NZ703441B - System and method for treating water or wastewater - Google Patents
System and method for treating water or wastewaterInfo
- Publication number
- NZ703441B NZ703441B NZ703441A NZ70344114A NZ703441B NZ 703441 B NZ703441 B NZ 703441B NZ 703441 A NZ703441 A NZ 703441A NZ 70344114 A NZ70344114 A NZ 70344114A NZ 703441 B NZ703441 B NZ 703441B
- Authority
- NZ
- New Zealand
- Prior art keywords
- chambers
- chamber
- discharge
- water
- control valve
- Prior art date
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D43/00—Separating particles from liquids, or liquids from solids, otherwise than by sedimentation or filtration
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03D—FLOTATION; DIFFERENTIAL SEDIMENTATION
- B03D1/00—Flotation
- B03D1/02—Froth-flotation processes
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03D—FLOTATION; DIFFERENTIAL SEDIMENTATION
- B03D1/00—Flotation
- B03D1/02—Froth-flotation processes
- B03D1/028—Control and monitoring of flotation processes; computer models therefor
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03D—FLOTATION; DIFFERENTIAL SEDIMENTATION
- B03D1/00—Flotation
- B03D1/14—Flotation machines
- B03D1/1406—Flotation machines with special arrangement of a plurality of flotation cells, e.g. positioning a flotation cell inside another
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03D—FLOTATION; DIFFERENTIAL SEDIMENTATION
- B03D1/00—Flotation
- B03D1/14—Flotation machines
- B03D1/1431—Dissolved air flotation machines
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03D—FLOTATION; DIFFERENTIAL SEDIMENTATION
- B03D1/00—Flotation
- B03D1/14—Flotation machines
- B03D1/1443—Feed or discharge mechanisms for flotation tanks
- B03D1/1462—Discharge mechanisms for the froth
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03D—FLOTATION; DIFFERENTIAL SEDIMENTATION
- B03D1/00—Flotation
- B03D1/14—Flotation machines
- B03D1/1443—Feed or discharge mechanisms for flotation tanks
- B03D1/1475—Flotation tanks having means for discharging the pulp, e.g. as a bleed stream
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03D—FLOTATION; DIFFERENTIAL SEDIMENTATION
- B03D1/00—Flotation
- B03D1/14—Flotation machines
- B03D1/24—Pneumatic
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/24—Treatment of water, waste water, or sewage by flotation
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/002—Grey water, e.g. from clothes washers, showers or dishwashers
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2103/00—Nature of the water, waste water, sewage or sludge to be treated
- C02F2103/32—Nature of the water, waste water, sewage or sludge to be treated from the food or foodstuff industry, e.g. brewery waste waters
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2209/00—Controlling or monitoring parameters in water treatment
- C02F2209/44—Time
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2301/00—General aspects of water treatment
- C02F2301/08—Multistage treatments, e.g. repetition of the same process step under different conditions
Abstract
The present invention relates to a treatment system, apparatus, assembly, facility, cycle and/or method for the treatment of water or wastewater, in particular, a system, apparatus, assembly, facility, cycle and/or method for treating water or wastewater received at high flowrates (including in excess of approximately 200L/min) through a series of two or more dissolved air flotation chambers. ss of approximately 200L/min) through a series of two or more dissolved air flotation chambers.
Description
SYSTEM AND METHOD FOR TREATING WATER OR WASTEWATER
FIELD OF THE INVENTION
The present invention relates to a treatment system, apparatus, assembly,
facility, cycle and/or method for the treatment of water or wastewater, in particular, a system,
apparatus, assembly, facility, cycle and/or method for treating water or wastewater.
BACKGROUND OF THE INVENTION
In the field of wastewater treatment, great efforts are continuously being made
to reduce the quantity and concentration of pollutants being discharged into rivers, lakes,
surface and ground water supplies, etc. This is evidenced by more and stricter government
regulations and requirements relating to wastewater treatment processes and discharges.
The quantities of human waste requiring treatment are constantly and rapidly increasing. In
the field of potable water purification, available surface and ground water sources are rapidly
deteriorating due to pollution caused by contaminated runoff and contaminates generated
by a growing population and their careless use of water and improper disposal of waste
products.
For example, one area of current concern is the discharge of grey water into
the Australian river system. House boats and other marine vessels are commonly used
recreational vehicles for families and holiday makers. Under some regulations, grey water
can be discharged into the river but some new regulations require appropriate treatment or
storage of grey water. Treatment of water for human consumption is also an important area
in which the present invention has application. There is also the industrial wastewater
industry where wastewater from small industries (such as food processing industries)
requires treatment.
The present Applicant is the owner of granted Australian patent 2010291882,
incorporated by reference herein, relating to an apparatus and method for the treatment of
water that has proven to be successful in the treatment of water and wastewater, including
in the abovementioned applications. An exemplary embodiment of such apparatus is shown
in Figures 1(a) to 1(d) which demonstrates sequential steps of a treatment cycle using the
apparatus, referenced by numeral 100.
