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Patent 1145073 Summary

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Claims and Abstract availability

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(12) Patent: (11) CA 1145073
(21) Application Number: 1145073
(54) English Title: ADVANCED MEANS FOR BIOLOGICAL TREATMENT OF WATER
(54) French Title: MOYENS LES PLUS AVANCES POUR LE TRAITEMENT BIOLOGIQUE DE L'EAU
Status: Term Expired - Post Grant
Bibliographic Data
(51) International Patent Classification (IPC):
  • C2F 3/12 (2006.01)
(72) Inventors :
  • ETLIN, VLADIMIR N. (United States of America)
(73) Owners :
  • ETLIN, VLADIMIR N.
(71) Applicants :
  • ETLIN, VLADIMIR N. (United States of America)
(74) Agent: J. WAYNE ANDERSONANDERSON, J. WAYNE
(74) Associate agent:
(45) Issued: 1983-04-19
(22) Filed Date: 1980-04-22
Availability of licence: Yes
Dedicated to the Public: N/A
(25) Language of filing: English

Patent Cooperation Treaty (PCT): No

(30) Application Priority Data: None

Abstracts

English Abstract


ABSTRACT
The invention disclosed relates to an apparatus for use in the
advanced biological treatment of waste water or sewage. The apparatus
described includes a conically shaped aeration chamber wherein the sewage
is subjected to activated sludge and a plurality of settling chambers through
which the sewage is passed. The treated water is removed from the settling
chambers and sludge is re-cycled back into the aeration chamber by means of
an aerator.


Claims

Note: Claims are shown in the official language in which they were submitted.


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Claims
1. In a device for the biological treatment of waste
water, including a first chamber for the aeration
of said water, and the exposure of the same to the
effect of activated sludge, said device having at
least one second chamber for the settling of said
sludge, from which treated water is removed, a wall
means separating said first chamber from said
second chamber and including an upper passageway for
the flow of liquid from the first chamber to the
second chamber; and a lower passageway for the flow
of sludge from the second chamber to the first
chamber, the improvement comprising said first
chamber being shaped to include a relatively smaller
horizontal sectional area at the lower end thereof,
and a relatively larger horizontal sectional area
at the upper end thereof; and means for introducing
water and air at the lower part of said first
chamber, creating a flow of liquid in which the
turbulence intensity increases along the way to
the top of the first chamber.
2. In a device for the biological treatment of waste
water comprising a chamber for the aeration of said
waste water and the exposure of said waste water
to activated sludge, said aeration chamber having a
horizontal sectional area which generally increases
in size from a relatively smaller horizontal
sectional area at the lower end thereof to a
relatively larger horizontal sectional area at,the
upper end thereof, said aeration chamber having a
waste water inlet in the lower area thereof so
that the water moves generally from bottom to top

-10-
of the aeration chamber, an aerator positioned in
the lower part of said aeration chamber to aerate
said waste water and cause said waste water to
circulate in said aeration chamber, and a plurality
of chambers for the settling of said sludge, at
least one wall separating each of said settling
chambers from said aeration chamber and said settling
chambers positioned in approximately the same
horizontal plane and surrounding said aeration
chamber, a passageway for waste water from the
upper part of said aeration chamber to one of said
settling chambers providing for a first step of the
activated sludge settling and having the water level
slightly lower than in the aeration chamber, trough
means for conducting effluent from the first step
settling chamber to another of said settling chambers
providing a second step of sludge settling and
having the water level slightly lower than in the
first step sludge settling chamber, a conduit for
sludge return from the second step sludge settling
chamber to the aeration chamber, said conduit having
a sludge inlet from the lower part of said second
step settling chamber and a sludge outlet into said
aeration chamber above said aerator in a zone of
rising air bubbles emanating from said aerator, so
that the pressure at said sludge outlet aspirates the
sludge through the conduit without the use of
pumps and is lower than at the port for sludge
return from the first step sludge settling chamber,
and a port in the lower part of the wall separating
the first step settling chamber from the aeration
chamber providing for the return of sludge from the
said first step settling chamber to the aeration
chamber, said port opening into said aeration chamber
at a location which will be aspirated by said cir-

