1. Field of the Disclosure
Embodiments disclosed herein relate generally to systems and methods for handling, processing and disposing of waste at a work site. More specifically, embodiments disclosed herein relate to systems and methods for processing drilling waste for injection into a downhole formation.
2. Background
In the drilling of wells, a drill bit is used to dig many thousands of feet into the earth's crust. Oil rigs typically employ a derrick that extends above the well drilling platform. The derrick supports joint after joint of drill pipe connected end-to-end during the drilling operation. As the drill bit is pushed further into the earth, additional pipe joints are added to the ever lengthening “string” or “drill string”. Therefore, the drill string includes a plurality of joints of pipe.
Fluid (e.g., “drilling mud,” “drilling fluid,” etc.) is pumped from the well drilling platform, through the drill string, and to a drill bit supported at the lower or distal end of the drill string. The drilling mud lubricates the drill bit and carries away well cuttings generated by the drill bit as it digs deeper. The cuttings are carried in a return flow stream of drilling mud through the well annulus and back to the well drilling platform at the earth's surface. When the drilling mud reaches the platform, it is contaminated with small pieces of shale and rock that are known in the industry as well cuttings or drill cuttings. Once the drill cuttings, drilling mud, and other waste reach the platform, various processing operations take place. For example, a “shale shaker” may be used to remove the drilling mud from the drill cuttings so that the drilling mud may be reused. The remaining drill cuttings, waste, and residual drilling mud (e.g., “drilling waste,” “waste,” etc.) are then transferred to a holding trough for disposal.
While the drilling mud is reusable, the drill cuttings and other solid particulate matter is generally not reusable. In some situations, even the mud may not be reused and it must be disposed. As such, drilling waste is often stored onsite for eventual removal from the drill site. Typically, the non-recycled drilling mud is disposed of separate from the drill cuttings and other waste by transporting the drilling mud via a vessel to a disposal site.
Traditional methods of disposal include dumping, bucket transport, conveyor belts, screw conveyors, and washing techniques that require large amounts of water. Adding water creates additional problems of added volume and bulk, pollution, and transport problems. Installing conveyors requires major modification to the rig area and involves extensive installation hours and expense. In some instances, the cuttings, which are still contaminated with some oil, are transported from a drilling rig to an offshore rig or ashore in the form of a thick heavy paste or slurry for injection into an earth formation. Typically, the material is put into special skips of about 10 ton capacity that are loaded by crane from the rig onto supply boats. This is a difficult and dangerous operation that may be laborious and expensive.
In addition, as hydrocarbonaceous products become rare, areas that were previously too remote and/or too cost prohibitive for production are being reconsidered. For example, some remote areas are subject to severe environmental and/or logistical constraints. Some of these areas are prone to produce drilling waste containing particulate matter, such as sand. Particulate matter like sand may cause problems because once the particulate accumulates in handling equipment, reinjection systems and/or storage containers, operations must be stopped in order to clear the particulate. Issues with sand may occur due to the particle size and composition of the sand, which cannot be degraded by a slurrification system. Thus, sand and other particulate matter may require removal from the system in order to prevent safe injection into a disposal domain, or otherwise, the sand/particulate matter must be removed from the system and disposed of through other channels, such as through onshore disposal. Thus, there exists a continuing need for more efficient slurrification methods and systems for processing drilling waste.
According to one aspect, embodiments disclosed herein relate to a waste processing system including a first container having an inlet and an outlet, a separator in fluid communication with the first container, and a mechanical degrading device configured to receive an overflow from the separator.
In another aspect, embodiments disclosed herein relate to a system for processing a waste stream for downhole injection, the system including a first container having an inlet and an outlet, a separator in fluid communication with the first container, and a mechanical degrading device configured to receive an overflow from the separator. Additionally, the system including a second container in fluid communication with the first container and the mechanical degrading device, wherein eh second container is configured to receive a ground waste from the mechanical degrading device.
