EP0120039A1 - Recovery of solids from dispersions - Google Patents

Recovery of solids from dispersions

Info

Publication number
EP0120039A1
EP0120039A1 EP83902942A EP83902942A EP0120039A1 EP 0120039 A1 EP0120039 A1 EP 0120039A1 EP 83902942 A EP83902942 A EP 83902942A EP 83902942 A EP83902942 A EP 83902942A EP 0120039 A1 EP0120039 A1 EP 0120039A1
Authority
EP
European Patent Office
Prior art keywords
dispersion
particles
flocculated
recovery
liquid medium
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Withdrawn
Application number
EP83902942A
Other languages
German (de)
French (fr)
Inventor
Jeremy James Lees
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Ilecard Pty Ltd
Original Assignee
Ilecard Pty Ltd
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Ilecard Pty Ltd filed Critical Ilecard Pty Ltd
Publication of EP0120039A1 publication Critical patent/EP0120039A1/en
Withdrawn legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION 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
    • B03BSEPARATING SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS
    • B03B9/00General arrangement of separating plant, e.g. flow sheets
    • B03B9/06General arrangement of separating plant, e.g. flow sheets specially adapted for refuse
    • B03B9/061General arrangement of separating plant, e.g. flow sheets specially adapted for refuse the refuse being industrial
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D37/00Processes of filtration
    • B01D37/03Processes of filtration using flocculating agents
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION 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
    • B03BSEPARATING SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS
    • B03B1/00Conditioning for facilitating separation by altering physical properties of the matter to be treated
    • B03B1/04Conditioning for facilitating separation by altering physical properties of the matter to be treated by additives
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION 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
    • B03BSEPARATING SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS
    • B03B7/00Combinations of wet processes or apparatus with other processes or apparatus, e.g. for dressing ores or garbage
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION 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
    • B03BSEPARATING SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS
    • B03B9/00General arrangement of separating plant, e.g. flow sheets
    • B03B9/005General arrangement of separating plant, e.g. flow sheets specially adapted for coal
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B03SEPARATION 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
    • B03DFLOTATION; DIFFERENTIAL SEDIMENTATION
    • B03D3/00Differential sedimentation
    • B03D3/06Flocculation
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/34Treatment of water, waste water, or sewage with mechanical oscillations
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F11/00Treatment of sludge; Devices therefor
    • C02F11/12Treatment of sludge; Devices therefor by de-watering, drying or thickening
    • C02F11/121Treatment of sludge; Devices therefor by de-watering, drying or thickening by mechanical de-watering
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W30/00Technologies for solid waste management
    • Y02W30/50Reuse, recycling or recovery technologies
    • Y02W30/52Mechanical processing of waste for the recovery of materials, e.g. crushing, shredding, separation or disassembly