-11-
culation of waste water, and the second step
settling chamber having an outlet for removal of
treated clarified waste water from the top thereof.
3. A device for the biological treatment of water
comprising an aeration chamber for the aeration of
said water and the exposure of said water to
activated sludge, an aerator positioned in said
aeration chamber, a waste water inlet in the lower
part of said aeration chamber, a plurality of
settling chambers, a first settling chamber provid-
ing a first step of sludge sedimentation, a second
settling chamber providing a second step of
sludge sedimentation, and a third settling chamber
for a third step of sludge sedimentation; septum
means for separating each of said settling cham-
bers from the aeration chamber, a passageway com-
municating between said aeration chamber and said
first settling chamber, first trough means for
conducting effluent from said first settling
chamber to said second settling chamber, second
trough means for conducting effluent from said
second settling chamber to said third settling
chamber, a first sludge return port from the first
settling chamber into said aeration chamber, said
first sludge return port opening into said aeration
chamber at a location aspirated by said circula-
tion of waste water, a conduit for sludge return
from the second settling chamber into said aeration
chamber, said sludge return conduit opening into
said aeration chamber at a location of lower
pressure than the opening location of the first
sludge return port, and a second conduit for
sludge return from the third settling chamber into
the aeration chamber, said second conduit opening

-12-
into the aeration chamber at a zone of rising air
bubbles above said aerator where the pressure is
even less than at the openings for said port and said
first conduit, said third settling chamber having an
outlet for removal of treated clarified waste
water, and said second and third chambers posi-
tioned in approximately the same horizontal plane
whereby settled sludge returns from the settling
chambers to the aeration chamber without the use
of pumps by the provision of suction effects at each
sludge return opening, so as to effect either
simultaneous operation in parallel of settling and
sludge return from all settling chambers with the
pressures at all sludge return openings into the
aeration chamber being maintained equal; or so as to
effect a step-by-step operation, with every sludge
return opening into the aeration chamber in an area
of less pressure, and therefore greater suction,
than the sludge return opening from the previous
step of sedimentation.

Description

Note: Descriptions are shown in the official language in which they were submitted.


f`~'.s
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.
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MEANS FOR ADVANCED WATER TREATM~NT
.-.
Technical Field
5 ~ My invention relates to water treatment devices
and particularly to physicochemical and biological
methods of sewage treatment devices. In the advanced - ;~
waste water treatment process of phosphorous removal
using two steps of lime reaction tanks suspended solids
settled down in the first step lime reaction tank are
collected and pushed back into reaction and flocculation
zone by rake arms~and solids settled down in the second
step lime reaction tank are pumped back into the first
¦ step tank by separate pumps. On the other hand, it is
essential in the biological process of sewage treat-
ment to have high concentration of the activated sludge
and high intensity of turbulence in the aeration
chamber so more sewage can be treated per same volume `
of an aeration tank. But the higher concentration of
~ 20 the activated sludge, the greater amount of suspended ~"
¦ solids is carried out from the activated sludge -~
settling tank. And it is required quite often to ~r~
provide for the second step settling tank to decrease ~i
suspended solids in the effluent. In this case an ;`
additional pump and pipe lines will be required to
recycle suspended solids settled in the second step
` settling tank back into the aeration tank. It is
essential in both cases to eliminate some of the equip-
ment for solids recirculation and consequently to
decrease expenditures.
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Background Art
.
The prior art, U.S. Patent ~o. 3,246,7~2,
provided for two settling chambers. Although sludge
return from the first settling chamber is produced
by the action of an aerator, sludge return from the
second settling chamber is produced by using a
separate pump. In case a third settling chamber is
3 needed, an additional pump will be required. So this
, 10 prior art is not as energy-efficient as my invention.
~ .
~ Disclosure of Invention
~ ~ .
In accordance with the present invention,
I provide a waste water treatment apparatus consisting
of a mixing or aeration chamber where mixing or aerat- ~ -
ing means is mounted, and a plurality of settling
chambers adjacent to the aeration chamber and which
work in series. My improved waste water treatment
apparatus possesses the advantage that suspended `
solids settled down in each of the serially operated
settling chambers are returned back into the aeration ~
chamber by the action of the single aerator. The latter
feature is of particular advantage and is a distinct
. 25 improvement over certain prior art apparati because
it eliminates special recycling pumps for each
settling chamber, and consequently reduced capital '
and operating expenses. Another advantage of my
apparatus is that its mixing (or aeration) chamber has
a horizontal sectional area which increases in size
from the bottom to the top, thereby greatly increasing
turbulence in the aeration chamber. The higher
turbulence, the higher biological activity of the'
sludge and higher concentration of the sludge can be
maintained in the aeration chamber. This shape of
~1
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:
,.
the aeration chamber effects a high degree of waste and
sludge mixing in the aeration chamber with minimum `'
power consumption.
,
Brief Description of_Drawings :
.
The details of my invention will be described ;
in connection with the accompanying drawings, in ,
which Figure 1 is a schematic vertical sectional
view showing a first embodiment of the invention with ¦
` two settling chambers and improved shape of the j
aeration chamber; Figure 2 is a schematic top plan
view of the first embodiment; Figure 3 is a schematic
vertical sectional view showing a second embodiment
of the invention with two settling chambers working
in series; Figure 4 is a schematic top plan Yiew
of the second embodiment; Figure 5 is a schematic -
top plan view showing a third embodiment of the inven- ~¦
tion with three settling chambers, two of which are
working in parallel and one is in series with those
two; Figure 6 is a schematic vertical sectional
view showing a fourth embodiment of the invention ~ -
with an air-diffuser as an aerator. ~,
: ;
Best Mode for Carrying Out the Invention '
In accordance with the first embodiment of the i;`
invention (Figures 1 and 2), the device of generally
trapezoidal configuration includes housing 1 with
number of septums which create inside of the housing 1
aeration chamber 2 and two settling chambers 3 and 4.
The housing element is bounded by a pair of side
walls 5 and 6, end walls 7 and 8 and a bottom wall 9.
A support (not shown) mounts an aerating element 10,
~ :~
.

