/cm3, respectively. The concentration fronts moving
within the column are hydrodynamically stable if the component above the front is less dense
than the component below the front (Silva and Rodrigues, 2002). The multi-component
adsorption equilibrium was measured at two different temperatures, 293.15 K and 323.15 K.
In Table 4.7 the optimized adsorption parameters and the molar volumes at the two
temperatures are presented.
86 CHAPTER 4. Fixed Bed Adsorptive Reactor: Experiments, Modelling and Simulation
Table 4.7 Adsorption parameters over A15 resin.
Component QV (ml/lwet solid) 20 ºC / 50 ºC
Q (mol/lwet solid) 20 ºC / 50 ºC
K (l/mol) 20 ºC / 50 ºC
Vmol (ml/mol) 20 ºC / 50 ºC
Ethanol 6.70 / 6.30 5.443 / 3.068 58.17 / 60.87
Lactic acid 5.22 / 4.94 4.524 / 4.085 74.64 / 77.56
Ethyl lactate 3.42 / 3.23 1.117 / 1.815 113.99 / 118.44
Water
390.0/383.5
21.57 / 20.58 15.353 / 7.055 18.08 / 18.63
In order to compare the selectivity of the resin to the components, two different experiments
were performed. One, where ethanol is fed to the column initially saturated with water, and
other, where ethanol is fed to the column initially saturated with ethyl lactate (see Figure 4.6).
In the first case (Figure 4.6a) the concentration front of ethanol has a dispersive character and
in the second one (Figure 4.6b) the ethanol concentration front is self-sharpening. This is due
to the fact that water is the preferentially adsorbed component and ethyl lactate is the weakest
adsorbed component.
02468
1012141618
0 10 20 30 40
Out
let c
once
ntra
tion
(mol
L)
Time (min)
Ethanol
Theoretical
02468
1012141618
0 10 20 30 40
Out
let c
once
ntra
tion
(mol
/L)
Time (min)
Ethanol
Theoretical
Figure 4.6 Breakthrough experiments: outlet concentration of ethanol as a function of
time; Q = 5 mL/min; T = 293.15 K; top-down direction flow; ( a) ethanol displacing water; (b) ethanol displacing ethyl lactate.
The breakthrough curves of the four components at 323.15 K are presented next in this
section, while the remaining breakthrough curves at 293.15 K used for the determination of
the adsorption parameters are shown in appendix D.
(a) (b)
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 87
0
10
20
30
40
50
60
0 50 100 150 200 250 300 350
Out
let c
once
ntra
tion
(mol
/L)
Time (min)
WaterEthanolTheoretical
0
10
20
30
40
50
60
0 20 40 60 80 100 120 140 160
Out
let c
once
ntra
tion
(mol
/L)
Time (min)
WaterEthanolTheoretical
Figure 4.7 Breakthrough experiments: outlet concentration of ethanol and water as a
function of time; Q = 5 mL/min; T = 323.15 K; (a) water displacing ethanol; Bottom up flow direction; (b) ethanol displacing water; Top-down flow direction.
The experimental and theoretical concentration history for the binary mixture ethanol / water
is shown in Figure 4.7. Comparing the experimental amount of water adsorbed in the
experiment of Figure 4.7a with the experimental amount of water desorbed in the experiment
of Figure 4.7b, the error obtained is 0.3 %. For ethanol, the error between the amount
adsorbed, Figure 4.7b, and the amount eluted, Figure 4.7a, is 0.31 %. The deviations found
between the experimental amount adsorbed of water and the one predicted by the model is of
4 %, while in the case of ethanol the difference between experimental amount adsorbed and
predicted is of 0.6 %.
(a)
(b)
88 CHAPTER 4. Fixed Bed Adsorptive Reactor: Experiments, Modelling and Simulation
0
2
4
6
8
10
12
14
16
18
0 40 80 120 160 200
Out
let c
once
ntra
tion
(mol
/L)
Time (min)
Ethyl lactateEthanolTheoretical
0
2
4
6
8
10
12
14
16
18
0 20 40 60 80 100
Out
let c
once
ntra
tion
(mol
/L)
Time (min)
Ethyl lactate
Ethanol
Theoretical
Figure 4.8 Breakthrough experiments: outlet concentration of ethanol and ethyl lactate
as a function of time; Q = 5 mL/min; T = 323.15 K; (a) ethyl lactate displacing ethanol; Bottom up flow direction (b) ethanol displacing ethyl lactate; Top-down flow direction.
The experimental and simulated results for the non reactive binary mixture ethanol / ethyl
lactate are shown in Figure 4.8. The difference obtained between the experimental amount of
ethyl lactate eluted in the experiment of Figure 4.8b, and the experimental amount of ethyl
lactate adsorbed in the experiment of Figure 4.8a, was 0.21 %. In the case of ethanol, the
error obtained between the experimental amount adsorbed, Figure 4.8b, and the experimental
amount eluted, Figure 4.8a, was 4.22 %.
For the non reactive pair lactic acid / water (Figure 4.9) the deviation found between the
experimental amount of lactic acid eluted (Figure 4.9b) and adsorbed (Figure 4.9a) was
0.45 % and between the experimental amount of water adsorbed (Figure 4.9b) and eluted
(Figure 4.9a) was -1.07 %.
(a)
(b)
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 89
0
10
20
30
40
50
60
0 40 80 120 160
Out
let c
once
ntra
tion
(mo/
L)
Time (min)
WaterLactic acidTheoretical
0
10
20
30
40
50
60
0 10 20 30 40 50 60
Out
let c
once
ntra
tion
(mol
/L)
Time (min)
Water
Lactic acid
Theoretical
Figure 4.9 Breakthrough experiments: outlet concentration of water and lactic acid as
a function of time; Q = 5 mL/min; T = 323.15 K; (a) lactic acid displacing water; Bottom up flow direction (b) water displacing lactic acid; Top-down flow direction.
All the binary adsorption experiments performed are very well described by the model,
except for the case of the experiment of Figure 4.9b, where pure water displaces an 86 wt %
lactic acid solution. This could be explained by the water/lactic acid high selectivity in A15
(about 7.2); however, this behaviour was not observed in the binary experiments
ethanol/water where the selectivity is very similar (about 7.5). Therefore, that behaviour
might be due to viscous fingering phenomenon, since the highest viscous fluid (85% lactic
acid solution: 9.40 cP at 323.15 K), is being displaced by the lowest viscous fluid (water:
0.55 cP at 323.15 K), in the top-down direction, inducing an unstable interface between them.
(b)
(a)
90 CHAPTER 4. Fixed Bed Adsorptive Reactor: Experiments, Modelling and Simulation
The difference in their viscosities is of about 9 cP and in this case fingering effects are
significant (Catchpoole et al., 2006). Viscous fingering is not accounted in the global mass
transfer coefficient (Equation 4.10). In order to verify this assumption, the effect of viscous
fingering can be described increasing the axial dispersion (Mallmann et al., 1998). Indeed, the
theoretical curve using an axial dispersion coefficient increased by a factor of 7 (thin line in
Figure 4.9b) fits the experimental data very well.
From the data reported it can be concluded that the most adsorbed component in A15 is water
followed by ethanol and lactic acid, being the less adsorbed the ethyl lactate, as expected due
to the polarity of the species.
4.4.2 Kinetic experiments
4.4.2.1 Fixed Bed Reactor
A reaction experiment was performed in the chromatographic reactor packed with A15
initially saturated with ethanol, at 20ºC. As shown in Figure 4.10, the lactic acid conversion is
very low due to both mass transfer and reaction kinetics limitations. Therefore, the fixed bed
reactor was operated at 50ºC in order to reduce mass transfer resistance and to increase
reaction kinetics.
0
2
4
6
8
10
12
14
16
18
0 10 20 30 40 50 60
Out
let c
once
ntra
tion
(mol
/L)
Time (min)
EthanolWaterEthyl lactateLactic acidTheoretical
Figure 4.10 Concentration histories at the outlet of the fixed bed adsorptive reactor;
column initially saturated with ethanol and then fed with a mixture of ethanol and lactic acid solution: 4.6 / minQ mL= , 293.15T K= ,
, 6.76 /La FC mol L= , , 6.76 /Eth FC mol L= and , 5.45 /W FC mol L= .
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 91
A mixture of ethanol and lactic acid was fed to the reactor saturated with ethanol and the
concentration history of ethanol, lactic acid, ethyl lactate and water at the end of the column
is shown in Figure 4.11a.
0
2
4
6
8
10
12
14
16
18
0 20 40 60 80 100 120 140
Out
let c
once
ntra
tion
(mol
/L)
Time (min)
EthanolWaterEthyl lactateLactic acidTheoretical
0
2
4
6
8
10
12
14
16
18
0 10 20 30 40 50 60 70
Out
let c
once
ntra
tion
(mol
/L)
Time (min)
EthanolWaterEthyl lactateLactic acidTheoretical
Figure 4.11 Concentration histories at the outlet of the fixed bed adsorptive reactor for
production steps. a) Experiment 1: Column initially saturated with ethanol and then fed with a mixture of ethanol and lactic acid solution.
1.0 / minQ mL= , 323.15T K= , , 5.88 /La FC mol L= , , 6.60 /Eth FC mol L= and , 5.87 /W FC mol L= . b) Experiment 2: Column initially saturated with ethanol and then fed with lactic acid solution (86 wt % in water). 1.3 / minQ mL= , 323.15T K= .
(a)
(b)
92 CHAPTER 4. Fixed Bed Adsorptive Reactor: Experiments, Modelling and Simulation
As the lactic acid solution enters the column it is adsorbed, reacts with ethanol to produce
ethyl lactate and water in the stoichiometric amount. Ethyl lactate is first eluted, since it has
less affinity with the resin than water. This process continues until the equilibrium is reached;
the resin is completely saturated with water and lactic acid. At this moment the selective
separation of ethyl lactate and water is no longer possible. The local compositions remain
constant and the steady state is achieved being the outlet stream constituted by a reactive
mixture at the equilibrium composition. Analysing the outlet concentration curves of ethyl
lactate and water, shown in Figure 4.11a, a difference between them is noticed although they
are formed at the same stoichiometric amount. This is related to the difference in the adsorbed
amount of these species in the resin and, mainly, due to the fact that in the feed there is
already some water content due to the lactic acid solution.
A second experiment was performed by only feeding the lactic acid solution (86 wt % in
water) to the fixed bed adsorptive reactor (see Figure 4.11b), in order to validate the model
under very different conditions. Similarly to the previous experiment, as the lactic acid and
water enter the column, they are adsorbed and start displacing the initially adsorbed ethanol.
Simultaneously, the lactic acid reacts with ethanol in the resin phase until complete depletion
of adsorbed ethanol and the formed ethyl lactate is adsorbed, forming a dispersive front with
ethanol once this is more adsorbed than ethyl lactate. The adsorption of lactic acid solution
continues till the resin saturation, displacing the ethyl lactate. Finally, lactic acid and water
exit the column, being water the last eluted component due to high affinity of A15 towards
this specie.
After the steady state is achieved and to perform a new reaction experiment it is necessary to
first regenerate the column. This step requires the use of a solvent to displace the adsorbed
species. The solvent used was ethanol, since lactic acid solution could not be used, because it
contains water and then the column wouldn’t be completely regenerated. In Figure 4.12, the
regeneration steps for each experiment are presented. As expected, ethyl lactate and lactic
acid are rapidly desorbed; however, a large amount of ethanol is required in order to
completely desorb all water.
Al the experimental results obtained for both production and regeneration steps, at 293.15 and
323.15 K, are well described by the proposed mathematical model.
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 93
0
2
4
6
8
10
12
14
16
18
0 10 20 30 40 50 60
Out
let c
once
ntra
tion
(mol
/L)
Time (min)
EthanolWaterEthyl lactateLactic acidTheoretical
0
2
4
6
8
10
12
14
16
18
0 10 20 30 40
Out
let c
once
ntra
tion
(mol
/L)
Time (min)
EthanolWaterEthyl lactateLactic acidTheoretical
Figure 4.12 Concentration histories at the outlet of the fixed bed adsorptive reactor
for regeneration steps with ethanol ( 4.3 / minQ mL= , 323.15T K= ). a) Experiment 1. b) Experiment 2.
(a)
(b)
94 CHAPTER 4. Fixed Bed Adsorptive Reactor: Experiments, Modelling and Simulation
4.5 Conclusions
A detailed study of the ethyl lactate synthesis in a fixed bed adsorptive reactor was carried
out. Adsorption experiments in absence of reaction at 20ºC and 50ºC were performed. For
each temperature, the adsorption parameters were obtained: a single volumetric monolayer
capacity for all components and one equilibrium constant for each component. A
mathematical model for the fixed bed adsorptive reactor was developed which includes: axial
dispersion, external and internal mass transfer resistances, multi-component Langmuir
adsorption isotherm, the reaction rate measured in a previous work and velocity variations
due to mixture molar volume variations. This model proved to be efficient in the prediction of
the reaction and regeneration steps performed in the fixed bed reactor and it will be very
useful for the study of the SMBR for the synthesis of ethyl lactate.
4.6 Notation
a liquid phase activity
C liquid phase concentration (mol/m3)
TC total liquid phase concentration (mol/m3)
pC average liquid phase concentration inside the particle (mol/m3)
df film thickness (µm)
pd particle diameter (m)
0,A BD diffusion coefficient for a dilute solute A into a solvent B (m2/s)
,A BD mutual diffusion coefficient for binary concentrated solutions (m2/s)
axD axial dispersion (m2/s)
mD molecular diffusivity (m2/s)
1,2G interaction parameter in Equation 4.19
K Langmuir equilibrium parameter (m3/mol)
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 95
ik internal mass transfer coefficient (m/s)
ek external mass transfer coefficient (m/s)
ck kinetic constant (mol/kgres.s)
eqK equilibrium constant
SK adsorption constant in Equation 4.5.
LK global mass transfer coefficient (m/s)
L bed length (m)
n number of moles (mol)
Pe Peclet number
q average solid phase concentration in equilibrium with pC (mol/m3res)
Q molar adsorption capacity, defined as ,/i V mol iQ Q V= (mol/m3res)
QV volumetric monolayer capacity (m3/m3res)
r reaction rate relative to fluid concentration inside the particle (mol/kgres.s)
pr particle radius (m)
pRe Reynolds number relative to particle
pSh Sherwood number relative to particle
Sc Schmidt number
T temperature (K)
t time (s)
t* switching time (min)
u interstitial velocity (m/s)
molV molar volume in the liquid phase (m3/mol)
V volume of the bulk (m3)
x liquid phase molar fraction
96 CHAPTER 4. Fixed Bed Adsorptive Reactor: Experiments, Modelling and Simulation
z axial coordinate (m)
Greek letters
ε bulk porosity
pε porosity of pellet
η fluid viscosity (kg/m.s)
mη mixture viscosity (kg/m.s)
φ volume fraction
ν stoichiometric coefficient
ρ liquid density (kg/m3)
bρ bulk density (kgres/m3)
τ tortuosity
Subscripts
0 relative to initial conditions
exp experimental
F relative to the feed
i relative to component i (i= Eth, La, EL, W)
out at the end of the fixed bed column
p relative to particle
theor theoretical
Eth relative to ethanol
La relative to lactic acid
EL relative to ethyl lactate
W relative to water
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 97
Superscripts
ads adsorbed
des desorbed
4.7 References
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Catchpoole H. J., R. Andrew Shalliker, G. R. Dennis and G. Guiochon, "Visualising the onset of viscous fingering in chromatography columns", J Chrom A 1117(2): 137-145, 2006.
Funk G. A., J. R. Lansbarkis and A. K. Chandhok, "Process for concurrent esterification and separation using a simulated moving bed", Patent 5,405,992 (1995).
Gandi G. K., V. M. T. M. Silva and A. E. Rodrigues, "Synthesis of 1,1-dimethoxyethane in a fixed bed adsorptive reactor", Ind Eng Chem Res. 45(6): 2032-2039, 2006.
Glueckauf E., "Theory of chromatography", Trans. Faraday Soc 51: 1540-1551 1955.
Gonzalez B., N. Calvar, E. Gomez and A. Dominguez, "Density, dynamic viscosity, and derived properties of binary mixtures of methanol or ethanol with water, ethyl acetate, and methyl acetate at T = (293.15, 298.15, and 303.15) K", J. Chem. Thermodyn. 39(12): 1578-1588, 2007.
Grunberg L. and A. H. Nissan, "Mixture law for viscosity", Nature 164(4175): 799-800, 1949.
Ihm S. K., M. J. Chung and K. Y. Park, "Activity difference between the internal and external sulfonic groups of macroreticular ion-exchange resin catalysts in isobutylene hydration", Ind Eng Chem Res. 27(1): 41-45, 1988.
Kawase M., Y. Inoue, T. Araki and K. Hashimoto, "The simulated moving-bed reactor for production of bisphenol A", Catal Today 48(1-4): 199-209, 1999.
Kawase M., T. B. Suzuki, K. Inoue, K. Yoshimoto and K. Hashimoto, "Increased esterification conversion by application of the simulated moving-bed reactor", Chem Eng Sci. 51(11): 2971-2976, 1996.
Li J. and P. W. Carr, "Accuracy of Empirical Correlations for Estimating Diffusion Coefficients in Aqueous Organic Mixtures", Anal. Chem. 69(13): 2530-2536, 1997.
Lode F., G. Francesconi, M. Mazzotti and M. Morbidelli, "Synthesis of methylacetate in a simulated moving-bed reactor: Experiments and modeling", AIChE J. 49(6): 1516-1524, 2003.
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Lode F., M. Houmard, C. Migliorini, M. Mazzotti and M. Morbidelli, "Continuous reactive chromatography", Chem Eng Sci. 56(2): 269-291, 2001.
Macias-Salinas R., F. Garcia-Sanchez and G. Eliosa-Jimenez, "An equation-of-state-based viscosity model for non-ideal liquid mixtures", Fluid Phase Equilib. 210(2): 319-334, 2003.
Mallmann T., B. D. Burris, Z. Ma and N. H. L. Wang, "Standing wave design of nonlinear SMB systems for fructose purification", AlChE J. 44(12): 2628-2646, 1998.
Mazzotti M., A. Kruglov, B. Neri, D. Gelosa and M. Morbidelli, "A continuous chromatographic reactor: SMBR", Chem Eng Sci. 51(10): 1827-1836, 1996.
Mazzotti M., B. Neri, D. Gelosa and M. Morbidelli, "Dynamics of a Chromatographic Reactor: Esterification Catalyzed by Acidic Resins", Ind Eng Chem Res. 36(8): 3163-3172, 1997.
Minceva M., P. S. Gomes, V. Meshko and A. E. Rodrigues, "Simulated moving bed reactor for isomerization and separation of p-xylene", Chem Eng J. 140(1-3): 305-323, 2008.
Motin M. A., M. H. Kabir and M. E. Huque, "Viscosities and excess viscosities of methanol, ethanol and n-propanol in pure water and in water + surf excel solutions at different temperatures", Phys. Chem. Liq. 43(2): 123-137, 2005.
Pereira C. S. M., P. S. Gomes, G. K. Gandi, V. M. T. M. Silva and A. E. Rodrigues, "Multifunctional Reactor for the Synthesis of Dimethylacetal", Ind Eng Chem Res. 47(10): 3515-3524, 2008.
Perkins L. R. and C. J. Geankoplis, "Molecular diffusion in a ternary liquid system with the diffusing component dilute", Chem. Eng. Sci. 24(7): 1035-1042, 1969.
Pöpken T., L. Götze and J. Gmehling, "Reaction kinetics and chemical equilibrium of homogeneously and heterogeneously catalyzed acetic acid esterification with methanol and methyl acetate hydrolysis", Ind Eng Chem Res. 39(7): 2601-2611, 2000.
Ruggieri R., G. Ranghino, G. Carvoli, A. Tricella, D. Gelosa and M. Morbidelli, "Process for esterification in a chromatographic reactor", Patent 6,586,609 (2003).
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Santacesaria E., M. Morbidelli, A. Servida, G. Storti and S. Carra, "Separation of xylenes on Y zeolites. 2. Breakthrough curves and their interpretation", Ind Eng Chem Process Des Dev 21(3): 446-451, 1982.
Scheibel E. G., "Correspondence. Liquid Diffusivities. Viscosity of Gases", Ind Eng Chem 46(9): 2007-2008, 1954.
Silva V. M. T. M. and A. E. Rodrigues, "Dynamics of a fixed-bed adsorptive reactor for synthesis of diethylacetal", AIChE J. 48(3): 625-634, 2002.
Silva V. M. T. M. and A. E. Rodrigues, "Novel process for diethylacetal synthesis", AIChE J. 51(10): 2752-2768, 2005.
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 99
Troupe R. A., W. L. Aspy and P. R. Schrodt, "Viscosity and Density of Aqueous Lactic Acid Solutions", Ind Eng Chem 43(5): 1143-1146, 1951.
Umesi N. O. and R. P. Danner, "Predicting diffusion coefficients in nonpolar solvents", Ind Eng Chem Proc DD 20(4): 662-665, 1981.
Vignes A., "Diffusion in binary solutions: Variation of diffusion coefficient with composition", Ind. Eng. Chem. Fundam. 5(2): 189-199, 1966.
Yu W., K. Hidajat and A. K. Ray, "Modeling, Simulation, and Experimental Study of a Simulated Moving Bed Reactor for the Synthesis of Methyl Acetate Ester", Ind Eng Chem Res. 42(26): 6743-6754, 2003.
Yu W., K. Hidajat and A. K. Ray, "Determination of adsorption and kinetic parameters for methyl acetate esterification and hydrolysis reaction catalyzed by Amberlyst 15", Appl Catal A: Gen. 260(2): 191-205, 2004.
Zhang Y., L. Ma and J. Yang, "Kinetics of esterification of lactic acid with ethanol catalyzed by cation-exchange resins", React Funct Polym 61(1): 101-114, 2004.
5. Simulated Moving Bed Reactor
Abstract. A novel approach for the synthesis of ethyl lactate using a simulated moving bed
reactor was evaluated by experiments as well as by simulations. A mathematical model
considering external and internal mass-transfer resistances and variable velocity due to
change of liquid composition was developed to describe the dynamic behaviour of the SMBR
and it was validated by the experiments performed; it was observed that the experimental
results were well predicted by the model. The effect of operating parameters, as the feed
composition, SMBR configuration and switching time on the SMBR performance parameters
at the optimal operating points and/or reactive/separation regions was studied. It was shown
that the SMBR is a very attractive technology for the production of ethyl lactate, since under
appropriate conditions the lactic acid conversion can be driven to completion and productivity
as high as 32 kgEL/(Lads.day) and purity of 95 % can be obtained.
Adapted from: Pereira C. S. M., M. Zabka, V. M. T. M. Silva and A. E. Rodrigues, "A novel process for the
ethyl lactate synthesis in a simulated moving bed reactor (SMBR)", Chem. Eng. Sci. 64(14): 3301-3310, 2009.
102 CHAPTER 5. Simulated Moving Bed Reactor
5.1 Introduction
Esterification and transesterification (Ferreira and Loureiro, 2004; Ma et al., 2008; Pereira et
al., 2008b; Schmid et al., 2008; Yadav and Devi, 2004), acetalization (Chopade and Sharma,
1997; Gandi et al., 2005; Silva and Rodrigues, 2001; Yadav and Pujari, 1999), and
etherification (Cruz et al., 2005; Yadav and Lande, 2005) reactions, that are limited by the
thermodynamic equilibrium should be performed using hybrid technologies where reaction
and separation take place in a single unit, like chromatographic reactors or membrane
reactors, given that the reaction yield will be increased by removing one or more products.