Definitions

  • the present invention relates to a process for the recovery of solid materials from dilute dispersions of finely divided particles of a solid material in a liquid medium.
  • the present invention consists in a process for the recovery of solid materials from dilute dispersions of finely divided particles of a solid material in a liquid medium, the process comprising adding to the dispersion an agglomeration agent capable of inducing flocculation and/or agglomeration of the particles, mixing the agglomeration agent and the dispersion, conditioning the mixture so formed to allow flocculation and/or agglomeration of the finely divided particles to take place until substantially all of the agglomeration agent has been utilized, and passing the flocculated and/or agglomerated mixture, substantially without shearing the flocculated and/or agglomerated particles, to a rapped or vibrated sieve bend such that the flocculated and/or agglomerated particles may be recovered as overflow from the sieve bend and at least part of the liquid medium may be recovered as an underflow therefrom.
  • the present invention further consists in a circuit for the recovery of solid materials from dilute dispersions of finely divided particles of solid material in a liquid medium, the circuit comprising supply means for the dispersion, means to mix the dispersion with a flocculation and/or agglomeration agent, a condition vessel in which the particles of the dispersion may flocculate and/or agglomerate and a rapped or vibrated sieve bend over which the flocculated and/or agglomerated dispersion may be passed to produce an oversize stream or an undersize stream.
  • the present invention is designed to flocculate such particles and remove them on a rapped or vibrated sieve bend.
  • a sieve bend would have the effect of breaking the floccs and would not be effective in recovery of the flocculated and/or agglomerated particles.
  • the present inventors have found, however, that the process according to this invention is extremely effective for the recovery of many types of fine particles from dispersions thereof.
  • Dispersions which have been found to be capable of effective treatment by the method according to this invention include animal wastes such as piggery wastes and cattle effluent wastes, sewage, asbestos and coal.
  • the process according to this invention may be utilised advantageously in respect of particles having a size down to 10 microns and in some cases even below that size.
  • an appropriate agglomeration agent will depend on the solid particles being agglomerated and/or flocculated, however, the selection may be made according to the known parameters in the art. Conveniently polyelectrolytes may be used, however, any of the known agglomeration or flocculation agents may be used.
  • the agglomeration agent must be mixed thoroughly with the dispersion being treated and this may be conveniently achieved by injection of the agglomeration agent into a stream of the dispersions immediately upstream from a pump. It has been found that the turbulence produced by the action of the pump is normally sufficient to adequately mix the agglomeration agent and the dispersion. Other conventional mixing means could, however, be used.
  • Conditioning preferably takes place by passing the stream of the dispersion containing the agglomeration agent through a conditioning vessel in which the rate of flow of the dispersion is substantially reduced. Under conditions of low flow rate the formation of floccs or agglomerates is encouraged and maximum flocc or agglomerate size is achieved. It is essential that the conditioning process be allowed to proceed until substantially all of the agglomeration agent has been utilized in the formation of floccs. If conditioning does not proceed for a sufficient time then there is a danger of floccs being formed in the sieve screen of the sieve bend which will cause blinding of the screen.
  • the conditioning vessel is operated under a mild overpressure in order that the pump used to produce the turbulence at the time of agglomeration agent addition may be used to feed the dispersion through the conditioning vessel and to the sieve bend substantially without shearing of the floccs and/or agglomerates. It is obvious that shearing or other destruction of the floccs and/or agglomerates would be deleterious to the process. It is therefore desirable to avoid the presence of a pump between the conditioning vessel and the sieve bend.
  • the dispersion to which the flocculation and/or agglomeration agent has been added is pumped from a conditioning vessel to the sieve bend by a pump which has only a limited shearing effect on the floccs or agglomerates such as a screw type pump.
  • the flocculation and/or agglomeration agent is preferably added to the dispersion in the conditioning vessel and the mixture slowly stirred as with a paddle stirrer.
  • the dispersion is in one embodiment of the invention preferably fed to the sieve bend as an upward flow through an elutriation device such that a substantially uniform flow of the dispersion occurs across the full width of the sieve bend.
  • the dispersion may be fed to the sieve bend through flow distribution device as described in Australian patent specification 80,859/82.
  • any rapped or vibrated sieve bend may be used in the process according to this invention it is highly desirable to use a sieve bend made according to Australian patent specification 90792/82.
  • This specification describes a sieve bend in which the sieve screen is connected to a surrounding frame only at its end edges. This allows the sieve screen to vibrate more freely under an applied rapping or vibrating force. It has been found that this free vibration of the sieve screen substantially reduces the chance of the screen blinding under any given circumstances.
  • the slot width of the sieve screen on the sieve deck is preferably from 4 millimeters down to 50 microns preferably 300 microns down to 75 microns. The exact size being selected to suit the particular floccs and agglomerates formed in the process.
  • the process according to the present invention has particular advantage when treating sewage or animal effluence. These materials commonly have to be transported for disposal and are normally obtained in a form having a solids content of from 1 to 2% by weight. The cost of transporting these materials is high in relation to their solids content. By utilizing the process according to this invention the solids content may be raised from 10 to 15%.
  • the water produced as underflow has been found to have a sufficiently low chemical and biological oxygen demand that it can be fed directly to conventional drains without adverse ecological effects.
  • the process according to this invention may also be used for the recovery of minerals slimes.
  • agglomeration may be brought about by the use of an agglomeration agent such as oil or polyelectrolytes which will preferentially agglomerate the hydrophobic particles leaving the hydrophilic particles at the water in a dispersed phase.
  • an agglomeration agent such as oil or polyelectrolytes which will preferentially agglomerate the hydrophobic particles leaving the hydrophilic particles at the water in a dispersed phase.
  • the circuit 10 is designed for the concentration of the solids content of piggery effluent.
  • the pigs In the conduct of a modern piggery the pigs are maintained in buildings with a grid like floor through which urine and faecal matter may fall into a disposal channel below the floor. Water is used to clean the styes and wash the effluent along the disposal channels.
  • the tank 11 receives this waste water in the circuit 10. Outflow from the tank 11 is controlled by valve 12 and flows through pipe 13 into a conditioning vessel 14.
  • a flocculent supply tank 15 is provided in the circuit 10. The flocculent is pumped by pump 16 through lines 17 and 18 through valves 19 and 21 respectively into the pipe 13 and the conditioning vessel 14.
  • a slowly moving paddle stirrer 22 is provided within the conditioning vessel 14. This stirrer 22 is driven by an electric motor 23 mounted on the top of the vessel 14 through a drive shaft 24.
  • a low shear, screw type pump 25 pumps the flocculated dispersion from the conditioning vessel through pipe 26 to a rapped sieve bend 27.
  • the sieve bend 27 includes a distribution box 28 to spread the flocculated dispersion evenly across the width of the sieve screen 29 of the sieve bend 27.
  • the sieve screen 29 is so mounted on surrounding frame (not shown) that it can vibrate and flex freely relative to
  • the sieve screen 29 is connected rigidly to the frame along a single end edge and is connected to the frame along the other end edge through a resilient attachment.
  • the sieve screen 29 is provided on its underside with a rapping bar and means 31 are provided to cause the sieve screen 29 to vibrate.
  • the undersize material which passes through the sieve screen 29 into a hopper 32 is discharged through pipe 33.
  • the oversize material is fed off the lower end of the screen 29 into pipe 34.
  • effluent is flowed from tank 11 down pipe 13.
  • the flocculation agent is pumped from tank 15 into pipe 13 to mix with the effluent stream. This mixed stream is then flowed into the conditioning vessel 14 where the slow stirring ensures thorough mixing of the effluent and the flocculation agent. Additional flocculation agent may be added to the conditioning vessel 14 through line 18 if required.
  • the conditioned and flocculated material is then pumped by pump 25, to the distribution means 28 where it is converted from a cylindrical flow into a flat stream flowing evenly onto the sieve bend 27.
  • the sieve screen 29 of the sieve bend 27 divides the dispersion into oversize and undersize streams.
  • the oversize stream largely comprises the flocculated particles of effluent and a proportion of the water while the undersize stream largely comprises water and dissolved organic and inorganic materials but very little solid material.
  • the flocculation reduced the suspended solids and B.O.D. content of the undersize material substantially and to an extent where it could be discharged as drainage effluent.
  • the oversize material was increased from 1 to 2% solids to approximately 15% solids. This substantially reduced the volume of high strength waste which had to be transported for disposal as sewage waste.

