KR20170011271A - Purification and oils recovery unit of contaminated soil using subcritical water - Google Patents
Purification and oils recovery unit of contaminated soil using subcritical water Download PDFInfo
- Publication number
- KR20170011271A KR20170011271A KR1020150103610A KR20150103610A KR20170011271A KR 20170011271 A KR20170011271 A KR 20170011271A KR 1020150103610 A KR1020150103610 A KR 1020150103610A KR 20150103610 A KR20150103610 A KR 20150103610A KR 20170011271 A KR20170011271 A KR 20170011271A
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- Prior art keywords
- water
- transferred
- reactor
- contaminated soil
- soil
- Prior art date
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- 239000002689 soil Substances 0.000 title claims abstract description 133
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 119
- 238000000746 purification Methods 0.000 title claims description 23
- 238000011084 recovery Methods 0.000 title claims description 22
- 239000003921 oil Substances 0.000 title description 53
- 239000002245 particle Substances 0.000 claims abstract description 48
- 239000000356 contaminant Substances 0.000 claims abstract description 35
- 238000001816 cooling Methods 0.000 claims abstract description 20
- 239000012535 impurity Substances 0.000 claims abstract description 13
- -1 floating matters Substances 0.000 claims abstract description 9
- 238000001914 filtration Methods 0.000 claims abstract description 8
- 238000007599 discharging Methods 0.000 claims abstract description 5
- 238000007667 floating Methods 0.000 claims abstract description 5
- 238000010438 heat treatment Methods 0.000 claims abstract description 4
- 238000000034 method Methods 0.000 claims description 23
- 239000003344 environmental pollutant Substances 0.000 claims description 13
- 231100000719 pollutant Toxicity 0.000 claims description 13
- 238000001035 drying Methods 0.000 claims description 5
- 238000005067 remediation Methods 0.000 claims description 4
- 230000001105 regulatory effect Effects 0.000 claims description 2
- 238000012546 transfer Methods 0.000 description 9
- 239000010779 crude oil Substances 0.000 description 7
- 239000000126 substance Substances 0.000 description 7
- 238000000605 extraction Methods 0.000 description 6
- 238000007254 oxidation reaction Methods 0.000 description 6
- 238000006243 chemical reaction Methods 0.000 description 4
- 230000000052 comparative effect Effects 0.000 description 4
- 239000007788 liquid Substances 0.000 description 4
- 239000000523 sample Substances 0.000 description 4
- YMWUJEATGCHHMB-UHFFFAOYSA-N Dichloromethane Chemical compound ClCCl YMWUJEATGCHHMB-UHFFFAOYSA-N 0.000 description 3
- OKKJLVBELUTLKV-UHFFFAOYSA-N Methanol Chemical compound OC OKKJLVBELUTLKV-UHFFFAOYSA-N 0.000 description 3
- 239000012530 fluid Substances 0.000 description 3
- 238000004817 gas chromatography Methods 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 description 2
- MHAJPDPJQMAIIY-UHFFFAOYSA-N Hydrogen peroxide Chemical compound OO MHAJPDPJQMAIIY-UHFFFAOYSA-N 0.000 description 2
- 238000004458 analytical method Methods 0.000 description 2
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 description 2
- 229910052799 carbon Inorganic materials 0.000 description 2
- 125000004122 cyclic group Chemical group 0.000 description 2
- 238000000354 decomposition reaction Methods 0.000 description 2
- 239000003599 detergent Substances 0.000 description 2
- 238000010586 diagram Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 239000007789 gas Substances 0.000 description 2
- 229930195733 hydrocarbon Natural products 0.000 description 2
- 150000002430 hydrocarbons Chemical class 0.000 description 2
- 229910052739 hydrogen Inorganic materials 0.000 description 2
- 238000002386 leaching Methods 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 229910052757 nitrogen Inorganic materials 0.000 description 2
- 239000003960 organic solvent Substances 0.000 description 2
- 239000001301 oxygen Substances 0.000 description 2
- 229910052760 oxygen Inorganic materials 0.000 description 2
- 239000002957 persistent organic pollutant Substances 0.000 description 2
- 239000012782 phase change material Substances 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 238000004064 recycling Methods 0.000 description 2
- 238000011160 research Methods 0.000 description 2
- 239000007787 solid Substances 0.000 description 2
- 239000002904 solvent Substances 0.000 description 2
