WO2012141024A1 - Method for recovering oil fraction in crude oil sludge - Google Patents

Method for recovering oil fraction in crude oil sludge Download PDF

Info

Publication number
WO2012141024A1
WO2012141024A1 PCT/JP2012/058898 JP2012058898W WO2012141024A1 WO 2012141024 A1 WO2012141024 A1 WO 2012141024A1 JP 2012058898 W JP2012058898 W JP 2012058898W WO 2012141024 A1 WO2012141024 A1 WO 2012141024A1
Authority
WO
WIPO (PCT)
Prior art keywords
oil
crude oil
sludge
crude
water
Prior art date
Application number
PCT/JP2012/058898
Other languages
French (fr)
Japanese (ja)
Inventor
均 南口
忠美 毛利
Original Assignee
システム機工株式会社
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by システム機工株式会社 filed Critical システム機工株式会社
Priority to JP2013509851A priority Critical patent/JP5925189B2/en
Publication of WO2012141024A1 publication Critical patent/WO2012141024A1/en

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
    • C10G1/00Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal
    • C10G1/02Production of liquid hydrocarbon mixtures from oil-shale, oil-sand, or non-melting solid carbonaceous or similar materials, e.g. wood, coal by distillation
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10GCRACKING HYDROCARBON OILS; PRODUCTION OF LIQUID HYDROCARBON MIXTURES, e.g. BY DESTRUCTIVE HYDROGENATION, OLIGOMERISATION, POLYMERISATION; RECOVERY OF HYDROCARBON OILS FROM OIL-SHALE, OIL-SAND, OR GASES; REFINING MIXTURES MAINLY CONSISTING OF HYDROCARBONS; REFORMING OF NAPHTHA; MINERAL WAXES
    • C10G2300/00Aspects relating to hydrocarbon processing covered by groups C10G1/00 - C10G99/00
    • C10G2300/10Feedstock materials
    • C10G2300/1033Oil well production fluids

