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Nanocomposite From Depolymerized PET Waste For Food packaging Application
5
Chapter-2
LITERATURE REVIEW
Polyethyleneterephthalate (PET)
PET is considered as one of the most important engineering polymers in the past two
decades due to rapid growth in its use. It is regarded as an excellent material for many
applications and is widely used for making liquid containers (bottles). It has excellent tensile
and impact strength, chemical resistance, clarity, process ability, color ability and reasonable
thermal stability.38
Many companies produce virgin PET globally giving it different trade
names.39-40
Commercial PET has a wide range of intrinsic viscosity [η] that varies from 0.45
to 1.2 dl g-1
with a polydispersity index generally equal to 2. The PET chain is considered to
be stiff above the glass transition temperature (Tg) unlike many other polymers. The low
flexibility of the PET chain is a result of the nature of short ethylene group and the presence
of p-phenylene group. This chain inflexibility significantly affects PET structure-related
properties such as thermal transitions.40-41
PET production process involves two different starting reactions. The first starting
reaction is an esterification reaction where terephthalic acid (TPA) reacts with ethylene
glycol (EG) at a temperature of between 240 oC and 260
oC and a pressure between 300 and
500 kPa. The second reaction is trans-esterification reaction, where dimethyl terephthalate
(DMT) is reacted with EG at 150 oC
42, 180–210
oC
39, 140–220
oC at 100 kPa
43shown in
Scheme 2.1. Trans-esterification is the much preferred process due to easier purification.
The output of both these processes is BHET. The pre-polymerization step follows in which
BHET is polymerized to a degree of polymerization (DP) of up to 30. Pre-polymerization
reactions conditions are 250–280 oC at 2–3 kPa.
39-40 The third stage is the polycondensation
Nanocomposite From Depolymerized PET Waste For Food packaging Application
6
process, where the DP is further increased to 100. Up to this stage, PET is suitable for
applications that do not require high molecular weight (MW) or [η] such as fibers and sheets.
Solid state polymerization (SSP) might be required to produce a high MW PET. SSP is used
to increase the DP to 150, and also increasing MW. SSP operating conditions are 200–240
oC at 100 kPa for 5–25 h.
43 Bottle grade PET that has an [η] of 0.7–0.81 dl g
-1 is normally
produced by SSP at 210 oC for around 15–20 h.
44-45
COOH
COOH
TPA
CH3COO
CH3COO
DMT
COOCH2CH2OH
COOCH2CH2OH
BHET
HOCH2CH
2OH
Direct esterification-H
20
HOCH2CH
2OH
Transesterification catalyst
-CH3OH
-HOCH2CH
2OH
Polycondensation
Catalyst
HOH2CH2COOC COOCH2CH2OH
130-150
PET
Scheme 2.1: PET polymerization process
Virgin PET manufacturers have tended in recent years to produce PET co-polymer;
such as isophthalic acid modified PET, rather than homopolymer PET. PET bottles are
normally made from co-polymer PET because of its lower crystallinity, improved ductility,
better process ability and better clarity.46-47
Nanocomposite From Depolymerized PET Waste For Food packaging Application
7
Virgin PET Thermal Transitions and Crystallization
Commercial PET has a melting temperature (Tm) of between 255 and 265 oC and for
more crystalline PET is 265 oC.
42 Tg of virgin PET varies between 67 and 140
oC. The
thermal transitions and crystallization of virgin PET with a focus on reversing crystallization
and melting have been analyzed by several researchers.48-49
An interesting phenomenon was
reported in which the virgin PET experiences multiple endothermic transition during thermal
analysis.48-50
It was reported that this phenomenon is attributable to morphological and
structural re-organization. As the temperature increases, better crystal structures are
achieved because of the re-organization of the less perfect crystals. Virgin PET is well
known for having very slow crystallization rate. The highest crystallization rate takes place
at 170 oC
42, or 190
oC.
41 Cooling PET rapidly from the melt to a temperature below Tg can
produce an amorphous, transparent PET. Semi-crystalline PET can be obtained by heating
the solid amorphous PET to a temperature above Tg where 30 % crystallinity can be
achieved.41
The rate of crystallization of virgin PET depends greatly on temperature and
reaches its maximum at a temperature of 150–180 oC. The rate of crystallization also
depends on other factors such as MW, the presence of nucleating agents, the degree of chain
orientation, the nature of the polymerization catalyst used in the original production of PET
and the thermal history.39
PET Applications and Processing
PET is used broadly in products such as bottles, electrical and electronic instruments,
automobile products, house-wares, lighting products, power tools, material handling
equipment and sporting goods.39
PET films and fibers are the oldest applications of PET.