In the example shown, the apparatus 100 includes a feed pump 102 for
transferring, under pressure, water or wastewater via a coagulation coil 104 (to which
coagulant and flocculent is added using respective pumps 106 and 108) to a dissolved air
flotation (DAF) chamber 110 having a submerged contact chamber 112 and an external
pressurised dissolver 114 associated therewith.
The water or wastewater to be treated is pumped into the contact chamber
together with air-saturated water from the dissolver 114 (which receives treated water from
chamber 110 using recirculation pump 116) which degasses upon entry into the contact
chamber 112 and forms bubbles which adhere to suspended matter in the water or
wastewater, causing the suspended matter to float to the surface of the chamber. This is
shown in Figures 1a and 1b. Treated effluent leaves the outlet pipe 118 which has associated
therewith an effluent valve 120 which in Figures 1a and 1b is open. When valve 120 is closed,
the water level in the chamber 110 rises and float material is discharged through the upper
discharge line 122 into a waste tank (not shown), as shown in Figure 1c. The apex shape at
the top of the DAF chamber 110 directs float material upwardly into discharge line 122 and
then outwardly along an outward extension of the discharge line 122, such flow referred to
as a “funnelling effect”. When the valve 120 is open again, as shown in Figure 1d, effluent
continues to discharge through outlet pipe 118 and the cycle starts again.
In this example, the outlet pipe 118 causes water to flow into an inlet 124 of
outlet pipework 126, wherein the height of the inlet dictates the liquid level in the chamber
110 when the valve 120 is open.
Apparatus such as that shown in Figures 1a-1d are adequate for treating
wastewater flows up to a certain flowrate. The flow which can be treated is determined by
the cross sectional surface area of the chamber 110. When the wastewater flowrate gets too
high, the tank geometry requires that the DAF chamber height becomes too high for most
practical applications. In addition, by increasing the cross sectional area (and hence the
height), the “funnelling effect” becomes less efficient as the cross sectional area becomes
too large. As such, there is a need for a water or wastewater treatment apparatus capable
of handling higher flowrates without necessarily increasing the cross sectional area and the
height of the DAF chamber 110.
It is therefore an object of the present invention to overcome at least some of
the aforementioned problems or to provide the public with a useful alternative.
SUMMARY OF THE INVENTION
According to an aspect, the present invention provides a water or wastewater
treatment system or apparatus characterised by two or more dissolved air flotation chambers
each including a submerged contact chamber for directing water entering the contact
chamber to the surface of the dissolved air flotation chamber, first discharge pipework for
float material associated with said two or more dissolved air flotation chambers, a feed pump
means to move water or wastewater into each contact chamber at substantially uniform flow
rates via a feed line, wherein the water or wastewater entering the contact chambers via the
feed line includes suspended matter, a pressurised dissolver for saturating water with air, a
recirculation pump means to move treated water via a recirculation line from each of the
dissolved air flotation chambers to the pressurised dissolver at substantially uniform flow
rates, and then back into the contact chambers, whereby air-saturated water from the
dissolver degasses upon entry into the contact chambers and forms bubbles which adhere
to said suspended matter causing the suspended matter to float to the surface of each
chamber to form a layer of float material, and second discharge pipework for treated water
associated with said two or more dissolved air flotation chambers, said second discharge
pipework including at least one discharge control valve which when closed prevents flow of
treated water from one or more of the dissolved air flotation chambers for a predetermined
time to thereby cause a liquid level in the chambers to rise and said float material to be
discharged through said first discharge pipework, wherein said recirculation line branches
into individual lines that feed each contact chamber with said air-saturated water, each said
branched recirculation line including a back pressure device enabling uniform flow into each
contact chamber.
In an embodiment, the feed line branches into separate lines that feed into
each contact chamber.
In an embodiment, each said branched feed line includes a back pressure
device enabling uniform flow of water or wastewater into each contact chamber. The back
pressure device may be an orifice plate assembly.
In an embodiment, when said control valve associated with the second
discharge pipework is closed, the liquid level in each chamber is caused to rise, and each of
said branched feed lines includes an inlet control valve which when closed prevents flow of
water or wastewater into the corresponding contact chamber, followed by said back pressure
device enabling uniform flow of water or wastewater into each contact chamber, wherein
when said control valve associated with the second discharge pipework is closed, the liquid
level in each chamber is caused to rise except for chambers having a closed inlet control
valve at the corresponding feed line branch.
[This paragraph left intentionally blank].
In an embodiment, each inlet control valve associated with a branched feed
line includes an automatic timer for opening and closing the valves at preset times.
In an embodiment, the control valve associated with the second discharge
pipework includes an automatic timer for opening and closing the valve at preset times, the
automatic timer configured such that after a preset time of the control valve associated with
the second discharge pipework for treated water being open, the control valve associated
with the second discharge pipework is closed, causing the liquid level in the chambers to rise
and float material in the chambers to be discharged through the first float discharge pipework,
and after a further preset time, the control valve associated with the second discharge
pipework is re-opened.
