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Sommaire du brevet 2561573 

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  • lorsque la demande peut être examinée par le public;
  • lorsque le brevet est émis (délivrance).
(12) Brevet: (11) CA 2561573
(54) Titre français: TRAITEMENT DE DECHETS BIOMEDICAUX
(54) Titre anglais: TREATMENT OF BIOMEDICAL WASTE
Statut: Périmé et au-delà du délai pour l’annulation
Données bibliographiques
Abrégés

Abrégé français

L'invention concerne un appareil pour traiter les déchets biomédicaux comprenant un récipient d'entrée des déchets présentant une porte d'entrée sur la partie supérieure et une porte de sorte située au fond du récipient. Une déchiqueteuse est montée sous l'orifice de sortie et permet de déchiqueter les déchets à une taille maximum souhaitée. Une chambre de traitement est située sous la déchiqueteuse, de sorte que, lorsque la porte de sortie est ouverte, les déchets solides déposés dans le récipient d'entrée des déchets passent à travers l'orifice de sortie et à travers la déchiqueteuse, et les déchets déchiquetés sont envoyés dans la chambre de traitement. Un gaz d'ozone est envoyé dans la chambre de traitement, et un indicateur d'ozone indique la concentration d'ozone. Les échappements permettent de manière sélective de vider l'atmosphère de la chambre de traitement et le récipient d'entrée de déchets.


Abrégé anglais


An apparatus for processing biomedical waste comprises a waste input container
having an input door in a top thereof and an output door in a bottom thereof.
A shredder is mounted under the output opening and is operative to shred waste
to a desired maximum size. A processing chamber is located under the shredder
such that, when the output door is open, solid waste deposited in the waste
input container passes through the output opening and through the shredder,
and shredded waste drops into the processing chamber. Ozone gas is directed
into the processing chamber, and an ozone indicator indicates ozone
concentration. Exhausts are selectively operative to exhaust the atmosphere
from the processing chamber and waste input container.

Revendications

Note : Les revendications sont présentées dans la langue officielle dans laquelle elles ont été soumises.


17
CLAIMS:
What is claimed is:
1. An apparatus for processing waste, the apparatus comprising:
a waste input container having an input opening in a top thereof and an output
opening in
a bottom thereof;
an input door operative to close and substantially seal the input opening;
an output door operative to close and substantially seal the output opening;
a shredder mounted under the output opening and operative to shred waste to a
desired
maximum size;
a processing chamber located under the shredder such that, when the output
door is open,
waste deposited in the waste input container passes through the output opening
and
through the shredder, and shredded waste drops into the processing chamber;
a sealable discharge opening in the processing chamber;

18
an ozone gas source connected to the processing chamber and operative to
direct ozone
gas into the processing chamber;
an ozone indicator operative to indicate a concentration of ozone gas present
in an
atmosphere inside the processing chamber;
a chamber exhaust selectively operative to exhaust the atmosphere from the
processing
chamber; and
a hopper exhaust selectively operative to exhaust the atmosphere from the
waste input
container.
The apparatus of Claim 1 further comprising a disposal container having a
filling opening
releasably attached and substantially sealed to the discharge opening, and
means to move
shredded waste from the processing chamber through the discharge opening into
the
disposal container.
The apparatus of Claim 2 wherein the means to move shredded waste from the
processing
chamber through the discharge opening into the disposal container comprises a
substantially upright wall located in the processing chamber opposite the
discharge

19
opening, and an actuator operative to move the wall toward the discharge
opening and
push the shredded waste through the discharge opening.
4. The apparatus of any one of Claims 2 and 3 further comprising a chamber
discharge door
operative to close and substantially seal the discharge opening in the
processing chamber.
5. The apparatus of any one of Claims 1 - 4 further comprising an agitator in
the processing
chamber operative to lift shredded waste contained therein and drop same
through the
atmosphere inside the processing chamber.
6. The apparatus of any one of Claims 1 - 5 further comprising a screen under
the shredder,
and wherein the screen prevents shredded material larger than a desired size
from
dropping into the processing chamber.
7. The apparatus of any one of Claims 1 - 4 further comprising a pusher
mechanism in the
waste input container operative when activated to exert a force on waste in
the waste
input container toward the input opening, and operative to force the waste
into the
shredder..