Definitions

  • the present invention relates to a method for recovering oil content in crude oil sludge accumulated at the bottom of a crude oil tank, for example.
  • Crude sludge treatment methods and treatment technologies include COW (Crude Oil Washing) method, warm water washing method, chemical treatment method, manual method, and centrifugal separation method.
  • the COW method heats crude oil to approximately 60 ° C., pressurizes it, crushes and dissolves sludge accumulated at the bottom of the tank with an injection nozzle, and transfers it to another tank.
  • crude sludge can be processed in a short period of time and has a lot of results, sludge is deposited again at the destination. For this reason, it can be said that it is a prescription for turning crude oil sludge.
  • the COW method is a method of forcibly stirring uprooted sludge to make it temporarily fluid and recovering it to another tank, so there is a merit that sludge is not carried out of the tank. The problem has occurred and the problem is not essentially solved.
  • Japanese Utility Model Laid-Open No. 6-81649 discloses a liquid ejecting apparatus used in the COW method.
  • the hot water washing method is a method that dissolves and floats crude sludge with hot water, and is a relatively safe treatment method, but it requires a large amount of hot water, so it is expensive, and oil that does not dissolve in hot water cannot be recovered. There are various problems such as emulsion generated by agitation and treatment of a large amount of waste water, and it is not so often used recently.
  • the chemical treatment method uses a chemical that dissolves sludge, but for reasons such as requiring heating and stirring operations, limited dissolution effects, and increased costs. This is rarely done recently.
  • the manual method has been practiced for a long time by a method in which an operator enters the tank and discharges it outside the tank with a manual or automatic excavator, and there are many places where it is still implemented.
  • HSE global environment conservation
  • the centrifugal separation method is a promising method in that, for example, a decanter type three-phase (solid matter, water, oil content) separator is used, and an oil content with little solid content or moisture content can be recovered.
  • SEPTEMBER 2009 / STORAGE TERMINALS; pages 27 to 30 disclose that oil is recovered from crude sludge using a decanter type three-phase separator.
  • JP-A-2004-243300 discloses a method for treating oil-water mixed sludge accumulated in a crude oil tank or the like.
  • an organic system is added to the liquid content.
  • a method is disclosed in which a polymer flocculant is added to coagulate and precipitate oil suspended in a liquid in a suspended state.
  • centrifugation method using a three-phase separator of the decanter type also the processing speed a large size is about 10 kL / hour, mass deposited in large tanks (typically 2000 m 3 or more) time to process Take it.
  • mass deposited in large tanks typically 2000 m 3 or more
  • time to process Take it.
  • it is difficult to feed from a crude oil tank to a centrifuge and in many cases, it is necessary to feed more than twice the amount of sludge in order to stir and mix with fresh crude oil.
  • pretreatment such as heating and injection of an emulsion breaker is necessary, and there is a problem that it is difficult to recover and oil is difficult to recover with a stable quality.
  • an object of the present invention is to provide an oil content recovery method for crude oil sludge that is a simple method, does not require pretreatment such as chemical injection, and has almost no water mixture in the recovered oil content.
  • the present inventor has intensively studied, and as a result, the crude oil sludge contains a water-in-oil emulsion phase, so that water is inevitably mixed in the recovered oil in the conventional centrifugal separation method.
  • Water-in-oil emulsions in crude oil sludge can be easily broken by vacuum evaporation under specific conditions using a vacuum evaporation tank. Evaporated substances and evaporation residues obtained from the vacuum evaporation tank are easily separated from water by a simple separation method.
  • the present inventors have found that oil can be recovered as oil components that do not contain oil, and have completed the present invention.
  • the present invention includes a step of introducing crude oil sludge into the vacuum evaporation tank, and a step II of evaporating light oil and water in the crude oil sludge by heating and stirring the crude oil sludge in the vacuum evaporation tank under vacuum. And step III for cooling the vaporized substance obtained in step II to separate into light oil and water, and step IV for taking out the evaporation residue in the vacuum evaporation tank obtained in step II outside the vacuum evaporation tank And providing a method for recovering oil content in crude oil sludge.
  • the crude oil sludge is evaporated in a vacuum evaporation tank, a strong water-in-oil emulsion can be broken without using chemicals, and light oil from heavy substances and heavy oil from evaporation residues can be destroyed. Each can be recovered efficiently.
  • these recovered oil components hardly contain moisture, they can be recovered by blending with crude oil or the like as they are, and the environmental load can be greatly reduced.
  • the oil recovery rate is high, the needs for oil recovery can be satisfied with the recent rise in crude oil prices.
  • the heavy oil can be recovered and used together with solids or separated into heavy oil and solids and used individually as industrial fuel.
  • sludge accumulated at the bottom of the crude oil tank outdoors
  • sludge accumulated at the bottom of the crude oil tank of the crude oil tanker crude oil sludge exposed to the outdoors
  • crude oil sludge drifting the ocean or after drifting the ocean Crude oil sludge berthed.
  • sludge accumulated on the bottom of an outdoor crude oil tank include, for example, those deposited at a thickness of 500 to 2000 mm on the bottom of the tank during regular inspection after long-term use for 5 to 10 years.
  • Crude oil sludge exposed to the open air is discharged into deserts that are larger than crude oil tanks by the conventional manual method, and is often found in oil producing countries such as the Caspian Sea coast and the Middle East.
  • the crude oil sludge drifting in the ocean or the crude oil sludge docked after drifting includes, for example, an oily pollutant in which crude oil that has flowed into or out of the ocean due to an undersea oil field accident or a tanker accident and seawater are mixed.
  • Such an oil pollutant is generally an emulsion produced by mixing crude oil and seawater, so it is an environmental pollutant called crude oil mousse.
  • crude oil mousse Compared with crude oil sludge accumulated in a crude oil tank, Although it has the same or similar composition, it has a high oil content and a low solid content.
  • Crude oil sludge contains asphaltenes, coke-like substances, oil and water.
  • the oil content contained in the crude oil sludge is not particularly limited and is usually 20 to 80% by weight. Crude oil sludge may be diluted with crude oil.
  • a coke-like substance is also called a coke precursor, and is a solid substance in which asphaltenes are condensed.
  • the water content in the crude oil sludge is usually 10 to 30% by weight.
  • Other substances contained in the crude oil sludge include those in which the wax content in the crude oil crystallizes and settles due to a decrease in temperature or the like, or inorganic substances such as iron and sand.
  • the amount of solids including asphaltene and coke is the remainder excluding oil and moisture.
  • Asphaltenes are a general term for petroleum components that are insoluble in n-hexane and soluble in toluene, and are solid components in crude oil alone. Asphaltenes include those that settle as solid particles and become sludge, and those that form an emulsion together with heavy components such as resin and moisture to settle and sludge.
  • Asphaltenes that settle as solid particles are those in which crude asphaltene particles are covered with resin (heavy oil) and exist stably in a colloidal form, mixed with different oil types such as light oil. In other cases, the resin is detached from the periphery of the asphaltenes due to a thermal history and settled as solid particles.
  • crude oil sludge contains about 10 to 30% by weight of water regardless of the crude oil type.
  • asphaltenes form a water-in-oil (W / O) emulsion that is stable and does not phase-separate with heavy components such as resins and moisture.
  • This water-in-oil (W / O) emulsion is stable and does not phase separate because the film formed around the water droplets is stable. This is because the asphaltene is three-dimensionally cross-linked and the resin is solvated.
  • This emulsion phase is extremely stable and is the most troublesome component in treating crude oil sludge and does not disappear by centrifugation or the like.
  • crude oil sludge is a complex mixture of asphaltene particles, coke-like substances, water-in-oil emulsion, wax crystallized product, etc., and interacts with each other such as aggregation, emulsion, and gelation.
  • crude oil sludge is deposited at the bottom of the tank, for example, it is mixed with oil, so what method should be used to separate the crude oil sludge from the oil when discharging it to the outside of the tank?
  • the oil and sludge are mixed in order to provide fluidity, and the oil is generally contained in a large amount such as 80% by weight at maximum.
  • Table 1 the properties of crude oil sludge accumulated in crude oil tanks of petroleum companies are shown in Table 1.
  • the heptane-insoluble fraction is soluble in the fraction (oil) up to the resin, and asphaltene is insoluble.
  • the benzene insoluble matter is soluble up to asphaltenes, and the insoluble matter is mud moisture, minerals and coke-like substances.
  • the coke-like substance is a main component of benzene insoluble matter.
  • the oil content is a calculated value, which is 100- (heptane insoluble content)-(water content), and the asphaltene is a calculated value, (heptane insoluble content)-(benzene insoluble content).
  • Step I is a step of introducing crude oil sludge into a vacuum evaporation tank.
  • reference numeral 21 denotes a crude oil sludge accumulated at the bottom of the crude oil tank transferred from the crude oil tank, a crude oil sludge left unattended in the field, and an oily pollutant that drifts or shores in the ocean (crude oil mousse). ) Are collected and transferred and stored in the crude oil sludge storage tank 2.
  • crude oil sludge and the like deposited on the bottom of these crude oil tanks may be directly transferred to the vacuum evaporation tank.
  • the method of introducing the crude oil sludge into the vacuum evaporation tank is not particularly limited, and a method of automatically conveying the crude oil sludge 21 heated by the heater 22 and having fluidity by the screw pump 3 or the like is mentioned.
  • Step II is a step of evaporating light oil and water in the crude oil sludge 21 by heating and stirring the crude oil sludge in the vacuum evaporation tank 1 under vacuum.
  • the vacuum evaporation method is used for drying waste containing a large amount of water, such as waste food or excess sludge, or for obtaining dry food.
  • a decompression process such as distillation of petroleum under reduced pressure using a vacuum distillation apparatus or the like is also known. Both are aimed at efficient evaporation with reduced boiling points of water and oil under reduced pressure.
  • the present invention aims to break the emulsion in the raw material, and is an operation in which oil is contained in the evaporating substance and the evaporation residue, respectively, which is greatly different from the conventional vacuum evaporation method.
  • the vacuum evaporation tank 1 having the stirring blades 11 is preferable in that the crude oil sludge can be stirred uniformly.
  • the vacuum evaporation tank 1 has means for heating the crude oil sludge in the vacuum evaporation tank 1 to a constant temperature.
  • the vacuum evaporation tank 1 has an outer heating space (jacket) 12 and is heated through steam 9 generated in a boiler.
  • shaft of the stirring blade 11 may be made into a hollow structure, and the vapor
  • the vacuum evaporation tank 1 has decompression means such as a vacuum pump 7 for decompressing the inside of the tank.
  • the decompression means is not limited to a vacuum pump, and for example, an ejector can be used.
  • the vacuum evaporation tank 1 has a crude oil sludge inlet 13, an evaporated substance outlet 14 connected to the aggregator 4, and an evaporation residue outlet 15 connected to the heavy oil separator 8.
  • symbol E 1 indicates the exhaust of the vacuum pump.
  • the inlet valve 16 and the distillation residue take-off valve 17 of the vacuum evaporation tank 1 are closed, and the condenser 4 and the light oil separator 6 are sealed in the system, and the vacuum pump 7 is operated to evacuate the system. Reduce pressure. Further, steam flows through the outer heating space 12 of the vacuum evaporation tank 1 to heat the crude oil sludge 21.
  • the heating and vacuum conditions are such that the evaporated substance of the crude oil sludge 21 contains moisture and some oil.
  • Some oil components are light oil components that evaporate with the evaporation of moisture.
  • the light oil has a boiling point of up to 250 ° C. under atmospheric pressure and particularly up to 200 ° C. under atmospheric pressure.
  • Specific examples of the heating and vacuum conditions include a heating temperature of 70 to 150 ° C., preferably 70 to 130 ° C., and a degree of vacuum (gauge pressure) of ⁇ 80 to ⁇ 100 KPa, preferably a degree of vacuum (gauge pressure) of ⁇ 90 to ⁇ 100 KPa.
  • the amount of light oil to be evaporated varies depending on the amount of light oil contained in the crude oil sludge and cannot be determined unconditionally. However, it is approximately 5% by weight or more, preferably 10% by weight to the oil content of the crude oil sludge. 50% by weight. If the amount of the light oil to be evaporated is too small, the evaporation of water becomes insufficient and the emulsion may not be completely extinguished. On the other hand, when the amount is too large, the heating temperature and the degree of vacuum are increased more than necessary, which is not efficient. On the other hand, if the lower limit value of the amount of light oil to be evaporated is the above value, the water is sufficiently evaporated and the emulsion can be completely extinguished.
  • the stirring of the crude oil sludge in the step II is carried out in order to uniformly heat and promote the evaporation of the evaporated substance in the crude oil sludge.
  • the stirring speed is not particularly limited, but may be about 2 to 30 revolutions / minute. With such a stirring speed, the evaporation of the evaporating substance in the crude oil sludge can be sufficiently promoted.
  • step II with the heating and decompression of the vacuum evaporation tank 1, evaporation of light oil such as gasoline in the crude oil sludge starts, and the water forming the emulsion also evaporates. The emulsion disappears due to the evaporation of moisture.
  • Step III is a step in which the evaporated substance obtained in Step II is cooled and separated into light oil and water.
  • a known condenser 4 may be used for cooling the evaporating substance.
  • the refrigerant 5 for cooling the condenser 4 is not particularly limited, and examples thereof include water such as seawater and industrial water and known refrigerants other than water.
  • the condensed material condensed by the condenser 4 is separated into a light oil component and water by stationary separation in the light oil component separator 6, and the light oil component is recovered.
  • the light oil separator 6 can use, for example, a known gravity type oil-water separation.
  • the light oil separator 6 of this example is divided into two chambers by a baffle plate 61 having a predetermined height lower than the internal height, and allows the condensed material 621 to flow into one chamber 62.
  • the condensate 621 flowing into the chamber 62 is a mixture of light oil and water and does not become an emulsion, but is completely separated vertically.
  • Light oil components having a specific gravity lighter than water, which is statically separated in one chamber 62 flow into the other chamber 63 by overflowing from the chamber 62. For this reason, the light oil component 622 recovered in the other chamber 63 is hardly mixed with water, and is usually 0.5% by weight or less, particularly 0.3% by weight or less, and further 0.1% by weight or less. Amount.
  • the light oil component 622 accumulated in the chamber 63 is recovered from the light oil component outflow pipe 65 (reference numeral P 1 in FIG. 1 ).
  • the separated water remaining in one chamber 62 may be drained by opening the drain valve 64 (symbol P 2 in FIG. 1).
  • the light oil separator 6 may have a one-chamber structure without a baffle plate.
  • a light oil recovery pipe or the like may be installed near the center of the light oil separator 6 in the height direction. Steps II and III proceed almost simultaneously.
  • the II process is completed when the evaporation of the water in the crude oil sludge almost stops and the operation of the vacuum pump 7 is stopped. Whether or not the evaporation of moisture in the crude oil sludge has been stopped can be determined by observing the level gauge of the light oil content separator 6. That is, when the oil-water interface (water level) of the liquid level gauge does not change with time, it can be determined that the evaporation of moisture has stopped. Further, by observing the rising tendency of the temperature in the vacuum evaporation tank 1, it can be determined that the evaporation of moisture has stopped. That is, in the vicinity of the end of the step II, the evaporation substance in the vacuum evaporation tank 1 decreases, and the heating proceeds while the internal temperature of the vacuum evaporation tank 1 rises.
  • the evaporation residue in the vacuum evaporation tank 1 consists of a solid content and heavy oil content containing asphaltenes and coke-like substances, and the emulsion in the evaporation residue disappears and contains almost no water.
  • the heavy oil is an oil that is heavier than the light oil in the evaporated substance.
  • the evaporation residue after Step II is high temperature and has sufficient fluidity. After completion of step II and step III, step IV is performed.
  • Step IV is a step of taking out the evaporation residue in the vacuum evaporation tank obtained in Step II, and is preferably a step of separating the extracted evaporation residue into a heavy oil and a solid residue. .
  • the valve 17 installed in the middle of the pipe connecting the vacuum evaporation tank 1 and the heavy oil separator 8 may be opened. Thereby, the evaporation residue in the vacuum evaporation tank 1 flows into the heavy oil separator 8 by gravity. That is, the evaporation residue in the vacuum evaporation tank 1 is taken out of the vacuum evaporation tank in a fluidized state.
  • the evaporation residue is separated into an oil and a solid in the heavy oil separator 8.
  • the heavy oil separator 8 is not particularly limited as long as it can separate a mixture (fluid) of oil and solids by standing, and a known separator can be used.
  • the inside of the heavy oil separator 8 is divided into three chambers by two baffle plates 81 and 82 that are lower than the inner height and different in height, and three chambers 83, 84, 85 having different heights are divided. Are sequentially adjacent. That is, the evaporation residue 831 flows into the chamber 83 having a height.
  • the evaporation residue that has flowed into the chamber 83 is a mixture of heavy oil and solids, and since there is no moisture, there is no emulsion and it is completely separated vertically.
  • the heavy oil component that has been allowed to stand and separate in the chamber 83 and a part of the solid content flow into the adjacent chamber 84 as it overflows from the chamber 83.
  • the heavy oil that has been allowed to stand and separate in the chamber 84 flows into the adjacent chamber 85 as it overflows from the chamber 84.
  • the heavy oil recovered in the most downstream chamber 85 contains almost no moisture, and is usually 1.5% by weight or less, particularly 1.0% by weight or less, and further 0.5% by weight or less. It is.
  • the heavy oil collected in the chamber 85 is recovered from the heavy oil outflow pipe 87 (reference numeral P 3 in FIG. 1).
  • the solid content after separation remaining in the chamber 83 may be discharged by opening the discharge valve 86 (code P 4 in FIG. 1).
  • the solid content contains asphaltene and heavy oil and can be used as a fuel. If the solid content is used as boiler fuel for generating the heating vapor in the vacuum evaporation tank 1, the oil recovery cost can be reduced.
  • the heavy oil separator 8 is not limited to the above three chambers, and may be one chamber, two chambers, or four or more chambers. When the heavy oil separator 8 has one chamber, a heavy oil recovery pipe or the like may be installed in the vicinity of the center of the heavy oil separator 8 in the height direction. If it is required that the remaining amount of solids in the heavy oil is very small, the heavy oil and solids mixture can be further separated by a filter or centrifuge using a metal filter. Also good.
  • the present invention there are a step of recovering the light oil separated in the step III and a step of recovering the heavy oil separated in the step IV. That is, the light oil separated and recovered in the step III and the heavy oil separated and recovered in the step IV are mixed and recovered, or individually recovered without mixing.
  • the recovered mixed oil or light oil and heavy oil may be returned to, for example, a crude oil tank.
  • the oil recovery method of the present invention since no chemicals are used, processing such as chemical recovery is unnecessary, and the environmental burden can be greatly reduced. In addition, the need for oil recovery can be satisfied with the recent rise in crude oil prices.
  • crude sludge having a low solid content such as crude oil mousse
  • the evaporation residue in the vacuum evaporation tank is simply taken out of the vacuum evaporation tank as it is in the IV process. Since crude mousse has a high oil content and a low solid content, it is efficient to recover the solid content and heavy oil without separating them. For example, the recovered heavy oil containing a small amount of solids may be returned to the crude oil tank.
  • the oil recovery method in the crude oil sludge of the present invention is a continuous process or a discontinuous process.
  • the continuous process is a method of continuously carrying out the steps I to IV described above, and some of the steps may be performed simultaneously, for example, steps II and III.
  • a discontinuous process means that there is a discontinuous part (idle time) that cannot be said to be continuous, for example, at one or more between steps I and II, between steps II and III, and between steps II and IV. Say how to do.
  • An all discontinuous process refers to a batch process. Either the continuous process or the discontinuous process has the effect of the present invention.
  • Step I Crude oil sludge fluidized by heating is continuously charged into the vacuum evaporation tank 1 by a screw pump 3 or the like.
  • Step II the evaporation of moisture and light oil continuously proceeds (step II), and the moisture and light oil are continuously sent to the condenser 4.
  • step III the evaporated substance obtained in the step II is continuously cooled and condensed, and the light oil component and water are continuously separated in the light oil component separator 6 and discharged to the outside.
  • the evaporation residue is continuously discharged from the vacuum evaporation tank 1. Further, when the separation step is performed in the IV step, the continuously discharged evaporation residue is also continuously separated into a heavy oil component and a solid component by the heavy oil separator 8.
  • the crude oil sludge inlet 13 and the evaporation residue outlet 15 to the vacuum evaporation tank 1 should be installed at a site as far as possible (particularly horizontal distance). It is preferable in that it is possible to prevent the crude oil sludge being charged from being short-circuited and mixed into the evaporation residue and discharged from the vacuum evaporation tank 1 while being insufficiently evaporated.
  • the processing retention time (retention time) of the crude oil sludge in the vacuum evaporation tank 1 varies depending on the operating conditions such as the degree of vacuum and temperature, and therefore cannot be determined in general. This is preferable in that vacuum evaporation is performed.
  • the recovery rate of the total oil content from the crude oil sludge that is, the total oil content with respect to the oil content in the raw material charged in the vacuum evaporation tank is almost 100%. Therefore, it can be recovered at approximately 98%.
  • the water content in the total oil which is the sum of the recovered light oil and heavy oil, is usually less than 1.0% by weight, preferably 0.5% by weight or less.
  • the recovered oil may be recovered as a mixture of light oil and heavy oil, or the heavy oil may be recovered as a mixture together with the solid. A mixture of heavy oil and solids can be used as an industrial fuel.
  • a vacuum evaporation tank for testing with the following specifications, a light oil separator and a heavy oil separator, each with a simple chamber separator, and recovering oil in crude oil sludge A under the following operating conditions went. That is, the crude oil sludge A was introduced into the vacuum evaporation tank A and heated and stirred under vacuum to evaporate the light oil and water in the crude oil sludge A (Step I and Step II). Next, the evaporated substance was cooled and separated into light oil and water, and the light oil was recovered (step III).
  • Vacuum evaporation tank and operating conditions ⁇ Vacuum evaporation tank A shown in FIG. ⁇ Average rotation speed of stirring blades: 20 rotations / minute ⁇ Vacuum degree: ⁇ 96 kPa, heating temperature (raw material temperature): 80 to 120 ° C. Evaporative material temperature (condenser inlet temperature): 50 to 85 ° C ⁇ Batch treatment: Raw material 47.8 kg, treatment for 2 hours ⁇ Crude oil sludge A: Moisture 22.9 wt%, oil content 29.3% wt, solid content 47.8 wt% (Related equipment) ⁇ Heating means: Jacket system with steam heating from outside ⁇ Vacuum pump; Water seal type ⁇ Condenser: Cooling water used
  • Example 2 The same method as in Example 1 was performed except that the following vacuum evaporation tank and operating conditions were used. As a result, 5.1% by weight of light oil having a specific gravity of 0.790 was recovered from the light oil separator. The water content in this light oil was 0.1% by weight or less. On the other hand, 13.1% by weight of heavy oil was recovered from the heavy oil separator, and 60.1% by weight of separation residue was recovered. The water content in the heavy oil was 1.0% by weight. The recovery rate as a liquid oil from crude oil sludge B was 58% by weight (18.2% by weight / 31.6% by weight). In addition, a part of heavy oil content is contained in the separation residue, and if the solid content or a mixture of the solid content and the heavy oil is used as the fuel, the recovery rate as an energy source is close to 100%.
  • Vacuum evaporation tank and operating conditions ⁇ Vacuum evaporation tank B shown in Fig.1 ⁇ Average speed of stirring blades: 20 revolutions / minute ⁇ Vacuum degree: ⁇ 100 kPa, heating temperature (raw material temperature): 75 to 97 ° C. ⁇ Evaporation substance temperature (condenser inlet temperature): 45-50 °C ⁇ Batch treatment: Raw material 41.2 kg, treatment for 5 hours ⁇ Crude oil sludge B: Moisture 20.4 wt%, oil content 31.6 wt%, solid content 48.0 wt%
  • Example 2 The same method as in Example 1 was performed except that the following vacuum evaporation tank and operating conditions were used. As a result, 9.2% by weight of light oil was recovered from the light oil separator. The water content in this light oil was 0.1% by weight or less. On the other hand, 13.4% by weight of heavy oil was recovered from the heavy oil separator, and 56.2% by weight of separation residue was recovered. The water content in the heavy oil was 1.0% by weight. The recovery rate as a liquid oil from crude oil sludge C was 64% by weight (22.6% by weight / 35.3% by weight). In addition, a part of heavy oil content is contained in the separation residue, and if the solid content or a mixture of the solid content and the heavy oil is used as the fuel, the recovery rate as an energy source is close to 100%.
  • Vacuum evaporation tank and operating conditions ⁇ Vacuum evaporation tank A shown in FIG. ⁇ Average rotation speed of stirring blades: 20 rotations / minute ⁇ Vacuum degree: ⁇ 94.3 kPa, heating temperature (temperature in the tank): 124.9 ° C. ⁇ Evaporation substance temperature (condenser inlet temperature): 58-80 °C ⁇ Batch treatment: Raw material 44.7 kg, treatment for 2 hours ⁇ Crude oil sludge C: Moisture 21.0 wt%, oil content 35.3% wt, solid content 43.7 wt%
  • the recovered oil content hardly contains any water, it can be recovered by blending it with crude oil or the like as it is.
  • the amount of crude oil sludge accumulated in a huge crude oil tank over a long period of time is large, and the oil recovered from it becomes a valuable resource under the recent rise in crude oil prices.
  • secondary processing such as chemical processing becomes unnecessary, and the environmental load can be reduced.
  • the oil content recovery method of the present invention can treat such an oil pollutant as it is without using chemicals and can be separated into an oil content and a solid content, thereby reducing the waste treatment burden, Contributes greatly to global environmental conservation.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Wood Science & Technology (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Production Of Liquid Hydrocarbon Mixture For Refining Petroleum (AREA)
  • Treatment Of Sludge (AREA)