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Mechanical Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Separation Of Suspended Particles By Flocculating Agents (AREA)
  • Treatment Of Sludge (AREA)
  • Addition Polymer Or Copolymer, Post-Treatments, Or Chemical Modifications (AREA)

Abstract

Un procédé de récupération de matériaux solides provenant d'une dispersion diluée d'un matériau solide finement divisé, comme des déchets animaux, des eaux résiduelles, de l'amiante et du charbon, comprend l'addition à cette dispersion d'un agent agglomérant capable d'induire la floculation des particules, le mélange de l'agent agglomérant et de la dispersion, le conditionnement du mélange ainsi formé pour permettre à la floculation d'avoir lieu, ainsi que le passage du mélange floculé, pratiquement sans cisailler les particules floculées, dans un coude cribleur que l'on ébranle ou que l'on fait vibrer et la récupération des particules floculées à partir du trop-plein du coude cribleur.A process for recovering solid materials from a dilute dispersion of a finely divided solid material, such as animal waste, waste water, asbestos and coal, comprises adding to this dispersion a caking agent capable of inducing flocculation of the particles, mixing of the agglomerating agent and of the dispersion, conditioning of the mixture thus formed to allow flocculation to take place, as well as the passage of the flocculated mixture, practically without shearing the particles flocculated, in a screening elbow that is shaken or vibrated and the recovery of flocculated particles from the overflow of the screening elbow.