20
8. The apparatus of any one of Claims 1 - 7 wherein the exhaust comprises at
least one of a
vent connected to an exterior atmosphere and a filter.
9. The apparatus of any one of Claims 1 - 8 further comprising a water source
connected to
the processing chamber and operative to direct water into the processing
chamber.
10. The apparatus of Claim 9 wherein the water source comprises a stem source.
11. The apparatus of any one of Claims 1 - 10 further comprising a waste cart
elevator
operative to raise a waste cart from substantially floor level adjacent to the
apparatus and
invert the waste cart to empty waste contained in the waste cart into the
waste input
container.
12. The apparatus of Claim 11 wherein the waste cart elevator is linked to the
input door of
the waste container such that opening the input door operates the waste cart
elevator to
empty waste into the waste input container, and such that closing the input
door returns
the waste cart to substantially floor level.

21
13. A method for processing biomedical waste, the method comprising:
providing a shredder above a substantially sealed processing chamber,
maintaining a selected concentration of ozone in an ozone rich atmosphere
inside the
processing chamber during shredding at a level sufficient to sterilize the
biomedical
waste;
feeding waste into the shredder and operating the shredder to shred the waste
to a desired
maximum size, and allowing shredded waste to fall through the ozone rich
atmosphere
inside the processing chamber and keeping the waste in the processing chamber
for a
length of time sufficient to sterilize the biomedical waste at the selected
concentration of
ozone;
exhausting the ozone rich atmosphere from the processing chamber and removing
sterilized waste.
14. The method of Claim 13 further comprising, prior to exhausting the ozone
rich
atmosphere, periodically moving waste from the processing chamber through a
discharge
opening in the processing chamber into a disposal container scaled to the
discharge

22
opening, and shredding more waste into the processing chamber as waste is
moved into
the disposal container until the disposal container is full.
15. The method of any one of Claims 13 and 14 wherein feeding waste into the
shredder
comprises feeding an tin-segregated waste comprising biomedical waste and
general
waste.
16. The method of any one of Claims 13 - 15 further comprising increasing a
level of
moisture in the processing chamber.

Description

Note : Les descriptions sont présentées dans la langue officielle dans laquelle elles ont été soumises.


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TREATMENT OF BIOMEDICAL WASTE
This invention is in the field of waste treatment and in particular in the
treatment and
disposal of biomedical waste products.
BACKGROUND
to
Within the medical field, and especially in hospital environments, controlling
the spread
of potentially pathogenic organisms is an important concern. A number of
studies have
shown that the risk of infection due to the spread of disease organisms is a
serious human
health problem. Infections can be transferred by contact with surfaces upon
which
organisms can be deposited by handling by patients or hospital staff, or by
airborne
dispersion after a cough or sneeze. The risk of infection is further
exacerbated by the
confined space of typical hospitals, and by the fact that people in hospitals
may have an
impaired ability to resist infection due to their own health problems. In some
cases as
well, the infectious organisms are sometime resistant to commonly used
antibiotics, so
called super-bugs, and so remediation of the infection through medical
intervention may
be difficult, if not impossible.
SUBSTITUTE SHEET (RULE 26)

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As a result, it is common practice in modern day medical setting to take
appropriate
measures to reduce the risk of infection. Such measures include hand washing
after
contact with patients, frequent cleaning of floors, walls and furniture with
disinfecting
solutions, and the use of disposable products. The use of disposable plastic
syringes,
cutlery and beverage containers are but a few examples of products designed
for single
use in order to reduce the risk of spreading pathogens, and which through use
become
biomedical waste.
Biomedical waste also comprises such things as blood and blood products,
tissues
to resected during surgery, as well as single use items used and discarded in
the normal
course of surgical procedures. It is well-recognized that contact with human
fluids such
as blood is a significant risk factor in the spread of the human
immunodeficiency virus
(HIV) that causes the disease acquired immune deficiency syndrome (AIDS).
is It is well recognized that health hazards are posed by the handling and
disposal of
biomedical wastes, and that care must be exercised in handling such waste and
in the
disposal thereof. It is desirable and mandated in many jurisdictions that
biomedical waste
be processed, typically by incineration, to destroy pathogens. Incineration
requires
significant amounts of energy, and also releases potentially harmful
combustion products
2o into the atmosphere.
SUBSTITUTE SHEET (RULE 26)