Abstract

Provided are: a first step for introducing crude oil sludge into a vacuum vaporizing chamber (1); a second step for heating the crude oil sludge in the vacuum vaporizing chamber (1), stirring in a vacuum, and vaporizing the water and light oil fraction in the crude oil sludge; a third step for separating the water and light oil fraction by cooling the vaporized material obtained in the second step; and a fourth step for removing the vaporization residue in the vacuum vaporizing chamber (1) obtained in the second step from the vacuum vaporizing chamber (1), and separating the heavy oil fraction and the solid residue. Using this simple method, the oil fraction of the crude oil sludge can be recovered without requiring chemical injection or another similar pretreatment, and with substantially no water being admixed with the recovered oil fraction.

Description

原油スラッジ中の油分回収方法Oil recovery method in crude oil sludge
 本発明は、例えば、原油タンク底部等に堆積した原油スラッジ中の油分回収方法に関するものである。 The present invention relates to a method for recovering oil content in crude oil sludge accumulated at the bottom of a crude oil tank, for example.
 原油タンク等に堆積する原油スラッジに含まれる油分は通常、30~80重量%程度であり、油分の回収ニーズは大きい。原油スラッジの処理方法及び処理技術としては、COW(Crude
Oil Washing)法、温水洗浄法、薬品処理法、マニュアル法及び遠心分離法等が挙げられる。
Oil contained in crude oil sludge accumulated in a crude oil tank or the like is usually about 30 to 80% by weight, and there is a great need for oil recovery. Crude sludge treatment methods and treatment technologies include COW (Crude
Oil Washing) method, warm water washing method, chemical treatment method, manual method, and centrifugal separation method.
 COW法は、原油を概ね60℃程度に加熱し、加圧して噴射ノズルによりタンク底部に堆積するスラッジを粉砕、溶解させて他のタンクに移送するものである。短期間に原油スラッジを処理でき実績も多いものの、移送先で再度スラッジの堆積が生じる。このため、原油スラッジのたらい回し的な処方ともいえる。COW法は、根こそぎスラッジ分を強制攪拌して一時的に流動性を持たせて他のタンクに回収する方法のため、タンク外にスラッジを搬出しないメリットはあるものの、前述のごとくスラッジの再沈降の問題が発生して本質的に問題解決していない。なお、実開平6-81649号公報には、COW法で使用する液体噴射装置が開示されている。 The COW method heats crude oil to approximately 60 ° C., pressurizes it, crushes and dissolves sludge accumulated at the bottom of the tank with an injection nozzle, and transfers it to another tank. Although crude sludge can be processed in a short period of time and has a lot of results, sludge is deposited again at the destination. For this reason, it can be said that it is a prescription for turning crude oil sludge. The COW method is a method of forcibly stirring uprooted sludge to make it temporarily fluid and recovering it to another tank, so there is a merit that sludge is not carried out of the tank. The problem has occurred and the problem is not essentially solved. Japanese Utility Model Laid-Open No. 6-81649 discloses a liquid ejecting apparatus used in the COW method.
 温水洗浄法は、温水で原油スラッジを溶解、浮上させる工法で、比較的安全な処理法であるが、大量の温水を必要とするためコストが嵩み、温水では溶解しない油分が回収できず、攪拌により生じるエマルジョン、大量の廃水処理が必要となるなど種々の問題があり、最近ではあまり用いられない。 The hot water washing method is a method that dissolves and floats crude sludge with hot water, and is a relatively safe treatment method, but it requires a large amount of hot water, so it is expensive, and oil that does not dissolve in hot water cannot be recovered. There are various problems such as emulsion generated by agitation and treatment of a large amount of waste water, and it is not so often used recently.
 薬品処理法は、スラッジを溶解させる薬剤(ケミカル)を使用するものであるが、加温や攪拌操作などが必要になること、溶解効果が限定的であること、費用が嵩むこと等の理由により最近ではほとんどおこなわれない。 The chemical treatment method uses a chemical that dissolves sludge, but for reasons such as requiring heating and stirring operations, limited dissolution effects, and increased costs. This is rarely done recently.
 マニュアル法は、作業員がタンク内に入り、人力あるいは自動ショベルカーのようなものでタンク外に排出する方法で古くからおこなわれており、現在でも実施しているところも多い。近年の健康、安全及び地球環境保全(HSE)、とりわけ安全性の問題がある。また排出した原油スラッジの油分を回収されるものではないという問題がある。 The manual method has been practiced for a long time by a method in which an operator enters the tank and discharges it outside the tank with a manual or automatic excavator, and there are many places where it is still implemented. There are health, safety and global environment conservation (HSE) in recent years, especially safety issues. There is also a problem that the oil content of the discharged crude oil sludge is not recovered.
 上記のいずれの方法も、原油スラッジ中の油分の回収という点では、大きな問題を抱えており、有効な方法とは言い難い。この点、遠心分離法は、例えばデカンター型の3相(固形物、水、油分)分離機を用いるもので、固形分や水分の混在が少ない油分を回収できる点で有望な方法である。SEPTEMBER 2009/STORAGE TERMINALS;第27頁~第30頁には、デカンター型の3相分離機を使用して、原油スラッジから油分を回収することが開示されている。また、特開2004-243300号公報には、原油タンク等に蓄積した、油水混合スラッジの処理方法に関して、スラッジを遠心分離機で、固形分と液体分に分離した後、液体分に有機系の高分子凝集剤を添加し、液体中に懸濁状態で浮遊している油分を凝集沈殿させる方法が開示されている。 Any of the above methods has a big problem in terms of recovery of the oil content in the crude oil sludge, and is not an effective method. In this respect, the centrifugal separation method is a promising method in that, for example, a decanter type three-phase (solid matter, water, oil content) separator is used, and an oil content with little solid content or moisture content can be recovered. SEPTEMBER 2009 / STORAGE TERMINALS; pages 27 to 30 disclose that oil is recovered from crude sludge using a decanter type three-phase separator. JP-A-2004-243300 discloses a method for treating oil-water mixed sludge accumulated in a crude oil tank or the like. After the sludge is separated into a solid content and a liquid content by a centrifugal separator, an organic system is added to the liquid content. A method is disclosed in which a polymer flocculant is added to coagulate and precipitate oil suspended in a liquid in a suspended state.
実開平6-81649号公報Japanese Utility Model Publication No. 6-81649 特開2004-243300号公報(請求項1)JP 2004-243300 A (Claim 1)
 しかしながら、デカンター型の3相分離機を使用した遠心分離法は、大型のものでも処理速度は10kl/時程度であり、大型タンクに堆積する大量(通常は2000m以上)の処理には時間がかかる。また、原油タンクから遠心分離機にフィードする方法が難しく、多くの場合、フレッシュ原油などで攪拌混合させるため、スラッジ量の2倍以上の量をフィードしなければならない。また、加温やエマルジョンブレーカーの注入等の前処理が必要であり、且つ運転が難しく安定した品質で油分を回収することが難しいという問題がある。また、固形スラッジ、油分及び水分の完全分離が困難であり、回収した油分には固形分や多くの場合少なくとも2%程度の水が残存するという問題がある。このため、簡易な方法であって、原油スラッジの希釈等やエマルジョンブレーカーの注入等の前処理を必要とせず、直接の処理が可能であって、回収油分に水の混入がほとんどない原油スラッジの油分回収方法が望まれていた。 However, centrifugation method using a three-phase separator of the decanter type, also the processing speed a large size is about 10 kL / hour, mass deposited in large tanks (typically 2000 m 3 or more) time to process Take it. In addition, it is difficult to feed from a crude oil tank to a centrifuge, and in many cases, it is necessary to feed more than twice the amount of sludge in order to stir and mix with fresh crude oil. In addition, pretreatment such as heating and injection of an emulsion breaker is necessary, and there is a problem that it is difficult to recover and oil is difficult to recover with a stable quality. In addition, it is difficult to completely separate solid sludge, oil, and moisture, and there is a problem that the recovered oil contains solids and, in many cases, at least about 2% of water. For this reason, it is a simple method that does not require pretreatment such as dilution of crude oil sludge and injection of emulsion breaker, etc., and can be directly treated, and the crude oil sludge with little water contamination in the recovered oil An oil recovery method has been desired.
 従って、本発明の目的は、簡易な方法であって、薬剤注入等の前処理を必要とせず、回収油分に水の混入がほとんどない原油スラッジの油分回収方法を提供することにある。 Therefore, an object of the present invention is to provide an oil content recovery method for crude oil sludge that is a simple method, does not require pretreatment such as chemical injection, and has almost no water mixture in the recovered oil content.
 かかる実情において、本発明者は鋭意検討を行った結果、原油スラッジには、油中水滴型エマルジョン相を含むため、従来の遠心分離法等では、どうしても回収油分中に水が混入してしまうこと、原油スラッジ中の油中水滴型エマルジョンは、真空蒸発槽を使用した特定条件下での真空蒸発により、容易に破壊できること、真空蒸発槽から得られる蒸発物質と蒸発残渣は簡易な分離方法により水分を含まない油分としてそれぞれ回収できること等を見出し、本発明を完成するに至った。 In such a situation, the present inventor has intensively studied, and as a result, the crude oil sludge contains a water-in-oil emulsion phase, so that water is inevitably mixed in the recovered oil in the conventional centrifugal separation method. Water-in-oil emulsions in crude oil sludge can be easily broken by vacuum evaporation under specific conditions using a vacuum evaporation tank. Evaporated substances and evaporation residues obtained from the vacuum evaporation tank are easily separated from water by a simple separation method. The present inventors have found that oil can be recovered as oil components that do not contain oil, and have completed the present invention.
 すなわち、本発明は、原油スラッジを真空蒸発槽に導入する1工程と、真空蒸発槽内の原油スラッジを加熱及び真空下にて撹拌して、原油スラッジ中の軽質油分と水を蒸発させるII工程と、該II工程で得られる蒸発物質を冷却して軽質油分と水とに分離するIII工程と、該II工程で得られる真空蒸発槽内の蒸発残渣を、該真空蒸発槽外に取り出すIV工程と、を有することを特徴とする原油スラッジ中の油分回収方法を提供するものである。 That is, the present invention includes a step of introducing crude oil sludge into the vacuum evaporation tank, and a step II of evaporating light oil and water in the crude oil sludge by heating and stirring the crude oil sludge in the vacuum evaporation tank under vacuum. And step III for cooling the vaporized substance obtained in step II to separate into light oil and water, and step IV for taking out the evaporation residue in the vacuum evaporation tank obtained in step II outside the vacuum evaporation tank And providing a method for recovering oil content in crude oil sludge.
 本発明によれば、原油スラッジを真空蒸発槽で真空蒸発させるため、薬剤を使用することなく、強固な油中水滴型エマルジョンを破壊でき、蒸発物質から軽質油分を、蒸発残渣から重質油分をそれぞれ効率よく回収できる。また、これらの回収油分は、いずれも水分をほとんど含まないため、そのまま原油等にブレンドして回収することができると共に、環境負荷を大きく低減できる。また、油分の回収率が高いため、近年の原油高騰の折り、油分回収ニーズを満足することができる。また、重質油分は回収して固形物と共に、あるいは重質油と固形分に分離して各々個別に工業燃料として使用できる。 According to the present invention, since the crude oil sludge is evaporated in a vacuum evaporation tank, a strong water-in-oil emulsion can be broken without using chemicals, and light oil from heavy substances and heavy oil from evaporation residues can be destroyed. Each can be recovered efficiently. In addition, since these recovered oil components hardly contain moisture, they can be recovered by blending with crude oil or the like as they are, and the environmental load can be greatly reduced. In addition, since the oil recovery rate is high, the needs for oil recovery can be satisfied with the recent rise in crude oil prices. Further, the heavy oil can be recovered and used together with solids or separated into heavy oil and solids and used individually as industrial fuel.
原油スラッジから油分を回収するフロー図である。It is a flow figure which collects oil content from crude oil sludge.
 本発明において、原油スラッジとしては、屋外の原油タンク底部に堆積したスラッジ、原油タンカーの原油タンク底部に堆積したスラッジ、野外に野晒しの原油スラッジ、海洋を漂流する原油スラッジまたは海洋を漂流後、着岸した原油スラッジが挙げられる。屋外の原油タンク底部に堆積したスラッジとしては、例えば5年~10年の長期間使用した後の定期点検の際、タンク底部に500~2000mmの厚さで堆積したものが挙げられる。野外に野晒しの原油スラッジとしては、従来のマニュアル法により原油タンクより広大な砂漠等に排出されたものであり、特にカスピ海沿岸や中東などの産油国で多く見られるものである。海洋を漂流する原油スラッジ又は漂流後、着岸した原油スラッジとしては、例えば、海底油田事故やタンカー事故により海洋に流出又は着岸した原油と海水が混合した油濁汚染物質が挙げられる。このような油濁汚染物質は、一般的には原油と海水が混合して生成するエマルジョンであるため、原油ムースと称される環境汚染物質であり、原油タンクに堆積した原油スラッジと比べると、同じ又は類似組成ではあるが、油分が多く、固形分が少ない。 In the present invention, as the crude oil sludge, sludge accumulated at the bottom of the crude oil tank outdoors, sludge accumulated at the bottom of the crude oil tank of the crude oil tanker, crude oil sludge exposed to the outdoors, crude oil sludge drifting the ocean or after drifting the ocean, Crude oil sludge berthed. Examples of sludge accumulated on the bottom of an outdoor crude oil tank include, for example, those deposited at a thickness of 500 to 2000 mm on the bottom of the tank during regular inspection after long-term use for 5 to 10 years. Crude oil sludge exposed to the open air is discharged into deserts that are larger than crude oil tanks by the conventional manual method, and is often found in oil producing countries such as the Caspian Sea coast and the Middle East. The crude oil sludge drifting in the ocean or the crude oil sludge docked after drifting includes, for example, an oily pollutant in which crude oil that has flowed into or out of the ocean due to an undersea oil field accident or a tanker accident and seawater are mixed. Such an oil pollutant is generally an emulsion produced by mixing crude oil and seawater, so it is an environmental pollutant called crude oil mousse. Compared with crude oil sludge accumulated in a crude oil tank, Although it has the same or similar composition, it has a high oil content and a low solid content.
