JP2011143351A - Device for removing phosphate in waste oil and treatment system for waste oil containing pcb - Google Patents

Abstract

<P>PROBLEM TO BE SOLVED: To provide a device for removing phosphate in waste oil and a treating system for waste oil containing PCB. <P>SOLUTION: There are provided a feed tank 14 feeding a predetermined amount of waste oil 13 containing phosphate 12, a mixing tank 18 provided with stirring means 17 for mixing the fed waste oil 13 with water 16 from a water feed tank 15, an emulsion means 20 for making emulsion 19 by feeding the waste oil 13 mixed with the water 16, a warming part 21 warming the emulsion means 20 at a predetermined temperature, an analyzer 22 analyzing phosphorus (P) or phosphoric acid (H<SB>3</SB>PO<SB>4</SB>) in the emulsion 19, a circulation line L<SB>4</SB>returning the emulsion 19 to the mixing tank 18, a standing tank 25 making the emulsion 19 stand based on the result of the analyzer 22 and separating an oil layer 23 from a water layer 24, a filter 26 removing the solid content in the oil layer 23, a storage tank 28 storing treated oil 27 in which the phosphate 12 after passing the filter 26 is removed, and a waste water treating part 29 removing the phosphate in the water layer 24. <P>COPYRIGHT: (C)2011,JPO&INPIT

Description

  The present invention relates to an apparatus for removing phosphate ester from waste oil and a treatment system for waste oil containing polychlorinated biphenyl (PCB).

Conventionally, it is known to add organometallic additives, phosphorus compounds, and the like to lubricating oils in order to improve wear resistance. As an organometallic additive, ZnDTP (zinc-dithiophosphate) effective for preventing wear and preventing oxidation is frequently used. TCP (tricresyl phosphate) and the like are known as typical phosphorus compounds (Patent Document 1). This tricresyl phosphate is adsorbed on the metal surface and decomposes to form a phosphate film to prevent wear.
By the way, after its use, it is stored as waste oil in drums.

  Since this tricresyl phosphate is flame retardant, lubricating oil containing tricresyl phosphate cannot be burned and may be stored for a long period of time. If it can be removed automatically, combustion treatment can be carried out, but an efficient removal method has not yet been established.

  Also, PCB (Polychlorinated biphenyl), a general term for polychlorinated biphenyls: chlorinated isomers of biphenyl, was used as an insulating oil for the heat medium, but is strictly stored. Has been in operation in various parts of the country and is currently being processed to be completely detoxified (Japan Environmental Safety Corporation (JESCO) was established as a PCB treatment facility, and several locations nationwide under the supervision of the country. A PCB waste treatment facility is installed in the city, and a treatment business is carried out (Non-patent Document 1).

  In recent years, various technologies for processing PCBs used for such insulating oils have been proposed (about the evaluation method and the evaluated technology of PCB processing technology in the Industrial Waste Treatment Business Promotion Foundation: Non Patent Document 2).

  The present applicant has previously proposed a hydrothermal oxidative decomposition apparatus as a PCB processing technique, and performs PCB processing for detoxification (Patent Document 2 or 3).

Japanese Patent Laid-Open No. 9-157681 JP-A-9-79531 JP 2003-285041 A

http://www.jesconet.co.jp/business/contents/characteristics/index.html http://www.jesconet.co.jp/business/pcb_technology/pdf/PCB_shori.pdf

  By the way, when the lubricating oil and insulating oil as described above are mixed and stored as waste oil, the phosphoric acid ester has flame retardancy and hygroscopicity. The dechlorination / decomposition treatment method used has the problem that PCB waste oil containing a phosphate ester treatment containing moisture cannot be treated, although PCB can be detoxified by itself.

In addition, although the PCB can be decomposed in the hydrothermal oxidative decomposition apparatus, if a phosphate ester is mixed, apatite (Ca ₅ (PO ₄ ) ₃ (F, Cl, OH)) is generated in the hydrothermal treatment process. From the viewpoint of the soundness of the processing equipment, establishment of an efficient method for removing the phosphate ester is desired as a pretreatment.

