Patent Application
20210261852
The present disclosure relates to the recovery of bitumen from oil sands. More particularly, the present disclosure is an improved method for bitumen recovery from oil sands through either surface mining or in-situ recovery. The improvement is the use of a propylene oxide capped glycol ether as an extraction aid in the water and/or steam used in the bitumen recovery process.
Deposits of oil sands are found around the world, but most prominently in Canada, Venezuela, and the United States. These oil sands contain significant deposits of heavy oil, typically referred to as bitumen. The bitumen from these oil sands may be extracted and refined into synthetic oil or directly into petroleum products. The difficulty with bitumen lies in that it typically is very viscous, sometimes to the point of being more solid than liquid. Thus, bitumen typically does not flow as less viscous, or lighter, crude oils do.
Because of the viscous nature of bitumen, it cannot be produced from a well drilled into the oil sands as is the case with lighter crude oil. This is so because the bitumen simply does not flow without being first heated, diluted, and/or upgraded. Since normal oil drilling practices are inadequate to produce bitumen, several methods have been developed over several decades to extract and process oil sands to remove the bitumen. For shallow deposits of oil sands, a typical method includes surface extraction, or mining, followed by subsequent treatment of the oil sands to remove the bitumen.
The development of surface extraction processes has occurred most extensively in the Athabasca field of Canada. In these processes, the oil sands are mined, typically through strip or open pit mining with draglines, bucket-wheel excavators, and, more recently, shovel and truck operations. The oil sands are then transported to a facility to process and remove the bitumen from the sands. These processes typically involve a solvent of some type, most often water or steam, although other solvents, such as hydrocarbon solvents, have been used.
After excavation, a hot water extraction process is typically used in the Athabasca field in which the oil sands are mixed with water at temperatures ranging from approximately 35° C. to 75° C., with recent improvements lowering the temperature necessary to the lower portion of the range. An extraction agent, such as sodium hydroxide (NaOH), surfactants, and/or air may be mixed with the oil sands.
Water is added to the oil sands to create an oil sands slurry, to which additives such as NaOH may be added, which is then transported to an extraction plant, typically via a pipeline. Inside a separation vessel, the slurry is agitated and the water and NaOH releases the bitumen from the oil sands. Air entrained with the water and NaOH attaches to the bitumen, allowing it to float to the top of the slurry mixture and create a froth. The bitumen froth is further treated to remove residual water and fines, which are typically small sand and clay particles. The bitumen is then either stored for further treatment or immediately treated, either chemically or mixed with lighter petroleum products, and transported by pipeline for upgrading into synthetic crude oil. Unfortunately, this method cannot be used for deeper tar sand layers. In-situ techniques are necessary to recover deeper oil in well production. It is estimated that around 80 percent of the Alberta tar sands and almost all Venezuelan tar sands are too far below the surface to use open pit mining.
In well production, referred to as in-situ recovery, Cyclic Steam Stimulation (CSS) is the conventional “huff and puff” in-situ method in which steam is injected into the well at a temperature of 250° C. to 400° C. The steam rises and heats the bitumen, decreasing its viscosity. The well is allowed to sit for days or weeks, and then hot oil mixed with condensed steam is pumped out for a period of weeks or months. The process is then repeated. Unfortunately, the “huff and puff” method requires the site to be shut down for weeks to allow pumpable oil to accumulate. In addition to the high cost to inject steam, the CSS method typically results in only 20 to 25 percent recovery of the available oil.
Steam Assisted Gravity Drainage (SAGD) is another in-situ method where two horizontal wells are drilled in the tar sands, one at the bottom of the formation and another five meters above it. The wells are drilled in groups off of central pads. These wells may extend for miles in all directions. Steam is injected into the upper well, thereby melting the bitumen which then flows into the lower well. The resulting liquid oil mixed with condensed steam is subsequently pumped to the surface. Typical recovery of the available oil is 40 to 60 percent.
The above methods have many costs, environmental and safety problems associated with them. For example, the use of large amounts of steam is energy intensive and requires the processing and disposal of large amounts of water. Currently, tar sands extraction and processing require several barrels of water for each barrel of oil produced. Strip mining and further treatment results in incompletely cleaned sand, which requires further processing, before it can be returned to the environment. Further, the use of a large quantity of caustic in surface mining not only presents process safety hazards but also contributes formation of fine clay particles in tailings, the disposal of which is a major environmental problem.