 原油スラッジは、アスファルテン、コーク状物質、油分及び水を含有するものである。原油スラッジに含まれる油分としては、特に制限されず、通常、20~80重量%である。原油スラッジは原油で希釈されたものであってもよい。コーク状物質は、コーク前駆体とも称されるもので、アスファルテンが縮合した固形物である。また、原油スラッジに含まれる水分としては、通常、10~30重量%である。原油スラッジ中に含まれる他の物質としては、原油中のワックス分が温度低下などで結晶化して沈降したもの、あるいは鉄や砂等の無機物が挙げられる。原油スラッジ中、アスファルテンとコーク状物質を含む固形分の量は、油分と水分を除く残部となる。 Crude oil sludge contains asphaltenes, coke-like substances, oil and water. The oil content contained in the crude oil sludge is not particularly limited and is usually 20 to 80% by weight. Crude oil sludge may be diluted with crude oil. A coke-like substance is also called a coke precursor, and is a solid substance in which asphaltenes are condensed. The water content in the crude oil sludge is usually 10 to 30% by weight. Other substances contained in the crude oil sludge include those in which the wax content in the crude oil crystallizes and settles due to a decrease in temperature or the like, or inorganic substances such as iron and sand. In crude oil sludge, the amount of solids including asphaltene and coke is the remainder excluding oil and moisture.
 アスファルテンは、n-ヘキサンに不溶でトルエンに可溶な石油成分の総称であり、原
油中、単体では固体成分である。アスファルテンは、固体粒子として沈降し、スラッジ化するものと、レジンなどの重質分と水分と共にエマルジョンを形成して沈降し、スラッジ化するものがある。
Asphaltenes are a general term for petroleum components that are insoluble in n-hexane and soluble in toluene, and are solid components in crude oil alone. Asphaltenes include those that settle as solid particles and become sludge, and those that form an emulsion together with heavy components such as resin and moisture to settle and sludge.
 固体粒子として沈降するアスファルテンは、原油中において、アスファルテン粒子がレジン(重質油)で覆われて、コロイド状で安定的に存在したものが、軽質油分等のような異なる油種と混合されたり、あるいは熱的履歴を受けたりして、アスファルテンの周囲からレジンが離脱し、固体粒子として沈降したものである。 Asphaltenes that settle as solid particles are those in which crude asphaltene particles are covered with resin (heavy oil) and exist stably in a colloidal form, mixed with different oil types such as light oil. In other cases, the resin is detached from the periphery of the asphaltenes due to a thermal history and settled as solid particles.
 一方、前記の通り、原油スラッジには、原油種にかかわらず、10~30重量%程度の水分が含まれている。このため、アスファルテンは、レジンなどの重質分、水分と共に、安定で相分離しない油中水滴(W/O)型エマルジョンを形成する。この油中水滴(W/O)型エマルジョンが安定で相分離しないのは、水滴まわりに形成された膜が安定だからである。この膜は、アスファルテンが3次元的に架橋し、それにレジンが溶媒和しているためである。このエマルジョン相は極めて安定であり原油スラッジを処理する上で最もやっかいな成分であり、遠心分離などでは消滅しない。 On the other hand, as described above, crude oil sludge contains about 10 to 30% by weight of water regardless of the crude oil type. For this reason, asphaltenes form a water-in-oil (W / O) emulsion that is stable and does not phase-separate with heavy components such as resins and moisture. This water-in-oil (W / O) emulsion is stable and does not phase separate because the film formed around the water droplets is stable. This is because the asphaltene is three-dimensionally cross-linked and the resin is solvated. This emulsion phase is extremely stable and is the most troublesome component in treating crude oil sludge and does not disappear by centrifugation or the like.
 このように、原油スラッジは、アスファルテン粒子、コーク状物質、油中水滴型エマルジョン、ワックス結晶化物などが複雑に混合し、凝集、エマルジョン、ゲル化などの相互作用を及ぼしあっている。また、原油スラッジは、例えばタンク底部に堆積しているとはいえ、油分と混在しているため、原油スラッジをタンク外に排出する場合には、どのような方法を採ろうが油分と分離させた状態では不可能であり、むしろ流動性を持たせるために油分とスラッジが混合しており、油分が概ね最大で80重量%のように大量に含まれることになる。参考までに石油各社の原油タンクに堆積した原油スラッジの性状を表1に示す。表1中、ヘプタン不溶分は、レジンまでの留分(油分)は可溶であり、アスファルテンは不溶のものである。ベンゼン不溶分は、アスファルテンまでの留分は可溶であり、不溶分は泥水分、無機質及びコーク状物質である。コーク状物質は、ベンゼン不溶分の主成分をなす。なお、トルエン不溶分とベンゼン不溶分は両溶媒がほぼ同じ溶解性を有することからほぼ同じ物質と考えられる。油分は計算値であり、100-(ヘプタン不溶分)-(水分)であり、アスファルテンは計算値であり、(ヘプタン不溶分)-(ベンゼン不溶分)である。 Thus, crude oil sludge is a complex mixture of asphaltene particles, coke-like substances, water-in-oil emulsion, wax crystallized product, etc., and interacts with each other such as aggregation, emulsion, and gelation. In addition, although crude oil sludge is deposited at the bottom of the tank, for example, it is mixed with oil, so what method should be used to separate the crude oil sludge from the oil when discharging it to the outside of the tank? However, the oil and sludge are mixed in order to provide fluidity, and the oil is generally contained in a large amount such as 80% by weight at maximum. For reference, the properties of crude oil sludge accumulated in crude oil tanks of petroleum companies are shown in Table 1. In Table 1, the heptane-insoluble fraction is soluble in the fraction (oil) up to the resin, and asphaltene is insoluble. The benzene insoluble matter is soluble up to asphaltenes, and the insoluble matter is mud moisture, minerals and coke-like substances. The coke-like substance is a main component of benzene insoluble matter. It should be noted that the toluene-insoluble component and the benzene-insoluble component are considered to be substantially the same substance because both solvents have substantially the same solubility. The oil content is a calculated value, which is 100- (heptane insoluble content)-(water content), and the asphaltene is a calculated value, (heptane insoluble content)-(benzene insoluble content).
Figure JPOXMLDOC01-appb-T000001
Figure JPOXMLDOC01-appb-T000001
 次に、本発明の原油スラッジ中の油分回収方法の一例を図1を参照して説明する。I工程は、原油スラッジを真空蒸発槽に導入する工程である。図1中、符号21は原油タンクの底部に堆積する原油スラッジを原油タンクから移送したもの、野外に放置された原油スラッジを移送したもの、海洋に漂流したり着岸した油濁汚染物質(原油ムース)を集積して移送したものであり、原油スラッジ貯留槽2に貯えられる。なお、これら原油タンクの底部に堆積する原油スラッジ等は直接、真空蒸発槽に移送するようにしてもよい。原油スラッジを真空蒸発槽に導入する方法としては、特に制限されないが、加熱器22で加熱して流動性を持たせた原油スラッジ21をスクリューポンプ3などで自動搬送する方法が挙げられる。 Next, an example of a method for recovering the oil content in the crude oil sludge according to the present invention will be described with reference to FIG. Step I is a step of introducing crude oil sludge into a vacuum evaporation tank. In FIG. 1, reference numeral 21 denotes a crude oil sludge accumulated at the bottom of the crude oil tank transferred from the crude oil tank, a crude oil sludge left unattended in the field, and an oily pollutant that drifts or shores in the ocean (crude oil mousse). ) Are collected and transferred and stored in the crude oil sludge storage tank 2. Note that crude oil sludge and the like deposited on the bottom of these crude oil tanks may be directly transferred to the vacuum evaporation tank. The method of introducing the crude oil sludge into the vacuum evaporation tank is not particularly limited, and a method of automatically conveying the crude oil sludge 21 heated by the heater 22 and having fluidity by the screw pump 3 or the like is mentioned.
 II工程は、真空蒸発槽1内の原油スラッジを加熱及び真空下にて撹拌して、原油スラッジ21中の軽質油分と水を蒸発させる工程である。従来、真空蒸発法は、廃食品や余剰汚泥など水分を多量に含む廃物の乾燥、あるいは乾燥食品を得るためなどに使用されている。また、減圧蒸留装置などで石油類を減圧下で蒸留するなどの減圧処理も知られている。いずれも減圧下で水や油分の沸点を下げた効率的な蒸発を目的にしている。これに対して、本発明は、原料中のエマルジョン破壊を目的としており、また、蒸発物質と蒸発残渣にそれぞれ油分を含有させるような運転であり、従来の真空蒸発法とは大きく相違する。 Step II is a step of evaporating light oil and water in the crude oil sludge 21 by heating and stirring the crude oil sludge in the vacuum evaporation tank 1 under vacuum. Conventionally, the vacuum evaporation method is used for drying waste containing a large amount of water, such as waste food or excess sludge, or for obtaining dry food. Further, a decompression process such as distillation of petroleum under reduced pressure using a vacuum distillation apparatus or the like is also known. Both are aimed at efficient evaporation with reduced boiling points of water and oil under reduced pressure. On the other hand, the present invention aims to break the emulsion in the raw material, and is an operation in which oil is contained in the evaporating substance and the evaporation residue, respectively, which is greatly different from the conventional vacuum evaporation method.
 真空蒸発槽1は、撹拌羽根11を有するものが、原油スラッジを均一に撹拌できる点で好ましい。また、真空蒸発槽1は、真空蒸発槽1内の原油スラッジを一定温度に加熱する手段を有する。本例では、真空蒸発槽1は外側加熱空間(ジャケット)12を有し、これにボイラーで発生した蒸気9を通して加熱するようになっている。また、攪拌羽根11の軸を成す回転シャフトの内部を空洞構造とし、その内部にボイラーで発生した蒸気9を通してもよい。これにより、更に伝熱面積を増やすことができる。また、真空蒸発槽1は槽内を減圧にする真空ポンプ7などの減圧手段を有する。減圧手段は真空ポンプに限定されず、例えばエジェクターなども使用できる。また、真空蒸発槽1には、原油スラッジ導入口13、凝集器4と連結する蒸発物質取り出し口14及び重質油分分離器8と連結する蒸発残渣取り出し口15を有する。図1中、符号Eは真空ポンプの排気を示す。 The vacuum evaporation tank 1 having the stirring blades 11 is preferable in that the crude oil sludge can be stirred uniformly. The vacuum evaporation tank 1 has means for heating the crude oil sludge in the vacuum evaporation tank 1 to a constant temperature. In this example, the vacuum evaporation tank 1 has an outer heating space (jacket) 12 and is heated through steam 9 generated in a boiler. Moreover, the inside of the rotating shaft which comprises the axis | shaft of the stirring blade 11 may be made into a hollow structure, and the vapor | steam 9 which generate | occur | produced with the boiler may be passed through the inside. Thereby, a heat transfer area can be increased further. Moreover, the vacuum evaporation tank 1 has decompression means such as a vacuum pump 7 for decompressing the inside of the tank. The decompression means is not limited to a vacuum pump, and for example, an ejector can be used. Further, the vacuum evaporation tank 1 has a crude oil sludge inlet 13, an evaporated substance outlet 14 connected to the aggregator 4, and an evaporation residue outlet 15 connected to the heavy oil separator 8. In FIG. 1, symbol E 1 indicates the exhaust of the vacuum pump.
 I工程後、真空蒸発槽1の入り口弁16及び蒸留残渣取り出し弁17をそれぞれ閉止すると共に、凝縮器4及び軽質油分分離器6までを系内密閉し、真空ポンプ7を稼働して系内を減圧とする。また、真空蒸発槽1の外側加熱空間12に蒸気を流して、原油スラッジ21を加熱する。 After the step I, the inlet valve 16 and the distillation residue take-off valve 17 of the vacuum evaporation tank 1 are closed, and the condenser 4 and the light oil separator 6 are sealed in the system, and the vacuum pump 7 is operated to evacuate the system. Reduce pressure. Further, steam flows through the outer heating space 12 of the vacuum evaporation tank 1 to heat the crude oil sludge 21.
 II工程において、加熱及び真空条件は、原油スラッジ21の蒸発物質中に水分と一部の油分が含まれるような条件とする。一部の油分とは、水分の蒸発と共に蒸発する軽質油分である。軽質油分は、沸点が大気圧下で250℃留分までのものであり、特に大気圧下で200℃留分までのものである。加熱及び真空条件の具体例としては、加熱温度70~150℃、好ましくは70~130℃であり、真空度(ゲージ圧)-80~-100KPa、好ましくは真空度(ゲージ圧)-90~-100KPaである。このような、加熱及び真空条件であれば、原油スラッジ中の水分を確実に蒸発させることができ、エマルジョンを消滅させることができる。また、蒸発物質として水分以外に軽質油分を同伴させたのは、水分を確実に蒸発させることと、エマルジョンを形成しない水と軽質油分は、凝縮後、静置等の手段により容易に且つ確実に分離できるからである。一方、原油スラッジから水分のみを蒸発させることはデリケートな運転が必要となり、例え水分のみを蒸発させたとしても、不可避に混入する微量の軽質油分の除去は容易ではない。 In step II, the heating and vacuum conditions are such that the evaporated substance of the crude oil sludge 21 contains moisture and some oil. Some oil components are light oil components that evaporate with the evaporation of moisture. The light oil has a boiling point of up to 250 ° C. under atmospheric pressure and particularly up to 200 ° C. under atmospheric pressure. Specific examples of the heating and vacuum conditions include a heating temperature of 70 to 150 ° C., preferably 70 to 130 ° C., and a degree of vacuum (gauge pressure) of −80 to −100 KPa, preferably a degree of vacuum (gauge pressure) of −90 to − 100 KPa. Under such heating and vacuum conditions, water in the crude oil sludge can be surely evaporated and the emulsion can be extinguished. Also, the light oil other than water was entrained as an evaporating substance because the water was surely evaporated, and the water and light oil that did not form an emulsion were easily and reliably placed by means such as standing after condensation. This is because they can be separated. On the other hand, evaporating only the moisture from the crude oil sludge requires a delicate operation, and even if only the moisture is evaporated, it is not easy to remove a trace amount of light oil that is inevitably mixed.
 II工程において、蒸発させる軽質油分の量は、原油スラッジ中に含まれる軽質油分の量により異なり一概に決定できないものの、原油スラッジの油分に対して、概ね5重量%以上、好ましくは10重量%~50重量%である。蒸発させる軽質油分の量が少なく過ぎると、水分の蒸発が不十分となり、エマルジョンを完全に消滅させることができない恐れがある。また、多過ぎると、加熱温度や真空度を必要以上に高めることになり、効率的ではない。一方、蒸発させる軽質油分の量の下限値が、上記の値であれば、水分の蒸発が十分となり、エマルジョンを完全に消滅させることができる。 In Step II, the amount of light oil to be evaporated varies depending on the amount of light oil contained in the crude oil sludge and cannot be determined unconditionally. However, it is approximately 5% by weight or more, preferably 10% by weight to the oil content of the crude oil sludge. 50% by weight. If the amount of the light oil to be evaporated is too small, the evaporation of water becomes insufficient and the emulsion may not be completely extinguished. On the other hand, when the amount is too large, the heating temperature and the degree of vacuum are increased more than necessary, which is not efficient. On the other hand, if the lower limit value of the amount of light oil to be evaporated is the above value, the water is sufficiently evaporated and the emulsion can be completely extinguished.