Moreover, the use of this kind of technologies allows cost reduction and higher product
purity. In order to improve the process the use of solid acid catalysts is preferable. Since they
are less corrosive and, in opposition to homogeneous ones, they not require a further step of
separation and neutralization. Among the solid acid catalysts, ion exchange resins, like
Amberlyst 15-wet (A15), offer to the ethyl lactate production the advantage of having a
double role, they act as catalyst and as selective adsorber between the two reaction products,
water and ethyl lactate. Therefore, the use of the Amberlyst 15-wet resin in a
chromatographic reactor to produce ethyl lactate seems to be interest. The principle of the
chromatography batch reactor has been developed by Dinwiddie and Morgan in the beginning
of the 1960s (Dinwiddie and Morgan, 1961). The reactant is injected as a sharp pulse into a
fixed-bed column; during its propagation along the column it reacts and leads to different
products. The different affinity of the components with the solid phase leads to different
propagation velocities and, because of that, it is possible to separate the products from the
reaction mixture. For equilibrium limited reactions where complete separation of the products
is achieved the conversion can overcome the thermodynamic equilibrium value. However, the
batch chromatographic reactor is not the best technology to overcome that limitation, since it
has the usual drawbacks of a batch operation, where high quantity of eluent is needed to
perform the separation, resulting in highly diluted products. These led to the development of
continuous chromatographic reactors in order to decrease the solvent consumption and to
enhance the productivity, where the continuous mode of operation can be achieved by
moving the adsorbent or simulating its motion. However, the flow of solid particles in the
columns leads to some difficulties such as particle attrition, fluid velocity limited by
fluidization phenomena, considerable pressure drops, lack of efficiency, that are overcome by
the simulated moving bed (SMB) technology (Broughton and Gerhold, 1961), in which the
counter-current movement of the solid is simulated by using a series of packed beds where
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 103
the inlet/outlet ports are synchronously shifted in direction of the liquid flow. The extension
of the SMB technology to integrate reaction and separation steps into a single apparatus led to
the Simulated Moving Bed Reactor (SMBR). This chromatographic reactor gained more and
more attention in the last years because of its potential to improve process efficiency, as in the
case of esterifications (Dunnebier et al., 2000; Kawase et al., 1996; Lode et al., 2003; Lode et
al., 2001; Mazzotti et al., 1996; Meissner and Carta, 2002; Migliorini et al., 1999; Yu et al.,
2003), etherifications (Zhang et al., 2001), sugars (Azevedo and Rodrigues, 2001; Da Silva
et al., 2005; Da Silva et al., 2006; Dunnebier et al., 2000; Pilgrim et al., 2006; Zhang et al.,
2004), bisphenol A (Kawase et al., 1999), acetals (Dubois, 2008a; Pereira et al., 2008a;
Rodrigues and Silva, 2005; Silva and Rodrigues, 2005) and polyacetals (Dubois, 2008b) and
will be applied in this work on the synthesis of the green solvent ethyl lactate. A schematic
diagram of a SMBR unit is presented in Figure 5.1 where a reaction of type A+B↔C+D is
considered. Similarly to the SMB, the SMBR consists of a set of columns connected in series
packed with a solid, which could be a mixture of catalyst and selective adsorbent or a solid
that acts both as catalyst and as adsorbent. Typically, there are two inlets, feed and desorbent,
and two outlets, extract and raffinate. In this case, the component A is used as reactant and
desorbent, therefore it is introduced in the system in the feed and desorbent streams. The
other reactant B is used as feed. At regular time intervals, called the switching time, all
streams are switched for one column distance in direction of the fluid flow. In this way, the
countercurrent motion of the solid is simulated and its velocity is equal to the length of a
column divided by the switching time. A cycle is completed when the number of switches is
equal to a multiple of the total number of columns. According to the position of the inlet and
outlet stream the unit can be divided in four sections. In section 1, positioned between the
desorbent and extract nodes, the adsorbent is regenerated by desorption of the more strongly
adsorbed product (D) from the solid. In section 2 (between the extract and feed node) and
section 3 (between the feed and raffinate node) the reaction is taking place and the products C
and D are formed. The more strongly adsorbed product, D, is adsorbed in sections 2 and 3
and transported with the solid phase to the extract port. The less strongly adsorbed product, C,
is desorbed in sections 2 and 3 and transported with the liquid in direction of the raffinate
port. In section 4, positioned between the raffinate and desorbent node, before being recycled
to section 1, the desorbent is regenerated by adsorption of the less adsorbed product (C).
104 CHAPTER 5. Simulated Moving Bed Reactor
Desorbent (A) Raffinate (A+C)
Extract(A+D)
Direction of fluid flow and port switching
1 2 3 4
5 6
12 11
10 9
8 7
Feed(A+B)
A + B C + D
Figure 5.1 Schematic diagram of a SMBR with three columns per section.
In this work an alternative technology, the SMBR, is proposed for the ethyl lactate
production. The ethyl lactate synthesis is experimentally studied using a SMBR pilot unit and
theoretically using the SMBR model proposed. This model results are verified by the
experiments performed and the effect of various operating parameters, as feed composition,
SMBR configuration and switching time, into the SMBR performance at the optimal
operating points and/or reactive/separation regions is evaluated. The SMBR model is
compared with the equivalent True Moving Bed Reactor (TMBR) model. All this study will
allow to future compare the SMBR and the membrane reactor processes in economic and
efficiency terms.
5.2 Modelling Strategies
5.2.1 SMBR mathematical model
The SMBR modelling strategy allows the visualization of the axial movement of
concentration profiles and the variations in extract and raffinate concentrations within a
period. The dynamic calculation of concentration profiles until the unit achieves the cyclic
steady state, accounting for the inlet and outlet discontinuous shift, was made considering
axial dispersion flow for the bulk fluid phase, linear driving force (LDF) approximation for
the inter and intra-particle mass transfer rates, multi-component adsorption equilibrium and
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 105
velocity variations due to adsorption/desorption rates leading to more accurate results. The
porosity of the packed bed and its length (packed bed length) were assumed to be constant.
The SMBR model equations are:
Bulk fluid mass balance to component i in column k:
( ) ( ),, , ,
1 3ik ik k ikp ikL ik ik ax k T k
p
C C u xK C C D Ct z r z z
εε−∂ ∂ ∂∂ ⎛ ⎞+ + − = ⎜ ⎟∂ ∂ ∂ ∂⎝ ⎠
(5.1)
where ikC and ,p ikC are the bulk and average particle concentrations in the fluid phase of
species i in column k respectively, ikLK , is the global mass transfer coefficient of the
component i, ε is the bulk porosity, t is the time variable, z is the axial coordinate, kaxD , , and
ku are the axial dispersion coefficient and the interstitial velocity in column k, respectively,
and pr is the particle radius.
The global mass transfer coefficient ( LK ) is defined as:
ipeL kkK ε111
+= (5.2)
wherein ek and ik are, respectively, the external and internal mass transfer coefficients. The
values of the external, internal and global mass transfer coefficients are shown in Table 5.1.
The methods used to obtain these values and the determination of axial dispersion
coefficient, axD , are presented in detail in Chapter 4.
Table 5.1 Mass transfer coefficients estimated at 50 ºC at the inlet of the SMBR for a simulation where the feed is lactic acid solution (86 % in water) at a flowrate of 7 mL/min.
Component ke (cm/min) ki (cm/min) KL (cm/min)
Ethanol 0.387 0.138 0.045
Lactic Acid 0.351 0.119 0.039
Ethyl Lactate 0.296 0.092 0.031
Water 0.623 0.280 0.090
106 CHAPTER 5. Simulated Moving Bed Reactor
Interstitial fluid velocity variation is calculated using the total mass balance:
( ) ( ),, ,1
1 3 nk
p ikL ik mol i ikip
du K V C Cdz r
εε =
−= − −∑ (5.3)
where Vmol,,i is the molar volume of component i that is 60.87 mL/mol, 77.56 mL/mol,
118.44 mL/mol and 18.63 mL/mol at 50 ºC for ethanol, lactic acid, ethyl lactate and water,
respectively.
Pellet mass balance to component i, in column k:
( ) ( ),, ,,
31 ( )p ik ikp ik p ikp p L ik ik i p
p
qC K C C r Ct t r
ε ε υ ρ∂∂+ − = − +
∂ ∂ (5.4)
where ikq is the average adsorbed phase concentration of species i in column k in equilibrium
with ,p ikC , pε the particle porosity, iυ the stoichiometric coefficient of component i, pρ the
particle density and r is the chemical reaction rate relative to the average particle
concentrations in the fluid phase and is given by (Chapter 3):
2
,1 ⎟⎠
⎞⎜⎝
⎛+
−=
∑=
W
Ethiiis
WELLaEth
c
aK
Kaaaa
kr (5.5)
where kc is the kinetic constant, isK , is the adsorption constant for species i and Keq is the
equilibrium reaction constant, a is the species activity (calculated by UNIQUAC model) and
the subscripts WELLaEth and , , refer to ethanol, lactic acid, ethyl lactate and water,
respectively.
Multi-component adsorption equilibrium isotherm:
,,
,1
1
p ikads i iik n
p ikll
Q K Cq
K C=
=⎛ ⎞
+⎜ ⎟⎝ ⎠
∑ (5.6)
where, iadsQ , and iK represent the total molar capacity per unit volume of resin and the
equilibrium constant for component i, respectively, and n the total number of components.
The adsorption parameters were determined and presented in Chapter 4.
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 107
Initial and Danckwerts boundary conditions:
0=t : , ,0p ikik ikC C C= = and ,0ik ikq q= (5.7)
0=z : , ,0
ikk ik ax k k ik F
z
Cu C D u Cz =
∂− =
∂ (5.8a)
,0k ku u= (5.8b)
cLz = : 0=∂
∂
=Lcz
ik
zC (5.8c)
where F and 0 refer to the feed and initial states, respectively.
Mass balances at the nodes of the inlet and outlet lines of the SMBR:
Desorbent node: 1( 4, ) ( 1, 0)
4 4
DDi j z Lc i j z i
u uC C Cu u= = = == − (5.9a)
Extract(j=2) and Raffinate (j=4) nodes: )0,(),1( ==− = zjiLczji CC (5.9b)
Feed node: Fi
FziLczi C
uuC
uuC
2)0,3(
2
3),2( −= == (5.9c)
where,
Dsuuu += 41 Desorbent (Ds) node ; (5.10a)
Xuuu −= 12 Extract (X) node ; (5.10b)
Fuuu += 23 Feed (F) node ; (5.10c)
Ruuu −= 34 Raffinate (R) node ; (5.10d)
The ratio between the fluid interstitial velocity, uj, and the simulated solid velocity, Us,
(defined by the column length and switching time relation,*t
LUs = ) could be defined for
each section giving a new parameter:
Usu j
j =γ (5.10e)
108 CHAPTER 5. Simulated Moving Bed Reactor
5.2.2 SMBR performance parameters
The SMBR process performance is calculated over a complete cycle according to the next
equations:
Raffinate Purity:
( )
*
*(%) 100
c
c
t N tR
ELt
t N tR R R
La EL Wt
C dtPUR
C C C dt
+
+=
+ +
∫
∫ (5.11a)
Extract Purity:
( )
*
*(%) 100
c
c
t N tX
Wt
t N tX X X
La EL Wt
C dtPUX
C C C dt
+
+=
+ +
∫
∫ (5.11b)
Lactic acid Conversion:
⎟⎟⎟⎟⎟
⎠
⎞
⎜⎜⎜⎜⎜
⎝
⎛+
−=∫ ∫
+ +
*1100(%)
* *
tNCQ
dtCQdtCQX
cFlaF
tNt
t
tNt
t
RLaR
XLaX
c c
(5.12)
Raffinate Productivitysin
EL
re
kgdayL
⎛ ⎞⎜ ⎟⎝ ⎠
: ( ) *1
*
tNV
dtCQPR
cunit
tNt
t
RELR
c
ε−=
∫+
(5.13)
Desorbent Consumption (LEth/kgEL):
∫+
−+= *
,,, )(* tNt
t
RELR
FLaFEthFDEthDc c
dtCQ
XCCQCQtNDC (5.14)
where Nc represents the total number of columns (the complete cycle). The productivity is
defined considering the ethyl lactate (desired product) produced and withdrew from the
raffinate stream. The ethanol consumed in the reaction is not taken into account to calculate
the desorbent consumption, being only considered the amount of ethanol used as desorbent.
5.2.3 Numerical Solution
The above model equations were solved numerically by using the gPROMS-general PROcess
Modelling System version: 3.0.3. The mathematical model involves a system of partial and
algebraic equations (PDAEs). The axial domain was discretized using third order orthogonal
collocation in finite elements method (OCFEM). Ten finite elements per column with two
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 109
collocation points in each element were used. The system of ordinary differential and
algebraic equations (ODAEs) was integrated over time using the DASOLV integrator
implementation in gPROMS. For all simulations was fixed a tolerance equal to 10-5. It is
assumed that an SMB simulation has reached the cyclic steady state when the columns
profiles in two consecutive cycles have less than 1.0 % of relative deviation and the global
mass balance is verified with less than 1.0 % of relative error.
5.3 Experimental Section
5.3.1 Chemicals and Catalyst / Adsorbent
The chemicals used in the experiments were ethanol (>99.5 % in water), lactic acid (>85 % in
water) and ethyl lactate (>98 % in water) from Sigma-Aldrich (U.K.).
The columns were packed with Amberlyst 15-wet (Rohm & Haas, France), which is a highly
cross-linked polystyrene-divinylbenzene ion exchange resin functionalized with sulfonic
groups (SO3H) that acts as catalyst and adsorbent in this system.
5.3.2 The SMBR LICOSEP 12-26 Unit
All SMBR experiments were performed in a pilot unit LICOSEP 12-26 by Novasep
(Vandoeuvre-dès-Nancy, France), where 12 columns Superformance SP 230 x 26 (length x
internal diameter, mm), by Götec Labortechnik (Mühltal, Germany), packed with the acid
resin Amberlyst 15-wet were connected. The characteristics of the SMBR columns are
presented in Table 5.2 and a side view of the pilot unit is shown in Figure 5.2. The bed
porosity and the Peclet number were determined as in previous Chapter (Chapter 4). These
columns can withstand up to 60ºC of temperature and 60 bar of pressure. The operating
temperature was 50ºC; this temperature was ensured in the jacketed columns using a
thermostatic bath (Lauda, Germany). Between every two columns exists a four-port valve
(Top-Industrie, France) actuated by the control system. When required, according to the
operating conditions set into the system, the valves allow either pumping of the feed or
desorbent into the system or withdrawal of extract or raffinate from the system. HPLC pumps
are used to pump each of the inlet streams (feed or desorbent) and outlet streams (extract or
raffinate). The maximum flow rate in the desorbent and extract pumps is 30 mL/min, while in
110 CHAPTER 5. Simulated Moving Bed Reactor
the feed and raffinate pumps is 10 mL/min. The recycling pump, which is a positive
displacement three-headed membrane pump (Dosapro Milton Roy, France), can deliver flow
rates as low as 20 mL/min up to 120 mL/min and it can hold up to 100 bar pressure. A six-
port valve, located between the twelfth and the first columns, was used to collect the samples
for internal concentration measurements (Novasep). All the samples were analysed in a gas
chromatograph using the analytical method described in Chapter 3.
Figure 5.2 Licosep 12-26 unit with the 12 packed columns.
Table 5.2 Characteristics of the SMBR columns.
Solid weight (A15) 47.6 g
Length of the bed (L) 23 cm
Internal diameter (Di) 2.6 cm
Average radius of resin beads (rp) 342.5 μm
Bulk density (ρ b) 390 kg/m3
Bed porosity (ε) 0.4
Resin particle porosity (εp) 0.36 (Lode et al., 2001)
Peclet number 300
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 111
5.4 Results and Discussion
5.4.1 Experimental Results
Three different experiments of ethyl lactate synthesis were performed at 50ºC in the SMBR
unit. In all the experiments the feed composition was a lactic acid solution (85 % in water).
The flow rates of feed and raffinate streams were QF = 1.80 mL/min and QR = 8.80 mL/min,
while for desorbent and recycle the flow rates were QD = 27.40 mL/min and
QRe c = 24.70 mL/min. Two different switching times (2.9 and 3.0 min) and two different
configurations (3-3-3-3 and 3-3-4-2) where tested, as shown in Table 5.3. The SMBR
performance parameters obtained experimentally are presented in Table 5.3, as well as the
corresponding values obtained by simulation. In Figure 5.3, the cyclic steady-state (CSS)
concentration profiles obtained experimentally at the middle of the switching time after 13
cycles are shown and compared with the profiles simulated by the SMBR model.
Table 5.3 Operating conditions for SMBR experiments and performance parameters obtained experimentally (bold) and by simulation (inside brackets).
Run 1 Run 2 Run 3
t* (min) 2.9 2.9 3
Configuration 3-3-3-3 3-3-4-2 3-3-4-2
PUR (%) 72.75 (79.24) 73.54 (79.80) 75.17 (81.32)
PUX (%) 95.54 (99.89) 95.22 (99.83) 97.76 (99.85)
X (%) 99.10 (97.46) 99.91 (97.87) 99.96 (98.00)
PR (kgEL.Lresin-1.day-1) 3.20 (3.66) 3.31 (3.68) 3.36 (3.68)
DC (LEth/kgEL) 13.41 (11.74) 12.99 (11.70) 12.77 (11.68)
For the first experiment the lactic acid conversion is about 99 %, being for the second and
third experiments around 100 %. However the raffinate purities are low, this is due to the fact
that the SMBR experiments realized were performed under conditions of incomplete
adsorbent regeneration in section 1 (see Figure 5.3) caused by equipment limitations
(maximum allowable desorbent flow rate of 30 mL/min).
112 CHAPTER 5. Simulated Moving Bed Reactor
b)
a)
c)
Figure 5.3 Experimental concentration profiles in SMBR unit at the middle of switching time at cyclic steady state (13th cycle) and simulated curves.
(a) Run 1; (b) Run 2; (c) Run3.
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 113
The feed is a lactic acid solution (85 % in water), so water is already introduced into the
system and as the reaction proceeds more water is being formed. Since water is the most
adsorbed component and there is a significant amount of this component in the SMBR, the
desorbent flow rate used was not high enough to completely regenerate (removing the water
adsorbed by the resin) the first section; because of that the adsorbed water was carried by the
resin entering in section 4 and transported to section 3, hydrolysing the ethyl lactate
producing ethanol and lactic acid (the opposite reaction). As consequence the ethyl lactate
productivity and its concentration in the raffinate stream is low. The use of a higher desorbent
flow rate will permit the complete regeneration of section 1 leading to higher purities and
productivity. From Figure 5.3, it can be perceived that the reaction takes place in sections 2
and 3; since the esterification reaction between lactic acid and ethanol is very slow, the
change of configuration from 3-3-3-3 to 3-3-4-2 increases the lactic acid conversion, due to
the increase of the number of columns available in the reactive sections 2 and 3. Increasing
the switching time (Figure 5.3c), increases the lactic acid conversion once the contact time
between liquid and solid streams is higher. Moreover, the ethyl lactate purity increases since
the value of γ1 is higher and therefore the resin is better regenerated. The CSS concentration
profiles obtained experimentally at 25 %, 50 % and 75 % of the switching time, at the 13th
cycle are compared with the simulated ones, in Figure 5.4. It is noticed that all the species
concentration fronts propagate along the column without changing its shape presenting,
therefore, a constant behaviour along the time. For the third experiment, the experimental
composition of extract and raffinate streams collected for a whole cycle at the 3rd, 5th, 7th,
9th and 11th cycles, and the extract and raffinate concentration histories calculated from the
SMBR model are shown in Figure 5.5.
As it can be observed, the mathematical model used predicts with reasonable accuracy the
experimental concentration profiles (Figure 5.3 and Figure 5.4), the raffinate and extract
histories (Figure 5.5) and the performance parameters (Table 5.3).
114 CHAPTER 5. Simulated Moving Bed Reactor
Figure 5.4 Experimental concentration profiles in SMBR unit at the 25 %, 50% and 75 % of the switching time at cyclic steady-state (13th cycle) and simulated curves for Run 3.
Figure 5.5 Experimental and theoretical average concentration of all species (ethanol, lactic acid, ethyl lactate and water) for the conditions of the third experience in the extract (a) and raffinate (b) streams.
a) b)
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 115
5.4.2 Simulated results
5.4.2.1 Comparison of SMBR and TMBR models
The equivalent TMBR model was also studied since it is a simpler model that implies less
computational time than that required by the SMBR model. However, comparing the
concentration profiles at the cyclic steady state calculated from the SMBR model with those
calculated from the equivalent TMBR model, as shown in Figure 5.6, some difference is
noticed and, because of that, the SMBR model was used for all the simulations presented in
this work. The operating conditions used in the simulations are presented in Table 5.4 and the
feed flow rate and raffinate flow rate used were 5 mL/min and 17 mL/min, respectively.
Figure 5.6 Comparison of the concentration profiles at the middle of the switching time at cyclic steady state determined with the SMBR model (solid lines) and steady state concentration profiles calculated with the TMBR model (dashed lines), for the operating conditions presented in Table 5.
116 CHAPTER 5. Simulated Moving Bed Reactor
Table 5.4 Operating conditions.
Operating conditions
Configuration (analyzed in section 5.4.2.5) 3-3-4-2
Feed Concentration (mol/L) (analyzed in section 5.4.2.4)
CEth,F =0.0; CEL,F = 0.0 CLA,F =10.75; CW,F = 9.48
Desorbent flow rate (mL/min) 58.0
Recycle flow rate (mL/min) 27.0
Switching time (min) (analyzed in section 5.4.2.6) 2.7
5.4.2.2 Reactive/separation regions
The proper design of a SMBR unit involves the correct choice of the operating conditions as
flow rates in each section of the unit, switching time, columns arrangement (SMBR
configuration) and feed concentration, among others. In the next sub-sections, the
reactive/separation regions and the optimal operating points for different operating conditions
are presented in order to understand the behaviour of the SMBR process for ethyl lactate
synthesis. The operating conditions used in the simulations indicating which parameter is
being changed in each sub-section are presented in Table 5.4. The reactive/separation regions
setting a criteria of 95 % for extract and raffinate purity and, also, for lactic acid conversion
were determined from the average concentrations over a cycle obtained by the SMBR model
at cyclic steady state. The cyclic steady state SMBR model was successively solved for
several values of γ2 and γ3, keeping the values of γ1 (4.698) and γ4 (1.492). The
reactive/separation region is located within the region between the diagonal γ2=γ3, the
horizontal line γ3 =1.492 and γ3 axis. The γ3 value must be higher than γ2, since the diagonal
γ2=γ3 corresponds to zero feed flow rate. The algorithm used in the construction of the
reactive/separation region begins by setting a feed flow rate of 0.01 ml/min and the value of
γ2 equal to 1.492. Then, the feed flow rate was kept constant and the γ2 values were gradually
increased. The value of γ3 was calculated from the mass balance in the feed node for each
value of γ2. For each set of γ2 and γ3, the conversion and the purities of extract and raffinate
were estimated and the values that satisfy the criteria of 95 % were selected to build the
reaction/separation region. After this set of simulations, the feed flow rate was increased and
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 117
the same procedure was repeated. The simulations procedure ends when the maximum value
of feed flow rate that gives required product purities and conversion is achieved. Above that
feed flow rate value the requirements can not be fulfilled for any pair of values of γ2 and γ3.
5.4.2.3 Separation Region vs Reactive/Separation Region
One can use a SMB unit to perform the separation of ethyl lactate and water, in absence of
reaction, considering the purity criteria of 95 %, to process a feed with composition of
CW = 12.17 mol/L and CEL = 6.47 mol/L that corresponds to complete conversion of the
lactic acid solution (CAL = 10.75 mol/L and CW = 9.48 mol/L) into ethyl lactate and water,
taking into consideration the expression ( ),i i n m kk
C x x V= ∑ , where ix is the molar fraction of
species i and nmV , is the molar volume of species n.
In Figure 5.7, the comparison between the separation region of the SMB and the
reactive/separation region of the SMBR indicates that the process is limited by the reaction.
As mentioned by Fricke and Schmidt-Traub, the reactive separation region is reduced by
decreasing either the equilibrium constant or the reaction kinetics (Fricke and Schmidt-Traub,
2003). The lactic acid esterification reaction is slow and, because of that, it is necessary to
keep the reactant as long as possible in sections 2 and 3 (between the extract and raffinate
ports). If the lactic acid is not fully consumed it will preferentially contaminate the raffinate
stream, since the resin selectivity between lactic acid and ethyl lactate is smaller than the one
between water and lactic acid. Thus, in the SMBR it is necessary to ensure the separation of
the products (ethyl lactate and water), but is crucial to guarantee the complete conversion of
the limiting reactant (lactic acid). One way of improving reaction kinetics is by increasing the
system temperature that will also benefit the equilibrium constant since the ethyl lactate
synthesis is an endothermic reaction. However, this leads to higher energy requirement and it
will affect the products separation: (i) if water adsorption is more affected than ethyl lactate
adsorption, less desorbent consumption is required, but maximum productivity decreases; (ii)
in the opposite case, productivity is enhanced while the consumption of desorbent increases.
The trade-off between those parameters should be evaluated through an economical
assessment. Another way to get the full conversion is increasing the reaction rate by using a
mixture of two stationary phases that increases the catalytic properties without losing
118 CHAPTER 5. Simulated Moving Bed Reactor
efficiency on the separation of the products (Silva and Rodrigues, 2008; Ströhlein et al.,
2004).
1.0
1.5
2.0
2.5
3.0
3.5
4.0
1.0 1.5 2.0 2.5 3.0 3.5 4.0
γ 3
γ2
Feed: lactic acid solution (SMBR)
Feed: ethyl lactate and water (SMB)
Figure 5.7 Reactive/separation region for the case where lactic acid solution is fed to
the SMBR (CLA,F = 10.75 mol/L; CW,F = 9.48 mol/L) and separation region for ethyl lactate and water fed to the SMB (CEL,F = 6.47 mol/L; CW,F = 12.17 mol/L). (γ1 = 4.698; γ4 =1.492; 95 % purity).