Description

ESC07BRT OF SOLIDS FROM DISPERSIONS TECHNICAL FIELD
The present invention relates to a process for the recovery of solid materials from dilute dispersions of finely divided particles of a solid material in a liquid medium. DISCLOSURE OF INVENTION
The present invention consists in a process for the recovery of solid materials from dilute dispersions of finely divided particles of a solid material in a liquid medium, the process comprising adding to the dispersion an agglomeration agent capable of inducing flocculation and/or agglomeration of the particles, mixing the agglomeration agent and the dispersion, conditioning the mixture so formed to allow flocculation and/or agglomeration of the finely divided particles to take place until substantially all of the agglomeration agent has been utilized, and passing the flocculated and/or agglomerated mixture, substantially without shearing the flocculated and/or agglomerated particles, to a rapped or vibrated sieve bend such that the flocculated and/or agglomerated particles may be recovered as overflow from the sieve bend and at least part of the liquid medium may be recovered as an underflow therefrom.
The present invention further consists in a circuit for the recovery of solid materials from dilute dispersions of finely divided particles of solid material in a liquid medium, the circuit comprising supply means for the dispersion, means to mix the dispersion with a flocculation and/or agglomeration agent, a condition vessel in which the particles of the dispersion may flocculate and/or agglomerate and a rapped or vibrated sieve bend over which the flocculated and/or agglomerated dispersion may be passed to produce an oversize stream or an undersize stream.
Problems have been experienced in the past in the recovery of very finely divided solid particles from dispersions of those particles in a liquid, normally water. It has been known to flocculate these particles as an aid to
OMPI - Z -
their natural settlement or by their removal in some other way. The present invention is designed to flocculate such particles and remove them on a rapped or vibrated sieve bend. In view of the vibratory force applied to the particles during the sieving conventional wisdom is that such a sieve bend would have the effect of breaking the floccs and would not be effective in recovery of the flocculated and/or agglomerated particles. The present inventors have found, however, that the process according to this invention is extremely effective for the recovery of many types of fine particles from dispersions thereof. Dispersions which have been found to be capable of effective treatment by the method according to this invention include animal wastes such as piggery wastes and cattle effluent wastes, sewage, asbestos and coal.
The process according to this invention may be utilised advantageously in respect of particles having a size down to 10 microns and in some cases even below that size.
The selection of an appropriate agglomeration agent will depend on the solid particles being agglomerated and/or flocculated, however, the selection may be made according to the known parameters in the art. Conveniently polyelectrolytes may be used, however, any of the known agglomeration or flocculation agents may be used. The agglomeration agent must be mixed thoroughly with the dispersion being treated and this may be conveniently achieved by injection of the agglomeration agent into a stream of the dispersions immediately upstream from a pump. It has been found that the turbulence produced by the action of the pump is normally sufficient to adequately mix the agglomeration agent and the dispersion. Other conventional mixing means could, however, be used.
Conditioning preferably takes place by passing the stream of the dispersion containing the agglomeration agent through a conditioning vessel in which the rate of flow of the dispersion is substantially reduced. Under conditions of low flow rate the formation of floccs or agglomerates is encouraged and maximum flocc or agglomerate size is achieved. It is essential that the conditioning process be allowed to proceed until substantially all of the agglomeration agent has been utilized in the formation of floccs. If conditioning does not proceed for a sufficient time then there is a danger of floccs being formed in the sieve screen of the sieve bend which will cause blinding of the screen.
In one preferred embodiment of the invention the conditioning vessel is operated under a mild overpressure in order that the pump used to produce the turbulence at the time of agglomeration agent addition may be used to feed the dispersion through the conditioning vessel and to the sieve bend substantially without shearing of the floccs and/or agglomerates. It is obvious that shearing or other destruction of the floccs and/or agglomerates would be deleterious to the process. It is therefore desirable to avoid the presence of a pump between the conditioning vessel and the sieve bend.
In another preferred embodiment of the invention the dispersion to which the flocculation and/or agglomeration agent has been added is pumped from a conditioning vessel to the sieve bend by a pump which has only a limited shearing effect on the floccs or agglomerates such as a screw type pump. In this embodiment of the invention the flocculation and/or agglomeration agent is preferably added to the dispersion in the conditioning vessel and the mixture slowly stirred as with a paddle stirrer.
The dispersion is in one embodiment of the invention preferably fed to the sieve bend as an upward flow through an elutriation device such that a substantially uniform flow of the dispersion occurs across the full width of the sieve bend. In another embodiment of the invention the dispersion may be fed to the sieve bend through flow distribution device as described in Australian patent specification 80,859/82.