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Alternatively, chemical sterilizing solutions can also be used to destroy
pathogens in
biomedical waste. These chemicals, being themselves toxic, pose added risks to
those
whose responsibility it is to handle biomedical wastes, as well as a risk to
the
environment upon their disposal.
Ozone is also well known as having disinfecting properties, and is well known
as a
sterilizing agent in certain applications. Ozone is considered very safe as
evidenced by
the approval of the U.S. Food &, brag Administratio n for use ir~ treating
food products.
Ozone is a chemically active radical species of oxygen, commonly produced by
ionization of either air or pure oxygen. Unlike conventional disinfecting
chemicals,
ozone does not form hazardous disinfectant by-products that are harrriful to
the
environment or are toxic to animals and humans. Once ozone has fully reacted
with
substances in water or air, excess gas decomposes quickly to normal oxygen and
is
reabsorbed into the atmosphere. Commercial ozone generators are available
which
economically produce significant amounts of ozone.
The use of ozone in the disposal of biomedical waste is disclosed in a number
of prior art
patents. United States Patent Numbers 5,078,965 and 5,116,574 to Pears on
disclose
grinding the waste and adding water to create a slurry over a fluidized bed,
and then
bubbling ozone up through the slurry. The systems disclosed in United S tates
Patent
Numbers 6,494,391 to Mosenson and 5,820,541 to Berlanga Barrera similarly add
water
to the ground waste, and add a disinfectant such as ozone, to the mixture.
United States
SUBSTITUTE SHEET (RULE 26)

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Patent Number 5,520,888 to Berndt uses a slush or slurry of waste and ice-
containing
ozone to sterilize medical waste.
Largely for reasons of economy, present waste practices in hospitals and the
like include
segregation of waste into general waste and biomedical waste with the
biomedical waste
being processed as such, and the general waste being processed as ordinary
garbage and
taken to landfills and disposal sites with no treatment. Typically, biomedical
waste must
be packaged ar~d transported accordi ng to strict regulations in or~3er to
move same from
the source, such as a hospital or the like, to off site processing.
to
Such segregation is subject to human error, and as well general waste is often
in contact
with biomedical waste prior to segregation. Further such segregation lengthens
the time
between creation of the biomedical waste and treatment thereof. Pathogens
therefore
have an extended time in which to multiply prior to treatment, thereby
increasing the
number of pathogens that the treatment process must inactivate. As well, waste
management personnel are exposed to these pathogens during the common manual
separation of biomedical waste from general waste.
SUBSTITUTE SHEET (RULE 26)

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-S-
SUMMARY OF THE INVENTION
It is an object of the present invention to provide an apparatus for the
treatment of
biomedical waste that overcomes problems with current methods of biomedical
waste
treatment and disposal.
The invention provides, in a first embodiment, an apparatus for processing
solid
biomedical vaaste. The apparatus comprises a waste input container ha«ing an
input
opening in a top thereof and an output opening in a bottom thereof. An input
door is
l0 operative to close and substantially seal the input opening, and an output
door is
operative to close and substantially seal the output opening. A shredder is
mounted under
the output opening and is operative to shred waste to a desired maximum size.
A
processing chamber is located under the shredder such that, when the output
door is open,
solid waste deposited in the waste input container passes through the output
opening and
through the shredder, and shredded waste drops into the processing chamber. A
sealable
discharge opening is provided in the processing chamber. An ozone gas source
is
connected to the processing chamber and is operative to direct ozone gas into
the
processing chamber, and an ozone indicator is operative to indicate a
concentration of
ozone gas present in an atmosphere inside the processing chamber. A chamber
exhaust is
2o selectively operative to exhaust the atmosphere from the processing
chamber, and a
hopper exhaust is selectively operative to exhaust the atmosphere from the
waste input
container.
SUBSTITUTE SHEET (RULE 26)