5.4.2.4 Effect of the Feed Composition
In order to study the influence of the feed composition, this was varied by adding pure
ethanol to the lactic acid solution remaining constant the other operation conditions (see
Table 5.4). As it can be seen in Figure 5.8, the size of the reactive/separation region decreases
with the increase of the lactic acid concentration in the feed. This could be justified by a lack
of ethanol in the sections 2 and 3, where reaction occurs, limiting the lactic acid conversion to
the thermodynamic equilibrium and so higher lactic acid concentrations will lead to higher
quantities of unreacted lactic acid and therefore the raffinate stream will be contaminated.
This could be confirmed by analyzing the influence of the lactic acid feed molar fraction in
the ethyl lactate productivity and the desorbent consumption for the optimal operating points
(see Figure 5.9). It can be seen that by increasing the lactic acid feed molar fraction until
72 %, where the lactic acid is the limiting reactant, the productivity increases with consequent
decrease in desorbent consumption; however, further increase in the lactic acid feed molar
fraction has a negative impact in the SMBR performance parameters since, as it was
mentioned, ethanol is the limiting reactant in sections 2 and 3. Thus, for the values of γ1 and
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 119
γ4 and SMBR configuration defined in Table 5.4, the feed molar composition of 72 % of
lactic acid leads to the optimal values of productivity (17.33 kgEL/(Lads.day)) and desorbent
consumption (5.36 LEth/kgEL). So, it can be concluded that the lactic acid concentration in the
SMBR feed should be high enough to increase the productivity without leading to a lack of
ethanol in the reaction zone (section 2 and 3).
1.5
2.0
2.5
3.0
3.5
1.5 2.0 2.5 3.0 3.5
γ 3
γ2
100 % La solution
88 % La solution
38 % La solution
Figure 5.8 Reactive/separation regions for different feed concentrations
of lactic acid solution. (γ1 = 4.698; γ4 =1.492; 95 % purity).
5.0
5.8
6.6
7.4
8.2
9.0
12.0
13.0
14.0
15.0
16.0
17.0
18.0
35 45 55 65 75 85 95
DC
(LEt
h/K
g EL)
PR (K
g EL/
(Lad
s.day
))
Lactic acid solution (85 % in water) feed composition (%)
PR
DC
Figure 5.9 SMBR performance for the optimal operating points as a
function of the lactic acid solution molar fraction in feed.
120 CHAPTER 5. Simulated Moving Bed Reactor
5.4.2.5 Effect of the SMBR columns arrangement
The influence of the columns arrangement on the SMBR system performance was studied by
simulating different SMBR configurations (3-3-3-3, 3-3-4-2 and 3-3-5-1), keeping the
remaining operating conditions as mentioned in Table 5.4. The performance parameters
corresponding to the optimal operating point (vertex of the reactive/separation region) for
each case are presented in Table 5.5, and the reactive/separation regions are shown in Figure
5.10. It can be perceived that, the introduction of more columns into the section 3 by taking of
the section 4 and keeping the total number of columns constant, does not improve
significantly the process performance. This is due to the fact that after about 3 mL/min of
lactic acid solution feed flow rate the ethanol is the limiting reactant and even when the
reaction zone is increased is not possible to completely convert the lactic acid, which will
cause contamination of the raffinate stream. Although the increase of the reaction zone in
these conditions does not improve much the ethyl lactate production on the SMBR unit it was
noticed that only one column in section 4 is enough to allow the complete regeneration of the
desorbent (see Figure 5.11).
The kinetics of the ethyl lactate synthesis is very slow and to allow full conversion of the
lactic acid is necessary not only to increase the reaction zone, but also to feed to the SMBR a
lactic acid concentration that does not lead to a lack of ethanol in the reaction zone.
1.5
2.0
2.5
3.0
3.5
1.5 2.0 2.5 3.0 3.5
γ 3
γ2
conf 3-3-3-3conf 3-3-4-2conf 3-3-5-1
Figure 5.10 Reactive/separation regions for different SMBR configurations.
(γ1 = 4.698; γ4 =1.492; 95 % purity).
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 121
Table 5.5 Performance parameters of the SMBR unit at cyclic steady state for the optimal operation points for the different SMBR configurations.
Columns arrangement 3-3-3-3 3-3-4-2 3-3-5-1
Raffinate productivity (kgEL/LA15/day) 14.97 15.33 15.36
Desorbent consumption (LEth/kgEL) 5.83 5.68 5.67
Figure 5.11 Concentration profiles at the middle of the switching time at cyclic
steady state for the optimal operating point of the SMBR configuration 3-3-5-1.
5.4.2.6 Effect of Switching Time
The switching time effect on the SMBR performance for the optimal operating point was
studied by two different ways: one varying the switching time and keeping constant the
remaining operating parameters of Table 5.4 (Figure 5.12); the other varying the switching
time and the desorbent and recycle flow rate in order to keep constant the γ1 (4.698) and
γ4 (1.492) values (Figure 5.13). For the first case (Figure 5.12), as the switching time
decreases until 2.1 minutes, the solid flow rate increases leading to a better SMBR
performance. However, decreasing the switching time below 2.1 min, the restriction of γ1 is
being violated and, therefore, is no longer possible to achieve the minimum purity of 95 % for
the raffinate stream, since the solid is not being completely regenerated in section 1, and,
because of that, the water appears in the raffinate stream, leading to a low purity. The SMBR
122 CHAPTER 5. Simulated Moving Bed Reactor
operation using a switching time of 2.1 min instead of 2.8 min enhances the productivity in
22.0 % (maximum of 18.06 kgEL/(Lads.day)) and decreases the desorbent consumption in
19.6 % (minimum of 4.75 LEth/kgEL), and will reduce downstream costs since the products are
less diluted.
4.4
4.8
5.2
5.6
6.0
14.0
15.0
16.0
17.0
18.0
19.0
2.1 2.2 2.3 2.4 2.5 2.6 2.7 2.8
DC (L
Eth/
KgEL
)
PR (K
g EL/
(Lad
s.da
y))
Switching time (min)
PRDC
Figure 5.12 SMBR performance for the optimal operating points as a function
of the switching time.
For the second case (Figure 5.13), where the γ1 and γ4 values are keeping the same, similarly
to the previous case, the productivity increases by decreasing the switching time; contrarily,
the desorbent consumption increases once the desorbent flow rate is increasing in order to
keep the value of γ1 constant. Changing the switching time from 2.8 to 2.1, increases the
productivity and desorbent consumption to 19.34 kgEL/(Lads.day) and 5.79 LEth/kgEL,
corresponding to a variation of +30.7 % and +2.0 %, respectively. The reduction of 2.8 min to
1.0 min, in switching time, leads to a significant increase in productivity in 114.4 %
(31.7 kgEL/(Lads.day)), while the desorbent consumption is increased in 33.3 %
(7.6 LEth/kgEL). The choice of the optimal switching time value requires an economical
assessment to the whole process, considering the downstream separation units, in order to
verify if the enhancement of productivity reimburses the increase of the cost associated to the
desorbent separation and recycle to the SMBR unit.
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 123
5.6
6.0
6.4
6.8
7.2
7.6
12.0
16.0
20.0
24.0
28.0
32.0
1.0 1.4 1.8 2.2 2.6
DC (L
Eth/
Kg E
L)
PR (K
g EL/
(Lad
s.day
))
Switching time (min)
PR
DC
Figure 5.13 SMBR performance for the optimal operating points as a function of
the switching time keeping γ1 = 4.698 and γ4 =1.492.
5.5 Conclusions
The ethyl lactate was produced in the Simulated Moving Bed Reactor pilot unit LICOSEP,
using Amberlyst 15-wet resin as catalyst and selective adsorbent. The experiments conducted
were not performed under optimal operating conditions since they were limited by restrictions
of the experimental set-up; therefore, the desorbent flow rate used was not enough to achieve
complete regeneration of the resin in section 1. The performance parameters and the
experimental profiles were predicted with good accuracy using the SMBR model. The
theoretical assessment of the SMBR unit behaviour was performed ensuring complete
regeneration of the resin (in section 1) and desorbent (in section 4), by using the mathematical
model to analyse the effect of SMBR configuration, feed composition and switching time into
the reactive/separation regions or/and into the process performance at the optimal operating
points. Since the kinetics of the ethyl lactate synthesis is very slow, even at 50ºC, its
production in the SMBR is determined by the reaction, and therefore, the complete
conversion of lactic acid is a decisive parameter in order to optimize the SMBR performance.
To get that target, several aspects should be regarded: to play with feed composition to avoid
a lack of ethanol in the reactive sections 2 and 3; to increase the number of columns in those
sections to increase the reaction zone; to choose the best switching time, that affects
significantly the SMBR process. The other key aspect that should be considered is the water
124 CHAPTER 5. Simulated Moving Bed Reactor
desorption in section 1 to ensure the complete regeneration of the resin; Amberlyst 15-wet is
very selective to water and therefore higher desorbent flow rates are required. The effects of
the various operating parameters, as the feed composition, the SMBR configuration and the
switching time, on the SMBR process showed that there is a complex interaction among all of
them in terms of their impacts on the performance of the process, as the extract and raffinate
purities, lactic acid conversion, ethyl lactate productivity and desorbent consumption.
Moreover, some set of parameters might act in conflicting ways, like the case of the switching
time for fixed values of γ1 and γ4, that increase significantly the productivity but also increases
the desorbent consumption. For a fixed switching time of 2.7 min the best feed molar
composition was 72 % of lactic acid leading to a productivity of 17.33 kgEL/(Lads.day) and
desorbent consumption of 5.36 LEth/kgEL. The higher value of productivity,
31.7 kgEL/(Lads.day), was obtained for a switching time of 1 min, 100% of lactic acid solution
in feed, γ1 = 4.698 and γ4 =1.492.
5.6 Notation
a liquid-phase activity
C liquid phase concentration (mol/L)
CT total liquid phase concentration (mol/L)
axD axial dispersion coefficient (m2/min)
DC desorbent consumption (L/mol)
ck kinetic constant (mol kg-1 min-1)
ek external mass transfer coefficient
eqK equilibrium reaction constant
ik internal mass transfer coefficient
iK Langmuir equilibrium constant of component i (L/mol)
LK global mass transfer coefficient
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 125
L column length (m)
n total number of components
Nc total number of columns
PR raffinate productivity (kgEL/(L resin.day))
PUR raffinate purity (%)
PUX extract purity (%)
q solid phase concentration in equilibrium with the fluid concentration inside the
particle (mol/L)
,ads iQ adsorption capacity of component i (mol/Lwet solid)
jQ volumetric flowrate in section j (L/min)
r rate of reaction (mol kg-1 min-1)
pr particle radius (m)
t time variable (min)
*t switching time (min)
Us solid velocity (m/min)
u interstitial velocity (m/min)
,mol iV molar volume of species i (L/mol)
unitV volume of adsorbent in SMBR (L)
x mole fraction
X lactic acid conversion
z axial coordinate (m)
Greek letters
γ interstitial velocities ratio
ε bulk porosity
126 CHAPTER 5. Simulated Moving Bed Reactor
pε particle porosity
iυ stoichiometric coefficient of component i
pρ particle density
Subscripts
i relative to component i (i= Eth, La, EL, W)
j relative to section in SMBR (j = 1, 2, 3, 4)
k relative to column in SMBR
Eth relative to ethanol
La relative to lactic acid
EL relative to ethyl lactate
W relative to water
0 relative to initial conditions
p relative to particle
F relative to the feed
R relative to raffinate
cRe relative to recycle
X relative to extract
Superscripts
F relative to the feed
R relative to raffinate
X relative to extract
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 127
5.7 References Cited
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Chopade S. P. and M. M. Sharma, "Reaction of ethanol and formaldehyde: use of versatile cation-exchange resins as catalyst in batch reactors and reactive distillation columns", React. Funct. Polym. 32(1): 53-65, 1997.
Cruz V. J., J. F. Izquierdo, F. Cunill, J. Tejero, M. Iborra and C. Fité, "Acid ion-exchange resins catalysts for the liquid-phase dimerization/etherification of isoamylenes in methanol or ethanol presence", React. Funct. Polym. 65(1-2): 149-160, 2005.
Da Silva E. A. B., A. A. U. De Souza, S. G. U. De Souza and A. E. Rodrigues, "Simulated moving bed technology in the reactive process of glucose isomerization", Adsorption 11(1 SUPPL.): 847-851, 2005.
Da Silva E. A. B., A. A. U. De Souza, S. G. U. De Souza and A. E. Rodrigues, "Analysis of the high-fructose syrup production using reactive SMB technology", Chem. Eng. J. 118(3): 167-181, 2006.
Dinwiddie J. A. and W. A. Morgan, " Fixed bed type reactor", Patent 2 976 132 (1961).
Dubois J.-L., "Procede de synthese d' acetals par transacetalisation dans un reacteur a lit mobile simule", Patent FR 2909669 (A1) (2008a).
Dubois J.-L., "Process for the synthesizing polyacetals in a simulated mobile-bed reactor", Patent WO 2008/053108 (2008b).
Dunnebier G., J. Fricke and K. U. Klatt, "Optimal Design and Operation of Simulated Moving Bed Chromatographic Reactors", Ind. Eng. Chem. Res. 39(7): 2290-2304, 2000.
Ferreira M. V. and J. M. Loureiro, "Number of actives sites in TAME synthesis: Mechanism and kinetic modeling", Ind. Eng. Chem. Res. 43(17): 5156-5165, 2004.
Fricke J. and H. Schmidt-Traub, "A new method supporting the design of simulated moving bed chromatographic reactors", Chem. Eng. Process. 42(3): 237-248, 2003.
Gandi G. K., V. M. T. M. Silva and A. E. Rodrigues, "Process Development for Dimethylacetal Synthesis: Thermodynamics and Reaction Kinetics", Ind. Eng. Chem. Res. 44(19): 7287-7297, 2005.
Kawase M., Y. Inoue, T. Araki and K. Hashimoto, "The simulated moving-bed reactor for production of bisphenol A", Catal. Today 48(1-4): 199-209, 1999.
128 CHAPTER 5. Simulated Moving Bed Reactor
Kawase M., T. B. Suzuki, K. Inoue, K. Yoshimoto and K. Hashimoto, "Increased esterification conversion by application of the simulated moving-bed reactor", Chem. Eng. Sci. 51(11): 2971-2976, 1996.
Lode F., G. Francesconi, M. Mazzotti and M. Morbidelli, "Synthesis of methylacetate in a simulated moving-bed reactor: Experiments and modeling", AlChE J. 49(6): 1516-1524, 2003.
Lode F., M. Houmard, C. Migliorini, M. Mazzotti and M. Morbidelli, "Continuous reactive chromatography", Chem. Eng. Sci. 56(2): 269-291, 2001.
Ma L., J. Hong, M. Gan, E. Yue and D. Pan, "Kinetics of esterification and transesterification for biodiesel production in two-step process", J. Chem. Ind. Eng. China 59(3): 708-712, 2008.
Mazzotti M., A. Kruglov, B. Neri, D. Gelosa and M. Morbidelli, "A continuous chromatographic reactor: SMBR", Chem. Eng. Sci. 51(10): 1827-1836, 1996.
Meissner J. P. and G. Carta, "Continuous regioselective enzymatic esterification in a simulated moving bed reactor", Ind. Eng. Chem. Res. 41(19): 4722-4732, 2002.
Migliorini C., M. Fillinger, M. Mazzotti and M. Morbidelli, "Analysis of simulated moving-bed reactors", Chem. Eng. Sci. 54(13-14): 2475-2480, 1999.
Novasep, "Licosep 12-26 Instructions manual, France",
Pereira C. S. M., P. S. Gomes, G. K. Gandi, V. M. T. M. Silva and A. E. Rodrigues, "Multifunctional Reactor for the Synthesis of Dimethylacetal", Ind. Eng. Chem. Res. 47(10): 3515-3524, 2008a.
Pereira C. S. M., S. P. Pinho, V. M. T. M. Silva and A. E. Rodrigues, "Thermodynamic equilibrium and reaction kinetics for the esterification of lactic acid with ethanol catalyzed by acid ion-exchange resin", Ind. Eng. Chem. Res. 47(5): 1453-1463, 2008b.
Pilgrim A., M. Kawase, F. Matsuda and K. Miura, "Modeling of the simulated moving-bed reactor for the enzyme-catalyzed production of lactosucrose", Chem. Eng. Sci. 61(2): 353-362, 2006.
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Silva V. M. T. M. and A. E. Rodrigues, "Synthesis of diethylacetal: thermodynamic and kinetic studies", Chem. Eng. Sci. 56(4): 1255-1263, 2001.
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PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 129
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6. Pervaporation Membrane Reactor
Abstract. Integrated membrane reactors are one of the most promising and sustainable
technologies to carry out equilibrium limited reactions. However, that integration leads to
lower process flexibility when trying to find suitable operating conditions for both reaction
and pervaporation process.
Pervaporation process using commercial microporous silica water selective membranes was
evaluated to contribute either for the separation of SMBR extract stream (water/ethanol
mixtures) or for the ethyl lactate process intensification by continuous pervaporation
membrane reactor (PVMR). Preliminary studies were performed in order to assess the
existence of membrane defects and mass transfer limitations, by studying the influence of
feed pressure and flowrate, respectively. After, in the absence of mass transfer limitations,
membrane performance was evaluated experimentally, at different composition and
temperature measuring the flux and selectivity of each species in binary mixtures
(water/ethanol, water/ethyl lactate and water/lactic acid). Thus, species permeances were
obtained for each experiment and correlated in order to account for the effect of temperature
and feed composition. Permeances of ethanol and ethyl lactate depend solely on the
temperature, following an Arrhenius equation; for water, its permeance follows a modified
Arrhenius equation taking into account also the dependence on the feed water content.
Mathematical models, considering concentration and temperature polarization, and non-
isothermal effects as well, were developed and applied to analyze the performance of batch
pervaporation and continuous pervaporation membrane reactor, in both isothermal and non-
isothermal conditions. The PVMR with 5 membranes in series, operating at 70ºC, leads to
98 % of lactic acid conversion and 96 % of ethyl lactate purity.
132 CHAPTER 6. Pervaporation Membrane Reactor
6.1 Introduction
In the past few years, the interest in the application of reactive separations to many chemical
processes has substantially increased. This is particularly true for equilibrium limited
reactions, where the removal of at least one of the reaction products shifts the equilibrium
towards the product formation. Among all the separation techniques, pervaporation is
becoming a promising technology, potentially useful in applications such as dehydration of
organic mixtures (Chapman et al., 2008; Slater et al., 2006; Van Hoof et al., 2006;
Yoshikawa et al., 2002), separation of organic mixtures (Lin et al., 2009; Smitha et al., 2004)
and removal of organic compounds from aqueous solutions (Khayet et al., 2008; Ohshima et
al., 2005). Aiming to produce esters, where water is a by-product, membranes suitable for
dehydration of organic mixtures can be applied for esters process intensification; being
polymeric (Hasanoglu et al., 2007; Krishna Rao et al., 2007; Namboodiri et al., 2006) and
ceramic (Asaeda et al., 2005; Casado et al., 2005; Li et al., 2009) membranes the most used.
Based on this, several works have been made regarding the use of pervaporation membrane
reactors for chemicals production (Feng and Huang, 1996; Lim et al., 2002; Park and Tsotsis,
2004; Peters et al., 2005; Zhu et al., 1996). In the literature, two main types of pervaporation
membrane reactors can be found; reactor and membrane housed in separate units (Figueiredo
et al., 2008; Korkmaz et al., 2009; Sanz and Gmehling, 2006) or membrane and reactor
incorporated into a single unit (de la Iglesia et al., 2007). Although the number of works
dealing with PVMR in the last years is significant, most of them use simplified mathematical
models to optimize and predict the behaviour of PVMR units. Usually, concentration and
temperature polarization effects on the pervaporation process are neglected, which can be
very significant under certain PVMR working conditions (Gómez et al., 2007).
In pervaporation processes, the transport of the components from the feed liquid mixture to
the vapor phase involves the following steps: (i) mass transfer from the feed bulk to the feed
membrane interface; (ii) partition of penetrants between feed and membrane; (iii) selective
transport (diffusion) through the membrane; and (iv) desorption into the vapor phase on the
permeate side. The partitioning and desorption steps are normally neglected and the
remaining steps are considered as the main contribution to the overall resistance to mass
transfer. The mass transfer resistance in membranes depends on its properties and also on the
chemical and physical properties of the feed components. In the past, the membrane materials
and dimensions were not optimized and, therefore, high membrane mass transfer resistance
was commonly observed. However, new developments in membrane materials and ultra-thin
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 133
composite membranes have led to much smaller membrane mass transfer resistances, which
are now mainly due to the diffusive transport at the boundary layer, like noticed in the
removal of volatile organic compounds from wastewaters (Wijmans et al., 1996) and in the
dehydration of cyclohexane (Ortiz et al., 2006). Diffusive transport depends on the
hydrodynamic conditions, physical properties of the fluid and of the solute, and the system
geometry. Several correlations based on Sherwood number for determination of the mass
transfer coefficient for transport in the boundary layer, blk , have been proposed over the years
on different membrane modules configurations (Bandini et al., 1997; Crowder and Cussler,
1998; Dotremont et al., 1994; Gekas and Hallstrom, 1987; Lipnizki and Field, 2001; Lipski
and Côté, 1990; Oliveira et al., 2001; Urtiaga et al., 1999).
Pervaporation is often considered as an isothermal process, but this process always induces a
temperature drop in the feed, since it involves vaporization. The heat transfer in pervaporation
involves: (i) heat transfer from the feed bulk to the feed membrane interface; (ii) heat transfer
through the membrane; and (iii) consumption of heat (vaporization followed by expansion) at
the permeate side of the membrane. In systems operating under laminar conditions, where the
membrane is thin and/or has high permeability, the temperature drop in the feed membrane
interface is considerable (Favre, 2003) and, therefore, the boundary layer heat transfer
resistance should be taken into account. The heat transfer coefficient in the boundary layer is
often determined by Nusselt correlations (Karlsson and Trägardh, 1996).
The ethyl lactate synthesis on pervaporation and vapour-permeation membrane reactors was
already studied by some authors. The two configurations adopted were: (i) batch reactor,
where the esterification reaction takes place, followed by a membrane for water removal, and
reflux of the retentate to the reactor (Benedict et al., 2003; Benedict et al., 2006; Rathin and
Shih-Perng, 1998; Wasewar et al., 2009) and (ii) membrane inside a batch reactor (Jafar et
al., 2002; Tanaka et al., 2002). In fact none of these studies considers a continuous integrated
membrane reactor for ethyl lactate production. Regarding the type of membranes tested,
polymeric membranes were used for pervaporation (Benedict et al., 2003; Benedict et al.,
2006; Rathin and Shih-Perng, 1998) and zeolites for vapour-permeation (Jafar et al., 2002;
Tanaka et al., 2002). In all of these studies, the pervaporation process is superficially
addressed; important membrane parameters, like selectivity and species permeances, at
different temperatures and feed concentrations were not determined. The most detailed
pervaporation study for the ethyl lactate system was performed by Delgado and co-authors for
binary and quaternary mixtures using a commercial polymeric membrane Pervap 2201 (from
134 CHAPTER 6. Pervaporation Membrane Reactor
Sulzer Chemtech) (2008; 2009, respectively). These studies, focused just on the separation,
still did not consider concentration and temperature polarization, and were not extended to the
reactive system.
Although most of studies involves the use of polymeric membranes that provide good
selectivity and flux, these membranes do not normally support reaction conditions (in terms
of concentrations, temperature, and pH, among others) and, therefore, are not appropriated for
applications under those conditions. Inorganic membranes, mainly those of silica and zeolites,
present better stability under acidic and high temperature conditions, and are the best
alternative to perform dehydration of a reaction medium. Since the commercial microporous
silica membrane (from Pervatech) revealed better selectivity and water flux than the
commercial membrane Pervap SMS (from Sulzer Chemtech) in the dehydration of aqueous
mixtures containing acetone and isopropanol (Casado et al., 2005), Pervatech membrane will
be considered in this work. Moreover, for the dehydration of ethanol, the Pervatech
membrane proved to have high flux and selectivity (Sommer and Melin, 2005).
The synthesis of ethyl lactate in a continuous integrated pervaporation membrane reactor,
using the commercial tubular membrane with higher flux and high selectivity (Pervatech), is
here, for the first time, implemented and evaluated. Furthermore, in order to better
characterize the pervaporation process and aiming to describe the PVMR unit, the effect of
feed pressure, flowrate, temperature and composition on the pervaporation performance is
studied by batch experiments (BP), testing the different binary mixtures involved in the
synthesis of ethyl lactate (ethanol/water, ethyl lactate/water and lactic acid/water).
Additionally, a new mathematical model accounting for the mass transport phenomena under
non-isothermal conditions is developed and applied to better understand and describe the
ethyl lactate production by means of the PVMR.