Films are produced by biaxial orientation through heat and drawing. PET films are used in
Nanocomposite From Depolymerized PET Waste For Food packaging Application
8
photographic applications, X rays sheets and in food packaging.40
PET films are also
reported to be used in electrical and for recording tapes.42
PET is also used as an electrical
insulator. PET’s insulating properties are regarded as good due to the severe restriction of
the dipole orientation at room temperature that is well below the transition temperature.42
PET fibers are another important application of PET and are produced by forcing molten
PET through small holes in a die. Fiber strength is achieved by applying tension to align the
chains through uniaxial stretching. Virgin PET is produced at different specifications
because different application requires different properties.51
PET granules can be processed
in many ways depending on the application and the final product requirements. The main
PET processes are extrusion, injection moulding and blow moulding.
PET/Montmorillonite Clay Nanocomposites
Polymer/clay nanocomposites are synthesized via melt-intercalation, common solvent
mixing, or in situ polymerization.52
In the process of melt mixing, the layered silicate is
mixed with a molten polymer matrix. If the silicate surfaces are sufficiently compatible with
the chosen polymer, then the polymer can enter the interlayer space and form either an
intercalated or an exfoliated nanocomposite.53
Exfoliation or a high level of intercalation, is
important in producing a polymer/clay nanocomposite, with such separation of individual
clay sheets the high aspect ratios are obtained with the inorganic reinforcing materials. The
synthesis of PET clay nanocomposites has not been as successful as compared with other
polymers. Takekoshi et-al54
prepared polyester clay nanocomposites via in situ
polymerization with quaternary ammonium salt modified clay and cyclic PET oligomers.
They observed good nanoparticle dispersion and improved physical properties, such as
improved impact strength and elastic modulus. A more commercially viable approach with
Nanocomposite From Depolymerized PET Waste For Food packaging Application
9
conventional polymer processing techniques is melt-mixing of the polyester with an
organicallymodified-clay.55
However, as Matayabas et al56
found, this approach has been far
less successful usually leading to poorly dispersed clay particles. This may be attributed to
the low decomposition temperature (250 °C) of the organic modifier bound to the clay
surface.
Need for PET Recycling
PET is saturated polyester of terephthalic acid and ethylene glycol. The growing
interest in PET recycling is due its widespread use mainly as jars and bottles. Since the
middle of the 1970s, first in the USA and Canada and subsequently in Western Europe,
increased quantities of PET are used for the production of soft drink bottles, and a further
increase in its application in this area is predicted. The overall world consumption of PET
currently amounts to about 13 million tons, of which 9.5 million tons is processed by the
textiles industry, 2 million tons is used in the manufacture of audio and video tapes, and 1.5
million tons is used in the manufacture of various types of packaging mainly bottles and jars.
PET is seen as a noxious material due to. its high resistance to the atmospheric and biological
agents. Ecological as well as economic considerations advocate the introduction of wide-
scale PET recycling, similar to the recycling of traditional materials such as glass, paper, or
metals.57
Classification of Polymer Recycle
Polymer recycling can be classified into four categories e.g. primary, secondary, tertiary and
quaternary recycling.
Nanocomposite From Depolymerized PET Waste For Food packaging Application
10
1. Primary Recycling (Pre-Consumer Industrial Scrap)
It is the recycling of clean, uncontaminated single-type waste which remains the most
popular, as it ensures simplicity and low cost, especially when done ‘‘in-plant’’ and feeding
with scrap of controlled history.58
The recycled scrap or waste is either mixed with virgin
material to assure product quality or used as a second-grade material.59
Primary recycling of
industrial scrap produced during the manufacture of food-contact articles is not expected to
pose a hazard to the consumer.
2. Mechanical Recycling (Secondary Recycling)
In this approach, the polymer is separated from its associated contaminants and it can
be readily reprocessed into granules by conventional melt extrusion. Mechanical recycling
includes the sorting and separation of the wastes, size reduction; melt filtration and reforming
of the plastic material. The basic polymer is not altered during the process. The main
disadvantage of this type of recycling is the deterioration of product properties in every
cycle. This occurs since the molecular weight of the recycled resin is reduced due to chain-
scission reactions caused by the presence of water and trace acidic impurities. A secondary
recycling process presents some unique problems that may cause it to be inappropriate for the
production of food-contact articles, particularly if the recycler had little or no control over the
waste stream entering the recycling facility.60
3. Chemical Recycling (Tertiary Recycling)
Unlike physical recycling, chemical recycling involves transformation of polymer
chain. The polymer backbone under the recycling process is degraded into monomer units
(i.e. depolymerization) or randomly ruptured into larger chain fragments (i.e. random chain
scission) with associated formation of gaseous products. The chemical recycling is carried
Nanocomposite From Depolymerized PET Waste For Food packaging Application
11
out either by solvolysis or by pyrolysis; the former through degradation by solvents including
water and the latter through degradation by heat in absence of air or vacuum. Chemical
recycling yields monomers, petroleum liquids and gases. Monomers are purified by
distillation and drying, and used for manufacture of polymers.