While any rapped or vibrated sieve bend may be used in the process according to this invention it is highly desirable to use a sieve bend made according to Australian patent specification 90792/82. This specification describes a sieve bend in which the sieve screen is connected to a surrounding frame only at its end edges. This allows the sieve screen to vibrate more freely under an applied rapping or vibrating force. It has been found that this free vibration of the sieve screen substantially reduces the chance of the screen blinding under any given circumstances. The slot width of the sieve screen on the sieve deck is preferably from 4 millimeters down to 50 microns preferably 300 microns down to 75 microns. The exact size being selected to suit the particular floccs and agglomerates formed in the process.
The process according to the present invention has particular advantage when treating sewage or animal effluence. These materials commonly have to be transported for disposal and are normally obtained in a form having a solids content of from 1 to 2% by weight. The cost of transporting these materials is high in relation to their solids content. By utilizing the process according to this invention the solids content may be raised from 10 to 15%. The water produced as underflow has been found to have a sufficiently low chemical and biological oxygen demand that it can be fed directly to conventional drains without adverse ecological effects. The process according to this invention may also be used for the recovery of minerals slimes. In this case agglomeration may be brought about by the use of an agglomeration agent such as oil or polyelectrolytes which will preferentially agglomerate the hydrophobic particles leaving the hydrophilic particles at the water in a dispersed phase. In this process not only is there a recovery of solids from the dispersion but also a conditioning of the minerals.
BRIEF DESCRIPTION OF THE DRAWINGS Hereinafter given by way of example only is a preferred embodiment of the present invention described with reference to the accompanying drawings which shows schematically a circuit for carrying out the process according to the present invention. • BEST MODE OF CARRYING OUT THE INVENTION
The circuit 10 is designed for the concentration of the solids content of piggery effluent. In the conduct of a modern piggery the pigs are maintained in buildings with a grid like floor through which urine and faecal matter may fall into a disposal channel below the floor. Water is used to clean the styes and wash the effluent along the disposal channels. The tank 11 receives this waste water in the circuit 10. Outflow from the tank 11 is controlled by valve 12 and flows through pipe 13 into a conditioning vessel 14. A flocculent supply tank 15 is provided in the circuit 10. The flocculent is pumped by pump 16 through lines 17 and 18 through valves 19 and 21 respectively into the pipe 13 and the conditioning vessel 14.
A slowly moving paddle stirrer 22 is provided within the conditioning vessel 14. This stirrer 22 is driven by an electric motor 23 mounted on the top of the vessel 14 through a drive shaft 24.
A low shear, screw type pump 25 pumps the flocculated dispersion from the conditioning vessel through pipe 26 to a rapped sieve bend 27. The sieve bend 27 includes a distribution box 28 to spread the flocculated dispersion evenly across the width of the sieve screen 29 of the sieve bend 27.
The sieve screen 29 is so mounted on surrounding frame (not shown) that it can vibrate and flex freely relative to
the frame. The sieve screen 29 is connected rigidly to the frame along a single end edge and is connected to the frame along the other end edge through a resilient attachment. The sieve screen 29 is provided on its underside with a rapping bar and means 31 are provided to cause the sieve screen 29 to vibrate. The undersize material which passes through the sieve screen 29 into a hopper 32 is discharged through pipe 33. The oversize material is fed off the lower end of the screen 29 into pipe 34. In use effluent is flowed from tank 11 down pipe 13.
The flocculation agent is pumped from tank 15 into pipe 13 to mix with the effluent stream. This mixed stream is then flowed into the conditioning vessel 14 where the slow stirring ensures thorough mixing of the effluent and the flocculation agent. Additional flocculation agent may be added to the conditioning vessel 14 through line 18 if required. The conditioned and flocculated material is then pumped by pump 25, to the distribution means 28 where it is converted from a cylindrical flow into a flat stream flowing evenly onto the sieve bend 27. The sieve screen 29 of the sieve bend 27 divides the dispersion into oversize and undersize streams. The oversize stream largely comprises the flocculated particles of effluent and a proportion of the water while the undersize stream largely comprises water and dissolved organic and inorganic materials but very little solid material.
The above circuit was use to treat piggery effluent with a high cationic flocculant sold under the registered trade mark "PRAESTOL". The results obtained were as follows:- Sample Suspended Solids B.O.D,
Feed 6800 5800
Undersize material 3300 4700 obtained by sieving without flocculation
Undersize material 1100 obtained by sieving after flocculation
It can be seen that the flocculation reduced the suspended solids and B.O.D. content of the undersize material substantially and to an extent where it could be discharged as drainage effluent. The oversize material was increased from 1 to 2% solids to approximately 15% solids. This substantially reduced the volume of high strength waste which had to be transported for disposal as sewage waste.