6.2 Experimental Section
6.2.1 Materials
The chemicals used were ethanol (>99.9% in water), lactic acid (>85% in water) and ethyl
lactate (>98% in water) from Sigma-Aldrich (U.K.). A commercial strong-acid ion-exchange
resin named Amberlyst 15-wet (A15-wet) (Rohm & Haas) was used as catalyst and
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 135
adsorbent. Commercial hydrophilic membrane supplied by Pervatech BV (The Netherlands)
was used. It is resistant for any solvent at any concentration, but sensitive to acidic and
alkaline media (preferred pH range from 2 up to 9) and so, exposure to inorganic acids or
caustic should be avoided. This membrane has a modified silica (methyl silica) selective layer
coated onto gamma alumina. The separation layer is applied inside of an asymmetric ceramic
tube that has an outer diameter of 10 mm, an inner diameter of 7 mm and a length of 50 cm. It
has an effective membrane area per tube of about 110 cm2. Two equal membrane modules
were used to perform the experiments.
6.2.2 Pervaporation Membrane Reactor Unit
The experiments were carried out in a pervaporation membrane reactor unit, which can
operate in batch (pervaporation studies) or in continuous mode (reaction pervaporation
experiments). This unit is equipped with temperature (TI) (type K thermocouple, accuracy of
about +/- 2.2ºC) and pressure sensors (PI) in order to monitor and register these two
parameters. The absolute pressure is measured through 2 analogue dials (accuracy of about
+/- 0.5 bar), filled with glycerine (Nuova Firma), while the pressure in the permeate side is
measured by means of 1 digital dial ceraphant-T PTC31 (Endress+Hausser) (accuracy of
about +/- 1 mbar). A schematic representation of the pervaporation membrane reactor unit is
shown in Figure 6.1. The temperature was controlled by a thermostated bath (Lauda,
Germany) with ethylene glycol/water solution that flows through the jackets of feed vessels 1
and 2; pressure was set at 2 bars by applying an overpressure of helium to the system in order
to prevent vaporization of feed mixture over the whole temperature range.
Pervaporation experiments
The feed was charged into the feed vessel 1 (1 L capacity) and heated to the desired
temperature. In order to heat the whole system (tubing and membranes) to that same
temperature, the feed mixture is after re-circulated over the membrane modules using a
positive displacement diaphragm pump (Hydra Cell G-03, Wanner International), in the
absence of vacuum on the permeate side. When the steady state is reached, the pervaporation
experiment starts by applying vacuum to the permeate side by means of a vacuum pump (Boc
Edwards, U.K.). During the whole run, all vapour permeated was condensed on two parallel
glass cold traps filled with liquid nitrogen. Finally, the collected permeate was defrosted,
weighted and analyzed. The duration of the experiment is conditioned by the trade-off
136 CHAPTER 6. Pervaporation Membrane Reactor
between ensuring the nearly constant feed composition and enough amount of permeate. To
verify the assumption of constant feed composition samples were collected before and after
each experiment.
Figure 6.1 Set-up of the pervaporation membrane reactor unit.
6.3 Pervaporation Studies
The experimental results of the pervaporation studies for the different binary mixtures
(ethanol/water, ethyl lactate/water and lactic acid/water) involved in the esterification reaction
between lactic acid and ethanol are presented in this section. The effect of the absolute feed
pressure, feed flowrate, operation temperature and water feed molar fraction onto the
membrane performance is evaluated. The membrane permeabilities were determined in
absence of mass transfer limitations in the boundary layer like shown by the preliminary
studies performed.
6.3.1 Pervaporation Transport
The pervaporation performance of the membrane was evaluated in terms of pervaporation
flux and separation factor (membrane selectivity). The process separation factor (α ) is
defined as:
i j
i j
y xx y
α = (6.1)
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 137
where ix is the liquid mole fraction of component i on the feed side and iy is the mole fraction
of component i on the permeate side.
The partial flux of one component through the membrane is given by:
,i perm i totJ w J= (6.2)
where totJ it the total permeation flux expressed in kg/(m2.s) and ,perm iw is the mass fraction of
component i on the permeate.
The solution-diffusion model (Wijmans and Baker, 1995) was successfully applied in the
description of solvent dehydration using microporous silica membranes (Ma et al., 2009;
Sommer and Melin, 2005). This model provides the following transport equation for the
permeation molar flux of a component through the membrane:
0,Q ( )i memb i i i i i permJ x p y Pγ= − (6.3)
where ,Qmemb i is the permeance of component i through the membrane (mol/(m2.s.Pa)), which
is equal to /iP ( iP is the permeability coefficient of component i (mol/(m.s.Pa)), and is
the thickness of the selective layer of the membrane), iγ is the activity coefficient (calculated
by the UNIQUAC model using the parameters determined in chapter 3), 0ip is the saturation
pressure of component i, permP is the total pressure on the permeate side and iy is the molar
fraction of component i in the vapor phase. The saturation pressure of pure components was
estimated by the Antoine equation and it is presented in Appendix B.
Some works consider the temperature influence on the total flux to measure an apparent
activation energy (Delgado et al., 2009; Khayet et al., 2008; Slater et al., 2006). However, in
this work, the activation energy of permeation is determined by an Arrhenius-type equation
for the permeance temperature dependence (Feng and Huang, 1997):
,, ,0 exp perm i
memb i memb
EQ Q
RT−⎛ ⎞
= ⎜ ⎟⎝ ⎠
(6.4)
138 CHAPTER 6. Pervaporation Membrane Reactor
where ,0membQ is the pre-exponential factor, ,perm iE is the activation energy of permeation,
which is a combination of activation energy of diffusion and the heat of adsorption on the
membrane ( , ,perm i D i sE E H= + Δ ), T is the absolute temperature and R is the ideal gas constant.
6.3.2 Preliminary Studies
6.3.2.1 Evaluation of the membrane quality
The driving force for the transport through the membrane is based on the species chemical
potential difference over the membrane and, theoretically, the absolute feed pressure affects
the chemical potentials via the Poynting factor, which might affect either the flux or the
selectivity. However, this influence is often negligible since the Poynting factor is one at low
pressures and, therefore, a way to detect membrane imperfections is by performing
pervaporation experiments at different feed pressures. If the permeate composition and the
total flux remains constant over the studied pressure range the membrane quality can be, in
principle, guaranteed (Pera-Titus et al., 2008).
The influence of the feed pressure onto the pervaporation membrane performance, is shown
in Figure 6.2, where the total permeation flux and permeate composition are represented as a
function of feed pressure, keeping constant the remaining conditions (temperature, flowrate,
water feed concentration, permeate pressure). The variations observed either on the permeate
compositions or on the total flux are within the experimental error, and, therefore, it is
possible to conclude that pervaporation is not affected by the feed pressure. This is
corroborated by other work (De Bruijn et al., 2007) where the effects of feed pressure on a
silica membrane performance were evaluated. Within the pressure range studied, the Poynting
factor is almost one for all species, and therefore these results indicate that the silica
membranes used are free of significant defects.
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 139
0.94
0.96
0.98
1.00
0.80
0.82
0.84
0.86
0.88
0.90
0.0 0.5 1.0 1.5 2.0 2.5
Perm
eate
Wat
er m
ole
fract
ion
J tot
(kg/
(h.m
2 ))
Absolute feed pressure (bar)
Total fluxPermeate composition
Figure 6.2 Pressure dependence of total permeation flux and of
permeates composition for the system ethanol/water. ( 321.15 , T K= , 0.183 0.001W Fx = ± , 20 permP mbar= ).
6.3.2.2 Evaluation of mass transfer limitations in the boundary layer
The effect of concentration polarization on the pervaporation process was studied for
water/ethanol mixtures, at constant feed water concentration and operating temperature,
varying the feed flowrate. Analyzing Figure 6.3, it is possible to conclude that for feed
flowrates higher than 19 L/h, the total flux remains constant, indicating absence of mass
transfer resistance from the bulk liquid phase to the feed-membrane interface. Therefore, the
remaining pervaporation experiments were performed at a feed flowrate of 20 L/h.
0.70
0.75
0.80
0.85
0.90
0.95
1.00
10 13 16 19 22 25
J tot
(kg/
(h.m
2 ))
Feed flowrate (L/h)
Figure 6.3 Total permeation flux as a function of feed flowrate ( 321.15 , T K= , 0.182 0.006W Fx = ± , 25 permP mbar= ).
140 CHAPTER 6. Pervaporation Membrane Reactor
6.3.3 Detailed Studies
6.3.3.1 Water/Ethanol System
The influence of feed composition at different operating temperatures on the total permeation
flux and on the permeate composition is shown in Figure 6.4 for the water/ethanol pair.
0.45
1.45
2.45
3.45
4.45
5.45
6.45
0.0 0.1 0.2 0.3 0.4 0.5 0.6
J tot
(kg/
(h.m
2 ))
Feed water mole fraction
T=321.15 K
T=336.15 K
T=344.15 K
0.95
0.96
0.97
0.98
0.99
1.00
0.0 0.1 0.2 0.3 0.4 0.5 0.6
Perm
eate
wat
er m
ole
facr
tion
Feed water mole fraction
T=344.15 K
T=321.15 K
T=336.15 K
Figure 6.4 Pervaporation performance for water/ethanol mixtures. (a) Influence of feed water mole fraction on total permeation flux at different operating temperatures; (b) Influence of feed water mole fraction on permeate composition at different operating temperatures.
As can be seen, the total permeation flux increases with water concentration (linearly) and
with the temperature in the feed (Figure 6.4a). From Figure 6.4b, it is also observed an
increase in water permeate mole fraction with the feed water concentration, but little
influence is noticed with the temperature.
6.3.3.2 Water/Ethyl lactate System
Like before, in the water/ethyl lactate system, it is observed an increase on the total flux with
the increase in the feed water mole fraction, except when the system was kept at 321.15 K,
where this effect of feed water composition on the total flux is not so significant (see Figure
6.5a). The temperature effect on the total flux is once again relevant, increasing with the
operation temperature, for the same feed composition, it is observed an increase around
167 % in the total flux. This is justified by the fact that the permeation driving force increases
with temperature. Figure 6.5b, shows that the water mole fraction in the permeate is almost
independent (varies from 0.996 to 0.999) from the feed water concentration and temperature,
considering the studied range.
(a) (b)
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 141
2.15
3.15
4.15
5.15
6.15
7.15
8.15
0.35 0.45 0.55 0.65 0.75
J tot
(kg/
(h.m
2 ))
Feed water mole fraction
T=321.15 KT=334.15 KT=343.15 K
0.990
0.992
0.994
0.996
0.998
1.000
0.35 0.45 0.55 0.65 0.75
Perm
eate
wat
er m
ole
fract
ion
Feed water mole fraction
T=321.15 KT=334.15 KT=343.15 K
Figure 6.5 Pervaporation performance for water/ethyl lactate mixtures. (a) Influence of feed water mole fraction on total permeation flux at different operating temperatures; (b) Influence of feed water mole fraction on permeate composition at different operating temperatures.
6.3.3.3 Water/Lactic acid System
Two pervaporation experiments were performed for the water/lactic acid mixtures with a feed
water molar fraction of 0.77, at two different temperatures (321.15 K and 343.15 K).
Experimentally, the permeate stream was only composed by water and, therefore, no more
experiments were performed for this mixture.
6.3.3.4 Membrane performance evaluation
For both ethanol/water and ethyl lactate/water systems, the flux increases with feed water
composition and temperature. It was shown that the flux depends strongly on the temperature
like already mentioned for dehydration in similar membranes (Casado et al., 2005; ten Elshof
et al., 2003). In the case of water/lactic acid mixtures, no lactic acid was detected in the
permeate side and no more measurements were made regarding this separation.
In the Figure 6.6 the process separation factor for the pairs water/ethanol and water/ethyl
lactate is plotted as a function of the temperature. It can be seen that the membrane presents
good selectivity towards water in both pairs, but the selectivity to water is higher in mixtures
with ethyl lactate most probably due to the higher molecular size of ethyl lactate compared
with that of ethanol. One indicative measure of the molecular size is given by the gyration
radius and their values presented in Table 6.1 support that hypothesis. However, according to
that, it was expected the permeation of lactic acid through the membrane. Naturally, this is
(a) (b)
142 CHAPTER 6. Pervaporation Membrane Reactor
not the only factor affecting selectivity; the lower lactic acid vapor pressure compared to all
other species (Table 6.1) significantly reduces the permeation driving force for this
component. Moreover, the affinity between species and membrane should be considered as a
secondary factor (the molecular diameter is the most important). This affinity is directly
related with the dipole moment of each component (Table 6.1): small dipole moment might
complicate the penetration of molecules into the hydrophilic silica layer. Comparing lactic
acid with ethyl lactate, the molecular sizes are similar, but the first has the lowest dipole
moment, which in addition to the lowest vapor pressure, leads to infinite membrane
selectivity towards water in lactic acid mixtures.
Table 6.1 Physical properties of the different species (water, ethanol, ethyl lactate and lactic acid) (Delgado et al., 2008).
Molecule Radius of gyration ( A ) Dipole moment (Debyes)
Water 0.615 1.8497 Ethanol 2.259 1.6908
Ethyl lactate 3.622 2.4000 Lactic acid 3.298 1.1392
0
200
400
600
800
1000
1200
320 325 330 335 340 345 350
Sepa
ratio
n fa
ctor
Temperature (K)
water/ethanol
water/ethyl lactate xW,F = 0.494 ± 0.008
xW,F = 0.435 ± 0.006
Figure 6.6 Influence of the temperature on the separation factor for the binary
mixtures water/ethanol and water/ethyl lactate.
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 143
6.3.4 Parameter Estimation
The pervaporation process design requires the knowledge of the permeance of each
component as function of temperature (Equation 6.4). However, there is evidence that the
feed water content affects permeance (Delgado et al., 2009) and therefore, both factors are
needed to be accounted for.
6.3.4.1 Permeance temperature dependence
Experimental permeance for each species can be calculated using the experimental
information found so far in Equation 6.3, simultaneously with the activity coefficients
calculated by the UNIQUAC model. Those values are presented in Figure 6.7.
-3.0
-2.5
-2.0
-1.5
-1.0
-0.5
0.0
2.85 2.90 2.95 3.00 3.05 3.10 3.15
ln Q
mem
b, w
1000/T (K-1)
-9.0
-8.5
-8.0
-7.5
-7.0
-6.5
-6.0
2.85 2.90 2.95 3.00 3.05 3.10 3.15
ln Q
mem
b, E
th
1000/T (K-1)
-9.0
-8.0
-7.0
-6.0
-5.0
-4.0
-3.0
-2.0
2.90 2.95 3.00 3.05 3.10 3.15
ln Q
mem
b, E
L
1000/T (K-1) Figure 6.7 Temperature dependence of species permeances (mol/(min.dm2.bar)) and
linear fittings: (a) water; (b) ethanol; (c) ethyl lactate.
From the slope and intercept of the linear regression, the activation energy of permeation and
the pre-exponential factor are determined for each species, like presented in Table 6.2.
(a) (b)
(c)
144 CHAPTER 6. Pervaporation Membrane Reactor
Although, the permeation flux increases with temperature due to the increasing driving
forces, the membrane permeability decreases with the temperature like the negative values of
the activation energies of permeation indicates (Table 6.2). As mentioned previously, the
activation energy is a sum of the diffusion activation energy and the heat of adsorption on the
membrane, indicating that the permeation of water, ethanol and ethyl lactate are governed by
the adsorption. Similar results were found for water/ethanol permeation through silica
microporous membranes (Ma et al., 2009).
Table 6.2 Pervaporation parameters of Equation 6.4 and the mean relative deviation (MRD).
Component Qmemb,0 (mol/(min.dm2.bar)) Eperm (kJ/mol) MRD (%) Ethanol 1.41×10-7 -22.60 14.51
Ethyl lactate 1.12×10-4 -10.42 24.13 Water 1.78×10-3 -13.93 13.94
The error introduced considering composition invariant permeances can be calculated from
the mean relative deviation (MRD), defined by Equation 6.5.
exp
, ,exp
exp ,exp
1 100%i calc i
n i
J JMRD
n J
⎛ ⎞−⎜ ⎟= ×⎜ ⎟⎝ ⎠∑ (6.5)
In order to decrease the deviations between theoretical and experimental fluxes, parameter
estimation considering also composition dependence will be addressed in following sub-
section.
6.3.4.2 Permeance temperature and water content dependence
The strategy developed is based on the linearization of equation 6.4 at each composition.
Considering water/ethanol and water/ethyl lactate mixtures, the permeances of water as a
function of temperature, at a constant feed water mole fraction, are shown in Figure 6.8 and
Figure 6.9, respectively. Except for an ethyl lactate aqueous solution with 68 % of water
content, where the activation energy is positive, in all other situations the activation energy of
permeation is negative has previously determined. This might indicate that, for water/ethyl
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 145
lactate mixtures, the water permeance at high feed water concentrations is controlled by
diffusion instead of adsorption.
-1.90
-1.70
-1.50
-1.30
-1.10
-0.90
-0.70
2.85 2.90 2.95 3.00 3.05 3.10 3.15
ln Q
mem
b, W
1000/T (K-1)
-1.70
-1.60
-1.50
-1.40
-1.30
-1.20
-1.10
2.85 2.90 2.95 3.00 3.05 3.10 3.15ln
Qm
emb,
W
1000/T (K-1)
-1.50
-1.40
-1.30
-1.20
-1.10
2.90 2.95 3.00 3.05 3.10 3.15
ln Q
mem
b, W
1000/T (K-1)
-1.60
-1.50
-1.40
-1.30
-1.20
2.85 2.90 2.95 3.00 3.05 3.10 3.15
ln Q
mem
b, W
1000/T (K-1) Figure 6.8 Temperature dependence of water permeances (mol/(min.dm2.bar)) and
linear fittings (water/ethanol mixtures): (a) , 0.105 0.001W Fx = ± ; (b) , 0.183 0.003W Fx = ± ; (c) , 0.298 0.006W Fx = ± (d) , 0.492 0.005W Fx = ± .
(a) (b)
(d)(c)
146 CHAPTER 6. Pervaporation Membrane Reactor
-1.50
-1.40
-1.30
-1.20
-1.10
-1.00
2.90 2.95 3.00 3.05 3.10 3.15
ln Q
mem
b, W
1000/T (K-1)
-1.14
-1.12
-1.10
-1.08
-1.06
-1.04
-1.02
-1.00
2.90 2.95 3.00 3.05 3.10 3.15
ln Q
mem
b, W
1000/T (K-1)
-1.18
-1.16
-1.14
-1.12
-1.10
2.95 3.00 3.05 3.10 3.15
ln Q
mem
b, W
1000/T (K-1) Figure 6.9 Temperature dependence of water permeances (mol/(min.dm2.bar)) and linear
fittings (water/ethyl lactate mixtures): (a) , 0.435 0.006W Fx = ± ; (b) , 0.564 0.015W Fx = ± ; (c) , 0.680 0.003W Fx = ± .
The pre-exponential factors as well as the activation energies of permeation calculated from
Figure 6.8 and Figure 6.9 are presented in Table 6.3. Independently of binary mixture
considered, the representation of those parameters as function of the water feed mole fraction
is shown in Figure 6.10.
Table 6.3 Pre-exponential factor and activation energy for different feed water contents.
Parameters Water/ethanol mixtures Water/ethyl lactate mixtures
Water molar (%) 10.5 18.3 29.8 49.2 43.2 56.4 68.0
Eperm,W (kJ/mol) -30.24 -17.56 -17.52 -7.84 -13.56 -4.31 3.46
Qmemb0,W (mol/min.dm2.bar) 4.62×10-6 4.55×10-4 4.47×10-4 1.47×10-2 2.00×10-3 7.12×10-2 1.13
(a) (b)
(c)
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 147
0.0
0.2
0.4
0.6
0.8
1.0
1.2
0.0 0.2 0.4 0.6 0.8
Qm
emb,
0(m
ol/(m
in.d
m2 .
bar))
Feed water mole fraction
-35-30-25-20-15-10-505
10
0 0.2 0.4 0.6 0.8
E per
m(k
J/m
ol)
Feed water mole fraction Figure 6.10 Influence of feed water mole fraction on: (a) pre-exponential factor;
(b) activation energy of permeation.
Analysing Figure 6.10, it is possible to conclude that the pre-exponential factor and water
permeance dependencies on feed water mole fraction are well described by exponential and
linear functions, respectively, leading to the following expressions:
6 2,0 1.967 10 exp(18.64 ) (mol/(min.dm . ))memb WQ x bar−= × (6.6)
, 50.377 32.326 (KJ/mol)perm w WE x= − (6.7)
These expressions were combined in a final empirical correlation that describes the
permeance of water as a function of the temperature and water feed content:
6 2,
50377 323261.967 10 exp(18.64 )exp (mol/(min.dm . ))Wperm W W
xQ x barRT
− −⎛ ⎞= × −⎜ ⎟⎝ ⎠
(6.8)
The error between experimental and theoretical permeances calculated by Equation 6.8 is of
10.35 % (MRD), which is about 26 % smaller than the one obtained when just the
temperature influence was considered. Although derived from binary mixtures, expression 6.8
can be applied to estimate the water permeance in quaternary mixtures, since it depends only
on water content no matters the remaining constituents. This is in agreement with
experimental pervaporation results using binary and quaternary mixtures involved in the ethyl
lactate synthesis, since for the same temperature and water feed content, the value of water
permeance is almost the same for binary or quaternary mixtures (Delgado et al., 2009).
Therefore, it can be stated that the water transport is barely affected by the presence of the
other components supporting the validity of Equation 1.8. For ethanol and ethyl lactate, no
(a) (b)
148 CHAPTER 6. Pervaporation Membrane Reactor
relation was found between their permeances in the membrane and the feed contents. Thus,
the parameters of Table 6.2 were used to determine the permeances of these species at
different operating temperatures and water feed contents.
6.3.4.3 Estimation of the boundary layer mass transfer coefficient (kbl)
In pervaporation processes, in addition to the permeation resistance in the membrane there is
also the resistance in the boundary layer (concentration polarization). This can be
conveniently represented by the resistance in series model, where the overall resistance to
transport is the sum of boundary layer and membrane resistances. The resistance in series
equation for pervaporation was derived by Wijmans and collaborators (1996):
0
,
, ,
1 1 i i mol ib
ov i memb i F
p Vk Q av
γ= + (6.9)
in which ,ov ik is a global membrane mass transfer coefficient 2(mol/(s.m . ))bar , that combines
the resistance due to the diffusive transport in the boundary layer with the membrane
resistance, Vmol,i is the molar volume of component i 3( / )m mol , bbl FK av= where Fv is the
feed liquid velocity ( / )m s . Equation 6.9 will be used to determine the mass transfer
resistance in the boundary layer.
The pervaporation data experimentally obtained for water/ethanol mixtures using different
feed flowrates was used to plot the inverse of the global membrane mass transfer coefficient
(1/ ovk ) of water and ethanol as a function of 1/ bFv , as shown in Figures 6.11 and 6.12,
respectively. The value of parameter b was chosen in order to keep the data points on a
straight line and also minimizing the difference between the inverse of the intercept of the
line and the experimental permeance measured in absence of mass transfer limitations on the
boundary layer (being the best fit for b=0.97), while the parameter a was obtained from the
slope of this line. By this analysis it was possible to obtain the following expressions to
determine the boundary layer mass transfer coefficients for both species (ethanol and water):
0.975, ( / ) 7.27 10 ( / )bl W FK m s v m s− ⎡ ⎤= × ⎣ ⎦ (6.10)
0.977, ( / ) 3.56 10 ( / )bl Eth FK m s v m s− ⎡ ⎤= × ⎣ ⎦ (6.11)
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 149
1.4
1.5
1.6
1.7
1.8
1.9
2.0
5 6 7 8 9 10
1/k o
v,W
((m2 .b
ar.s
)/mol
)
1/vFb (m/s)-b
Figure 6.11 ,1/ ov Wk versus 1/ bFv , b=0.97.
600
700
800
900
1000
5 6 7 8 9 10
1/k o
v,Et
h((m
2 .ba
r.s)/m
ol)
1/vFb (m/s)-b Figure 6.12 ,1/ ov Ethk versus 1/ b
Fv , b=0.97.
6.4 Modelling
6.4.1 Batch Pervaporation Model
The mathematical model developed to describe the behaviour of the batch pervaporation
membrane (BPM) considers:
- Plug flow for the bulk fluid phase;
- Total feed volume inside the tank and the retentate velocity variations (inside membrane)
due to permeation of components;
- Concentration polarization, where the resistance due to the diffusive transport in the
boundary layer is combined with the membrane resistance in a global membrane resistance;
- Non-isothermal operation due to heat consumption for species vaporization;
- Temperature polarization.
