DISSOLUTION DYNAMICS OF A BINARY SWITCHABLE HYDROPHILICTY SOLVENT - POLYMER DROP INTO AN ACIDIC AQUEOUS PHASE

2025-05-03 0 0 2.75MB 15 页 10玖币
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DISSOLUTION DYNAMICS OF A BINARY SWITCHABLE
HYDROPHILICTY SOLVENT - POLYMER DROP INTO AN ACIDIC
AQUEOUS PHASE
Romain Billet
Department of Chemical and Materials Engineering
University of Alberta
Edmonton, T6G 1H9, Canada
Binglin Zeng
Department of Chemical and Materials Engineering
University of Alberta
Edmonton, T6G 1H9, Canada
James Lockhart
BC Research Inc.
Richmond, BC V6V 1M8, Canada
Mike Gattrell
BC Research Inc.
Richmond, BC V6V 1M8, Canada
Hongying Zhao
BC Research Inc.
Richmond, BC V6V 1M8, Canada
hzhao@bcri.ca
Xuehua Zhang
Department of Chemical and Materials Engineering
University of Alberta
Edmonton, T6G 1H9, Canada
xuehua.zhang@ualberta.ca
October 27, 2022
ABSTRACT
Switchable hydrophilicity solvents (SHSs) are solvents defined by their ability to switch from their
hydrophobic form to a hydrophilic form when put in contact with an acidic trigger such as
CO2
. As
a consequence, SHSs qualify as promising alternatives to volatile organic compounds during the
industrial solvent extraction processes, as greener and inexpensive methods can be applied to separate
and recover SHSs. Furthermore, because of their less volatile nature, SHSs are less flammable and
so increase the safety of a larger-scale extraction process. In this work, we study the dynamics and
in-drop phase separation during the dissolution process of a drop composed of SHS and polymer,
triggered by an acid in the surrounding aqueous environment. From 70 different experimental
conditions, we found a scaling relationship between the drop dissolution time and initial volume with
an overall scaling coefficient
0.53
. We quantitatively assessed and found a shorter dissolution time
related with a decrease in pH of the aqueous phase or an increase in initial polymer concentration in
the drop. Examining the internal state of the drop during the dissolution revealed an in-drop phase
separation behavior, resulting in a porous morphology of the final polymer particle. Our experimental
results provide a microscopic view of the SHS dissolution process from droplets, and findings may
help design SHS extraction processes for particle formation from emulsions.
1 Introduction
Solvent removal is one of the most common processes in the chemical industry. Being able to remove and recover the
solvent from a system is of the utmost importance and can be done by evaporation induced by heating and/or vacuum. A
common way to make such solvent removal and recovery easier is to use low boiling point Volatile Organic Compounds
(VOCs). However, these solvents are also usually hazardous pollutants known for their toxicity and smog-forming
properties [
1
,
2
] These VOCs are also typically highly flammable, requiring special considerations in the design and
arXiv:2210.14398v1 [cond-mat.soft] 26 Oct 2022
APREPRINT - OCTOBER 27, 2022
operation of the solvent recovery processes. Therefore, to respect the principles of green-chemistry, the search for an
alternative is necessary. [3, 4]
Switchable Hydrophilicity Solvents (SHSs) constitute a family of solvents that exhibits hydrophobic (immiscibility
with water) properties in their neutral form. However, when ionized (for example by contact with an acid such as
CO2
for a cationic SHS) they become hydrophilic (miscible with water). This switching process is also reversible, and SHS
can be "switched" back to their hydrophobic form by, for example, removing
CO2
by flushing with
N2
. [
5
] [
6
] The
mechanism behind this switching process is the acid-base chemical reaction described below:
SHSorg + H+
aq *
)SHSH+
aq
For the
CO2
trigger, it is the dissolution of
CO2
and the acidification of water that allows the SHS to switch. This
switching behavior can more generally be observed with other kinds of acid. [7, 8, 9]
SHSs present an economically viable and green alternative to VOCs due to the simplicity to "switch on" and "off" the
hydrophobicity of the solvent with high recoverability coming from the "switching off" process. Potential applications
of SHS have already been demonstrated in soybean oil extraction[
10
] [
11
], separation of bitumen from oil sands[
12
],
biofuel extraction from microalgae [
13
,
14
], polystyrene foam [
15
] and multi-layer packaging recycling[
16
,
17
],
liquid-liquid micro-extraction (SHS-LLME) for analytical chemistry [18, 19] or latex formation [20].
