System and method for removing dissolved contaminants, particulate contaminants, and oil contaminants from industrial waste water

Information

  • Patent Grant
  • 8840786
  • Patent Number
    8,840,786
  • Date Filed
    Wednesday, January 9, 2008
    17 years ago
  • Date Issued
    Tuesday, September 23, 2014
    10 years ago
Abstract
A system for removing dissolved contaminants, particulate contaminants, and oil contaminants from industrial waste water, the system including a gas floatation and primary oil contaminant removal subsystem including a tank for receiving a flow of the industrial waste water and a flow of gaseous microspheres, wherein the gaseous microspheres combine with oil droplets in the waste water to form flocs which float to the surface and are removed to provide processed waste water with the majority of the oil contaminants removed, and a contaminant removal subsystem for removing dissolved contaminants, particulate contaminants, and any remaining oil contaminants from the processed waste water.
Description
FIELD OF THE INVENTION

This invention relates to a system and method for removing dissolved contaminants, particulate contaminants and oil contaminants from industrial waste water.


BACKGROUND OF THE INVENTION

The oil industry produces large amounts of waste water during exploration and production of petroleum. It has been estimated that approximately 800 gallons of water are used for the production of a barrel of oil of which approximately 80% is used for cooling in the refinery process. Oil wastes are classified depending on their origin, e.g., from oil production or from oil refining. Waste water from oil production is generally a mixture of drilling muds, salt water, free and emulsified oil and natural gas. Waste water from oil refineries includes, inter alia, free and emulsified oils from leaks, spills, and other sources. The combined refinery wastes or spills may contain crude oil and various fractions thereof, dissolved or suspended mineral and organic compounds discharged in liquors and sludges in various stages of processing.


Cleaning of industrial waste water from oil production and oil refining is important for both environmental and industry purposes. There are many conventional processes for cleaning oil industrial waste water which include, for example, gravity separation, floatation, filtration, chemical treatments, electrochemical treatments, biochemical treatments, and the like. These systems are typically large, inefficient, and expensive to operate. The only known process which can achieve a final effluent with less than 5 p.p.m. oil contaminants is membrane filtration. However, membrane filtration is expensive and difficult to operate because the membranes quickly foul.


BRIEF SUMMARY OF THE INVENTION

It is therefore an object of this invention to provide a system and method for removing dissolved contaminants, particulate contaminants, and oil contaminants from industrial waste water.


It is a further object of this invention to provide such a system and method which removes dissolved contaminants, particulate contaminants, and oil contaminants from industrial waste water generated by oil production and oil refining processes.


It is a further object of this invention to provide such a system and method which removes dissolved contaminants, particulate contaminants, and oil contaminants from industrial waste water to an acceptable level required by the Environmental Protection Agency (EPA).


It is a further object of this invention to provide such a system and method which produces a final effluent which can be reused by oil production and oil refining processes.


It is a further object of this invention to provide such a system and method which provides a final effluent with less than 5 p.p.m. of oil contaminants.


It is a further object of this invention to provide such a system and method which provides a final effluent with less than 5 p.p.m. of particulate contaminants.


It is a further object of this invention to provide such a system and method which utilizes less space.


It is a further object of this invention to provide such a system and method which eliminates the problems associated with using membranes.


It is a further object of this invention to provide such a system and method which reduces costs.


It is a further object of this invention to provide such a system and method which recycles weighting agents.


It is a further object of this invention to provide such a system and method which is more effective.


The subject invention, however, in other embodiments, need not achieve all these objectives and the claims hereof should not be limited to structures or methods capable of achieving these objectives.


This invention features a system for removing dissolved contaminants, particulate contaminants, and oil contaminants from industrial waste water, the system including a gas floatation and primary oil contaminant removal subsystem including a tank for receiving a flow of the industrial waste water and a flow of gaseous microspheres, wherein the gaseous microspheres combine with oil droplets in the waste water to form flocs which float to the surface and are removed to provide processed waste water with the majority of the oil contaminants removed, and a contaminant removal subsystem for removing dissolved contaminants, particulate contaminants, and any remaining oil contaminants from the processed waste water.


In a preferred embodiment, the gas floatation and primary oil contaminant removal subsystem may further include a floc removal subsystem for removing the flocs from the surface of the waste water. The subsystem may include a skimmer. The system may include a cooling subsystem for reducing the temperature of the waste water to an appropriate temperature for use with a desired flocculant. The system may further include a buffer tank for regulating the flow of waste water and removing coarse particulates in the waste water. The contaminant removal subsystem may include a coagulation mixing tank for receiving the processed waste water and introducing and mixing a coagulant with the processed waste water to precipitate the dissolved contaminants and form flocs of the precipitated dissolved contaminants and of the particulate contaminants. The system may further include a weighting agent mixing tank for receiving the processed waste water from the coagulation mixing tank and introducing and mixing a weighting agent with the processed waste water. The system may further include a flocculation subsystem for receiving the processed waste water from the weighting agent mixing tank and introducing and mixing a flocculant to form large flocs of the weighting agent and the microflocs of the particulate contaminants and/or large flocs of the weighting agent and the precipitated dissolved contaminants and/or large flocs of the weighting agent and any remaining oil particulates and/or large flocs of the weighting agent and any other particulates present in the waste water. The system may further include a separation subsystem for separating the large flocs from the processed waste water to form a clear effluent. The system may further include an oxidation subsystem for introducing an oxidation agent to the processed waste water for changing the electrical charges on one or more of the particulate contaminants and/or the oil contaminants. Oxidation agent may include hydrogen peroxide. The weighting agent may include magnetite. The weighting agent may include coal fines. The separation subsystem may include a clarifier. The separation subsystem may include a rapid settler. The separation subsystem may include hydrocyclone. The system may further include a weighting agent recovery subsystem for recovering the weighting agent. The weighting agent recovery system may include a high shear mixer subsystem. The weighting agent recovery subsystem may include a high gradient magnetic filter for removing fine magnetized weighting agents from the clear effluent. The weighting agent recovery subsystem may include a wet drum magnetic separator. The system may further include a recycling subsystem for recycling the weighting agent to the weighting agent mixing tank. The system may further include a re-circulation system for re-circulating sludge formed from large flocs of the weighting agent and the microflocs of the particulate contaminants and/or large flocs of the weighting agent and the precipitated dissolved contaminants and/or large flocs of the weighting agent and any remaining oil particulates and/or large flocs of the weighting agent and any other particulates present in the waste water. The flocculation subsystem may include a static mixer and/or a mixing tank. The oxidation subsystem may include a static mixer. The separation subsystem may include a skimmer disposed inside the clarifier for coalescing the oil contained in the processed waste water and driving the coalesced oil particulates to the surface of the clarifier. The clear effluent may have less than about 5 p.p.m. of oil contaminants, dissolved contaminants, and particulate contaminants.


