In vitro modelfor the degradation
nanoparticles
of aJ&ylcyanoacrylate
Rainer H. ~~er, ~a~er~e Lherm,Jens He&ox% Patrick Co~e~
and
UnticeMt6 de Paris-&d, Lab&at&? de Pharmacie GalMque
France
(Received 2 7 December
et Biopharmacie. 5 rua J. 8. Cl&ment. F-92290
Chatenay-Malabry.
1989: eccepted 3 May 1990)
A photometric assay was developed to study the surface erosion of polymeric nanoparticles. The hydrolytic
deg~dation of polyalkylcyanoac~late
particles was studied in different environments (NaOH, buffer, cell
culture medium and serum). The influence of particle modification on the degradation rate was assessed.
Particularly, the effect of polymer coating for particle targeting and fluorescence labelling was
investigated. From the absorption data, a t50# and tlOO% can be calculated for fast degrading particles
and obtained by an extrapolation in case of a slow degradation process. The degradation rate was found to
decrease with increasing alkyl chain length from methyl-, ethyl-, isobutyl- to isohexylcyanoacrylate
particles. Polymer coating and fluorescent labelling had little effect on the rate of degradation.
Kevords:
8i~egr~atjon,
drug deikery, ~anupa~icles
Polymeric devices, such as implants” ‘, microparticles and
nanoparticles4 are employed for controlled release and sitespecific drug delivery. Relatively long degradation times
have been described for implants made from polyesters, e.g.
1 yr for poly(lactic acid) (PLA) and 3-6 wk for its copolymer
with glycolic acid (PLA/GA)‘.
The degradation of larger
surgical PLA/GA implants has been reported to take more
than 6 month”. Particles from these PLA/GA copolymers
were, however, found to degrade almost completely within
4 wk’. Possible reasons are the absence of a lag time before
weight loss occurs’, the larger surface area adsorbing
hydrolysis accelerating proteins’ and a more porous particle
structure’.
Incorporation of additives accelerated drug release but
had little effect on the degradation rate”.Fast-degrading
alkylcyanoacrylate polymers should be more suitable for
accumulation in the body for the production of particulate
drug carriers’ ‘* ‘*. However, a too rapid degradation can lead
to a burst release of degradation products, possibly causing
cytotoxic effects l3 . Therefore, particle degradation rate is
determined to provide basic information for the comprehension
of possible cytotoxic effects of such products. Indeed,
cytotoxicity was observed even with degradation products
which are non-toxic metabolic compounds (e.g. lactic acid)
but which appear in a very high local concentration’4.
In addition, the degradation kinetics could change
after modification of the particles. Coating nanoparticles for
site-specific drug delivery (drug targeting) changed the
Correspondence to Or P. Couvreur.
surface properties such as hydrophobicity’5 which, in turn,
may be supposed to modify the degradation profile of the
polymer.
To assess these effects, this paper proposes an in vitro
model based on the measurement of the degradation of the
nanoparticles themselves rather than, as generally proposed,
on assaying the concentration of the final degradation
products after total chemical decomposition
of the
polymer’*-‘*.
MATERIALS
Biomaterials
1990, Vol 11 October
METHODS
Materials
Methylcyanoacrylate
and ethylcyanoacrylate monomers
(MCA and ECA) were provided by Loctite Ltd (Ireland),
isobutylcyanoacrylate (IBCA) was purchased from Sigma
(USA), isohexylcyan~c~late
(IHCA) was a gift from Sopar
(Belgium). The other compounds used for particle preparation
were reagent or pharmacopeia grade and used without
further purification.
Propidium iodide, the fluorescent marker for the
nanoparticles, was purchased from Sigma (USA). The
polymers for the coating of nanoparticles Poloxamer 407
and Poloxamine 908 were obtained from BASF-Wyandotte
(USA).
Cell culture medium and related chemicals were
obtained from Flobio (Paris, France), fetal calf serum from
IBF (Paris, France).
0
590
AND
1990
Butterworth-Heinemann
Ltd. 0142-96
1 Z/90/080590-06
Oegrauon of aiky’cyenoacrykte
METHODS
Nanoparticle preparation. Nanoparticles were prepared by
polymerization of the alkylcyanoacrylate monomers in an
aqueous solution as described previously”. The polymerization medium contained HCI (0.01 N), Tween 20
(0.36%)
for the production of polymeth~~yanoac~late
particles (PMCA) or dextran 70 (1%) and glucose (5%) for
the polymerization of polyethyf- (PECA), polyisobutyl- (PISCA)
and polyisohexylcyanoacrylate particles (PIHCA). The particle
radii were 102 nm (PMCA), 155 nm (PECA), 165 (PIBCA)
and 68 nm (PIHCA). The nanoparticles were used in the
experiments dispersed in their polymerization medium
(nanopa~icle suspension f % w/w).
