METHOD FOR THE PURIFICATION AND RECOVERY OF WASTE GELATIN
Field of the Invention
This invention is generally directed to a process for recovery, purifying and
recycling gelatin waste made from gelatin and derivatives thereof and in particular, to
a process for recovery, purifying and recycling gelatin waste, its derivatives, and
components contained within gelatin waste resulting from industrial encapsulation
processes.
Background of the Invention
Gelatin and gelatin derivatives are used to encapsulate the products of several
industries. Examples are described in U.S. Pat. No. 5,074,102, issued to Simpson et
al, and include the encapsulation of medicinal compounds such as drugs and vitamins;
employment of gelatin encapsulation in food packaging, such as for powdered instant
coffee or spices; in candy manufacturing; in fertilization of ornamental plants and/or
indoor plants; in packaging of sensitive seeds in combination with protective agents
and/or fertilizers; and in the packing of single dyestuffs or mixtures of various drugs.
In each of the above-recited manufacturing and production processes, a certain
amount of the encapsulating material and the encapsulated material (e.g. vitamins) is
lost as waste. Frequently, the amount lost as waste of the encapsulating material
approaches 50% or more of the total starting material, depending on the arrangement
of production employed. When considering that the cost of the encapsulating material
in the United States averages approximately $3.10 per pound ($6.82 per kilo) as of
September, 1997, it is clear that the economic consequences of such waste can be
significant. As a result, manufacturers have attempted to off-set poor production
efficiency by recycling the waste material for reuse. Such attempts, however, have not
been met with a great deal of success.
Prior art methods of gelatin recovery and purification suffer from a variety of
shortcomings to be discussed in further detail below. Before these shortcomings can
be fully appreciated, however, the composition of the encapsulation waste material itself
should be further understood. In general, waste material of encapsulation processes
is comprised of a variable number of components added to a gelatin base. Among
them are solvents (usually water); softening agents and oil coatings (when desired);
and, contaminants in the form of residual active ingredients, i.e. the substance being
encapsulated. In addition, colorings and preservatives may also be added. Thus, it can
be observed that successful recycling involves not only the recovery of gelatin from
surrounding oils, but also the removal of the remaining components of the waste in
order to achieve a relatively pure, reusable product.
Extraction has been the principle method for accomplishing removal of oils,
actives and the like in the pharmaceutical industry. While several solvents have been
used in the prior art in an effort to accomplish separation, each suffer from a variety of
shortcomings not the least of which is the necessity of ultimately removing yet another
component, i.e. the solvent itself, from the recycled materials. To date, the most
popular and widely used solvents used to separate gelatin from oils and actives are
chlorinated solvents such as, for example, 1 ,1 ,1 ,-trichloroethane with naphtha. The use
of chlorinated solvents, however, is accompanied by high costs, disposal problems, and
most importantly, environmental concerns. Attempts have been made to use other
solvents including isopropyl alcohol, methyl isobutyl ketone, toluene, hexane, heptane,
acetone, and acetone/water mixtures, but the resulting yields are insufficient and/or the
separation is poor. Furthermore, some of these chemicals are relatively expensive and
present similar environmental, disposal, and safety concerns as the chlorinated
solvents. None of them have been found to separate oils and actives with a high
degree of efficiency.
U.S. Patent No. 5,288,408, issued to Schmidt et al, discloses a method of
recycling gelatin-based encapsulation waste material, and more specifically, to a
process for the recovery and purification of gelatin and softening agents therefrom. In
the preferred embodiment, deionized water is added to the waste material thereby
forming an aqueous solution of gelatin and glycerin dispersed within the remaining oil
and residual active-ingredient components of the waste material. Extraction methods
are employed under specific conditions to effect separation of the lower aqueous phase
from the upper oil phase. The lower phase is hot filtered to remove any remaining
traces of oil or other contaminants and the filtrate is then charged to a concentration
vessel adapted for vacuum distillation. The water solvent is thus removed under
specific thermal and atmospheric conditions until the desired concentration of gelatin
and glycerin is achieved. A pure, concentrated aqueous gelatin-glycerin solution results
which may be stored or further prepared for immediate reuse. Although this process
lends itself to the removal of dyes and active ingredients with additional chemical
reactions and processing, such dyes, active ingredients, and glycerin are not removed
in situ.