The invention may also feature a system for removing dissolved contaminants, particulate contaminants, and oil contaminants from industrial waste water, the system including a gas floatation and primary oil contaminate removal subsystem including a tank for receiving a flow of the industrial waste water and a flow of gaseous microspheres, wherein the gaseous microspheres combine with oil droplets in the waste water to form flocs which float to the surface and are removed to provide processed waste water with the majority of the oil contaminants removed, a cooling subsystem for reducing the temperature of the waste water to an appropriate temperature for use with a desired flocculent, and a contaminant removal subsystem for receiving the waste water from the gas floatation subsystem for removing dissolved contaminants, particulate contaminants, and any remaining oil contaminants from the processed waste water.


The invention further features a system for removing dissolved contaminants, particulate contaminants, and oil contaminants from industrial waste water, the system including a gas floatation and primary oil removal subsystem including a tank for receiving a flow of industrial waste water and a flow of gaseous microspheres, wherein the gaseous microspheres combine with oil droplets in the waste water to form flocs which float to the surface and are removed to provide processed waste water with the majority of the oil contaminants removed, a buffer tank for regulating the flow of oily waste water and removing coarse particulates in the waste water, and a contaminant removal subsystem for receiving the waste water from the gas floatation subsystem for removing dissolved contaminants, particulate contaminants, and any remaining oil contaminants from the processed waste water.


The invention further features a system for removing dissolved contaminants, particulate contaminants, and oil contaminants from industrial waste water, the system including a gas floatation and primary oil removal subsystem including a tank for receiving a flow of the industrial waste water and a flow of gaseous microspheres, wherein the gaseous microspheres combine with oil droplets in the waste water to form flocs which float to the surface and are removed to provide processed waste water with the majority of the oil contaminants removed, a cooling subsystem for reducing the temperature of the waste water to an appropriate temperature for use with a desired flocculant, a buffer tank for regulating the flow of waste water and removing coarse particulates in the oily waste water, and a contaminant removal subsystem for receiving the waste water from the gas floatation subsystem for removing dissolved contaminants, particulate contaminants, and any remaining oil contaminants from the processed waste water.


This invention further features a system for removing dissolved contaminants, particulate contaminants, and oil contaminants from industrial waste water, the system including a gas floatation and primary oil removal subsystem including a tank for receiving a flow of the industrial waste water and a flow of gaseous microspheres, wherein the gaseous microspheres combine with oil droplets in the waste water to form flocs which float to the surface and are removed to provide processed waste water with the majority of the oil contaminants removed, a cooling tank for reducing the temperature of the waste water to an appropriate temperature for use with a desired flocculant, a buffer tank for regulating the flow of waste water and removing coarse particulates in the oily waste water, and a contaminant removal subsystem for removing dissolved contaminants, particulate contaminants, and any remaining oil contaminants from the processed waste water. The contaminant removal subsystem includes a coagulation mixing tank for receiving the processed waste water and introducing and mixing a coagulant with the waste water to form microflocs of the particulate contaminants and to precipitate the dissolved contaminants. A weighting agent mixing tank receives the processed waste water from the coagulation mixing tank and introduces and mixing a weighting agent with the processed waste water, a flocculation mixing tank receives the processed waste water from the weighting agent mixing tank and introduces and mixes a flocculant to form large flocs of the weighting agent and the microflocs of the particulate contaminants and/or large flocs of the weighting agent and the precipitated dissolved contaminants and/or large flocs of the weighting agent and remaining oil particulates and/or large flocs of the weighting agent and any other particulates present in the waste water. A separation subsystem separates the large flocs from the processed waste water to form a clear effluent.





BRIEF DESCRIPTION OF THE SEVERAL VIEWS OF THE DRAWINGS

Other objects, features and advantages will occur to those skilled in the art from the following description of a preferred embodiment and the accompanying drawings, in which:



FIG. 1 is a schematic block diagram of one embodiment of the system for removing dissolved contaminants, particulate contaminants, and oil contaminants from industrial waste water of this invention;



FIG. 2 is a schematic block diagram of the system shown in FIG. 1 incorporating a cooling subsystem in accordance with one embodiment of this invention;



FIG. 3 is a schematic block diagram of another embodiment of the system shown in FIG. 2 utilizing coal fines as a weighting agent in accordance with this invention;



FIG. 4 is a schematic block diagram of another embodiment of the system shown in FIGS. 1-3 incorporating a buffer subsystem and also showing the primary components of one embodiment of the contaminant removal subsystem;



FIG. 5 is a schematic block diagram of yet another embodiment of the system for removing dissolved contaminants, particulate contaminants, and oil contaminants from industrial waste water of this invention; and



FIG. 6 is a schematic side view of one embodiment of a clarifier and oil skimmer that may be employed with the system shown in FIGS. 1-5.





DETAILED DESCRIPTION OF THE INVENTION

Aside from the preferred embodiment or embodiments disclosed below, this invention is capable of other embodiments and of being practiced or being carried out in various ways. Thus, it is to be understood that the invention is not limited in its application to the details of construction and the arrangements of components set forth in the following description or illustrated in the drawings. If only one embodiment is described herein, the claims hereof are not to be limited to that embodiment. Moreover, the claims hereof are not to be read restrictively unless there is clear and convincing evidence manifesting a certain exclusion, restriction, or disclaimer.


As discussed in the Background section above, conventional processes for cleaning oil industry waste water, such as gravity separation, floatation, filtration, chemical treatments, electrochemical treatments, biochemical treatments, and the like, are inefficient, large, expensive to operate, and typically incapable of producing a final effluent with less than 5 p.p.m. of oil and/or particulate contaminants. Although membrane filtration systems can produce a final effluent with less than 5 p.p.m. of oil contaminants, these systems are expensive and difficult to operate because the membrane filter quickly fouls.


In contrast, system 10, FIG. 1, for removing dissolved contaminants, particulate contaminants, and oil contaminants from industrial waste water of this invention includes gas floatation and primary oil contaminant removal subsystem 12 which receives flow of industrial waste water 14, e.g., from oil production processes, oil refining processes, and the like. Subsystem 12, e.g., a dissolved air floatation (DAF) subsystem, receives flow of gaseous microspheres 16, e.g., from an air source with a bubble flow distribution subsystem. The flow of gaseous microspheres 16 combines with oil droplets in flow of industrial wastewater 14 in subsystem 12.


When oil is in an emulsified state, it exists as a colloidal suspension. When oil is in a free state, it is present as micro-droplets. The micro-droplets, when suspended in waste water, possess negative charge surfaces which creates repulsive forces between the droplets. The gaseous microspheres from flow of gaseous microspheres 16 are positively charged and are attracted to the oil droplets. The interaction of gaseous microspheres 16 with the oil droplets in industrial waste water 14 forms flocs. The flocs of the oil micro-droplets and the gaseous microspheres float to the surface of the waste water and are removed as recovered oil 18, e.g., with a skimmer or similar type device. This removes the majority of oil contaminants from the industrial waste water and is output as processed waste water by line 22.