In another aspect, a method of processing drilling waste including providing drilling waste to a source, transferring drilling waste from the source to a first container, and pumping drilling waste from the first container to a separator. The method also including receiving an overflow from the separator in a mechanical degrading device, processing the overflow in the mechanical degrading device, and discharging the processed overflow from the mechanical degrading device to a second container.
Other aspects of the present disclosure will be apparent from the following description and the appended claims.
a is an overhead sectional view of a mechanical degrading device in accordance with embodiments of the present disclosure.
b is an isometric view of a mechanical degrading device in accordance with embodiments of the present disclosure.
Embodiments disclosed herein relate generally to systems and methods for handling, processing, and disposing of waste at a drilling location. Other embodiments disclosed herein relate to systems and methods for processing drilling waste for injection into a downhole formation. More specifically, embodiments disclosed herein relate to systems and methods for handling drilling waste, including use of a grinder in a waste processing system. Examples of drilling waste include water-based and/or oil-based fluids, fluids with cuttings or other particulate matter entrained therein, recycled wellbore fluids, etc.
Embodiments of the present disclosure discussed herein are generally described as may be found at a drilling site. Examples of drilling sites may be onshore or offshore, and may include on-shore rigs or off-shoe rigs, which may further include platforms, submersibles, semi-submersibles, spars, tension line rigs, and tender assist rigs. Furthermore, because the systems disclosed herein may be incorporated as modular components, they may be readily transportable, relatively easy to install, and substantially self-contained.
Referring to
To control the flow of drilling waste through the container, a valve (not shown) may be added to one or more of the inlets of the first container 104. Those of ordinary skill in the art will appreciate the valve may include airtight rotational valves, three-way valves, or other valves capable of controlling a flow of drilling waste. In some embodiments, a valve may also be added to one or more of the outlets of the first container 104.
Additionally, first container 104 may have a circular external geometry, with a plurality of inlets and outlets for receiving and discharging drilling waste therethrough. The first container 104 may be any size or shape that is needed to meet operational needs. Though first container 104 is depicted with a circular shape, it may include various external or internal geometries. For example, in certain aspects, the first container 104 could be a rectangular horizontal drum. The first container may also have other configurations, such as floating roof tanks. Internally, first container 104 may have an internal weir or baffle arrangement (not shown). In other embodiments, the first container may be ventilated and configured with a pressure relief system (not shown).
Pump 108a may be a centrifugal pump disposed horizontally or vertically, the choice of which may depend upon spatial or process requirements. However, pump 108a may also include non-centrifugal pumps. For example, pump 108a may be multi-stage, positive displacement, or single-impellar pumps. Additionally, system 100 may include a plurality of pumps 108a and 108b. As illustrated, pumps 108a and 108b may be in fluid communication with the first container, whereby pump 108b is operatively configured akin to pump 108a.
Pumps 108a and 108b may have internal components such as shafts, bearings, impellers and/or diffusers (not shown) that may be formed from materials known in the art to reduce the wear and increase the life of pump components. For example, shafts, bearings, impellers and/or diffusers may be formed from a ferritic steel material, a ceramic material or a composite material including nickel, chrome, and silicone (i.e., NiResist™, 5530 alloy). Additionally, the impellers and/or diffusers may be coated with a wear-resistant material to reduce wear on the pump components. For example, coatings may include polymer-based (e.g., polyurethane), ceramics, metals, or hardfacing. Pumps 108a,b may also be coupled to a drive device (not shown), such as a direct drive, belt drive, variable speed drive, variable frequency drive, inverter, or gas drive.
Those of ordinary skill in the art will appreciate that the lines (e.g., suction, discharge, transfer, etc.) in system 100 may include piping or other comparable conduit material. The lines may include various cross-sectional geometries and dimensions. For example, discharge line 109 may include square, circular, rectangular, or elliptical cross-sections. These lines may also contain additional components, such as flow control devices, valves, restricting orifices, etc.