 II工程における原油スラッジの撹拌は、加温を均一に行うと共に、原油スラッジ中の蒸発物質の蒸発を促進するために行なわれる。その撹拌速度(回転速度)としては、特に制限されないが、2回転/分~30回転/分程度でよい。このような撹拌速度であれば、原油スラッジ中の蒸発物質の蒸発を十分に促進することができる。 The stirring of the crude oil sludge in the step II is carried out in order to uniformly heat and promote the evaporation of the evaporated substance in the crude oil sludge. The stirring speed (rotational speed) is not particularly limited, but may be about 2 to 30 revolutions / minute. With such a stirring speed, the evaporation of the evaporating substance in the crude oil sludge can be sufficiently promoted.
 II工程において、真空蒸発槽1の加熱と減圧に伴い、原油スラッジ中のガソリン等の軽質油分の蒸発が始まり、更にはエマルジョンを形成している水分も蒸発する。水分の蒸発離脱により、エマルジョンは消滅する。 In step II, with the heating and decompression of the vacuum evaporation tank 1, evaporation of light oil such as gasoline in the crude oil sludge starts, and the water forming the emulsion also evaporates. The emulsion disappears due to the evaporation of moisture.
 III工程は、II工程で得られる蒸発物質を冷却して軽質油分と水とに分離する工程である。蒸発物質の冷却には、公知の凝縮器4を使用すればよい。凝縮器4の冷却用冷媒5としては、特に制限されず、海水、工業用水等の水及び水以外の公知の冷媒が挙げられる。凝縮器4により凝縮された凝縮物質は、軽質油分分離器6で、静置分離により、軽質油分と水に分離され、軽質油分が回収される。軽質油分分離器6は、例えば公知の重力式油水分離が使用できる。本例の軽質油分分離器6は、内部が内部高さより低い所定高さの邪魔板61で2つ室に分割されたものであり、一方の室62に凝縮物質621を流入させる。室62に流入した凝縮物質621は、軽質油分と水の混合物であり、エマルジョンになることはなく、上下に完全分離する。他方の室63には、一方の室62で静置分離した、比重が水より軽い軽質油分が室62から溢れることで流れ込むようになっている。このため、他方の室63に回収された軽質油分622には水分の混入はほとんどなく、通常は0.5重量%以下、特に0.3重量%以下、更には0.1重量%以下の水分量である。室63に溜まった軽質油分622は、軽質油分流出配管65から回収される(図1中の符号P)。なお、一方の室62に残留する分離後の水は、水切り弁64を開くことで排水(図1中の符号P)すればよい。軽質油分分離器6は、邪魔板のない1室構造のものであってもよい。軽質油分分離器6が1室の場合、軽質油分分離器6の高さ方向の中央部近傍に、軽質油分回収配管などを設置すればよい。II工程とIII工程はほとんど同時に進行する。 Step III is a step in which the evaporated substance obtained in Step II is cooled and separated into light oil and water. A known condenser 4 may be used for cooling the evaporating substance. The refrigerant 5 for cooling the condenser 4 is not particularly limited, and examples thereof include water such as seawater and industrial water and known refrigerants other than water. The condensed material condensed by the condenser 4 is separated into a light oil component and water by stationary separation in the light oil component separator 6, and the light oil component is recovered. The light oil separator 6 can use, for example, a known gravity type oil-water separation. The light oil separator 6 of this example is divided into two chambers by a baffle plate 61 having a predetermined height lower than the internal height, and allows the condensed material 621 to flow into one chamber 62. The condensate 621 flowing into the chamber 62 is a mixture of light oil and water and does not become an emulsion, but is completely separated vertically. Light oil components having a specific gravity lighter than water, which is statically separated in one chamber 62, flow into the other chamber 63 by overflowing from the chamber 62. For this reason, the light oil component 622 recovered in the other chamber 63 is hardly mixed with water, and is usually 0.5% by weight or less, particularly 0.3% by weight or less, and further 0.1% by weight or less. Amount. The light oil component 622 accumulated in the chamber 63 is recovered from the light oil component outflow pipe 65 (reference numeral P 1 in FIG. 1 ). The separated water remaining in one chamber 62 may be drained by opening the drain valve 64 (symbol P 2 in FIG. 1). The light oil separator 6 may have a one-chamber structure without a baffle plate. When the light oil separator 6 has one chamber, a light oil recovery pipe or the like may be installed near the center of the light oil separator 6 in the height direction. Steps II and III proceed almost simultaneously.
 II工程は、原油スラッジ中の水分の蒸発がほぼ止まり、真空ポンプ7の運転を停止することで終了する。原油スラッジ中の水分の蒸発が止まったか否かは、軽質油分分離器6の液面計を観察することで判断できる。すなわち、液面計の油水界面(水面レベル)が時間経過と共に変化しなくなれば、水分の蒸発が止まったと判断できる。また、真空蒸発槽1内の温度の上昇傾向を観察することで、水分の蒸発が止まったと判断できる。すなわち、II工程の終了近傍においては、真空蒸発槽1内の蒸発物質が少なくなる一方で加熱が進行するため、真空蒸発槽1の内部温度が上昇するからである。 The II process is completed when the evaporation of the water in the crude oil sludge almost stops and the operation of the vacuum pump 7 is stopped. Whether or not the evaporation of moisture in the crude oil sludge has been stopped can be determined by observing the level gauge of the light oil content separator 6. That is, when the oil-water interface (water level) of the liquid level gauge does not change with time, it can be determined that the evaporation of moisture has stopped. Further, by observing the rising tendency of the temperature in the vacuum evaporation tank 1, it can be determined that the evaporation of moisture has stopped. That is, in the vicinity of the end of the step II, the evaporation substance in the vacuum evaporation tank 1 decreases, and the heating proceeds while the internal temperature of the vacuum evaporation tank 1 rises.
 真空ポンプ7の運転を停止した後、更に減圧解除弁71を開放して大気を系内に送り、系内を大気圧にする。真空蒸発槽1内の蒸発残渣は、アスファルテンやコーク状物質を含む固形分及び重質油分からなり、該蒸発残渣中のエマルジョンは消滅し、水分をほとんど含まないものである。重質油分とは、蒸発物質中の軽質油分を除くそれより重質の油分である。また、II工程後の蒸発残渣は高温であり、十分な流動性を有している。II工程及びIII工程の終了後、IV工程を実施する。 After the operation of the vacuum pump 7 is stopped, the decompression release valve 71 is further opened to send the atmosphere into the system so that the system is at atmospheric pressure. The evaporation residue in the vacuum evaporation tank 1 consists of a solid content and heavy oil content containing asphaltenes and coke-like substances, and the emulsion in the evaporation residue disappears and contains almost no water. The heavy oil is an oil that is heavier than the light oil in the evaporated substance. Further, the evaporation residue after Step II is high temperature and has sufficient fluidity. After completion of step II and step III, step IV is performed.
 IV工程は、II工程で得られる真空蒸発槽内の蒸発残渣を、該真空蒸発槽外に取り出す工程であり、好ましくは、取り出された蒸発残渣を重質油分と固形残渣に分離する工程である。真空蒸発槽1内の蒸発残渣を真空蒸発槽1外に取り出すには、真空蒸発槽1と重質油分分離器8を接続する配管途中に設置される弁17を開にすればよい。これにより、真空蒸発槽1内の蒸発残渣は、重力により重質油分分離器8に流入する。すなわち、真空蒸発槽1内の蒸発残渣は、流動状態で真空蒸発槽外に取り出される。 Step IV is a step of taking out the evaporation residue in the vacuum evaporation tank obtained in Step II, and is preferably a step of separating the extracted evaporation residue into a heavy oil and a solid residue. . In order to take out the evaporation residue in the vacuum evaporation tank 1 to the outside of the vacuum evaporation tank 1, the valve 17 installed in the middle of the pipe connecting the vacuum evaporation tank 1 and the heavy oil separator 8 may be opened. Thereby, the evaporation residue in the vacuum evaporation tank 1 flows into the heavy oil separator 8 by gravity. That is, the evaporation residue in the vacuum evaporation tank 1 is taken out of the vacuum evaporation tank in a fluidized state.
 蒸発残渣は、重質油分分離器8において、油分と固形分に分離される。重質油分分離器8は、油分と固形分の混合物(流動物)を静置により分離することができるものであれば、特に制限されず、公知の分離器が使用できる。本例では、重質油分分離器8の内部が内部高さより低く且つ高さの異なる2つの邪魔板81、82で3室に分割されており、高低差のある3つの室83、84、85を順次隣接させたものである。すなわち、高さのある室83に蒸発残渣831を流入させる。室83に流入した蒸発残渣は、重質油分と固形分の混合物であり、水分がないため、エマルジョンはなく、上下に完全分離する。隣接する室84には、室83で静置分離した重質油分と一部の固形分が室83から溢れることで流れ込むようになっている。また、隣接する室85には、室84で静置分離した重質油分が室84から溢れることで流れ込むようになっている。最下流側の室85に回収された重質油分には水分の混入はほとんどなく、通常は1.5重量%以下、特に1.0重量%以下、更には0.5重量%以下の水分量である。室85に溜まった重質油分は、重質油分流出配管87から回収される(図1中の符号P)。なお、室83に残留する分離後の固形分は、排出弁86を開くことで排出すればよい(図1中の符号P)。固形分は、アスファルテンや重質油分を含むものであり、燃料して利用できる。固形分を真空蒸発槽1の加熱蒸気を発生させるボイラー燃料として使用すれば、油分回収コストを低減することができる。重質油分分離器8は、上記の3室に限定されず、1室、2室または4室以上であってもよい。重質油分分離器8が1室の場合、重質油分分離器8の高さ方向の中央部近傍に、重質油分回収配管などを設置すればよい。なお、重質油分中の固形分残量が微少となることが要求される場合、重質油分と固形分の混合物を金属フィルター等を使用した濾過器や遠心分離器などにより更に分離処理してもよい。 The evaporation residue is separated into an oil and a solid in the heavy oil separator 8. The heavy oil separator 8 is not particularly limited as long as it can separate a mixture (fluid) of oil and solids by standing, and a known separator can be used. In this example, the inside of the heavy oil separator 8 is divided into three chambers by two baffle plates 81 and 82 that are lower than the inner height and different in height, and three chambers 83, 84, 85 having different heights are divided. Are sequentially adjacent. That is, the evaporation residue 831 flows into the chamber 83 having a height. The evaporation residue that has flowed into the chamber 83 is a mixture of heavy oil and solids, and since there is no moisture, there is no emulsion and it is completely separated vertically. The heavy oil component that has been allowed to stand and separate in the chamber 83 and a part of the solid content flow into the adjacent chamber 84 as it overflows from the chamber 83. In addition, the heavy oil that has been allowed to stand and separate in the chamber 84 flows into the adjacent chamber 85 as it overflows from the chamber 84. The heavy oil recovered in the most downstream chamber 85 contains almost no moisture, and is usually 1.5% by weight or less, particularly 1.0% by weight or less, and further 0.5% by weight or less. It is. The heavy oil collected in the chamber 85 is recovered from the heavy oil outflow pipe 87 (reference numeral P 3 in FIG. 1). Incidentally, the solid content after separation remaining in the chamber 83 may be discharged by opening the discharge valve 86 (code P 4 in FIG. 1). The solid content contains asphaltene and heavy oil and can be used as a fuel. If the solid content is used as boiler fuel for generating the heating vapor in the vacuum evaporation tank 1, the oil recovery cost can be reduced. The heavy oil separator 8 is not limited to the above three chambers, and may be one chamber, two chambers, or four or more chambers. When the heavy oil separator 8 has one chamber, a heavy oil recovery pipe or the like may be installed in the vicinity of the center of the heavy oil separator 8 in the height direction. If it is required that the remaining amount of solids in the heavy oil is very small, the heavy oil and solids mixture can be further separated by a filter or centrifuge using a metal filter. Also good.
 本発明においては、III工程で分離された軽質油分を回収する工程と、IV工程で分離された重質油分を回収する工程を有する。すなわち、III工程で分離し回収された軽質油分とIV工程で分離し回収された重質油分を混合して回収するか、若しくは混合することなくそれぞれ個別に回収する。回収された混合油分または軽質油分と重質油分は、例えば原油タンクに戻せばよい。本発明の油分回収方法によれば、薬剤などを使用することがないため、薬剤回収などの処理が不要であり、環境負荷を大きく低減できる。また、近年の原油高騰の折り、油分回収ニーズを満足することができる。 In the present invention, there are a step of recovering the light oil separated in the step III and a step of recovering the heavy oil separated in the step IV. That is, the light oil separated and recovered in the step III and the heavy oil separated and recovered in the step IV are mixed and recovered, or individually recovered without mixing. The recovered mixed oil or light oil and heavy oil may be returned to, for example, a crude oil tank. According to the oil recovery method of the present invention, since no chemicals are used, processing such as chemical recovery is unnecessary, and the environmental burden can be greatly reduced. In addition, the need for oil recovery can be satisfied with the recent rise in crude oil prices.
 原油ムースなど固形分が少ない原油スラッジの場合、IV工程において、真空蒸発槽内の蒸発残渣を、そのまま、真空蒸発槽外に取り出すだけでよい。原油ムースは、油分が多く、固形分が少ないため、固形分と重質油を分離することなく回収するのが効率的である。回収された少量の固形分を含む重質油分は、例えば原油タンクに戻せばよい。 In the case of crude sludge having a low solid content such as crude oil mousse, the evaporation residue in the vacuum evaporation tank is simply taken out of the vacuum evaporation tank as it is in the IV process. Since crude mousse has a high oil content and a low solid content, it is efficient to recover the solid content and heavy oil without separating them. For example, the recovered heavy oil containing a small amount of solids may be returned to the crude oil tank.
 本発明の原油スラッジ中の油分回収方法は、連続プロセス又は非連続プロセスである。連続プロセスとは、上記I~IV工程を連続的に実施する方法であり、例えばII工程とIII工程のように、一部の工程が同時進行であってもよい。また、非連続プロセスとは、例えばI工程とII工程間、II工程とIII工程間、II工程とIV工程間のひとつ又はそれ以上において、連続とは言えない非連続部分(アイドル時間)が存在する方法を言う。全部が非連続プロセスとは、バッチ式プロセスを言う。連続プロセスあるいは非連続プロセスのいずれも、本願発明の効果を奏する。 The oil recovery method in the crude oil sludge of the present invention is a continuous process or a discontinuous process. The continuous process is a method of continuously carrying out the steps I to IV described above, and some of the steps may be performed simultaneously, for example, steps II and III. In addition, a discontinuous process means that there is a discontinuous part (idle time) that cannot be said to be continuous, for example, at one or more between steps I and II, between steps II and III, and between steps II and IV. Say how to do. An all discontinuous process refers to a batch process. Either the continuous process or the discontinuous process has the effect of the present invention.