Nanoparticle modification. PIHCA nanoparticfe suspension
(1% w/w) was mixed with an equal volume of a Poloxamer
407 or Poloxamine 908 solution (1% w/w polymer in
distilled water) and incubated overnight. The polymers
adsorbed on the particles, forming a hydrophilic coat. These
coating layers were measured by photon correlation spectroscopy (PCS) and found to be 6.4 nm (+ 0.3 nm) for
Poloxamer 407 and 7.5 nm (F 0.4 nm) for Poloxamine 908.
The coating layers increased the PCS panicle radius by 6.47.5 nm, which is equivalent to about 5%, which can be a
significant increase, detected by PCS. Aggregation of the
particles was monitored using the PCS polydispersity index.
Swelling effects were excluded by using uncoated particles
as a control. No swelling period was observed with
uncoated particles during the incu~tion, because equilibrated
aqueous particle suspensions were used. This avoided
swelling effects occurring after redispersion of freeze-dried
particles. Nanoparticles were ffuorescently labelled by
addition of propidium iodide during the polymerization
process of the cyanoacrylate monomers*‘, leading to a
propidium iodide content of 0.3% (w/w). The content was
determined by measuring the remaining free propidium
iodide in the dispersion medium by spe~trophotomet~
(absorption at 285 nm).
Degradation experiments. Degradation of the nanoparticles
was followed by spectrophotometric measurements using a
Uvikon 8 10 (Kontron Instruments, FRG). A multiple cuvette
carriage allowed the performance of five degradation studies
simultaneously. The reduction in light transmission caused
by the nanoparticles was determined at 400 nm, a wavelength with a linear relationship between r~uction in light
transmission and nanoparticle concentrated (0.2-0.8 mg/
ml). Although the reduction in light transmission is caused
by light scattering and not by absorption, the term absorption
is used in this paper. The standard deviation of the
absorption data was generally found to be between 5 and
10%.
Degradation was studied during incubation of nanoparticles in aquaous solutions with a pH adjusted by NaOH
(pH 10 and 12) and in isotonic phosphate buffer at pH 7.4.
Experiments were also performed using MEM cell culture
medium and fetal calf serum as the incubation medium.
THEORETICAL
Spectrophotometric
assay
Absorption measurements with a spectrometer can be
employad when the degradation takes place by surface
erosion rather than by bulk hydrolysis. Polyalkylcyano-
nanoparticles: R.H. MiNer er al.
acrylate nanoparticles degrade mainly by surface erosion, as
indicated by the size reduction during the degradation
process2’. An immediate, continuous decrease in particle
diameter was shown by size measurements using PCS”‘.
PCS can be used to follow particle degradation as a
function of size, but only for the initial phase of the
degradation process. After the initial drop in particle size, a
plateau and a size increase were observed”. This effect
occurred when most small particles had disappeared. Larger
particles and aggregates remained in the sample. Owing to the
measuring principle of PCS, which is based on the scattered
light intensity, the larger particles contribute more to the
calculated mean PCS diameter. This led to the size increase
found by PCS. Although the disappearance of particles by
degradation can be monitored using the PCS count rate, this
is a relatively expensive apparatus for particle concentration
measurement and limited in its availability. It was therefore
replaced by a spectrophotometric assay.
The measured absorption depended on particle size
but also on particle concentration. At the beginning and at
the intermediate phase of the degradation, the reduction in
the measured absorption was only due to the size decrease.
Towards the end, the concentration was reduced, due to the
dissolution of particles contributing to the observed decay in
absorption. This decreased particle concentration is detected
by an absorption measurement, but leads to an apparent
particle size increase in PCS measurements2’. For an ideal
monodisperse particle population, the reduction in absorption
will be determined by the size decrease until final dissolution
of the degraded particles.
Data analysis
Absorption measurements provided information about the
time required for 100% degradation of the particles. For fast
degrading nanoparticles (e.g. PMCA and PECA), a decay to
zero absorption can be measured within minutes to a few
hours, representing the time required for 100% degradation
t(deg) 100%. Degradation media containing physiol~ical
salt concentrations (e.g. 0.14 M NaCl) caused some particle
aggregation after a few hours.