4. Energy Recovery (Quaternary Recycling)
The energy content of the plastics waste can be recovered by incineration. When the
collection, sorting and separation of plastics waste are difficult or economically not viable, or
the waste is toxic and hazardous to handle, the best waste management option is incineration
to recover the chemical energy stored in plastics waste in the form of thermal energy. This is
carried out in special type of reactors called incinerators, to burn wastes in the presence of air
in a controlled manner to convert hydrocarbons of the plastic into carbon dioxide and water.
The heat produced by burning plastics in the waste in the form of superheated steam can be
utilized for generating electricity through turbine generators and the residual heat from the
waste stream for heating residential and industrial buildings. The melt residue from the
incinerator is free from toxicity hazards and may be disposed off by landfill. It should admit
that it is not possible to have zero-emission in the incineration of waste plastic. Apart from
the aforementioned methods, direct reuse of a plastic material (i.e., PET) could be considered
as a ‘‘zero-order’’ recycling technique.58
Worldwide, the main end-use of post-consumed
PET is for the production of fibers (almost 70 %), with only 4 % of PET recycled with
chemical methods.
Among the above recycling techniques, the only one acceptable according to the
principles of sustainable development is chemical recycling, since it leads to the formation of
the raw materials (monomers) from which the polymer is made.59
In this way the
Nanocomposite From Depolymerized PET Waste For Food packaging Application
12
environment is not surcharged and there is no need for extra resources (monomers) for the
production of PET.
PET Chemical-Recycling Techniques
The world’s most recyclable polymer is polyester. PET is polyester with functional
ester groups that can be cleaved by some reagents, such as water (hydrolysis), alcohols
(alcoholysis), acids (acidolysis), glycols (glycolysis), and amines (aminolysis). The recycled
PET is mostly used in the form of fibers, films, foams, sheets, bottles etc. Thus, chemical-
recycling processes for PET are divided as follows: (i) hydrolysis, (ii) glycolysis, (iii)
methanolysis and (iv) other processes. The chemical recycling of PET is discussed in
Scheme 2.2.
Scheme 2.2: Chemical-recycling processes for PET
According to the reagent used, different products are obtained. The main depolymerization
processes that have reached commercial maturity up to now are glycolysis and methanolysis.
Chemical Recycling of PET
Glycolysis
Main Product
BHET + Oligomers
Methanolysis
Main Product
DMT + EG
Hydrolysis
Main Product
TPA +EG
Other Processes
Aminolysis
Ammonolysis
Acid Alkaline Neutral
Nanocomposite From Depolymerized PET Waste For Food packaging Application
13
Nowadays there is growing interest in hydrolysis for the chemical recycling of PET, since it
is the only method with the reaction products TPA and EG, i.e. the monomer from which
PET is produced. This is associated with the trend in the new factories for PET synthesis to
produce it directly from TPA and EG, thus replacing DMT (the traditional monomer) from
the technological process. The main disadvantage of this method is the use of high
temperature (200–250 oC) and pressure (1.4–2 MPa) as well as long time needed for
complete depolymerization. Commercially, hydrolysis is not widely used to produce food-
grade recycled PET, because of the cost associated with purification of the recycled TPA.
Hydrolysis of PET can be carried out as (a) alkaline hydrolysis, (b) acid hydrolysis and (c)
neutral hydrolysis. Among previous chemical recycling methods, a recent growing interest
has been applied for the production of specialized products such as saturated, unsaturated
polyester resins, polyurethane and polymer concrete using glycolysis due to consumer needs
and cost.
Glycolysis
Another most important method in chemical processing of PET is glycolysis. This
process is used widely on a commercial scale. The glycolysis reaction is the molecular
degradation of PET polymer by glycols, in the presence of trans-esterification catalysts,
mainly metal acetates, where ester linkages are broken and replaced with hydroxyl terminals.