In an alternate embodiment, the automatic timers are configured such that at
the commencement of a treatment cycle, the inlet control valves of feed line branches
associated with a first, second and any additional dissolved air flotation chamber/s are open,
and the control valve associated with the second discharge pipework for treated water is
open.
In this alternate embodiment, the automatic timers are configured such that
after a preset time, the at least one discharge control valve associated with the second
discharge pipework is closed, and the inlet control valves associated with feed line branches
of the second and any additional chambers are closed for a preset time, causing the liquid
level in the first chamber to rise and float material in the first chamber to be discharged
through the first float discharge pipework.
In this alternate embodiment, the automatic timers are configured such that
after a further preset time, the inlet control valve associated with the feed line branch of the
second chamber opens and then the inlet control valve associated with the feed line branch
of the first chamber closes for a preset time, causing the liquid level in the second chamber
to rise and float material in the second chamber to be discharged through the first float
discharge pipework.
In this alternate embodiment, the automatic timers are configured such that
after a further preset time, the control valve associated with the feed line branch of any
additional chamber opens and then the control valve associated with the feed line branch of
the previously open chamber closes for a preset time, causing the liquid level in the additional
chamber to open, and wherein this process is repeated for each additional chamber.
In this alternate embodiment, the automatic timers are configured such that
after a further preset time, the control valves associated with the feed line branches of all
chambers are open, and the at least one discharge control valve associated with the second
discharge pipe for treated water is open.
In an embodiment, said feed pump means is in the form of a first positive
displacement pump for pumping water or wastewater to said chambers, and said
recirculation pump means is in the form of a second positive displacement pump for
recirculating treated water via the recirculation line from the dissolved air flotation chambers
into the contact chambers via the dissolver.
In an embodiment, said treatment cycle repeats until a signal is transmitted to
the positive displacement pumps to discontinue operation, wherein prior to the pumps
discontinuing operation, the control valve associated with the second discharge pipework for
treated water is closed and the liquid level in all chambers is caused to rise and float material
in all chambers caused to be discharged through the first float discharge pipework.
In an embodiment, the means of at least flocculating said water is in the form
of a flocculation chamber.
In an embodiment, the first discharge pipework includes individual branches
from each dissolved air flotation chamber which join to form a single discharge line.
In an embodiment, an upper end of each chamber has an inverted funnel
shape to direct float material through said individual float discharge pipework branches.
In an embodiment, said individual float discharge pipework branches are
vented and extend substantially vertically from an apex of each chamber and then outwardly
and downwardly to enable said discharge before joining said single line, wherein the outward
extension of the branch defines a minimum level at which float material is discharged.
In an alternative embodiment, each vertical extension has associated therewith
an exit control valve, such that when an exit control valve is closed, and the at least one
discharge control valve associated with the second discharge pipework is also closed, only
the chamber/s having an open exit control valve at the corresponding float discharge
pipework branch will see float material discharged.
In an embodiment, said second discharge pipework for treated water includes
a substantially vertical branch which is vented to atmosphere and a substantially horizontal
branch extending from an upper end thereof which defines a liquid level in the chambers.
In an embodiment, said recirculation line extends from a bottom portion of each
dissolved air flotation chamber, and said bottom portion includes a funnel shape to direct any
suspended matter which accumulates in the bottom portion of the chamber into the
recirculation line.
In an embodiment, at the commencement of a treatment cycle, the recirculation
pump means is operated prior to the pump means to ensure that suspended matter which
was not directed to the surface of each chamber in a previous cycle and which has
accumulated at or towards the bottom of each chamber is drawn into the recirculation line
prior to treated water discharging from each chamber.
In another aspect, the present invention provides a method or treatment cycle
for water or wastewater, said method or treatment cycle characterised by pumping water or
wastewater including contaminants via a feed line to each of two or more dissolved air
flotation chambers at substantially uniform flow rates, each said chamber further including
treated water, pumping said treated water from each of the two or more dissolved air flotation
chambers to a pressurised dissolver at substantially uniform flow rates, and then back into
the two or more dissolved air flotation chambers, thereby feeding said chambers with air-
saturated water from the dissolver which causes said contaminants to float towards a top
surface of water in each chamber, thereby forming a layer of float material, each chamber
including a minimum discharge level above the top surface of water defining a height at
which rising float material will exit each chamber into first discharge pipework, discharging
treated water from each chamber via a second discharge pipework for treated water,
discharging said float material by providing at least one discharge control valve at said
second discharge pipework for treated water, and closing the discharge control valve for a
period of time during said treatment cycle to thereby prevent said discharge of treated water
from the chambers and cause the water level in the chambers to rise above said minimum
discharge level causing said float material to be discharged through said first discharge
pipework, wherein said recirculation line branches into individual lines that feed each contact
chamber with said air-saturated water, each said branched recirculation line including a back
pressure device enabling uniform flow into each contact chamber.
[0032a] In an embodiment, the method further includes, after a preset time of the at
least one discharge control valve associated with the second discharge pipework for treated
water being open, closing the at least one discharge control valve associated with the second
discharge pipework, causing the liquid level in one or more of the chambers to rise and float
material in one or more of the chambers to be discharged through the first float discharge
pipework, and after a further preset time, re-opening the at least one discharge control valve
associated with the second discharge pipework for treated water.