For slowly degrading nanoparticles (e.g. PIHCA) a
decrease in absorption occurred over larger time periods
(e.g. 24 h) and therefore did not permit us to determine
directly t (deg) 100%. To characterize slow degrading particles
in physiological salt concentrations, a t 50% of the absorption
can be used instead (r(abs)50%).
The semilogarithmi~ plot of the absorption data yields
a straight line, indicating pseudo-first order kinetics for the
hydrolytic degradation of the polymer. From this plot, a
t50% value of absorption (t(abs)50%) based on measured
data can be obtained tocharacterize the degradation velocity.
If a 50% degradation does not occur during the observation
period or if a particle aggregation takes place, a t(abs)50%
can be extrapolated. It should be noted that the absorption
decays, not linearly, but exponentially with decreasing
particle size. For example, the r(abs)50%
of a 200 nm
particles corresponds to a size decrease of < 50% when
considering the relation between scattering intensity and
particle size for particles up to 200 nm. Calculating the
reduction in the volume of spherical particles when reducing
the size from 200 to 130 nm, this is equivalent to a decrease
in polymer mass of 60%. For all particles, a theoretical
t(abs)O% which is equivalent to a r(deg)lOO%
can be
extrapolated from the semil~ar~thmic plot. From the slope
of the semilogarithmic plot, a degradation rate constant
Biomaterials
1990. Vol 7 I October
591
Begration of al~l~affo~~late
nanopartictes: Rff. artier
et al.
0
0,O
40
20
0
20
60
TIME (min)
I
I
0,2
0,4
1
I
0,s
0,8
I,0
I
TiME(hours)
Figure ;I Degradation of PACA nanoparticles in NaOH, the fast degrading
PMCA cm) and PECA (0) at pH 10, the slower degrading P&Y
(+) and
PitfCA (@I_) pfi 12.
at
kfabs) can be obtained or alternatively
f (abs)50% (K = inZ/f (abs)50%).
calculated
using
Figure 2
Degrsdatidn of PMCA fmj and PECA {O)
isotonic, physiotogica~ phosphate buffer (pH 7.4).
nanoparticles
in
This yielded 20 and 75 min for PMCA and PECA, respectively.
These values were close to the measured zero absorption
values in Figure
2. The degradation rate constants k(abs)
calculated from the slope were -0.071
and -0.223
min-’
for PMCA and PECA, respectively.
The semilogarithmic plot of the absorption values
obtained with PIBCA and PIHCA nanoparticles in NaOH
2,o
RESULTS AND DISCUSSION
Influence of alkyl~hain on particle degradation
Polyalkylcyanoacrylates can be degraded by hydrolysis in
sodium hydroxide whereby the rate of degradation decreases
with increasing length 0; the alkyl chain”. PMCA and PECA
nanoparticles degrade very quickly in NaOH at pH 10
(Figure I) with corresponding t(deg)lOO%
values of C.
3 min. The degradation velocity of PIBCA and PIHCA is too
slow at pH 10 to measure a distinct decrease in absorption
over a period of 1 h. At pH 12, a fast initial decay was
observed. The decrease in absorption decelerated after some
time, due to particle aggregation caused by the ionic strength
of the dispersion medium. In such cases, a direct d~ermination
of t(deQ) 100% was not possible and could only be
extrapolated.
The differences in the hydrolytic degradation of the
nanoparticles corresponded to the relative decomposition
rate of the polymers’ ‘. There was a large difference between
the fast-degrading PMCA and PECA and the slow-degrading
PIBCA and PIHCA, as indicated by the one hundred fold
higher hydroxyl ion concentration required. This should
result in different kinetics of drug liberation and release of
possibly cytotoxic degradation products. The faster release
of degradation products affects the cytotoxicity of the
nanoparticles’3.
The hydroi~ic degradation of PMCA and PECA in
NaOH at pH 10 was too fast to differentiate between the
two. Studies in physiological phosphate buffer at pH 7.4
showed a faster degradation for PMCA and yielded information about the hydrolytic contribution to the degradation
under physiological conditions (figure 2). The absorption
decaystozero(f(abs)O%)in20
minforPMCAandin60
min
for PECA. From these experiments, nanoparticles can be
placed in order of decreasing hydrolytic degradation velocity:
PMCA > PECA > PIBCA > PIHCA.