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~5~73
.. :
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which may be of conventional type including a prime
mover ll and a rotating shaft 12 mo~unting an impeller ` "
13. A concentric air passage 14 has a lower end 15
adjacent to the impeller 13, so that with rotation
.. ~
5 of the impeller~ air is mixed into the treaked water
in a well known manner. First, second and third
pairs of septums 16, 17 and 18 respectively,`
interconnect an aeration chamber 2 with a pair of
~. :
settling chambers 3 and 4. The septums 17 are sloped
outwardly and terminate above the end walls 7 and 8 -
and form lower ports l9 and 20 through which
activated sludge settled in the chambers 3 and 4 is
recycled or inducted into the aeration chamber 2 under
¦ action of the impeller 13. An effluent trough 21
communicates with an effluent pipe 22 for discharge
of treated water. Sewage inflow pipe 23 is positioned
as shown in Figure l at the lower part o~ the aera-
tion chamber, such that sewage will be immediately
subjected to the action of air bubbles 24 formed by
the impeller. Sewage enters the aeration chamber 2 ~ ~;
and moves upwards, then flows through the passageways ;
between septums 16 and 17 into the settling chambers
from which it is discharged. Activated sludge settles`
in the settling chambers because of its density, t
and collects at the bottom of the settling chambers,
from where it is drawn back into the aeration chamber
by suction produced by the circulating water. Re-
ferring to Figure l, pressure at ports l9 and 20 is
the same because the water is moving at the same
velocity in those two areas, inasmuch as they are equi-
distant from the aerator. Ak any such area where~such ~ ;i
~ a port or conduit exists, the higher the velocity,
.~ of the water, the lower pressure at the port and
hence the greater suction effect. Therefore, if the
aerator lO is not symmetrically placed but is closer
~9 ' , ' '. ,
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~45C~7:~
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to settling chamber 4, a greater water velocity will
be produced in the area of port 19 than at port 20;
therefore, pressure at port 19 wil~ be lower than at
20 and consequently there will be greater suction
effect at port 19 than at port 20. In this arrange-
ment of the impeller, settling chambers will work
in series (settling c~lamber 3 as first step and
~ settling chamber 4 as second step). From a considera-
¦ tion of Figures 1 and 2 it will be apparent that only
a single impeller is necessary to create the circula-
tion which draws recycling sludge from both settling
chambers which are working in parallel. Having the
septums 17 slope outwards creates a cross-sectional
area which increases toward the top of the aeration
chamber 2, thereby producing greater turbulence in
the waste water than turbulence in aeration chambers
of the prior art. The net result is increased
capacity of one aeration chamber to treat sewage, ~i
- coupled with a lower requirement for power which must
be delivered by the aerator, to make total operating
expenses lower than the same in the prior art. ,
In Figures 3 and 4 is the second embodiment of
the invention in which is shown another way of putting
two settling chambers in serial operation and recycling
sludge back into aeration chamber from both of them
and yet using only one aerator. This enables a major
portion of' the activated sludge to be removed in ~'
` the first step settling chamber and the remaining ~;
sludge to be removed in the second step settling
chamber downstream, with resultant higher efficiency
of sludge recovery.
As best seen in F'igures 3 and 4, the second step
settling chamber 25 is interconnected by conduit'
sections 26, 27 and 28 to the first step settling
chamber 29. The chamber 25 is bounded by a pair of
`' f
.~ :