Thus, there remains a need for efficient, safe and cost-effective methods to improve the recovery of bitumen from oil sands.
The present disclosure is an improved bitumen recovery process comprising treating oil sands with a propylene oxide capped glycol ether wherein the treatment is to oil sands recovered by surface mining or in-situ production to oil sands in a subterranean reservoir. The propylene oxide capped glycol ethers of the present disclosure have been found to particularly demonstrate improved bitumen recovery for Steam Assisted Gravity Drainage (SAGD) in-situ production relative to other glycol ethers or no-additive present.
In one embodiment of the bitumen recovery process described herein the propylene oxide capped glycol ether is described by the structure:
RO—(CH2CH2O)m(CH2CH(CH3)O)nH
where R is a linear, branched, cyclic alkyl, phenyl, or alkyl phenyl group of at least 4 carbons and where m and n are independently 1 to 3. Preferably R is n-butyl, n-pentyl, 2-methyl-1-pentyl, n-hexyl, n-heptyl, n-octyl, 2-ethylhexyl, 2-propylheptyl, phenyl, alkyl phenyl or cyclohexyl. Preferably, m is 1 and n is 1. Preferably the propylene oxide capped glycol ether is one of, or a combination thereof, preferably propylene oxide capped n-butyl ether of ethylene glycol, propylene oxide capped n-hexyl ether of ethylene glycol, or propylene oxide capped 2-ethylhexyl ether of ethylene glycol.
In another embodiment of the present disclosure, the bitumen recovery process by surface mining described herein includes: i) surface mining oil sands, ii) preparing an aqueous slurry of the oil sands, iii) treating the aqueous slurry with the propylene oxide capped glycol ether provided herein, iv) agitating the treated aqueous slurry, v) transferring the agitated treated aqueous slurry to a separation tank, and vi) separating the bitumen from the aqueous portion, preferably the propylene oxide capped glycol ether is present in the aqueous slurry in an amount of from 0.01 to 10 weight percent based on the weight of the oil sands.
In another embodiment of the present disclosure, the bitumen recovery process by in-situ production described herein includes: i) treating a subterranean reservoir of oil sands by injecting steam containing the propylene oxide capped glycol ether provided herein into a well, and ii) recovering the bitumen from the well, preferably the concentration of the propylene oxide capped glycol ether in the steam is in an amount of from 100 ppm to 10 weight percent based on the total weight of the propylene oxide capped glycol ether and the steam.
The separation of bitumen and/or heavy oil from oil sands is accomplished by, but not limited to, two methods; surface mining or in-situ recovery sometimes referred to as well production. The oil sands may be recovered by surface or strip mining and transported to a treatment area. A good summary can be found in the article “Understanding Water-Based Bitumen Extraction from Athabasca Oil Sands”, J. Masliyah, et al., Canadian Journal of Chemical Engineering, Volume 82, August 2004. The basic steps in bitumen recovery via surface mining include: extraction, froth treatment, tailings treatment, and upgrading. The steps are interrelated; the mining operation affects the extraction and in turn the extraction affects the upgrading operation.
Typically, in commercial bitumen recovery operations, the oil sand is mined in an open-pit mine using trucks and shovels. The mined oil sands are transported to a treatment area. The extraction step includes crushing the oil sand lumps and mixing them with (recycle process) water in mixing boxes, stirred tanks, cyclo-feeders or rotary breakers to form conditioned oil sands slurry. The conditioned oil sands slurry is introduced to hydrotransport pipelines or to tumblers, where the oil sand lumps are sheared and size reduction takes place. Within the tumblers and/or the hydrotransport pipelines, bitumen is recovered or “released”, or “liberated”, from the sand grains. Chemical additives can be added during the slurry preparation stage; for examples of chemicals known in the art see US2008/0139418, incorporated by reference herein in its entirety. In typical operations, the operating slurry temperature ranges from 35° C. to 75° C., preferably 40° C. to 55° C.