PET degradation is carried out most frequently using EG,61–67
DEG,68–70
, PG,69–71
and
DPG.66, 71
etc. Research concerning this process has been mainly conducted from the point
of view of the utilization of the products obtained; very few works have been devoted to the
description of the kinetics of glycolysis reactions.63, 65, 72
The process is conducted in a wide
range of temperatures 180–250 oC,
72–76 during a time period of 0.5–8 h. Usually 0.5 % by
Nanocomposite From Depolymerized PET Waste For Food packaging Application
14
weight of catalyst (most often zinc acetate) in relation to the PET content is added. Much
attention has been devoted to glycolysis by EG. In this system, the effect of the reaction
parameters, i.e., temperature (190–240 oC), pressure (0.1–0.6 MPa) and PET to EG ratio on
the reaction rate has been investigated.65
It has been observed that the rate of the reaction is
proportional to the square of the EG concentration at constant temperature, pressure and PET
concentration.
PET glycolyzates found application in the manufacture of unsaturated polyester
resins,69, 70, 74, 76–81
polyurethane foams,67, 71, 73, 82–85
, and polyisocyanurate foams.61, 63–66, 72, 83
One of the first method of the synthesis of unsaturated polyester resins (UPR), was
developed by Ostrysz.86
in which partial PET glycolyzed product was used. The product of
partial PET glycolysis was applied together with maleic anhydride and propylene glycol so
as to obtain unsaturated polyester. After dissolving the synthesized polyester alkyd in
styrene, UPR resin was obtained. During the following years, the Industrial Chemistry
Research Institute in Warsaw developed technology for the production of UPR with built-in
segments of oligo(ethylene terephthalate) obtained as a result of partial PET waste glycolysis
with propylene glycol at a temperature of 200 oC (240–250
oC) and a reaction time of 2 h.
68,
76 Due to difficulties in obtaining a glycolyzates with reproducible properties, a new type of
unsaturated polyester has been evolved, containing ethylene-diethylene diester obtained as a
result of PET degradation by diethylene glycol as its terephthalic part. This resin was used in
the production of polyester molding compounds.87
Recently, there is an increased interest in
the manufacture of UPR, utilizing PET waste. In one of the patents81
, PET glycolysis
products undergo a reaction with MA and subsequently a reaction with di-cyclopentadiene
Nanocomposite From Depolymerized PET Waste For Food packaging Application
15
(DCP). The polyesters obtained have wide possibilities of application, e.g., for gel coats,
casting marble, bath fixtures, car elements, etc.
Interesting research results on the synthesis and viscosity of UPR obtained by
polycondensation of PET glycolysis product and maleic anhydride was published by Kim.74
It was observed that the molecular weights of UPR increase with an increase of PET content
in the reaction system or an increase of the dicarboxylic acid/glycol ratio as well as in the
case of the application of DPG instead of propylene glycol in the same condition of
glycolysis. PET waste can be depolymerized by glycolysis to obtain oligomeric diols and
polyols, or glycolyzed into its monomeric units, (BHET) or DMT.88–90
The influence of various parameters on the kinetics of PET glycolysis by DEG,
temperature profile, catalysis and PET morphology was studied by Francis Pardal.91
The
results showed a strong influence of some experimental conditions (temperature and
catalysis) on the mixture evolution during depolymerization. The temperature study showed
a critical temperature between 210 and 220 oC which seems to be the consequence of a better
diffusion of DEG in PET, allowing easier reactions in solid phase. The initial morphology of
PET scraps does not affect the rates of reactions much, in contrast to the temperature profile,
which has a great importance. Time of PET dissolution at 220 oC is considerably shorter by
heating PET and DEG separately at 220 oC before mixing, than by heating a cold mixture of
the two reagents to 220 oC. PET fibre wastes from an industrial manufacturer was
depolymerized using excess EG in the presence of metal acetate as a transesterification
catalyst. The glycolysis reactions were carried out at the boiling point of EG under nitrogen
atmosphere up to 10 h. Influences of the reaction time, volume of EG, catalysts and their
concentrations on the yield of the glycolysis products were investigated by M. Ghaemy.92
Nanocomposite From Depolymerized PET Waste For Food packaging Application
16
The methods of glycolysis depolymerization with catalyst optimization technique
described by A.S Goje and S. Mishra reveal that it is possible to obtain almost complete and
optimal conversion of PET into value added monomeric products (EG and DMT). Optimal
reactant size is recorded as 127.5 mm. Depolymerization of PET was increased with increase
in the reaction time and temperature. Yields (%) of value added monomeric products DMT
and EG are almost equal to PET conversion. Results suggest that EG does not have a
significant role as an internal catalyst in glycolysis of PET. Depolymerization of PET was
decreased with increase in the particle size of PET. Zinc salt as well as cobalt salt show
identical results and the numerical values were greater than that of lead salt and manganese
salt during glycolysis depolymerization of PET. Zinc salt and cobalt salt appear to have
more catalytic effect on glycolysis seem to influence rates at atmospheric pressure.93
Nanocomposites
Nanocomposites are a new class of composites in which the filler dimensions are in
the nanometer (10-9
m) range.94
The concept of nanoscale reinforcement provides opportunity
for synthesis of new polymer materials with unique properties.95
Conventional composites
are based on microscale reinforcement. However, owing to the large interfacial area per unit
volume94
, dispersion of the inorganic filler at the nanometer scale have led to significant
improvements in the properties of polymer nanocomposites.95
Three types of nanocomposites can be distinguished, depending on how many
dimensions of the dispersed particles are in the nanometer range:
1. When three dimensions are in the order of nanometers, they are called isodimensional
nanoparticles, such as spherical silica nanoparticles.