- 229910052717 sulfur Inorganic materials 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- 239000004215 Carbon black (E152) Substances 0.000 description 1
- 241000239218 Limulus Species 0.000 description 1
- VYPSYNLAJGMNEJ-UHFFFAOYSA-N Silicium dioxide Chemical compound O=[Si]=O VYPSYNLAJGMNEJ-UHFFFAOYSA-N 0.000 description 1
- PMZURENOXWZQFD-UHFFFAOYSA-L Sodium Sulfate Chemical compound [Na+].[Na+].[O-]S([O-])(=O)=O PMZURENOXWZQFD-UHFFFAOYSA-L 0.000 description 1
- NINIDFKCEFEMDL-UHFFFAOYSA-N Sulfur Chemical compound [S] NINIDFKCEFEMDL-UHFFFAOYSA-N 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 238000010170 biological method Methods 0.000 description 1
- 238000009835 boiling Methods 0.000 description 1
- 238000004364 calculation method Methods 0.000 description 1
- 239000012159 carrier gas Substances 0.000 description 1
- 238000002485 combustion reaction Methods 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 230000001276 controlling effect Effects 0.000 description 1
- 239000000498 cooling water Substances 0.000 description 1
- 238000005260 corrosion Methods 0.000 description 1
- 230000007797 corrosion Effects 0.000 description 1
- 238000003795 desorption Methods 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 239000002360 explosive Substances 0.000 description 1
- 239000001307 helium Substances 0.000 description 1
- 229910052734 helium Inorganic materials 0.000 description 1
- SWQJXJOGLNCZEY-UHFFFAOYSA-N helium atom Chemical compound [He] SWQJXJOGLNCZEY-UHFFFAOYSA-N 0.000 description 1
- 239000001257 hydrogen Substances 0.000 description 1
- 125000004435 hydrogen atom Chemical class [H]* 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 238000000691 measurement method Methods 0.000 description 1
- 229910052751 metal Inorganic materials 0.000 description 1
- 239000002184 metal Substances 0.000 description 1
- 238000006864 oxidative decomposition reaction Methods 0.000 description 1
- 230000000737 periodic effect Effects 0.000 description 1
- 230000002085 persistent effect Effects 0.000 description 1
- 239000003209 petroleum derivative Substances 0.000 description 1
- 125000001997 phenyl group Chemical group [H]C1=C([H])C([H])=C(*)C([H])=C1[H] 0.000 description 1
- 238000011197 physicochemical method Methods 0.000 description 1
- 125000005575 polycyclic aromatic hydrocarbon group Chemical group 0.000 description 1
- 239000002861 polymer material Substances 0.000 description 1
- 230000002265 prevention Effects 0.000 description 1
- 230000002035 prolonged effect Effects 0.000 description 1
- 230000000630 rising effect Effects 0.000 description 1
- 239000000741 silica gel Substances 0.000 description 1
- 229910002027 silica gel Inorganic materials 0.000 description 1
- 239000011593 sulfur Substances 0.000 description 1
- 239000006228 supernatant Substances 0.000 description 1
- 238000000108 ultra-filtration Methods 0.000 description 1
- 238000005406 washing Methods 0.000 description 1
- 239000002699 waste material Substances 0.000 description 1
Images
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/02—Extraction using liquids, e.g. washing, leaching, flotation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D35/00—Filtering devices having features not specifically covered by groups B01D24/00 - B01D33/00, or for applications not specifically covered by groups B01D24/00 - B01D33/00; Auxiliary devices for filtration; Filter housing constructions
- B01D35/02—Filters adapted for location in special places, e.g. pipe-lines, pumps, stop-cocks
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B03—SEPARATION OF SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS; MAGNETIC OR ELECTROSTATIC SEPARATION OF SOLID MATERIALS FROM SOLID MATERIALS OR FLUIDS; SEPARATION BY HIGH-VOLTAGE ELECTRIC FIELDS
- B03B—SEPARATING SOLID MATERIALS USING LIQUIDS OR USING PNEUMATIC TABLES OR JIGS
- B03B5/00—Washing granular, powdered or lumpy materials; Wet separating
- B03B5/28—Washing granular, powdered or lumpy materials; Wet separating by sink-float separation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/06—Reclamation of contaminated soil thermally
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B09—DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
- B09C—RECLAMATION OF CONTAMINATED SOIL
- B09C1/00—Reclamation of contaminated soil
- B09C1/08—Reclamation of contaminated soil chemically
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F26—DRYING
- F26B—DRYING SOLID MATERIALS OR OBJECTS BY REMOVING LIQUID THEREFROM