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The invention provides, in a second embodiment, a method for processing solid
biomedical waste. The method comprises providing a shredder above a
substantially
sealed processing chamber; maintaining a selected concentration of ozone in an
ozone
rich atmosphere inside the processing chamber during shredding at a level
sufficient to
sterilize the biomedical waste; feeding waste into the shredder and operating
the shredder
to shred the waste to a desired maximum size, and allowing shredded waste to
fall
~h_rnugh tlZ~ Oz~??le rich atmosphere inside t_he processing cha_~r!ber and
keeping the Waste
in the processing chamber for a length of time sufficient to sterilize the
biomedical waste
to at the selected concentration of ozone; and exhausting the ozone rich
atmosphere from
the processing chamber and removing sterilized waste.
The present invention uses gaseous ozone in a simple system that does not
require the use
of slurries as in the prior art. A considerable level of automation can be
provided by the
inclusion of sensors and control mechanisms. The sensors operate to provide
information
about ozone levels in the processing chamber, or to indicate when the hopper
is full or
when the treatment process is complete and another batch of material can ~e
safely added
to the processing chamber.
2o The present invention provides an apparatus that is relatively simple and
easy to install
and which is relatively inexpensive to operate, and allows for substantially
automated and _
continuous treatment of biomedical waste. Biomedical waste treated with the
apparatus
SUBSTITUTE SHEET (RULE 26)

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will be essentially free from pathogens, and as such safe for disposal in
municipal
landfills and the like. The apparatus for practicing the method of the
invention is simple
and economical, such that same could be installed in a hospital or like source
of
biomedical waste and all waste could be processed therein. Chemicals and
pharmaceuticals would still require separation, however these wastes are not
presently
considered general waste suitable for conventional disposal in any event.
DESCRIPTION OF THE DRAWINGS:
While the invention is claimed in the concluding portions hereof, preferred
embodiments
are provided in the accompanying detailed description which may be best
understood in
conjunction with the accompanying diagrams where like parts in each of the
several
diagrams are labeled with like numbers, and where:
Fig. 1 is a perspective schematic view of an embodiment of the invention for
the
treatment of biomedical waste;
Fig. 2 is an exploded perspective view of the embodiment of Fig. 1;
Fig. 3 is a schematic side view of the embodiment of Fig. 1;
SUBSTITUTE SHEET (RULE 26)

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_g_
Fig. 4 is a schematic side view of an alternate embodiment of the invention,
showing in particular a waste cart lifting and dumping mechanism.
DETAILED DESCRIPTION OF THE ILLUSTRATED EMBODIMENTS:
The present invention provides a waste processing apparatus 100 for processing
b?omedzCal waste, Such that the processed waste is sterilized to ar~ extent
SiiffiClent fOr
disposal in sites such as sanitary landfills. In the illustrated embodiment of
Figs. 1 - 3,
to the apparatus comprises a waste input container, illustrated as a hopper 1
into which
untreated waste is placed though an input opening provided by the open top of
the hopper
1.
The hopper 1 includes an input door 3 operative to close and substantially
seal the input
opening provided by the open top of the hopper 1 to prevent the escape of air
from the
hopper 1. The level of waste in the hopper 1 can be visually monitored, or an
indicator 7
can be provided to inform the operator of the waste treatment system that the
hopper is at
maximum capacity by activating a visible or audible warning or a combination
of the
two. The apparatus may further comprise a lift 2, such as hydraulic or
mechanical lift,
2o which is operative to lift waste carts and like containers up to the input
opening in the top
of the hopper 1, and the contents dumped into the hopper 1 without the need
for manual
handling of the waste carts.
SUBSTITUTE SHEET (RULE 26)