Following these assumptions the BPM model equations are:
Feed tank mass balance to component i
( ),, ,
f iret ret i f f i
d VCQ C Q C
d t= − (6.12)
150 CHAPTER 6. Pervaporation Membrane Reactor
where t is the time variable, V is the volume of the feed thank, fQ is the flowrate fed to the
membrane modules and retQ is the flowrate at the end of the membrane modules, fC and retC
are the liquid phase concentration fed to the membrane and at the end of the membrane
modules, respectively.
Feed volume variation
ret fdV Q Qd t
= − (6.13)
Retentate mass balance to component i
( ),, 0ret iret im i
vCCA J
t z∂∂
+ + =∂ ∂
(6.14)
where z is the axial coordinate at the membrane modules, v is the superficial velocity, mA is
the membrane area per unit membrane modules volume and iJ is the permeate molar flux of
species i, through the membrane, defined as:
0,k ( )i ov i i i i i permJ x p y Pγ= − (6.15)
where ,kov i is the global membrane mass transfer coefficient, that combines the resistance due
to the diffusive transport in the boundary layer with the membrane resistance (Wijmans et al.,
1996):
0,
, ,
1 1 i i mol i
ov i memb i bl
p Vk Q K
γ= + (6.16)
in which Vmol,i is the molar volume of component i and blK is the boundary layer mass transfer
coefficient. For laminar flow and Graetz number ( 2 /( )int md v D L ) much greater than one, the
mass transfer coefficient for transport in the boundary layer, blk , is determined by the Lévêque
correlation (Lévêque, 1928):
0.330.33 0.33 int1.62 Re dSh Sc
L⎛ ⎞= ⎜ ⎟⎝ ⎠
(Re 2300)< (6.17)
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 151
where int /bl mSh k d D= , int /Re d vρ η= and /( )mSc Dη ρ= are the Sherwood, Reynolds and
Schmidt numbers, respectively, mD is the solute diffusivity in the boundary layer, intd is the
inside diameter of the membrane, L is the membrane length, ρ is the density and η is the
viscosity. The accuracy of the Lévêque correlation to estimate the mass transfer coefficient in
the laminar regime has been validated experimentally by several works (Crowder and
Cussler, 1998; Wickramasinghe et al., 1992). The prediction of the solute diffusivity was
made using the Perkins and Geankoplis method (Perkins and Geankoplis, 1969). Further
details concerning its calculation can be found in Chapter 4.
The molar fraction of component i on the vapor phase (permeate side), iy , is defined as:
1
ii n
ii
JyJ
=
=
∑ (6.18)
Fluid velocity variation in the membrane feed side calculated from the total mass balance
,1
n
m i mol ii
dv A J Vdz =
= − ∑ (6.19)
where n is the total number of components.
Retentate heat balance
( ), ,, ,1 1
0n n
p i p iret i ret i m F mi i
T TC C vC C A h T Tt z= =
∂ ∂+ + − =
∂ ∂∑ ∑ (6.20)
where ,p iC is the liquid heat capacity of component i, T is the absolute temperature in the
feed side of the membrane, mT is the membrane temperature and Fh is the heat transfer
coefficient in the liquid boundary layer.
Membrane heat balance
int int2 2 2 2
1int int int int
( )( / 2) ( / 2)
nV
F m i ii
d dh T T H Jr r r r
δδ δ =
+− = Δ
+ − + − ∑ (6.21)
152 CHAPTER 6. Pervaporation Membrane Reactor
where intr is the internal radius of the membrane, δ is the membrane thickness and ViHΔ is the
heat of vaporization of species i. The heat transport coefficient was estimated by the Sieder-
Tate correlation, valid for laminar pipe flow (Welty et al., 2008):
0.140.33int1.86 Re Pr b
w
dNuL
ηη⎛ ⎞⎛ ⎞= ⎜ ⎟⎜ ⎟
⎝ ⎠ ⎝ ⎠ (6.22)
where int /FNu h d λ= , Pr /pCη λ= are the Nusselt and Prandtl numbers, respectively, bη and
wη are the viscosity of the liquid in the feed and in the membrane wall, respectively and λ is
the thermal conductivity.
Initial boundary conditions:
, , ,00 : f i ret i it C C C= = = (6.23a)
0V V= (6.23b)
FT T= (6.23c)
0 : Fz T T= = (6.24a)
Fv v= (6.24b)
, ,ret i f iC C= (6.24c)
where subscripts 0 and F refer to initial state and membrane feed conditions, respectively.
6.4.2 Pervaporation Membrane Reactor Model
A mathematical model was also developed to describe the behaviour of the tubular
pervaporation membrane reactor that similarly to the BPM model considers:
- Concentration polarization, where the resistance due to the diffusive transport in the
boundary layer is combined with the membrane resistance in a global membrane resistance;
- Temperature polarization;
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 153
Additionally, it also takes in account:
- Axial dispersion flow for the bulk fluid phase;
- External and internal mass transfer for adsorbable species combined in a global particle
resistance;
- Non-isothermal operation due to heat effects during species vaporization and reaction
(slightly endothermic);
- Velocity variations due to permeation of components and adsorption/desorption rates;
- Constant column length and packing porosity.
Following this assumption the PVMR model equations are:
Bulk fluid mass balance to component i:
( ) ( ), ,(1 ) 3ii i m
L i i p i ax T ip
u CC x AK C C D C Jt z r z z
εε ε
∂ ⎛ ⎞∂ ∂− ∂+ + − = −⎜ ⎟∂ ∂ ∂ ∂⎝ ⎠
(6.25)
where iLK , is the global mass transfer coefficient of the component i, ε is the bed porosity,
axD , and u are the axial dispersion coefficient and the interstitial velocity, respectively, pr is
the particle radius, pC is the average particle concentration and all the other variables were
already defined. The determination of the global mass transfer coefficient ( LK ) is presented
in detail in Chapter 4 and the axial dispersion coefficient ( axD ) is estimated from the
empirical correlation (Butt, 1980) valid for liquids in packed beds:
0.480.2 0.011RePeε = + (6.26)
in which int / axPe d u D= and int /Re d uρ η= are the Peclet and Reynolds numbers,
respectively.
The permeate flux of membrane is defined by Equation 6.15 (BPM model).
Interstitial fluid velocity variation calculated from the total mass balance
( ) ( ),, ,1 1
1 3 n nm
p iL i mol i i ii ip
Adu K V C C Jdz r
εε ε= =
−= − − −∑ ∑ (6.27)
154 CHAPTER 6. Pervaporation Membrane Reactor
where Vmol,i is the molar volume of component i and n is the total number of components.
Pellet mass balance to component i
( ) ( )ipbii
pip
pipiiLp
Crt
qt
CCCK
r ,,
,, 1)1(3
ερν
εε−
−∂∂
−+∂
∂=− (6.28)
where iν is the stoichiometric coefficient of component i , bρ is the bulk density, pε the
particle porosity, iq is the average adsorbed phase concentration of species i in equilibrium
with ipC , , and r is the kinetic rate of the chemical reaction relative to the average particle
concentrations in the fluid phase. The reaction rate and adsorption isotherms are those
determined in Chapters 3 and 4, respectively.
Retentate heat balance
( ), ,1 1
0n n
m bp i p ii i F m r
i i
AT TC C uC C h T T H rt z
ρε ε= =
∂ ∂+ + − +Δ =
∂ ∂∑ ∑ (6.29)
where rHΔ is the reaction enthalpy, determined in Chapter 3. It must be considered that the
heat of adsorption was neglected since while some species are being adsorbed, others are
being desorbed and there is compensation on the heat released or absorbed, respectively.
The equation of the membrane heat balance is the one represented in the BPM model
(Equation 6.21).
Initial and Danckwerts boundary conditions
0=t : , ,0p ii iC C C= = , ,0i iq q= and FT T= (6.30)
0=z : ,0
ii ax i F
z
CuC D uCz =
∂− =
∂ (6.31a)
0u u= (6.31b)
FT T= (6.31c)
cLz = : 0i
z Lc
Cz =
∂=
∂ (6.31d)
where F and 0 refer to the feed and initial states, respectively.
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 155
The viscosities, heat capacities, thermal conductivities and heats of vaporization of pure
components were calculated for each temperature by the expressions presented in Appendix
B. The mixture heat capacity was estimated assuming linear mole fraction averages, while the
mixture density and thermal conductivity were estimated assuming linear mass fraction
averages. The methods used to predict binary and multi-component mixture viscosities were
presented in detail in Chapter 4. Details on numerical solution are the same presented in
Chapter 5.
6.5 Results and Discussion
6.5.1 Batch Pervaporation
Within the mathematical model proposed for the batch pervaporation, the mass transfer
coefficient in the boundary layer is, for all the species, estimated through the Lévêque
correlation. However, its accuracy should be validated experimentally. In Section 6.3.4.3, the
boundary layer mass transfer coefficients, for water and ethanol, were determined from the
experimental data (Equations 6.10 and 6.11) and will be applied in the BPM model. The
water permeation fluxes were calculated either by using the experimental mass transfer
coefficient in the boundary layer (Equations 6.10 and 6.11) or using the Lévêque correlation
(Equation 6.17). As can be observed in Figure 6.13, there is a good agreement between the
water permeation flux estimated using the experimental mass transfer coefficients with the
one using the Lévêque correlation, proving its accuracy in the prediction of the boundary
layer mass transfer coefficients. Besides, small deviations are observed between the
experimental fluxes and the ones determined by the BPM model.
In order to validate the BPM non-isothermal model, the dehydration of ethanol and ethyl
lactate aqueous solutions was studied. The evolution of water mole fraction in the retentate
stream is in agreement with the experimental data: for both ethanol and ethyl lactate cases the
retentate composition after 15 and 10 minutes, respectively, is similar to the theoretical
values, as shown in Figure 6.14. In terms of temperature drop, experimentally it was not
observed any temperature variation for ethanol dehydration, while it has dropped 2ºC for the
ethyl lactate experiment. According to the simulation it would be expected a decrease of 2
and 4ºC for ethanol and ethyl lactate dehydrations, respectively. This deviation might be due
to experimental error of the thermocouple used (accuracy of 2.2ºC).
156 CHAPTER 6. Pervaporation Membrane Reactor
0.0
0.5
1.0
1.5
2.0
2.5
0.0 0.5 1.0 1.5 2.0 2.5
J W(m
ol/(h
.dm
2 )
JW,exp (mol/(h.dm2)
Estimated mass transfer coefficient (Lévêque correlation)
Experimental mass transfer coefficient
Figure 6.13 Experimental water permeation flux as a function of water permeation flux
determined by the BPM model with the Kbl estimated (Lévêque correlation) and determined from experimental data.
334
335
336
337
0.175
0.177
0.179
0.181
0.183
0.185
0.187
0.189
0 2 4 6 8 10 12 14
Tem
pera
ture
(K)
Wat
er m
olar
frac
tion
Time (min)
Feed (Experimental)Retentate (Experimental)Retentate (BPM model)Temperature (BPM model)
338
339
340
341
342
343
344
345
0.535
0.539
0.543
0.547
0.551
0.555
0.559
0 2 4 6 8 10
Tem
pera
ture
(K)
Wat
er m
olar
frac
tion
Time (min)
Feed (Experimental)Retentate (Experimental)Retentate (BPM model)Temperature (BPM model)
Figure 6.14 Evolution of water composition on retentate and temperature predicted by
the non-isothermal BPM model: a) dehydration of 81 % of ethanol in aqueous solution at 336 K; b) dehydration of 44 % of ethyl lactate in aqueous solution at 344 K.
6.5.2 Pervaporation Membrane Reactor
The performance of the pervaporation membrane reactor unit, packed with A15-wet resin in
the lumen side of the tubular membranes (where the active layer of the silica membranes is
placed) was evaluated by simulation. It was considered that the resin was initially saturated
with ethanol and then it was fed with a mixture of ethanol and 85 wt. % lactic acid aqueous
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 157
solution. The permeation fluxes were estimated using the expressions previously obtained in
section 6.3.3 and a summary of the parameters used in the simulations is presented in Table
6.4.
Table 6.4 Parameters used in the simulations.
Parameters
Feed temperature 323.15 K Feed composition , , W,F0.3546; 0.3424; x =0.3030Eth F LA Fx x= =
Feed flowrate 1.0 mL/min Permeate pressure 10 mbar Bed porosity 0.424 Bulk density 374.0 g/L Length of the bed 100 cm Internal diameter 0.7 cm
The PVMR unit was evaluated considering isothermal and non-isothermal operation and its
performance was compared with the one of a fixed bed reactor (FBR) in the same operational
conditions. The concentration histories at the end of the PVMR and FBR, considering
isothermal operation, are shown in Figure 6.15. It can be observed that the enhancement
introduced by the water removal through the membranes is significant for the ethyl lactate
production, where a 69 % lactic acid conversion was achieved in the PVMR unit, at the
steady-state, while in the FBR the conversion obtained was just 29 %.
158 CHAPTER 6. Pervaporation Membrane Reactor
02468
1012141618
0 20 40 60 80 100
C (m
ol/L
)
Time (min)
EthanolLactic acidEthyl lactateWater
02468
1012141618
0 20 40 60 80 100
C (m
ol/L
)
Time (min)
EthanolLactic acidEthyl lactateWater
Figure 6.15 Concentration histories at the reactor outlet, considering isothermal operation: a) PVMR; b) FBR.
02468
1012141618
0 20 40 60 80 100
C (m
ol/L
)
Time (min)
EthanolLactic acidEthyl lactateWater
02468
1012141618
0 20 40 60 80 100
C (m
ol/L
)
Time (min)
EthanolLactic acidEthyl lactateWater
Figure 6.16 Concentration histories at the reactor outlet, considering non-isothermal
operation: a) PVMR; b) FBR.
Considering, alternatively, a non-isothermal operation (see Figure 6.16b), the lactic acid
conversion at steady state of the FBR is about 29 %, much better than 11 % found for the
PVMR (Figure 6.16a). This low performance of the PVMR is due to the temperature drop
noticed in the bulk, around 36ºC, while only 2ºC was noticed for the FBR (Figure 6.17). This
slightly decrease in the FBR is due to the heat needed to the reaction only (endothermic
reaction), while for the PVMR there is a large heat consumption to vaporize the species.
Since the flowrate is very small, the heat capacitance provided by the liquid stream is low and
therefore its temperature is drastically decreased, leading to lower reaction kinetic rates,
higher mass transfer resistances and lower water permeation fluxes through the membranes.
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 159
280
290
300
310
320
330
0 20 40 60 80 100 120 140
T (K
)
Time (min)
FBRPVMR
Figure 6.17 Temperature histories at the outlet of the FBR and of the PVMR.
Clearly, to operate the PVMR for efficient ethyl lactate production, it is necessary to provide
the heat required for vaporization and reaction, operating in isothermal conditions. As stated
before, the silica membranes used in this work have the selective layer coated inside the
membrane tube. Therefore, the most suitable way to supply heat to the retentate liquid is
introducing a heated sweep gas in the permeate side instead of using vacuum. However, when
the membrane selective layer is coated on the external side of the membrane tube (shell side),
the heat can be supplied through an appropriate heated solution re-circulated through jacketed
modules; in this situation, the heat is rapidly transferred to the retentate liquid stream.
Assuming that the PVMR unit could operate isothermally replacing vacuum by a heated
sweep gas, it is possible to determine by simulation the number of membranes connected in
series needed to maximize the lactic acid conversion of the same feed processed before. For
an operating temperature of 50ºC (same conditions from Table 6.4), it is possible to achieve
93 % of lactic acid conversion and 84 % of ethyl lactate purity when using a 250 cm long
membrane reactor (5 tubular membranes, effective area of about 550 cm2), as it can be seen in
Figure 6.18.
160 CHAPTER 6. Pervaporation Membrane Reactor
02468
1012141618
0 40 80 120 160 200 240
C (m
ol/L
)
Time (min)
EthanolLactic acidEthyl lactateWater
Figure 6.18 Concentration histories at the outlet of the PVMR for a bed
length of 250 cm at 323.15 K.
Trying to further enhance the separation performance, as well as the reaction rate, the PVMR
temperature was increased to 70ºC. In this case, it was obtained a lactic acid conversion of
98 % and an ethyl lactate purity of 96 %, as shown in Figure 6.19. From the analysis of the
internal concentration profiles on the retentate side, shown in Figure 6.20, it is concluded that
using only two membranes it is possible to get about 90 % of lactic acid conversion, but only
82 % of ethyl lactate purity; being necessary 3 more membranes to maximize both lactic acid
conversion and ethyl lactate purity.
02468
1012141618
0 40 80 120 160 200 240
C (m
ol/L
)
Time (min)
EthanolLactic acidEthyl lactateWater
Figure 6.19 Concentration histories at the outlet of the PVMR at 343.15 K
(L=250 cm).
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 161
0
2
4
6
8
10
0 0.2 0.4 0.6 0.8 1
C (m
ol/L
)
Z
EthanolLactic acidEthyl lactateWater
Figure 6.20 Concentration profiles at steady state at 343.15 K.
These results demonstrate that the PVMR has a great potential for the ethyl lactate
production, where high conversions and purities can be obtained, when this reactor is
operated under isothermal conditions.
6.6 Conclusions
Commercial hydrophilic silica membrane from Pervatech BV (The Netherlands) was
evaluated for the dehydration of ethanol, ethyl lactate and lactic acid, in the temperature range
varied from 48ºC to 72ºC. First pervaporation studies indicate that the membranes have no
major imperfections since the total flux and water selectivity is barely affect by absolute feed
pressure. The influence of hydrodynamic conditions on the membrane polarization was
analyzed, and for velocity values higher than 0.14 m/s polarization effects are eliminated. The
effect of feed temperature and composition on the pervaporation performance was evaluated
by batch experiments. It was concluded that the microporous silica membranes have high flux
and high selectivity for water, while ethanol and ethyl lactate permeation is reduced and lactic
acid does not permeate at all. In summary, the permeances for all species through the
microporous silica membranes, as a function of temperature and feed water content, are
described by the following equations: 3
7,
22.60 101.41 10 expmemb EthQRT
− ⎛ ⎞×= × ⎜ ⎟
⎝ ⎠2/( min)mol dm bar
162 CHAPTER 6. Pervaporation Membrane Reactor
, 0memb LAQ = 2/( min)mol dm bar
34
,10.42 101.12 10 expmemb ELQ
RT− ⎛ ⎞×
= × ⎜ ⎟⎝ ⎠
2/( min)mol dm bar
6,
50377 323261.967 10 exp(18.64 )exp Wmemb W W
xQ xRT
− −⎛ ⎞= × −⎜ ⎟⎝ ⎠
2/( min)mol dm bar
A mathematical model was developed for the batch pervaporation membrane, considering (i)
plug flow for the bulk fluid phase; (ii) total feed volume inside the tank and retentate velocity
inside the membrane variations due to permeation of components; (iii) concentration
polarization, where the resistance due to the diffusive transport in the boundary layer is
combined with the membrane resistance in a global membrane resistance; (iv) non-isothermal
operation due to heat consumption for species vaporization; and (v) temperature polarization.
The batch pervaporation membrane model was validated experimentally and, therefore, it was
extended to the integrated pervaporation membrane reactor packed with the catalyst
Amberlyst-15wet. This model was used to evaluate the performance of the PVMR in both
isothermal and non-isothermal conditions. It was concluded that non-isothermal operation
worsens the performance of the PVMR, being even worse than that obtained in the fixed bed
reactor. In isothermal conditions, the PVMR is a very attractive solution leading to a lactic
acid conversion of 90 % and ethyl lactate purity of 82 %, for the PVMR set-up designed in
this work (100 cm of length, 2 membrane modules) operating at 70ºC. For near lactic acid
depletion (98 % conversion), it is produced ethyl lactate with 96 % purity if the membrane
modules has 250 cm (5 membranes in series), as indicated by the model predictions.
6.7 Notation
mA membrane area per unit membrane modules volume (m2/m3)
C liquid phase concentration (mol/m3)
fC liquid phase concentration in the thank (mol/m3)
pC average particle concentration (mol/m3particle)
pC liquid heat capacity (J/(mol.K))
retC liquid phase concentration in the retentate (membrane feed side) (mol/m3)
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 163
axD axial dispersion coefficient (m2/s)
intd internal diameter of the membrane (m)
mD solute diffusivity in the boundary layer (m2/s)
DE activation energy of diffusion (J/mol)
permE activation energy of permeation (J/mol)
Fh heat transfer coefficient in the liquid boundary layer (W/K)
sHΔ heat of adsorption (J/mol)
VHΔ heat of vaporization (J/mol)
rHΔ enthalpy of reaction (J/mol)
J permeate flux (mol/(m2s))
totJ total permeate flux (mol/(m2s))
blK boundary layer mass transfer coefficient (m/s)
LK global mass transfer coefficient
ovk global membrane mass transfer coefficient (mol/(m2sPa))
L column length (m)
n total number of components
Nu Nusselt
P permeability coefficient (mol/(m.s.Pa)) 0p saturation pressure (s)
permP total pressure on the permeate side (s)
Pr Prandtl
q solid phase concentration in equilibrium with the fluid concentration inside the
particle (mol/m3)
Qmemb permeance (mol/(m2sPa))
,0membQ pre-exponential factor (mol/(m2sPa))
fQ flowrate fed to the membrane modules (m3/s)
retQ flowrate at the exit of the membrane modules (m3/s)
r rate of reaction (mol kg-1 s-1)
R gas constant (J/(mol.K))
164 CHAPTER 6. Pervaporation Membrane Reactor
intr internal radius of the membrane (m)
pr particle radius (m)
Re Reynolds
Sc Schmidt
Sh Sherwood
t time variable (s)
T temperature in the feed side of the membrane (K)
mT membrane temperature (K)
u interstitial velocity (m/s)
V volume of the feed thank (m3)
v superficial velocity (m/s)
molV molar volume (m3/mol)
w mass fraction
ix liquid molar fraction of component i in the feed side
iy molar fraction in the vapor phase of component i
z axial coordinate at the membrane modules (m)
Greek letters
iγ activity coefficient
ε bulk porosity
pε particle porosity
iυ stoichiometric coefficient of component i
bρ bulk density (kg/m3bed)
ρ fluid density (kg/m3)
μ viscosity (Pa.s)
δ membrane thickness (m)
λ thermal conductivity (W/(m.K))
thickness of the selective layer of the membrane (m)
α process separation factor
Subscripts
F relative to the feed
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 165
i relative to component i (i= Eth, La, EL, W)
0 relative to initial conditions
Perm relative to permeate
Eth relative to ethanol
La relative to lactic acid
EL relative to ethyl lactate
W relative to water
6.8 References
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166 CHAPTER 6. Pervaporation Membrane Reactor
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Gekas V. and B. Hallstrom, "Mass transfer in the membrane concentration polarization layer under turbulent cross flow. I. Critical literature review and adaptation of existing sherwood correlations to membrane operations", J. Membr. Sci. 30(2): 153-170, 1987.
Gómez P., R. Aldaco, R. Ibáñez and I. Ortiz, "Modeling of pervaporation processes controlled by concentration polarization", Computers & Chemical Engineering 31(10): 1326-1335, 2007.
Hasanoglu A., Y. Salt, S. Keleser, S. Özkan and S. Dinçer, "Pervaporation separation of organics from multicomponent aqueous mixtures", Chemical Engineering and Processing: Process Intensification 46(4): 300-306, 2007.
Jafar J. J., P. M. Budd and R. Hughes, "Enhancement of esterification reaction yield using zeolite A vapour permeation membrane", J. Membr. Sci. 199(1): 117-123, 2002.
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Korkmaz S., Y. Salt, A. Hasanoglu, S. Ozkan, I. Salt and S. Dincer, "Pervaporation membrane reactor study for the esterification of acetic acid and isobutanol using polydimethylsiloxane membrane", Applied Catalysis A: General 366(1): 102-107, 2009.
Krishna Rao K. S. V., M. C. S. Subha, M. Sairam, N. N. Mallikarjuna and T. M. Aminabhavi, "Blend membranes of chitosan and poly(vinyl alcohol) in pervaporation dehydration of isopropanol and tetrahydrofuran", J. Appl. Polym. Sci. 103(3): 1918-1926, 2007.
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 167
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168 CHAPTER 6. Pervaporation Membrane Reactor
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PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 169
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7. PermSMBR – A New Hybrid Technology
Abstract. In this Chapter, a new technology, the Simulated Moving Bed Membrane Reactor
(PermSMBR), was presented and applied for the esterification of lactic acid with ethanol. Its
conception was a result of ethyl lactate process re-intensification by integrating a permeable
membrane reactor with a simulated moving bed reactor, since the products separation by
selective adsorption is enhanced by continuous water removal through the membrane, shifting
the equilibrium till high lactic acid conversion with high ethyl lactate purity. It was
demonstrated that the PermSMBR technology applied for the ethyl lactate synthesis can
reduce the desorbent consumption in 62 % and increase the ethyl lactate productivity in 33 %
when compared with the SMBR and in 98 % when compared with reactive distillation for the
same purity and conversion requirements.