  In view of the above problems, the present invention provides a phosphate ester removing device and polychlorinated biphenyl (PCB) in waste oil that can remove phosphate esters in advance when the waste oil is decomposed by a hydrothermal oxidative decomposition device. It is an object to provide a treatment system for contained oil.

A first invention of the present invention for solving the above-mentioned problems is a supply tank for supplying a predetermined amount of waste oil containing a phosphate ester, and mixing for mixing water from a water tank with the waste oil supplied from the supply tank A tank, an emulsifying means using the waste oil mixed with water as an emulsified liquid, a heating unit for heating the emulsifying means, and phosphorus (P) or phosphoric acid (H ₃ PO ₄ ) in the emulsified liquid. An analysis unit for analysis, a circulation line for returning the emulsion to the mixing tank, a stationary tank for allowing the emulsion to stand based on a result of the analysis unit, and separating the oil into a water layer, and a solid in the oil layer An apparatus for removing phosphate ester from waste oil, comprising: a filter for removing water and a waste water treatment unit for removing phosphoric acid in the aqueous layer.

  According to a second aspect of the present invention, there is provided the apparatus for removing phosphate ester from waste oil according to the first aspect, wherein the amount of water added is 10% by weight or less.

  3rd invention is the phosphate ester removal apparatus in waste oil characterized by the heating temperature of the said heating part being 80-100 degreeC in 1st or 2nd invention.

  According to a fourth invention, in any one of the first to third inventions, when the analysis unit analyzes and the phosphoric acid concentration in water or the phosphoric acid ester concentration in oil reaches a predetermined concentration, It is in the phosphate ester removal apparatus in waste oil characterized by having the determination part which performs operation which switches to a storage tank.

  In a fifth aspect of the present invention, the wastewater treatment unit according to any one of the first to fourth aspects further includes an inorganic filling tank filled with a solid adsorbent containing at least one of Ca, Mg, Na, and Al. In the apparatus for removing phosphate ester from waste oil, phosphoric acid is fixed with a metal salt.

  A sixth aspect of the present invention is the phosphate ester removing apparatus in the waste oil according to any one of the first to fifth aspects, wherein the waste oil contains polychlorinated biphenyl (PCB).

  The seventh invention comprises a phosphate ester removing device in the sixth waste oil, and a hydrothermal oxidative decomposition device that decomposes polychlorinated biphenyl (PCB) in the waste oil from which the phosphate ester has been removed. A waste oil treatment system containing polychlorinated biphenyl (PCB) is featured.

According to the present invention, the phosphate ester in the waste oil can be efficiently treated by hydrolysis, and the subsequent waste oil treatment is simplified.
In addition, when decomposing PCB in waste oil with hydrothermal oxidative decomposition equipment, phosphate ester is removed in advance, so that apatite of phosphate ester does not occur, so hydrothermal decomposition of insulating oil and lubricating oil The reaction can be performed efficiently.

FIG. 1 is a schematic view of an apparatus for removing a phosphate ester from waste oil according to a first embodiment. FIG. 2 is a schematic diagram of a waste oil treatment system including a phosphate ester removing device in waste oil according to a second embodiment.

  Hereinafter, the present invention will be described in detail with reference to the drawings. Note that the present invention is not limited to the embodiments. In addition, constituent elements in the following embodiments include those that can be easily assumed by those skilled in the art or those that are substantially the same.