Entrained or introduced air attaches to bitumen in the tumblers and hydrotransport pipelines creating froth. In the froth treatment step, the aerated bitumen floats and is subsequently skimmed off from the slurry. This is accomplished in large gravity separation vessels, normally referred to as primary separation vessels (PSV), separation cells (Sep Cell) or primary separation cells (PSC). Small amounts of bitumen droplets (usually un-aerated bitumen) remaining in the slurry are further recovered using either induced air flotation in mechanical flotation cells and tailings oil recovery vessels, or cyclo-separators and hydrocyclones. Generally, overall bitumen recovery in commercial operations is about 88 to 95 percent of the original oil in place. The recovered bitumen in the form of froth normally contains 60 percent bitumen, 30 percent water and 10 percent solids.
The bitumen froth recovered as such is then de-aerated and diluted (mixed) with solvents to provide sufficient density difference between water and bitumen and to reduce the bitumen viscosity. The dilution by a solvent (e.g., naphtha or hexane) facilitates the removal of the solids and water from the bitumen froth using inclined plate settlers, cyclones and/or centrifuges. When a paraffinic diluent (solvent) is used at a sufficiently high diluent to bitumen ratio, partial precipitation of asphaltenes occurs. This leads to the formation of composite aggregates that trap the water and solids in the diluted bitumen froth. In this way gravity separation is greatly enhanced, potentially eliminating the need for cyclones or centrifuges.
In the tailings treatment step, the tailings stream from the extraction plant goes to the tailings pond for solid-liquid separation. The clarified water is recycled from the pond back to the extraction plant. To accelerate tailings handling, gypsum may be added to mature fine tailings to consolidate the fines together with the coarse sand into a non-segregating mixture. This method is referred to as the consolidated (composite) tailing (CT) process. CT is disposed of in a geotechnical manner that enhances its further dewatering and eventual reclamation. Optionally, tailings from the extraction plant are cycloned, with the overflow (fine tailings) being pumped to thickeners and the cyclone underflow (coarse tailings) to the tailings pond. Fine tailings are treated with flocculants, then thickened and pumped to a tailings pond. Further, the use of paste technology (addition of flocculants/polyelectrolytes) or a combination of CT and paste technology may be used for fast water release and recycle of the water in CT to the extraction plant for bitumen recovery from oil sands.
In the final step, the recovered bitumen is upgraded. Upgrading either adds hydrogen or removes carbon to achieve a balanced, lighter hydrocarbon that is more valuable and easier to refine. The upgrading process also removes contaminants such as heavy metals, salts, oxygen, nitrogen and sulfur. The upgrading process includes one or more steps such as: distillation wherein various compounds are separated by physical properties, coking, hydro-conversion, solvent deasphalting to improve the hydrogen to carbon ratio, and hydrotreating which removes contaminants such as sulfur.
In one embodiment of the present disclosure, the improvement to the process of recovering bitumen from oil sands is the addition of a propylene oxide capped glycol ether during the slurry preparation stage. The sized material is added to a slurry tank with agitation and combined with a propylene oxide capped glycol ether. The propylene oxide capped glycol ether may be added to the oil sands slurry neat or as an aqueous solution having a concentration of from 100 ppm to 10 weight percent propylene oxide capped glycol ether based on the total weight of the aqueous solution (e.g., propylene oxide capped glycol ether and water). Preferably, the propylene oxide capped glycol ether is present in the aqueous oil sands slurry in an amount of from 0.01 to 10 weight percent based on the weight of the oil sands.
Preferred propylene oxide capped glycol ethers of the present disclosure are represented by the following formula:
RO—(CH2CH2O)m(CH2CH(CH3)O)nH
where R is a linear, branched, cyclic alkyl, phenyl, or alkyl phenyl group of at least 4 carbons and where m and n are independently 1 to 3. Preferably R is n-butyl, n-pentyl, 2-methyl-1-pentyl, n-hexyl, n-heptyl, n-octyl, 2-ethylhexyl, 2-propylheptyl, phenyl, alkyl phenyl group or cyclohexyl. Preferably, m is 1 and n is 1.