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An output door 9 is provided in the bottom of the hopper 1 and is opened to
allow the
waste to move from the hopper 1 into the processing chamber 5. The apparatus
includes
a shredder 11, which shreds and grinds the waste material as it passes from
the hopper 1
into the chamber 5. Shredding and grinding exposes increased internal areas of
the waste
to the ozone, increasing the effectiveness of the sterilizing effects of the
ozone. A screen
retains the waste in the shredder 11 until the shredded waste pieces are below
a
minim>?m size, at which time they can pass through ts~:e screen 10 and into
the processing
chamber 5.
to
While many types of shredders could provide satisfactory shredding, one
suitable
shredder is Model STQ-50 Four Shaft Industrial Shredder manufactured by Shred-
Tech
of Cambridge, Ontario, Canada. The Shred-Tech shredder includes a screen such
that the
waste passes around the shredder until it is small enough to pass through the
screen.
The shredder 11 and screen 10 combine to allow only pieces of waste smaller
than about
2 - 3 centimeters across to drop from the shredder into the processing chamber
5.
In operation the hopper 1 is filled and the input door 3 is closed. An ozone
generator 15
is operated to inject ozone gas into the atmosphere inside the processing
chamber 5 until
2o the concentration of ozone reaches a desired level, contemplated to be
between 100 parts
per million (ppm) and 10,000 ppm. Time and ozone concentration are related in
that
inactivating a given number of pathogens requires less time at higher ozone
SUBSTITUTE SHEET (RULE 26)

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- 10-
concentrations. For example, where it is required to expose a pathogenic strip
to an
atmosphere with a concentration of 10,000 ppm for 3 minutes to kill the
pathogens, it will
be required to expose the same strip to a concentration of 100 ppm for 300
minutes to kill
the same pathogens.
Ozone sensors 19 in the processing chamber 5 are connected to indicators on a
control
panel. An operator can control the concentration of ozone in the atmosphere
inside the
pr'JCeSsiiag Ch?.u'Iiber 5 by C3ntrOiilitg the atWOi;u'2t Of l?izone
li"3~eCted Illt(5 t'fle Chan ~l7et~ J'
from the ozone generator 15. Conveniently, the ozone generator 15 may be
adapted to
to use either commercially available portable compressed air or oxygen
cylinders, or where
available, piped in hospital breathing air or oxygen, as the oxygen source 17.
Some
commercially available ozone generators also have the ability to extract
oxygen from
ambient air for ozonation, and as such do not require any special oxygen
supply. Such
devices would be readily adaptable to the apparatus 100.
When the desired ozone concentration in the atmosphere is achieved, the output
door 9 in
the bottom of the hopper 1 is opened to allow the materials to move from the
hopper 1
into the shredder 11 and then into the processing chamber 5. A pusher
mechanism 6 is
provided in the hopper 1 that can pivot as schematically shown in the phantom
lines in
2o Fig. 3 to force waste through the output door 9 and into the shredder 11.
SUBSTITUTE SHEET (RULE 26)

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As the waste is shredded to a size sufficiently small to pass through the
screen 10 it falls
through the ozone rich atmosphere in the processing chamber 5, and is thus
exposed to
the sterilizing effects of the ozone. As the waste falls into the chamber, the
pieces pile up
on the bottom of the processing chamber 5, and ozone rich air is present in
the spaces
between the pieces in the pile. Once the contents of the hopper 1 have been
shredded and
have dropped into the processing chamber 5, the output door 9 can be closed if
desired,
and the waste pile can be retained in the sealed processing chamber 5 for the
time
calculated to be required to satisfactorily sterilize the waste by
inactivating tl'le biGlGgiCai
organisms that may be present in the waste material.
to
The length of treatment time can be varied, such that different types or
quantities of
pathogens that may be present in waste, and which may be more or less
resistant to
inactivation, can be effectively inactivated during the ozone sterilization
process. Based
on known studies, it will be readily determinable as to what combinations of
time and
ozone concentration will be appropriate to achieve the goal of the process to
inactivate
substantially all pathogens that may be present in the waste. The outputs from
sensors
and the timer and other desired controls may be included in a control panel
31,
conveniently placed for use by an operator. Control of the ozone concentration
and
treatment time could be automated.
Sealing the processing chamber 5 prevents the release of ozone rich air into
the
surrounding atmosphere. As ozone is toxic to humans, controlling the release
of ozone
SUBSTITUTE SHEET (RULE 26)