An apparatus for removing phosphate ester from waste oil according to Embodiment 1 of the present invention will be described with reference to the drawings. FIG. 1 is a schematic view of an apparatus for removing a phosphate ester from waste oil according to a first embodiment.
As shown in FIG. 1, phosphoric acid ester removal apparatus 10 in the waste oil, and storage tank 11 for storing the waste oil 13 containing phosphoric acid ester 12, phosphoric acid ester, which is fed by the line L ₁ from-holding tube tank 11 A mixing tank provided with a supply tank 14 for supplying a predetermined amount of waste oil 13 containing 12 and a stirring means 17 for mixing the water 16 from the water supply tank 15 with the waste oil 13 fed from the supply tank 14 via the line L _2. 18, is fed to waste oil 13 the water 16 is mixed by the line L _3, (such as a line mixer) emulsifying means to emulsion 19 20 and, warming to warming the emulsifying means 20 to a predetermined temperature and parts 21, an analysis unit 22 for analyzing the phosphorus in the emulsion 19 (P) or phosphoric acid (H ₃ PO _4), a circulation line L ₄ returning the emulsion 19 to the mixing tank 18, the analysis unit 2, the emulsified liquid 19 is allowed to stand, a stationary tank 25 that separates into an oil layer 23 and an aqueous layer 24, a filter 26 that removes solid content in the oil layer 23, and a phosphorus after passing through the filter 26. A storage tank 28 for storing the treated waste oil 27 from which the acid ester 12 has been removed and a waste water treatment unit 29 for removing phosphoric acid from the aqueous layer 24 are provided.
In FIG. 1, reference numerals V ₁ and V ₂ denote switching valves, P _{1 to} P ₃ denote feed pumps, and lines L _{5 to} L ₈ denote feed lines.

The water 16 supplied from the water supply tank 15 is supplied in order to hydrolyze the phosphate ester 12 and is added to the waste oil 13 by about 10% by weight.
In addition, when there is little content of the phosphate ester 12, it is trying to reduce the addition amount.
Here, in order to promote emulsification, water vapor may be supplied instead of supplying water 16.

The emulsifying means 20 may be any means as long as it is a finely mixed state of oil and water, but it is particularly preferable to use a line mixer.
This line mixer can be made into a fine emulsion 19 in order to efficiently treat the hydrolysis.
The emulsifying means 20 other than the line mixer may be any stirring means that can give a high share to the fluid, and examples thereof include a rotary mill, a blade rotation type, and an ultrasonic vibration type. it can.

The emulsifying means 20 is provided with a heating part 21 such as a heater for heating to about 80 to 100 ° C. as necessary in order to promote hydrolysis as shown in [Chemical Formula 1] below.
In the following [Chemical Formula 1], TCP (tricresyl phosphate) is taken as an example of the phosphate ester. As shown in the reaction formula, TCP (tricresyl phosphate) is decomposed by hydrolysis, and P is mineralized as phosphoric acid (H ₃ PO ₄ ).

The waste oil 13 emulsified by the emulsifying means 20 is monitored for its hydrolysis state by an analysis unit 22 that chemically analyzes the proportion of phosphoric acid (H ₃ PO ₄ ) in the water or phosphorus (P) in the oil. ing.
While the hydrolysis does not proceed, the circulation line L ₄ is used to return to the mixing tank 18 and the emulsification by the emulsifying means 20 is repeated again.

The analysis result in the analysis unit 22 is sent to the determination unit 30, where the hydrolysis is completed when the ratio of phosphoric acid (H ₃ PO ₄ ) or phosphorus (P) reaches a predetermined concentration. Then, the switching valve V ₁ is switched and fed to the stationary tank 25 via the line L ₅ .
Here, as the predetermined concentration, for example, when the lubricating oil contains 10% or less phosphate ester, the proportion of phosphoric acid (H ₃ PO ₄ ) in the water of the emulsion 19 is about 20%. When it becomes above, it will be judged that hydrolysis progressed and transfer to the water layer 24 from the oil layer 23 was completed.
On the other hand, in the case of the ratio of phosphorus (P) in the oil, when it becomes about 10 to 100 ppm, it is determined that the hydrolysis proceeds and the transfer from the oil layer 23 to the water layer 24 is completed.
This determination may be performed both or one of them.
The oil tank 23 and the water layer 24 are separated by being allowed to stand for a predetermined time in the stationary tank 25.