As used hereafter, propylene oxide capped glycol ethers of the present disclosure mean that the propylene oxide cap comprises 1 to 3 ethylene oxide units. Preferred propylene oxide capped glycol ethers are the propylene oxide capped n-butyl ethers of ethylene glycol, the propylene oxide capped n-butyl ethers of diethylene glycol, the propylene oxide capped n-butyl ethers of triethylene glycol, the propylene oxide capped n-pentyl ethers of ethylene glycol, the propylene oxide capped n-pentyl ethers of diethylene glycol, the propylene oxide capped n-pentyl ethers of triethylene glycol, the propylene oxide capped 2-methyl-1-pentyl ethers of ethylene glycol, the propylene oxide capped 2-methyl-1-pentyl ethers of diethylene glycol, the propylene oxide capped 2-methyl-1-pentyl ethers of triethylene glycol, the propylene oxide capped n-hexyl ethers of ethylene glycol, the propylene oxide capped n-hexyl ethers of diethylene glycol, the propylene oxide capped n-hexyl ethers of triethylene glycol, the propylene oxide capped n-heptyl ethers of ethylene glycol, the propylene oxide capped n-heptyl ethers of diethylene glycol, the propylene oxide capped n-heptyl ethers of triethylene glycol, the propylene oxide capped n-octyl ethers of ethylene glycol, the propylene oxide capped n-octyl ethers of diethylene glycol, the propylene oxide capped n-octyl ethers of triethylene glycol, the propylene oxide capped 2-ethylhexyl ethers of ethylene glycol, the propylene oxide capped 2-ethylhexyl ethers of diethylene glycol, the propylene oxide capped 2-ethylhexyl ethers of triethylene glycol, the propylene oxide capped 2-propylheptyl ethers of ethylene glycol, the propylene oxide capped 2-propylheptyl ethers of diethylene glycol, the propylene oxide capped 2-propylheptyl ethers of triethylene glycol, the propylene oxide capped phenyl ethers of ethylene glycol, the propylene oxide capped phenyl ethers of diethylene glycol, the propylene oxide capped phenyl ethers of triethylene glycol, the propylene oxide capped cyclohexyl ethers of ethylene glycol, the propylene oxide capped cyclohexyl ethers of diethylene glycol, the propylene oxide capped cyclohexyl ethers of triethylene glycol, or mixtures thereof.
The propylene oxide capped glycol ether solution/oil sand slurry is typically agitated from 5 minutes to 4 hours, preferably for an hour or less. Preferably, the propylene oxide capped glycol ether solution oil sands slurry is heated to equal to or greater than 35° C., more preferably equal to or greater than 40° C., more preferably equal to or greater than 55° C., more preferably equal to or greater than 60° C. Preferably, the propylene oxide capped glycol ether solution oil sands slurry is heated to equal to or less than 100° C., more preferably equal to or less than 80° C., and more preferably equal to or less than 75° C.
As outlined herein, the propylene oxide capped glycol ether treated slurry may be transferred to a separation tank, typically comprising a diluted detergent solution, where the bitumen and heavy oils are separated from the aqueous portion. The solids and the aqueous portion may be further treated to remove any additional free organic matter.
In another embodiment of the present disclosure, bitumen is recovered from oil sands through well production wherein the propylene oxide capped glycol ether as described herein above can be added to oil sands by means of in-situ treatment of the oil sand deposits that are located too deep for strip mining. The two most common methods of in-situ production recovery are cyclic steam stimulation (CSS) and steam-assisted gravity drainage (SAGD). CSS can utilize both vertical and horizontal wells that alternately inject steam and pump heated bitumen to the surface, forming a cycle of injection, heating, flow and extraction. SAGD utilizes pairs of horizontal wells placed one over the other within the bitumen pay zone. The upper well is used to inject steam, creating a permanent heated chamber within which the heated bitumen flows by gravity to the lower well, which extracts the bitumen. However, new technologies, such as vapor recovery extraction (VAPEX) and cold heavy oil production with sand (CHOPS) are being developed.
The basic steps in the in-situ treatment to recover bitumen from oil sands includes: steam injection into a well, recovery of bitumen from the well, and dilution of the recovered bitumen, for example with condensate, for shipping by pipelines.
In accordance with this method, the propylene oxide capped glycol ether is used as a steam additive in a bitumen recovery process from a subterranean oil sand reservoir. The mode of steam injection may include one or more of steam drive, steam soak, or cyclic steam injection in a single or multi-well program. Water flooding may be used in addition to one or more of the steam injection methods listed herein above.