5~73
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., ~
converging walls 30 and 31, an end wall 32, a flat
hollow conduit 33, and a wall 34. The lower end
of the conduit 33 is positioned at the bottom of the
second step settling chamber 25, and terminates at a ! r~
medial level or location 35 of the aeration chamber 36.
Effluent from the chamber 25 flows through a trough 37
feeding an exit pipe 38.
During normal operati~n, the head in the aera-
tion chamber 36 is higher than the head in the first :;
step settling chamber 29, and the head in the second
step settling chamber 25 is below that of the `~
chamber 29. Thus, as water is introduced into the
aeration chamber 36 through a pipe 39 and aeration ;~
takes place, water first travels through the passageway
between septums 40, 41 and 42 to the first step
settling chamber 29 which operates in a manner similar~
to that in the first embodiment. Then water flows
through troughs 26, 27 and 28 to the second step ; j
settling chamber 25 where further settling occurs. ` ¦
Effluent from the chamber 25 flows at the top
through a trough 37 feeding an exit pipe 38. The ~ j
amount of sludge in the effluent from the chamber 25
-is considerably less than that in the chamber 29.
Because of the difference in liquid levels between the
chamber 36 and the chamber 25, sludge can be moved
back into the aeration chamber from the chamber 25 ¦
by creating at the point 35 a pressure lower than at
the point 43. It is accomplished by the fact that ;
two different phenomena are used: in the vicinity
of point 43 pressure differential is produced by the
circulation of water; while at the point 35 pressure -
differential is produced by the motion of the air
bubbles rising to the surface. Because the ~elocity
of rising air bubbles is higher than the velocity of ~,
the clrculating water, it creates lower pressure at ,
.:
~' , ',

~ 5~73
the point 35 of conduit 33 than at port 43, as was
'explained'in the first embodiment~descrip,tion. That
is why a single aerating device 44 for recirculating
sludge from both settling chambers is used in this
5~ embodiment. The aerating device 44 can be either a
mechanical aerator as shown in Figures 1, 2, 3, 4 and
5 or an air diffuser as in Figure 6.
The third embodiment, illustrated in Figure 5
will be seen to be a combination of the features
of the first and second embodiments, in that a pair
of first step settling chambers 51 and 52 are dis-
posed on either side of the aerating chamber 53, this
portion of the third embodiment functioning in
exactly the same manner as the first embodiment. In ¦
addition a second step settling chamber is provided
which receives the effluent through troughs 45, 46
and 47 from the two first step parallel connected
settling chambers. Effluent from the second step
settling chamber 49 leaves the treatment unit at the
top through a trough 50. Sludge from the second step
settling chamber 49 is returned back into aeration . ,
chamber 53 at the end 55 of conduit 54 in exactly
the same manner as the second embodiment. A single
impeller aerating device 48 is used to recover sludge
from each settling chamber in this embodiment. All
three settling chambers 51, 52 and 49 of this emb'odi-
ment can work in series if needed by proper arrange-
ment of the aerating device 48 as is explained in
the first embodiment.
In the fourth embodiment (Figure 6) is shown
(for convenience only) an aeration chamber 56 and
part of the first step settling chamber 57 and'the
second step settling chamber 58. This embodiment
differs from the second embodiment in the use of an
air diffuser aerator 59 instead of a mechanical
.

~9~45~i73
--8--
aerator~ The large amount of air tends to rise to
the surface of the aeration cham~er at a very rapid
rate, creating substantial turbulence to achieve
the same hydrodynamic effect as an impeller.
Return of sludge from the settling chambers 57 and 58
back into the aeration chamber 56 is achieved by
positioning the air diffuser 59 underneath an upper
end 60 of the conduit 61. In this embodiment as
well as in the previous ones, no pumps are needed to
circulate sludge from the settling chambers back
into the aeration chamber.
I wish it to be understood that I do not
consider the invention limited to the precise details
of structure shown and set forth in this specifica-
tion, for obvious modifications will occur to those
skilled in the art to which the invention pertains.
~5

Representative Drawing

Sorry, the representative drawing for patent document number 1145073 was not found.

Administrative Status

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Event History

Description Date
Inactive: Expired (old Act Patent) latest possible expiry date 2000-04-19
Grant by Issuance 1983-04-19

Abandonment History

There is no abandonment history.

Owners on Record

Note: Records showing the ownership history in alphabetical order.

Current Owners on Record
ETLIN, VLADIMIR N.
Past Owners on Record
VLADIMIR N. ETLIN
Past Owners that do not appear in the "Owners on Record" listing will appear in other documentation within the application.
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Document
Description 
Date
(yyyy-mm-dd) 
Number of pages   Size of Image (KB) 
Cover Page 1994-01-05 1 11
Claims 1994-01-05 4 144
Abstract 1994-01-05 1 16
Drawings 1994-01-05 3 63
Descriptions 1994-01-05 8 353