- F26B3/00—Drying solid materials or objects by processes involving the application of heat
- F26B3/02—Drying solid materials or objects by processes involving the application of heat by convection, i.e. heat being conveyed from a heat source to the materials or objects to be dried by a gas or vapour, e.g. air
Landscapes
- Engineering & Computer Science (AREA)
- Life Sciences & Earth Sciences (AREA)
- Soil Sciences (AREA)
- Environmental & Geological Engineering (AREA)
- Chemical & Material Sciences (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Physics & Mathematics (AREA)
- Thermal Sciences (AREA)
- Microbiology (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Processing Of Solid Wastes (AREA)
Abstract
The present invention relates to a water tank (10) in which water is stored; A pump 20 for pressurizing the water transferred from the water tub 10; A storage tank (30) for storing the water transferred from the pump (20); A distributor / distributor 40 for distributing and transferring the water transferred from the storage tank 30 to the water tank 10 and the pressure regulator 50; A pressure regulator 50 for pressurizing or depressurizing the water transferred from the distributor / transporter 40 to a subcritical pressure condition; A preheater (60) for heating the water transferred from the pressure regulator (50) to a temperature condition of a subcritical state to generate a subcritical coefficient; A reactor (70) for passing the submerged coefficient transferred from the preheater (60) through the contaminated soil loaded therein to dissolve contaminants contained in the contaminated soil into the submerged coefficient; A tube particle remover 80 for filtering particles, floating matters, and impurities of contaminants included in the submixture transferred from the reactor 70; A heat exchanger (90) for cooling the subcritical water transferred from the tube particle remover (80) to generate water at room temperature; A flow rate controller 100 that adjusts the flow rate of the water at room temperature sent from the heat exchanger 90 to a constant value; And a density separator 110 for separating the water at room temperature transferred from the flow rate regulator 100 by density difference and discharging the oil to the oil collecting tank 120 and discharging the water at room temperature to the water tank 10 .
Description
The present invention relates to a method for purifying a contaminated soil, and more particularly, to a method for purifying a contaminated soil by extracting pollutants including oil, polyunsaturated hydrocarbons, explosives, And a device for recovering the oil contained in the pollutant.
The subcritical water, which is called the ideal low-cost "green" solvent, has a wide range of temperatures and pressures, and in these conditions the properties of water vary widely. For example, properties such as water polarity, viscosity, surface tension and the like can be rapidly changed. Using these various characteristics, there is a great advantage that the effect of removing the contaminants from the soil can be obtained without using the conventional chemical solvent.
Generally, water has a boiling point of 100 degrees at atmospheric pressure. However, in the high pressure state, the liquid state is maintained even when the temperature is raised. The water with this state is called the submergence coefficient. When the temperature is increased to 374 ° C or more, supercritical water is obtained. The subcritical water used in the present invention is water at a temperature of 100 to 374 degrees and a pressure of 4 to 400 bar. The dielectric constant (ε) according to the temperature of the submersion coefficient is similar to the organic solvent such as methanol (ε = 32) and ethanol (ε = 24) within a range of 2 to 50, The dielectric constant of water at room temperature and normal pressure is ε = 79. In this state, substances that are not dissolved in water can also be dissolved and extracted in the asymmetric state.
Oil spills due to marine oil spills and ship overturning accidents and soil contamination due to leakage of gas stations and oil storage tanks throughout the country are frequently occurring. Polycyclic aromatic hydrocarbons, which are compounds with two or more benzene rings, are highly persistent and accumulative and are highly degradable. Biological and physico-chemical methods are widely used to restore environmentally friendly soils contaminated with oil and PAHs.