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by the apparatus is important to ensure the safety of the operator, or those
who may
happen to be in the area of the apparatus while it is in operation.
The waste processing apparatus 1 can further comprise an agitator 13 in the
processing
chamber 5 if it is found to be required or desirable, depending on the waste
being
processed and the process steps being used. For example if some waste is
present in the
processing chamber prior to the introduction of ozone into the atmosphere in
the
processing chamber, ti~:e agitator 13 ~t.~ill Lift that waste and drop same
through fee czone
rich atmosphere to ensure contact with ozone during the treatment process.
to
It is contemplated that introducing moisture into the atmosphere of the
processing
chamber 5 could be beneficial in aiding penetration of ozone into the shredded
waste. A
water source could spray water into the processing chamber 5, or a steam
source 33 could
be connected to the processing chamber 5 to add moisture.
In the illustrated embodiment a disposal container 23 has a filling opening
releasably
attached and sealed to the discharge opening 21 in a wall of the processing
chamber 5.
Means such as conveyors or the like are provided to move shredded waste from
the
processing chamber 5 through the discharge opening 21 into the disposal
container 23.
2o Conveniently the means can be provided by a mechanism analogous to a trash
compactor
comprising a substantially upright wall located in the processing chamber 5
opposite the
discharge opening 21, and an actuator operative to move the wall toward the
discharge
SUBSTITUTE SHEET (RULE 26)

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opening 21 and push the shredded waste through the discharge opening 21 and
into the
disposal container 23. Thus several batches can be processed in the processing
chamber
and pushed into the disposal container 23.
5 As ozone is a toxic substance, exhausts are provided in the processing
chamber 5 and
hopper 1. In Fig. 2, the exhausts comprise filters 25, 35 containing
CaruliteTM or a like
substance operative to break ozone down into oxygen, and vacuum vents 27, 37
mounted
on and connected to the processing chamber 5 and hopper I. The filters 25, 35
break
down ozone and the vacuum vents 27, 37 are connected to a vacuum source that
can be
activated to draw the ozone rich atmosphere from the processing chamber 5 and
hopper 1
through the filters 25, 35 and out to an exterior atmosphere where the
remaining ozone
will be dispersed. A heater may be added to increase the effectiveness of the
filters 25,
35. It is contemplated that the filters 25, 35 may not be required if the
venting area is not
near people.
Because the output door 9 at the bottom of the hopper 1 is open during
shredding, high
levels of ozone are present in the hopper after the waste material has been
emptied
therefrom. Thus when all waste from the hopper 1 has been shredded into the
processing
chamber 5, and the output door 9 at the bottom of the hopper 1 has been
closed, the
hopper 1 is exhausted prior to opening the input door 3 by operating the
vacuum source
through vent 37. Once the ozone has been vented from the hopper 1, the input
door 3 can
SUBSTITUTE SHEET (RULE 26)

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be opened and further waste added, and the output door 3 re-closed and sealed,
and the
output door 9 then opened and the shredding process repeated.
In the illustrated embodiment this process can be repeated until such time as
the disposal
container 23 is full. Since the processing chamber 5 is in open communication
with the
interior of the disposal container 23 through discharge opening 21, the
atmosphere inside
the disposal container has substantially the same ozone concentration as the
atmosphere
in the processing eharnber 5. Thus the waste is exposed to ozone from the time
it enters
the shredder until the disposal container is full and the ozone exhausted
prior to removal.
to This period can last up to several days in many applications. For best
results the
atmosphere has the chosen high ozone concentrations prior to waste entering,
all waste in
the processing chamber 5 or disposal container 23 is at all times fully
exposed to ozone as
it piles up and as it is pushed into the disposal container, and as it rests
in the disposal
container.
Once full, the disposal container 23 can be removed and replaced with another
empty
disposal container 23. The full disposal container can be transported to
disposal sites
such as a sanitary landfill, and the contents, now sterilized, can be disposed
of without
fear of harm to either humans or the surrounding environment.
An alternate embodiment of a waste processing apparatus 150 for processing
biomedical
waste is schematically illustrated in Fig. 4 comprising a hydraulic lift 102
which is
SUBSTITUTE SHEET (RULE 26)