Claims

THE CLAIMS DEFINING THE INVENTION ARE AS FOLLOWS:
1. A process for the recovery of solid materials from dilute dispersions of finely divided particles of a solid material in a liquid medium, the process comprising adding to the dispersion an agglomeration agent capable of inducing flocculation and/or agglomeration of the particles, mixing the agglomeration agent and the dispersion, conditioning the mixture so formed to allow flocculation and/or agglomeration of the finely divided particles to take place until substantially all of the agglomeration agent has been utilized, and passing the flocculated and/or agglomerated mixture, substantially without shearing the flocculated and/or agglomerated particles, to a rapped or vibrated sieve bend such that the flocculated and/or agglomerated particles may be recovered as overflow from the sieve bend and at least part of the liquid medium may be recovered as an underflow therefrom.
2. A process as claimed in Claim 1 in which the liquid medium is selected from the group comprising piggery wastes, cattle effluent wastes, sewage, asbestos slurries and coal slurries.
3. A process as claimed in Claim 1 or Claim 2 in which the agglomeration agent is a polyelectrolyte.
4. A process as claimed in any one of Claims 1 to 3 in which the conditioning of the mixture is brought about by passing the stream of the dispersion containing the agglomeration agent through a conditioning vessel in which the rate of flow of the dispersion is substantially less than its rate of flow immediately prior to its entering the conditioning vessel.
5. A process as claimed in Claim 1 in which the sieve bend has a sieve screen having apertures with a width of from 200 microns to 75 microns.
6. A circuit for the recovery of solid materials from dilute dispersion of finely divided particles of solid material in a liquid medium, the circuit comprising supply means for the dispersion means to mix the dispersion with a flocculation and/or agglomeration agent, a condition vessel in which the particles of the dispersion may flocculate and/or agglomerate and a rapped or vibrated sieve bend over which the flocculated and/or agglomerated dispersion may be passed to produce an oversize stream and an undersize stream.
7. A circuit as claimed in Claim 6 in which the sieve bend has a sieve screen having apertures with a width of from 200 microns to 75 microns.
8. A circuit as claimed in Claim 6 in which stirring means are provided in the conditioning vessel to slowly mix the dispersion and the flocculating and/or agglomeration agent.
9. A process for the recovery of solid materials from dilute dispersions of finely divided particles of a solid material in a liquid medium substantially as hereinbefore described with reference to the accompanying drawing.
10. A circuit for the recovery of solid materials from dilute dispersions of firmly divided particles of a solid material in a liquid medium substantially as hereinbefore described with reference to the accompanying drawing.
OMPr
EP83902942A 1982-09-29 1983-09-26 Recovery of solids from dispersions Withdrawn EP0120039A1 (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
AUPF611382 1982-09-29
AU6113/82 1982-09-29

Publications (1)

Publication Number Publication Date
EP0120039A1 true EP0120039A1 (en) 1984-10-03

Family

ID=3769764

Family Applications (1)

Application Number Title Priority Date Filing Date
EP83902942A Withdrawn EP0120039A1 (en) 1982-09-29 1983-09-26 Recovery of solids from dispersions

Country Status (5)

Country Link
EP (1) EP0120039A1 (en)
JP (1) JPS59501616A (en)
AU (1) AU1948183A (en)
WO (1) WO1984001313A1 (en)
ZA (1) ZA837242B (en)