 次に、本発明の原油スラッジ中の油分回収方法における連続プロセスの一例を挙げる。原油スラッジは貯留槽2内で加熱される。加熱により流動化した原油スラッジは、スクリューポンプ3などで連続的に真空蒸発槽1に投入される(I工程)。真空蒸発槽1では、加熱、真空及び撹拌の全ての操作が同時に連続して行われる。これにより、水分と軽質油分の蒸発も連続的に進行し(II工程)、水分と軽質油分は凝縮器4に連続的に送られる。III工程においても、II工程で得られる蒸発物質は連続的に冷却凝縮され、軽質油分分離器6において、軽質油分と水は連続的に分離され、各々外部へ排出される。IV工程においても、蒸発残渣は真空蒸発槽1から連続的に排出される。また、IV工程において分離工程を行う場合、連続的に排出された蒸発残渣も重質油分離器8で重質油分と固形分に連続的に分離される。 Next, an example of a continuous process in the method for recovering oil in crude sludge according to the present invention will be given. Crude oil sludge is heated in the storage tank 2. Crude oil sludge fluidized by heating is continuously charged into the vacuum evaporation tank 1 by a screw pump 3 or the like (Step I). In the vacuum evaporation tank 1, all the operations of heating, vacuum and stirring are performed continuously at the same time. Thereby, the evaporation of moisture and light oil continuously proceeds (step II), and the moisture and light oil are continuously sent to the condenser 4. Also in the step III, the evaporated substance obtained in the step II is continuously cooled and condensed, and the light oil component and water are continuously separated in the light oil component separator 6 and discharged to the outside. Also in the IV process, the evaporation residue is continuously discharged from the vacuum evaporation tank 1. Further, when the separation step is performed in the IV step, the continuously discharged evaporation residue is also continuously separated into a heavy oil component and a solid component by the heavy oil separator 8.
 なお、連続プロセスの場合、真空蒸発槽1への原油スラッジ導入口13と蒸発残渣取り出し口15は、可能な限り距離(特に水平距離)を離した部位に設置することが、真空蒸発槽1に投入された原油スラッジの蒸発処理が不十分なまま、短絡して蒸発残渣に混入して真空蒸発槽1から排出されることを防止することができる点で好ましい。真空蒸発槽1における原油スラッジの処理保有時間(滞留時間)としては、真空度や温度等の運転条件の相違により変化するため、一概に決定できないものの、概ね2時間以上とすることが、十分な真空蒸発を行う点で好ましい。 In the case of a continuous process, the crude oil sludge inlet 13 and the evaporation residue outlet 15 to the vacuum evaporation tank 1 should be installed at a site as far as possible (particularly horizontal distance). It is preferable in that it is possible to prevent the crude oil sludge being charged from being short-circuited and mixed into the evaporation residue and discharged from the vacuum evaporation tank 1 while being insufficiently evaporated. The processing retention time (retention time) of the crude oil sludge in the vacuum evaporation tank 1 varies depending on the operating conditions such as the degree of vacuum and temperature, and therefore cannot be determined in general. This is preferable in that vacuum evaporation is performed.
 本発明において、原油スラッジからの全油分の回収率、すなわち、真空蒸発槽に充填された原料中の油分に対する全油分は、ほぼ100%、実際には真空ポンプで吸引される回収できない油分などがあるため、概ね98%程度で回収することができる。回収された軽質油分と重質油分の合計である全油分中の水分量は、通常は1.0重量%未満、好ましくは0.5重量%以下である。回収油分は、軽質油分と重質油分の混合油分として回収してもよく、また、重質油分は固形分と共に混合物として回収してもよい。重質油分と固形分の混合物は工業用燃料として使用できる。 In the present invention, the recovery rate of the total oil content from the crude oil sludge, that is, the total oil content with respect to the oil content in the raw material charged in the vacuum evaporation tank is almost 100%. Therefore, it can be recovered at approximately 98%. The water content in the total oil, which is the sum of the recovered light oil and heavy oil, is usually less than 1.0% by weight, preferably 0.5% by weight or less. The recovered oil may be recovered as a mixture of light oil and heavy oil, or the heavy oil may be recovered as a mixture together with the solid. A mixture of heavy oil and solids can be used as an industrial fuel.
 次に、実施例を挙げて本発明を更に具体的に説明するが、これは単に例示であって、本発明を制限するものではない。 Next, the present invention will be described more specifically with reference to examples. However, this is merely an example and does not limit the present invention.
 下記仕様の試験用真空蒸発槽を使用し、軽質油分分離器及び重質油分分離器として、それぞれ1室の簡易構造の分離器を使用し、下記運転条件で原油スラッジA中の油分の回収を行った。すなわち、原油スラッジAを真空蒸発槽Aに導入し、加熱及び真空下において撹拌し、原油スラッジA中の軽質油分と水分を蒸発させた(I工程及びII工程)。次いで、蒸発物質を冷却して軽質油分と水に分離し、軽質油分を回収した(III工程)。一方、凝縮液体の発生終焉に伴い、真空蒸発槽Aの運転を停止し、真空状態を大気圧に戻して真空蒸発槽の下部から残渣を重質油分分離器に排出した。そして、重質油分分離器で分離した重質油を回収した。 Using a vacuum evaporation tank for testing with the following specifications, a light oil separator and a heavy oil separator, each with a simple chamber separator, and recovering oil in crude oil sludge A under the following operating conditions went. That is, the crude oil sludge A was introduced into the vacuum evaporation tank A and heated and stirred under vacuum to evaporate the light oil and water in the crude oil sludge A (Step I and Step II). Next, the evaporated substance was cooled and separated into light oil and water, and the light oil was recovered (step III). On the other hand, with the end of generation of the condensed liquid, the operation of the vacuum evaporation tank A was stopped, the vacuum state was returned to atmospheric pressure, and the residue was discharged from the lower part of the vacuum evaporation tank to the heavy oil separator. And the heavy oil isolate | separated with the heavy oil content separator was collect | recovered.
 その結果、軽質油分分離器から比重0.770の軽質油分8.2重量%を回収した。この軽質油分中には水分が検出されなかった。一方、重質油分分離器から比重0.950~0.990の重質油分20.6重量%を回収し、分離残渣48.1重量%を回収した。この重質油分中の水分量は0(ゼロ)重量%であった。なお、分離残渣はほとんどが固形分であり、重質油分を少量含むものであった。原油スラッジAからの油分回収量は98%(28.8重量%/29.3重量%)であった。 As a result, 8.2% by weight of a light oil having a specific gravity of 0.770 was recovered from the light oil separator. No moisture was detected in this light oil. On the other hand, 20.6% by weight of heavy oil having a specific gravity of 0.950 to 0.990 was recovered from the heavy oil separator, and 48.1% by weight of the separation residue was recovered. The water content in this heavy oil was 0 (zero) wt%. The separation residue was mostly solid and contained a small amount of heavy oil. The amount of oil recovered from the crude oil sludge A was 98% (28.8% by weight / 29.3% by weight).
(真空蒸発槽及び運転条件)
・図1に示す真空蒸発槽A
・撹拌羽根の平均回転速度;20回転/分
・真空度;-96kPa、加熱温度(原料温度);80~120℃
・蒸発物質温度(凝縮器入り口温度);50~85℃
・バッチ処理;原料47.8kg、2時間処理
・原油スラッジA;水分22.9重量%、油分29.3重量%、固形分47.8重量%
(関連装置)
・加熱手段;外部からスチーム加熱するジャケット方式
・真空ポンプ;水封式
・凝縮器:冷却水使用
(Vacuum evaporation tank and operating conditions)
・ Vacuum evaporation tank A shown in FIG.
・ Average rotation speed of stirring blades: 20 rotations / minute ・ Vacuum degree: −96 kPa, heating temperature (raw material temperature): 80 to 120 ° C.
Evaporative material temperature (condenser inlet temperature): 50 to 85 ° C
・ Batch treatment: Raw material 47.8 kg, treatment for 2 hours ・ Crude oil sludge A: Moisture 22.9 wt%, oil content 29.3% wt, solid content 47.8 wt%
(Related equipment)
・ Heating means: Jacket system with steam heating from outside ・ Vacuum pump; Water seal type ・ Condenser: Cooling water used
 下記真空蒸発槽及び運転条件とした以外は、実施例1と同様の方法により行った。その結果、軽質油分分離器から比重0.790の軽質油分5.1重量%を回収した。この軽質油分中の水分量は0.1重量%以下であった。一方、重質油分分離器から重質油分13.1重量%を回収し、分離残渣60.1重量%を回収した。この重質油分中の水分量は1.0重量%であった。原油スラッジBからの液状油分としての回収率は58重量%(18.2重量%/31.6重量%)であった。なお、分離残渣には一部の重質油分が含まれており、固形分、あるいは固形分と重質油の混合物を燃料として利用すれば、エネルギー源としての回収率は100%近くになる。 The same method as in Example 1 was performed except that the following vacuum evaporation tank and operating conditions were used. As a result, 5.1% by weight of light oil having a specific gravity of 0.790 was recovered from the light oil separator. The water content in this light oil was 0.1% by weight or less. On the other hand, 13.1% by weight of heavy oil was recovered from the heavy oil separator, and 60.1% by weight of separation residue was recovered. The water content in the heavy oil was 1.0% by weight. The recovery rate as a liquid oil from crude oil sludge B was 58% by weight (18.2% by weight / 31.6% by weight). In addition, a part of heavy oil content is contained in the separation residue, and if the solid content or a mixture of the solid content and the heavy oil is used as the fuel, the recovery rate as an energy source is close to 100%.
(真空蒸発槽及び運転条件)
・図1に示す真空蒸発槽B
・撹拌羽根の平均回転速度;20回転/分
・真空度;-100kPa、加熱温度(原料温度);75~97℃
・蒸発物質温度(凝縮器入り口温度);45~50℃
・バッチ処理;原料41.2kg、5時間処理
・原油スラッジB;水分20.4重量%、油分31.6重量%、固形分48.0重量%
(Vacuum evaporation tank and operating conditions)
・ Vacuum evaporation tank B shown in Fig.1
・ Average speed of stirring blades: 20 revolutions / minute ・ Vacuum degree: −100 kPa, heating temperature (raw material temperature): 75 to 97 ° C.
・ Evaporation substance temperature (condenser inlet temperature): 45-50 ℃
・ Batch treatment: Raw material 41.2 kg, treatment for 5 hours ・ Crude oil sludge B: Moisture 20.4 wt%, oil content 31.6 wt%, solid content 48.0 wt%
 下記真空蒸発槽及び運転条件とした以外は、実施例1と同様の方法により行った。その結果、軽質油分分離器から軽質油分9.2重量%を回収した。この軽質油分中の水分量は0.1重量%以下であった。一方、重質油分分離器から重質油分13.4重量%を回収し、分離残渣56.2重量%を回収した。この重質油分中の水分量は1.0重量%であった。原油スラッジCからの液状油分としての回収率は64重量%(22.6重量%/35.3重量%)であった。なお、分離残渣には一部の重質油分が含まれており、固形分、あるいは固形分と重質油の混合物を燃料として利用すれば、エネルギー源としての回収率は100%近くになる。 The same method as in Example 1 was performed except that the following vacuum evaporation tank and operating conditions were used. As a result, 9.2% by weight of light oil was recovered from the light oil separator. The water content in this light oil was 0.1% by weight or less. On the other hand, 13.4% by weight of heavy oil was recovered from the heavy oil separator, and 56.2% by weight of separation residue was recovered. The water content in the heavy oil was 1.0% by weight. The recovery rate as a liquid oil from crude oil sludge C was 64% by weight (22.6% by weight / 35.3% by weight). In addition, a part of heavy oil content is contained in the separation residue, and if the solid content or a mixture of the solid content and the heavy oil is used as the fuel, the recovery rate as an energy source is close to 100%.
(真空蒸発槽及び運転条件)
・図1に示す真空蒸発槽A
・撹拌羽根の平均回転速度;20回転/分
・真空度;-94.3kPa、加熱温度(槽内温度);124.9℃
・蒸発物質温度(凝縮器入り口温度);58~80℃
・バッチ処理;原料44.7kg、2時間処理
・原油スラッジC;水分21.0重量%、油分35.3重量%、固形分43.7重量%
(Vacuum evaporation tank and operating conditions)
・ Vacuum evaporation tank A shown in FIG.
・ Average rotation speed of stirring blades: 20 rotations / minute ・ Vacuum degree: −94.3 kPa, heating temperature (temperature in the tank): 124.9 ° C.
・ Evaporation substance temperature (condenser inlet temperature): 58-80 ℃
・ Batch treatment: Raw material 44.7 kg, treatment for 2 hours ・ Crude oil sludge C: Moisture 21.0 wt%, oil content 35.3% wt, solid content 43.7 wt%
 本発明によれば、回収油分は、いずれも水分をほとんど含まないため、そのまま原油等にブレンドして回収することができる。巨大な原油タンクに長期間に亘り堆積した原油スラッジの量は大量であり、これから回収される油分は、近年の原油高騰の状況下、貴重な資源となる。また、薬剤を使用しないため、薬剤処理などの二次処理が不要となり、環境負荷を低減できる。 According to the present invention, since the recovered oil content hardly contains any water, it can be recovered by blending it with crude oil or the like as it is. The amount of crude oil sludge accumulated in a huge crude oil tank over a long period of time is large, and the oil recovered from it becomes a valuable resource under the recent rise in crude oil prices. In addition, since no chemical is used, secondary processing such as chemical processing becomes unnecessary, and the environmental load can be reduced.
 海洋に流出した原油や重質油は、海洋に漂流中、風と波の影響を受けてアスファルテン等の重質分が海水と混ざってエマルジョンを形成し、ムースと称される油濁汚染物質となって、海洋及び沿岸周辺に多大な環境汚染を引き起こす。従来、海洋に漂流あるいは着岸した油濁汚染物質は、多くの場合、油分を回収することなく、廃棄物として処理したり、甚だしい場合は、漂流している油濁汚染物質を薬剤により海底に沈降させていたため、長期間に亘り、甚大な環境汚染を引き起こしていた。これに対して、本願発明の油分回収方法は、このような油濁汚染物質を薬剤を使用することなく、そのまま処理して、油分と固形分に分離できるため、廃棄物処理負担が軽減でき、地球環境保全に大きく貢献できる。 Crude oil and heavy oil spilled into the ocean, while drifting into the ocean, are affected by wind and waves, and heavy components such as asphaltene are mixed with seawater to form an emulsion. It causes great environmental pollution around the ocean and coast. In the past, oil pollutants that drifted or shored in the ocean were often treated as waste without collecting the oil, and in extreme cases, the drifting oil pollutants settled on the seabed with chemicals. For a long period of time, it caused enormous environmental pollution. On the other hand, the oil content recovery method of the present invention can treat such an oil pollutant as it is without using chemicals and can be separated into an oil content and a solid content, thereby reducing the waste treatment burden, Contributes greatly to global environmental conservation.
  1  真空蒸発槽
  2  原油タンクまたは原油スラッジ貯留槽
  4  凝縮器
  6  軽質油分分離器
  7  真空ポンプ
  8  重質油分分離器
 10  原油スラッジ中の油分回収装置
DESCRIPTION OF SYMBOLS 1 Vacuum evaporation tank 2 Crude oil tank or crude oil sludge storage tank 4 Condenser 6 Light oil separator 7 Vacuum pump 8 Heavy oil separator 10 Oil recovery apparatus in crude oil sludge