In an alternate embodiment, the method or treatment cycle for water or
wastewater further includes at a commencement of a treatment cycle, opening inlet control
valves of feed line branches associated with a first, second and any additional dissolved air
flotation chambers, and opening at least one discharge control valve associated with the
second discharge pipework for treated water.
In this alternate embodiment, the method or treatment cycle for water or
wastewater further includes after a preset time, closing the at least one discharge control
valve associated with the second discharge pipework, and closing the inlet control valves
associated with feed line branches of the second and any additional chambers for a preset
time, causing the liquid level in the first chamber to rise and float material in the first chamber
to be discharged through the float discharge pipework.
In this alternate embodiment, the method or treatment cycle for water or
wastewater further includes after a further preset time, opening the inlet control valve
associated with the feed line branch of the second chamber and then closing the inlet control
valve associated with the feed line branch of the first chamber for a preset time, causing the
liquid level in the second chamber to rise and float material in the second chamber to be
discharged through the first float discharge pipework.
In this alternate embodiment, the method or treatment cycle for water or
wastewater further includes after a further preset time, opening the inlet control valve
associated with the feed line branch of an additional chamber and then closing the inlet
control valve associated with the feed line branch of the previously opened chamber for a
preset time, causing the liquid level in the additional chamber to rise, and repeating this step
for any additional chambers.
In this alternate embodiment, the method or treatment cycle for water or
wastewater further includes after a further preset time, opening the inlet control valves
associated with the feed line branches of all chambers, and opening the at least one
discharge control valve associated with the second discharge pipework for treated water.
In an embodiment, the method or treatment cycle for water or wastewater
further includes repeating the treatment cycle until such time that a signal is transmitted to a
first positive displacement pump responsible for pumping water or wastewater through to
said chambers and a second positive displacement pump responsible for recirculating water
via said dissolver, to discontinue operation of the pumps.
In an embodiment, the method or treatment cycle for water or wastewater
further includes, when said signal is transmitted to the positive displacement pumps and prior
to the pumps discontinuing operation, closing the control valve associated with the second
discharge pipework for treated water to thereby cause the liquid level in all chambers to rise
and float material in all chambers to be discharged through the first discharge pipework, and
then discontinuing operation of the feed pump.
[0039a] In an embodiment, pumping treated water to the pressurised dissolver is
performed at the commencement of a treatment cycle prior to pumping water or wastewater
to the dissolved air flotation chambers, to ensure that suspended matter which was not
directed to the surface of the chambers in a previous treatment cycle and which has
accumulated at or towards the bottom of the chambers is drawn into the recirculation line
prior to treated water discharging from each chamber.
[0039b] In an embodiment, said feed pump means is in the form of a first pump for
pumping water or wastewater to said chambers, and said recirculation pump means is in the
form of a second pump for recirculating treated water via the recirculation line from the
dissolved air flotation chambers into the contact chambers via the dissolver, wherein the first
and second pumps are positive displacement pumps.
BRIEF DESCRIPTION OF THE FIGURES
The accompanying drawings, which are incorporated in and constitute a part
of this specification, illustrate several implementations of the invention and, together with the
description, serve to explain the advantages and principles of the invention. In the drawings:
Figures 1a-1d illustrate schematically the cycle stages of a prior art water or
wastewater treatment apparatus including a single dissolved air flotation
chamber;
Figure 2 illustrates schematically a system for treating high flowrate wastewater
including two or more dissolved air flotation chambers in accordance with an
embodiment of the present invention;
Figure 3 illustrates schematically the system of Figure 2 including inlet control valves at
the feed line inlet branch to each dissolved air flotation chamber in accordance
with an embodiment;
Figure 4 illustrates schematically the system of Figure 2 including an exit control valve
at the float discharge line branch from each dissolved air flotation chamber in
accordance with an embodiment;
Figure 5 illustrates schematically the system of Figure 2 including back pressure
devices at the feed line inlet branch to each dissolved air flotation chamber in
accordance with an embodiment; and
Figure 6 illustrates schematically the system of Figure 2 including an inlet control valve
and a back pressure device at the feed line inlet branch to each dissolved air
flotation chamber in accordance with an embodiment.
DESCRIPTION OF THE PREFERRED EMBODIMENTS
The following detailed description of the invention refers to the accompanying
drawings. Although the description includes exemplary embodiments, other embodiments
are possible, and changes may be made to the embodiments described without departing
from the spirit and scope of the invention. Wherever possible, the same reference numbers
will be used throughout the embodiments and the following description to refer to the same
and like parts.