Nanocomposite From Depolymerized PET Waste For Food packaging Application
17
2. When two dimensions are in the nanometer scale and the third is larger, they form
elongated strucures like nanotubes or whiskers.
3. When only one dimension is in the nanometer range, the filler is in the form of sheets
of one to a few nanometers thick, and to hundreds to thousands nanometer long.
The third type constitutes the family of composites, which can be gathered under the
name of polymer-layered crystal nanocomposites.96
Polymer-layered crystal nanocomposite materials are almost exclusively obtained by
the intercalation of the polymer (or a monomer subsequently polymerized) inside the
galleries of layered host crystals.96
Owing to the nanocomposite structure, they exhibit
concurrent improvements in several material properties, for very moderate inorganic loadings
(typically less than 6 %). Enhanced properties include improved tensile characteristics,
higher heat deflection temperature, higher barrier properties and increased flame retardancy.
At the same time, optical clarity and light weight are largely maintained. Uses for this new
class of materials can be found in aerospace, automotive, electronics and biotechnology
applications, to list only a few.97
There is a wide variety of both synthetic and natural crystalline fillers that are able,
under specific conditions, to intercalate a polymer. Amongst all the potential nanocomposite
precursors, those based on clays and layered silicates have been more widely investigated,
probably because the starting clay minerals are easily available and because their
intercalation chemistry has been studied for a long time.96
Because of its suitable layer
charge density98
, montmorillonite is nowadays the most widely used clay as nanofiller. The
model structure of montmorillonite is given in Scheme 2.3.
Nanocomposite From Depolymerized PET Waste For Food packaging Application
18
Scheme 2.3: The model structure of montmorillonite
It consists of two fused silica tetrahedral sheets sandwiching an edge-shared
octahedral sheet of either aluminum or magnesium hydroxide.
They have charge deficiencies partly due to isomorphous substitutions of Al3+
and
Si4+
in each layer, which are counter balanced by cations, principally sodium and calcium.
Water, other hydroxyl-containing groups and amines readily break these ionic bonds. Once
the sheets have been parted, many layers can be adsorbed producing a marked expansion of
the structure. Under certain conditions, separation of the platelets into primary layers can
occur giving very high aspect ratio products.99
Stacking of the layers leads to regular van der
Waals gaps called interlayers or galleries. The sum of the single layer thickness (9.6 Å) and
the interlayer represents the repeat unit of the multilayer material, so called d-spacing or
basal spacing. The d-spacing between the layers for Na-montmorillonite varies from 9.6 Å
Nanocomposite From Depolymerized PET Waste For Food packaging Application
19
for the clay in the collapsed state to approximately 20 Å when the clay is dispersed in the
water solution. The microstructure of montmorillonite can be seen in Scheme 2.4.
Scheme 2.4: The microstructure of montmorillonite
Clays are in the form of aggregates consisting of primary particles with thickness of
8-10 nm, which contains five to ten lamellae associated by interlayer ions. The grey circles
in the primary particle represent the intercalated cations (Na+, Ca
++, K
+,...). On a larger scale,
each layer can be seen as a high aspect ratio lamella about 100-200 nm in diameter and 1 nm
in thickness.98
Nanocomposite Synthesis Methods
In-Situ Polymerization Method
It is the conventional process used to synthesize thermoset-clay nanocomposites
shown in Scheme 2.5.