Claims (11)

  1.  原油スラッジを真空蒸発槽に導入するI工程と、
     真空蒸発槽内の原油スラッジを加熱及び真空下にて撹拌して、原油スラッジ中の軽質油分と水を蒸発させるII工程と、
     該II工程で得られる蒸発物質を冷却して軽質油分と水とに分離するIII工程と、
     該II工程で得られる真空蒸発槽内の蒸発残渣を、該真空蒸発槽外に取り出すIV工程と、を有することを特徴とする原油スラッジ中の油分回収方法。
    I process for introducing crude oil sludge into the vacuum evaporation tank;
    II step of evaporating light oil and water in the crude oil sludge by heating and stirring the crude oil sludge in the vacuum evaporation tank under vacuum;
    A step III in which the evaporated substance obtained in step II is cooled and separated into light oil and water;
    And a step IV of taking out the evaporation residue in the vacuum evaporation tank obtained in the step II to the outside of the vacuum evaporation tank, and a method for recovering oil in crude oil sludge.
  2.  該原油スラッジが、屋外の原油タンク底部に堆積したスラッジ、原油タンカーの原油タンク底部に堆積したスラッジ、野外に野晒しの原油スラッジ、海洋を漂流する原油スラッジまたは海洋を漂流後、着岸した原油スラッジであることを特徴とする請求項1記載の原油スラッジ中の油分回収方法。 Crude oil sludge accumulated at the bottom of an outdoor crude oil tank, sludge accumulated at the bottom of a crude oil tank of a crude oil tanker, crude oil sludge exposed to the outdoors, crude oil sludge drifting in the ocean, or crude oil sludge docked after drifting in the ocean The method for recovering oil in crude oil sludge according to claim 1, wherein:
  3.  該原油スラッジが、アスファルテン、コーク状物質、油分及び水を含有するものであることを特徴とする請求項1または2記載の原油スラッジ中の油分回収方法。 The method for recovering oil content in crude oil sludge according to claim 1 or 2, wherein the crude oil sludge contains asphaltene, coke-like substance, oil and water.
  4.  該原油スラッジが油中水滴型エマルジョン相を含むことを特徴とする請求項1~3のいずれか1項に記載の原油スラッジ中の油分回収方法。 The method for recovering oil content in crude oil sludge according to any one of claims 1 to 3, wherein the crude oil sludge contains a water-in-oil emulsion phase.
  5.  該II工程で得られる蒸発物質中の油分は、250℃沸点(大気圧下)留分までの軽質油分であることを特徴とする請求項1~4のいずれか1項に記載の原油スラッジ中の油分回収方法。 The crude oil sludge according to any one of claims 1 to 4, wherein the oil in the evaporated substance obtained in the step II is a light oil up to a boiling point of 250 ° C (under atmospheric pressure). Oil recovery method.
  6.  該II工程は、加熱温度70~150℃であり、真空度(ゲージ圧)-85~-100KPaであることを特徴とする請求項1~4のいずれか1項に記載の原油スラッジ中の油分回収方法。 The oil content in the crude oil sludge according to any one of claims 1 to 4, wherein the step II has a heating temperature of 70 to 150 ° C and a degree of vacuum (gauge pressure) of -85 to -100 KPa. Collection method.
  7.  該III工程において、冷却により凝縮された凝縮物を静置して軽質油分と水に分離することを特徴とする請求項1~6のいずれか1項に記載の原油スラッジ中の油分回収方法。 The method for recovering oil content in crude sludge according to any one of claims 1 to 6, wherein in step III, the condensate condensed by cooling is allowed to stand and be separated into light oil and water.
  8.  該IV工程において、真空蒸発槽内の蒸発残渣を、流動状態で該真空蒸発槽外に取り出すことを特徴とする請求項1~7のいずれか1項に記載の原油スラッジ中の油分回収方法。 The method for recovering oil in crude oil sludge according to any one of claims 1 to 7, wherein in the step IV, the evaporation residue in the vacuum evaporation tank is taken out of the vacuum evaporation tank in a fluidized state.
  9.  該IV工程において、取り出された流動物を、重質油分と固形分に分離するか、又は重質油分と、重質油分と固形分の混合物に分離することを特徴とする請求項8記載の原油スラッジ中の油分回収方法。 9. In the step IV, the removed fluid is separated into a heavy oil and a solid, or separated into a heavy oil and a mixture of the heavy oil and the solid. Oil recovery method for crude oil sludge.
  10.  該III工程で分離された軽質油分を回収する工程と、該IV工程で分離された重質油分を回収する工程を有することを特徴とする請求項9記載の原油スラッジ中の油分回収方法。 10. The method for recovering oil content in crude oil sludge according to claim 9, comprising a step of recovering the light oil component separated in the step III and a step of recovering the heavy oil component separated in the step IV.
  11.  連続プロセス又は非連続プロセスであることを特徴とする請求項1~10のいずれか1項に記載の原油スラッジ中の油分回収方法。 The method for recovering oil content in crude oil sludge according to any one of claims 1 to 10, wherein the process is a continuous process or a discontinuous process.
PCT/JP2012/058898 2011-04-14 2012-04-02 Method for recovering oil fraction in crude oil sludge WO2012141024A1 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2013509851A JP5925189B2 (en) 2011-04-14 2012-04-02 Oil recovery method in crude oil sludge