Typically, the steam is injected into an oil sands reservoir through an injection well, and wherein formation fluids, comprising reservoir and injection fluids, are produced either through an adjacent production well or by back flowing into the injection well.
In most oil sand reservoirs, a steam temperature of at least 180° C., which corresponds to a pressure of 150 psi (1.0 MPa), or greater is needed to mobilize the bitumen. Preferably, the propylene oxide capped glycol ether-steam injection stream is introduced to the reservoir at a temperature in the range of from 150° C. to 300° C., preferably 180° C. to 260° C. The particular steam temperature and pressure used in the process of the present disclosure will depend on such specific reservoir characteristics as depth, overburden pressure, pay zone thickness, and bitumen viscosity, and thus will be worked out for each reservoir.
It is preferable to inject the propylene oxide capped glycol ether simultaneously with the steam to ensure or maximize the amount of propylene oxide capped glycol ether actually moving with the steam. In some instances, it may be desirable to precede or follow a steam-propylene oxide capped glycol ether injection stream with a steam-only injection stream. In this case, the steam temperature can be raised above 260° C. during the steam-only injection. The term “steam” used herein is meant to include superheated steam, saturated steam, and less than 100 percent quality steam.
For purposes of clarity, the term “less than 100 percent quality steam” refers to steam having a liquid water phase present. Steam quality is defined as the weight percent of dry steam contained in a unit weight of a steam-liquid mixture. “Saturated steam” is used synonymously with “100 percent quality steam”. “Superheated steam” is steam which has been heated above the vapor-liquid equilibrium point. If super heated steam is used, the steam is preferably super heated to between 5° C. to 50° C. above the vapor-liquid equilibrium temperature, prior to adding the propylene oxide capped glycol ether.
The propylene oxide capped glycol ether may be added to the steam neat or as a concentrate. If added as a concentrate, it may be added as a 1 to 99 weight percent solution in water, where the weight percent is based on the total weight of the concentrate. Preferably, the propylene oxide capped glycol ether is substantially volatilized and carried into the reservoir as an aerosol or mist. Here again, the rationale is to maximize the amount of propylene oxide capped glycol ether traveling with the steam into the reservoir.
The propylene oxide capped glycol ether is preferably injected intermittently or continuously with the steam, so that the steam-propylene oxide capped glycol ether injection stream reaches the downhole formation through common tubing. The rate of propylene oxide capped glycol ether addition is adjusted to maintain the preferred propylene oxide capped glycol ether concentration of 100 ppm to 10 weight percent in steam. The rate of steam injection for a typical oil sands reservoir might be on the order of enough steam to provide an advance through the formation of from 1 to 3 feet/day.
An effective SAGD additive must satisfy many requirements to be considered as successful. The major criteria of a successful additive is the ability of the additive to travel with steam and reach unrecovered in-situ bitumen in reservoir formation, favorably interact with water/bitumen/rock to enhance bitumen recovery, and not adversely interfere with existing operations. Among the three, the requirement of an additive to vaporize at SAGD operating temperatures and travel with steam limits the choice and consideration of different chemistries in SAGD technology. For example, many high molecular weight surfactants even though are known to help enhance oil recovery are not considered as SAGD additives due to their inability to travel with steam owing to high boiling point. However, many propylene oxide capped glycol ethers which have high boiling point than water are an exception to this. Phase equilibrium studies have shown favorable partitioning of this class of materials in vapor (i.e., steam) compared to that in liquid (i.e., water) phase. The unique ability to partition more in vapor arises from the ability of many propylene oxide capped glycol ethers to form water-additive azeotrope especially when present at low concentration and thereby many including those mentioned in this embodiment can travel with steam.
Comparative Example A comprises only water. Examples 1 to 2 are described by the following structure:
RO—(CH2CH2O)m(CH2CH(CH3)O)nH
Comparative Examples B and C are described by the following structure:
RO—(CH2CH(CH3)O)n(CH2CH2O)mH
For Comparative Examples A to C and Examples 1 to 2 the interfacial tension (IFT) between oil and water is determined at four different temperatures and the results are shown in Table 1.