Nanocomposite From Depolymerized PET Waste For Food packaging Application
20
Scheme 2.5: In-Situ polymerization method
First, the organoclay is swollen in the monomer. This step requires a certain amount
of time, which depends on the polarity of the monomer molecules, the surface treatment of
the organoclay and the swelling temperature, then the reaction is initiated. For thermoset
such as epoxies or unsaturated polyesters, a curing agent or a peroxide, respectively, is added
to initiate the polymerization. For thermoplastics, the polymerization can be initiated either
by the addition of a curing agent or by an increase of temperature. During the swelling
phase, the high surface energy of the clay attracts polar monomer molecules so that they
diffuse between the clay layers. When a certain equilibrium is reached the diffusion stops and
the clay is swollen in the monomer to a certain extent. When the polymerization is initiated,
the monomer starts to react with the curing agent. Polymer-clay nanocomposites based on
epoxy, unsaturated polyester, polyurethanes and polyethylene terephthalate have been
synthesized by this method.98
Nanocomposite From Depolymerized PET Waste For Food packaging Application
21
The “Melt Intercalation” Process
This process is shown in shown in the scheme 2.6. The layered silicate is mixed with
the polymer matrix in the molten state. Under these conditions and if the layer surfaces are
sufficiently compatible with the chosen polymer, the polymer can crawl into the interlayer
space and form either an intercalated or an exfoliated nanocomposite. In this technique, no
solvent is required.96
Polypropylene nanocomposites are generally synthesized by this
method shown in Scheme 2.6.
Scheme 2.6: Melt intercalation method
The “Solution Intercalation”
The layered silicate is exfoliated into single layers using a solvent in which the
polymer (or a prepolymer in case of insoluble polymers such as polyimide) is soluble. It is
well known that such layered silicates, owing to the weak forces that stack the layers together
can be easily dispersed in an adequate solvent. The polymer then adsorbs onto the
delaminated sheets, and when the solvent is evaporated (or the mixture precipitated), the
Nanocomposite From Depolymerized PET Waste For Food packaging Application
22
sheets reassemble, sandwiching the polymer to form, in the best case, an ordered multilayer
structure96
shown in Scheme 2.7.
Scheme 2.7: The “solution intercalation” method
Nanocomposite Structures
The key to the performance of nano-clays is how well they can be dispersed into a
polymer matrix. Types of dispersion that can be achieved need to be considered. Three
types of structures can be recognized99
in Scheme 2.8.
1. Conventional Composite:
Silicate tactoids exist in their original aggregated state with no intercalation of the
polymer matrix into the galleries. For this case, the particles act as microscale fillers.95
2. Intercalated Nanocomposite:
A single (or sometimes more than one) extended polymer chain is intercalated
between the silicate layers resulting in a well ordered multilayer morphology built up with
alternating polymeric and inorganic layers.96
3. Exfoliated/Delaminated Nanocomposite:
Nanocomposite From Depolymerized PET Waste For Food packaging Application
23
Extensive polymer penetration, resulting in disorder and eventual delamination of the
silicate layer, produces exfoliated structures consisting of inidividual 1 nm thick silicate
layers suspended in the polymer matrix.100
Scheme 2.8: Nanocomposite structures
The fully dispersed form is most useful for the majority of commercial applications,
and is the one that is normally aimed for, although conventional processing methods often
give mixed structures.99
Unsaturated Polyesters and Their Application Areas
Unsaturated polyesters (UP) are linear polycondensation products based on
unsaturated and saturated acids/anhydrides and diols or oxides dissolved in unsaturated vinyl
monomers. They comprise a versatile family of thermosetting materials, which are generally
pale yellow oligomers with a low degree of polymerization. Depending on the chemical
composition and the molecular weight (1200-3000 g/mol), these oligomers may be viscous,
liquids or brittle solids. The unsaturation in the backbone provides sites for reaction with
vinyl monomers using free-radical initiators, leading to the formation of a three-dimensional
Nanocomposite From Depolymerized PET Waste For Food packaging Application
24
network. The solutions of unsaturated polyesters and vinyl monomers which are reactive
diluents are known as UP resins.101
UP resins either in the form of pure resin or in the compounded form with fillers find
a wide range of applications. Their main applications are in the construction industry (non-
reinforced or glass-fiber-reinforced products), automotive industry, and industrial wood and
furniture finishing. Some of the important products based on UP resins are cast items such as
pearl buttons, knife and umbrella handles, and encapsulated electronic assemblies. Polyester
compounds have been formulated for the manufacture of bathroom fixtures. Floor tiles have
been manufactured by mixing UP resin with fillers such as limestone, silica, china clay, and
more. The applications of UP resins in a variety of areas such as transportation, electrical
appliances, and building and construction are largely due to development of bulk and sheet
molding compounds using glass fibers.101
Synthesis, Curing and Casting of Unsaturated Polyester Resins
The polyester backbone is composed of three basic types of structural units Scheme
2.9. They are synthesized by the polycondensation reaction of a saturated acid or anhydride,
an unsaturated acid or anhydride and a glycol. In the case of the general-purpose polyester,
these components usually consist of phthalic acid, maleic acid and propylene glycol.