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
JP2011-089764 2011-04-14
JP2011089764 2011-04-14

Publications (1)

Publication Number Publication Date
WO2012141024A1 true WO2012141024A1 (en) 2012-10-18

Family

ID=47009204

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/JP2012/058898 WO2012141024A1 (en) 2011-04-14 2012-04-02 Method for recovering oil fraction in crude oil sludge

Country Status (2)

Country Link
JP (1) JP5925189B2 (en)
WO (1) WO2012141024A1 (en)

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111925085A (en) * 2020-08-25 2020-11-13 西安德兴环保科技有限公司 Oil sludge treatment method suitable for heavy bottom oil sludge and tank cleaning oil sludge
CN113289362A (en) * 2021-05-20 2021-08-24 高密市超越应升机械科技有限公司 Electric spark oil residue separator for tire mold
CN114477369A (en) * 2022-01-18 2022-05-13 华东理工大学 Phenol-ammonia wastewater pretreatment device and process for degassing and light and heavy oil synchronous separation

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN113149397A (en) * 2020-01-20 2021-07-23 中国石油天然气股份有限公司 Skid-mounted equipment for recovery and reduction treatment of crude oil containing silt and treatment method

Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH03229682A (en) * 1990-02-06 1991-10-11 Taiho Ind Co Ltd Recovery of sludge in oil tank
JPH05320658A (en) * 1992-05-19 1993-12-03 Kazumi Miyai Process for waste disposal and apparatus therefor
JP2000129270A (en) * 1998-10-29 2000-05-09 Toshiba Corp Device and process for liquefaction of waste plastic
JP2000334738A (en) * 1999-05-31 2000-12-05 Sony Corp Recycling method for styrol resin waste material
JP2004243300A (en) * 2003-02-16 2004-09-02 Toshikatsu Hamano Processing method of oil and water mixed sludge accumulated in crude oil tank
JP2005349240A (en) * 2004-06-08 2005-12-22 Cosmo Oil Co Ltd Method for treating sludge
JP2006282858A (en) * 2005-03-31 2006-10-19 National Institute Of Advanced Industrial & Technology Method for producing high-quality liquid fuel from organic waste and liquid fuel produced therefrom
JP2006526033A (en) * 2003-05-15 2006-11-16 簡 泗仁 How to separate oil sludge and crude oil

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR100475172B1 (en) * 2001-02-20 2005-03-08 에스케이 주식회사 Method for Removing Sludges in A Crude Oil Tank and Recovering Oil Therefrom
US20030075515A1 (en) * 2001-10-23 2003-04-24 Roger Maki Apparatus for the treatment of oil-containing sludge and methods of doing the same
WO2003106058A2 (en) * 2002-06-18 2003-12-24 Awazel Waterproofing Company Extraction methods and apparatus
JP6004562B2 (en) * 2011-04-14 2016-10-12 システム機工株式会社 Oil recovery equipment for crude oil sludge

Patent Citations (8)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH03229682A (en) * 1990-02-06 1991-10-11 Taiho Ind Co Ltd Recovery of sludge in oil tank
JPH05320658A (en) * 1992-05-19 1993-12-03 Kazumi Miyai Process for waste disposal and apparatus therefor
JP2000129270A (en) * 1998-10-29 2000-05-09 Toshiba Corp Device and process for liquefaction of waste plastic
JP2000334738A (en) * 1999-05-31 2000-12-05 Sony Corp Recycling method for styrol resin waste material
JP2004243300A (en) * 2003-02-16 2004-09-02 Toshikatsu Hamano Processing method of oil and water mixed sludge accumulated in crude oil tank
JP2006526033A (en) * 2003-05-15 2006-11-16 簡 泗仁 How to separate oil sludge and crude oil
JP2005349240A (en) * 2004-06-08 2005-12-22 Cosmo Oil Co Ltd Method for treating sludge
JP2006282858A (en) * 2005-03-31 2006-10-19 National Institute Of Advanced Industrial & Technology Method for producing high-quality liquid fuel from organic waste and liquid fuel produced therefrom

Cited By (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111925085A (en) * 2020-08-25 2020-11-13 西安德兴环保科技有限公司 Oil sludge treatment method suitable for heavy bottom oil sludge and tank cleaning oil sludge
CN111925085B (en) * 2020-08-25 2022-07-19 西安德兴环保科技有限公司 Oil sludge treatment method suitable for heavy bottom oil sludge and tank cleaning oil sludge
CN113289362A (en) * 2021-05-20 2021-08-24 高密市超越应升机械科技有限公司 Electric spark oil residue separator for tire mold
CN114477369A (en) * 2022-01-18 2022-05-13 华东理工大学 Phenol-ammonia wastewater pretreatment device and process for degassing and light and heavy oil synchronous separation

Also Published As

Publication number Publication date
JPWO2012141024A1 (en) 2014-07-28
JP5925189B2 (en) 2016-05-25

Similar Documents

Publication Publication Date Title
JP6004562B2 (en) Oil recovery equipment for crude oil sludge
WO2013091032A1 (en) Method for processing of oil sludge and oil sediments
US9676684B2 (en) Process and unit for solvent recovery from solvent diluted tailings derived from bitumen froth treatment
US9314713B2 (en) Apparatus and method for recovering a hydrocarbon diluent from tailings
JPH06501722A (en) How to recover oil from waste oil sludge
JP5925189B2 (en) Oil recovery method in crude oil sludge
CN112079540B (en) Method for treating oil sludge
KR0133527B1 (en) Oil recovery process and apparatus for oil refinery waste
US20190022555A1 (en) Method and system for cleaning oily waste
CN107050916A (en) A kind of extractant and its methods and applications that discarded object is handled based on extractant
CN101792224A (en) Method and device for processing emptied water of delayed coking
EP2174697A1 (en) Petroleum residue recycling process and unit.
CN108751635A (en) A kind of Sludge in Oilfields processing equipment
CN115403243B (en) Fatlute processing system
FI85339C (en) Process for further processing of the vacuum distillation residue in a crude oil refinery
CN105950212A (en) Aged sump oil treatment process
KR20170088898A (en) Method of processing and/or recovering and/or reutilizing residues, especially from refinery processes
JPH01275692A (en) Method of treating waste engine oil
US2030480A (en) Process for reclaiming oil containing carbon
CN106977064A (en) A kind of biological extractant handles the method and its application of oily sludge
JP5836737B2 (en) VOC processing system
EP0348707A1 (en) Process for treating oil sludge
CA3014968A1 (en) High temperature paraffinic froth treatment process
CN109097085A (en) The pretreated method of coal tar
Min et al. Experimental Study on Three-phase Separation of Oily Sludge.

Legal Events

Date Code Title Description
121 Ep: the epo has been informed by wipo that ep was designated in this application

Ref document number: 12771077

Country of ref document: EP

Kind code of ref document: A1

ENP Entry into the national phase

Ref document number: 2013509851

Country of ref document: JP

Kind code of ref document: A

NENP Non-entry into the national phase

Ref country code: DE

122 Ep: pct application non-entry in european phase

Ref document number: 12771077

Country of ref document: EP

Kind code of ref document: A1