Clear gelatin contains no dye, colorants or the like. It is used to make clear
gelatin capsules in the pharmaceutical, neutraceutical, and nutrient industries and other
industries as well. Because dyes are not present, there is a need to provide a cost
efficient and effective manner for recycling the gelatin and glycerin for reuse. Gelatin
may have suspended particles such as titanium dioxide which impart a color to the
gelatin. Such particles can be more easily removed from the waste gelatin than dyes
and colorants which are water soluble.
It would, therefore, be desirable to provide a method for recycling gelatin-based
encapsulation waste material that recycles gelatin and glycerin in situ without the need
for any additional processing. It would be a further advance in the art of recycling waste
gelatin if an in situ process could be developed that is especially effective in recycling
gelatin and gelatin containing suspended particles without thermal degradation in a cost
efficient and effective manner. It would be a still further advance in the art to provide
a cost efficient and effective method of recycling gelatin whether clear or colored and
whether or not the gelatin contains suspended particles (e.g. a colorant).
It would be a still further advance in the art to provide a method of recovering
valuable components from a waste gelatin recovery process.
Summary Of The Invention
The present invention is generally directed to the recovery of waste gelatin alone
or in combination with other components of a waste gelatin product through the
separation and treatment of a waste gelatin stream into an aqueous and non-aqueous
substream.
In one aspect of the present invention there is provided a method of treating a
waste material containing gelatin comprising:
a) combining the waste material and a solvent for the gelatin to form a liquid
containing gelatin;
b) separating the liquid into a solvent based phase or layer and a non-
solvent based phase or layer; and
c) removing residual oils and/or particulates from the solvent based layer to
form a second liquid containing gelatin having a higher purity than the first liquid.
If desired, the second liquid may be concentrated by removing at least some of
the solvent, solvent soluble active ingredients, softening agent, dyes and other solvent
soluble impurities to provide at least a substantially purified second liquid.
Brief Description of the Drawings
The following drawings in which like reference characters indicate like parts are
illustrative of embodiments of the invention and are not intended to limit the invention
as encompassed by the claims forming part of the Application.
Figure 1 is a schematic view of an embodiment of the method of gelatin recovery
and purification in accordance with the present invention; and
Figure 2 is a schematic view of a further embodiment of the invention similar to
Figure 1 in which a separate, external degassing operation is provided to remove
dissolved gases (e.g. air) from the recovered gelatin.
Detailed Description Of The Preferred Embodiments
Gelatin is a protein derivative of collagen obtained, in general, by the boiling of
skin, white connective tissues, and bones of animals, and by the partial hydrolysis of
collagen, in particular. As a colloid it has unique physical properties. Of particular
significance to the present invention is its tendency to stay in solution and its ability to
form dispersions in oils. Gelatin remains a solid at standard atmospheric pressure and
temperature absent the presence of a sufficient quantity of solvent.
Softening agents are sometimes added to plasticize the gelatin when soft, gelatin
shells are desired. Agents such as glycerin, sorbitol, or other similar polyols are
commonly employed as softening agents. Glycerin is a preferred softening agent.
The soft elastic capsule-forming material may be used to enclose active
components in the form of powders, liquids, or combinations thereof. Oils, such as
vitamin A, vitamin E, and beta-carotene, for example, are frequently encapsulated by
such soft gel materials in the pharmaceutical, cosmetic, and nutritional industries.
Additionally, other oils like mineral oil or medium chain triglycerides (MCT's) may be
used to coat the outer surface of the gel-capsule during processing. Thus, it can be
seen that the waste product of the encapsulation process may have, in addition to
gelatin and a softening agent such as glycerin, many components (e.g. oily
components) which must be removed before the gelatin waste is available for reuse as
a relatively pure product. In some instances, coloring agents and preservatives may
also be incorporated into the gelatin mass. Commonly used preservatives include
methylparaben, propylparaben, and sorbic acid.