In an aspect, the present invention relates to a plant, apparatus and/or system
for treating liquids such as water or wastewater 12 and which works on the principles of
dissolved air flotation (DAF) as described in the background of the invention. In another
aspect, the invention relates to a method and/or treatment cycle for treating liquids such as
water or wastewater. The invention is intended for particular use in treating high liquid flow
rates in the order of, but not limited to, 400 to 1600 litres per minute. By way of comparison,
the Applicant’s single-chamber treatment referenced and described in the background of the
invention is used to treat water or wastewater flowrates of approximately 200 litres per
minute. It is to be understood that reference herein to “high liquid flowrates” is intended to
define flowrates in excess of approximately 200 litres per minute which single chamber
treatment facilities such as that shown in Figures 1a-1d may have difficulty handling for
reasons already described in the background of the invention.
A simplified schematic illustration of the system 10 according to an
embodiment is shown in Figure 2. The components of the system 10 may include a feed
pump 12, which according to an embodiment is a positive displacement pump, for feeding
water or wastewater to be treated through the system, at least one pressurised flocculation
chamber 14 for receiving the water or wastewater and configured to introduce coagulant and
flocculant (not shown), and a plurality of dissolved air flotation (DAF) chambers or tanks
(three chambers 16, 18 and 20 in the embodiment shown) each including a respective
submerged contact chamber 22, 24 and 26. As shown in Figure 3, each contact chamber
may have associated input control valves 28, 30 and 32. The system 10 may further include
a second positive displacement pump 34 for recirculating treated water from the bottom of
each DAF chamber through a pressurised dissolver 36 (otherwise known as an “air
saturator”) and wherein air-saturated water is fed back into each contact chamber via a back
pressure device 38, 40 and 42, an effluent line 44 through which treated water from the
bottom of each DAF chamber is discharged via a non-return valve 46, 48 and 50, a further
control valve 52 associated with the effluent line, and a waste float line 54 connected across
the top of each DAF chamber through which float material from each DAF chamber is
discharged. At times throughout this specification, the waste float line 54 will be referred to
as a first discharge pipework, and the effluent line 44 will be referred to as a second
discharge pipework.
It is to be understood that whilst three separate DAF chambers are shown in
the system of Figure 2, any number of two or more DAF chambers could be utilised. It should
also be noted that the inlet control valves 28, 30 and 32 shown in the Figure 3 embodiment
on the inlet lines could be replaced by exit control valves 60, 62 and 64 fitted as an alternative
on the waste float discharge line 54 before the vent line and before they join into a single
common float discharge line, as shown in the Figure 4 embodiment. Still further, there may
be applications which do not require the use of inlet control valves or exit control valves, but
may require the use of back pressure devices 66, 68 and 70 on the branched inlet lines to
each contact chamber to ensure uniform flow into each chamber, as shown in the Figure 5
embodiment. Indeed, combinations of these features may well be utilised according to the
specific application, and the embodiment of Figure 6 as an example shows both inlet control
valves 28, 30 and 32 together with back pressure devices 66, 68 and 70 in use. Whilst it
appears that back pressure devices are present at the inlet and outlet to the dissolver 36,
these are not back pressure devices but are merely to signify a flange connection and hence
have not been referenced or described in detail.
The dissolved air flotation method of the present invention involves taking
treated effluent from the DAF chambers 16, 18 and 20, saturating the effluent with air in the
dissolver 36, and then introducing the air-saturated effluent back into the contact chambers
22, 24 and 26. When the pressurised dissolved air enters the chambers, it degasses,
resulting in the formation of tiny bubbles in the contact chambers (as shown by example in
Figs. 1a-1d). The bubbles adhere to suspended matter in the water or wastewater feed,
causing the suspended matter to float to the top of each DAF chamber forming a layer of
float material which may be in the form of scum or froth.
The float material may be discharged using valve 52 on the effluent line 44.
Those skilled in the art will appreciate that when this valve 52 is shut and water continues to
be pumped into any one of the DAF chambers 16, 18 and 20, the level of water in each DAF
chamber will rise because it can no longer flow downstream of valve 52. Thus, at the start of
a treatment cycle, the automatic valve 52 may be shut, as described in more detail below,
and a timer may be initiated to open the valve 52 after a preset period of time to allow treated
water or wastewater to discharge. Valve 52 may be an automatic valve in this regard. In
having the valve closed for a period of time, the water level in the DAF chamber rises and
the float material is also discharged through line 54. Then, when the valve 52 opens again,
the water level in each DAF chamber will slowly lower as effluent flows beyond valve 52
again, that is, until the original water level is reached again. In an embodiment, the water
level in each tank is set by an uppermost section of pipework in the discharge line 44 through
which vented water flows. In Figures 2-6 this section is referenced using numeral 56 and
represents a pipe which veers horizontally from vertical pipework, however, other pipework
arrangements for setting the level of water in each chamber may be utilised. The physical
appearance of the above described pipework is not shown in Figures 2-6 but can be
appreciated in the prior art Figures 1a-1d with inlet 124 being the equivalent to section 56 of
the present system 10.