Contaminant removal subsystem 20 receives the processed waste water from subsystem 12 by line 22 and removes dissolved contaminants, particulate contaminants, and any remaining oil contaminants from the processed waste water by line 22 to provide a final clear effluent by line 50 which preferably has a concentration of oil contaminants, particulate contaminants, and dissolved contaminants which are less than about 5 p.p.m. each, as discussed in detail below.


In one embodiment, contaminant removal subsystem 20 includes coagulation mixing tank 24 with mixer 26 which receives the processed waste water from subsystem 12, by line 22 and introduces coagulant 28, e.g., aluminum, FeCl3, PAC (polyaluminum chloride), and the like, to tank 24. Mixer 26 mixes the coagulant and the processed waste water to precipitate the dissolved contaminants in the waste water and form microflocs of precipitated dissolved contaminants and particulates.


Contaminant removal subsystem 20 also preferably includes weighting agent mixing tank 30 with mixer 32 which receives the processed waste water from coagulation mixing tank 24 by line 34 and introduces weighting agent or magnetic ballast 34, e.g., magnetite or similar type weighting agents known to those skilled in the art. Mixer 32 mixes the weighting agent 34 with the processed waste water in tank 30. As known by those skilled in the art, the weighting agent provides for rapid settling of flocs, as discussed below.


Subsystem 20 preferably includes flocculation mixing tank 36 which receives the processed waste water from weighting agent mixing tank 30 by line 40 and introduces flocculant 42. Mixer 38 mixes flocculant 42 with the processed waste water in tank 36 to form large flocs of the weighting agent and the microflocs of the particulate contaminants and/or large flocs of the weighting agent and the precipitated dissolved contaminants and/or large flocs of the weighting agent and any remaining oil particulates and/or large flocs of any other particulates present in the processed waste water received by line 40. The flocculant, e.g., a polymer, has an electrical charge (anionic or cationic) which attracts the weighting agent, the microflocs of the particulate contaminants, the precipitated dissolved contaminants, any remaining oil particulates, and any other particulates present in the waste water to form the large flocs which are separated using separation subsystem 44. The weighting agent provides for rapid settling of the flocs separation subsystem 44.


Separation subsystem 44 separates the large flocs of the weighting agent and the microflocs of the particulate, large flocs of the weighting agent and the precipitated dissolved contaminants and/or large flocs of the weighting agent and any remaining oil particulates and/or large flocs of any other particulates present in the processed waste water to provide a clear effluent on line 50, e.g., a final effluent having less than 5 p.p.m. each of oil contaminants, and particulate contaminants. As known to those skilled in the art, separation subsystem 44 may include a clarifier, a rapid settler, or a hydrocyclone.


In one design, system 10 may include recycling and re-circulating subsystem 46 which recovers and recycles weighting agent or magnetic ballast 34 from the processed waste water in separation subsystem 40 by line 48 and also re-circulates the sludge of the large flocs of the weighting agent and contaminants by line 48 (discussed below).


In one embodiment, system 10 includes an oxidation subsystem 29 for introducing an oxidation agent, e.g., hydrogen peroxide or similar oxidation agent known to those skilled in the art, to the processed water in coagulation mixing tank 24 in order to change the electrical charges of one or more of the particulate contaminants and/or the oil contaminants in the waste water and to improve the formation of flocs. Additional examples of contaminant removal subsystem 20 are disclosed in U.S. Pat. No. 6,099,738 by the inventors hereof, incorporated by reference herein.


The result is system 10 for removing dissolved contaminants, particulate contaminants, and oil contaminants from industrial waste water of this invention effectively and efficiently removes dissolved contaminants, particulate contaminants, and oil contaminants from industrial waste water. e.g., generated from oil production and/or oil refining processes. System 10 provides a final clean effluent, preferably having a level of oil contaminants and particulate contaminants less than about 5 p.p.m. each. Such a level is an acceptable level required by the EPA and can be reused by oil production and/or oil refining processes. Moreover, system 10 does not require the use of any membranes or filters, thus the problems associated therewith are eliminated. System 10 is less expensive and utilizes less space than conventional industrial waste water cleaning systems. The ability to recycle the weight agents further decreases processing costs.


In one embodiment, system 10′, FIG. 2, where like parts have been given like numbers, includes cooling subsystem 52. Cooling subsystem 52 reduces the temperature of the waste water received from gas floatation and primary oil contaminant removal subsystem 12 by line 22 to an appropriate temperature on line 23, e.g., about 50° C., for use with a desired flocculant, e.g., a polymer such as Cytec A-130 or similar flocculant type known by those skilled in the art.


In one design, weighting agent 34′, FIG. 3, where like parts have been given like numbers, may be coal fines. Using coal fines as the weighting agent generates a final sludge which can be filtered, dried, and used as a combustible.


In another design, system 10′″, FIG. 4, where like parts have been given like numbers, includes gas floatation and primary oil contaminant subsystem 12 which receives flow of industrial waste water 14 and operates similar as discussed above with reference to FIG. 1. System 10′ also preferably includes buffer tank 56 which regulates the flow of waste water, e.g., from cooling subsystem 52 by line 23 and removes coarse particulates from the waste water. Although, as shown in FIG. 4 buffer tank 56 is located between cooling subsystem 52 and contaminant removal subsystem 20, this is not a necessary limitation of this invention, as buffer tank 56 may be located at any desired location in system 10.


In one design, contaminant removal subsystem 20′ receives the cooled and regulated waste water from cooling subsystem 52 and buffer tank 56 by line 57. Static mixers 60 introduce and mix the coagulant via coagulant feed R1-92 by line 83 and/or the oxidation agent via oxidation feed R2-84 by line 85. The coagulant and/or oxidation agent interacts with plates 62 of static mixers 60 to effectively mix of the coagulant and/or the oxidizing agent with the processed waste water in line 57. The statically mixed coagulant and/or oxidizing agent with the processed waste water from subsystem 12 are fed into mixing tanks T-1 and T-2 by line 89. Tanks T-1 to T-2, e.g., weighting agent tank 30 with mixer 32 and flocculant mixing tank 36 with mixer 38 introduce and mix the waste water from static mixers 60 with weighting agents and flocculant to form large flocs of the weighting agent and the microflocs of particulate contaminants and/or large flocs of the weighting agent and the precipitated dissolved contaminants and/or large flocs of the weighting agent and any remaining oil particulates and/or large flocs of any other particulates present in the waste processed, similar as discussed above with reference to FIG. 1. Separation subsystem 44′ includes clarifier 70 which removes the large flocs of the weighting agent and the microflocs of particulate contaminants, and/or the large flocs of the weighting agent and precipitated dissolved contaminants and/or large flocs weighting agent and any remaining oil particulates to provide a clear effluent on line 50′, e.g., by rapid settling, as known by those skilled in the art.


