Lessard et al.
1871
NMR techniques (12). Most of these studies dealt with
polydisperse PDEA samples, and none of them addressed
clearly the question of the molecular weight effect on the
LCST of the polymers.
In the present work, using fractional precipitation, we pre-
pared 11 PDEA fractions with molar masses ranging from
9.6 × 103 to 1.3 × 106 g mol–1. Turbidimetry, also called
cloud point technique, and microcalorimetry were used to
study the effect of molecular weight on the LCST of these
fractions in aqueous solutions.
A number of parameters have been reported to influence
the LCST of thermosensitive polymers. It was shown that
the presence of salts in the solution generally decrease the
LCST of the solution (5, 20) and added surfactants improve
the solubility of the polymer, thereby raising the LCST (20–
22). Also, phase separations were studied as functions of the
amount of cosolvent (23), polymer concentration (24), and
pressure (25). Investigations of molecular weight influence
on the LCST, however, showed a large discrepancy in the re-
sults obtained. Some authors reported an inverse dependence
of the LCST on the molar mass (5, 24), while others claimed
the opposite (26). Several studies also reported that the mo-
lecular weight had no influence on the LCST (6, 27). It is
worthwhile to mention that the fractionation of this kind of
polymers is quite difficult due to the amphiphilicity of the
macromolecule.
allowed to cool down to the precipitation temperature. The
system was kept without stirring for at least 1 day before the
precipitated fraction was recovered. The remaining solution
underwent further precipitation in the same way as described
above. This process was repeated to obtain further fractions.
In total, 11 fractions were obtained.
The molecular weight and its distribution of the polymer
samples were determined by size exclusion chromatography
(SEC) on a Waters system equipped with an online Waters
410 differential refractometer and a set of three Ultrastyragel
columns. Tetrahydrofuran was used as the mobile phase, and
polystyrene samples as the standards in the calibration of the
molar masses.
Determination of LCST
The cloud point of PDEA in water was set as the tempera-
ture at the inflexion point of the curve obtained by turbi-
dimetry. A CARY 1 BIO UV–vis spectrophotometer coupled
to a temperature controller was used in the absorbance mode
at a wavelength of 500 nm. A 1-cm sample cell containing
ca. 80 L of solution was used for the measurement against
deionized Milli-Q water as the reference. The cloud point of
sample with higher concentration was impossible to deter-
mine with enough precision due to the saturation of the sig-
nal on the spectrophotometer.
Microcalorimetry was also used to determine the LCST of
PDEA aqueous solutions. The endothermic signal at its max-
imum (corresponding to the LCST) was recorded for each
sample on a DSC VP-microcalorimeter from Microcal Inc.
A cell filled with deionized Milli-Q water was used as the
reference. Heating rates of 0.1 and 1.0°C min–1 were used,
with both methods, to see their effect on the LCST.
The LCST values of aqueous PDEA solutions with differ-
ent molecular weight were determined by means of turbi-
dimetry and microcalorimetry at a concentration of 1 wt% to
ensure an exact value of the cloud point and the LCST.
Experimental section
All chemicals were purchased from Sigma (St. Louis,
Missouri, U.S.A.) and Aldrich (Milwaukee, Wisconsin,
U.S.A.) and were used as received. Ammonium persulfate
was recrystallized before use.
Polymer synthesis
N,N-Diethylacrylamide (DEA) was prepared, as reported
previously (11), by reacting acryloyl chloride (97%) with an
excess of diethylamine (98%) in methylene chloride at 0°C.
The salt was filtered off and the solvent was evaporated.
Distillation of the liquid under 0.5 mmHg (1 mmHg =
133.322 Pa) vacuum at 40–50°C in the presence of hydro-
quinone yielded a clear liquid, which was kept in a freezer
until use.
Results and discussion
The fractionated samples of PDEA have a wide range of
molar masses, from 9.6 × 103 to 1.3 × 106 g mol–1. The
polydispersity of the fractions were lower than that of the
bulk sample (Mw/Mn = 3.59) as shown in Table 1.
PDEA was obtained by radical solution polymerization of
DEA using ammonium persulfate as the initiator and
N,N,N>,N>-tetramethylethylenediamine as the accelerator.
Purified water was degassed with nitrogen and was used as
the solvent. The reaction was carried out at room tempera-
ture for 4 h. The solvent was then evaporated and PDEA,
after dissolution into a small amount of acetone, was puri-
fied twice by precipitation in petroleum ether, resulting in a
white solid.
The LCST of a solute dissolved in a solvent can be ob-
tained from the phase diagram of the system. The phase dia-
grams of two polymer samples F2 and F9 are shown in
Fig. 1, where the cloud point is plotted as a function of con-
centrations ranging from 0.0001 to 10 wt%. The LCST is
given by the lower temperature at which the phase transition
occurs. It appears that the most accurate value of the LCST
can be obtained for concentrations ranging from 1 to 5 wt%
for low and high molecular weight samples, and no signifi-
cant differences on the LCST are observed within this inter-
val of polymer concentrations.
Fractionation and characterization
PDEA fractions were obtained by fractional precipitation
using acetone as the solvent and hexane as the nonsolvent.
To ensure good results, the concentration of the PDEA solu-
tion was kept low (less than 0.1 wt%) and the temperature
was maintained constant at 25°C. Hexane was added until
the solution turned cloudy. Then the temperature was raised
by 1 or 2°C to dissolve the precipitated polymer and then
As shown in Fig. 2a, the transmittance of the 1 wt%
PDEA solution decreases sharply at a certain temperature
owing to the turbidity of the solutions when precipitation oc-
curred. The exact values of the cloud point (LCST), DH, and
DS are listed in Table 1. The general trend observed for this
series of samples is that the LCST is lower for the higher
molecular weight polymers.
© 2001 NRC Canada