Families Citing this family (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
GB8411192D0 (en) * 1984-05-02 1984-06-06 Celltech Ltd Separating animal cells from liquid culture
AU617698B2 (en) * 1987-10-22 1991-12-05 Edward Harris Greenwald Sr. Method and apparatus for separating clay from and then dewatering ultra fine coal
AU622805B2 (en) * 1989-06-05 1992-04-16 Malco Engineering Pty. Limited Combination bend screen
DE19828027A1 (en) * 1998-06-24 1999-12-30 Rheinische Werkzeug & Maschf Screening machine for separating granular materials
GB2339425A (en) * 1998-07-11 2000-01-26 Clearmasters Environmental Lim De-watering apparatus
JP2013081895A (en) * 2011-10-07 2013-05-09 Ulvac Japan Ltd Recovering apparatus and recovering method

Family Cites Families (7)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
AU2307370A (en) * 1970-12-07 1972-06-08 N. B. Love Industries Pty. Ltd Flocculating particles in washing streams
AU474017B2 (en) * 1972-09-12 1976-07-08 Ceres Land Company Process and apparatus for recovering feed products from animal manure
PL104587B1 (en) * 1976-03-27 1979-08-31 Kopalnia Wegla Kamiennego Bolesl MACHINE FOR CONTINUOUS DEWATERING IN THE PROCESS OF HYDROMECHANICAL AND MECHANICAL PROCESSING OF FLOCKED MULLS
AT357118B (en) * 1978-10-27 1980-06-25 Andritz Ag Maschf DEVICE FOR CONTROLLING A DRAINAGE MACHINE
JPS6089B2 (en) * 1980-09-05 1985-01-05 日立機電工業株式会社 Sludge dewatering treatment method and its equipment
AU539260B2 (en) * 1981-11-19 1984-09-20 Ilecard Pty. Ltd. Sieve screen deck
JPS6099416A (en) * 1983-11-04 1985-06-03 Mitsubishi Electric Corp Speed control device of rolling mill

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
See references of WO8401313A1 *

Also Published As

Publication number Publication date
JPS59501616A (en) 1984-09-13
ZA837242B (en) 1984-11-28
AU1948183A (en) 1984-04-24
WO1984001313A1 (en) 1984-04-12

Similar Documents

Publication Publication Date Title
KR100851456B1 (en) Method and apparatus for treatment of water
KR100599985B1 (en) Coagulation reaction device
JP3691768B2 (en) Sludge treatment method
US20080296232A1 (en) Wastewater clarifier and process
US5942115A (en) Self flocculating separation medium and method
CA1227294A (en) Process for separating mineral ultra-fine grain from washings obtained in coal processing or from coal slurries
MXPA97006284A (en) Method and method of separation of auto-floculac
US2204703A (en) Treatment of wastes
EP0120039A1 (en) Recovery of solids from dispersions
US3300403A (en) Sewage treatment
US4671881A (en) Sewage treatment process
JPH03118896A (en) Method for removing the solid phase from a liquid substance, particularly waste water purification method
US11319247B2 (en) Fine grit classifier
JP2020525274A (en) Water treatment plant with integrated ballasted flocculation and sedimentation and corresponding method
KR100859873B1 (en) Method and treatment apparatus of dredged sediment
EP1371614B1 (en) Process for treating sludge involving a particular shear stirrer
KR102481981B1 (en) Solidification treatment system for recycling of coagulation sediment
JP2003010900A (en) Sludge treatment method, sludge treatment system and sludge improving apparatus
CN210419616U (en) Reaction zone structure and sewage sedimentation system of quick compounding
NO841866L (en) RECOVERY OF SOLID SUBSTANCES FROM DISPERSIONS
JPH0686986A (en) Method for treating waste liquid and device using the method
JPS59193993A (en) De-ashing device for coal
JP6199223B2 (en) Stirring device used for removing radioactive substance, removing device therefor, and removing method
JPS61129085A (en) Treatment of sewage
JPS6146300A (en) Excrement treating apparatus

Legal Events

Date Code Title Description
PUAI Public reference made under article 153(3) epc to a published international application that has entered the european phase

Free format text: ORIGINAL CODE: 0009012

AK Designated contracting states

Designated state(s): AT CH DE FR GB LI NL SE

17P Request for examination filed

Effective date: 19841001

STAA Information on the status of an ep patent application or granted ep patent

Free format text: STATUS: THE APPLICATION HAS BEEN WITHDRAWN

18W Application withdrawn

Withdrawal date: 19870206

RIN1 Information on inventor provided before grant (corrected)

Inventor name: LEES, JEREMY, JAMES