Present methods of encapsulating active components employ a ribbon or sheet
of gelatin which is then die punched to form capsules. As much as 50% or more of the
gelatin starting material (i.e. gelatin ribbon) is either discarded as a waste by-product
or recycled. The latter option requires the removal of all of the above-mentioned
components. The present invention provides a novel and efficient method of purifying
and recycling the waste material without experiencing the shortcomings of the prior art.
It will be understood that other proteins with ; hysical and chemical properties similar
to gelatin exist and may also be recycled by the present process. Similarly, glycerin is
only one example of a softening agent which may be recovered; thus, neither gelatin
nor glycerin are intended to be limiting.
Reference is now made to Figure 1 wherein an embodiment of the present
invention for the purification and recovery of gelatin and/or glycerin is illustrated. A
suitable solvent such as deionized (D.I.) water is added through a conduit 2 in an
amount sufficient to dissolve the waste gelatin material, typically in an amount of up to
about five volumes, based on the quantity of waste gelatin, preferably from about 0.5
to 5.0 volumes is added to a dissolution/separation vessel 4 which may be provided
with a heating jacket known in the art. The solvent is preheated to a temperature of
from about 30 to 70°C to make the waste gelatin in a convenient flowable condition. The
waste gelatin material is then charged either batchwise or continuously to the
dissolution/separation vessel 4 via a conduit 5 which may be made of stainless steel
or glass-lined construction and sized according to a desired batch size. The
dissolution/separation vessel 4 may also be provided with a conventional agitation
device such as a stirrer (not shown). The waste material to be recovered is diluted with
the solvent (e.g. deionized water) typically at atmospheric pressure under heating at a
temperature from about 30 to 70°C to a preferred concentration of from about 8% to
45% gelatin by weight. Agitation is simultaneously performed to effect dissolution of the
gelatin and the softening agent (e.g. glycerin).
A solution of gelatin and glycerin [i.e. solvent based layer (e.g. aqueous layer)]
is thus formed within the remaining oily component and residual active-ingredient
components [i.e. non-solvent based layer (e.g. non-aqueous layer)]. As used herein
the term "solvent based layer" shall mean a layer or phase in which the components
contained therein are dissolved in the solvent. The term "non-solvent based layer" shall
mean a layer or phase in which the components therein do not dissolve in the solvent
and therefore may be separated from the solvent based layer. Since water is the
preferred solvent, reference will be made hereinafter to the aqueous layer and non-
aqueous layer.
The above recited concentration level of gelatin (from about 8% to 45%) is a
preferred concentration for achieving rapid and thorough separation of the upper non-
solvent based layer (e.g. non-aqueous layer) from a lower solvent based layer (e.g.
aqueous layer). The upper non-aqueous layer is either discarded or sent via a conduit
6 to a recycling system 8 which is known in the art. If recycled, the non-aqueous layer
may be separated into oily components including, but not limited to, vitamins (for
vitamin containing products (e.g. vitamin E)), mineral oil, garlic oil, fish oil, beta
carotene, and vitamin E, which emerge through conduit 10.
Once the gelatin is completely dissolved within the vessel 4, agitation is
terminated and the mass is allowed to either 1 ) stand to effect separation of the solvent
based layer (e.g. aqueous layer) from the non-aqueous layer then further processed to
remove residual oils and/or particulates or, 2) alternatively, the entire mass may be sent
directly to an appropriate apparatus for separation of the aqueous and non-aqueous
layers.
If the mass is allowed to stand to effect separation of the oils, it has been
observed that for a batch size of about 150 Kg, for example, approximately 1 to 3 hours
were required for separation. Separation of the lower aqueous layer from the upper
non-aqueous layer within the vessel 4 can be facilitated by a sight glass incorporated
into the recycling system 8. Accordingly, differences between the two layers are
visually determined to effect accurate separation. Alternatively, an oil skimmer may be
employed to remove the non-aqueous layer, as previously indicated, which is discarded
or further processed in the recycle system, while the lower aqueous layer is further
processed as discussed below.
