The field of the present disclosure is directed to wash fluid containment and fluid treatment systems such as used for treating and recycling fluids.
In certain environments there is a need to wash vehicles, trailers and various equipment. It is desirable to contain the wastewater fluids from washing activities and treat these fluids for recycling and reuse.
The present inventors have recognized various limitations in the prior systems and the desirability for an improved system.
Additional aspects and advantages will be apparent from the following detailed description of preferred embodiments, which proceeds with reference to the accompanying drawings.
Preferred embodiments will now be described with reference to the drawings. To facilitate description, any element numeral representing an element in one figure will represent the same element in any other figure.
The water treatment system 50 includes an enclosure or cabinet 52 that houses/encloses the various system components. The cabinet 52 is drawn generally to scale to itself but at a slightly enlarged scale relative to the wash pad. The size dimensions for the cabinet 52 are illustrated in
Further details of the wash pad 40 are described in U.S. patent application Ser. No. 12/032,562 filed Feb. 15, 2008 hereby incorporated by reference. In a preferred configuration, the trench 44 is reversible. Depending on the orientation of the trench 44, wastewater may be drained either forwardly or rearwardly for connection to the sump hose 38.
The wash pad assembly 40 may also include an integrated pressure washer system comprised of a hose reel and housing assembly 46 and pressure washer assembly 48. The pressure washer assembly 48 includes a trigger valve mechanism, a wand and nozzle attached to a water source by a hose 48a. The hose 48a is wound onto a hose reel that is disposed within the hose reel housing 46. The hose reel housing 46 may be located either on the right side of the wash pad (as shown in
A grating 44a is installed over the trench 44 between the left and right wash pad sections 42. The grating 44a has perforations for allowing the water flowing downward from the wash pad sections 42 to pass therethrough and into the trench 44. The perforations are preferably of a desired size large enough to allow for passage of the water into trench 44, but small enough to prevent passage of larger size debris. Such debris may then be removed from the pad by sweeping or other manual collection. Under the grating 44a, the trench 44 includes two weirs and a screen (not shown) disposed near the exit end of the trench 44 such that water must pass over the weirs and through the screen whereby some debris and heavy solids are inhibited from reaching the exit pipe 38.
The wastewater from the trench 44 then passes via pipe 38 to the sump 30. The sump 30 comprises a sludge separator 32 and a holding tank 33 including a weir (not shown). The wastewater from pipe 38 must pass over the weir in the holding tank 33, the weir capturing certain debris and heavy solids, and the wastewater thereafter is transferred to the treatment system 50 via hose 22. Recycled/treated water from the treatment system 50 is returned to the wash pad area for use by the pressure washer assembly 48. Sludge waste from the treatment system 50 is purged into the sludge separator 32 via hose 24 through fitting 24a. The sludge separator 32 includes an outer tank 32a with a top lid 32b. Inside the tank 32a is a bucket-shaped filter screen 32c that filters/separates the sludge waste and other particulates from the water, the water passing through the filter and into the holding tank 33. A fabric filter 32d is disposed in the filter screen 32c to provide enhanced particle removal. The sludge waste (which may be referred to as solids) may be manually removed from both the holding tank 33 and the filter screen 32c. The fabric filter 32d is typically a disposable element.
Thus even before reaching the water treatment system 50, the wastewater has undergone three processes for removing debris and solids namely: (a) grating 44a, (b) the trench 44 (via the weirs and screen) and (c) the sump 30.
Details of the water treatment process will now be described with particular reference the perspective view of the water treatment system of
After passing through the electrolytic cell 114, the wastewater enters a mixer 118 which is preferably one or more in-line static mixers. A suitable static mixer is the series 50 mixer available for TAH Industries Inc., Robbinsville N.J. A second metering pump 132 injects a polymer solution from vessel 130 via injector 134 into the water line between the electrolytic cell 114 and the static mixer 118. In its preferred form, the polymer solution is an organic long-chain high molecular weight emulsion flocculent designed to enhance conglomeration, i.e., enlarge the impurity particles to facilitate removal of particles later in the process. One preferred polymer is the NALCLEAR 7763 polymer flocculent available from Nalco Chemical Products of Naperville, Ill. The actual polymer solution selected will depend upon various factors including the input flow and the expected system impurities being treated by the water treatment system. After passing through the in-line mixer 118, the wastewater is passed through retention tubes 120, 122. This portion of the treatment system is a continuous flow system and the retention tubes 120, 122 are intended to provide sufficient residency and development time (reaction time) for the electro-coagulation and polymer flocculation to operate on the wastewater.