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operative to lift waste carts 155 and like containers from substantially floor
level adjacent
to the apparatus 150 up to the input opening in the top of the hopper 101, and
dump the
-contents into the hopper 1 without the need for manual handling of the waste
carts. The
lift 102 engages a front portion 157 of the waste cart 155 and is linked by
arms 159 to the
input door 103. The input door 103 is opened by hydraulic cylinders 161. As
the input
door 103 moves up to the open position OP, the arms 159 pull the cart 155 up
to the
inverted dumping position DP such that waste is emptied into the hopper 101.
When the
in_p~t d~nr ~lpgeg~ ~P .art 155 ie _rPtyPd tn flrJpr ie'rel,
to The waste processing apparatus 100, 150 are relatively simple and
economical, such that
same could be located at a source of biomedical waste, such as a hospital or
the like, and
such that un-segregated waste containing both biomedical and general waste
could be
shredded and processed therein, removing the problems associated with
segregating the
waste. The time between creation of the biomedical waste and treatment could
thus be
reduced, and handling of the waste would not be necessary. Errors in
segregation, and
exposure of personnel to pathogens would be reduced as well, along with
packaging and
transport concerns.
The foregoing is considered as illustrative only of the principles of the
invention.
2o Further, since numerous changes and modifications will readily occur to
those skilled in
the art, it is not desired to limit the invention to the exact construction
and operation
shown and described, and accordingly, all such suitable changes or
modifications in
SUBSTITUTE SHEET (RULE 26)

CA 02561573 2006-09-28
WO 2005/097215 PCT/CA2005/000516
-16-
structure or operation which may be resorted to are intended to fall within
the scope of
the claimed invention.
SUBSTITUTE SHEET (RULE 26)

Dessin représentatif
Une figure unique qui représente un dessin illustrant l'invention.
États administratifs

2024-08-01 : Dans le cadre de la transition vers les Brevets de nouvelle génération (BNG), la base de données sur les brevets canadiens (BDBC) contient désormais un Historique d'événement plus détaillé, qui reproduit le Journal des événements de notre nouvelle solution interne.

Veuillez noter que les événements débutant par « Inactive : » se réfèrent à des événements qui ne sont plus utilisés dans notre nouvelle solution interne.

Pour une meilleure compréhension de l'état de la demande ou brevet qui figure sur cette page, la rubrique Mise en garde , et les descriptions de Brevet , Historique d'événement , Taxes périodiques et Historique des paiements devraient être consultées.

Historique d'événement

Description Date
Inactive : CIB expirée 2022-01-01
Le délai pour l'annulation est expiré 2012-04-05
Lettre envoyée 2011-04-05
Lettre envoyée 2011-02-17
Inactive : Lettre officielle 2011-02-17
Requête visant une déclaration du statut de petite entité reçue 2010-03-29
Déclaration du statut de petite entité jugée conforme 2010-03-29
Accordé par délivrance 2009-10-13
Inactive : Page couverture publiée 2009-10-12
Requête visant une déclaration du statut de petite entité reçue 2009-07-21
Préoctroi 2009-07-21
Déclaration du statut de petite entité jugée conforme 2009-07-21
Inactive : Taxe finale reçue 2009-07-21
Déclaration du statut de petite entité jugée conforme 2009-04-01
Requête visant une déclaration du statut de petite entité reçue 2009-04-01
Un avis d'acceptation est envoyé 2009-03-20
Lettre envoyée 2009-03-20
month 2009-03-20
Un avis d'acceptation est envoyé 2009-03-20
Inactive : Approuvée aux fins d'acceptation (AFA) 2009-03-17
Modification reçue - modification volontaire 2009-01-30
Inactive : Dem. de l'examinateur par.30(2) Règles 2008-07-31
Déclaration du statut de petite entité jugée conforme 2008-03-28
Requête visant une déclaration du statut de petite entité reçue 2008-03-28
Avancement de l'examen jugé conforme - alinéa 84(1)a) des Règles sur les brevets 2007-12-03
Lettre envoyée 2007-12-03
Lettre envoyée 2007-11-30
Requête d'examen reçue 2007-11-30
Inactive : Lettre officielle 2007-11-21
Inactive : Taxe de devanc. d'examen (OS) traitée 2007-10-31
Inactive : Avancement d'examen (OS) 2007-10-31
Requête d'examen reçue 2007-10-29
Exigences pour une requête d'examen - jugée conforme 2007-10-29
Toutes les exigences pour l'examen - jugée conforme 2007-10-29
Inactive : Page couverture publiée 2006-11-27
Inactive : Inventeur supprimé 2006-11-23
Inactive : Notice - Entrée phase nat. - Pas de RE 2006-11-23
Demande reçue - PCT 2006-10-26
Exigences pour l'entrée dans la phase nationale - jugée conforme 2006-09-28
Déclaration du statut de petite entité jugée conforme 2006-09-28
Demande publiée (accessible au public) 2005-10-20