By plotting the absorption data in a semilogarithmic
manner and a straightline fit, the theoretical r(d~)~OO%
was obtained by the interception with thex-axis (Figure
3s).
592
Homaterials
t990,
Vol 11 October
0
20
80
40
80
TIME (min)
Figure3e
Semilogarithmic plot of absorption dare for PMCA (ml and
PECA (0) nanopariicles in PBS at pH 7.4. The interception of tl;e fitted
straight Iine with the x-axis yields the theoretical t (degl 1DO%.
2,o
196
03
090
0,5
1,o
1,s
2,o
2,s
TIME (hours)
Figure 3b
Semilogarithmic plot of absorption data for PfECA {8I and
PIHCA fl/ nanoparticles in NaOfi a? pH 12. The extrapolation of the fitted
straight line u&g the data~jnts
of the initial degradation phase yields the
theoreticai tfdegj t 00%.
&g&ion
in different
media
The influence of the medium on the degradation of PECA
nanoparticles at pH 7.4 is shown in Figure 4. Compared to
the hydrolytic degradation in phosphate buffer, acceleration
was observed in the cell culture medium. This acceleration
was attributed to the presence of esterases because of the
5% FCS in the medium. Esterases are still active in serum,
e.g. the activity of choline esterase in FCS was found to be
770 munit/ml. However, inactivation of the serum reduced
the esterase activity. Heating to 40°C for 30 min reduced
the activity moderately to 650 munit/ml, whereas inactivation at 80°C (2 min) removed the activity (18 mu&/ml).
Therefore active FCS was used in the studies. The contribution
of esterases was described for the in vivu degradation of
alkyl~yanoac~iates’6.
The further accelerated particle
degradation observed in FCS supported this assumption
(Figure
nanopart~cies: R.H. Miiller et al.
loo
yielded only a straight line for the initial phase of the
degradation. interference of the decreasing absorption
caused by particle degradation and increasing absorption
due to particle aggregation led to the positive deviation
(Figure 3b). The theoretical t(deg)lOO%
in NaOH (pH 12)
obtained by extrapolation were 18 min (PIBCA) and 127 min
(PIHCA), the velocity constants -15.14
and -2.1 7 h-‘,
respectively.
Degradation
of ai~l~anoac~tare
s
20
1
8
6
12
I
I
18
24
TIME (hours)
Figure 5
Degradation of Plt?CA in cell culture medium
fetal calf serum) (-G-j and in fetal calf serum l-t).
(containing 5%
4).
The enzymatic degradation played a more important
role for the slowly degrading PIBCA and PIHCA. In buffer at
pH 7.4, no reduction in absorption could be observed for
PIBCA over a period of 10 h, but a decrease was found in cell
culture medium and, still more marked, in serum (Figure 5).
This was in agreement with in viva degradation studies
describing the excretion of 80% of radioactive PIBCA
polymer within 3 d’*.
For PIBCA, the semilogarithmic plot of the absorption
data in cell culture medium showed a positive deviation
from the straight line (Figure 6). The straight line in Figure 6
was fitted using only data points obtained during the first
2 h, when distortion by aggregation was minor. PIBCA data
points measured between 2 and 18 h are above the fitted
line (positive deviation) due to aggregation and must not be
included in the fit. This is an identical effect to that discussed
above (Figure 36). In serum, the particles were sterically
8
18
12
TIME
24
(hours)
Figure 6
Semiiogarifhmicplot of absorption data from PlsCA {Figure 51 in
ceil culture medium (0) and in fetal calf serum (mJ. Only data points
obtained during the first 2 h of degradation were used for the fit (not all data
points used for the calculation are plotted in the figure): for explanation
compare text.
stabilized against aggregation by an adsorbed serum
albumin layer. This excluded a positive deviation (Figure 6).
On the contrary, a tendency towards a negative deviation
was observed when applying the same fit procedure as for
the culture medium (fit through data points obtained within
the first 2 h). This might be possibly due to some superposition
of the pseudo-first order degradation kinetic in aqueous
media with the zero order kinetics resulting from enzymatic
degradation. This effect was only observed with slowly
degrading nanoparticles where the enzymatic degradation
played a more important role.
Degradation
TIME (min)
Figure
(-II-).