As shown, system 100 may also include a second container 116, similar in nature to the first container 104. However, it is not necessary that the first container 104 and second container 116 be identical. The second container 116 may include an inlet 140 and an outlet 136. In one embodiment, the second container 116 may have additional inlets and outlets, including inlet 142. The additional inlets and outlets may be used for transferring drilling waste between various components of the system 100. In one embodiment, the second container 116 may be a fines cuttings tank or a secondary cuttings receiving tank. The second container 116 may be any size or shape that is needed to meet operational needs. In certain aspects, the second container 116 may also include a mixing device 152 (
To control the flow of drilling waste through the second container 116, a valve (not shown) may be added to one or more of the inlets. Those of ordinary skill in the art will appreciate the valve may include airtight rotational valves, three-way valves, or other valves capable of controlling a flow of drilling waste and/or cuttings. In some embodiments, a valve (not shown) may be added to any of the outlets of the second container 116. Thus, the flow of drilling waste through the second container 116 may be controlled by adjusting one or more valves.
Second container 116 may also have a circular external geometry, with a plurality of inlets and outlets for receiving and discharging drilling waste therethrough. The second container 116 may be any size or shape that is needed to meet operational needs. Though second container 116 is depicted with a circular shape, it may include various external or internal geometries. For example, in certain aspects, the second container 116 could be a rectangular horizontal drum. The second container may also have other configurations, such as floating roof tanks. Internally, second container 116 may have an internal weir or baffle arrangement (not shown). In other embodiments, the first container may be ventilated and configured with a pressure relief system (not shown).
System 100 may also have a second pump 110a in fluid communication with an outlet of the second container 116. In one embodiment, the pump 110a may be located within structure 101 proximate the second container 116. In another embodiment, the pump 110a may be in fluid communication with the second container 116 to circulate or transfer drilling waste. As shown, a suction side 170 of the pump 110a may be connected to the outlet 136. However, the suction side 170 may be connected to additional outlets on the second container.
Pump 110a may be a centrifugal pump disposed horizontally or vertically, the choice of which may depend upon spatial or process requirements. However, pump 110a may also include non-centrifugal pumps. For example, pump 110a may be multi-stage, positive displacement, or single-impellar pump. Additionally, system 100 may include a plurality of pumps 110a and 110b. As illustrated, pumps 110a and 110b may be in fluid communication with the second container, whereby pump 110b is operatively configured like pump 110a.
Pump 110 may have internal components such as shafts, bearings, impellers and/or diffusers (not shown) that may be formed from materials known in the art to reduce the wear and increase the life of pump components. For example, shafts, bearings, impellers and/or diffusers may be formed from a ferritic steel material, a ceramic material or a composite material including nickel, chrome, and silicone (i.e., NiResist™, 5530 alloy). Additionally, the impellers and/or diffusers may be coated with a wear-resistant material to reduce wear on the pump components. For example, coatings may include polymer-based (e.g., polyurethane), ceramics, metals, or hardfacing. Pump 108a may be coupled to a drive device (not shown), such as a direct drive, belt drive, variable speed drive, variable frequency drive, inverter, or gas drive.
System 100 may also include a plurality of separators 106, 107. Separators 106, 107 may be used to separate drilling waste into a fluids phase (i.e., “underflow”), which may pass through screens (not shown) of the separators 106, 107 and be directed towards other areas of the system 100. Separators 106, 107 may also separate drilling waste into a separated solids phase (i.e., “overflow”) that may be retained on the screens and may exit the separators 106, 107 at a discharge end 99a, 99, respectively. Those of ordinary skill in the art will appreciate that in certain embodiments, system 100 may include less than two separators, or more than two separators.