Adapted from: V. M. T. M. Silva, Pereira C. S. M. and A. E. Rodrigues, "Reactor de membranas adsorptivo de
leito móvel simulado, novo processo híbrido de separação e respectivas utilizações”, (PT 104496, patent
pending, 2009)
172 CHAPTER 7. PermSMBR – A New Hybrid Technology
7.1 Introduction
The paradigm of chemical engineering process is changing. Traditional processes (where the
reactor is followed by separation units in order to recover the desirable product, to remove the
by-product and to recycle the unconverted reactants to the reactor) are being replaced by
integrated processes where reaction and separation occur in the same device. These integrated
processes are of considerable interest, mainly for equilibrium-limited reactions where the
continuous removal of at least one reaction product shifts the equilibrium in order to increase
conversion and reduce by-product formation. The term multifunctional reactor is often used
to embrace reactive separations technology, which main advantages are higher yields,
reduction of energy requirements, decrease of solvents consumption and lower capital
investments. Typical examples of equilibrium-limited reactions include:
Esterification: R´-COOH + HO-R = R´COOR + H2O
Acetalization: R´-CHO + 2 HO-R = R´CH-(OR)2 + H2O
Ketalization: R´R´´CO + 2 HO-R = R´R´´C(OR)2 + H2O
In the state of the art, the custom multifunctional reactors used for that type of reactions are:
reactive distillations, reactive extractions, membrane reactors and chromatographic reactors.
Regarding to reactive distillation (RD) the best example is the methyl acetate synthesis
developed and patented by the company Eastman Kodak Company (Agreda and Partin,
1984). The entire process is carried out in a single column and represents one-fifth of the
capital investment and consumes one-fifth of the energy of the traditional process (reaction
followed by separation by distillation) (Krishna, 2002). However, there are some
disadvantages in the use of RD for systems that exhibit azeotropes formation and/or the
boiling points of the products are similar. Membrane reactors are widely used and typical
examples are pervaporation and permeation reactors, where the catalyst is in fluidized
(Alonso et al., 2001; Lee et al., 2006) or fixed bed (Lafarga and Varma, 2000; Zhu et al.,
1996). Several times, processes where the reactor and membrane are housed in separate units
in series or parallel are also regarded as membrane reactors (Datta and Tsai, 1998; Tsotsis et
al., 2007). Chromatographic reactors include fixed bed (FBR) (Pereira et al., 2009a; Silva
and Rodrigues, 2002), pressure swing adsorption (PSAR) and simulated moving bed reactors
(SMBR) (Kawase et al., 1996; Pereira et al., 2009b; Silva and Rodrigues, 2005). However,
from all the mentioned chromatographic reactors, the most common for process
intensification for the production of oxygenated products is the SMBR. The SMBR is well-
PROCESSES INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 173
known equipment (Broughton and Gerhold, 1961) that consists of a set of interconnected
columns packed with an acid solid or a mixture of solids (catalysts and adsorbents). The
description of an SMBR unit is presented in Chapter 5. The SMBR has several advantages, as
the ones already mentioned for the reactive separations; however, it also has some
disadvantages, as for example, the difficulty in removing the more adsorbed species, which
implies high desorbent consumptions. Besides, in several applications, the feed is a mixture
of reactants with one of the products, which will influence the performance of the unit
resulting in low reactants conversion and products purities, low unit productivity and high
eluent/desorbent consumption. This is even worse for the case where the product in the feed
is the more retained one, since then the desorbent consumption will increase significantly. In
order to overcome these issues, it was developed a novel technology, the Simulated Moving
Bed Membrane Reactor (SMBMembR or PermSMBR), which comprises a reactor with two
different separation techniques (chromatography – Simulated Moving Bed (SMB) with a
selective permeable membrane – Pervaporation or Permeation) into a single device. It is a
clean and economic alternative to conventional processes and even competitive when
compared with the intensified processes. If reactive separations embrace the concept of
Process Intensification, the reactive hybrid separations (as PermSMBR) embody the Process
“ReIntensification” (Table 7.1).
Table 7.1 Chemical engineering process evolution.
Traditional Process Reactor + Separator
Distillation Adsorption Crystallization Membranes Extraction
Process Intensification Reactive Separations
• Reactive Distillation • Membrane Reactor • SMB Reactor
Process ReIntensification Reactive Hybrid Separations
• SMB Membrane Reactor
The PermSMBR technology is suitable mainly for oxygenated compounds as esters, acetals
and ethers, used as biofuels, solvents, flavours, among others. In this Chapter, the
PermSMBR will be exploited for the ethyl lactate synthesis. This new reactor leads to near
depletion of lactic acid and high ethyl lactate purity with higher concentration, and,
consequently, lower down streaming costs associated to the separation units.
174 CHAPTER 7. PermSMBR – A New Hybrid Technology
7.2 Technical description of the PermSMBR technology
The PermSMBR consists of a set of columns with membranes connected in series and packed
with a solid, which could be a mixture of catalyst and selective adsorbent or a solid that acts
both as catalyst and as adsorbent. Typically, there are two inlets, feed and desorbent, and
three outlets, extract, raffinate and permeate. In Figure 7.1, there is schematic representation
of a PermSMBR unit, where a reaction of type A+B ↔ C+D is considered.
Figure 7.1 Schematic diagram of a PermSMBR unit with 4 sections and three columns per section.
In this case, the component A is used as reactant and desorbent, therefore it is introduced in
the system in the feed and desorbent streams. The other reactant B is used as feed. The
products formed (C and D) are removed from the PermSMBR in three different streams:
raffinate that is rich in the less strongly adsorbed product, C, extract, rich in the more strongly
adsorbed product, D, and total permeate that combines all the permeate streams and that
comprises mainly product D, for which the membranes are selective. All the inlet/outlet
streams, with exception of the permeate streams, are introduced/removed from the system
through ports positioned between the columns, and at regular time intervals, called the
switching time, this streams are switched for one column distance in direction of the fluid
flow. In this way, the countercurrent motion of the solid is simulated and its velocity is equal
to the length of a column divided by the switching time. A cycle is completed when the
number of switches is equal to a multiple of the total number of columns. The PermSMBR is
Liquid direction and ports switch A+B ⇔ C+D
Feed (A+B)
Raffinate (A+C)
Extract (A+D)
Desorbent (A)
Desorbent Extract
Raffinate Feed
Liquid direction and ports switch A+B ⇔ C+D
Feed (A+B)
Raffinate (A+C)
Extract (A+D)
Desorbent (A)
Desorbent Extract
Raffinate Feed
PROCESSES INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 175
equipped with a rotary valve or a number of valves arranged in manner such that any feed
stream may be introduced to any column and any outlet stream may be withdrawn from any
column; it is also equipped with vacuum (or sweep gas flow) in order to withdraw the
permeate stream from each column. The vacuum (or sweep gas flow) can be turned on in all
the columns or just in some. Similarly to the SMBR, the position of the inlet/outlet streams
defines different sections existing in the PermSMBR unit, each one accomplishing a certain
function and containing a variable number of columns. The typical PermSMBR contains 4
sections, as represented in Figure 7.1 and Figure 7.2, where the section 1 is comprised
between the desorbent and extract nodes, the section 2 is comprised between the extract and
feed node; the section 3 is comprised between the feed and raffinate node, and the section 4 is
comprised between the raffinate and desorbent node. In section 1, the adsorbent is
regenerated by desorption of the more strongly adsorbed product (D) from the solid using the
desorbent (A); In sections 2 and 3, reactive sections, the products C and D are separated as
they are being formed. These products are continuously removed from the unit by adsorption
and also through the selective membranes and, therefore, the reaction will proceed beyond the
thermodynamic equilibrium, being possible to obtain 100 % of reactants conversion. In
section 4, before being recycled to section 1, the desorbent is regenerated by adsorption of the
less adsorbed product (C).
Section 1 Section 2 Section 3
XD F
PPP
Section 4
R
P
Figure 7.2 Schematic diagram of a PermSMBR unit with 4 sections: 2 inlet ports for
feed (F) and desorbent (D) streams; 2 outlet ports for extract (X) and raffinate (R) streams; and outlet permeate streams (P).
The PermSMBR can have different configurations depending on the number of streams
fed/removed from the unit. The total number of streams, with exception of the permeate
streams, corresponds to the total number of sections. For example, the PermSMBR unit can
be simplified to a unit of three sections: eliminating the extract stream, when the membrane is
selective to the more adsorbed product (Figure 7.3); or eliminating the raffinate stream, when
the membrane is selective to the less retained product (Figure 7.4).
176 CHAPTER 7. PermSMBR – A New Hybrid Technology
Figure 7.3 Schematic diagram of a PermSMBR unit with 3 sections: 2 inlet ports for
feed (F) and desorbent (D) streams and 1 outlet port for raffinate (R) stream.
Figure 7.4 Schematic diagram of a PermSMBR unit with 3 sections: 2 inlet ports for
feed (F) and desorbent (D) streams and 1 outlet port for Extract (X) stream.
If necessary, the PermSMBR unit can also be more complex, having five or more sections.
For example, the schematic diagram of the process represented in Figure 7.5 is similar to the
one described for the Figure 7.2, but it has 5 sections since an additional feed stream (F2) is
introduced to the system. In this case, the regeneration of the solid and the desorbent is
accomplished in sections 1 and 5, respectively; and the complete conversion of reactants and
separation of the formed products occurs in section 2, 3 and 4. The feed F2 can comprise the
same reactants as the ones in feed F1, but in different proportions, or other reactants in order
to obtain the desired product. In the case where 3 products are formed, it will be necessary to
have other extra stream designed as R2 in Figure 7.6. Additionally, if it is observed a decrease
in the PermSMBR unit performance (decrease of products purity, reduction of reactants
conversion and/or loss of productivity, among others) due to problems related to
deactivation/poisoning of the catalyst/adsorbent and/or of the membranes, the PermSMBR
unit can be operated in order to correct those problems, making a bypass to each one of the
columns during a cycle to perform the necessary treatments (treatments with acids, solvents,
replacement of the solid and/or of the membrane, thermal treatments, …). For example, if the
desorbent is more expensive than the more adsorbed product, the treatment should by applied
to the last column of section I (Figure 7.7), since this column is still saturated with the most
PROCESSES INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 177
adsorbed product, avoiding the unnecessary consumption of desorbent if other column of the
same section was selected. This procedure can also be performed in other sections in the most
appropriate column. Other ways of correction along time can be performed to the operational
variables of the PermSMBR unit, similarly to the procedure described in literature for the
SMB unit (Sá Gomes et al., 2007).
Section 1 Section 2 Section 3 Section 4
XD
Section 5
F1
P PPPP
RF2 Figure 7.5 Schematic diagram of a PermSMBR unit with 5 sections: 3 inlet ports for 2
feed streams (F1 and F2) and a desorbent stream (D), and 2 outlet ports for extract (X) and raffinate (R) streams.
Figure 7.6 Schematic diagram of a PermSMBR unit with 6 sections: 3 inlet ports for 2
feed streams (F1 and F2) and a desorbent stream (D), and 3 outlet ports for extract (X) and raffinate (R1 and R2) streams.
Figure 7.7 Schematic representation of the bypass to perform the
regeneration/activation of catalyst/adsorbent and/or of the membrane in section 1 of the PermSMBR unit.
178 CHAPTER 7. PermSMBR – A New Hybrid Technology
7.3 PermSMBR mathematical model
Since the PermSMBR results from the integration of pervaporation membrane reactor and
simulated moving bed reactor, its model will combine the specificities of each model
previously described on Chapters 6 and 5, respectively; namely:
- axial dispersion flow for the bulk fluid phase;
- linear driving force (LDF) approximation for the inter and intra-particle mass transfer
rates;
- multi-component adsorption equilibrium;
- velocity variations due to adsorption/desorption rates and species permeation;
- constant porosity and length of the packed bed;
- membrane concentration polarization;
- isothermal operation.
In Figure 7.8 a schematic representation of the fluxes inside one membrane of the
PermSMBR is shown, where F is the molar flux in the feed side (retentate) and J is the
permeate molar flux through the membrane.
membrane
bPermeate
F|z
F|z+dz
z
z+dzJ|zJ|z
Feed Flow
Permeate Flow
Figure 7.8 Schematic representation of the fluxes inside one membrane of
the PermSMBR.
PROCESSES INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 179
Following this assumption the PermSMBR model equations are:
Bulk fluid mass balance to component i in column k
( ) ( )2
,, , 2
1( ) 3ik ik k ik mp ikL ik ik ax k ik
p
C C u C AK C C D Jt z r z
εε ε−∂ ∂ ∂
+ + − = −∂ ∂ ∂
(7.1)
where ikC and ,p ikC are the bulk and average particle concentrations in the fluid phase of
species i in column k respectively, ikLK , is the global mass transfer coefficient of the
component i, ε is the bulk porosity, t is the time variable, z is the axial coordinate, kaxD , , and
ku are the axial dispersion coefficient and the interstitial velocity in column k, respectively,
pr is the particle radius, mA is the membrane area per unit reactor volume and ikJ is the
permeate flux of species i in column k.
The permeate flux ( iJ ) is defined as:
0ov,k ( )i i i i i permJ a p y P= − (7.2)
where ,ov ik is a mass transfer coefficient based on a partial vapour pressure driving force (see
Chapter 6), ia is the activity of component i in bulk, 0ip is the saturation pressure of
component i, permP is the total pressure on the permeate side and iy is the molar fraction of
component i in the vapour phase (permeate side) defined as:
1
ii n
ii
JyJ
=
=
∑ (7.3)
The determination of the global mass transfer coefficient ( LK ) is presented in detail in
Chapter 4 and the calculation of the axial dispersion coefficient ( axD ) is presented in previous
Chapter (Chapter 6).
Interstitial fluid velocity variation calculated from the total mass balance
( ) ( ),, ,1 1
1 3 n nk m
p ikL ik mol i ik iKi ip
du AK V C C Jdz r
εε ε= =
−= − − −∑ ∑ (7.4)
180 CHAPTER 7. PermSMBR – A New Hybrid Technology
where Vmol,i is the molar volume of component i (60.87 mL/mol, 77.56 mL/mol,
118.44 mL/mol and 18.63 mL/mol at 50 ºC for ethanol, lactic acid, ethyl lactate and water,
respectively) and n is the total number of components.
Pellet mass balance to component i, in column k
( ) ( ),, ,,
31 ( )p ik ikp ik p ikp p L ik ik i p
p
qC K C C r Ct t r
ε ε υ ρ∂∂+ − = − +
∂ ∂ (7.5)
where ikq is the average adsorbed phase concentration of species i in column k in equilibrium
with ,p ikC , pε the particle porosity, iυ the stoichiometric coefficient of component i, pρ the
particle density and r is the chemical reaction rate relative to the average particle
concentrations in the fluid phase. The reaction rate and adsorption isotherms are those
determined in Chapters 3 and 4, respectively.
Initial and Danckwerts boundary conditions
0=t : , ,0p ikik ikC C C= = and ,0ik ikq q= (7.6)
0=z : , ,0
ikk ik ax k k ik F
z
Cu C D u Cz =
∂− =
∂ (7.7a)
,0k ku u= (7.7b)
cLz = : 0=∂∂
=Lcz
ik
zC (7.7c)
where F and 0 refer to the feed and initial states, respectively.
Mass balances at the nodes of the inlet and outlet lines of the PermSMBR:
Desorbent node: 1( 4, ) ( 1, 0)
4 4
DDi j z Lc i j z i
u uC C Cu u= = = == − (7.8a)
Extract (j=2) and Raffinate (j=4) nodes: )0,(),1( ==− = zjiLczji CC (7.8b)
Feed node: Fi
FziLczi C
uuC
uuC
2)0,3(
2
3),2( −= == (7.8c)
where,
PROCESSES INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 181
Dsuuu += 41 Desorbent (Ds) node ; (7.9a)
Xuuu −= 12 Extract (X) node ; (7.9b)
Fuuu += 23 Feed (F) node ; (7.9c)
Ruuu −= 34 Raffinate (R) node ; (7.9d)
The ratio between the fluid interstitial velocity, uj, and the simulated solid velocity, Us,
(defined by the column length and switching time relation,*t
LUs = ) could be defined for
each section giving a new parameter:
Usu j
j =γ (7.9e)
The PermSMBR process performance and details on numerical solution are the same
presented in Chapter 5.
7.4 PermSMBR geometrical specifications
The PermSMBR unit considered consists in 12 columns where each column has 13
commercial hydrophilic tubular membranes (Pervatech BV) in order to dehydrate the reaction
medium. Regarding to the position of the membrane separation layer, it is possible to have
different configurations. In the case of the silica membranes from Pervatech, the selective
layer is inside the tube and consequently, it was considered that these membranes were
packed with the resin Amberlyst 15-wet in the lumen side (inside the membrane tube). The
PermSMBR parameters were chosen in order to compare its performance to the one of
SMBR, since this technology will be the most competitive regarding to the PermSMBR. The
same mass of catalyst and effective area was considered. The porosity of the SMBR unit was
determined experimentally and presented in Chapter 5, while the PermSMBR porosity was
estimated in agreement with the experimental results in fixed bed columns with ratio between
tube diameter and particle diameter of 10 (Theuerkauf et al., 2006). The characteristics of the
columns are presented in Table 7.2.
182 CHAPTER 7. PermSMBR – A New Hybrid Technology
Table 7.2 Characteristics of the columns for both SMBR and PermSMBR.
SMBR PermSMBR
Solid weight (A15) 47.6 g 47.6 g
Length of the bed (L) 23 cm 25.45 cm
Internal diameter (Di) 2.6 cm 0.7 cm
Bed porosity (ε ) 0.4 0.424
Bulk density (ρb) 390 kg/m3 374 kg/m3
7.5 Simulated Results
The ethyl lactate synthesis using the SMBR was previously studied (Chapter 5) and the best
performance obtained for that unit was under the following operation conditions: a feed of
lactic acid solution (85 wt. % in water), a desorbent of ethanol (99.5 wt. % in water), a
configuration of 3-3-4-2, a working temperature of 50ºC, a switching time of 2.1 min,
and 1 43.654 and 1.161γ γ= = . In this section the PermSMBR will be evaluated and compared
with the SMBR in order to demonstrate that the ethyl lactate production is enhanced by the
integration of perm selective membranes in the SMBR unit and, therefore, the same operation
conditions will be used. In order to keep the same 1γ and 4γ , the switching time ( *t ) was
changed to 2.323, since the PermSMBR column length is different of the one of the SMBR
unit (see Table 7.2). A summary of the operating conditions used is presented in Table 7.3.
Table 7.3 Operating conditions.
Operating conditions
Temperature 50 ºC Feed lactic acid (85 wt. % in water) Desorbent ethanol (99.5 wt. % in water) Configuration 3-3-4-2 Desorbent flow rate 58 mL/min Recycle flow rate 27 mL/min Switching time 2.323 min
PROCESSES INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 183
Aiming to evaluate the geometrical parameters equivalence between the two units, the SMBR
was compared to the PermSMBR in absence of permeation (considering in the model zero
flux through the membranes) by using the parameters of Table 7.2 and operating conditions
of Table 7.3. The feed flow rate and extract flow rate used were 7 mL/min and 39 mL/min,
respectively. The performance parameters for both processes, presented in Table 7.4, are very
similar, as expected.
Table 7.4 Comparison between SMBR and PermSMBR*
SMBR PermSMBR*
PUX 99.92 99.94
PUR 96.19 97.85
X 99.51 99.37
PR (kgEL.Lresin-1.day-1) 14.64 14.63
DC (LEth/kgEL) 5.98 5.98
* Results obtained from the PermSMBR model considering zero flux through the membranes (equal to a SMBR).
7.5.1 Reactive/Separation Region: PermSMBR vs SMBR
The reactive/separation region is a feasible region (in the γ2 - γ3 plane), which determines the
operating conditions in sections 2 and 3, for given conditions on sections 1 and 4, to obtain
products with specific purity requirement. The reactive/separation regions were calculated for
both PermSMBR and SMBR processes, setting the conditions for complete regeneration on
sections 1 and 4, 1 4(3.654) and (1.161)γ γ , and imposing a 95 % criteria for extract and
raffinate purities and for lactic acid conversion. As it can be seen in Figure 7.9, the size of the
reactive/separation region using the PermSMBR technology is higher than the one for the
SMBR. This is justified by the fact that in the PermSMBR unit the water is removed not only
by the selective adsorption onto the resin but also by the selective removal through the
membrane; and therefore, the quantity of water removed from the system will be higher
allowing higher feed flowrates of lactic acid solution without the contamination of the
raffinate stream. It can be perceived that the PermSMBR allows working with higher feed
flowrates (12.1 mL/min) than the SMBR (8.8 mL/min) to obtain the same purity and
conversion requirements, and consequently higher productivity and lower desorbent
consumption are achieved using this new technology. This is corroborated by the
184 CHAPTER 7. PermSMBR – A New Hybrid Technology
performance parameters obtained for both units working under the optimal operating
conditions, presented in Table 7.5. As it can be seen, the ethyl lactate synthesis on the
PermSMBR benefits its productivity in about 34 % and, additionally, decreases the desorbent
consumption in 28 % which will reduce downstream costs since the products are less diluted.
1.0
1.4
1.8
2.2
2.6
3.0
1.0 1.4 1.8 2.2 2.6 3.0
γ 3
γ2
PermSMBR
SMBR
Figure 7.9 Reactive/separation region for PermSMBR and SMBR processes
(PermSMBR switching time of 2.323 min and SMBR switching time of 2.1 min; remaining conditions of Table 7.3)
Table 7.5 Performance parameters of the SMBR and PermSMBR for the EL synthesis.
SMBR PermSMBR Improvement
PR (kgEL.Lresin-1.day-1) 18.06 24.19 33.94 %
DC (LEth/kgEL) 4.75 3.41 28.21 %
7.5.2 PermSMBR 3 zones
As stated before, the PermSMBR technology can be operated in different configurations,
depending on the products to be separated and on the membrane performance. The ethyl
lactate synthesis involves the formation of water, a by-product for which the membrane here
considered is selective; therefore, it might be convenient to simplify the PermSMBR unit
from 4 to 3 sections, eliminating the extract stream, which change the previous configuration
3-3-4-2 to 6-4-2. Setting the feed and desorbent flowrates at 8 / minFQ mL= and
25 / minDQ mL= , respectively, and using the remaining conditions of Table 7.3, the
PROCESSES INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 185
PermSMBR performance can be significantly enhanced by adjusting the permeate pressure,
as shown in Table 7.6. Lactic acid conversion and ethyl lactate purity are the parameters most
significantly improved. The analysis of internal concentration profiles at the cyclic steady-
state, shown in Figure 7.10, allows better understanding the PermSMBR unit behaviour.
Table 7.6 Performance parameters for different permeate pressures.
Pperm 10 mbar 6 mbar 0 mbar
PUR (%) 92.85 96.15 99.63
X (%) 97.56 99.18 99.86
PR (kgEL.Lresin-1.day-1) 16.27 16.51 16.59
DC (LEth/kgEL) 2.00 1.96 1.95
Water, the most adsorbed component is formed from the esterification reaction but is also fed
to the system since an 85 % lactic acid aqueous solution is used. In order to have a high ethyl
lactate purity and high lactic acid conversion, water should be removed from section 2, and
desorbed from the resin in section 1. Since water is removed by pervaporation, the desorbent
flowrate can be reduced below the value used in the SMBR unit, without compromising the
resin regeneration. The reduction of the permeate pressure from 10 mbar (Figure 7.10a), to
6 mbar (Figure 7.10b) and 0 mbar (Figure 7.10c), increases the water permeation flux
(Equation 7.2), enhancing significantly the resin regeneration on section 1, which avoids
water to pass from section 1 to section 3 and increases the ethyl lactate purity. Since the
reaction is equilibrium limited, this decrease on water content near the raffinate port prevents
the ethyl lactate hydrolysis, increasing the lactic acid conversion, as consequence.
A SMBR unit to have the same raffinate purity, lactic acid conversion and ethyl lactate
productivity as the PermSMBR ( 6 permP mbar= ), would have to operate in the following
conditions: configuration of 3-3-4-2, * 2.1 mint = , 8 / minFQ mL= , 38 / minXQ mL= ,
58 / minDQ mL= and Re 27 / mincQ mL= . However, this would imply a desorbent
consumption of 5.20 LEth/kgEL, which is 62 % higher than the one needed for the PermSMBR.
186 CHAPTER 7. PermSMBR – A New Hybrid Technology
0
2
4
6
8
10
12
14
16
18
0 3 6 9 12
Con
cent
ratio
n (m
ol/L
)Ethanol
Lactic acid
Ethyl lactate
Water
D F RP1 P2 P3 P4 P10 P11P7P5 P6 P8 P9 P12
0
2
4
6
8
10
12
14
16
18
0 3 6 9 12
Con
cent
ratio
n (m
ol/L
)
Ethanol
Lactic acid
Ethyl lactate
Water
D F RP1 P2 P3 P4 P10 P11P7P5 P6 P8 P9 P12
0
2
4
6
8
10
12
14
16
18
0 3 6 9 12
Con
cent
ratio
n (m
ol/L
)
Ethanol
Lactic acid
Ethyl lactate
Water
D F RP1 P2 P3 P4 P10 P11P7P5 P6 P8 P9 P12
Figure 7.10 Influence of permeate pressure on the concentration profiles at the middle
of the switching time at cyclic steady state for the PermSMBR with 3 sections and configuration 6-4-2: a) 10 permP mbar= ; b) 6 permP mbar= and c) 0 permP mbar= .