In one design, contaminant removal subsystem 20′ includes weighting agent recovery subsystem 46′ for removing fine magnetized weighting agents from the clear effluent on line 50′. In one example, magnetic filter subsystem 72 and/or high shear subsystem 74 and/or magnetic wet drum separator 76 is used to remove and recover the weighting agent from the clear effluent in line 50′. Weighting agent recovery subsystem 70 recovers the weighting agent which is then recycled back to weighting agent mixing tanks, e.g., any of tank T-1 to T-2, by line 78. See, e.g., U.S. Pat. No. 6,099,738 cited supra.


Although, as discussed above with reference to FIGS. 1-4 above, gas floatation and primary oil contaminant removal subsystem 12 is located before contaminant removal subsystem 20, this is not a necessary limitation of this invention. In another embodiment, system 10iv, FIG. 5, where like parts have been given like numbers, for removing dissolved contaminants, particulate contaminants, and oil contaminants from industrial waste water of this invention, may include gas floatation and primary oil contaminants removal subsystem 12 located after contaminant removal subsystem 20″. In this embodiment, contaminant removal subsystem 20″ receives flow of industrial waste water 14 by line 120. Subsystem 20′ includes tanks 100 which receive coagulants 102 by line 103, weighting agents or magnetic ballast 104 by line 105 and a flocculant 106 by line 107. Mixing tanks 100 operate similar to coagulation mixing tank 24 with mixer 24, weighting agent mixing tank 30 with mixer 32, and flocculation mixing tank 36 with mixer 38, as described above with reference to FIG. 1. The output of mixing tanks 100 by line 103 is large flocs of the weighting agent and oil contaminants, large flocs of the weighting agent, and the microflocs of the particulate contaminants, and/or large flocs of the weighting agent and the precipitated dissolved contaminants, and/or large flocs of any other particulates present in the waste water. Clarifier 82 preferably removes the large flocs by rapid sedimentation. Clarifier 82, FIG. 6, may also include skimmer 170, disposed inside clarifier 82, which coalesces the oil contained in the processed waste water, e.g., as shown at 172, and drives the coalesced oil particulates to the surface of the clarifier for removal as shown by arrow 174. Clarifier 82 with skimmer 170 may be utilized in any of the embodiments of system 10 discussed above with reference to FIGS. 1-4. Gas floatation and primary oil contaminant removal subsystem 12′, FIG. 5, of similar design as gas floatation and primary oil contaminant removal subsystem discussed above with reference to FIG. 1, receives the clear effluent output by clarifier on line 123 and introduces gaseous microspheres which combine with any remaining oil droplets in the waste water to form flocs which float to the surface and are removed as recovered oil 18. The final clear effluent is output by line 50″. Sludge 130 output by clarifier 82 by line 132 can the be re-circulated by line 110 to tanks 100 and/or processed by magnetic separator 114 which recycles the weighting agents by line 112 to mixing tanks 100. The final sludge 140 can be sent to filtration pond and incineration when the weighting agent is coal fines, indicated at 144. System 10iv may also be combined with system 10, FIGS. 1-4, such that gas floatation and primary oil contaminant subsystem 12, 12′, is located at before and after contaminant removal subsystem 20, 21′. Such a design is useful for applications requiring more complete removal of oil contaminants.


Although specific features of the invention are shown in some drawings and not in others, this is for convenience only as each feature may be combined with any or all of the other features in accordance with the invention. The words “including”, “comprising”, “having”, and “with” as used herein are to be interpreted broadly and comprehensively and are not limited to any physical interconnection. Moreover, any embodiments disclosed in the subject application are not to be taken as the only possible embodiments. Other embodiments will occur to those skilled in the art and are within the following claims.


In addition, any amendment presented during the prosecution of the patent application for this patent is not a disclaimer of any claim element presented in the application as filed: those skilled in the art cannot reasonably be expected to draft a claim that would literally encompass all possible equivalents, many equivalents will be unforeseeable at the time of the amendment and are beyond a fair interpretation of what is to be surrendered (if anything), the rationale underlying the amendment may bear no more than a tangential relation to many equivalents, and/or there are many other reasons the applicant can not be expected to describe certain insubstantial substitutes for any claim element amended.