In one embodiment, separators 106, 107 may include a vibratory shale shaker. While a number of different vibratory separators are known in the art, an example of a vibratory separator that may be used according to embodiments of the present disclosure is the MONGOOSE PT™, commercially available from M-I LLC, Houston, Tex. Separator 107 may be fitted with any size screen (not shown) as required by operational constraints. In some aspects, the separators 106, 107 may be fitted with a 300 micron screen, such that an overflow composition that may have retained particles greater than about 300 microns. In other aspects, the separators 106, 107 may be fitted with a 100 micron screen, such that the overflow composition may include particles greater than about 100 microns. The separators may also include a control system (not shown), such that variables effecting the separatory operation may be controlled. Examples of variables that a drilling operator may need to adjust during the separatory operation include a type of motion used and a deck angle.
Referring to
Referring to
Referring back to
Those of ordinary skill in the art will appreciate that third container 118 may include any type of storage vessel known in the art, such as a pressurized vessel. One type of pressure vessel that may be used in embodiments disclosed herein includes an ISO-PUMP™, commercially available from M-I LLC, Houston, Tex.
Additionally, third container 118 includes an inlet 150. In one embodiment, the inlet 150 may be located below separators 106, 107. In another embodiment, third container 118 may have multiple inlets, where any of the inlets may be in fluid communication with a discharge side of a third pump 120. There may also be additional outlets (not shown) disposed on the third container 118. Additional inlets and outlets may be used for receiving and discharging drilling waste to other components of system 100.
System 100 may further include multiple pumps 120a and 120b in fluid communication with an outlet (not shown) of the third container 118. In this embodiment, the pumps 120a and 120b may be located within structure 101 proximate to the third container 118. A suction side of either of the pumps 120a or 120b may be connected to an outlet of the third container 118. In some aspects, the pumps 120a,b may also be in fluid communication with container 118 via additional outlets on the third container. In further aspects, pumps 120a and 120b may include a suction side connected to a bypass line (not shown) that bypasses flow around the third container 118. Pumps 120a,b may include a centrifugal pump; however, the type of pump 120 used in system 100 is not limited. For example, pump 120 could be a positive displacement pump, or a booster pump.
System 100 may have a high pressure (“HP”) pump 122 within the structure 101. In one embodiment, HP pump 122 may be located proximate, and in fluid communication with pump 120. Alternatively, HP pump 122 may be in fluid communication with the third container 118. HP pump 122 may also have a discharge side in fluid communication with a downhole formation (not shown). For example, HP pump 122 may be in fluid communication with third container 118, such that pump 122 may pressurize drilling waste for injection into a downhole formation.
Referring to
In one embodiment, source 102 may be a reservoir. Examples of reservoirs may include storage tanks, pits, collection vats, and waste vessels, which those of ordinary skill in the art will appreciate may already exist as part of the rig infrastructure. In other embodiments, source 102 may be cuttings boxes, sumps, pits, or a pressure or atmospheric vessel configured for transferring drilling waste to the system 100. Those of ordinary skill in the art will appreciate that in certain embodiments, source 102 may include a flow line. The flow line may include piping or other conduits to provide drilling waste from source 102 to system 100. In some embodiments, the drilling waste may be provided from source 102 to first container 104.
System 100 may have multiple pumps in fluid communication with the first container 104. For example, as represented in
In operation, drilling waste enters pump 108a from a suction line 115a, wherein the pump 108a pressurizes the flow and circulates the waste via a discharge line 109 that branches to a return line 109b or to other equipment in system 100, depending on operating conditions. In one aspect, pump 108a may discharge drill waste to separator 107 thru transfer line 161.