The main techniques for treating organic pollutants from conventional contaminated soils include soil washing, steam extraction, and the like. Soil cleansing technique is a technique to treat contaminated soil by separating harmful organic contaminants attached to soil particles by using appropriate detergent. In the case of steam extraction, the soil is vacuumed by the vacuum pump in the unsaturated water layer, It is a restoration technology to remove semi-volatile contaminants. Soil physico-chemical properties affect the desorption rate, bioavailability, etc. of contaminants and also affect the purification and restoration of contaminated soil. Applying these techniques requires the choice of an appropriate detergent, may result in secondary treatment costs for dissolved contaminants, and has the disadvantage of prolonged processing time and inefficiency for quasi-volatile contaminants.
In addition, these treatment methods have limitations in treatment of soil contaminated with high concentrations, and soil contaminated with high concentrations is generally incinerated. In the case of incineration treatment, it is treated at a high cost, and a complex treatment facility for prevention of air pollution after incineration is required.
In domestic universities, overseas universities, research institutes and industries, many researches have been carried out on the oxidation reaction by ultrafiltration fluid for food processing, decomposition of polymer materials, and waste.
By adding oxygen, hydrogen peroxide, and the like in the super critical fluid, it is possible to maximize the oxidation reaction. However, the oxidation reaction in the supercritical fluid may increase the corrosiveness to the oxidation reaction apparatus, which may cause the extraction and the reaction vessel to be destroyed, and increase the cost of the apparatus for preventing corrosion. Also, secondary treatment due to the substances generated in the oxidative decomposition reaction is also necessary. On the other hand, in the extraction by the asymptotic reduction of the oxidation reaction, the water is elevated to a high temperature under the condition of maintaining the constant pressure, and the contaminants in the soil are effectively extracted using the reduced coefficient of the dielectric constant and the polarity. Unlike the oxidation reaction, it is a soil remediation method that can dramatically reduce the amount of organic solvent used to extract pollutants in the environment, minimize the decomposition of organic pollutants, and simplify the process after treatment. In order to recover environmentally friendly soils contaminated with organic contaminants, it is necessary to overcome the limitations of existing methods, to remove contaminants by using pure water, to increase the removal efficiency of residual contaminants, to recover the removed oil, It is still required to develop a soil remediation method using a limulus coefficient and a device capable of operating the soil remediation method.
Accordingly, the applicant of the present invention has attempted to solve the above-mentioned problems by improving the contaminated soil purification apparatus using the subcodes of Korean Patent No. 10-1339775.
However, according to the prior art, since the reactor is composed of one reactor, it is possible to rapidly supply the thermal energy to the water when the amount of the contaminated soil throughput of the reactor is increased (the reactor scale is increased) And there is a problem that the efficiency of the transfer of pollutants contained in the contaminated soil is reduced.
In addition, the prior art has a problem that the pollutants separated from the density separator and the water at room temperature are passed through without being discharged to the outside, thereby making it difficult to recover the oil.
In addition, in the prior art, there is a problem that the ash coefficient discharged from the reactor is reduced to the room temperature by the heat exchanger in the state where the particles and the impurities are mixed, and these are included in the recovered oil.
Further, the conventional art has a problem in that when operating the submodule in a cyclic mode in which the submerged soil periodically passes through the contaminated soil loaded in the reactor, the entire apparatus must be periodically repeatedly operated.
Therefore, in order to solve the above-mentioned problems, there is a need for an improved soil purification and oil recovery system.
It is an object of the present invention to provide a contaminated soil purification and oil recovery apparatus capable of recycling a limp coefficient.
Another object of the present invention is to provide a contaminated soil purification and oil recovery apparatus capable of easily recovering the oil contained in pollutants extracted by the submerged factor after the submerged leaching of the pollutants contained in the contaminated soil .
The apparatus for purifying contaminated soil and collecting oil according to the present invention comprises a water tank (10) in which water is stored; A
In addition, the
The
The
The contaminated soil purification and oil recovery apparatus 1000 using the subordinate coefficient may further include a plurality of
The
In addition, the water tank 10 is provided with a
Accordingly, the contaminated soil purification and oil recovery apparatus according to the present invention has an advantage that the ash coefficient can be recycled.