  The determination of completion is made by comparing the concentration of phosphorus (P) in the aqueous layer with the target concentration. For example, if the target value is <100 ppm, it is less than that. The determination may be made by performing analysis by a determination method based on a combination with a method, a determination method based on a combination of a bomb combustion decomposition method and chemical analysis (such as an absorptiometry), or the like.

Thereafter, the oil layer 23 is fed to the filter 26 through the line L ₆ and the line L ₇ , where the solid content in the oil is removed. Thereafter, the treated waste oil 27 from which the phosphate ester 12 has been removed is stored in a storage tank 28.
Here, as the filter 26, in order to efficiently remove a small amount of phosphate ester remaining in the oil layer 23, phosphorus is attached to the metal (iron) using a metal filter (for example, an iron-based mesh filter). Try to remove.

  Thereafter, the treated waste oil 27 is treated by a predetermined waste oil treatment device (combustion treatment, hydrothermal decomposition treatment, etc.).

  According to the present invention, the phosphate ester in the waste oil can be efficiently treated by hydrolysis, and the subsequent waste oil (lubricating oil) becomes incombustible and combustion treatment is possible.

Further, after the processing of the oil layer 23 is completed, the switching valve V ₂ is switched, and the water layer 24 is fed to the waste water treatment unit 29 through the line L ₈ to fix the phosphoric acid.
The wastewater treatment section for fixing phosphoric acid has an inorganic filling tank filled with a solid adsorbent containing at least one of Ca, Mg, Na, and Al, for example, and phosphoric acid is fixed with a metal salt ( For example, apatite (Ca ₅ (PO ₄ ) ₃ (F, Cl, OH)) is generated). Thereafter, the pH is adjusted in a pH adjusting tank and then discharged to the outside.

  Further, even when the waste oil is processed by the hydrothermal oxidative decomposition apparatus 120, since the phosphate ester is removed in advance, the apatite formation due to the phosphate ester does not occur in the hydrothermal oxidative decomposition process. The hydrothermal decomposition reaction of insulating oil or lubricating oil can be performed efficiently.

A waste oil processing system including a phosphate ester removing device in waste oil according to an embodiment of the present invention will be described with reference to the drawings. FIG. 2 is a schematic diagram of a waste oil treatment system including a phosphate ester removing device in waste oil according to a second embodiment.
As shown in FIG. 2, a waste oil treatment system 100 including a phosphate ester removal device in waste oil includes a phosphate ester removal device 10 in waste oil according to Example 1 and water for hydrothermal oxidative decomposition treatment of PCB. And a thermal oxidative decomposition apparatus 120.
Here, the schematic structure of the hydrothermal oxidative decomposition apparatus 120 is as follows: the treated waste oil 27 from which the phosphate ester has been removed, oil (for reaction promotion) 31, sodium hydroxide (NaOH) 32, pure water 33, and oxygen (O ₂ ). 34 is provided with a cylindrical primary reaction tower 101 for charging 34, a secondary reaction tower 107 for completing the decomposition treatment reaction, a cooler 108, and a pressure reducing valve 109 for the reactor. A gas-liquid separator 110 that separates waste water (H ₂ O, NaCl) 114 and exhaust gas (CO ₂ ) 112 is disposed downstream of the pressure reducing valve 109. The secondary reactor 107 can be omitted as necessary.