O
O
O + O +HO
OH
O
O
HOO
O
O
O
CH3
OH
O
O CH3 O
X Y
CH3
Scheme 2.9: Synthesis reaction of UP from maleic anhydride, o-phthalic anhydride and
propylene glycol
Nanocomposite From Depolymerized PET Waste For Food packaging Application
25
The unsaturated acid provides the sites for the cross-linking, the saturated acid determines the
degree of spacing or concentration of the unsaturated acid molecules along the polyester
chains and the glycol, of course, provides the means for esterification and for bridging the
acids to form a prepolymer.102
The obtained unsaturated prepolymer is then diluted in
styrene and the resin solution is cross-linked by the addition of a peroxide initiator.
Unsaturated polyesters are versatile, since a large amount of different glycols and unsaturated
as well as saturated acids can be used to design different polymers. The composition of the
prepolymer and the curing process can be tailored for a specific purpose.103
The curing of
unsaturated polyester resins can be described as a free-radical copolymerization reaction
Scheme 3.0. As there are several double bonds per polyester molecule, the polymerization
proceeds with extensive crosslinking and results in a three-dimensional network.104
Hydroquinone is widely used in commercial resins to provide stability during the
dissolution of the hot prepolymer in styrene. The addition polymerization reaction between
the unsaturated polyester and the styrene monomer is initiated by free-radical catalysts
usually benzoyl peroxide (BPO) or methyl ethyl ketone peroxide (MEKP), which can be
dissociated by heat or redox metal activators like cobalt naphthanate into peroxy and
hydroperoxy free radicals. This catalyst system is temperature sensitive and does not
function effectively at temperatures below 10 oC, but at temperatures over 35
oC, the
generation of free radicals can be too prolific, giving rise to incomplete cross-linking
formation.105
.
Nanocomposite From Depolymerized PET Waste For Food packaging Application
26
C CH CH C O CH2 CH2 O
O O
( )n +RO + CH CH2
Polyester Peroxide initiator Crosslinking agent
Styrene
C CH CH C O CH2 CH2 O
O O
( )n
O R
.
Free radical formed
from double bond
Attatchment of free radical
from initiator
Initiation step
.
C CH CH C O CH2 CH2 O
O O
( )n
OR
.
CH CH2.New free radical
Bond formed between polymer & crosslinking agent
( )
Bridging step( )
.
.
C CH CH C O CH2 CH2 O
O O
( )n
OR
.
CH CH2
.
.
C CH CH C O CH2 CH2 O
O O
( )n. .
Bond between crosslinker & second polymer
Site for other crosslinks
Crosslinked polymers( )
Scheme 3.0: Schematic view of crosslinking of unsaturated polyester
In the casting process, a liquid material is poured into a mold and allowed to solidify
by chemical (e.g., polymerization) means, resulting in a rigid object that generally reproduces
the mold cavity detail with great fidelity. A large number of resins are available and a
variety of molds and casting methods are used in casting processes. Therefore, the choice of
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material, mold type and casting technique is determined by the particular application. In
casting processes, the resin is added with an appropriate amount of hardener, catalyst, or
accelerator, mixed manually or mechanically and then poured into a mold, which is normally
coated with a mold-release agent. Air is removed if necessary, and the resin is allowed to
solidify. The casting process is relatively slow and employs comparatively cheap equipment.
To facilitate the removal of the cast part from the mold, mold releasing agents such as high
melting waxes, silicone oil, greases and some film-forming agents are used to coat the mold.
Among other considerations, the choice of mold-release agents is based upon the absence of
interaction between the resin system and the release agent.106
Sorption and Diffusion Studies of Polymer
Sorption and diffusion of the solvents in and through polymers have been widely
investigated from both theoretical as well as experimental point of view.107–109
The swelling
technique is a commonly used method to determine various coefficients such as diffusion,
sorption, and permeability coefficient.110-114
In swelling experiments, the polymer of known
dimension is dispersed in a solvent and the solvent mass uptake versus time is recorded and
the data is used to calculate the various coefficients. These coefficients give an idea about
the use of polymers in various applications such as membranes, ion-exchangers, controlled
release systems, packaging, microchip manufacturing, etc. Sorption kinetics in polymers
exhibit a variety of deviations from normal Fickian behavior, attributable to (a) slow viscous
relaxations of the swelling polymer or (b) differential swelling stresses generated by the
constraints imposed on local swelling during sorption. Several models have been proposed
for the study of swelling behavior of the polymers.115-120
In situ study by FTIR- is also
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carried out by many researchers for the prediction the sorption behavior of the polymers.118-
120
Polymer nanocomposites are the future of the global industries.121
The polymer nano-
composites are prepared by dispersing a nano-filler into the polymer.120-123
These platelets
are then distributed into a polymer matrix creating multiple parallel layers, which force flow
of gases and liquids through the polymer in a torturous path, forming a complex barrier.124
Different types of fillers are utilized for the preparation of nano-composites. Amongst these,
the most common is a nano-clay called montmorillonite - a layered smectite clay.125-130
Additional nano-fillers include carbon nano-tubes, graphite platelets, carbon nano-fibers,
etc.128,131-133
The barrier properties of the nano-composites are supposed to increase due to
nano-clay loading.124,134
These properties of saturated and unsaturated polyester synthesized
from glycolyzed PET and their nanocomposites are studied in the subsequent chapters.