In addition, the contaminated soil purification and oil recovery apparatus according to the present invention can extract pollutants contained in contaminated soil using a density separator and can easily recover the oil contained in pollutants extracted from the contaminated soil There are advantages.
The apparatus for purifying contaminated soil according to the present invention comprises a plurality of reactors for extracting contaminants contained in contaminated soil by passing a submerged coefficient through contaminated soil loaded therein to maximize the purification capacity of the contaminated soil There is an effect that can be done.
FIG. 1 is a conceptual diagram of a contaminated soil purification and oil recovery apparatus using a subordinate coefficient according to the present invention.
Hereinafter, the technical idea of the present invention will be described more specifically with reference to the accompanying drawings.
BRIEF DESCRIPTION OF THE DRAWINGS The accompanying drawings, which are included to provide a further understanding of the technical concept of the present invention, are incorporated in and constitute a part of the specification, and are not intended to limit the scope of the present invention.
FIG. 1 is a conceptual diagram of a contaminated soil purification and oil recovery apparatus 1000 using a subordinate factor according to the present invention.
1, the contaminated soil purification and oil recovery apparatus 1000 using the subordinate coefficient according to the present invention includes a water tank 10, a
At this time, the components for generating the submerged coefficient are the water tank 10, the
The water tank 10 stores water at room temperature for conversion into an index coefficient. At this time, the water at normal temperature may be water having a low inorganic content or water recycled in the process.
The
The storage tank (30) stores the water transferred from the pump (20). More specifically, the
The
At this time, the distributor /
The distribution sensor controls the rate at which the
The
The
The reactor (70) passes the submergence coefficient transferred from the preheater (60) to the contaminated soil loaded therein, and contaminants contained in the contaminated soil are eluted into the submerged coefficient. At this time, contaminant soil contained in the contaminated soil is converted into purified soil by the subcritical coefficient.
The
In addition, the
The
The
The
The
Accordingly, the contaminated soil purification and oil recovery apparatus 1000 according to the present invention has an advantage of being able to recycle the ash coefficient.
The apparatus 1000 for collecting and purifying contaminated soil according to the present invention is a system for collecting pollutants contained in contaminated soil using a
Meanwhile, the
At this time, the plurality of
Accordingly, the contaminated soil purification and oil recovery apparatus 1000 according to the present invention includes a plurality of
The
The
The
The
The drying
The cooling
The cooling
The cooling means 75 is connected to both ends of the cooling
The cooling
Meanwhile, the contaminated soil purification and oil recovery apparatus 1000 using the subclaim according to the present invention may further include a plurality of
The plurality of
The
On the other hand, the
The intrusion
The
In other words, the tube-
The water tank 10 may be provided with a
In addition, the contaminated soil purification and oil recovery apparatus 1000 using the subordinate coefficient according to the present invention may further include a
The warmer 150 surrounds the
The
In addition, the
At this time, the phase-change material accumulates heat energy through the phase change process or emits the stored heat energy, so that a kind of physical change process in which a substance changes from a solid state to a liquid state, from a liquid state to a solid state, from a liquid state to a gas state, It is a substance that uses heat to accumulate or store heat.
Further, a piezoelectric element (not shown) for applying ultrasonic vibration to the
Hereinafter, a method for purifying contaminated soil using the contaminated soil purification and oil recovery apparatus using the subclaim according to the present invention will be described.
1) The contaminated soil to be purified is loaded on the
2) The water stored in the water tank 10 is pressurized by the
3) The water is pressurized or depressurized in the subcritical state by using the
4) By using the
5) By using the
6) By using the
7) The
8) Using the
9) The
Hereinafter, an experimental example in which the recovery of the polluted soil is confirmed by using the contaminated soil purification and oil recovery apparatus using the subclaim according to the present invention will be described in detail.