4
Degradation of PECA nanopanicles atpH 7.4inphosphate
cell culture medium (+)
and fetal calf serum (-+-I.
buffer
of surface-modified
nanoparticles
To determine whether polymer coating layers on nanoparticles could influence the degradation velocity, Poloxamer
407 and Poloxamine 908-coated PIHCA nanoparticles were
degraded in NaDH at pH 12 (Figure 7). No distinct
differences were found over the initial degradation period of
1 h. During this time, particle aggregation interferred little
with the assay of the uncoated particles (deceleration of
decrease in absorption); aggregation cannot take place for
Biomaterials
1990, Voi 11 October
593
Degration of af~~~anoa~~iate
nanoparticles: ff. H. ~~tlef
et a/.
40
20
0,o
0;2
0,s
0,8
0.8.
1
0
2
3
TIME
TIME (hours)
Figure 7 Degradation of uncoated PM&A fi3) particles and particles
coated with PIHCA 407 (0) and PIHCA 908 /8) in NaOH (pH 121 over a
period of 1 h.
1
*m
1,O
(hours)
4
5
Figure8
Degradation of uncoated PIHCA (m) particles and particles
coated with PIHCA 407 (0) and PIHCA 908 (+) in setum over a period
ofdh.
the sterically stabilized Poloxamer- and Poloxamine-coated
particles l5 . The similar decay in absorption for coated and
uncoated nanoparticles indicated no effect of the coating
layers on degradation velocity. After 60 min increased
aggregation was observed for the uncoated particles as
shown in Figure 36. However, after 145 min the coated
particles were fully degrade which is close to the theoretical
value of 127 min calculated from the fit in Figure 36.
’
An identical decay for uncoated PIHCA and coated
PIHCA particles was also observed in serum (Figure 8). In
serum, the uncoated particles are sterically stabilized by
adsorbed serum proteins, minimizing interference byaggreg&ion. In serum the Poloxamer and Poloxamine coating also
had no effect on the enzymatic d~radation
process. This
allows the use of Poloxamer 407 and Poloxamine 908 as
aggregation-avoiding agents, e.g. in long-term degradation
studies where particle aggregation can cause distortions.
Degradation Of flUOr88C8ntly labelled nanOpartiCleS
The incor~ration of fluorescent markers can change particle
properties such as surface hydrophobicityor particle charge15.
However, no effect was observed on the degradation when
incubating PIHCA nanoparticles labelled with propidium
iodide in NaOH and in cell culture medium (Figures 9 and
70). This result permits the use of fluorescently labelled
cyanoacrylate nanoparticles for easy detection in cell culture
studies. The degradation rate, an important parameter
determining the cytotoxicity of the nanoparticles’, was
therefore not affected by the labelling.
This spectrophotometric method could also be employed
to measure the effects of drug incorporation on to nanoparticle degradation. The dependence of the release rate of
incorporated compounds on the degradation can be assessed
by a simultaneous assay of particle degradation and drug
release rate.
The photometric assay was found to be simple, fast and easy
for the determination of nanoparticle degradation. It required
no sophisticated equipment as for PCS.
Basic information can be obtained about the relative
Biomaterials
)
OS0
r
6
I
I
0,6
0.4
0.2
0.8
I
180
TIME (hours)
Figure 9
Degradation of PlHCA (OJ nanoparticles and particles fiuorescently labelled with PIHCAIP (+) in NaOH (pH 12) within 1 h.
60
1
60
I
0
I
I
6
12
I
18
I
24
TIME (hours)
Figure 10
Degradation of PIHCA (0) nanoparticles and particles fluoresce&y labekl with PlHCAiP/eJ in cell wfture medium within apet&i of 24 h.
CONCLUSIONS
594
0
1990, Vol I 1 October
hydrolytic degradation of different polymeric particles in
aqueous media. Furthermore, hydrolytic degradation of
slowly degrading particles can be measured in accelerated
assays, e.g. increasing hydroxyl ion concentration.
Degrarion of alkylcyanoacrylate
In contrast to the chemical methods which measure
sometimes complex degradation products, the drug releasedetermining process of particle erosion is directly monitored
in our method.
Finally, the degradation can be studied in different
media to simulate degradation under in vitro or in viva
conditions (cell cultures, incubation with blood). Assessment
of the effect of nanoparticle modification (surface coating,
labelling, drug incorporation) is also possible.
8
9
10
11
ACKNOWLEDGEMENT
12
The research was supported within the framework of the
Biotechnology programme by the Commission of the
European Community, to whom we would like to express our
sincere thanks.
13
14
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1990, Vol 7 1 October
595