Historique d'abandonnement

Il n'y a pas d'historique d'abandonnement

Taxes périodiques

Le dernier paiement a été reçu le 2009-04-01

Avis : Si le paiement en totalité n'a pas été reçu au plus tard à la date indiquée, une taxe supplémentaire peut être imposée, soit une des taxes suivantes :

  • taxe de rétablissement ;
  • taxe pour paiement en souffrance ; ou
  • taxe additionnelle pour le renversement d'une péremption réputée.

Les taxes sur les brevets sont ajustées au 1er janvier de chaque année. Les montants ci-dessus sont les montants actuels s'ils sont reçus au plus tard le 31 décembre de l'année en cours.
Veuillez vous référer à la page web des taxes sur les brevets de l'OPIC pour voir tous les montants actuels des taxes.

Historique des taxes

Type de taxes Anniversaire Échéance Date payée
Taxe nationale de base - petite 2006-09-28
TM (demande, 2e anniv.) - petite 02 2007-04-05 2007-04-02
Requête d'examen (RRI d'OPIC) - petite 2007-10-29
Avancement de l'examen 2007-10-31
TM (demande, 3e anniv.) - petite 03 2008-04-07 2008-03-28
TM (demande, 4e anniv.) - petite 04 2009-04-06 2009-04-01
Taxe finale - petite 2009-07-21
TM (brevet, 5e anniv.) - petite 2010-04-06 2010-03-29
Enregistrement d'un document 2011-01-27
Titulaires au dossier

Les titulaires actuels et antérieures au dossier sont affichés en ordre alphabétique.

Titulaires actuels au dossier
PETER KLAPTCHUK
Titulaires antérieures au dossier
S.O.
Les propriétaires antérieurs qui ne figurent pas dans la liste des « Propriétaires au dossier » apparaîtront dans d'autres documents au dossier.
Documents

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Liste des documents de brevet publiés et non publiés sur la BDBC .

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Description du
Document 
Date
(yyyy-mm-dd) 
Nombre de pages   Taille de l'image (Ko) 
Description 2006-09-27 16 576
Revendications 2006-09-27 7 167
Abrégé 2006-09-27 1 67
Dessins 2006-09-27 4 89
Dessin représentatif 2006-11-23 1 15
Page couverture 2006-11-26 1 48
Revendications 2009-01-29 6 111
Page couverture 2009-09-21 1 49
Rappel de taxe de maintien due 2006-12-05 1 112
Avis d'entree dans la phase nationale 2006-11-22 1 194
Accusé de réception de la requête d'examen 2007-11-29 1 176
Avis du commissaire - Demande jugée acceptable 2009-03-19 1 163
Avis concernant la taxe de maintien 2011-05-16 1 171
Courtoisie - Certificat d'enregistrement (document(s) connexe(s)) 2011-02-16 1 102
Avis concernant la taxe de maintien 2011-05-16 1 171
PCT 2006-09-27 2 85
Taxes 2007-04-01 4 119
Correspondance 2007-11-20 1 14
Taxes 2008-03-27 4 149
Correspondance 2008-03-27 4 147
Taxes 2009-03-31 4 118
Correspondance 2009-03-31 4 118
Correspondance 2009-07-20 3 72
Taxes 2010-03-28 3 116
Correspondance 2010-03-28 2 61
Correspondance 2011-02-16 1 13