(a)
(b)
(c)
PROCESSES INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 187
7.5.3 Comparison between PermSMBR, SMBR and RD technologies
The ethyl lactate synthesis using Amberlyst 15-wet as catalyst was successfully implemented
by means of RD processes; and the best unit performance was obtained using 88 wt. % lactic
acid solution, at 128ºC (bottom temperature), achieving 95 % of lactic acid conversion and
95 % of ethyl lactate purity (Asthana et al., 2005). From the previous studies on the SMBR
and PermSMBR processes for the ethyl lactate synthesis at 50ºC, the best ethyl lactate
productivity obtained for a criteria of 95 % of ethyl lactate purity and 95 % of lactic acid
conversion (see Table 7.7), is 48 and 98 % higher than that of the RD process, respectively.
However, in the SMBR and PermSMBR processes the excess of ethanol used to desorb water
is higher than in the case of RD, leading to higher ethanol consumption.
Table 7.7 Performance parameters for RD, SMBR and PermSMBR technologies.
RD+ SMBR PermSMBR
PR (kgEL.Lresin-1.day-1) 12.19 18.06 24.19
DC (LEth/kgEL) 2.17 4.75 3.41
+ (Asthana et al., 2005)
Another factor to take in consideration is that the RD operates at 128ºC, while the SMBR and
PermSMBR systems work at 50ºC; thus, the energy consumption will be higher on the RD
process. Therefore, comparison of technologies must be done in terms of economical
assessment.
7.6 Conclusions
In this Chapter a new technology was proposed, the PermSMBR, that consists in a SMBR
integrated with a permeable membrane reactor by using selective permeable membranes
inside the columns of the SMBR. The PermSMBR proved to be more effective than the
SMBR when applied to the ethyl lactate synthesis; higher ethyl lactate productivities and
lower desorbent consumptions were obtained for the same purity and conversion criterions
188 CHAPTER 7. PermSMBR – A New Hybrid Technology
with this new reactor, since additionally to the driven force for product separation by selective
adsorption there is the selective membrane removal of water.
The 3 sections PermSMBR operated in configuration 6-4-2 was studied, and it was concluded
that it is not necessary the completely regeneration of the resin by water desorption in section
1 by introducing the sufficient amount of desorbent (ethanol), since water is also removed by
the permeable membranes, preventing the ethyl lactate contamination. It was stated a
decrease of 62 % in the desorbent consumption with this new technology using a 6 mbar
vacuum pressure when comparing with the SMBR to attain the same ethyl lactate purity,
productivity and lactic acid conversion.
When compared with the RD process, the PermSMBR requires higher ethanol consumption,
but allows a significantly ethyl lactate productivity increase of 98 %, operating at quite lower
temperatures.
Concluding, the PermSMBR is a very interesting technology, even compared with other
intensified processes, that allows complete reactants conversion, high productivity, high
purity, significant reduction of solvent consumption and consequently lowers downstreaming
costs associated to the separation units.
7.7 Notation
ia liquid-phase activity of component i in bulk side
mA membrane area per unit reactor volume (m2membrane/m3
bulk)
C liquid phase concentration (mol/L)
axD axial dispersion coefficient (m2/min)
DC desorbent consumption (L/mol)
iJ permeate flux of species i (mol/(m2min))
LK global mass transfer coefficient
ovk global membrane mass transfer coefficient (mol/(m2sPa))
L column length (m)
PROCESSES INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 189
n total number of components
0ip saturation pressure of component i (bar)
permP total pressure on the permeate side (bar)
PR raffinate productivity (kgEL/(L resin.day))
PUR raffinate purity (%)
PUX extract purity (%)
q solid phase concentration in equilibrium with the fluid concentration inside the
particle (mol/L)
Q volumetric flowrate (L/min)
r rate of reaction (mol kg-1 min-1)
pr particle radius (m)
t time variable (min)
*t switching time (min)
Us solid velocity (m/min)
u interstitial velocity (m/min)
,mol iV molar volume of species i (L/mol)
X lactic acid conversion
iy molar fraction in the vapor phase of component i
z axial coordinate (m)
Greek letters
γ interstitial velocities ratio
ε bulk porosity
190 CHAPTER 7. PermSMBR – A New Hybrid Technology
pε particle porosity
iυ stoichiometric coefficient of component i
pρ particle density
Subscripts
i relative to component i (i= Eth, La, EL, W)
j relative to section in SMBR (j = 1, 2, 3, 4)
k relative to column in SMBR
0 relative to initial conditions
Eth relative to ethanol
La relative to lactic acid
EL relative to ethyl lactate
W relative to water
F relative to the feed
p relative to particle
R relative to raffinate
cRe relative to recycle
X relative to extract
Superscripts
F relative to the feed
R relative to raffinate
X relative to extract
PROCESSES INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 191
7.8 References
Agreda V. H. and L. R. Partin, "Reactive distillation process for the production of methyl acetate", U. S. Patent 4435595 (1984).
Alonso M., M. J. Lorences, M. P. Pina and G. S. Patience, "Butane partial oxidation in an externally fluidized bed-membrane reactor", Catal. Today 67(1-3): 151-157, 2001.
Asthana N., A. Kolah, D. T. Vu, C. T. Lira and D. J. Miller, "A continuous reactive separation process for ethyl lactate formation", Org. Process Res. Dev. 9(5): 599-607, 2005.
Broughton D. B. and C. G. Gerhold, "Continuous Sorption Process Employing Fixed Bed of Sorbent and Moving Inlets and Outlets", US Patent No. 2 985 589 (1961).
Datta R. and S.-P. Tsai, "Esterification of Fermentation-Derived Acids via Pervaporation", WO Patent No. 9823579 (1998).
Kawase M., T. B. Suzuki, K. Inoue, K. Yoshimoto and K. Hashimoto, "Increased esterification conversion by application of the simulated moving-bed reactor", Chem. Eng. Sci. 51(11): 2971-2976, 1996.
Krishna R., "Reactive separations: more ways to skin a cat", Chem. Eng. Sci. 57(9): 1491-1504, 2002.
Lafarga D. and A. Varma, "Ethylene epoxidation in a catalytic packed-bed membrane reactor: Effects of reactor configuration and 1,2-dichloroethane addition", Chem. Eng. Sci. 55(4): 749-758, 2000.
Lee W. N., I. J. Kang and C. H. Lee, "Factors affecting filtration characteristics in membrane-coupled moving bed biofilm reactor", Water Res. 40(9): 1827-1835, 2006.
Pereira C. S. M., V. M. T. M. Silva and A. r. E. Rodrigues, "Fixed Bed Adsorptive Reactor for Ethyl Lactate Synthesis: Experiments, Modelling, and Simulation", Sep. Sci. Technol. 44(12): 2721 - 2749, 2009a.
Pereira C. S. M., M. Zabka, V. M. T. M. Silva and A. E. Rodrigues, "A novel process for the ethyl lactate synthesis in a simulated moving bed reactor (SMBR)", Chem. Eng. Sci. 64(14): 3301-3310, 2009b.
Sá Gomes P., M. Minceva and A. E. Rodrigues, "Operation strategies for simulated moving bed in the presence of adsorbent ageing", Sep. Sci. Technol. 42(16): 3555-3591, 2007.
Silva V. M. T. M. and A. E. Rodrigues, "Dynamics of a fixed-bed adsorptive reactor for synthesis of diethylacetal", AIChE J. 48(3): 625-634, 2002.
Silva V. M. T. M. and A. E. Rodrigues, "Novel process for diethylacetal synthesis", AlChE J. 51(10): 2752-2768, 2005.
Theuerkauf J., P. Witt and D. Schwesig, "Analysis of particle porosity distribution in fixed beds using the discrete element method", Powder Technol. 165(2): 92-99, 2006.
192 CHAPTER 7. PermSMBR – A New Hybrid Technology
Tsotsis T. T., M. Sahimi, B. Fayyaz-Najafi, A. Harale, B.-G. Park and P. K. T. Liu, "Hybrid adsorptive membrane reactor", US Patent No. 2007053811 (A1) (2007).
Zhu Y., R. G. Minet and T. T. Tsotsis, "A continuous pervaporation membrane reactor for the study of esterification reactions using a composite polymeric/ceramic membrane", Chem. Eng. Sci. 51(17): 4103-4113, 1996.
8. Conclusions and Suggestions for Future Work
This thesis focused on the development of a new efficient process to produce ethyl lactate
based in the esterification reaction between ethanol and lactic acid by using hybrid
technologies of reaction/separation based on the Simulated Moving Bed Reactor (SMBR) and
Pervaporation Membrane processes. Therefore, several topics were addressed from the
fundamentals (thermodynamic equilibrium and kinetics of reaction, multi-component
adsorption equilibria and pervaporation data), to the process development (modelling and
simulation) and intensification (simulated moving bed reactor, pervaporation membrane
reactor and an integration of both). The main results and conclusions are:
(i) Batch Reactor: Thermodynamic Equilibrium and Reaction Kinetics
To circumvent the lack of a suitable estimative for the thermodynamic equilibrium constant
as function of temperature, the equation ( )KTK 13.5159625.2ln −= , based on the
UNIQUAC method, and valid in the temperature range of 50-90ºC, was proposed.
The kinetic law was described by a Langmuir-Hinshelwood rate expression based on
activities, considering the surface reaction as the rate-controlling step. The following kinetic
law was proposed for the temperature range of 50-90 ºC, for the Amberlyst 15-wet catalyst:
( ) 2/ (1 )c Eth La EL W Eth Eth W Wr k a a a a K K a K a= − + + ; and the model parameters are
( )7( /( .min)) 2.70 10 exp 6011.55 / ( )ck mol g T K= × − , ( ))(/01.12exp19.15 KTKW = and
( ))(/63.359exp22.1 KTK Eth = .
(ii) Fixed Bed Adsorptive Reactor
The multi-component adsorption equilibria were determined from dynamic adsorption
experiments in absence of reaction, at 20 ºC and 50 ºC, using Amberlyst 15-wet as selective
194 CHAPTER 8 Conclusions and Suggestions for Future Work
adsorbent. The multi-component Langmuir adsorption isotherm was modified in order to
reduce the adjustable adsorption parameters from 8 (one molar monolayer capacity and one
equilibrium constant for each component) to 5 (one volumetric monolayer capacity for all
components and one equilibrium constant for each component):
( ) ( ),/ 1i V mol i i i j jq Q V K C K C= +∑ using the following parameters:
Component QV (ml/lwet solid) 20 ºC / 50 ºC
K (l/mol) 20 ºC / 50 ºC
Vmol (ml/mol) 20 ºC / 50 ºC
Ethanol 5.443 / 3.068 58.17 / 60.87
Lactic acid 4.524 / 4.085 74.64 / 77.56
Ethyl lactate 1.117 / 1.815 113.99 / 118.44
Water
390.0/383.5
15.353 / 7.055 18.08 / 18.63
(iii) Simulated Moving Bed Reactor
The ethyl lactate was produced in the Simulated Moving Bed Reactor pilot unit LICOSEP,
using Amberlyst 15-wet resin as catalyst and selective adsorbent. A mathematical model
considering external and internal mass-transfer resistances and variable velocity due to
change of liquid composition was developed to describe the dynamic behaviour of the SMBR
and it was validated by the experiments performed. The theoretical assessment of the SMBR
unit behaviour was performed ensuring complete regeneration of the resin (in section 1) and
desorbent (in section 4), by using the mathematical model to analyse the effect of SMBR
configuration, feed composition and switching time into the reactive/separation regions
or/and into the process performance at the optimal operating points. It was shown that the
SMBR is a very attractive technology for the production of ethyl lactate, since under
appropriate conditions the lactic acid conversion can be driven to completion and productivity
as high as 32 kgEL/(Lads.day) and purity of 95 % can be obtained.
(iv) Pervaporation Membrane Reactor
Pervaporation process using commercial Hydrophilic silica membranes from Pervatech was
evaluated for the ethyl lactate system aiming to contribute either for the separation of SMBR
extract stream (water/ethanol mixtures) or for the ethyl lactate process intensification by
continuous pervaporation membrane reactor (PVMR). First pervaporation studies indicate
that the membranes have no major imperfections since the total flux and water selectivity is
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 195
barely affected by absolute feed pressure. The influence of hydrodynamic conditions on the
membrane polarization was analyzed, and for velocity values higher than 0.14 m/s
polarization effects are eliminated. It was concluded that the permeances for all species as
function of temperature and feed water content, are described by the following equations for
the temperature range 48ºC - 72ºC: 3
7,
22.60 101.41 10 expmemb EthQRT
− ⎛ ⎞×= × ⎜ ⎟
⎝ ⎠2/( min)mol dm bar
, 0memb LAQ = 2/( min)mol dm bar
34
,10.42 101.12 10 expmemb ELQ
RT− ⎛ ⎞×
= × ⎜ ⎟⎝ ⎠
2/( min)mol dm bar
6,
50377 323262 10 exp(18.642 )exp Wmemb W W
xQ xRT
− −⎛ ⎞= × −⎜ ⎟⎝ ⎠
2/( min)mol dm bar
A mathematical model was developed for the batch pervaporation membrane (BPM),
considering (i) plug flow for the bulk fluid phase; (ii) total feed volume inside the tank and
retentate velocity inside the membrane variations due to permeation of components; (iii)
concentration polarization, where the resistance due to the diffusive transport in the boundary
layer is combined with the membrane resistance in a global membrane resistance; (iv) non-
isothermal operation due to heat consumption for species vaporization; and (v) temperature
polarization. The BPM model was validated experimentally and, therefore, it was extended to
the integrated pervaporation membrane reactor packed with the catalyst Amberlyst-15wet. In
isothermal conditions, the PVMR is a very attractive solution being possible to achieve near
lactic acid depletion (98 % conversion) and ethyl lactate with 96 % purity, at 70ºC.
(v) PermSMBR – A New Hybrid Technology
A new technology, the Simulated Moving Bed Membrane Reactor (PermSMBR), was
developed and applied for the esterification of lactic acid with ethanol. Its conception was a
result of process re-intensification by integrating a permeable membrane reactor with a
simulated moving bed reactor. The PermSMBR proved to be more effective than the SMBR
when applied to the ethyl lactate synthesis; higher ethyl lactate productivities and lower
desorbent consumptions were obtained for the same purity and conversion criterions with this
new reactor, since additionally to the driven force for product separation by selective
adsorption there is the selective membrane removal of water. It was demonstrated that the
196 CHAPTER 8 Conclusions and Suggestions for Future Work
PermSMBR technology can reduce the desorbent consumption in 62 % and increase the ethyl
lactate productivity in 33 % when compared with the SMBR and in 98 % when compared
with RD for the same purity and conversion requirements. Concluding, the PermSMBR is a
promising technology, even if compared with other intensified processes that allows complete
reactants conversion, high productivity, high purity, significant reduction of solvent
consumption and consequently lowers downstream costs associated to the separation units.
This thesis is focused on the ethyl lactate synthesis with a special contribution on its process
intensification. The SMBR technology exhibits higher productivity than that of the PVMR,
but has the disadvantage of requiring further separation units for recovery of ethanol from
both extract and raffinate streams. Integrating the benefits of SMBR and PVMR, a new
technology was invented, the PermSMBR. However, certain topics were not exploited and
others are unfinished and, therefore, can be deeper investigated. For that reason it is suggested
to explore, in a near future, the following research lines:
(i) Screening of new catalysts
Smopex 101 fibre has proved to be an efficient catalyst for acetalization and esterification
reactions; since it has negligible adsorption capacity is not suitable for chromatographic
reactor, namely the SMBR and PermSMBR, although would be valuable for the PVMR.
Another interesting catalyst is the Amberlyst 36-wet (A36), a strongly acidic ion exchange
resin, which proved to be more active than Amberlyst 15-wet (A15) for esterification
reactions; moreover, as adsorbent has selectivity to water since the swelling from dry to water
is 54 %, while A15 only swells 37 %. Therefore, A36 will enhance the performance of SMBR
and PermSMBR by improving both reaction kinetics and products separation.
(ii) Deactivation studies
It is known that catalyst and/or adsorbent ageing affects significantly the performance of
industrial processes, and might compromise the process feasibility. Ageing studies should
consider not only pro-analytical reactants but also industrial reactants (lactic acid from
fermentation broth and bio-ethanol). Its influence on the ion-exchange resin deactivation, in
terms of reaction kinetics and multi-component adsorption equilibria, should be addressed, in
PROCESS INTENSIFICATION FOR THE GREEN SOLVENT ETHYL LACTATE PRODUCTION 197
order to understand its implications on the processes performance. Analysis of non-isothermal
effects onto the SMBR and PermSMBR unit performance should also be performed.
(iii) Process Integration and Economical Evaluation
The economical assessment of the ethyl lactate synthesis should be carried out considering its
integration with the subsequent separation units. Comparison between technologies (SMBR,
PVMR, PermSMBR, RD, ...) should be based on financial project evaluation using the Net
Present Value analysis, net annual profit or annual production cost. Alternatively, the
evaluation of the most sustainable technology should be based on the Life Cycle analysis.
Appendix A: Safety Data
1.1 Ethyl lactate
NFPA
1.1.1 General
Synonyms: lactic acid ethyl ester
Molecular formula: C5H10O3
CAS No: 97-64-3
1.1.2 Physical Data
Appearance: colourless liquid
Melting point: -26 ºC
Boiling point: 154 ºC
Vapour density: 4.07 (air = 1)
Vapour pressure (mmHg): 5 @ 30ºC (86ºF)
Density (g cm-3): 1.03
Flash point: 46 ºC (closed cup)
Explosion limits: 1.5 – 11.4%
Autoignition temperature: 400 ºC
Water solubility: appreciable
1.1.3 Stability
Stable. Combustible. Incompatible with strong oxidizing agents.
• Health: 3
• Flammability: 2
• Reactivity: 0
23 0
APPENDIX A. Safety Data A 2
1.1.4 Toxicology
Skin, eye and respiratory irritant.
Toxicity data:
Oral-mouse lethal dose 50% kill 2500 mg kg-1
Intraperitoneal – rat lowest published lethal dose 1000 mg kg-1
Subcutaneous – mouse lethal dose 50% kill 2500 mg kg-1
Risk phrases:
• R36 Irritating to eyes.
• R37 Irritating to respiratory system.
• R38 Irritating to skin.
1.1.5 Personal Protection
Minimize contact.
Safety phrases:
• S26 In case of contact with eyes, rinse immediately with plenty of water and seek
medical advice.
1.1.6 Hazard Summary
• Ethyl lactate can affect you when breathed in and may be absorbed through the skin.
• Prolonged contact can irritate the skin and eyes.
• Breathing ethyl lactate may cause dizziness, lightheadedness, and passing out.
1.1.7 How to determine if you are being expose
• Exposure to hazardous substances should be routinely evaluated. This may include
collecting personal and area air samples. Under OSHA 1910.20, you have a legal right to
obtain copies of sampling results from your employer. If you think you are experiencing
any work-related health problems, see a doctor trained to recognize occupational diseases.
Take this Fact Sheet with you.
APPENDIX A. Safety Data A 3
1.1.8 Workplace exposure limits
No occupational exposure limits have been established for ethyl lactate. This does not mean
that this substance is not harmful. Safe work practices should always be followed.
• It should be recognized that ethyl lactate may be absorbed through the skin, thereby
increasing your exposure.
1.1.9 Ways of reducing exposure
Where possible, enclose operations and use local exhaust ventilation at the site of chemical
release. If local exhaust ventilation or enclosure is not used, respirators should be worn.
Wear protective work clothing.
Wash thoroughly immediately after exposure to ethyl lactate and at end of the workshift.
Post hazard and warning information in the work area. In addition, as part of an ongoing
education and training effort, communicate all information on the health and safety hazards of
ethyl lactate to potentially exposed workers.
1.1.10 Health hazard information
Acute Health Effects
The following acute (short-term) health effects may occur immediately or shortly after
exposure to ethyl lactate:
Prolonged contact can irritate the skin and eyes.
Breathing ethyl lactate may cause dizziness, lightheadedness and passing out.
Chronic Health Effects
The following chronic (long-term) health effects can occur at some time after exposure to
ethyl lactate and can last for months or years:
Cancer Hazard
According to the information presently available to the New Jersey Department of Health and
Senior Services, ethyl lactate has not been tested for its ability to cause cancer in animals.
APPENDIX A. Safety Data A 4
Reproductive Hazard
According to the information presently available to the New Jersey Department of Health and
Senior Services, ethyl lactate has not been tested for its ability to affect reproduction.
Other Long-Term Effects
Ethyl lactate has not been tested for other chronic (long-term) health effects.
Medical Testing
There is no special test for this chemical. However, if illness occurs or overexposure is
suspected, medical attention is recommended.
Any evaluation should include a careful history of past and present symptoms with an exam.
Medical tests that look for damage already done are not a substitute for controlling exposure.
Request copies of your medical testing. You have a legal right to this information under
OSHA 1910.1020.
1.1.11 Workplace controls and practices
Unless a less toxic chemical can be substituted for a hazardous substance, ENGINEERING
CONTROLS are the most effective way of reducing exposure. The best protection is to
enclose operations and/or provide local exhaust ventilation at the site of chemical release.
Isolating operations can also reduce exposure. Using respirators or protective equipment is
less effective than the controls mentioned above, but is sometimes necessary.
In evaluating the controls present in your workplace, consider: (1) how hazardous the
substance is, (2) how much of the substance is released into the workplace and (3) whether
harmful skin or eye contact could occur. Special controls should be in place for highly toxic
chemicals or when significant skin, eye, or breathing exposures are possible.
In addition, the following controls are recommended:
• Where possible, automatically pump liquid Ethyl Lactate from drums or other storage
containers to process containers.
Good WORK PRACTICES can help to reduce hazardous exposures. The following work
practices are recommended:
• Workers whose clothing has been contaminated by Ethyl Lactate should change into clean
clothing promptly.
APPENDIX A. Safety Data A 5
• Contaminated work clothes should be laundered by individuals who have been informed of
the hazards of exposure to Ethyl Lactate.
• Eye wash fountains should be provided in the immediate work area for emergency use.
• If there is the possibility of skin exposure, emergency shower facilities should be provided.
• On skin contact with Ethyl Lactate, immediately wash or shower to remove the chemical.
At the end of the workshift, wash any areas of the body that may have contacted Ethyl
Lactate, whether or not known skin contact has occurred.
• Do not eat, smoke, or drink where Ethyl Lactate is handled, processed, or stored, since the
chemical can be swallowed. Wash hands carefully before eating, drinking, smoking or
using the toilet.
Personal Protective Equipment
WORKPLACE CONTROLS ARE BETTER THAN PERSONAL PROTECTIVE
EQUIPMENT. However, for some jobs (such as outside work, confined space entry, jobs
done only once in a while, or jobs done while workplace controls are being installed),
personal protective equipment may be appropriate.
The following recommendations are only guidelines and may not apply to every situation.
Clothing
• Avoid skin contact with Ethyl Lactate. Wear solvent-resistant gloves and clothing. Safety
equipment suppliers/manufacturers can provide recommendations on the most protective
glove/clothing material for your operation.
• All protective clothing (suits, gloves, footwear, headgear) should be clean, available each
day, and put on before work.
Eye Protection
• Wear indirect-vent, impact and splash resistante goggles when working with liquids.
• Wear a face shield along with goggles when working with corrosive, highly irritant or
toxic substances.
APPENDIX A. Safety Data A 6
Respiratory Protection
IMPROPER USE OF RESPIRATORS IS DANGEROUS. Such equipment should only be
used if the employer has a written program that takes into account workplace conditions,
requirements for worker training, respirator fit testing and medical exams, as described in
OSHA 1910.134.
• Engineering controls must be effective to ensure that exposure to Ethyl Lactate does not
occur.
• Where de potential for overexposure exists, use a MSHA/NIOSH a approved supplied-air
respirator with a full facepiece operated in a pressure-demand or other positive-pressure
mode. For increased protection use in combination with an auxiliary self-contained
breathing apparatus operated in a pressure-demand or other positive-pressure mode.
1.1.12 Handling Storage
• Prior to working with Ethyl Lactate you should be trained on its proper handling and
storage.
• Ethyl Lactate is not compatible with OXIDIZING AGENTS( such as PERCHLORATES,
PEROXIDES, PERMANGANATES, CHLORATES, NITRATES, CHLORINE,
BROMINE and FLUORINE).