[Experimental Example]
[Method for measuring residual oil in contaminated soil]
After treating the oil contaminated soil with the apparatus of the present invention, the concentration of hydrocarbon oil residue, which is the residual oil in the contaminated soil, was measured as follows. Transfer the soil sample (about 10 g) treated in the apparatus of the present invention to a 250 mL beaker, add a sufficient amount of anhydrous sodium sulfate and mix well, then add 100 mL of dichloromethane for GC analysis. Extract for 3 minutes using an ultrasonic extractor and filter out the extract with a 5B open-topped funnel. The extract obtained by repeating this operation twice was concentrated to 2 mL with a rotary evaporator. 0.3 g of silica gel was added to the concentrated extract for shaking for 5 minutes, and the supernatant was added to 2 mL of Bai And then analyzed by gas chromatography. The analysis conditions of gas chromatography are as follows.
- Analysis conditions -
Detector: Flame Ionization Detector (FID);
Column: DB-5 (30 m * 32 mm * 0.25 m);
Oven temperature: 45 占 폚 (2 minutes)? [10 占 폚 / min]? 310 占 폚 (25 minutes);
Sample material inlet temperature: 280 ° C
Detector temperature: 300 ° C
Carrier gas (helium): 2 mL / min.
[Method of measuring the oil recovered in the apparatus of the present invention]
The chemical components and the high calorific value of the oil recovered in the apparatus of the present invention were measured by an element analyzer as follows. 0.5 g to 1 g of the oil sample collected from the apparatus of the present invention is injected into the combustion tube, and the sample burned at about 1,000 ° C. is reduced in the reaction tube, separated by the component according to the moving speed while passing through the GC column, . The column used is Porapack PQS (C, H, N, S component) and SM3A (O component). Also, the high calorific value (HHV) was calculated using each component ratio data.
- High calorific value formula -
HHV (MJ / kg) = 0.3383 * C + 1.422 * (H? O / 8)
[Comparative Example 1]
The soil contaminated with crude oil was prepared and the concentration of total petroleum hydrocarbon (TPH) was measured by extracting contaminants from the contaminated soil. The calculated results are shown in Table 1 below.
[Comparative Example 2]
The elemental ratios and high calorific value (HHV) of the major elements carbon, hydrogen, nitrogen, sulfur, and oxygen in crude oil were measured and the calculated results are shown in Table 2 below.
[Example 1 using residual oil measurement method of contaminated soil]
The soil contaminated with crude oil was placed in a soil container in the reactor, the pressure was adjusted to 60 bar, and water was pumped into the preheater at a rate of 1 mL / min. At the same time, the reactor temperature was maintained at 275 DEG C for 60 minutes. After the reaction was completed, the temperature and pressure were both adjusted to room temperature and normal pressure. The concentration of the contaminants remaining in the soil in the soil container and the recovered oil separated from the extracted water were calculated and the results are shown in Table 1.
[Example 2 using the method of measuring the oil recovered in the apparatus of the present invention]
Table 2 shows the calculation results of the elemental ratio and the high calorific value of the recovered oil in the apparatus of the present invention.
At this time, the soil contaminated with crude oil was used as the soil material contaminated with crude oil, but the present invention is not limited thereto.
Thus, it can be seen that the apparatus of the present invention can easily recover the oil contained in the pollutant extracted by the sub-coefficient.
It will be understood by those skilled in the art that various changes in form and details may be made therein without departing from the scope of the present invention as defined by the appended claims.
1000: Contaminated soil purification and oil recovery device using subcycle according to the present invention
10: Water tank
11: Screen filter
20: Pump
30: Storage tank
40: Distributing Transmitter
50: Pressure regulator
60: preheater
70: Reactor
71: soil container
72: soil filter
73: Drying valve
74: Cooling coil
75: cooling means
76: Cooling fan
80: tube particle remover
81: Intrusion free entrance
82: tube particle filter
90: Heat exchanger
100: Flow rate regulator
110: density separator
120: Oil collecting tank
130: Exhaust control valve
140: Collection tube
150: thermos
151: Electric heater
152: first temperature sensor
153: second temperature sensor
160: Pressure gauge
Claims (7)
A pump 20 for pressurizing the water transferred from the water tub 10;
A storage tank (30) for storing the water transferred from the pump (20);
A distributor / distributor 40 for distributing and transferring the water transferred from the storage tank 30 to the water tank 10 and the pressure regulator 50;
A pressure regulator 50 for pressurizing or depressurizing the water transferred from the distributor / transporter 40 to a subcritical pressure condition;
A preheater (60) for heating the water transferred from the pressure regulator (50) to a temperature condition of a subcritical state to generate a subcritical coefficient;
A reactor (70) for passing the submerged coefficient transferred from the preheater (60) through the contaminated soil loaded therein to dissolve contaminants contained in the contaminated soil into the submerged coefficient;
A tube particle remover 80 for filtering particles, floating matters, and impurities of contaminants included in the submixture transferred from the reactor 70;
A heat exchanger (90) for cooling the subcritical water transferred from the tube particle remover (80) to generate water at room temperature;
A flow rate controller 100 that adjusts the flow rate of the water at room temperature sent from the heat exchanger 90 to a constant value; And
And a density separator 110 for separating the water at room temperature transferred from the flow rate regulator 100 by density difference to discharge the oil to the oil collecting tank 120 and discharge the water at room temperature to the water tank 10 (1000). ≪ RTI ID = 0.0 > (1000) < / RTI >
(1000). The apparatus for collecting and purifying contaminated soil according to claim 11, wherein the plurality of the pollutants are disposed in parallel in a row.
