Patent Number: 061370282
Section: description

DETAILED DESCRIPTION A method for the disposal of oil field wastes contaminated with naturally occurring radioactive materials in accordance with the present invention is illustrated in the accompanying drawing FIGURE. The method includes the drilling of an injection well 10 and a recovery well 12 so that they intersect within a subterranean salt formation 14. Next, fresh water from storage tank 16 is flowed between the wells 10 and 12 to dissolve a cavern 18 in the salt formation 14. A slurry 22 of NORM wastes 20 and a liquid carrier (fresh water from tank 16 or salt water from storage tank 24) is then pumped down injection well 10 and into the cavern 18. As the slurry 22 is injected, the cavern 18 acts as an liquids/solids separator. The relatively dense NORM wastes 20 sink and accumulate on the bottom of the cavern 18. Salt water 26 displaced by the incoming slurry 22 is removed from the cavern 18 through the recovery well 12 and is subsequently discarded in a disposal well 28 open to a permeable subterranean formation 30 isolated from the salt 14. As the cavern 18 fills with NORM wastes 20, the recovered water 26 tends to become "dirtier" with a higher concentration of wastes. The cavern 18 may be considered to be "full" of NORM wastes 20 when the return of wastes with the displaced salt water 26 becomes problematic. The cavern 18 is sealed when full. It is essential that the injection well 10 and recovery well 12 be drilled in a manner that permits fluid communication between them. This is accomplished by drilling the injection well 10 so that it has a horizontal section 32 in the salt 14 and a vertical section 34 connecting the horizontal section 32 to the ground surface 36. Next, from a place on the surface 36 above the bottom hole location 38 of the injection well 10, the recovery well 12 is drilled vertically to intersect the horizontal section 32. During drilling, the injection well 10 and the recovery well 12 are reinforced to prevent collapse. For both wells 10 and 12, a relatively-short conductor pipe 40 is provided adjacent the ground surface 36. An intermediate string of casing 42, long enough to isolate the wells 10 and 12 from fresh water aquifer 44, is positioned within each conductor pipe 40 and is cemented in place. Finally, a work string of casing 46, having a length sufficient to penetrate the salt 14, is positioned within each intermediate string 42 and is cemented in place to further protect aquifer 44. The injection well 10 and the recovery well 12 are both provided with a tubing string 48 extending from the ground surface 36 to the salt 14. A packer 50 on each tubing string 48 isolates the annulus 52 of each well 10 and 12 from the salt 14. To provide back-pressure on each packer 50, the annulus of each well 10 and 12 is filled with a liquid such as fresh water (not shown). After the injection well 10 and the recovery well 12 are completed, a predetermined volume of fresh water from tank 16 is pumped down the tubing string 48 of the injection well 10, through the salt 14, and up the tubing string 48 of the recovery well 12. If the flow rate is too high, the water obtained at the ground surface 36 from the recovery well 12 will be unsaturated with salt and may be returned to injection well 10 for reuse. Once the fresh water becomes saturated with salt, it is discarded by injection into disposal well 28. After pumping the first volume of fresh water through the salt 14, the roles of the injection well 10 and recovery well 12 are reversed by appropriate switching of valves 54. Now, a second volume of fresh water equal to the first is pumped down the tubing string 48 of recovery well 12, through the salt 14, and up the tubing string 48 of injection well 10. The pumping of water into the recovery well 12 continues until salt-saturated water is recovered from the injection well 10. When such a recovery is made, the nominal diameter of the horizontal section 32 of the injection well 10 optimally will have increased from several inches to many feet thereby forming a salt cavern 18 of large capacity. NORM slurry 22, comprising fresh water from tank 16 and NORM wastes 20, is pumped along the flow path indicated by arrows "A" in the drawing. First, the slurry 22 travels down the tubing string 48 of injection well 10 into the cavern 18. Due to density differences, the NORM wastes 20 settle out of suspension in the cavern 18 between the injection well 10 and the recovery well 12. By controlling slurry flow rates and slurry rheology, an operator can vary the distance from the injection well 10 that NORM wastes 20 will settle thus ensuring that the cavern 18 will be filled with NORM wastes to the maximum possible extent. The fresh water used to form the NORM slurry 22 continues to dissolve salt 14 and transport such from the recovery well 12. The recovered salt water 26 is retained in storage tank 45. When there is a sufficient volume of water 26 in tank 45, a pump 55 whose outlet is in fluid communication with the disposal well 28 is energized to deliver the water 26 to permeable formation 30. Thus, the cavern 18 is automatically enlarged as the deposition of NORM wastes 20 therein continues. The periodic reversal of the roles of the injection well 10 and the recovery well 12 ensures both the even dissolution of the salt 14 and the even deposition of NORM wastes 20 in the cavern 18. Upon reversal to the fluid flow path indicated by arrows "B" in the drawing, NORM slurry 22 is pumped down the tubing string 48 of recovery well 12 into the cavern 18 where the NORM wastes 20 will settle to the bottom of the cavern. Fresh water used to form the NORM slurry dissolves the salt 14, is removed from the cavern 18 through tubing string 48 of injection well 10, and is discarded through the disposal well 28. Once it is determined through volumetric calculations or otherwise that the cavern 18 has reached its maximum safe dimensions. The NORM wastes 20 are slurried with salt-saturated water from tank 24 rather than fresh water from tank 16. Thus, dissolution of the salt 14 is terminated, and the cavern 18 can continue to be filled with NORM wastes 20 as described above until NORM waste returns become problematic. When the return of NORM wastes from the cavern 18 becomes excessive, the injection well 10 and the recovery well 12 are plugged and abandoned. NORM wastes 20 are initially delivered to the slurry production apparatus 56 by means of trucks (not shown) driven onto off-load ramp 58. NORM wastes in excess of 1" nominal diameter are deposited from the trucks into an aggregate pit 60 where they are transported by a conveyor belt 62 to a cone crusher 64. The crusher 64 reduces the nominal diameter of the wastes 20 delivered to it to less than 1" and subsequently delivers them by means of a bucket-lift conveyor 66 to a feed stock tank 68. NORM wastes 20 having a nominal diameter of less than 1" at the time of off-loading, however, are diverted from the crusher 64 and, instead, deposited in a mixing pit 70 where they are combined with fresh water from the storage tank 16 and fed to the feed stock tank 68. NORM wastes 20 are transported from the feed stock tank 68 by a drag-bottom conveyor 72 to a ball mill 74 which further reduces the particle size of the NORM wastes delivered to it. NORM wastes 20 leaving the ball mill 74 are passed over a trommel screen 76 and through a hydrocyclone 78 to ensure that NORM wastes of a predetermined size are delivered to the slurry tank 80. NORM wastes 20 having a particle size which is too large as determined by the screen 76 or the hydrocyclone 78 are captured, respectively, in tanks 82 and 84 and are returned to the feed stock tank 68. In the slurry tank 80 the finely ground NORM wastes 20 are mixed with additional volumes of water from storage tank 16 or 24 to form a slurry 22 having suitable Theological characteristics. A pump 86 delivers the slurry 22 to either the injection well 10 or recovery well 12 as desired by the operator. Thus, according to the described method, the disposal of NORM wastes 20 in cavern 18 may be performed in a safe and cost effective manner. While the inventive method and the apparatus for performing such has been described with a high degree of particularity, it will be appreciated by those skilled in the art that modifications may be made thereto. For example, the number and location of injection and recovery wells may be varied to maximize the cavern's size or the rate at which NORM wastes can be pumped into the cavern. Therefore, it is to be understood that the present invention is not limited to the method described above, but encompasses any and all methods within the scope of the following claims.