• Store in tightly closed containers in a cool, dark, well-ventilated area.
• Sources of ignition, such as smoking and open flames, are prohibited where Ethyl Lactate
is handled, used, or stored.
1.1.13 Fire Hazards
• Ethyl Lactate is a COMBUSTIBLE LIQUID.
• Use dry chemical, CO2, water spray or alcohol resistant foam extinguishers.
• CONTAINERS MAY EXPLODE IN FIRE.
• Use spray to keep fire-exposed containers cool.
• If employees are expected to fight fires, they must be trained and equipped as stated in
OSHA 1910.156.
APPENDIX A. Safety Data A 7
1.1.14 Spills and emergencies
If Ethyl Lactate is spilled or leaked, take the following steps:
• Evacuate person’s not wearing protective equipment from area of spill or leak until clean-
up is complete.
• Remove all ignition sources.
• Ventilate area of spill or leak.
• Absorb liquids in vermiculite, dry sand, earth, or a similar material and deposit in sealed
containers.
• It may be necessary to contain and dispose of Ethyl Lactate as a HAZARDOUS WASTE.
Contact your Department of Environmental Protection (DEP) or your regional office of the
federal Environmental Protection Agency (EPA) for specific recommendations.
• If employees are required to clean-up the spills, they must be properly trained and
equipped. OSHA 1910.120(q) may be applicable.
1.1.15 First aid
Eye Contact
Immediately flush with large amounts of water. Continue without stopping for at least 15
minutes, occasionally lifting upper and lower lids.
Skin Contact
Remove contaminated clothing. Wash contaminated skin with soap and water.
Breathing
• Remove the person from exposure.
• Begin rescue breathing if breathing has stopped and CPR if heart action has stopped.
• Transfer promptly to a medical facility.
APPENDIX A. Safety Data A 8
1.2 Lactic Acid
NFPA
1.2.1 General
Synonyms: 2-hydroxypropanoic acid, ethylideneactic acid, 1-hydroxyethanecarboxylic acid
Molecular formula: CH3CHOHCOOH
CAS No: 50-21-5
EC No: 200-018-0
1.2.2 Physical Data
Appearance: colourless to yellow liquid
Melting point: 18 ºC
Boiling point: 122 ºC @12mmHg
Specific gravity: 1.05
1.2.3 Stability
Stable. Combustible. Incompatible with strong oxidizing agents.
1.2.4 Toxicology
Eye or skin contact may cause severe irritation or burns.
Toxicity data:
Oral-rat lethal dose 50% kill 3730 mg kg-1
Subcutaneous – mouse lethal dose 50% kill 4500 mg kg-1
Risk phrases:
• R34 Causes burns.
• Health: 2
• Flammability: 1
• Reactivity: 0
12 0
APPENDIX A. Safety Data A 9
1.2.5 Personal Protection
Safety glasses.
Safety phrases:
• S26 In case of contact with eyes, rinse immediately with plenty of water and seek
medical advice.
• S27 Take off immediately all contaminated clothing.
• S36 Wear suitable protective clothing.
• S37 Wear suitable gloves.
• S39 Wear eye / face protection.
1.2.6 Health Effects
• Inhalation: causes burns on contact with mucous membranes.
• Eye: Causes burns on contact with eyes.
• Skin: Causes burns on contact with skin.
• Ingestion: Harmful if swallowed. Can cause abdominal pain, diarrhea, and burns of
digestive tract.
• Routes of Entry: Inhalation, Ingestion or skin contact.
1.2.7 First Aid
• Inhalation: Remove to fresh air; give artificial respiration if breathing has stopped.
Get medical attention.
• Eye: Immediately flush eyes with large amounts of water for at least 15 minutes.
• Skin: Immediately flush thoroughly with large amounts of water. Remove
contaminated clothing and wash before reuse.
• Ingestion: Do not induce vomiting; get medical immediate attention.
1.2.8 Fire Hazard
• Extinguishing Media: water fog, foam, carbon dioxide, dry chemical
APPENDIX A. Safety Data A 10
• Special Procedures: Wear self-contained breathing apparatus.
• Unusual Hazard: Emits acrid fumes when heated.
1.3 Ethanol
NFPA
1.3.1 General
Synonyms: ethyl alcohol, grain alcohol, fermentation alcohol, alcohol, methylcarbinol,
absolute alcohol, absolute ethanol, anhydrous alcohol, alcohol dehydrated, algrain, anhydrol.
Molecular formula: C2H5OH
CAS No: 64-17-5
1.3.2 Physical data
Appearance: colourless liquid
Melting point: -130 C
Boiling point: 78 C
Specific gravity: 0.789
Vapour pressure: 1.59
Flash point: 56 F
Explosion limits: 3.3% - 24.5%
Autoignition temperature: 683 F
Water solubility: miscible in all proportions
• Health: 0
• Flammability: 3
• Reactivity: 0
30 0
30 0
APPENDIX A. Safety Data A 11
1.3.3 Stability
Stable. Substances to be avoided include strong oxidising agents, peroxides, acids, acid
chlorides, acid anhydrides, alkali metals, ammonia, moisture. Forms explosive mixtures with
air.
1.3.4 Toxicology
Causes skin and eye irritation. Ingestion can cause nausea, vomiting and inebriation; chronic
use can cause serious liver damage. Note that “absolute” alcohol, which is close to 100%
ethanol, may nevertheless contain traces of 2-propanol, together with methanol or benzene.
The latter two are very toxic, while “denatured” alcohol has substances added to it which
make it unpleasant and possibly hazardous to consume.
Risk phrases:
• R11 Highly flammable.
• R20 Harmful by inhalation.
• R21 Harmful in contact with skin.
• R22 Harmful if swallowed.
• R36 Irritating to eyes.
• R37 Irritating to respiratory system.
• R38 Irritating to skin.
• R40 Possible risk of irreversible effects.
1.3.5 Personal protection
Safety glasses. Suitable ventilation.
Safety phrases:
• S7 Keep container tightly closed.
• S16 Keep away from sources of ignition.
• S24 Avoid contact with skin.
• S25 Avoid contact with eyes.
APPENDIX A. Safety Data A 12
• S36 Wear suitable protective clothing.
• S37 Wear suitable gloves.
• S39 Wear eye / face protection.
• S45 In case of accident or if you feel unwell, seek medical advice immediately (show
the label whenever possible.)
Appendix B: Thermodynamic Properties
1.1 Available Literature Data
The data presented in this section are from Yaws (Yaws, 1999), excepted when mentioned.
In Table B.1 some physical and thermodynamic properties of lactic acid, ethanol, ethyl lactate
and water are presented.
Table B.1 Basic properties of lactic acid, ethanol, ethyl lactate and water.
Properties Lactic Acid Ethanol Ethyl Lactate Water
Molecular weigh - M (g/mol) 90.079 46.069 118.133 18.015
Density- ρ (g/cm3) 1.209 0.789 1.031 1.027
Melting temperature - Tf (K) 289.95-291.15 159.15 248.25 273.15
Normal boiling temperature - Tb (K) 395.15 351.45 426.15-427.15 373.15
Critical temperature - Tc (K) 616.00 516.25 588.00 647.13
Critical pressure - Pc (bar) 59.65 63.84 38.60 221.20
Critical volume - Vc (cm3/mol) 216.9 166.9 354.0 57.1
Acentric factor - ω 1.035 0.637 0.793 0.344
1.1.1 Density
The modified form of the Rackett equation was selected for correlation of saturated liquid
density as a function of temperature.
n
cTT
L AB)1( −−
=ρ (B.1)
with )/( 3cmgLρ and T (K).
APPENDIX B. Thermodynamic Properties B2
Table B.2 Constants used for density calculation.
Constants Lactic Acid Ethanol Water Ethyl Lactate
A 0.39816 0.26570 0.34710 0.33372
B 0.26350 0.26395 0.27400 0.21190
n 0.28570 0.23670 0.28571 0.45530
Tmin (K) 291.15 159.05 273.16 247.15
Tmax (K) Tc Tc Tc Tc
1.1.2 Viscosity
The correlation for liquid viscosity as a function of temperature is given by Equation B.2.
210log DTCT
TBAL +++=η (B.2)
with )(cPLη and T (K).
Table B.3 Constants used for viscosity calculation.
Constants Ethanol Water Ethyl Lactate
A -6.4406E+00 -10.2158E+00 -20.0105E+00
B 1.1176E+03 1.7925E+03 3.2123E+03
C 1.3721E-02 1.7730E-02 4.1891E-02
D -1.5465E-05 -1.2631E-05 -3.2733E-05
Tmin (K) 240 273 247
Tmax (K) Tc 643 Tc
1.1.3 Vapour Pressure
The Antoine-type equation with extended term was selected for correlation of vapour
pressure as a function of temperature:
21010 loglog ETDTTC
TBAPvp ++++= (B.3)
with Pvp (mmHg) and T (K).
APPENDIX B. Thermodynamic Properties B3
Table B.4 Constants used for vapour pressure calculation.
Constants Lactic Acid Ethanol Water Ethyl Lactate A -27.0836E+00 23.8442E+00 29.8605E+00 32.0863E+00
B -3.9661E+03 -2.8642E+03 -3.1522E+03 -2.9164E+03
C 2.0233E+01 -5.0474E+00 -7.3037E+00 -9.5666E+00
D -4.2176E-02 3.7448E-11 2.4247E-09 6.5114E-03
E 2.0310E-05 2.7361E-07 1.8090E-06 4.5645E-13
Tmin (K) 291.15 159.05 273.16 247.15
Tmax (K) Tc Tc Tc Tc
1.1.4 Liquid Heat Capacity
The correlation for heat capacity of liquid is a series expansion in temperature, given by
Equation B.4.
42 3 ETC A BT CT DTp += + + + (B.4)
with Cp (J/(Kmol.K)) and T (K), with exception for the ethyl lactate specie where Cp is given
in (J/(mol.K)).
Table B.5 Constants used for heat capacity calculation.
Constants Ethanol* Water* Ethyl Lactate Lactic acid*
A 1.0264E+05 2.7637E+05 -46.239E+00 6.1082E+04
B -1.3963E+02 -2.0901E+03 2.1823E+00 5.0343E+02
C -3.0341E-02 8.1250E+00 -5.9832E-03 ---------
D 2.0386E-03 -1.4116E-02 6.8683E-06 ---------
E --------- 9.3701E-06 --------- ---------
Tmin (K) 159.05 273.16 248.00 289.90
Tmax (K) 390.00 533.15 529.00 675.00
Error < 3% < 1% ----------- < 10%
* parameters taken from (DIPPR, 1998).
APPENDIX B. Thermodynamic Properties B4
1.1.5 Heat of Vaporization
The correlation selected for the calculation of the heat of vaporization as a function of
temperature is given by Equation B.5 (DIPPR, 1998).
( )21V B CT DTr rTrAH + +⎡ ⎤−⎣ ⎦=Δ (B.5)
with /r cT T T= and VHΔ in (J/(Kmol).
Table B.6 Constants used for heat vaporization calculation.
Constants Ethanol Water Ethyl Lactate Lactic acid
A 5.5789E+07 5.2053E+07 8.0260E+07 1.0436E+08
B 3.1245E-01 3.1990E-01 4.0930E-01 3.8548E-01
C --------- -2.1200E-01 --------- ---------
D --------- 2.5795E-01 --------- ---------
Tmin (K) 159.05 273.16 247.15 289.90
Tmax (K) 514.00 647.13 588.00 675.00
Error < 1% < 1% < 10% < 25%
1.1.6 Thermal Conductivity
The thermal conductivity was calculated by Equation B.6 (DIPPR, 1998).
42 3 ETA BT CT DTλ += + + + (B.6)
with λ (W/(m.K)) and T (K).
Table B.7 Constants used for thermal conductivity calculation.
Constants Ethanol Water Ethyl Lactate Lactic acid
A 2.4680E-01 -4.3200E-01 2.8358E-01 3.4850E-01
B -2.6400E-04 5.7255E-03 -3.5110E-04 -3.7085E-04
C --------- -8.0780E-06 --------- ---------
D --------- 1.8610E-09 --------- ---------
Tmin (K) 159.05 273.16 247.15 289.90
Tmax (K) 353.15 633.15 427.65 490.00
Error < 5% < 1% < 25% < 10%
APPENDIX B. Thermodynamic Properties B5
1.2 Properties Estimation
1.2.1 Estimation of Liquid Viscosity
The lactic acid viscosity was estimated by the following expression (DIPPR, 1998):
4097.9exp 14.403 0.4407 ln( )LA TT
η ⎛ ⎞= − + − ×⎜ ⎟⎝ ⎠
(B.7)
with ( . )L Pa sη and T (K).
Table B.8 Viscosity of lactic acid.
T (K) 293.15 323.15 η (cP) 53.67 13.99
For the estimation of the viscosity of the remaining species (ethanol, ethyl lactate and water)
it was used the Equation B.2 presented in section 1.1.2.
1.2.2 Estimation of Vapour Pressure
For correlation of vapour pressure as a function of temperature the Antoine equation with
extended term was chosen (Equation B.3).
0.00
0.50
1.00
1.50
2.00
2.50
290 320 350 380
P vp
(atm
)
T (K)
Lactic acidEthanolWaterEthyl lactate
Figure B. 1 Variation of the vapour pressure of the compounds with the
temperature.
APPENDIX B. Thermodynamic Properties B6
1.2.3 Estimation of Liquid Heat Capacity
The liquid heat capacity was estimated by the correlation given by Equation B.4 (see Figure
B.2).
0
50
100
150
200
250
300
350
290 310 330 350 370
Cp (J
/ (m
ol.K
))
T (K)
Ethanol WaterEthyl lactate Lactic acid
Figure B.2 Variation of the liquid heat capacity of the different species with the
temperature.
1.2.4 Estimation of Heat of Vaporization
The heat of vaporization was estimated by the correlation given by Equation B.5 (see Figure
B.3).
3.0E+04
4.5E+04
6.0E+04
7.5E+04
9.0E+04
290 310 330 350 370
ΑH V
(J /
mol
)
T (K)
EthanolWaterEthyl lactateLactic acid
Figure B.3 Variation of the heat of vaporization of the different species with the
temperature.
APPENDIX B. Thermodynamic Properties B7
1.2.5 Estimation of Molar Volumes
The molar volumes for all components were estimated with Gunn-Yamada method (Reid et
al., 1987):
( ) ( )( )
R
RV
Tf
TfTV = (B.8)
where
( ) ( )21 1 HHTf ω−= (B.9)
4321 11422.102512.251941.133953.033593.0 rrrr TTTTH +−+−= (B.10)
22 04842.009045.029607.0 rr TTH −−= (B.11)
c
R
cr T
TorTTT = (B.12)
VR is the molar volume at the reference temperature TR (cm3/mol), ω is the acentric factor
and Tc is the critical temperature (K).
Gunn-Yamada method could be used just in the case when the liquid molar volume is known
at some temperature (reference temperature). The reference molar volumes are presented at
Table B.9.
Table B.9 Molar volumes at the reference temperature used for all calculations.
VR (cm3/mol) Reference Temperature TR (K) Lactic Acid Ethanol Ethyl Lactate Water
293.15 74.640 58.174 113.986 18.082
1.3 References
DIPPR, "Thermophysical Properties Database", (1998).
Reid R. C., P. J.M. and P. B.E., "The Properties of Gases and Liquids", McGraw-Hill, (1987).
Yaws C. L., "Chemical Properties Handbook", McGraw-Hill, (1999).
Appendix C: Calibration
1.1 Calibration
1.1.1 Pure Components
The calibration was realized by injecting different volumes of pure components at 20 ºC and
registering the respective peak area values. The molar volume, VM, of each species was used
to convert volume, V, in number of moles, n. In the case of lactic acid the volume was
converted to number of moles using the solution density (ρ), since lactic acid is not pure
(lactic acid 85 w/w % pure).
The response factor (fi) was defined as:
iii Afn = (C.1)
where in is the number of moles of component i (μmol) and iA is the area of component i (u.a.)
nEth = 5.879AEthR2 = 0.983
0
2
4
6
8
10
0 0.4 0.8 1.2 1.6
n Eth
(µm
ol)
AEth (u.a.)
Figure C.1
Table C.1 Ethanol
VM (cm3/mol) V (μL) n (μmol) A (u.a.)
0.1 1.7093 0.3394 0.1 1.7093 0.3410 0.2 3.4185 0.6408 0.2 3.4185 0.6385 0.3 5.1278 0.9178 0.3 5.1278 0.9208 0.4 6.8371 1.1555 0.4 6.8371 1.1796 0.5 8.5464 1.4011
58.17
0.5 8.5464 1.3564
APPENDIX C. Calibration C2
nLA = 6.994ALAR2 = 0.990
1
2
3
4
5
6
0.3 0.5 0.7 0.9
n LA
(µm
ol)
ALA (u.a.)
Figure C.2
nEL = 3.345AELR2 = 0.986
0
1
2
3
4
5
0 0.4 0.8 1.2 1.6
nEL(µmol)
AEL (u.a.) Figure C.3
nW= 11.826AWR2 = 0.988
0
5
10
15
20
25
30
0 0.5 1 1.5 2 2.5
n W(µ
mol
)
AW (u.a.) Figure C.4
Table C.2 Lactic acid ρ (g/cm3) V (μL) n (μmol) A (u.a.)
0.2 2.2375 0.3144 0.2 2.2375 0.3212 0.3 3.3562 0.4732 0.3 3.3562 0.4574 0.4 4.4750 0.6262 0.4 4.4750 0.6612 0.5 5.5937 0.7800
1.209
0.5 5.5937 0.8294
Table C.3 Ethyl lactate VM (cm3/mol) V (μL) n (μmol) A (u.a.)
0.1 0.8695 0.3074 0.1 0.8695 0.3020 0.2 1.7390 0.5713 0.2 1.7390 0.5721 0.3 2.6085 0.8174 0.3 2.6085 0.8202 0.4 3.4780 1.0289 0.4 3.4780 1.0371 0.5 4.3475 1.2496
113.99
0.5 4.3475 1.2407
Table C.4 Water
VM (cm3/mol) V (μL) n (μmol) A (u.a.)
0.1 5.5253 0.5409 0.1 5.5253 0.5434 0.2 11.0506 1.0200 0.2 11.0506 1.0287 0.3 16.5759 1.4712 0.3 16.5759 1.4729 0.4 22.1012 1.8591 0.4 22.1012 1.8350 0.5 27.6266 2.2369
18.08
0.5 27.6266 2.2602
APPENDIX C. Calibration C3
1.1.2 Binary mixtures
Several standard binary mixtures with known concentration were prepared, analysed and the
molar fraction of each component was determined, accordingly to Equation C.2.
,i i
est in n
n
f Axf A
=∑
(C.2)
In order to introduce a correction factor, the estimated molar fraction (obtained from Equation
C.2) and the real molar fraction of each component were adjusted for each pair by a linear
fitting (see Figure C.5).
, ,Calc i est ix a bx= + (C.3)
xreal,EL = 1.1304xest,EL - 0.0177R2 = 0.9998
0
0.2
0.4
0.6
0.8
1
0 0.2 0.4 0.6 0.8 1
x rea
l,EL
xest,EL
Ethyl lactate/Ethanol
xreal,Eth = 1.0492xest,Eth - 0.018R2 = 0.9995
0
0.2
0.4
0.6
0.8
1
0 0.2 0.4 0.6 0.8 1
x rea
l,Eth
xest,Eth
Ethanol/Water
Figure C.5 Real molar fraction as function of estimated molar fraction of a specie in
different binary mixtures.
xreal,LA = 1.089xest,LA + 0.0118R2 = 0.9984
0
0.1
0.2
0.3
0.4
0 0.1 0.2 0.3 0.4
x rea
l,LA
xest,LA
Lactic acid/Water
xreal,EL = 0.9706xest,EL - 0.0044R² = 0.9993
0
0.2
0.4
0.6
0.8
0 0.2 0.4 0.6 0.8
x rea
l,EL
xest,EL
Ethyl lactate/Water
APPENDIX C. Calibration C4
1.1.3 Multicomponent mixtures
Several standard multicomponent mixtures with known concentrations were prepared and
analysed. The real molar fraction and the estimated molar fraction (from Equation C.2) of
each component were adjusted by a linear fitting (Figure C.6).
xreal,EL = 0.8803xest,EL + 0.0031R² = 0.9993
0
0.2
0.4
0.6
0 0.2 0.4 0.6
x rea
l,EL
xest,EL
Figure C.6 Real molar fraction as function of estimated molar fraction of a specie in multicomponent mixtures.
The lactic acid molar fraction was calculated from mass balance: 1 ( )LA Eht EL Wx x x x= − + + .
1.2 Validation of Calibration
The molar fraction of a component in a binary mixture is calculated using Equation C.2 and
the equation obtained from the linear fitting of the respective pair (presented in Figure C.5).
For the case of multicomponent mixtures the procedure for the calculation of a specie molar
fraction is the same that the one used for binary mixtures; first it is used Equation C.2 and
then the equation obtained from the linear fitting of the specie in a multicomponent mixture
(presented in Figure C.6). For both cases, the concentration is then evaluated using the liquid
molar volumes (Equation C.4):
xreal,Eth = 0.9986xest,Eth - 0.016R² = 0.9986
0
0.2
0.4
0.6
0.8
1
0 0.2 0.4 0.6 0.8 1
x rea
l,Eth
xest,Eth
xreal,W = 0.9969xest,W - 0.0144R² = 0.999
0
0.2
0.4
0.6
0 0.2 0.4 0.6
x rea
l,W
xest,W
APPENDIX C. Calibration C5
,
ii
n M nn
xCx V
=∑
(C.4)
In order to verify the analysis accuracy for the binary and quaternary mixtures several
samples with known concentration were prepared and analysed, as shown in Tables C.4-C.8.
Table C.4 Analysis of Ethanol/Ethyl lactate mixtures.
Ethyl lactate molar fraction Sample
Real Calculated Error (%) 1 0.1919 0.1935 0.82
2 0.5078 0.5075 -0.07
3 0.8968 0.8991 0.26
Table C.5 Analysis of Lactic acid/Water mixtures. Lactic acid molar fraction
Sample Real Calculated Error (%)
1 0.0818 0.0809 -1.12
2 0.3182 0.3213 0.98
3 0.4098 0.4146 1.17
Table C.6 Analysis of Ethanol/Water mixtures.
Ethanol molar fraction Sample
Real Calculated Error (%) 1 0.1560 0.1574 0.87
2 0.6025 0.5912 -1.88
Table C.7 Analysis of Ethyl lactate/Water mixtures.
Ethyl lactate molar fraction Sample
Real Calculated Error (%) 1 0.2789 0.2781 -0.27 2 0.6565 0.6622 0.87
APPENDIX C. Calibration C6
Table C.8 Analysis of a quaternary mixture. Molar fraction Component
Real Calculated Error (%) Ethanol 0.3969 0.3981 0.29
Lactic acid 0.1865 0.1900 1.88 Ethyl lactate 0.2275 0.2233 -1.85
Water 0.1891 0.1886 -0.24
Appendix D: Binary adsorption experiments at 293.15 K
The breakthrough curves for the binary adsorption experiments performed at 293.15 K are
presented below.
(a)
0
10
20
30
40
50
60
0 40 80 120 160 200
Out
let c
once
ntra
tion
(mol
/L)
Time (min)
Water
Ethanol
Theoretical
(b)
0
10
20
30
40
50
60
0 10 20 30 40 50 60
Out
let c
once
ntra
tion
(mol
/L)
Time (min)
waterethanolTheorical
Figure C.1 Breakthrough experiments: outlet concentration of ethanol and water as a
function of time; Q = 5 mL/min; T = 293.15 K; (a) water displacing ethanol; Bottom up flow direction; (b) ethanol displacing water; Top-down flow direction.
APPENDIX D. Breakthrough curves at 293.15 K D 2
(a)
0
2
4
6
8
10
12
14
16
18
0 40 80 120 160 200
Out
let c
once
ntra
tion
(mol
/L)
Time (min)
Ethyl lactate
Ethanol
Theoretical
(b)
0
2
4
6
8
10
12
14
16
18
0 10 20 30 40
Out
let c
once
ntra
tion
(mol
/L)
Time (min)
ethyl lactateethanolTheorical
Figure C.2 Breakthrough experiments: outlet concentration of ethanol and ethyl
lactate as a function of time; Q = 5 mL/min; T = 293.15 K; (a) ethyl lactate displacing ethanol; Bottom up flow direction (b) ethanol displacing ethyl lactate; Top-down flow direction.
APPENDIX D. Breakthrough curves at 293.15 K D 3
0
10
20
30
40
50
60
0 20 40 60 80 100
Out
let c
once
ntra
tion
(mol
/L)
Time (min)
Water
Lactic acid
Theoretical
Figure C.3 Breakthrough experiments: outlet concentration of water and lactic acid
as a function of time; Q = 5 mL/min; T = 293.15 K; Lactic acid displacing water; Bottom up flow direction.