Claims
  • 1. A system for removing dissolved contaminants, the contaminants comprising: particulate contaminants, emulsified oil contaminants, and micro-oil droplet contaminants from a refinery waste water, the system comprising: a gas floatation and primary oil contaminant removal subsystem comprising a tank having a processed water outlet, the tank connected to a source of the refinery waste water and a source of positively charged gaseous microspheres, the source of positively charged microspheres positioned to contact the free-oil contaminants in the refinery wastewater to form flocs of oil micro-droplets and gaseous microspheres in the tank;a floc removal subsystem positioned in the tank and having a skimmer positioned to remove the flocs of oil micro-droplets and gaseous microspheres from the tank to produce a processed water effluent; anda contaminant removal subsystem positioned downstream from, and in fluid communication with the processed water outlet of the gas floatation and primary oil contaminant removal subsystem, the contaminant removal subsystem comprising a source of a weighting agent positioned to contact at least the emulsified oil contaminants in the processed water to settle contaminants, the contaminant removal subsystem having an outlet constructed and arranged to provide a clarified water having less than about 5 ppm of at least one of oil contaminants and particulate contaminants without the use of any membranes or filters.
  • 2. The system of claim 1 further comprising a cooling subsystem constructed and arranged to reduce a temperature of the waste water to a temperature for use with a flocculant.
  • 3. The system of claim 1 further comprising a buffer tank constructed and arranged to regulate a flow of the waste water and to remove particulates in the waste water.
  • 4. The system of claim 1 in which the contaminant removal subsystem comprises a coagulation mixing tank constructed and arranged to receive the processed waste water and connected to a source of a coagulant.
  • 5. The system of claim 4 further comprising a weighting agent mixing tank connected to an outlet of the coagulation mixing tank and to the source of the weighting agent.
  • 6. The system of claim 5 further comprising a flocculation subsystem connected to an outlet of the weighting agent mixing tank and to a source of a flocculant.
  • 7. The system of claim 6 further comprising a separation subsystem.
  • 8. The system of claim 4 further comprising an oxidation subsystem connected to a source of an oxidation agent and to the processed waste water.
  • 9. The system of claim 8 in which the oxidation agent comprises hydrogen peroxide.
  • 10. The system of claim 5 in which the weighting agent comprises magnetite.
  • 11. The system of claim 5 in which the weighting agent comprises coal fines.
  • 12. The system of claim 7 in which the separation subsystem comprises a clarifier.
  • 13. The system of claim 7 in which the separation subsystem comprises a settler.
  • 14. The system of claim 7 in which the separation subsystem comprises a hydrocyclone.
  • 15. The system of claim 7 further comprising a weighting agent recovery subsystem having an inlet connected to the separation subsystem.
  • 16. The system of claim 15 in which the weighting agent recovery system comprises a high shear mixer subsystem.
  • 17. The system of claim 15 in which the weighting agent recovery subsystem comprises a high gradient magnetic filter.
  • 18. The system of claim 15 in which the weighting agent recovery subsystem comprises a wet drum magnetic separator.
  • 19. The system of claim 15 further comprising a recycling subsystem having an inlet connected to the weighting agent recovery subsystem and an outlet connected to the weighting agent mixing tank.
  • 20. The system of claim 7 further comprising a re-circulation system having an inlet connected to the separation subsystem.
  • 21. The system of claim 6 in which the flocculation subsystem comprises at least one of a static mixer and a mixing tank.
  • 22. The system of claim 8 in which the oxidation subsystem comprises a static mixer.
  • 23. The system of claim 7 in which the separation subsystem comprises a skimmer disposed inside of a clarifier.
  • 24. A system for removing dissolved contaminants, particulate contaminants, emulsified oil contaminants, and free-oil contaminants from industrial waste water, the system comprising: a gas floatation and primary oil contaminant removal subsystem comprising a tank having a processed water outlet, the tank connected to a source of the industrial waste water and a source of positively charged gaseous microspheres, the source of positively charged microspheres positioned to contact the free-oil contaminants in the refinery wastewater to form flocs of oil micro-droplets and gaseous microspheres in the tank;a floc removal subsystem positioned in the tank and having a skimmer positioned to remove the flocs of oil micro-droplets and gaseous microspheres from the tank to produce a processed water effluent;a cooling subsystem constructed and arranged to reduce the temperature of the waste water to a temperature for use with a flocculent;a buffer tank constructed and arranged to regulate a flow of the waste water and to remove coarse particulates in the waste water;a contaminant removal subsystem positioned downstream from, and in fluid communication with the processed water effluent of the gas floatation and primary oil contaminant removal subsystem, the contaminant removal subsystem comprising a source of a weighting agent positioned to contact at least the emulsified oil contaminants and the remaining free oil contaminants in the processed water to settle contaminants, the contaminant removal subsystem constructed and arranged to provide a clarified water having less than about 5 ppm of at least one of oil contaminants and particulate contaminants without the use of any membranes or filters.
  • 25. A system for removing dissolved contaminants, particulate contaminants, emulsified oil contaminants, and free-oil contaminants from waste water, the system comprising: a gas floatation and primary oil contaminant removal subsystem comprising a tank having a processed water outlet, the tank connected to a source of the industrial waste water and a source of positively charged gaseous microspheres, the source of positively charged microspheres positioned to contact the free-oil contaminants in the refinery wastewater to form flocs of oil micro-droplets and gaseous microspheres in the tank;a floc removal subsystem positioned in the tank and having a skimmer positioned to remove the flocs of oil micro-droplets and gaseous microspheres from the tank to produce a processed water effluent;a cooling tank constructed and arranged to reduce the temperature of the waste water to a temperature for use with a flocculent;a buffer tank constructed and arranged to regulate a flow of the waste water and to remove coarse particulates in the waste water; anda contaminant removal subsystem positioned downstream from, and in fluid communication with the processed water effluent of the gas floatation and primary oil contaminant removal subsystem, the contaminant removal subsystem comprising a source of a weighting agent positioned to contact at least the emulsified oil contaminants and the remaining free oil contaminants in the processed water to settle contaminants, the contaminant removal subsystem constructed and arranged to provide a clarified water, the contaminant removal subsystem comprising: a coagulation mixing tank constructed and arranged to receive the processed waste water and to a source of a coagulant to provide microflocs of the particulate contaminants and to precipitate the dissolved contaminants;a weighting agent mixing tank connected to an outlet of the coagulation mixing tank and to a source of a weighting agent;a flocculation mixing tank connected to the weighting agent mixing tank and to a source of a flocculant; anda separation subsystem to provide a clear effluent having less than about 5 ppm each of at least one of oil contaminants and particulate contaminants without the use of any membranes or filters.
RELATED APPLICATIONS

This application claims priority of and benefit to provisional patent application Ser. No. 60/879,429, filed Jan. 9, 2007, incorporated by reference herein.