The separation and recovery of the individual oily components within the non-
aqueous layer of the recycling system can be accomplished by a variety of processes
including, but not limited to, fractional distillation, short path distillation, and reverse
osmosis.
In general, distillation is a process in which a liquid is vaporized, recondensed,
and collected in a receiver. The liquid which has vaporized is collected in a receiver.
The resultant liquid (i.e. condensed vapor) is referred to as the condensate or distillate.
Distillation is a process for purifying liquids by separating the liquid into its
components. It is based on the difference in the volatility of the liquids. Volatility is a
general term used to describe the relative ease with which molecules (liquid or solid)
may escape from the surface to form a vapor. The vapor pressure of a liquid is related
to the ease with which the liquid volatilizes (i.e. a relatively volatile substance exerts a
relatively high vapor pressure at room temperature). The more volatile a substance,
the higher its vapor pressure and the lower its boiling point.
Fractional distillation is the separation and purification, by distillation, of two or
more liquids into various fractions. It is a systematic redistillation of progressively purer
distillates or fractions. A fractionating column is used to essentially perform a large
number of successive distillations without the necessity of actually collecting and
redistilling the various fractions. A fractionating column may be packed with glass
beads, glass helices, metal screens or ceramic saddles to effect fractionation.
A series of distillations involving partial vaporization and condensation
concentrates the more volatile component in the first fraction of distillate and the less
volatile component in the last fraction or in the residual liquid. The vapor leaves the
surface of the liquid and passes up the packing of the column. The vapor condenses
on the cooler surfaces and redistills, typically many times before entering the
condenser. By means of long and efficient distillation columns, two liquids may be
completely separated.
Short path distillation is especially suitable for substances that cannot be distilled
by any of the ordinary distillation methods because (1) the substance is viscous, and
any condensed vapors tend to plug the distilling column or condenser; and/or (2) the
vapors of the substance are extremely susceptible to condensation.
Short path distillation differs from other distillations because (1) a condensed
vapor flows to the distillate receiver or collector; (2) very low pressure (high vacuum)
in the system favors vaporized molecules reaching the condensing surface without
collision with other molecules to condense prematurely; (3) there is a very short
distance between the surface of the evaporating liquid and the condenser surface; and
(4) the substance has a residence time in the presence of heat which is very short so
that thermal degradation is prevented.
A short path distillation apparatus typically includes a rotating still. Materials are
fed into the rotating still and distributed evenly and thinly over a heated evaporating
surface. The substance distills in a short time and the vapors condense and run into
a collector. The degree of vacuum is controlled to collect the distillate effectively at the
condenser. The pressure can be as low as 1 μm Hg.
Short path distillation as described herein is also known as molecular, wiped film,
thin film, falling film, and rising film distillation. Short path distillation systems are
commercially available from companies such as Pope Scientific in Saukville, Wl and
Artisan Industries in Waltham, MA.
Reverse osmosis is a process whereby dissolved solids or a miscible liquid are
removed from water by applying a pressure differential across a semi-permeable
membrane. The semipermeable membrane allows water to flow therethrough, but does
not allow other components from passing through the membrane. Reverse osmosis
equipment is commercially available from companies such as Pall Filtron in
Northborough, MA and Millipore Corporation in Bedford, MA.
As described above, the dissolved gelatin is separated into a solvent based layer
(e.g. aqueous layer) and a non-solvent based layer (e.g. non-aqueous layer). The non-
aqueous layer is then treated by any of the above described methods to recover the oils
contained in the non-aqueous stream.
If the separated aqueous layer contains particulates and/or oily type materials,
the aqueous layer may then be treated, to remove residual oils and/or particulates
preferably by means of hot filtration processes as more fully described below.
The aqueous layer is sent through a heated transfer conduit 14, to a hot filtration
assembly 18. The hot filtration assembly 18 is particularly desirable if the aqueous layer
contains particulate matter or residual oil matter.