The apex or funnel shape at the top of each chamber shown in Figure 2 may
be incorporated to assist in directing float material up through each vertical branch extending
from the top of each chamber to the waste float discharge line 54 as the liquid level in each
chamber rises. The waste float discharge line may also be vented to avoid air locks. The
advantage of this “funnel effect” is that all the scum material may be pushed off the top by
the rising water rather than sticking to surfaces and causing water to flow under the float
material. In using two or more DAF chambers as embodied in the present invention, the
effectiveness of the “funnelling effect” is not compromised as would otherwise be the case
when increasing the cross sectional area and height of a single DAF tank.
[0047a] According to an embodiment, the bottom of each chamber is also funnel
shaped as shown in all of the Figures, and the recirculation line feeds the dissolver 36 from
a bottom portion of the chamber. As an example, the prior art Figures 1a-1d show
recirculation line pipework extending vertically downwardly from the very bottom of the
chamber, however, other configurations may also be suitable. The funnel shape at the
bottom of each DAF chamber ensures that any solids settling to the bottom of the tank are
directed into the recirculation line leading to the dissolver 36 through operation of pump 34.
The accumulation of suspended solids at the bottom of each chamber will have settled
mostly in the time between processing cycles. In the period of time between cycles (which
may be overnight in some instances), the suspended solids in the entire DAF chamber
contents may settle to the bottom of the funnel shape in the DAF chamber. The recirculation
pump 34 may run at the start of each cycle before the feed pump 12 starts to ensure that the
settled solids are re-circulated and floated before the effluent starts to discharge.
Accordingly, the recirculation line may provide two benefits, the first being to ensure solid
matter which has not floated to the top of each chamber but instead accumulated at the
bottom is transferred back up into the contact chamber for removal, and for introducing air
saturated water into each chamber as previously described.
A treatment cycle according to an embodiment of the present invention will now
be described with reference to the physical embodiment shown in Figure 3.
At the commencement of the cycle, inlet control valves 28, 30 and 32 on the
feed lines to the DAF chambers 16, 18 and 20 may be opened. The control valve 52 on the
effluent line 44 may be opened and the feed pump 12 may receive a signal and turn on. This
allows effluent to discharge from each DAF tank 16, 18 and 20 via effluent line 44.
After a preset time, the inlet control valves 30 and 32 on the feed lines to DAF
tanks 18 and 20 may be closed for a preset time at the same time as the effluent line control
valve 52. This causes a rise in the water level in DAF chamber 16 and float material in that
chamber to be pushed off the top through the float discharge pipe 54.
After a further preset time, the inlet control valve 30 on the feed line to the DAF
chamber 18 may be opened and the inlet control valve 28 on the feed line to DAF chamber
16 may be closed for a preset time. This causes a rise in the water level in DAF chamber 18
and float material within that chamber is pushed off the top through the float discharge pipe
After a further preset time, the control valve 32 on the feed line to the DAF
chamber 20 may be opened and the control valve 30 on the feed line to DAF chamber 18
may be closed for a preset time. Float material is pushed off the top of DAF chamber 20
through the float discharge pipe 54.
After a further preset time, the inlet control valves 28 and 32 on feed lines to
the DAF chambers 16 and 20 may be opened and the effluent control valve 52 opened. This
allows effluent to discharge from each DAF chamber 16, 18 and 20 in the same way which
occurred at the commencement of the cycle.
After a further preset time, the inlet control valves 28, 30 and 32 closing and
opening sequence described above may be repeated. This sequence may continue until
such time as the signal to turn off the feed pump 12 and recirculation pump 34 is received,
at which time the control valve 52 on the effluent line is closed and float material is pushed
off the top of the three DAF chambers 16, 18 and 20 for a preset time, after which time the
pumps may be turned off.
In an embodiment, the inlet control valves 28, 30, 32 and control valve 52
include automatic timers for automatically opening and closing said valves in a controlled
sequence.
It is to be understood that the above paragraphs describe but one possible
sequence of float discharge, and the present invention is not intended to be limited to the
discharge sequence of the described embodiment.
The use of two or more dissolved air flotation chambers configured such that
the water level in each chamber is caused to rise and push off float material at preset times
during a treatment cycle results in an efficient water/wastewater treatment system that is
capable of handling high feed flow rates without the need to increase the size or height of a
single-DAF chamber treatment facility. This makes the system ideal for use in environments
with height and space restrictions and wherein water or wastewater requires treatment at
high flowrates.
The back pressure devices 38, 40 and 42 mentioned above may be in the form
of orifice plate assemblies whose function is to cause back pressure in the dissolver 36, and
may be fitted before the dissolved air floatation tanks 16, 18 and 20 on branches off the main
recirculating line as shown in Figures 2-6. This ensures a uniform flow of degassing water
into each DAF chamber 16, 18 and 20 and also ensures degassing does not occur
prematurely. The back pressure devices 66, 68 and 70 described above provide similar
benefits, but for the purpose of providing uniform flow of incoming water or wastewater.
Non return valves 46, 48 and 50 may also be located on the effluent lines from
each DAF chamber 16, 18 and 20 respectively before it joins in with the main effluent line 44
connected to the effluent control valve 52 to prevent water from flowing back from one tank
to the other during the push off cycles.