US Referenced Citations (368)
Number Name Date Kind
438579 Faunce et al. Oct 1890 A
531183 Harris Dec 1894 A
653010 Koyl Jul 1900 A
728062 Wilson May 1903 A
1064807 Yost Jun 1913 A
1310461 Williams Jul 1919 A
1383287 Campbell Jul 1921 A
1401288 Sodeau Dec 1921 A
1948080 Thomas Feb 1934 A
2065123 Downes Dec 1936 A
2129267 Fischer Sep 1938 A
2232294 Urbain et al. Feb 1941 A
2232296 Urbain et al. Feb 1941 A
2268461 Nichols Dec 1941 A
2326575 Stearns Aug 1943 A
2359748 Clemens Oct 1944 A
2391494 Walker Dec 1945 A
2401924 Goetz Jun 1946 A
2564515 Vogel Aug 1951 A
2597561 Blind May 1952 A
2652925 Vermeiren Sep 1953 A
2713028 Jenks Jul 1955 A
2758715 Fowler Aug 1956 A
2825464 Mack Mar 1958 A
2945590 Stearns Jul 1960 A
3066095 Hronas Nov 1962 A
3080264 Zimmie Mar 1963 A
3142638 Blaisdell et al. Jul 1964 A
3228878 Moody Jan 1966 A
3350302 Demeter et al. Oct 1967 A
3575852 Hughes Apr 1971 A
3617561 Fanselow Nov 1971 A
3622461 Wagner et al. Nov 1971 A
3627678 Marston et al. Dec 1971 A
3676337 Kolm Jul 1972 A
3690454 Bekhtle et al. Sep 1972 A
3693795 Robinson et al. Sep 1972 A
3697420 Blaisdell et al. Oct 1972 A
3767351 Blaser Oct 1973 A
3819589 Fauke et al. Jun 1974 A
3856666 Yashima et al. Dec 1974 A
3886064 Kosonen May 1975 A
3887457 Marston et al. Jun 1975 A
3920543 Marston et al. Nov 1975 A
3929632 Buriks et al. Dec 1975 A
3929635 Buriks et al. Dec 1975 A
3950319 Schmidt et al. Apr 1976 A
3951807 Sanderson Apr 1976 A
3959133 Fulton May 1976 A
3983033 de Latour Sep 1976 A
4024040 Phalangas et al. May 1977 A
4025432 Nolan et al. May 1977 A
4033864 Nolan et al. Jul 1977 A
4046681 Marston et al. Sep 1977 A
4066991 Marston et al. Jan 1978 A
4089779 Neal May 1978 A
4110208 Neal Aug 1978 A
4139456 Yabuuchi et al. Feb 1979 A
4142970 von Hagel et al. Mar 1979 A
4151090 Brigante Apr 1979 A
4153559 Sanderson May 1979 A
4167480 Mach Sep 1979 A
4176042 Fahlstrom Nov 1979 A
4190539 Besik Feb 1980 A
4193866 Slusarczuk et al. Mar 1980 A
4204948 Wechsler et al. May 1980 A
4274968 Grutsch et al. Jun 1981 A
4290898 von Hagel et al. Sep 1981 A
4297484 Quinlan Oct 1981 A
4320012 Palm et al. Mar 1982 A
4339347 Quinlan Jul 1982 A
4341657 Quinlan Jul 1982 A
4343730 Becker et al. Aug 1982 A
4357237 Sanderson Nov 1982 A
4358382 Quinlan Nov 1982 A
4359382 Morgan Nov 1982 A
4377483 Yamashita et al. Mar 1983 A
4388195 von Hagel et al. Jun 1983 A
4402833 Bennett et al. Sep 1983 A
4454047 Becker et al. Jun 1984 A
4465597 Herman et al. Aug 1984 A
4482459 Shiver Nov 1984 A
4502958 Sasaki Mar 1985 A
4522643 Quinlan Jun 1985 A
4563286 Johnson et al. Jan 1986 A
4579655 Louboutin et al. Apr 1986 A
4588508 Allenson et al. May 1986 A
4595506 Kneer Jun 1986 A
4626354 Hoffman et al. Dec 1986 A
4654139 Baba et al. Mar 1987 A
4655933 Johnson et al. Apr 1987 A
4686035 Estabrook Aug 1987 A
4689154 Zimberg Aug 1987 A
4699951 Allenson et al. Oct 1987 A
4735725 Reischl et al. Apr 1988 A
4752401 Bodenstein Jun 1988 A
4765900 Schwoyer et al. Aug 1988 A
4765908 Monick et al. Aug 1988 A
4783265 Timmons Nov 1988 A
4795557 Bourbigot et al. Jan 1989 A
4827890 Pociask et al. May 1989 A
4843105 Reischl et al. Jun 1989 A
4849128 Timmons et al. Jul 1989 A
4851123 Mishra Jul 1989 A
4864075 Thompson et al. Sep 1989 A
4872993 Harrison Oct 1989 A
4874508 Fritz Oct 1989 A
4882064 Dixon et al. Nov 1989 A
4921597 Lurie May 1990 A
4921613 Nordberg et al. May 1990 A
4927543 Bablon et al. May 1990 A
4938876 Ohsol Jul 1990 A
4940550 Watson Jul 1990 A
4944278 Woodard Jul 1990 A
4944279 Woodard Jul 1990 A
4956099 Thompson et al. Sep 1990 A
4981593 Priestley et al. Jan 1991 A
5009791 Lin et al. Apr 1991 A
5013451 Thompson et al. May 1991 A
5019274 Thompson et al. May 1991 A
5023012 Buchan et al. Jun 1991 A
5026483 Thompson et al. Jun 1991 A
5055194 Goetz et al. Oct 1991 A
5064531 Wang et al. Nov 1991 A
5069783 Wang et al. Dec 1991 A
5084733 Katoh et al. Jan 1992 A
5089120 Eberhardt Feb 1992 A
5089227 Thompson et al. Feb 1992 A
5089619 Thompson et al. Feb 1992 A
5112494 Yan May 1992 A
5112499 Murray et al. May 1992 A
5149438 Hebert Sep 1992 A
5187326 Shirai Feb 1993 A
5234603 Potts Aug 1993 A
5266200 Reid Nov 1993 A
5298168 Guess Mar 1994 A
5310642 Vargas et al. May 1994 A
5369072 Benjamin et al. Nov 1994 A
5377845 Hamen et al. Jan 1995 A
5383539 Bair et al. Jan 1995 A
5395527 Desjardins Mar 1995 A
5397476 Bradbury et al. Mar 1995 A
5462670 Guess Oct 1995 A
5545330 Ehrlich Aug 1996 A
5560493 Perry Oct 1996 A
5593590 Steyskal Jan 1997 A
5595666 Kochen et al. Jan 1997 A
5596392 Danzuka Jan 1997 A
5597479 Johnson Jan 1997 A
5616241 Khudenko Apr 1997 A
5616250 Johnson et al. Apr 1997 A
5637221 Coyne Jun 1997 A
5693461 Bagchi et al. Dec 1997 A
5702809 Tixier et al. Dec 1997 A
5730864 Delsalle et al. Mar 1998 A
5731134 Honan et al. Mar 1998 A
5770091 Binot et al. Jun 1998 A
5779908 Anderson et al. Jul 1998 A
5800717 Ramsay et al. Sep 1998 A
5805965 Tsuda et al. Sep 1998 A
5840185 Hughes et al. Nov 1998 A
5840195 Delsalle et al. Nov 1998 A
5856072 Leone et al. Jan 1999 A
5893355 Glover et al. Apr 1999 A
5925290 Hills Jul 1999 A
5976375 Dorica et al. Nov 1999 A
5976771 Kosugi et al. Nov 1999 A
6010631 Delsalle et al. Jan 2000 A
6030761 Taguchi et al. Feb 2000 A
6093318 Saho et al. Jul 2000 A
6099738 Wechsler et al. Aug 2000 A