The method of hot filtration employed for the removal of oils and/or particulates
may include, but is not limited to, techniques such as liquid:liquid centrifugation, sub-
micro/micro-filtration, liquid.liquid coalescers, absorbents and filter aids such as, but not
limited to, diamataceous earth, activated carbon, clay or activated clay, colloidal silica,
porous acrylic resins and the use of oil soluble salts to break any emulsion that may
exist.
Liquid:liquid centrifugation is based on the principal that the rate of separation
of two immiscible liquids is increased significantly by the application of centrifugal force
which can be thousands of times that of gravity. The force exerted on the liquids is
directly proportional to the speed of rotation, the radius of rotation, and the mass of the
liquids.
The force exerted on rotating immiscible liquids, i.e, aqueous and non-aqueous
liquids, is described in terms of relative centrifugal force or number of g's which is
expressed as multiples of the force of gravity. Centrifuges are rated by their relative
centrifugal force which can typically range from 10 to hundreds of thousands. Relative
centrifugal force can be controlled by varying the speed or the centrifuge head or rotor.
As a method of hot filtration in the subject invention, the aqueous layer to be hot
filtered is maintained at a temperature sufficient to allow flow into the centrifuge; higher
temperatures and/or higher dilutions may also enhance an efficient separation by
reducing the viscosity of the liquids to be separated. A temperature of from about 30°C
to 70°C and a dilution volume of up to 5 volumes, preferably from about 0.5 to 5
volumes of a suitable solvent, such as water, is preferred.
The efficiency of separation may be enhanced by employing a relatively higher
centrifugal force in the range of from about 5,000 to 25,000. The resulting, clarified
aqueous layer containing gelatin and glycerin is collected for reuse and the residual oils
and/or particulates are either discarded or collected for potential recovery as discussed
hereinafter.
Liquid:liquid:solid centrifugation can also be utilized to achieve separation of the
gelatin and softening agent (e.g. glycerin) from the particulates and/or residual oils.
This procedure is preferred when the waste gelatin stream contains particulates which
are at least a part of the coloring system (e.g. titanium dioxide).
Commercial liquid:liquid and/or liquid:liquid:solid centrifugation equipment is
available from companies such as Westfalia Separator U.S. in Northvale, NJ and Alfa
Laval in Warminster, PA.
Micro or sub-micro filtration refers to a method of removing small particles from
a liquid. Particulates as used herein include, but are not limited to, solid particulates
which do not have sufficient mass to settle out of solution and/or emulsions and micro-
emulsions which do not readily separate from a liquid. Micro or sub-micro filtration can
be achieved through the use of micron or sub-micron pore sized filters including, but not
limited to cartridge type filters, also known as "depth" or "dead end" filters and
tangential flow type filters. Tangential flow type filters are the preferred filters for this
purpose. The pore size of the preferred filters is typically in the range of from about 0.1
and 2.0 microns.
Temperature and dilution are important considerations in improving the efficiency
of the filtration process by varying the viscosity of the liquid. A temperature of from
about 30°C to 70°C and a dilution volume of up to 5 volumes preferably from about 0.5
to 5 volumes of a suitable solvent, such as water, is preferred.
Micro or sub-micro filtration equipment is commercially available from suppliers
such as Millipore Corporation in Bedford, MA.
A liquid:liquid coalescer, may be used to remove residual oils from the aqueous
layer. The coalescer enhances the collection of the oil droplets (the dispersed phase
liquid) into larger droplets which will separate more easily from the aqueous layer (the
continuous phase liquid).
Generally, for the subject application, a multiple stage system may be employed.
Such systems remove the designated materials in stages such as by first removing
particulates. Once the particulates are removed the remaining liquid may then be
treated with a coalescer to remove residual oil from the aqueous gelatin and glycerin.
A temperature of from about 30°C to 70°C and a dilution volume of typically up to 5
volumes, preferably from about 0.5 to 5 volumes of a suitable solvent, such as water,
is desirable. Commercial coalescers are readily available such as those supplied by
Millipore Corporation in Bedford, MA.