Response Surface Methodology
Response surface methodology (RSM) is a collection of mathematical and statistical
techniques for empirical model building. By careful design of experiments, the objective is
to optimize a response (output variable), which is influenced by several independent variables
(input variables). An experiment is a series of tests, called runs, in which changes are made
in the input variables in order to identify the reasons for changes in the output response.
Response surface-based methods aim to develop approximate functions that are
surrogates for long running computer codes.135,136
Techniques for constructing response
surfaces in reliability problems can be classified in two broad categories. In methods
developed from statistical sampling theory, factorial designs and regression analyses are used
to fit response surfaces. This approach has been used for studying soil structure interaction
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problems137,138
static nonlinear structures139,140
and to obtain statistics of response for
nonlinear oscillators.141
As the design of experiments is centered around the mean and is
independent of the limit surface geometry, the fitted response surface may not always
conform to the true failure surface, especially, when it is at a great distance from the mean.
Alternative methods, which however, by pass some of the mathematical requirements of
response surfaces, obtain satisfactory results by incorporating reliability concepts for fitting
the response surface in the vicinity of the design point. These methods have been widely
reported in the literature for assessing the reliability of a variety of linear/nonlinear,
static/dynamic problems.142-149
It has been shown, that the failure probability estimates are
highly sensitive to the algorithm parameters.150
Moreover, it is implicitly assumed that the
contribution to the failure probability arises only from a single design point. This leads to
erroneous estimates, when there are multiple design points or multiple regions that make
significant contributions to failure probability.151
Techniques Used for the Characterization of Nanocomposites
Generally, the structure of nanocomposites has typically been established using
WAXRD analysis and transmission electron microscopic (TEM) observation. Due to its
easiness and availability WAXRD is most commonly used to probe the nanocomposite
structure 152-156
and occasionally to study the kinetics of the polymer melt intercalation.157
By monitoring the position, shape and intensity of the basal reflections from the distributed
silicate layers, the nanocomposite structure (intercalated or exfoliated) may be identified.
For example, in an exfoliated nanocomposite, the extensive layer separation associated with
the delamination of the original silicate layers in the polymer matrix results in the eventual
disappearance of any coherent X-ray diffraction from the distributed silicate layers. On the
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other hand, for intercalated nanocomposites, the finite layer expansion associated with the
polymer intercalation results in the appearance of a new basal reflection corresponding to the
larger gallery height.
Although WAXRD offers a convenient method to determine the interlayer spacing of
the silicate layers in the original layered silicates and in the intercalated nanocomposites
(within 1–4 nm), little can be said about the spatial distribution of the silicate layers or any
structural non-homogeneities in nanocomposites. Additionally, some layered silicates
initially do not exhibit well-defined basal reflections. Thus, peak broadening and intensity
decreases are very difficult to study systematically. Therefore, conclusions concerning the
mechanism of nanocomposites formation and their structure based solely on WAXRD
patterns are only tentative. On the other hand, TEM allows a qualitative understanding of the
internal structure, spatial distribution of the various phases, and views of the defect structure
through direct visualization. The WAXRD patterns and corresponding TEM images of three
different types of nanocomposites are presented in Figure 2.1. Both TEM and WAXRD are
essential tools 158
for evaluating nanocomposite structure. However, TEM is time-intensive,
and only gives qualitative information on the sample as a whole, while low-angle peaks in
WAXRD allow quantification of changes in layer spacing. Typically, when layer spacing
exceed 6–7 nm in intercalated nanocomposites or when the layers become relatively
disordered in exfoliated nanocomposites, associated WAXRD features weaken to the point of
not being useful. However, recent simultaneous small angle X-ray scattering (SAXS) and
WAXRD studies yielded quantitative characterization of nanostructure and crystallite
structure in N6 based nanocomposites.159
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Figure 2.1: (a) WAXRD patterns and (b) TEM images of three different types of
nanocomposites.