In the hydrothermal oxidative decomposition apparatus 120, the pressure in the primary reaction tower 101 is increased to, for example, about 26 MPa by pressurization with a pressure pump. The heat exchanger 121 preheats H ₂ O to about 300 ° C. Further, oxygen 34 from the high-pressure oxygen supply equipment 117 is jetted into the primary reaction tower 101, and the temperature is raised to 350 ° C. to 400 ° C. (preferably up to 370 ° C.) by the internal reaction heat. By this stage, an oxidative decomposition reaction has occurred in the primary reaction tower 101, and the PCB contained in the waste oil 27 has been decomposed into CO ₂ and H ₂ O. Next, in the cooler 108, the fluid from the secondary reaction tower 107 is cooled to about 100 ° C. and the pressure is reduced to atmospheric pressure by the pressure reducing valve 109 at the subsequent stage. Then, CO ₂ and water vapor and the treatment liquid are separated by the gas-liquid separator 110, and the CO ₂ and water vapor are exhausted from the chimney 113 into the environment as the exhaust gas 112 through the activated carbon layer 111. The drainage 114 is treated to a predetermined standard and temporarily stored in the discharge tank 115. 120a to 120d are storage tanks, 121 is a heat exchanger, 122a to 122d are pumps, and 123 is a mixer.

  Thus, according to the present embodiment, even when waste oil is processed by the hydrothermal oxidative decomposition apparatus 120, the phosphate ester is removed in advance by the phosphate ester removing apparatus 10 in the waste oil. In the hydrothermal decomposition treatment in the apparatus 120, apatite formation due to the phosphate ester does not occur, and the hydrothermal decomposition reaction of the waste oil (insulating oil or lubricating oil) 13 can be performed stably.

  As mentioned above, according to the phosphate ester removal apparatus in waste oil which concerns on this invention, the phosphate ester in waste oil can be processed efficiently by hydrolysis, and subsequent waste oil processing becomes easy.

DESCRIPTION OF SYMBOLS 10 Phosphate ester removal apparatus in waste oil 12 Phosphate ester 13 Waste oil 16 Water 18 Mixing tank 19 Emulsification liquid 20 Emulsification means (for example, line mixer)
DESCRIPTION OF SYMBOLS 21 Heating part 22 Analyzing part 23 Oil layer 24 Water layer 25 Static tank 26 Filter 27 Processing waste oil 29 Waste water processing part 30 Determination part

Claims (7)

A supply tank for supplying a predetermined amount of waste oil containing phosphate ester;
A mixing tank for mixing water from a water tank with waste oil supplied from the supply tank;
An emulsifying means using the waste oil mixed with water as an emulsified liquid;
A heating unit for heating the emulsifying means;
An analysis unit for analyzing phosphorus (P) or phosphoric acid (H ₃ PO ₄ ) in the emulsion;
A circulation line for returning the emulsion to the mixing tank;
Based on the result of the analysis unit, the emulsion is allowed to stand, and a stationary tank that separates the oil layer and the water layer;
A filter for removing solids in the oil layer;
An apparatus for removing phosphate esters in waste oil, comprising: a wastewater treatment section for removing phosphoric acid in the aqueous layer. In claim 1,
An apparatus for removing a phosphate ester from waste oil, wherein the amount of water added is 10% by weight or less. In claim 1 or 2,
The apparatus for removing a phosphate ester in waste oil, wherein the heating temperature of the heating section is 80 to 100 ° C. In any one of Claims 1 thru | or 3,
In the waste oil characterized by having a determination unit that performs an operation of switching to a stationary tank when the concentration of phosphoric acid in water or the concentration of phosphate ester in oil reaches a predetermined concentration Phosphate ester removal equipment. In any one of Claims 1 thru | or 4,
In the waste oil characterized in that the waste water treatment unit has an inorganic filling tank filled with a solid adsorbent containing at least one of Ca, Mg, Na, and Al, and fixes phosphoric acid with a metal salt. Phosphate ester removal equipment. In any one of Claims 1 thru | or 5,
The apparatus for removing a phosphate ester from waste oil, wherein the waste oil contains polychlorinated biphenyl (PCB). An apparatus for removing a phosphate ester from waste oil according to claim 6;
A waste oil treatment system containing polychlorinated biphenyl (PCB), comprising a hydrothermal oxidative decomposition apparatus for decomposing polychlorinated biphenyl (PCB) in the waste oil from which the phosphate ester has been removed.

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