In latex formation, binary drops of SHS and dissolved polymer are made to deposit solid polymer particles by switching
off SHS hydrophobicity in an aqueous environment. A typical example is the formation of polystyrene particles by the
dissolution of N-N Dimethylcyclohexylamine (DMCHA) from binary drops of DMCHA and polystyrene. When the
DMCHA-polystyrene drop contacts an acidic phase, DMCHA reacts with protons producing the protonated counterpart
DMCHAH+ following the biphasic reaction below:
DMCHAorg + H+
aq )
*DMCHAH+
aq
The produced DMCHAH
+
is solubilized in the aqueous environment at the surface of the binary drop. In this way,
the DMCHA in the DMCHA-polystyrene drop begins to dissolve into the aqueous phase and the drop shrinks with
time. Subsequently, the insoluble polystyrene part of the drop is left behind and forms a solid polystyrene particle.
Understanding of the dissolution dynamics of the binary drop is required to obtain the desirable morphology, size, and
properties of final polymer particles.
The dissolution process of drops with a low solubility in their environment is a problem that has already been studied
previously. In an early work, Duncan et al [
21
] showed experimentally that the diffusion-driven model for bulk
bubbles in an undersaturated liquid phase developed by Epstein [
22
] could be also applied to dissolution of a free oil
microdroplet. The diffusion-driven model was further developed to describe the dissolution of a drop deposited on
a substrate (i.e. sessile drop) with effects of the drop geometry taken into account. [
23
] The lifetime of a dissolving
sessile drop in various modes such as constant contact radius, constant contact angle, stick-slide, or stick-jump modes
of the drop have been experimentally and theoretically studied.[24, 25, 26]
To add to the diffusion-driven dissolution, the influence of gravity-induced convection in the bulk liquid on the
dissolution process has also been shown to speed up the dissolution dynamics.[
27
]. More recently, the dissolution
process of multicomponent drops, as opposed to pure liquid drops, has been found to exhibit complex dynamics. The
components in the drop may undergo preferential dissolution [
28
], phase separation [
29
], or self-assembling [
30
]. For
instance, dissolution of polymer solution drops may lead to formation of polymer capsules [
31
,
32
,
33
,
34
], while
snowballs of graphene oxide may develop from dissolution of colloidal drops. [35] [36]
The dynamic of the switching SHS and corresponding solvent extraction process has previously been shown to be time
consuming, in some cases reaching hours [
6
]. It is therefore important to understand what conditions may possibly
shorten the switching-extraction time and minimize residual solvent in a cost-effective manner. In the extraction process
assisted by
CO2
-switching SHS, two steps may play a role: (1) the slow mass transfer of
CO2
gas into the aqueous
phase, followed by the chemical reactions of dissociation and hydrolysis of
CO2
to
HCO
3
,
CO2
3
and
H+
, and (2)
the liquid phase reaction (switching) of neutral SHS (hydrophobic form) and dissolution of switched SHS (hydrophilic
form) into the aqueous solution. In previous work by Han et al the acceleration of the switching-extraction dynamics
was studied using a microfluidic device. The improved specific interfacial area between the aqueous phase and
CO2
gas
accelerated the extraction process inside the microfluidic device. [
37
,
38
] However, to the best of our knowledge, there
is no quantitative understanding on the SHS dissolution dynamics of the reaction-induced mass transfer of the SHS, and
in-particular inside a liquid drop and its impact on the final morphology of the polymer particles post solvent extraction.
2
APREPRINT - OCTOBER 27, 2022
Table 1: Experimental parameters to study the influence of the initial drop composition, the pH in the aqueous phase is
fixed at 2.53.