Upon leaving the retention tube 122, the wastewater proceeds via piping 61 into the water tank having three water compartments 60, 70, 80 arranged in a side-by-side, consecutive arrangement disposed within the cabinet 52. Pipe 61 enters the first water compartment 60 and is directed into a swirling cone mixer 62, the cone mixer 62 is a cone-shaped sub-compartment preferable disposed in the first water compartment 60 (for space efficiency reasons but could be located elsewhere). Wastewater entering via the pipe 61 is directed in a centrifugal motion around the cone mixer 62 (due to the cone shape and the tangential inlet direction of the inlet stream from the pipe 61) to create a swirling motion for the water flow. Some of the flocculated material is heavier than the remaining water and passes downward out through the bottom opening of the cone 62 and to the bottom of the first stage water compartment 60. Flocculation material and certain oils that are lighter than the remaining wastewater float to the surface of the first water compartment 60, is removed via oil skimmer or funnel 64, and purged out via piping 66 for recirculation to the sludge separator 32. As shown in
Wastewater from the first water compartment 60 passes through an opening 68 in tank divider 60a and then passes laterally through pipe 72 into the second water compartment 70. The opening 78 is at a mid-level position within the tanks. Heavy particles pass to the bottom of the tank 60 and are purged out through opening 69 into purge pipe 24, while lighter particles floating to the top of the tank are purged out through funnel 64 and purge pipe 66. It is intended that the wastewater at the mid-level of the tank 60 passing through the opening 78 would have the fewest particles. The pipe 72 provides a tortuous path for the “cleaned” wastewater (cleaned wastewater meaning somewhat cleaner wastewater due to the removal of certain particulates, etc. in the first water compartment 60) exiting the first water compartment 60 and entering the second water compartment 70 for further enhancing particle removal. Once in the second water compartment 70, the wastewater is provided with a relatively long residency time to allow for heavier particles and flocculation to settle down into the bottom of the compartment and be purged out of opening 79 into the recycle line 24. Exit pipe 74 is also positioned at mid-level within the tank compartment 70 and has an opening at an opposite side of the tank 70 from the inlet of the pipe 72. Thus the “cleaned” wastewater enters the tank 70 at one lateral side but must exit at the other lateral side. Similar to pipe 72, the pipe 74 provides a tortuous path for the water to pass from compartment 70 out through opening 78 and into the third tank compartment 80. Any heavy particles or heavy flocculation is purged out through the bottom opening 89 into recycle line 24. The flow of sludge water through recycle line 24 is controlled by a control valve 88 and passed to the holding tank 32 and the sludge separator 30. One-way check valves are provided below opening 79 and 89 to prevent backflow of sludge water into the tank 70, 80.
The cleaned wastewater within the third water compartment 80 is recirculated out from the tank via line 92 by pump 152 and through an ozone generator 156, thereby neutralizing bacteria within the water. The ozone pump 152 is controlled via manual switch 154 as permitted by level switch 159 on the tank compartment 80.
At the conclusion of these steps, the water within the tank compartment 80 is recyclable clean water and is pumped out by pump 90 via line 91 for reuse by pressure washer 48.
Since there is some water loss within the system, a fresh water line 158 is controlled by control valve 158a and level switch 157 allows additional water to be injected into the tank compartment 80.
A space heater 170, preferably controlled by a thermostat, is provided within the cabinet structure to provide a desired internal temperature in cold weather climates.
The treatment system 50 is provided with a control panel 165 located behind the doors 53a, 53b. Control panel 165 includes various controllers and gauges for the system, including the sump pump switch 146, the ozone system switch 154, the tank purge switch 167, and the electrolytic cell check light 169. When the sump pump 112 is running, the amperage gauge 172 will normally have an expected reading. For example, the operator may make the necessary adjustments on the amperage potentiometer 113 to provide a desired amperage reading on the gauge 172 corresponding to the electrolytic cell 114. The control panel 165 also includes a cell voltage gauge 174 to visually monitor cell condition, a cell check light 169 to visually identify cell depletion, a voltage light 178 to show that electrical is connected, and a run-time meter 176 to indicate hours of run time for electric cell. The pressure washer is preferably provided with a time-delay shutdown mechanism that turns off the pressure washer if too much time has elapsed since the trigger gun was activated, such as when the operator walks away without turning it off.
An example operation at first use by the following steps may comprise the steps of:
Adding a five-gallon container 130 with the polymer solution, inserting pump tubing into the container and setting a control dial on the pump 132 to a desired position;
Mixing the desired conductivity fluid solution within the tank 140, inserting pump tubing into the tank 140 and setting the controller on the pump 142 to the desired position;
Connecting electrical power to the control panel 165;
Connecting fresh water supply 100 to connection 102 wherein control valve 158a will cause compartments 80, 70, and 60 to automatically fill to proper levels;
Priming the sump pump 112 as needed by connecting freshwater 100 to connection 102a;
Turning on the various systems from the control panel 165, including the sump pump switch 146, the ozone system switch 154, the conductivity solution pump 142 and the polymer pump 132.
Though the present invention has been set forth in the form of its preferred embodiments, it is nevertheless intended that modifications to the disclosed systems and methods may be made without departing from inventive concepts set forth herein.