Filter aids containing diatomaceous earth can be employed for removal of
particulates and/or residual oils. Diatomaceous earth, more commonly known as Celite
or Filter Aid, is a very pure and inert material which forms a porous film or cake on a
filter medium such as, but not limited to, filters made from paper, nylon and
polypropylene as are typically used in filtration systems using filtration apparatus such
as, but not limited to Nutsch filters, Rosenmund filters and/or centrifuges.
Diatomaceous earth can be employed: 1 ) by forming a slurry with an appropriate
solvent, such as water, then filtering the slurry through an appropriate apparatus, such
as a Nutsch or Rosenmund type filter, or a plate/coated plate filter such as a sparkler
filter, to form a thin film or cake or 2) by adding the diatamaceous earth directly to the
product to be filtered to form a slurry which is then filtered forming a porous thin cake
or film. A temperature of from about 30°C to 70°C and a dilution volume of up to 5
volumes, preferably from about 0.5 to 5 volumes of a suitable solvent, such as water,
is desirable. Other filter aids besides diatamaceous earth include, but are not limited
to silica, acrylic resins, clay and activated carbon.
Absorbents which may be used to treat the solvent based layers include zeolitic
materials.
In particular, the lower aqueous phase may be heated, preferably hot filtered in
the filtration assembly 18 if particulates and/or residual oils are present at a temperature
of approximately the same as above (i.e. from about 30°C to 70°C) preferably through
liquid:liquid centrifugation or micro/sub-micro filtration as described above to remove
any remaining traces of oily components or other contaminants through a conduit 20
and optionally forwarded to the recycling system 8 . Other types of filtration equipment
which may be employed include plate filters, or coated plate filters like, for example, a
sparkler filter. The preferred material of construction for these type of filters is stainless
steel. Alternatively, nutche filters of the Rosenmund type or cartridge filters may be
used for the purpose.
The employment of the hot filtration systems mentioned above separates
particulates and/or oils from the aqueous layer containing gelatin and the softening
agent (e.g. glycerin).
Depending on the concentration of the gelatin and glycerin in the resulting
filtrate, the filtrate may be returned directly to gelatin mass manufacturing or the filtrate
may be transported via heated conduit 22 to a concentration assembly 16 which may
be in the form of a diafiltration assembly and concentrated by removing some of the
solvent (e.g. water). For solutions having a gelatin concentration greater than about
10% gelatin wt/wt (e.g. 10% wt wt to 45% wt/wt), the aqueous solution may be charged
to a concentration apparatus adapted for vacuum distillation such as disclosed in
Schmidt et al., U.S. Patent No. 5,288,408, or to a diafiltration system such as disclosed
in Schmidt U.S. Patent No. 5,945,001 each of which is incorporated herein by
reference. Alternatively, the filtrate may be subjected to short path distillation as
previously described.
Short path distillation for this aspect of the present invention is carried out under
controlled conditions to facilitate the removal of water at a lower temperature to prevent
thermal degradation of the recoverable gelatin. Evaporator temperatures typically from
about 50°C to 120°C, and typically pressures 20 to 30 in. Hg, preferably 22-28 in. Hg
are employed to remove water. Such temperatures and short contact time do not
cause decomposition of the protein-based gelatin which affects its bloom strength. The
water distillate is passed through a condenser to waste or recycle. The residue
contains the gelatin/glycerin mixture for reuse.
As an example, waste gelatin material is diluted with solvent (e.g. water) at a
ratio of 3:1 , wateπwaste gelatin material, the following illustrates the distillate:residue
ratios which may be via the chosen distillation process, to achieve a desired level of
recycled gelatin and glycerin.
To achieve a 25% recycle level for gelatin and glycerin from the above described
3:1 dilution, the distillation should preferably result in a distillate: residue ratio of 50:50.