Interfacial Tension
The IFT is measured using a Tracker dynamic drop tensiometer equipped with a cell to enable measurement at high temperature and pressure (max 200° C. and 200 bar). The principal behind this technique involves the formation of a droplet of the dispersed phase (oil) of known volume within the continuous phase (water). The curvature of the droplet is measured and from this the IFT can be calculated.
The oil used for screening of new formulations consisted of a 50:50 mix by weight of dodecane and toluene. The oil sample to be measured is drawn into a syringe. Next, a “J” hook needle is placed on the syringe. The syringe is subsequently installed into the holder inside the pressure cell. A cuvette is filled with deionized water and the desired amount of additive (generally 2000 ppm) and also placed in the holder in the pressure cell. The placement of the cuvette was such that the tip of the needle from the syringe was submerged in the fluid contained within the cuvette. The pressure cell assembly is completed, and then placed on the Tracker instrument. The cell is heated to the desired measurement temperature (in the range of 110-170° C.). Upon reaching the desired set point temperature, the oil is pushed through the syringe needle to form a stable drop at the needle tip. Droplets with a volume of approximately 10 μL volume are formed. All measurements are taken within 400 seconds of droplet formation to allow for equilibration to occur. The IFT value is recorded and the measurement is repeated 2 to 3 times. Data is reported as the average value over all of the measurements. Subsequently, additional temperature set points are measured for a given formulation. The experimental uncertainty of IFT measurement is less than 1.0 dyn/cm. Table 1 summarizes the experimental results.
Equilibrium Partitioning
The major limitation in chemical co-injection with steam in SAGD is transport. When an additive is injected into the steam line, the additive must stay in the vapor phase for it to be carried to the reservoir. Once down hole, the additive in steam must then travel to the steam chamber edge where the bitumen extraction takes place.
For Example 1 the equilibrium partitioning of phenol ethoxypropoxylate (where R is phenyl, m is 1, and n is 1) is measured in a vapor-liquid-liquid equilibrium (VLLE) system at high temperature. 350 g of water and 350 g of tert-butylbenzene containing 8000 ppm of phenol propoxyethoxylate is loaded into a 1.8 L Lab Max stirred tank reactor. Small aliquots of vapor phase, organic (TBB) phase, and aqueous phase are sampled at 150° C., 175° C., and 200° C. The concentrations of Example 1 (the phenol ethoxypropoxylate) are measured by gas chromatography equipped with a FID. The concentration of Example 1 in each phase is shown in Table 2. KV/A value is greater than 1 at 175° C. and 200° C., indicating the existence of a positive azeotrope. The preferential partitioning of the additive into the vapor phase shows that the additive can be carried down hole and through the steam chamber edge along with steam in SAGD applications.
Gravity Drainage
The effect of additive on bitumen recovery is investigated using a gravity drainage apparatus and is compared against the baseline (i.e., without any additive). Gravity drainage apparatus consists of a cylindrical steam chamber with a bitumen-saturated synthetic sand core hanging along the central axis from the ceiling of the steam chamber. The synthetic core (dimensions 1.5″×6″; DXH) sits inside a mesh basket such that steam or steam plus additive can easily diffuse and interact with the core from all directions. Steam at high temp and pressure (comparable to SAGD steam chamber conditions) is then injected along the annular space inside the steam chamber. Steam or steam plus additive diffuses and interacts with the core and cause bitumen and condensed steam to gravity drain at the bottom of the chamber and is collected as a function of time. The chamber pressure is controlled and held constant using a back-pressure regulator. The experiments provide information on oil recovery rates (i.e., percentage of original oil in place (OOIP) recovered as a function of time) and total oil recovered (i.e., oil drained with time plus recovered oil along chamber walls and lines) at the end of the experiment. Experiments last 5.5 hours along and are operated under same conditions of temperature and pressure. Steam was injected at a rate of 5 ml/min and the additive concentration was kept at 4000 ppm.
Com Ex A has no additive, i.e., just steam (Steam Baseline), Com Ex B (steam plus phenol propoxyethoxylate) and Ex 1 (steam plus phenol ethoxypropoxylate). The overall recovery after 5.5 hours experiment is provided in
| Filing Document | Filing Date | Country | Kind |
|---|---|---|---|
| PCT/US2019/039831 | 6/28/2019 | WO | 00 |
| Number | Date | Country | |
|---|---|---|---|
| 62691692 | Jun 2018 | US |