This application claims priority to provisional application No. 60/906,664 filed Mar. 12, 2007 hereby incorporated by reference.
Number | Name | Date | Kind |
---|---|---|---|
1602105 | Geer et al. | Oct 1926 | A |
2765997 | Motts | Oct 1956 | A |
3064486 | Aplin | Nov 1962 | A |
3652044 | Manross | Mar 1972 | A |
3831849 | Studinger | Aug 1974 | A |
3834657 | Freitas, Jr. | Sep 1974 | A |
3858761 | O'Dell | Jan 1975 | A |
3908941 | Bromley et al. | Sep 1975 | A |
3923658 | Lancaster | Dec 1975 | A |
4120210 | Sloyan | Oct 1978 | A |
4246982 | Pretnick | Jan 1981 | A |
4306967 | Trautwein | Dec 1981 | A |
D263037 | Brown | Feb 1982 | S |
4355834 | Alford | Oct 1982 | A |
4367145 | Simpson et al. | Jan 1983 | A |
4431548 | Lipowski et al. | Feb 1984 | A |
D276902 | Plugge | Dec 1984 | S |
4561624 | Freeman | Dec 1985 | A |
4652368 | Ennis et al. | Mar 1987 | A |
4792274 | Cockram | Dec 1988 | A |
5031602 | Vick | Jul 1991 | A |
D329996 | Ciszewski | Oct 1992 | S |
5286302 | Wickham, III | Feb 1994 | A |
5413128 | Butts | May 1995 | A |
5445730 | Pattee | Aug 1995 | A |
5498329 | Lamminen et al. | Mar 1996 | A |
5601659 | Rohrbacher | Feb 1997 | A |
5611487 | Hood | Mar 1997 | A |
5695121 | Stillions, Jr. et al. | Dec 1997 | A |
5746904 | Lee | May 1998 | A |
5833295 | Farlow, Jr. | Nov 1998 | A |
5908550 | Kaipainen | Jun 1999 | A |
5958240 | Hoel | Sep 1999 | A |
5975480 | Schaefer et al. | Nov 1999 | A |
6021792 | Petter et al. | Feb 2000 | A |
6042702 | Kolouch et al. | Mar 2000 | A |
6106712 | New | Aug 2000 | A |
6132509 | Kuschnereit | Oct 2000 | A |
6132599 | Chaffee | Oct 2000 | A |
6234408 | Stevens et al. | May 2001 | B1 |
6234409 | Aslakson | May 2001 | B1 |
6301848 | Whitaker | Oct 2001 | B1 |
6346197 | Stephenson et al. | Feb 2002 | B1 |
6349715 | McBroom | Feb 2002 | B1 |
6416101 | Bartch | Jul 2002 | B1 |
6495048 | Stephenson et al. | Dec 2002 | B2 |
6550692 | Schacht | Apr 2003 | B1 |
6575858 | Green et al. | Jun 2003 | B2 |
6641721 | Mullerheim | Nov 2003 | B2 |
6655396 | Krenzel | Dec 2003 | B2 |
6663783 | Stephenson et al. | Dec 2003 | B2 |
6715517 | Tobin | Apr 2004 | B2 |
6766822 | Walker | Jul 2004 | B2 |
6790349 | Sawyer | Sep 2004 | B1 |
6799591 | McCormick et al. | Oct 2004 | B2 |
6932412 | Paproski | Aug 2005 | B1 |
D510545 | Riegel et al. | Oct 2005 | S |
6964820 | Shimonosono et al. | Nov 2005 | B2 |
7066096 | Harker et al. | Jun 2006 | B1 |
7118633 | Jenkins | Oct 2006 | B2 |
7121288 | Jenkins | Oct 2006 | B2 |
7203979 | O'Brien | Apr 2007 | B2 |
7258749 | McCormick et al. | Aug 2007 | B2 |
D555303 | Taylor et al. | Nov 2007 | S |
D566624 | Dempsey et al. | Apr 2008 | S |
D572212 | Taylor et al. | Jul 2008 | S |
7431835 | Lack | Oct 2008 | B2 |
7530362 | McCormick et al. | May 2009 | B2 |
7775221 | Zeile | Aug 2010 | B2 |
20040099599 | Van Vliet et al. | May 2004 | A1 |
20060118149 | Benson et al. | Jun 2006 | A1 |
20060273622 | Laird | Dec 2006 | A1 |
20070056510 | Antaya | Mar 2007 | A1 |
20080000507 | Snyder et al. | Jan 2008 | A1 |
20090062046 | Lindemann | Mar 2009 | A1 |
Number | Date | Country |
---|---|---|
2298122 | Jul 2001 | CA |
Number | Date | Country | |
---|---|---|---|
20090065442 A1 | Mar 2009 | US |
Number | Date | Country | |
---|---|---|---|
60906664 | Mar 2007 | US |