To achieve a 40% recycle level for gelatin and glycerin from the above described 3:1
dilution, the distillation should preferably result in a distillate: residue ratio of 62.5:37.5.
In both examples the residue contains the gelatin and glycerin for recycle.
Diafiltration may be employed at the concentration assembly 16 to remove
residual water soluble active ingredients, glycerine, water, and other water-soluble
components such as preservatives and dyes and to provide gelatin in a form that is of
sufficient purity and quality to permit reuse.
Diafiltration is a technique using ultrafiltration membranes to remove or
fractionate different size molecules in macromolecular solutions. An ultrafiltration
membrane retains macromolecules that are larger than the nominal molecular weight
limit (NMWL) of the membrane and freely passes molecular species which are
significantly smaller than the NMWL of the membrane. Macromolecules retained by the
membrane are concentrated, while the low molecular weight species are removed.
Typically, the macromolecules must be "washed" using multiple wash volumes to
remove residual smaller molecules, hence the name diafiltration (i.e. filtration using
ultrafiltration membranes and washing).
For continuous diafiltration, a supply of macromolecules (e.g. gelatin) is added
via the conduit 22 to the diafiltration assembly 16 at the same rate as the filtrate is being
removed. This is also referred to as constant volume diafiltration. The concentration
of the macromolecules does not change during the diafiltration process.
Discontinuous diafiltration involves first concentrating the macromolecule (e.g.
gelatin) batch to a predetermined volume, and then reconstituting the sample to its
original volume with replacement solvent. This is repeated until the smaller molecules
are removed.
Referring to Figure 1 diafiltration may be accomplished by first heating the
system from about 50°C to 65°C by recirculating heated, deionized water typically for
about 15 minutes through the conduit 24. The hot, aqueous feed stream is then
pumped through fhe assembly 16 via a conduit 22 and concentrated to the desired
gelatin/water concentration as discussed hereinafter. When the desired water/gelatin
concentration is achieved, fresh, hot (e.g. from about 50 to 65°C), deionized water is
fed into the system at exactly the same rate as the effluent exiting the system; the
effluent being water and all water soluble components. Once the water soluble
components have been removed, the remaining gelatin/water solution is recycled for
gelatin encapsulation.
The filters that can be employed in the concentration/diafitration step are known
and available in the art. Such filters include screen filters including open channel filters
and the like. The selection of a suitable filter for the purification of gelatin must be
capable of separating gelatin (typically having a molecular weight of from about 30,000
to 50,000) from smaller molecules.
The recovered aqueous gelatin solution is concentrated to a final solids (gelatin)
concentration of at least between about 20% by weight, preferably from about 30% and
50%. The remaining concentrated gelatin is then purified using between about 1 and
20 diafiltration volumes of water, preferably between about 3 and 10 diafiltration
volumes to provide recovered gelatin that is sufficiently pure to permit reuse and which
leaves the diafiltration assembly 16 via a conduit 26 to a receiver 34. A portion of the
purified recycled gelatin may be sent back to the gelatin dissolving step via a conduit
28 to remove additional impurities from the gelatin to thereby obtain an even purer
product.
Impurities such as dyes, actives, water, preservatives and glycerine can be
removed from the diafiltration assembly via conduit 30.
Recovery of the above-mentioned impurities obtained from the diafiltration
assembly 16 via the conduit can be performed in a recycling system 32. This system
can be based on distillation systems including fractional distillation, short path distillation
and reverse osmosis as previously described in connection with the recycle system 8.
Fractional distillation and reverse osmosis are preferred for recovery of the stream 30
with reverse osmosis being the most preferred method.
The process stream 30 in addition to containing the above mentioned impurities
may contain from about 1 % to 10% by volume of glycerol in water, typically from about
3% to 7% by volume. The process stream 30 is treated at temperature of from about
0°C to 30°C, more typically from about 5°C to 20°C. Typically recovery of glycerol is at
least 65% by volume, more typically from about 65% to 95%, most preferably from
about 80% to 95% by volume.