6149014 Mankosa et al. Nov 2000 A
6151467 Yamaguchi Nov 2000 A
6160976 Karakama et al. Dec 2000 A
6185393 Karakama et al. Feb 2001 B1
6210587 Vion Apr 2001 B1
6210588 Vion Apr 2001 B1
6221253 Fukase et al. Apr 2001 B1
6221262 MacDonald et al. Apr 2001 B1
6228269 Cort May 2001 B1
6228565 Ohzeki et al. May 2001 B1
6251576 Taguchi et al. Jun 2001 B1
6277285 Vion Aug 2001 B1
6290849 Rykaer et al. Sep 2001 B1
6379549 LePoder et al. Apr 2002 B1
6383370 Keever et al. May 2002 B1
6386781 Gueret May 2002 B1
6406624 DeVos Jun 2002 B1
6423485 Yamada et al. Jul 2002 B1
6432303 Chesner et al. Aug 2002 B1
6447686 Choi et al. Sep 2002 B1
6472132 Yamada et al. Oct 2002 B1
6485652 Le Poder et al. Nov 2002 B1
6517714 Streat Feb 2003 B2
6613232 Chesner et al. Sep 2003 B2
6645386 Moreau et al. Nov 2003 B1
6689277 Streat Feb 2004 B2
6692173 Gueret Feb 2004 B2
6706467 Howe et al. Mar 2004 B2
6740245 Johnson May 2004 B2
6759018 Arno et al. Jul 2004 B1
6783679 Rozich Aug 2004 B1
6811885 Andriessen et al. Nov 2004 B1
6824692 Binot et al. Nov 2004 B2
6832691 Miles et al. Dec 2004 B2
6875351 Arnaud Apr 2005 B2
6896815 Cort May 2005 B2
6902678 Tipton Jun 2005 B2
6919031 Blumenschein et al. Jul 2005 B2
6923901 Leffler et al. Aug 2005 B2
6960294 Arnaud Nov 2005 B2
6966993 Binot Nov 2005 B2
6968138 Akutsu Nov 2005 B2
7001525 Binot et al. Feb 2006 B2
7083715 Binot Aug 2006 B2
7153431 Daugherty Dec 2006 B2
7160448 Johnson Jan 2007 B2
7210581 Robinson et al. May 2007 B2
7244362 Binot Jul 2007 B2
7255793 Cort Aug 2007 B2
7276165 Morgoun Oct 2007 B2
7309435 Rozich Dec 2007 B2
7311841 Binot et al. Dec 2007 B2
7323108 Garbett et al. Jan 2008 B1
7407582 Sun Aug 2008 B2
7407593 Frederick, Jr. et al. Aug 2008 B2
7438817 Nagghappan et al. Oct 2008 B2
7449105 Hastings Nov 2008 B2
7476324 Ciampi et al. Jan 2009 B2
7494592 Deskins Feb 2009 B2
7563366 Sun Jul 2009 B2
7601261 Palacios Donaque Oct 2009 B2
7608190 Banerjee et al. Oct 2009 B1
7625490 Cort Dec 2009 B2
7648637 Sauvignet et al. Jan 2010 B1
7648638 Essemiani et al. Jan 2010 B2
7651620 Vion Jan 2010 B2
7678278 Binot et al. Mar 2010 B2
7686079 Gamache et al. Mar 2010 B2
7686960 Cort Mar 2010 B2
7691261 Deskins Apr 2010 B2
7691269 Cort Apr 2010 B2
7695623 Woodard et al. Apr 2010 B2
7695630 de Guevara Apr 2010 B2
7704390 Leffler et al. Apr 2010 B2
7704399 Condit Apr 2010 B2
7722843 Srinivasachar May 2010 B1
7729778 Eggers et al. Jun 2010 B2
7820025 Ciampi et al. Oct 2010 B2
7820053 Cort Oct 2010 B2
7820054 Hastings et al. Oct 2010 B2
7828976 Banerjee et al. Nov 2010 B2
8012582 Luo et al. Sep 2011 B2
8470172 Woodard et al. Jun 2013 B2
8506800 Woodard et al. Aug 2013 B2
8540877 Woodard Sep 2013 B2
20010030160 Wechsler et al. Oct 2001 A1
20020003115 Conaway et al. Jan 2002 A1
20020017483 Chesner et al. Feb 2002 A1
20020030019 Keever et al. Mar 2002 A1
20020054783 Gueret May 2002 A1
20020088758 Blumenschein et al. Jul 2002 A1
20020148780 Tiemeyer Oct 2002 A1
20020158025 Streat Oct 2002 A1
20020170816 Leffler et al. Nov 2002 A1
20020185452 Johnson Dec 2002 A1
20020190004 Wechsler et al. Dec 2002 A1
20030082084 Cort May 2003 A1
20030089667 Binot et al. May 2003 A1
20030132160 Khudenko Jul 2003 A1
20030150817 Keever et al. Aug 2003 A1
20030222027 Streat Dec 2003 A1
20030224301 Howe et al. Dec 2003 A1
20040055959 Wechsler et al. Mar 2004 A1
20040055961 Binot Mar 2004 A1
20040060876 Tipton Apr 2004 A1
20040129642 Binot Jul 2004 A1
20040144730 Binot et al. Jul 2004 A1
20040149653 Johnson et al. Aug 2004 A1
20040206680 Johnson Oct 2004 A1
20040213721 Arno et al. Oct 2004 A1
20050005471 Pan Jan 2005 A1
20050035030 Oder et al. Feb 2005 A1
20050045534 Kin et al. Mar 2005 A1
20050051488 Nagghappan et al. Mar 2005 A1
20050101719 Ishihara May 2005 A1
20050103719 Binot et al. May 2005 A1
20050131266 Carman et al. Jun 2005 A1
20050173354 Binot et al. Aug 2005 A1
20050194311 Rozich Sep 2005 A1
20050218056 Binot Oct 2005 A1
20050230299 Saho et al. Oct 2005 A1
20050258103 Cort Nov 2005 A1
20050271575 Ciampi et al. Dec 2005 A1
20050277712 Daly Dec 2005 A1
20050282144 Wechsler et al. Dec 2005 A1
20060006114 Deskins Jan 2006 A1
20060018273 Yamada et al. Jan 2006 A1
20060108273 Perri et al. May 2006 A1
20060108283 Johnson et al. May 2006 A1
20060138047 Morgoun Jun 2006 A1
20060175252 Upendrakumar et al. Aug 2006 A1
20060186056 Ivan Aug 2006 A1
20060213832 Hudson et al. Sep 2006 A1
20060254770 Hou Nov 2006 A1
20060270888 Carman et al. Nov 2006 A1
20060289357 Wechsler et al. Dec 2006 A1
20070039894 Cort Feb 2007 A1
20070062883 Frederick et al. Mar 2007 A1
20070108132 de Guevara May 2007 A1
20070114184 Essemiani et al. May 2007 A1
20070119776 Isaka et al. May 2007 A1
20070138093 Bossler et al. Jun 2007 A1
20070163955 Sun Jul 2007 A1
20080019780 Hastings Jan 2008 A1
20080073267 Cort Mar 2008 A1
20080073268 Cort Mar 2008 A1
20080073270 Smith Mar 2008 A1
20080073271 Cort Mar 2008 A1
20080073278 Cort Mar 2008 A1
20080073279 Cort Mar 2008 A1
20080073280 Cort Mar 2008 A1
20080073281 Cort Mar 2008 A1
20080073282 Cort Mar 2008 A1
20080073283 Cort Mar 2008 A1
20080073284 Cort Mar 2008 A1
20080078721 Binot et al. Apr 2008 A1
20080135491 Cort Jun 2008 A1
20080156709 Johnson Jul 2008 A1
20080164183 Marston et al. Jul 2008 A1
20080164184 Marston et al. Jul 2008 A1
20080203015 Marston et al. Aug 2008 A1