System 100 may also include a second container 116 having various inlets and outlets. As shown by
As depicted, second pumps 110a and 110b may be used to circulate the flow to the second container for further processing via discharge line 119, or forward the flow via transfer line to other downstream operations. Though shown as multiple pumps 110a and 110b, the pumps do not have to operate together, nor do they have to be in a parallel configuration. Further, in certain aspects, system 100 may only include one pump 110. In operation, flow from the second container 116 may enter the second pump 110a from a suction line 170, wherein the pump 110a pressurizes the flow and circulates the waste via a discharge line 119 that branches to a return line 119a or to other equipment in system 100, depending on operating conditions. As shown, the pumps 110a and 110b may have the suction side connected to a two-way flow bypass line 113 that may be used for bypassing flow from the first container 104 to the pumps 110a and 110b. In one embodiment, the flow from pumps 110a and 110b may be forwarded through transfer line 161 to separator 107.
Still referring to
The overflow received by the mechanical degrading device 112 may be processed into a ground waste. In operation, the conveyor 114 conveys the drilling waste to the inlet 216 of the mechanical degrading device 112. The motor 200 operates to drive the assemblies 206 used for macerating the drilling waste into a ground waste. Typically, the ground waste produced by the mechanical degrading device 112 exits the outlet 97 and may be fed back to the first or second containers 104, 116 for further processing. The overflow produced from the separator may have particles greater than 300 micron. Thus, the ground waste produced from the mechanical degrading device 112 may reduce the particles to less than 300 micron.
Referring to
As illustrated, system 100 may have multiple pumps 108a and 108b in a parallel configuration that may be used to circulate the flow back to first container 104 for further processing, as well as forward flow via a transfer line 111 to other downstream operations. The pumps 108a and 108b may have their suction side connected to a bypass line 113 that transfers flow from the second container 116 to the pumps. Though shown as multiple pumps 108a and 108b, the pumps do not have to operate together, and in certain aspects, there may only be one pump 108 if desired.
In operation, drilling waste may enter pump 108a from a suction line 115a, wherein the pump 108a pressurizes the flow and circulates the waste via a discharge line 109 that branches to a return line 109b or to other equipment in system 100, depending on operating conditions. In one aspect, the pumps 108a and 108b may discharge drill waste to separators 106, 107 thru transfer lines 161, 161a. In other aspects, the pumps may discharge drilling waste to the grinding device 112 via transfer line 181.
System 100 may also include a second container 116 having various inlets and outlets. As shown in
As depicted in
System 100 may include multiple separators 106, 107, which may be used to process the drilling waste into an underflow and an overflow. In operation, an overflow from the separators 106, 107 may be fed to a conveyor 114. In some aspects, the overflow may be gravity fed to the conveyor 114. As overflow is produced from the separators 106, 107 and fed to the conveyor 114, the conveyor 114 may transfer the overflow to the mechanical degrading device 112. As shown, underflow produced from the separator 107 may be fed to a third container 118. In one aspect, the underflow may be gravity fed to the third container 118. Alternatively, the separator 106 may provide underflow to the first container 104 via transfer line 96. This may provide an operator greater flexibility to further process underflow within system 100.
The overflow received by the mechanical degrading device 112 may be processed into a ground waste. In operation, the conveyor 114 conveys the drilling waste to the inlet 216 of the mechanical degrading device 112. The motor 200 operates to drive the assemblies 206 used for macerating the drilling waste into a ground waste. Typically, the ground waste produced by the mechanical degrading device 112 exits the outlet 97 and may be fed back to the first or second containers 104, 116 for further processing. In one embodiment, the ground waste is gravity fed to the containers.
Third container 118 may be a raw material storage tank, waste storage tank, or any other vessel commonly used in association with processing, handling, or storing drilling waste. Specifically, third container 118 may include cuttings boxes, ISO-tanks, and pneumatic transfer vessels. In some embodiments, third container 118 may include several individual vessels connected to allow the transference of underflow therebetween. The third container 118 may be portable, as such, that those of ordinary skill in the art will appreciate that container 118 may be used for both storage and transport of drilling waste.