A soil container 71 installed in the reactor 70 and loaded with contaminated soil so that the contaminated soil loaded on the soil container 71 is not discharged to the preheater 60 and the heat exchanger 90; And a soil filter (72) surrounding a predetermined portion of the soil container (71)
Wherein the soil container (71) is detachably installed in the reactor (70).
Further comprising a drying valve (73) communicating with an upper end of the reactor (70) and discharging the steam generated by the submerged coefficient to the contaminated soil so that the contaminated soil is dried, Soil remediation and oil recovery apparatus (1000).
A plurality of exhaust control valves 130 for regulating the amount of feed of the submerged feeds respectively transferred from the plurality of reactors 70 to the tube particle remover 80; And
And a collecting pipe (140) collecting the aseism coefficients transferred from the plurality of discharge control valves (130) and transferring them to the tube particle remover (80). Device (1000).
A penetration-free inlet 81 for introducing a submerged coefficient transferred from the reactor 70 into the tube-particle remover 80 inside the tube-particle remover 80; And a tubular particle filter (82) for filtering particles, floating matters, and impurities of the contaminants contained in the submergence coefficient in which the water level rises, are installed, respectively. .
And a screen filter (11) for filtering the contaminants contained in the water at room temperature transferred from the density separator (110) is installed inside the apparatus (1000).
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Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107386264A (en) * | 2017-09-19 | 2017-11-24 | 河海大学 | A kind of vacuum backwashes Polluted Soil in-situ remediation method from migrating |
CN111250523A (en) * | 2020-01-15 | 2020-06-09 | 北京石油化工学院 | Gas thermal desorption heating well with longitudinal soil heated uniformly |
CN112547779A (en) * | 2021-01-15 | 2021-03-26 | 上海沫依生物科技有限公司 | Automatic soil recycling and repairing equipment |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
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KR101276118B1 (en) | 2011-01-24 | 2013-06-18 | 전남대학교산학협력단 | Purification method for contaminated soil using subcritical water |
KR101339775B1 (en) | 2012-11-30 | 2013-12-11 | 전남대학교산학협력단 | Purification system for contaminated soil using subcritical water |
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Patent Citations (2)
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KR101276118B1 (en) | 2011-01-24 | 2013-06-18 | 전남대학교산학협력단 | Purification method for contaminated soil using subcritical water |
KR101339775B1 (en) | 2012-11-30 | 2013-12-11 | 전남대학교산학협력단 | Purification system for contaminated soil using subcritical water |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN107386264A (en) * | 2017-09-19 | 2017-11-24 | 河海大学 | A kind of vacuum backwashes Polluted Soil in-situ remediation method from migrating |
CN111250523A (en) * | 2020-01-15 | 2020-06-09 | 北京石油化工学院 | Gas thermal desorption heating well with longitudinal soil heated uniformly |
CN112547779A (en) * | 2021-01-15 | 2021-03-26 | 上海沫依生物科技有限公司 | Automatic soil recycling and repairing equipment |
CN112547779B (en) * | 2021-01-15 | 2022-12-09 | 中化学土木工程有限公司 | Automatic soil recycling and repairing equipment |
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