20080217244 Gaid Sep 2008 A1
20080257810 Sun Oct 2008 A1
20080272065 Johnson Nov 2008 A1
20080290030 Nagghappan et al. Nov 2008 A1
20080296228 Sauvignet et al. Dec 2008 A1
20080314820 Prulhiere et al. Dec 2008 A1
20080314830 Banerjee et al. Dec 2008 A1
20090047076 Hastings Feb 2009 A1
20090050570 Sauvignet Feb 2009 A1
20090065404 Paspek, Jr. et al. Mar 2009 A1
20090084730 Mabille et al. Apr 2009 A1
20090098262 Mabille et al. Apr 2009 A1
20090127180 Deskins May 2009 A1
20090178979 Hastings et al. Jul 2009 A1
20090206040 Berg et al. Aug 2009 A1
20090218281 Sauvignet et al. Sep 2009 A1
20090261037 Clifford, III et al. Oct 2009 A1
20090272693 Mabille et al. Nov 2009 A1
20090299143 Conlon et al. Dec 2009 A1
20090301948 Essemiani et al. Dec 2009 A1
20090308815 Sauvignet et al. Dec 2009 A1
20100038081 Gamache et al. Feb 2010 A1
20100057085 Holcomb et al. Mar 2010 A1
20100072142 Lean et al. Mar 2010 A1
20100096335 Sauvignet et al. Apr 2010 A1
20100101309 Klyamkin et al. Apr 2010 A1
20100102006 Quevillon Apr 2010 A1
20100155327 Woodard et al. Jun 2010 A1
20100213123 Marston et al. Aug 2010 A1
20100219372 Hook et al. Sep 2010 A1
20100251571 Woodard Oct 2010 A1
20100274209 Roe et al. Oct 2010 A1
20110036771 Woodard Feb 2011 A1
20110147304 Sauvignet et al. Jun 2011 A1
20120067824 Berg et al. Mar 2012 A1
20130020255 Woodard Jan 2013 A1
Foreign Referenced Citations (51)
Number Date Country
1686862 Oct 2005 CN
101186410 May 2008 CN
101244884 Aug 2008 CN
19600647 Jul 1997 DE
12594 Jun 1980 EP
0087223 Aug 1983 EP
0139572 May 1985 EP
266098 May 1988 EP
392321 Oct 1990 EP
392322 Oct 1990 EP
1244601 Oct 2002 EP
1785400 May 2007 EP
2165980 Mar 2010 EP
1411792 Sep 1965 FR
2378550 Aug 1978 FR
2719235 Nov 1995 FR
07-299495 Nov 1995 JP
08-257583 Oct 1996 JP
11-169866 Jun 1999 JP
2000-233198 Aug 2000 JP
2001-170404 Jun 2001 JP
2003-010874 Jan 2003 JP
1136839 Jan 1985 SU
9312041 Jun 1993 WO
9735654 Oct 1997 WO
9735655 Oct 1997 WO
9803433 Jan 1998 WO
9919261 Apr 1999 WO
9931016 Jun 1999 WO
0114260 Mar 2001 WO
0128931 Apr 2001 WO
0140121 Jun 2001 WO
0200556 Jan 2002 WO
0242223 May 2002 WO
2005077835 Aug 2005 WO
2005087381 Sep 2005 WO
2006086384 Aug 2006 WO
2006102362 Sep 2006 WO
2007059141 May 2007 WO
2007098298 Aug 2007 WO
2008022192 Feb 2008 WO
2008039711 Apr 2008 WO
2008039936 Apr 2008 WO
2008085196 Jul 2008 WO
2008085197 Jul 2008 WO
2008086009 Jul 2008 WO
2008086010 Jul 2008 WO
2009083346 Jul 2009 WO
2010027895 Mar 2010 WO
2010081903 Jul 2010 WO
2010086249 Aug 2010 WO
Non-Patent Literature Citations (14)
Entry
Buchanan et al., “Aerobic Treatment of Wastewater and Aerobic Treatment Units,” University Curriculum Development for Decentralized Wastewater Management Aerobic Treatment of Wastewater and Aerobic Treatment Units Buchanan and Seabloom, p. i-v and 1-22, Nov. 2004, [Retrieved on Mar. 9, 2011].
Catlow et al. “Ballasted Biological Treatment Process Removes Nutrients and Doubles Plant Capacity”. WEFTEC Conference. Date Unkown.
Kolm et al., “High Gradient Magnetic Separation,” Scientific American, Nov. 1975, vol. 233, No. 5, 10 pages (unnumbered).
Lubenow et al. “Maximizing Nutrient Removal in an Existing SBR with a Full-Scale BioMag Demonstration”. WEFTEC Conference. Date Unknown.
Moody et al. “Beyond Desktop Evaluation: Key Design Criteria for Mixing and Settling of Magnetite-Impregnated Mixed Liquor”. WEFTEC Conference 2011.
Raskin et al., “Quantification of Methanogenic Groups in Anaerobic Biological Reactors by Oligonucleotide Probe Hybridization,” Applied and Environmental Microbiology, Apr. 1994, vol. 60, No. 4, pp. 1241-1248.
Sakai et al., “A Sewage Treatment Process Using Highly Condensed Activated Sludge with an Apparatus for Magnetic Separation,” 1994, Journal of Fermentation and Bioengineering, vol. 78, No. 1, pp. 120-122.
Sakai et al., “Magnetic Forced Sedimentation of Flocs in Activated Sludge Supplemented with Ferromagnetic Powder of Iron Oxide,” 1991, Journal of Fermentation and Bioengineering, vol. 71, No. 3, pp. 208-210.
Sakai et al., “Recovery and Reuse of Ferromagnetic Powder Supplemented in Activated Sludge for Magnetic Separation,” Dept. of Applied Chemistry, Faculty of Engineering, Utsunomiya University, Japan, Submitted: Jun. 28, 1991; Accepted: Oct. 22, 1991, pp. 1-11. Japanese language original (pp. 52-56), and translated English language copy (pp. 1-11).
Sakai et al., “Sewage Treatment under Conditions of Balancing Microbial Growth and Cell Decay with a High Concentration of Activated Sludge Supplemented with Ferromagnetic Powder,” 1992, Journal of Fermentation and Bioengineering, vol. 74, No. 6, pp. 413-315.
Sakai et al., “Simultaneous Removal of Organic and Nitrogen Compounds in Intermittently Aerated Activated Sludge Process Using Magnetic Separation,” 1997, Technical Note Wat. Res., vol. 31, No. 8, pp. 2113-2116.
http://www.envirosim.com/includes/weftec08.htm, downloaded Dec. 16, 2012.
Tozer, “Study of Five Phosphorus Removal Processes,” The Georgia Operator, vol. 45, No. (Winter 2008).
www.ingentaconnect.com/content/wef/wefproc/2009/00002009/00000004/art0020, downloaded Dec. 16, 2012.
Related Publications (1)
Number Date Country
20080210613 A1 Sep 2008 US
Provisional Applications (1)
Number Date Country
60879429 Jan 2007 US