Additionally, storing or handling of the underflow may be to facilitate the transfer of the underflow to a waste injection system through a transfer line 194. The outlet 195 of the third container 118 may be in fluid communication with third pump 120. Alternatively, the third container 118 may be in fluid communication with second pumps 110a and 110b via a two-way flow bypass line 190.
In accordance with embodiments disclosed herein, system 100 may include the use of high-pressure pumps 122 (
Embodiments disclosed herein also pertain to a method of processing drilling waste. The method may include providing drilling waste from a wellbore to a source, which may be a reservoir. The method may include transferring drilling waste from the source to a first container, which may be located in a structure containing other equipment used in the method for processing waste. The method may further include a set of pumps for circulating flow within the first container, and for pumping drilling waste from the first container to a separator, which may be a vibratory shale shaker that produces an overflow and underflow.
The method may also include receiving the overflow from the separator in a grinder. In an embodiment, the overflow may be conveyed from the separator to the grinder by an intermittent conveying step. Once the grinder receives the overflow, the overflow is processed in the grinder to produce a ground waste. After grinding, the ground waste is discharged from the grinder to a second container.
The method may further include operating conditions yielding an amount of overflow received by the grinder in the range of 5 to 30 tons per hour. In one embodiment, the amount of overflow received by the grinder may be less than 25 tons per hour. In certain embodiments, the overflow composition may contain particles greater than 300 microns.
In addition to producing an overflow, the separator may also produce an underflow, such that the method of processing drilling waste may further include the steps of receiving the underflow from the separator into a second container. The second container may also be located in the structure, and may be used for holding processed drilling waste. The method may include another set of pumps for circulating flow within the second container, as well as using the pumps to convey processed drilling waste through an outlet of the second container, and injecting the drilling waste into a downhole formation.
The method of injecting a slurry into a formation in accordance with embodiments disclosed herein may include providing a flow of processed waste to a high pressure injection pump, increasing the pressure of the flow, and delivering or pumping the waste downhole into the formation.
Advantageously, embodiments disclosed herein may provide systems and methods for processing a drilling waste that provides reinjection slurries in compliance with environmental regulations. Additionally, the systems and methods disclosed herein may allow a drilling operator to more efficiently process drilling waste. The process may further increase the efficiency of the system, while producing cleaner reinjection slurries for recycling into the well bore. Embodiments disclosed herein may also reduce or eliminate shut down time as a result of particulate accumulation. Reduced particle size also means lower pressure drops that may result decreased energy consumption. The device may provide the ability of operations to efficiently and profitably produce hydrocarbonaceous fluids from offshore and onshore environments, as well as locations that require very low or zero emissions from disposed waste.
Advantageously, embodiments disclosed herein may also allow for a modularized drilling waste system that may be transported and installed on drilling rigs with relative ease. Because of the system's modularity, the entire separatory operation may be maintained within a support structure, installed and uninstalled on a rig as may be necessary. As such, the modularity of the system may provide a solution to bulky systems of existing rigs, especially tender-assist and other mobile drill rigs. Furthermore, because the system may be modular and substantially self-contained, systems in accordance with the present disclosure may be retrofitted onto existing rigs. Such retrofitting operations may further increase the cuttings processing and drilling efficiency of offshore rigs. The modularity and retrofitting aspects of the present disclosure may further provide the advantage of faster methods for rigging up and manipulating aspects of drilling waste management.
Advantageously, embodiments disclosed herein may further provide for systems and methods that allow for the processing and injecting of reduced particle size solids content of a slurry at a work site.
While the present disclosure has been described with respect to a limited number of embodiments, those skilled in the art, having benefit of this disclosure, will appreciate that other embodiments can be devised which do not depart from the scope of the disclosure as described herein. Accordingly, the scope of the invention should be limited only by the attached claims.
Filing Document | Filing Date | Country | Kind | 371c Date |
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PCT/US09/68623 | 12/18/2009 | WO | 00 | 6/17/2011 |
Number | Date | Country | |
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61140572 | Dec 2008 | US |