Initial polystyrene (wt%) 0 10
Drop volume (µL) 0.15 0.20 0.35 0.50 0.55 0.65 0.80 2.30 4.25 0.25 0.40 0.55 0.70
Initial polystyrene (wt%) 10 20
Drop volume (µL) 0.90 1.20 2.00 2.40 2.95 3.65 0.30 0.45 0.70 0.85 0.95 1.45 2.20
Initial polystyrene (wt%) 20 30
Drop volume (µL) 2.55 3.00 3.25 0.35 0.75 1.00 1.30 1.50 2.10 2.40 2.75 2.85
In this work, we study the dissolution of a binary DMCHA/polystyrene sessile drop immersed in a controlled acidic
aqueous solution environment as it is presented in Fig. 1. We aim at understanding the reaction-induced mass transfer
of the SHS from the drop to the aqueous phase. We find a scaling relationship between the drop dissolution time and
the initial size of the drop, and study the impact of the aqueous phase pH and initial drop composition on this scaling
law. We also follow the internal state of the drop during the dissolution process, and show the existence of a phase
separation behavior and its implication on the final morphology of the final polymer particle. Our findings may help to
give a quantitative understanding of the switching dynamics of SHS drops during the initial external reaction/diffusion
dominated phase, and provide useful insights for internal drop dynamics and improved design for SHS switching
processes in applications such as latex formation.
2 Experimental section
2.1 Materials, solutions and substrates
The SHS polymer solutions were prepared using a mixture of N-N Dimethylcyclohexylamine (Sigma-Aldrich, 99%,
DMCHA) and polystyrene (Sigma-Aldrich,
Mw
= 40 000 g/mol, beads >99%). The weight ratio ranged from 10 to 30
wt% of polystyrene. Both chemicals were mixed under ambient condition in sealed vials using a magnetic stirrer for 2
hours until complete dissolution of the polystyrene beads in DMCHA. Acid solutions were freshly made before each
dissolution using formic acid (Sigma-Aldrich, > 95%) and (Milli-Q) water. The solution concentration used in this
work ranged from
1.1×101
M to
2.7×104
M (0.4 vol% to 0.001 vol%). The pH of the solutions was measured
using a benchtop pH meter (Fisher Scientific, Accumet AE150) and ranged from 2.37 to 3.83. Small square (
1×1cm
)
silicon substrates were cut from wafers and thoroughly rinsed with water, ethanol and then sonicated for 20 minutes
with ethanol before finally being dried with a stream of air. The partial solubilities of DMCHA in water as well as
water inside of DMCHA were measured by progressively adding one compound in a vial of the other until saturation.
A solubility of DMCHA in water of
15.3±1.7g/L
and water in DMCHA of
155 ±7g/L
(
18.3±0.8
vol
%
) were
measured close to what was previously reported in the literature. [39]
2.2 Drop dissolution
To study the dynamics of this dissolution, a side view camera was used to record the drop dissolution. The drop
dissolution setup is shown in Fig. 1. The substrates were placed at the bottom of a glass cuvette (Krüss Scientific,
36 ×36 ×30 mm W ×D×H
). The polymer solution was then filled in a glass syringe that was controlled by a
connected Drop Shape Analyzer instrument (DSA-100, Krüss Scientific).
For each experiment, the glass cuvette was filled with 30 mL of the acidic solution and drops of initial volume ranging
from 0.15 to 3.65
µ
L were introduced by the motorized syringe on the surface of the substrate inside the aqueous
acidic phase. In total, 70 dissolution conditions were studied, as summarized in Table 1 for the polystyrene content
parameter and in Table 2 for the pH levels. During the drop dissolution, the side view images were captured directly by
the DSA-100 with a 9x magnification. For the top view, an upright optical microscope (Nikon H600l) equipped with a
4x magnification lens and a camera was used to image the drops.
After the drop dissolution, the substrate was carefully removed from the acidic solution. The excess water on the sample
was gently blown with air and the remaining water left to dry under ambient conditions for 48 hours.
2.3 Image analysis and characterization
Video footage of the drops was analyzed using MATLAB. The MATLAB code used analyzed each frame of the side
view videos and detected the drop using an intensity threshold. The detected drop was then used to measure the
quantities of interest. This can be done either by assuming a spherical model and fitting a spherical-cap shape to the
3
摘要:

DISSOLUTIONDYNAMICSOFABINARYSWITCHABLEHYDROPHILICTYSOLVENT-POLYMERDROPINTOANACIDICAQUEOUSPHASERomainBilletDepartmentofChemicalandMaterialsEngineeringUniversityofAlbertaEdmonton,T6G1H9,CanadaBinglinZengDepartmentofChemicalandMaterialsEngineeringUniversityofAlbertaEdmonton,T6G1H9,CanadaJamesLockhartBC...

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