In some instances, dyes and pigments that are used to color gelatin capsules
have an affinity for the gelatin in the waste stream. Recovery of the gelatin alone may,
therefore, require that steps be taken to eliminate this affinity so that the dyes can be
removed. In general, it is necessary to take these steps following the hot filtration
process and prior to the concentration/diafiltration process.
Suitable methods for eliminating the affinity between dyes and/or pigments and
the gelatin include use of, for example, activated clay, carbon cartridge filtration; carbon
slurry formation followed by filtration to remove the carbon; pH adjustment to eliminate
adhesion of the dye to the gelatin, followed by direct diafiltration to remove the dyes,
and then adjustment of the pH back to the normal processing pH (e.g. from about 5 to
7); or, a combination of these methods.
If an affinity exists between the dyes and/or pigments, once the affinity has been
eliminated, diafiltration can be performed to obtain recovered gelatin. Alternatively,
diafiltration itself will remove these dyes and/or pigments with sufficient diafiltration
volumes. It is understood that the recycling system described can be incorporated into
a conventional encapsulation apparatus to provide repeated or continual recycling of
waste encapsulation materials.
Entrapped air may be a consideration during the process of manufacturing
gelatin mass for encapsulation into soft gelatin capsules. General practice in the soft
gelatin capsule manufacturing industry is to manufacture the gelatin mass under
vacuum, for the express purpose of removing air, on a mezzanine or second floor then
feed the molten gelatin mass, by gravity, to the encapsulation machines on the first
floor.
In the absence of a building configuration conducive to gravity feed to the
encapsulation machines, gelatin mass can be transferred by air pressure or pumps.
The choice of pump must be such that as little air as possible is introduced into the
gelatin mass. Examples of appropriate pumps may be, but are not limited to, peristaltic,
moyno, and sine type pumps.
The ultrafiltration process of the present invention can generate flow rates in
excess of 200 liters per minute. Although proper engineering and design of the
diafiltration system will minimize or eliminate introduction of air from external sources,
the flow rates generated may nonetheless, introduce some air into the gelatin. The air
can be entrapped or dissolved in the viscous gelatin mass. Under these circumstances,
it is desirable to degas or remove at least most of the air from the gelatin.
Typical practices in analytical chemistry for degassing dissolved air in water
and/or organic solvents used as a mobile phase for High Performance Liquid
Chromatography (HPLC) are: 1 ) pass the water and/or organic solvents through a 0.45
micron membrane filter and/or 2) sparge the water and/or organic solvent with an inert
gas such as nitrogen and/or 3) allow the water and/or organic solvent to be exposed to
molecular sieves until completely degassed.
It is also known in the art that microfilters are available commercially in the
micron range similar to that used to degas mobile phase for HPLC analysis. Such filters
may be obtained for example from A G Technology of Needham, Massachusetts.
Any of the above-mentioned methods of degassing may be employed in the
present invention. If, for example, a membrane filter (e.g. 0.45 micron) were employed
to degas the gelatin, the filter could be incorporated into the diafiltration system 16
shown in Figure 1. For example, the aqueous layer passing through the conduit 14 to
the diafiltration system 16 is first treated as described above to remove impurities via
the conduit 30. The recovered gelatin may then be filtered with a membrane filter to
remove air within the diafiltration system 16.
In another embodiment of the present invention, the degassing operation may
be established externally of the diafiltration system. Referring to Figure 2, the
recovered gelatin is sent via the conduit 26 to a conduit 27 which leads to a degassing
system 29 (e.g. a membrane filter). Once the gas (e.g. air) is removed from the gelatin,
the degassed gelatin is sent via the conduit 31 to be recycled or recovered.
It is understood that the above described recycling system may be incorporated
into a conventional encapsulation apparatus to provide repeated or continual recycling
of waste encapsulation materials.
Although the present invention has been described with reference to the
particular embodiments herein set forth, it is understood that the present disclosure has
been made only by way of example and that numerous changes in details of
construction may be resorted to without departing from the spirit and scope of the
invention. Thus, the scope of the invention should not be limited by the foregoing
specifications.