Water or wastewater may be supplied to the tanks from a collection chamber
which may be a separate tank, a flocculation chamber as per the embodiment shown, or a
river or reservoir, depending on the application.
The flocculation chamber may be in the form of a flocculation coil in which a
suitable coagulant such as aluminium sulphate is injected. In addition, a suitable polymer
may be injected to flocculate suspended matter in the water or wastewater.
The system 10 may further include other water treatment facilitators such as
chlorinators and the like (not shown).
Although not shown, the system 10 may include a suitable control means for
controlling the operation of each of the pumps, the valve 52, and any other device in the
system which may require automatic operation.
The person skilled in the art would now appreciate the various advantages of
the system 10 embodying the present invention. The system 10 provides a means of treating
water or wastewater at high flowrate without compromising the cross sectional size and
height of the system and without compromising efficiency.
Further advantages and improvements may very well be made to the present
invention without deviating from its scope. Although the invention has been shown and
described in what is conceived to be the most practical and preferred embodiment, it is
recognized that departures may be made therefrom within the scope and spirit of the
invention, which is not to be limited to the details disclosed herein but is to be accorded the
full scope of the claims so as to embrace any and all equivalent devices and apparatus.
In any claims that follow and in the summary of the invention, except where the
context requires otherwise due to express language or necessary implication, the word
“comprising” is used in the sense of “including”, i.e. the features specified may be associated
with further features in various embodiments of the invention.
Claims (20)
1. A water or wastewater treatment system or apparatus characterised by: two or more dissolved air flotation chambers each including a submerged contact chamber for directing water entering the contact chamber to the surface of the dissolved air flotation chamber; first discharge pipework for float material associated with said two or more dissolved air flotation chambers; a feed pump means to move water or wastewater into each contact chamber at substantially uniform flow rates via a feed line, wherein the water or wastewater entering the contact chambers via the feed line includes suspended matter; a pressurised dissolver for saturating water with air; a recirculation pump means to move treated water via a recirculation line from each of the dissolved air flotation chambers to the pressurised dissolver at substantially uniform flow rates, and then back into the contact chambers, whereby air-saturated water from the dissolver degasses upon entry into the contact chambers and forms bubbles which adhere to said suspended matter causing the suspended matter to float to the surface of each chamber to form a layer of float material; and second discharge pipework for treated water associated with said two or more dissolved air flotation chambers, said second discharge pipework including at least one discharge control valve which when closed prevents flow of treated water from one or more of the dissolved air flotation chambers for a predetermined time to thereby cause a liquid level in the chambers to rise and said float material to be discharged through said first discharge pipework, wherein said recirculation line branches into individual lines that feed each contact chamber with said air-saturated water, each said branched recirculation line including a back pressure device enabling uniform flow into each contact chamber.
2. A system or apparatus as characterised in claim 1, wherein the feed line branches into separate lines that feed into each contact chamber, each said branched feed line including a back pressure device enabling uniform flow of water or wastewater into each contact chamber.
3. A system or apparatus as characterised in claim 2, wherein when said control valve associated with the second discharge pipework is closed, the liquid level in each chamber is caused to rise, and each of said branched feed lines includes an inlet control valve which when closed prevents flow of water or wastewater into the corresponding contact chamber, followed by said back pressure device enabling uniform flow of water or wastewater into each contact chamber, wherein when said control valve associated with the second discharge pipework is closed, the liquid level in each chamber is caused to rise except for chambers having a closed inlet control valve at the corresponding feed line branch.
4. A system or apparatus as characterised in claim 3, wherein each inlet control valve associated with a branched feed line includes an automatic timer for opening and closing the valves at preset times.
5. A system or apparatus as characterised in any one of the preceding claims, wherein the control valve associated with the second discharge pipework includes an automatic timer for opening and closing the valve at preset times, the automatic timer configured such that: after a preset time of the control valve associated with the second discharge pipework for treated water being open, the control valve associated with the second discharge pipework is closed, causing the liquid level in the chambers to rise and float material in the chambers to be discharged through the first float discharge pipework; and after a further preset time, the control valve associated with the second discharge pipework is re-opened.
6. A system or apparatus as characterised in claim 5 wherein said feed pump means is in the form of a first positive displacement pump for pumping water or wastewater to said chambers, and said recirculation pump means is in the form of a second positive displacement pump for recirculating treated water via the recirculation line from the dissolved air flotation chambers into the contact chambers via the dissolver.
7. A system or apparatus as characterised in claim 6, wherein said treatment cycle repeats until a signal is transmitted to the positive displacement pumps to discontinue operation, wherein prior to the pumps discontinuing operation, the control valve associated with the second discharge pipework for treated water is closed and the liquid level in all chambers is caused to rise and float material in all chambers caused to be discharged through the first float discharge pipework.
8. A system or apparatus as characterised in any one of the preceding claims, wherein said feed line includes a means of at least flocculating said water or wastewater prior to entry into said contact chambers.
9. A system or apparatus as characterised in any one of the preceding claims, wherein the first discharge pipework includes individual branches from each dissolved air flotation chamber which join to form a single discharge line, and wherein an upper end of each chamber has an inverted funnel shape to direct float material through said individual float discharge pipework branches.
10. A system or apparatus as characterised in claim 9, wherein said individual float discharge pipework branches are vented and extend substantially vertically from an apex of each chamber and then outwardly and downwardly to enable said discharge before joining said single line, wherein the outward extension of the branch defines a minimum level at which float material is discharged, wherein each vertical extension has associated therewith an exit control valve, such that when an exit control valve is closed, and the at least one discharge control valve associated with the second discharge pipework is also closed, only the chamber/s having an open exit control valve at the corresponding float discharge pipework branch will see float material discharged.
11. A system or apparatus as characterised in any one of the preceding claims, wherein said second discharge pipework for treated water includes a substantially vertical branch which is vented to atmosphere and a substantially horizontal branch extending from an upper end thereof which defines a liquid level in the chambers.
12. A system or apparatus as characterised in any one of the preceding claims, wherein said recirculation line extends from a bottom portion of each dissolved air flotation chamber, and said bottom portion includes a funnel shape to direct any suspended matter which accumulates in the bottom portion of the chamber into the recirculation line.
13. A system or apparatus as characterised in claim 12, wherein at the commencement of a treatment cycle, the recirculation pump means is operated prior to the feed pump means to ensure that suspended matter which was not directed to the surface of each chamber in a previous cycle and which has accumulated at or towards the bottom of each chamber is drawn into the recirculation line prior to treated water discharging from each chamber.
14. A method or treatment cycle for water or wastewater, said method or treatment cycle characterised by: pumping water or wastewater including contaminants via a feed line to each of two or more dissolved air flotation chambers at substantially uniform flow rates, each said chamber further including treated water; pumping said treated water from each of the two or more dissolved air flotation chambers to a pressurised dissolver at substantially uniform flow rates, and then back into the two or more dissolved air flotation chambers, thereby feeding said chambers with air- saturated water from the dissolver which causes said contaminants to float towards a top surface of water in each chamber, thereby forming a layer of float material, each chamber including a minimum discharge level above the top surface of water defining a height at which rising float material will exit each chamber into first discharge pipework; discharging treated water from each chamber via a second discharge pipework for treated water; and discharging said float material by providing at least one discharge control valve at said second discharge pipework for treated water, and closing the at least one discharge control valve for a period of time during said treatment cycle to thereby prevent said discharge of treated water from the chambers and cause the water level in the chambers to rise above said minimum discharge level causing said float material to be discharged through said first discharge pipework, wherein said recirculation line branches into individual lines that feed each contact chamber with said air-saturated water, each said branched recirculation line including a back pressure device enabling uniform flow into each contact chamber.
15. A method or treatment cycle as characterised in claim 14, further including: after a preset time of the at least one discharge control valve associated with the second discharge pipework for treated water being open, closing the at least one discharge control valve associated with the second discharge pipework, causing the liquid level in one or more of the chambers to rise and float material in one or more of the chambers to be discharged through the first float discharge pipework; and after a further preset time, re-opening the at least one discharge control valve associated with the second discharge pipework for treated water.
16. A method or treatment cycle as characterised in claim 15, further including repeating the treatment cycle until such time that a signal is transmitted to a first positive displacement pump responsible for pumping water or wastewater through to said chambers and a second positive displacement pump responsible for recirculating water via said dissolver, to discontinue operation of the pumps.
17. A method or treatment cycle as characterised in claim 16, further including, when said signal is transmitted to the positive displacement pumps and prior to the pumps discontinuing operation, closing the at least one discharge control valve associated with the second discharge pipework for treated water to thereby cause the liquid level in all chambers to rise and float material in all chambers to be discharged through the first discharge pipework, and then discontinuing operation of the feed pump.
18. A method or treatment cycle as characterised in any one of claims 14 to 17 wherein pumping treated water to the pressurised dissolver is performed at the commencement of a treatment cycle prior to pumping water or wastewater to the dissolved air flotation chambers, to ensure that suspended matter which was not directed to the surface of the chambers in a previous treatment cycle and which has accumulated at or towards the bottom of the chambers is drawn into the recirculation line prior to treated water discharging from each chamber.
19. A system or apparatus as characterised in any one of claims 1 to 13, wherein said feed pump means is in the form of a first pump for pumping water or wastewater to said chambers, and said recirculation pump means is in the form of a second pump for recirculating treated water via the recirculation line from the dissolved air flotation chambers into the contact chambers via the dissolver.
20. A system or apparatus as characterised in claim 19 wherein said first and second pumps are positive displacement pumps.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
NZ729423A NZ729423A (en) | 2014-01-09 | 2014-12-24 | System and method for treating water or wastewater |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
AU2014900061 | 2014-01-09 | ||
AU2014900061A AU2014900061A0 (en) | 2014-01-09 | System and method for treating water or wastewater |
Publications (2)
Publication Number | Publication Date |
---|---|
NZ703441A NZ703441A (en) | 2017-03-31 |
NZ703441B true NZ703441B (en) | 2017-07-04 |
Family
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